The Issue Did the site in question fail to meet monitoring and retrofitting requirements within the schedules established under Chapter 17-61, Florida Administrative Code, and thereby not be eligible for the Early Detection Incentive Program?
Findings Of Fact The State Underground Petroleum Environmental Response (SUPER) Act of 1986 was enacted as Chapter 86-159, Laws of Florida, and codified primarily in Section 376. 071, Florida Statutes. It provides for the expeditious cleanup of property contaminated as the result of storage of petroleum or petroleum product. As part of the SUPER Act, the legislature created the program which is of direct relevance in this litigation. The EDI Program, Section 376.3071(9), Florida Statutes,, provides for state cleanups of sites contaminated as a result of a discharge from a petroleum storage system. Petitioner now owns and operates a facility at Route 1, Box 167 Jay, Florida. (Hearing Officer's Exhibit 2). The facility contains two underground petroleum storage tanks which were installed on or before 1970. (T8, 9). Monitoring wells were installed for the tanks in December, 1988. (T7). Monitoring wells are pipes which are installed in the ground around a tank excavation to allow for detection of leaks from the tanks. (T8).
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 site owned by Petitioner be determined to be ineligible for the Early Detection Incentive Program, pursuant to Section 376.3071(9), Florida Statutes. DONE AND ORDERED this 9th day of January, 1990, in Tallahassee, Leon County, Florida. STEPHEN F. DEAN Hearing Officer Division of Administrative Hearings The DeSoto 1230 Apalachee Parkway Tallahassee, FL 32399-15SO (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 9th day of January, 1990. COPIES FURNISHED: E. Gary Early, Esq. Assistant General Counsel Florida Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400 Mr. Thomas L. MCNAUGHTON MCNAUGHTON's Store Route 1 Jay, FL 32565 Mr. Dale H. Twachtmann Secretary Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400 Daniel H. Thompson, Esq. General Counsel Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400
Findings Of Fact Since 1984, the Department has been the state agency charged with the responsibility to establish rules and regulate underground pollutant storage facilities in Florida. In 1988, the Legislature added the administration of the newly enacted Florida Petroleum Liability and Restoration Program to the Department's duties. The program was to be established on or before January 1, 1989. The Applicant is the owner of a petroleum storage system in Jacksonville, Florida. Since 1984, it has been subject to the rules regarding underground pollutant storage facilities promulgated by the Department. On September 18, 1989, an odor indicative of possible petroleum contamination was discovered at the site during the installation of monitoring wells. A Discharge Notification Form was sent to the Department by the Applicant on October 23, 1989. The form advised that there were no leaks in the system. It was suggested that the odor may have resulted from surface spill at the site over a number of years. In response to the notification, an inspection of the site was completed by the Department on December 5, 1989. The inspection revealed the following on-site violations: Registration requirements were not being met. The forms had not been updated to include the presence of monitoring wells and overfill protection at the facility. Two underground tanks had not been properly abandoned. Inventory and reconciliation records had not been properly maintained, as required by rule since 1987. This violation was reviewed, and discussed in detail with on-site representatives of the Applicant. The monitoring wells were not installed by the time deadlines set forth in the Department's rules regarding stationary tanks. Since the wells were installed in September 1989, samples had not been taken for visual signs of petroleum contamination. The purpose of the system is to allow the owner of the storage tanks to learn if there is a leak in the tanks that can be quickly controlled to limit contamination. The day after the inspection, the Applicant applied for a determination of eligibility for participation in the restoration coverage portion of the new Florida Petroleum Liability Insurance and Liability Program. An affidavit was signed stating that all of the Department's rules regarding stationary tanks were being complied with by the Applicant. Six days after the inspection, the Department sent the Applicant written notice of the results of the inspection. The Applicant was given time frames and instructions for correcting the listed violations that could be corrected. A contamination assessment and clean up were also required in the letter. This letter did not address the issue of eligibility for the restoration funding program because that was a matter unrelated to the inspection results. On March 7, 1990, the Department determined the facility was ineligible for participation in the restoration funding provided by the Florida Petroleum Liability and Coverage Program. The following reasons were given: Failure to properly abandon underground storage tanks, pursuant to Section 17-61.050(3)(c), Florida Administrative Code. Failure to maintain inventory records, reconciliations, and significant loss/gain investigation as per Section 17-61.050(4)(c), Florida Administrative Code. Failure to install monitoring system and overfill protection by the dates set forth in Section 17-61.06(2)(c)2, Florida Administrative Code. Failure to properly monitor leak detection system, pursuant to Section 17-61.050(5)(c), Florida Administrative Code. The 10,000 gallon fuel oil tank and the 3,000 gallon waste oil tank present at the facility were abandoned in March 1990. The notice issued by the Department after its inspection in December 1989, gave the Applicant sixty days after receipt of the notice to properly abandon the tanks. The Applicant substantially complied with this requirement after the written notice was received. Although the Applicant failed to maintain the inventory records, reconciliations, and significant loss/gain investigations required by the Department rules, some of these violations had been corrected prior to the Department's inspection in December 1989. Correct inventory recordkeeping was discussed during the inspection, and the need to immediately implement the proper recordkeeping practices was emphasized in the post-inspection notice of violations. All of the recordkeeping violations were not cured until August 1990. The records kept by the Applicant during the noncompliance period from 1984 to August 1990, did not provide a substantially equivalent degree of information regarding possible leak detection or prohibited discharges as the required recordkeeping procedures. Two underground stationary storage tanks on the site have been part of the Applicant's petroleum storage system since 1970 and 1975, respectively. The monitoring wells and overfill protection for these tanks should have been in place by December 31, 1987. Neither monitoring system was installed until September 1989. The Applicant began the contract negotiations for installation in September 1988. The Applicant did not demonstrate that the facility contained an alternative procedure between December 31, 1987 and September 1989, that provided a substantially equivalent degree of protection for the lands, surface waters, or groundwaters of the state as the established requirement for monitoring wells and overfill protection. In December 1989, the Department's notice advised the Applicant that the monitoring wells should be sampled monthly for visual signs of petroleum contamination. Since April 1990, the Applicant has been completing the monthly sampling in the monitoring wells as part of its leak detection system, as required by the Department's rule regarding underground stationary tanks.
Recommendation Accordingly, it is RECOMMENDED: That the Department enter a Final Order denying Petitioner's application for restoration coverage in the Florida Petroleum Liability and Restoration Program at the Jacksonville location. DONE and ENTERED this 28 day of December, 1990, in Tallahassee, Leon County, Florida. VERONICA E. DONNELLY 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 _28_ day of December, 1990. APPENDIX TO RECOMMENDED ORDER The proposed findings of fact submitted by Petitioner are addressed as follows: Rejected. Improper interpretation of law. As for the facts in the first sentence, they are accepted. See HO #8. Rejected. Irrelevant. See HO #9. Rejected. Contrary to fact. See HO #9 and #11. Rejected. Contract to fact. See HO #11. Rejected. Contrary to fact. See HO #12 and #13. Rejected. Contrary to fact. Improper shifting of duty ad legal responsibility. Rejected . Improper application of law. The Respondent's proposed findings of fact are addressed as follows: Accepted. Accepted. Accepted. Accepted. See HO #8. Accepted. See HO #8. Accepted. See HO #3. Accepted. See HO #3. Accepted. See HO #3. Accepted. See HO #5. Accepted. Accepted. See HO #4. Accepted. See HO #4. Accepted. Accepted. See HO #6. Accepted. See HO #4 and #6. Accepted. See HO #4 and #6. Accepted. Accepted. Accepted. See HO #4 and #9. Accepted. Accepted. See HO #4 and #9. Accepted. Accepted. See HO #9. Accepted. See HO #4 and #10. Accepted. Rejected. Contrary to fact. See HO #10. Accepted. Accepted. Accepted. See HO #10. Accepted. See HO #3 and #12. Accepted. Accepted. See HO #13. Accepted. Accepted. See HO #6. Accepted. See HO #4 and #6. Accepted. See HO #6. Accepted. Rejected. Not established by evidence. See HO #6. Accepted. Accepted. Accepted. Accepted. See HO #7. Accepted. Accepted. COPIES FURNISHED: William Chadeayne, Qualified Representative 8933 Western Way, Suite 16 Jacksonville, Florida 32256 Janet E. Bowman, Esquire Assistant General Counsel Department of Environmental Regulation 2600 Blairstone Road Tallahassee, Florida 32399-2400 Dale H. Twachtmann, Secretary Department of Environmental Regulation 2600 Blairstone Road Tallahassee, Florida 32399-2400 Daniel H. Thompson, Esquire General Counsel Department of Environmental Regulation 2600 Blairstone Road Tallahassee, Florida 32399-2400
Findings Of Fact Petitioner, SuperAmerica of Florida, Inc. (SuperAmerica) is affiliated with SuperAmerica Group, Inc., a corporation with headquarters in Lexington, Kentucky. SuperAmerica markets petroleum products from convenience store facilities in an eleven-state area concentrated in the Ohio Valley and upper Midwest. In 1985, SuperAmerica began constructing convenience store facilities in Florida, and opened its first stores in 1986. It installed state-of-the-art petroleum storage tanks, lines, dispensers and leak detection equipment at each new site. Casey McKenzie became SuperAmerica's administrative manager for its Florida facilities in October 1990. At that time there were approximately thirty-seven SuperAmerica convenience store facilities in Florida. Mr. McKenzie's duties included monthly reporting to corporate headquarters, environmental compliance, and emergency petroleum discharge response at the Florida sites. Mr. McKenzie left Florida in June 1993, after SuperAmerica completed its sale to Shell Oil Company of what was then over fifty sites. Virtually all of SuperAmerica's Florida sites had three separate tanks for different grades of gasoline, plus one tank for diesel fuel. The tanks were either 12,000 or 8,000 gallons in volume. Each site had between twelve and sixteen dispensers, and each dispenser had up to six nozzles for dispensing different grades of gasoline and diesel fuel. The Florida sites, including the sites at issue, experienced high volume sales as they were open twenty-four hours a day and were located in areas of heavy private and commercial traffic. The volume of sales required frequent storage tank refilling, sometimes daily or every other day. The volume of sales and frequent refillings made petroleum discharges in the form of spills, splashes and drips caused by human error a common occurrence. Customer overfill incidents involving small quantities of fuel were the most common occurrence. Other spills resulted when the underground storage tanks were being filled. SuperAmerica had procedures to minimize the risk of spills and to detect the spills or discharges. The tanks were all fitted with Gilbarco automatic tank gauging devices which computed volume of fuel and water in the tanks, the inches of fuel and water and the temperatures inside the tanks. Operators or staff also used long sticks to manually measure volume of fuel and water in the tanks. And a third method of measure was a daily sales inventory. Mr. McKenzie received the reports of these inventories on a periodic basis and store operators were instructed to watch for, and report unexplained discrepancies. To his knowledge, during his tenure as administrative manager, there were no unexplained discrepancies nor discrepancies in those inventories resulting from leaking tanks. At each site, including the sites at issue, there were six groundwater monitoring wells. The wells were generally installed during installation of the underground storage tanks in the same excavation pit. The monitoring wells were accessible through manhole covers on the surface of the concrete pad. Locked caps below the manhole covers were intended to maintain the environmental integrity of the wells. Water entered the wells through slots in the pipes which lined the well, from about a foot below the pad surface and extending below the water table. Prior to June 1991, the SuperAmerica area managers took water samples from the wells each month, performed sight and smell tests and recorded the results on an inspection report. Beginning in June 1991, SuperAmerica hired National Environmental Services and Testing (NEST) to perform the monthly groundwater sampling from the monitoring wells. NEST used a vapor monitoring device (organic vapor analyzer - OVA) in the monitoring wells to detect the pressure of organic vapors in addition to performing groundwater sampling. The monitoring wells at the seven sites at issue contained groundwater. At various times, as more specifically addressed below, NEST's monitoring reports for the sites at issue noted elevated organic vapor readings, odor present, and product in the form of skim, light skim, or sheen. Mr. McKenzie had procedures in place and carried out those procedures to respond to large volume spills or accidents above ground, as well as catastrophic leaks of underground tanks. These were his primary concerns. He did not expect a catastrophic leak in the relatively new equipment, and none occurred. Mr. McKenzie did not attribute any of the reports of elevated vapor readings, odor or presence of petroleum or diesel product in the form of skim or sheen, as evidence of tank or line failure. There are other rational explanations for the readings. Specifically, rainfall could easily dissolve and wash spilled fuel, antifreeze, oil or road grease into cracks in the pad, into manhole covers and onto the ground where it could easily seep into the monitoring wells. As conceded by counsel for SuperAmerica, there was a discharge at each of the seven sites, for purposes of the FPLRIP program. Printed text on the top of the Discharge Reporting Forms advises facilities of their obligation to report discharges or suspected releases within one day of discovery. For each site at issue, monitoring well records contained evidence of odor, product or elevated vapor readings more than one day prior to SuperAmerica's filing Discharge Reporting Forms. After filing Discharge Reporting Forms with DEP, Mr. McKenzie contacted Tanknology Corporation to schedule testing of the tanks and lines. The company was busy and was not able to complete the tests until some time (more than three days) after Mr. McKenzie filed the Discharge Reporting Forms. SuperAmerica did not intentionally cause a discharge at any of the sites, nor intentionally disable leak detection devices. When the Discharge Reporting Forms were filed, Mr. McKenzie was not aware of any spill or other discharge in excess of 25 gallons for which he had failed to file a reporting form within twenty-four hours. As of the date of the hearing there was no conclusive evidence of what caused the odor, product and elevated OVA readings in the monitoring wells. SuperAmerica's expert conjectures that they were caused by surface water runoff, sloppy transport deliveries, customer overfills and other routine problems of the high-volume facilities. In determining whether SuperAmerica was eligible under FPLRIP with regard to the sites at issue, DEP's program administrator, William Truman, considered only whether SuperAmerica properly reported suspected releases and whether it timely tested the storage systems. Those were appropriate considerations. The basis for denial as to each site is more specifically described below. On January 19, 1993, counsel for the parties executed a joint stipulation relating to an eighth facility site. In that stipulation, the agency recited its agreement that failure to report suspected releases within one working day of discovery could no longer, standing alone, serve as a basis for denial of restoration coverage eligibility under 1992 amendments to Chapter 376, Florida Statutes, governing FPLRIP. The stipulation also recited: Nothing in this Joint Stipulation shall be construed to mean that violation of the discharge response requirements contained in section 376.3072(2)(d), F.S. (1992) , and implemented in rules 17-769, 17-769.600(15) and (16), Florida Administrative Code is no longer a valid basis for denial of eligibility for restoration coverage on an incident by incident basis under FPLRIP. (Petitioner's Exhibit No. G) Hudson-DEP Facility No. 51-8837646 DOAH Case 92-6871 (Site 8023) At all material times, SuperAmerica was the owner/operator of a petroleum storage tank system located at 9508 SR 52, Hudson, Pasco County, Florida. The facility consisted of four underground storage tanks (USTs): two 12,000 gallon gasoline USTS; one 8,000 gallon gasoline UST; and one 8,000 gallon diesel UST. The USTs were installed in or about March 1988. On August 21, 1991, NEST sampled the monitor wells at the facility. There was an odor in monitor wells four, five and six. The OVA reading for monitor well five was 3800 ppm, while the OVA reading for monitor well six was 2800 ppm. On September 16, 1991, NEST sampled the monitor wells at the facility. There was an odor in monitor wells four and six. The OVA reading for monitor well four was 1000 ppm, while the OVA reading for monitor well six was 2000 ppm. On October 15, 1991, NEST sampled the monitor wells at the facility. There was an odor in monitor wells four, five and six. The OVA reading for monitor well four was 2400, five was 2900 ppm, and the OVA reading for monitor well six was 2200 ppm. On November 20, 1991, NEST sampled the monitor wells at the facility. There was an odor in monitor wells four, five and six. The OVA reading for monitor well four was 3600, five was 3000 ppm, and the OVA reading for monitor well six was 6900 ppm. On December 4, 1991, NEST sampled the monitor wells at the facility. There was an odor in monitor wells four, five and six. The OVA reading for monitor well four was 3100, five was 2800 ppm, and the OVA reading for monitor well six was 5100 ppm. On January 4, 1992, NEST sampled the monitor wells at the facility. There was an odor in monitor wells four, five and six. The OVA reading for monitor well four was 1100, five was 2400 ppm, and the OVA reading for monitor well six was 2900 ppm. On March 6, 1992, NEST sampled the monitor wells at the facility. There was product in monitor wells four, five and six. The report also indicates there was an odor in monitor wells five and six. The OVA reading for monitor well six exceeded 10,000 ppm. Elevated readings and odor persisted in well six in April and June. On July 14, 1992, NEST sampled the monitor wells at the facility. There was an odor in monitor wells five and six. The OVA reading for monitor well four was 1400 ppm, while the OVA reading for monitor well six was 2600 ppm. On or about July 24, 1992, SuperAmerica filed a Discharge Notification Form with the Department. The form was signed by Casey McKenzie. The form indicates the date of discovery was July 14, 1992 (the most recent date on which NEST sampled the monitor wells). The method of initial discovery was a Vapor Reading Report from Monitoring Company. The Type of pollutant discharged was Unleaded gasoline. The Cause of leak and Estimated number of gallons lost were both Unknown. On or about August 26, 1992, Tanknology Corporation International performed tank and line tests at the site and issued a certificate of tightness. The test report commented that one dispenser had leaks at the nozzle when pumping and the tester had the store put an Out of Order sign on the nozzle. On or about September 1, 1992, the Department issued an order declaring SuperAmerica site no. 8023 eligible for FPLRIP restoration coverage for the reported discharge. On October 6, 1992, and again on October 21, 1993, the Department issued its amended orders of ineligibility for FPLRIP restoration coverage for the discharge reported. Melbourne-DEP Facility No. 05-8840685 DOAH Case 93-4402 (Site 8024) At all material times, SuperAmerica was the owner/operator of a petroleum storage tank system (site no. 8024) located at 700 West New Haven Avenue, Melbourne, Brevard County, Florida. The facility consisted of four underground storage tanks: two 12,000 gallon gasoline USTs; one 8,000 gallon gasoline UST; and one 8,000 gallon diesel UST. The USTs were installed in or about August 1988. On December 13, 1991, NEST sampled the monitor wells at the above- referenced facility. There was product and an odor in all six wells. The OVA readings for the monitor wells ranged from 4200 ppm to 8500 ppm. On January 16, 1992, NEST sampled the monitor wells at the above- referenced facility. There was product and an odor in all six wells. The OVA readings for the monitor wells ranged from 1200 ppm to 8000 ppm. On February 19, 1992, NEST sampled the monitor wells at the above- referenced facility. There was product present in wells one, two, five and six. There was an odor in all six wells. The OVA readings for the monitor wells ranged from 2100 ppm to an excess of 10,000 ppm. On March 19, 1992, NEST sampled the monitor wells at the above- referenced facility. There was product and an order in monitor wells one and five. The OVA readings for wells one and five both exceeded 10,000 ppm. Odor and elevated readings persisted in April. On June 20, 1992, NEST sampled the monitor wells at the above- referenced facility. The OVA reading for well six exceeded 10,000 ppm. There was odor in wells one, five and six. The report contains the notation Charlie will check early July. If readings have not declined, he will file DNF. On July 9, 1992, NEST sampled the monitor wells at the above- referenced facility. The OVA readings for the wells ranged from 220 ppm to 7100 ppm. There was odor in wells three, four, five and six. On July 17, 1992, Brevard County conducted an inspection of the facility. The Natural Resources Management Division of Brevard County is DEP's designated local program for purposes of the FPLRIP. The report noted the excess OVA readings since December. It required a tightness test and investigation into the source of the discharge, and it required a contamination assessment. It also noted that administrative action will be taken on this facility for major violation of 17-761, Florida Administrative Code . . . (Respondent's Exhibit No. 1) On or about July 21, 1992, SuperAmerica filed a Discharge Notification Form with the Department. The DNF indicates the date of discovery was July 9, 1992 - the date on which NEST sampled the monitor wells. The method of initial discovery was Vapor Readings. The Type of pollutant discharged was Unleaded gasoline. The Cause of leak and the "Estimated number of gallons lost were both Unknown. On or about July 28, 1992, Tanknology Corporation International performed tank and line tests at the site and issued a certificate of tightness. On or about July 1, 1993, the Department issued its Order of Ineligibility for FPLRIP restoration coverage for the reported discharge. Cocoa-DEP Facility No. 05-8841566 DOAH Case 93-4402 and 93-4403 (Site 8034) At all material times, SuperAmerica was the owner/operator of a petroleum storage tank system (site no. 8034) located at 1600 Clear Lake Road, Cocoa, Brevard County, Florida. The facility consisted of three underground storage tanks: two 12,000 gallon gasoline USTs; and one 8,000 gallon UST. The USTs were installed in or about January 1989. On December 13, 1991, NEST sampled the monitor wells at the above- referenced facility. There was product present in well number five. There was an odor present in all of the wells. The OVA readings for wells one, two, three, four and six all exceeded 10,000 ppm. On January 16, 1992, NEST sampled the monitor wells at the above- referenced facility. There was an odor present in wells one through four and well six. With the exception of well three, the OVA readings for all of the wells exceeded 10,000 ppm. On February 16, 1992, NEST sampled the monitor wells at the above- referenced facility. There was an odor present in all of the wells. The OVA readings for the wells ranged from 2100 ppm to an excess of 10,000 ppm. On March 19, 1992, NEST sampled the monitor wells at the above- referenced facility. There was an odor present in all of the wells. The OVA readings for the wells ranged from 4100 ppm to an excess of 10,000 ppm. On or about March 31, 1992, Brevard County conducted an inspection at site no. 8034. The Pollutant Storage Tank System Inspection Report Form cover sheet prepared by the Brevard County Inspector noted in part: From 12/31/91, OVA readings in all wells have exceeded reportable quantity (>500 ppm); in some instances, 5 wells >10,000 ppm. (Respondent's Exhibit No. 2) The Inspection form also noted the facility failed to report Suspected releases within one working day of discovery. The above-referenced Underground Storage Tank Compliance Inspection Form also noted the facility failed to report Confirmed releases (positive response of a release detection device) within one working day of discovery (Respondent's Exhibit No. 2). The form requires a DRF within one day and a tightness test ASAP. On or about March 31, 1992, SuperAmerica filed a Discharge Notification Form with the Department. The DNF was signed by Mr. Casey McKenzie. The DNF indicated the date of test or discovery was March 30, 1992. The method of initial discovery was a DER Compliance Audit. The DNF does not contain information concerning the estimated number of gallons lost. The Cause of leak and the Type of pollutant discharged were both Unknown. On or about April 5, 1992, Tanknology Corporation International performed tank and line tests at the site and issued a tightness certificate. The test report noted no product visible in the monitoring wells, but odor was present. On July 1, 1993 and again on October 21, 1993, the Department issued its order and amended order of ineligibility for FPLRIP restoration coverage for the reported discharge. Sarasota-DEP Facility No. 58-8840985 DOAH Case 93-5734 (Site 8035) At all material times, SuperAmerica was the owner/operator of a petroleum storage tank system (site no. 8035) located at 4405 North Washington Boulevard, Sarasota, Sarasota County, Florida. The facility consisted of four underground storage tanks: two 12,000 gallon gasoline USTs; one 8,000 gallon gasoline UST; and one 8,000 gallon diesel UST. The USTs were installed in or about August 1988. On September 17, 1991, NEST sampled the monitor wells at the above- referenced facility. There was product present in well six. There was an odor in all six wells. The OVA reading for wells one, two, three and five all exceeded 1500 ppm. On October 18, 1991, NEST sampled the monitor wells at the above- referenced facility. Both product and an odor were present in all six wells. The OVA readings for wells one through five exceeded 700 ppm. On November 22, 1991, NEST sampled the monitor wells at the above- referenced facility. Both product and an odor were present in all six wells. The OVA readings for wells one, two and five were 2200 ppm, 1200 ppm and 4000 ppm. On December 10, 1991, NEST sampled the monitor wells at the above- referenced facility. Product and odor were present in all six wells. The OVA reading for well five was 3100 ppm. On January 20, 1992, NEST sampled the monitor wells at the above- referenced facility. There was both product and an odor present in all six wells. The OVA reading for well five was 3200 ppm. On February 12, 1992, NEST sampled the monitor wells at the above- referenced facility. There was both product and an odor present in all six wells. The OVA reading for well two was 900 ppm. On March 11, 1992, NEST sampled the monitor wells at the above- referenced facility. There was product in all six wells and odor present in wells one, two and five. The OVA reading for well two was 900 ppm. On April 12, 1992, NEST sampled the monitor wells at the above- referenced facility. There was both product and an odor present in wells one, two and three. On or about April 16, 1992, Sarasota County conducted a routine inspection at the above-referenced facility. The Sarasota County Pollution Control Division is DEP's designated local program agency for purposes of FPLRIP. On the Pollutant Storage Tank System Inspection Report Form the Sarasota County Inspector noted: Monitor wells 1, 2, 3 and 5 had OVA readings exceeding 5000 ppm. - High readings and product in wells has been recorded in monthly report by the facility since October, 1991. (Respondent's Exhibit 4) The inspector also noted the facility Has recorded high OVA readings in several MW's but not filed DRF. The County Inspector also noted the facility failed to report Any spill, overfill, or other discharge within one working day of discovery and that the facility failed to report Suspected releases within one working day of discovery. The County Inspector made the following notations on the back of the report: Monitoring well log indicates excessive contamination free product in all wells high OVA readings as [far] back as October '91 no records of any tightness testing in regards to the increase of contamination levels found in wells. DRF on file? (Respondent's Exhibit 4) A letter from Sarasota County dated April 22, 1992, required laboratory analysis of monitor well water within 45 days. The analysis was done by NEST and was provided to Sarasota County on June 29, 1992. On July 7, 1992, Sarasota County received the report and requested that SuperAmerica file a Discharge Reporting Form due to the appearance of excessive contamination. On or about July 15, 1992, SuperAmerica filed a DNF with the Department. The DNF indicates July 14, 1992 as the Date of receipt of test results or discovery. On or about August 29, 1992, Tanknology Corporation International performed tank and line tests at the site and issued a certificate of tightness. On or about September 17, 1993, the Department issued its order declaring SuperAmerica ineligible for FPLRIP restoration coverage for the reported discharge. Clearwater DEP Facility No. 52-8944446 DOAH Case No. 93-4406 (Site 8036) At all times, SuperAmerica was the owner/operator of a petroleum storage tank system (site no. 8036) located at 4450 Easy Bay Drive, Clearwater, Pinellas County, Florida. The above- referenced facility consisted of four underground storage tanks: two 12,000 gallon gasoline USTs; one 8,000 gallon gasoline UST; and one 8,000 gallon diesel UST. The USTs were installed in or about August 1989. On September 16, 1991, NEST sampled the monitor wells at the above- referenced facility. The OVA reading for well five was 8000 ppm while the OVA reading for monitor well six was 3000 ppm. On October 17, 1991, NEST sampled the monitor wells at the above- referenced facility. There was product and an odor present in well five. The OVA reading for well five was 8500 ppm. On January 1, 1992, NEST sampled the monitor wells at the above- referenced facility. The OVA reading for wells four and five was 1100 ppm. On February 6, 1992, NEST sampled the monitor wells at the above- referenced facility. There was product present in well five. The OVA reading for well five was 400 ppm. On March 11, 1992, NEST sampled the monitor wells at the above- referenced facility. The OVA reading for well five was 2800 ppm. On April 7, 1992, NEST sampled the monitor wells at the above- referenced facility. The OVA reading for well five was 650 ppm. On July 13, 1992, NEST sampled the monitor wells at the above- referenced facility. The OVA reading for well five was 1100 ppm. Casey McKenzie prepared a Discharge Notification Form but did not file it because he believed the local agency had instructed him to hold it pending further investigation. On or about August 28, 1992, Tanknology Corporation performed tank and line tests at the site and issued a Certificate of Tightness. On October 12, 1992, Pinellas County conducted a routine inspection at the above-referenced facility. The HRS Pinellas County Health Unit is the agency's designated local agency for FPLRIP. The County Inspector made the following notation on the Inspection Report Form Cover Page: What actions were taken in response to positive responses in one or more monitor wells for the following months - 10/91; 9/91; 11/91; 1/92; 2/92; 3/92; 4/92; 7/92 - provide copy of monitor these monitor reports - take appropriate actions at this time. (Respondent's Exhibit 5) On or about October 27, 1992, SuperAmerica filed the July 13, 1992 DNF with the Department. The DNF reflected a discovery date of July 13, 1992. The DNF indicated the method of initial discovery was a vapor reading from monitor well testing company. On or about July 1, 1993, the Department issued its order declaring SuperAmerica ineligible for FPLRIP restoration coverage for the reported discharge. Englewood-DEP Facility No. 08-8945143 DOAH Case 93-2710 (Site 8038) At all material times, SuperAmerica was the owner/operator of a petroleum storage tank system (site no. 8038) located at 2710 South McCall Road, Englewood, Charlotte County, Florida. The facility consisted of four USTs: two 12,000 gallon gasoline USTs; one 8,000 gallon gasoline UST; and one 8,000 gallon diesel UST. The USTs were installed in or about September 1989. On December 10, 1991, NEST sampled the monitor wells at the above- referenced facility. The OVA reading for well four was 6200 ppm while the OVA reading for monitor well five was 9800 ppm. On January 20, 1992, NEST sampled the monitor wells at the above- referenced facility. The OVA reading for well four was 2000 ppm while the OVA reading for monitor well five was 1100 ppm. On February 13, 1992, NEST sampled the monitor wells at the above- referenced facility. The OVA reading for well four was 1500 ppm. On April 10, 1992, NEST sampled the monitor wells at the above- referenced facility. The OVA reading for well four was 1100 ppm while the OVA reading for monitor well five was 5900 ppm. An Interoffice Memo dated April 24, 1992, from Mr. McKenzie to the manager of store no. 8038 provided in part: The monthly test of your store's monitor wells revealed the following results which need to be addressed: Monitor well number 5 showed vapor readings exceeding 5900 PPM. This is a reportable quantity to the DER. No previous results have show [sic] levels this high. (Petitioner's Exhibit 38C) This latter assertion is obviously in error given the fact that in December, 1991, the OVA reading for well four was 6200 ppm while the OVA reading for well five was 9800 ppm. On May 12, 1992, NEST sampled the monitor wells at the above- referenced facility. The OVA reading for well four was 2100 ppm while the OVA reading for monitor well five was 3000 ppm. On June 15, 1992, NEST sampled the monitor wells at the above- referenced facility. The OVA reading for well five was 2500 ppm. On July 20, 1992, NEST sampled the monitor wells at the above- referenced facility. The OVA reading for well five was 1100 ppm. On or about July 24, 1992, SuperAmerica filed a Discharge Notification Form with DEP. The DNF was signed by Casey McKenzie. The DNF indicated the Date of Test or discovery was July 20, 1992. The method of initial discovery was Vapor Reading Report from Monitoring Reports. The estimated number of gallons lost and the cause of leak were both unknown. On or about September 1, 1992, Tanknology Corporation International performed tank and line tests at the site and issued a certificate of tightness. On September 4, 1992, Casey McKenzie wrote to DEP's South District Office with regard to the DNFs filed for Englewood Facility and the Punta Gorda Facility. With regard to SuperAmerica's failure to timely report the releases, the letter provided in part: In your letter, you refer to the elevated OVA readings recorded several months ago but not reported. This was simply an error on my part. SuperAmerica began utilizing an outside contractor to perform monitor well sampling at these locations in December. Prior to that, we performed the monthly sampling ourselves using the sight and smell method appropriate for ground water well monitoring... I was not aware of the thresholds for reporting of vapor levels. I was aware we had no sheen or odor present. When our contractor and I finally discussed the importance of the vapor readings and the ramifications involved, we immediately filed Discharge Notification Forms for suspected releases. . . Any errors made in reporting were due to lack of knowledge on my part, ... (Respondent's Exhibit 3) Mr. McKenzie's assertion of ignorance cannot be reconciled with the statements set forth in his Interoffice Memo dated April 24, 1992. See paragraph 85, above. On or about April 23, 1993, and again on October 20, 1993, DEP issued its order and amended order declaring SuperAmerica ineligible for FPLRIP restoration coverage for the reported discharge. Punta Gorda-DEP Facility No. 08-9045849 DOAH Case 93-2711 (Site 8039) At all material times, SuperAmerica was the owner/operator of its petroleum storage tank system (site no. 8039) located at 3035 Tamiami Trail, Punta Gorda, Charlotte County, Florida. The facility consisted of four underground storage tanks: two 12,000 gallon gasoline USTs; one 8,000 gallon gasoline UST; and one 8,000 gallon diesel UST. The USTs were installed in or about January 1990. On December 10, 1991, NEST sampled the monitor wells at the above- referenced facility. There was product in well four. There was an odor in all of the wells. The OVA readings for wells one, three, four, five and six all exceeded 10,000 ppm. On January 20, 1992, NEST sampled the monitor wells at the above- referenced facility. The OVA reading for well two was 600 ppm; well three was 4500 ppm; well four was 900 ppm; and well five was 2500 ppm. On February 20, 1992, NEST sampled the monitor wells at the above- referenced facility. There was an odor present in wells two, three and five. The OVA reading for well one was 6000 ppm; wells two and three were in excess of 10,000 ppm; well four was 4100 ppm; and well five was 3800 ppm. On March 9, 1992, NEST sampled the monitor wells at the above- referenced facility. There was an odor present in wells two, three and five. The OVA reading for well two was in excess of 10,000 ppm; well three was 2000 ppm; and well four was 3000 ppm. 26 On April 10, 1992, NEST sampled the monitor wells at the above- referenced facility. There was an odor present in wells two and three. The OVA reading for well two was 1500 ppm while the OVA reading for well three was 550 ppm. On May 14, 1992, NEST sampled the monitor wells at the above- referenced facility. There was an odor present in wells two and three. The OVA reading for well two was 2200 ppm while the OVA reading for well three was 1100 ppm. On June 15, 1992, NEST sampled the monitor wells at the above- referenced facility. There was an odor present in well two. The OVA reading for well two was 7300 ppm; well three was 1500 ppm; and well four was 1100 ppm. On July 20, 1992, NEST sampled the monitor wells at the above- referenced facility. There was an odor present in wells two and three. The OVA reading for well one was in excess of 10,000 ppm; well three was 2000 ppm; and well four was 3100 ppm. On or about July 24, 1992, SuperAmerica filed a Discharge Notification Form with the Department. The DNF was signed by Casey McKenzie. The DNF was dated July 24, 1992. However, the DNF did not include the information as to the date of test or discovery of the discharge. The cause of the leak and the estimated number of gallons lost were both unknown. The DNF indicated the method of discovery was a Vapor Reading Report from Monitoring Company. On or about August 27, 1992, the agency conducted an inspection at Site 8039. During the inspection, no obvious odors were detected in the monitoring wells, indicating that there may have been errors in the original OVA readings. The agency directed SuperAmerica to have groundwater samples analyzed. The analysis was provided to the agency on October 27, 1992. On or about August 27 and September 4, 1992, Tanknology Corporation International performed tank and line tests at the sight and issued certificates of tightness. On or about April 23, 1993, and again on October 20, 1993, DEP issued its order and amended order declaring SuperAmerica ineligible for FPLRIP restoration coverage for the reported discharge. North Ft. Myers-DEP Facility No. 36-8631544 DOAH Case 93-4405 (Site 8006) At all material times, SuperAmerica was the owner/operator of a petroleum storage tank system (site no. 8006) located at 4600 Bayline Drive, North Ft. Myers, Lee County, Florida. The facility consisted of four underground storage tanks: two 12,000 gallon gasoline USTs; one 8,000 gasoline UST; and one 8,000 gallon diesel UST. The tanks were installed on or about April 1987. In or about November 1992, SuperAmerica hired Environmental Science and Engineering, Inc. (ESE) to perform an environmental audit in conjunction with SuperAmerica's planned sale of the property. On January 7, 1993, ESE was performing soil borings in the tank farm and pump island areas. Soil samples were being analyzed for the presence of excessive contamination, if any. Those borings were made with a four-inch diameter hand auger. At boring SB-2, near the easternmost fuel island, the ESE employee cracked the fiberglass midgrade unleaded product line with the hand auger causing an underground discharge. SuperAmerica discovered the discharge on January 16, 1992 and filed a Discharge Reporting Form on that same date. On July 1, 1993, DEP issued its Order denying SuperAmerica eligibility for restoration coverage.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is hereby recommended that the Department of Environmental Protection enter its final order denying eligibility to SuperAmerica in cases nos. 92-6871, 93-2710, 93- 2711, 93-4402, 93-4403/93-4404, 93-4406 and 93-5734; granting eligibility in case no. 93-4405; and dismissing case no. 93-2712 (voluntary dismissal). DONE and ENTERED this 6th day of March, 1996, in Tallahassee, Florida. MARY CLARK 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 6th day of March, 1996. APPENDIX TO RECOMMENDED ORDER The findings of fact proposed by both parties, or stipulated by the parties, have been adopted in whole or in substance, except for the following: SuperAmerica's Proposed Findings of Fact. Rejected as unnecessary or immaterial: 11-17, 20-23, 26-29, 39-40, 48-52, 59-66, 72-75, 79-87, 90- 92, 94-96, 98, 101, 104, 106-107, 109-147, 166, 173, 181,183, 203, 211-212, and 220. Rejected as contrary to the weight of evidence or unsupported by credible evidence: 97, 108, 149-155. DEP's Proposed Findings of Fact. These findings have all been adopted in substance. Additional findings have been made however, to explain the background and include facts common to all of the sites. COPIES FURNISHED: Douglas Beason, Esquire Department of Environmental Protection 2600 Blair Stone Road, Suite 654 Tallahassee, Florida 32399 Kenneth Plante General Counsel 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 Virginia B. Wetherell, Secretary Department of Environmental Protection Douglas Building 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 Gary M. Pappas, Esquire POPHAM, HAIK, SCNOBRICH and KAUFMAN, LTD. 4000 International Place 100 Southeast Second Street Miami, Florida 33138 James M. Ellerbe, Esquire SuperAmerica Group Law Department 3499 Dabney Drive Lexington, Kentucky 40509
The Issue Whether Respondent violated Section 381.0065 and Chapter 489, Part III, Florida Statutes (2004), and Florida Administrative Code Chapter 64E-6, by engaging in septic tank contracting without registration as alleged by Petitioner in the Administrative Complaint and Order to Crease Operations, dated January 26, 2005.
Findings Of Fact Based upon observation and the demeanor of the witnesses while testifying, documentary materials received in evidence, stipulation of the parties, and evidentiary rulings during the hearings, and the record compiled, the following relevant and material facts are determined: The Department of Health ("Department"), Lee County Health Department, is the state agency charged with enforcing the statutory provisions pertaining to the practice of septic tank contracting in Florida, pursuant to Chapter 489 Part II and Section 381.0065, Florida Statutes (2004). Violators of these laws are subject to penalty assessments of Section 381.0061, Florida Statutes, and Florida Administrative Code Rule 64E-6.002. At all times relevant to these proceedings, Respondent, Keithon M. Patterson, has not been licensed as a plumber pursuant to Subsection 489.105(3)(m), Florida Statutes (2004). All times relevant to these proceedings, Respondent was doing business using the business name Full Spectrum Home Improvement, Inc. (Full Spectrum). The business is not nor has it ever been licensed under Subsection 489.105(3)(m), Florida Statutes (2004). All times relevant to these proceedings, the City of Cape Coral, Florida, has an ongoing utility expansion program extending city water services and city sewer services to properties within the limits of the city. All homeowners are required to connect or hookup to city water/sewer systems when such services become available in their respective location within the city. Each homeowner connection or hookup process to city- provided water and sewer, once completed, requires the homeowner to get the Department's abandonment permit to abandon their septic system after hookup to the city water/sewer system. Abandonment requires trenching from the street hookup to the water/sewer hookup. It requires disconnection from the home and the septic tank. It requires pumping or emptying of the septic tank followed by a crushing of the septic tank and filling in of soil. Vicki Adams lives in her home located at 3216 Southeast 1st Place, Cape Coral, Florida. When city services extended to her location, she was required to hookup to the city water/sewer system and have her septic tank system abandoned. To abandon a septic tank means to have a registered person, empty the septic tank, crush the septic tank, fill the septic tank space with clean fill, dig up the underground septic lines from the home to the septic tank, remove piping, and fill the trench with clean fill. For reasons of sanitation and safety, a Departmental permit is required for each property owner before they can abandon their private septic tank system. On or about November 22, 2004, Ms. Adams obtained her septic system abandonment permit from the Department. At some undetermined date but subsequent to November 22, 2004, Ms. Adams, for promise of monetary payment, hired Mr. Patterson to connect her home to the city sewer and to abandon her septic tank. When she was leaving for work, Ms. Adams observed Mr. Patterson doing trench work (i.e. digging, removing soil, hauling sod, etc.) and actually laying some pipe. Ms. Adams' son, Jeff, observed Mr. Patterson with a sledge hammer while in their front yard. Ms. Adams told Mr. Patterson where to park the trucks hauling the clean fill needed to fill the hole after the septic tank was crushed. Mr. Patterson rightly pointed out that neither Jeff nor Ms. Adams personally saw him crush the septic tank. However, when Ms. Adams returned home from work that afternoon she saw clean fill in the spot her crushed septic tank once occupied. Ace Septic Service, Inc. (Ace), a Department authorized septic tank contracting company, removed all residue from Ms. Adams' septic tank by pumping the tank contents into its truck. It invoiced Ms. Adams for pumping her tank. Carlos Casanova, manager of Ace at the time, gave undisputed testimony that his company only pumped out Ms. Adams' septic tank--they did not perform abandonment (i.e. crushing of the tank and filling the abandoned hole with fresh soil). Ms. Adams paid Mr. Patterson $790.00 for his work at her home, which included hooking-up her home to the city sewer line and abandoning her septic tank system. Mr. Patterson gave her a receipt indicating that she paid him in full, in cash, received by him, "K.M. Patterson's," on December 8, 2004, by his signature thereon. The receipt, however, is from "Full Spectrum Home Improvement," and under the "Description" states: "50' trench excavation, 50'4 DWV PVC pipe w/fitting, 6" X4" PVC DWV WVE, trench backfill and restoration (w/out sod)." It is abundantly clear from evidence of record that Ms. Adams' septic tank was abandoned, and, for the septic tank abandonment service rendered, Ms. Adams paid Mr. Patterson, who was not registered with the Department as required. Ace Septic Service, Inc. (Ace), a Department-authorized septic tank contracting company, did not abandon Ms. Adams' septic tank. On January 5, 2005, Department inspector, Ms. Pickerill (no first name in the record), went to the Adams' residence to inspect and confirm proper septic tank abandonment. Her inspection included probing the area where the tank had been located, confirming that the tank had been crushed and that clean fill was used to fill the hole. Satisfied by her inspection that Ms. Adams' septic tank had been properly abandoned, Ms. Pickerill signed the Department's abandonment permit for the Adams' property. Nicola Verna's home is located at 4117 Southwest 20th Avenue, Capt Coral, Florida. City sewer and water had been extended to his home, and he was required to hookup to the city water/sewer system and to abandon his septic system. Mr. Verna obtained the Department's septic system abandonment permit on May 7, 2004. At some undetermined time before September 27, 2004, Mr. Verna hired Mr. Patterson to connect his home to the city water/sewer system and to abandon his septic system. At his home site, Mr. Verna observed Mr. Patterson crush his septic tank with a sledgehammer and bring in a truckload of clean fill material that Mr. Patterson placed in the hole where he had crushed the septic tank. The arrangements to have Mr. Verna's septic tank pumped by Ace were made by Mr. Patterson, for which Mr. Verna paid Ace $165.00 for pumping only, evidenced by a September 27, 2004, invoice. As with Ms. Adams, Mr. Casanova gave undisputed testimony that his company only "pumped out the septic tank-- they did not perform septic tank abandonment," the issue in this cause. For services rendered (hooking-up home to city water, irrigation services, to city sewer, and abandoning the septic tank), Mr. Verna paid Mr. Patterson a total of $1,073.00. Mr. Patterson gave Mr. Verna two receipts. One August 16, 2004, receipt from Full Spectrum "for '120' trench for 120' water and irrigation lines, $619.00 paid in full ch# 1083 rec'd by K.M. Patterson." The second September 27, 2004 receipt "for '1 40' trenching sewer line" for a total of $454.00, with notation at the bottom, "deposit ch# 1086, Balance of $200.00 Rec'vd by K. Patterson ch# 1088." Mr. Verna is certain that the two receipts represented his payments to Mr. Patterson for a part of the work he performed in abandoning his sewer system, because Mr. Patterson is the only person who performed those services for him. As with Ms. Adams, Ms. Pickerill went to Mr. Verna's home on December 27, 2004, to conduct her inspection and to confirm Mr. Verna's septic system was abandoned properly. Her probing the area where the tank was located confirmed that it had been crushed and clean fill had been used to fill the hole. Satisfied by her inspection that Mr. Verna's septic tank had been properly abandoned, Ms. Pickerill signed the Department's abandonment permit for the Verna's property. The Department has taken previous enforcement actions for engaging in septic tank contracting without registration against Mr. Patterson. On June 4, 2004, the Department served an Administrative Complaint on Mr. Patterson seeking to impose a $1,500.00 fine for three separate episodes of tank contracting without being a registered septic tank contractor. Mr. Patterson settled the complaint for septic tank contracting without being a registered septic tank contractor with the Department by his agreement to pay a $750.00 fine. The Department memorialized the agreement in its Final Order Number DOH-04-1071-S-HST of September 15, 2004. Mr. Patterson paid his fine of $750.00 in January 2005, but not before the filing of the instant Cease Order entered by the Department in this proceeding. Based upon the above allegation of septic tank contracting without being a registered septic tank contractor with the Department, in the instant proceeding are "repeat violations" for penalty purposes as provided in disciplinary guidelines of Florida Administrative Code Rule 64E-6.002. The Department demonstrated by clear and convincing evidence that Mr. Patterson, did on two separate occasions violate Section 381.0065, and Chapter 489, Part III, Florida Statutes (2004), and Florida Administrative Code Chapter 64E-6, by engaging in septic tank contracting abandonment without registration as alleged by the Department in the Administrative Complaint and Order to Crease Operations, dated January 26, 2005. Mr. Patterson's protestations to the contrary are without merit and unworthy of belief.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Health enter a final order affirming its January 26, 2005, Order to Crease Operations and imposing a $1,000.00 fine against Respondent, Keithon M. Patterson. DONE AND ENTERED this 28th day of July, 2005, in Tallahassee, Leon County, Florida. S FRED L. BUCKINE 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 28th day of July, 2005.
The Issue Whether Petitioner's site located at 2188 N.W. 20th Street, Miami, Florida, is eligible to participate in the Early Detection Incentive Program.
Findings Of Fact Petitioner is the owner of a gasoline service station located at 2188 N.W. 20th Street, Miami, Florida 33142. Tomas Pequeno, Sr., is the President and owner of X.O. # 1 Corporation. International Petroleum currently operates the facility located at 2188 N.W. 20th Street, Miami, Florida 33142 pursuant to a lease agreement with X.O. #1 Corporation. The mailing address of the subject facility and of X.O. #1 Corporation is 12190 S.W. 99th Street, Miami, Florida 33186. Aurelio Rodriguez is part owner of International Petroleum and has been the manager and operator of the facility in question since 1988. Since 1988 Tomas Pequeno, Sr., has delegated authority to his son, Tomas Pequeno, Jr., to act on his behalf with regard to the business of X.O. #1 Corporation and the facility located at 2188 N.W. 20th Street, Miami, Florida 33142. At the subject facility there are six underground storage tanks which receive and dispense petroleum products. These underground storage tanks are owned by X.O. #1 Corporation and constitute part of the property leased to International Petroleum. At all times pertinent to this proceeding, there were functioning monitoring wells on the premises for the purpose of detecting leaks in the underground storage system. At the formal hearing, Tomas Pequeno, Jr., testified that on September 21, 1987, an odor of petroleum in one of the monitoring wells on the subject site was detected during a routine inspection of the premises. Mr. Pequeno, Jr., was advised by the inspector that there might be a leak in the system. On November 17, 1987, Mr. Pequeno, Jr., caused the tanks on the premises to be relined. No leaks were detected by the tests that were conducted following the relining of the tanks. Paragraph 9 of the Pretrial Stipulation filed by the parties on July 24, 1991, is as follows: 9. That the date of discovery of petroleum contamination at this facility was September 21, 1987, as indicated by Tomas Pequeno. On December 9, 1988, Petitioner submitted to Respondent an "Early Detection Incentive Program Notification Application" which was signed by Tomas Pequeno, Sr., as president of X.O. #1 Corporation. This form had been completed by Tomas Pequeno, Jr., and given to his father for his execution. This form represented that contamination at the site was detected September 21, 1987, by a manual test of the monitoring wells, that the number of gallons lost was unknown, that the petroleum contamination was due to leaking storage tanks, and that the system had been repaired. The cause of the leak in the piping and the cause of the leak in the tanks were stated as being unknown. Mr. Pequeno, Jr., testified at the formal hearing that: "There was never a discharge from that site and there is not a discharge right now at this moment." Mr. Pequeno, Jr., also answered in the affirmative to the following question: "Mr. Pequeno, are you testifying there is no contamination at this facility?" 1/ Mr. Pequeno, Jr., testified further that he submitted the Early Detection Incentive Program Notification Application as a precaution in the event contamination was discovered. The testimony of Mr. Pequeno, Jr., at the formal hearing contradicted the representations made on the Early Detection Incentive Program Notification Application. At all times pertinent to this proceeding both Mr. Pequeno, Jr., and Mr. Rodriguez were aware that the primary purpose of a monitoring well is to detect leaks from a petroleum storage system. At all times pertinent to this proceeding both Mr. Pequeno, Jr., and Mr. Rodriguez were aware of the existence of the monitoring wells on the subject site. The Dade County Department of Environmental Management (DERM) had asked the operator of the facility to submit monitoring reports. 2/ Mr. Rodriguez was unable to recall when DERM first requested the monitoring reports, but it is clear from his testimony that the request was made several months before the hearing. The operator knew that monitoring system checks were required and had been requested by DERM to provide reports of those monitoring system checks. The failure to conduct regular, periodic monitoring system checks creates the risk that a leak in a petroleum storage system will continue undetected. Neither the operator nor the owner monitored the underground petroleum storage system on a regular basis until July of 1991, when the operator began to monitor the system on a regular basis and began to keep a log of the results. Since September 21, 1987, Petitioner was aware that a sample of water from one of the monitoring wells (monitoring well #9) at the subject facility consistently contained the odor of petroleum. At the time of the formal hearing, monitoring well #9 still contained the odor of petroleum. On January 26, 1989, Mr. Rodriguez, as the operator of the facility, received a copy of the Pollutant Storage Tank System Inspection Report form completed by a DERM inspector. This report placed the operator of the facility on notice that evidence of a discharge of pollutants had been discovered at the facility. On March 3, 1989, DERM sent to Petitioner by certified mail a letter which provided, in pertinent part, as follows: The Department of Environmental Resources Management acknowledges that you have applied for a state administered cleanup under the "Early Detection Incentive Program" ... . However, a review of the Department's records reveals that the source of contamination has not been determined. Therefore, the discharge of hazardous materials from the underground storage system to the adjacent soils or waters may be continuing. * * * ... [Y]ou are required to: Immediately upon receipt of this letter, CEASE and DESIST from any further unauthorized discharges to the ground and/or groundwater of Dade County. Immediately upon receipt of this letter, hydrostatically test, and repair any leaks to all underground tanks and transmission lines at the subject site. Within thirty (30) days of receipt of this letter, submit to this Department certifica- tion that all underground tanks and transmis- sion lines at the subject site are tight and are not discharging contaminants to the environment. ... The letter dated March 3, 1989, was received by Petitioner on March 7, 1989. By that letter, Petitioner was placed on notice that there was a risk that a discharge of hazardous materials from the underground storage system to the adjacent soils and waters was continuing. By that letter, Petitioner was also placed on notice that DERM required that it hydrostatically test all underground tanks and transmission lines at the subject site in order to determine if leaks existed in the tanks and lines. By that letter, Petitioner was also placed on notice that DERM required that Petitioner certify that all underground tanks and transmission lines at the subject site are tight and are not discharging contaminants to the environment. Mr. Pequeno, Jr., believed that by having the tanks relined and repaired in November 1987, Petitioner had complied with the requests made in DERM's letter of March 3, 1989. On March 13, 1989, Mr. Pequeno, Jr., called DERM to determine whether the tests that were conducted following the relining and the repair of the tanks in November 1987, satisfied the requirements contained in DERM's letter of March 3, 1989. When Mr. Pequeno, Jr., did not get a response to his inquiry, he assumed that Petitioner was in compliance. Petitioner took no steps until two years later to hydrostatically test its underground tanks and transmission lines. On March 21, 1991, Petitioner had a tank tightness test conducted at the facility. The tank system tightness test conducted on March 21, 1991, indicated that five tanks did not test tight. There was no evidence that Petitioner has filed a certification with DERM that all underground tanks and transmission lines at the subject site are tight and are not discharging contaminants to the environment. No fuel transmission line tightness test has been conducted pursuant to DERM's March 3, 1989, request. As of the date of the formal hearing, Petitioner had not performed a complete investigation to determine the source of contamination as DERM had requested. The underground storage system at the subject site were continuously used for the storage and dispensing of petroleum products from September 21, 1987, to the date of the formal hearing. At all times pertinent to this proceeding deliveries of petroleum products were made to the tanks which had been identified by Petitioner as leaking. Petitioner's failure to conduct a complete investigation to determine the source of contamination, its failure to repair the tanks which failed the tank tightness, and its continued use of these tanks, create the risk that a discharge of hazardous materials may be continuing at the present time. By letter dated February 13, 1991, Respondent denied Petitioner's eligibility to participate in the Early Detection Incentive Notification Program. This letter provided, in pertinent part, as follows: The Department of Environmental Regulation has completed its eligibility review of your Early Detection Incentive Notification Application. Based upon information given in this application and a compliance verification evaluation, the Department has determined that this site is not eligible for state-administered cleanup pursuant to Section 376.3071(9), Florida Statutes (1986) for the following reasons: Failure to have storage tanks tightness tested. Request was made by the Department of Environ- mental Resources Management (DERM) on March 3, 1989. This shall be construed to be gross negligence in the maintenance of a storage system. According to Section 376.3071(9)(b)3, Florida Statutes, sites shall not be eligible for state- administered cleanup where the owner or operator has been grossly negligent in the maintenance of a petroleum storage system. By Pre-Trial Stipulation filed July 24, 1991, the parties entered into certain factual stipulations and framed the following two issues of law to be resolved: Whether X.O. #1 Corporation was grossly negligent as defined under Section 376.3071(9)(b)3, Florida Statutes, for failing to immediately investigate and abate the source of a petroleum contamination by conducting a tank and line tightness test pursuant to a request by DERM (Dade County Department of Environmental Resources Management). Whether X.O. #1 Corporation was grossly negligent as defined under Section 376.3071(9)(b)3, Florida Statues, for failing to make monthly monitoring system checks where such systems are in place.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is recommended that a Final Order be entered by the Florida Department of Environmental Regulation which denies the application of Petitioner to participate in the Early Detection Incentive Program for its facilities located at 2188 N.W. 20th Street, Miami, Florida 33142. RECOMMENDED in Tallahassee, Leon County, Florida, this 25th day of September, 1991. CLAUDE B. ARRINGTON 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 25th day of September, 1991.
The Issue Whether the Petitioners are eligible for restoration coverage under the Abandoned Tank Restoration Program (ATRP) with regard to the remediation of petroleum contamination at DEP Facility No. 588631316, located in Venice, Florida.
Findings Of Fact Upon consideration of the oral and documentary evidence adduced at the hearing, the following relevant findings of fact are made: The Petitioners are the operators of Gulf Car Care (DEP Facility No. 588631316) located at 207 South Tamiami Trail, Venice, Florida. The Department is the agency charged with the responsibility of administering the Abandoned Tank Restoration Program. The Petitioners' ATRP Application was dated May 17, 1992 and received by the Department on June 17, 1992. The Petitioners' ATRP Application indicates that two 2,000-gallon underground storage tanks (UST's) were located at the facility and that one of those tanks was utilized for the storage of diesel fuel while the other tank was utilized for the storage of gasoline. Petitioners' ATRP Application indicates that two 4,000-gallon UST's and two 6,000-gallon UST's were also located at the facility and were utilized for the storage of gasoline. At least some, if not all, of the UST's identified in Petitioners' ATRP Application continued to store petroleum products for consumption, use or sale after March 1, 1990, and in fact, continued to store petroleum products for consumption, use or sale until some time in April, 1990. Petitioner Parr was operated on for colon cancer in late 1989 and Petitioner Homer suffered a heart attack on March 3, 1990. Petitioners contend that because of Petitioner Parr's illness the Petitioners were unable to make a decision to remove the petroleum storage system from service until after March 1, 1990. The petroleum storage system at the facility has been closed in accordance with Department's applicable rules.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is recommended that the Department enter a Final Order denying the Petitioners' application for eligibility or restoration coverage under the Abandoned Tank Restoration Program. RECOMMENDED this day 21st of April, 1994, at 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 21st day of April, 1994. APPENDIX TO RECOMMENDED ORDER, CASE NO. 93-6555 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. Petitioners, Harold R, Parr and George H, Homer, Sr. Petitioners did not submit any proposed findings of fact per se. However, based on the record, including the testimony of the Petitioners, it does not appear that the Petitioners would disagree with any of the Findings of Fact presented in this Recommended Order. Respondent, Department's Proposed Findings of Fact. 1. The following proposed findings of fact are adopted in substance as modified in the Recommended Order. The number in parenthesis is the Finding(s) of Fact which so adopts the proposed finding(s) of fact: 1(1); 2(3); 3-4(4); 5-6(5); 7- 9(6); 10-11(7) and 12(8). COPIES FURNISHED: Harold R. Parr 913 E. Shanon Court Venice, Florida 34293 George H. Homer, Sr. 3674 Roslyn Road Venice, Florida 34293 W. Douglas Beason, Esquire Department of Environmental Protection Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 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
Findings Of Fact Friends of Lloyd, Inc. is a Florida non-profit corporation formed for the purpose of protecting Jefferson County from harmful development. The Council of Neighborhood Associations of Tallahassee/Leon County (CONA) is a non- profit Florida corporation whose members are the neighborhood associations in Leon county; members of those associations reside in 42 Leon County neighborhoods dispersed throughout Leon County. CONA's purposes and goals include protection of the quality of life and environment in Leon County. The Thomasville Road Association's members are principally residents of Leon County. The Association was formed to promote responsible growth management in northern Leon County. None of the Petitioners are owners or "developers" of a Development of Regional Impact within the terms or scope of Chapter 380, Florida Statutes. Rather, Petitioners are members of non-profit organizations interested in the environment and growth management of Leon County. The Department of Community Affairs (the "Department") is the state land planning agency with the power and duty to administer and enforce Chapter 380, Florida Statutes, and the rules and regulations promulgated thereunder. Sections 380.031(18), and 380.032(1), Florida Statutes (1987). Texaco is a business entity that proposes to develop a "tank farm" near the community of Lloyd in Jefferson County, Florida. The Texaco tank farm is a "petroleum storage facility" as that term is used in Rule 28-24.021, F.A.C. Colonial is a business entity that proposes to develop a petroleum pipeline that will connect to the Texaco tank farm. The pipeline is designed to carry and contain petroleum products For purposes of standing, the parties have stipulated that certain environmental hazards can reasonably be expected to occur as a result of the existence of the pipeline/tank farm. No competent evidence was submitted regarding those hazards. As a result of the stipulation, Petitioners have each established injury-in-fact so that they are "adversely affected" by the challenged rule to an extent sufficient to confer upon them standing to maintain this action under Section 120.56, Florida Statutes. On September 7, 1989, one of the Petitioners sent Respondent a letter suggesting that the proposed tank farm development to be built in Jefferson County should be required to undergo review as a DRI. Enclosed with the letter was a proposed circuit court complaint pursuant to Section 403.412(2)(c), Florida Statutes. Petitioner expressed its intention of filing this circuit court action, but first provided Respondent a copy of the proposed complaint in accordance with the provisions of Section 403.412, Florida Statutes. In two letters dated September 8 and 25, 1989, Petitioner supplied additional information to Respondent concerning the tank farm project and contended that in making its determination as to whether the development must undergo DRI review, Respondent should consider the storage capacity of both the tank farm and the pipeline. On October 9, 1989, Respondent answered Petitioner's first letter, and stated that the proposed project was not required to undergo DRI review because the total storage capacity of the tanks was only seventy-eight percent (78%) of the threshold set out in Chapter 28-24, F.A.C. On October 13, 1989, Respondent answered Petitioner's second and third letters, stating that with respect to the pipeline, it has been long standing departmental policy to interpret "storage facilities" as meaning only the tanks, not the pipeline, when determining whether petroleum storage facilities meet the DRI thresholds set out in Chapter 28-24. The proposed tank farm would have nine tanks with a total capacity of 155,964 barrels, which is, as Respondent determined in its letters, approximately seventy-eight percent (78%) of the applicable DRI threshold for "petroleum storage facilities" set forth in Chapter 28-24, F.A.C. The proposed pipeline's capacity over its approximate forty-five mile length from Bainbridge, Georgia to the tank farm is approximately 34,000 barrels. The proposed pipeline's volume flow capacity from the Florida/Georgia state line to the site of the prosed tank farm is approximately 13,500 barrels over approximately 18 miles. If the pipeline's volume capacity from Bainbridge, Georgia is added to the tank farm's volume capacity, the resulting project would be approximately ninety-five percent (95%) of the applicable DRI threshold in Chapter 28-24. If the pipeline's volume capacity from the state line is added to the tank farm's volume capacity, the resulting project would be approximately eighty-five percent (85%) of the threshold. In either instance, the project would exceed the eighty percent (80%) threshold that may require it to undergo DRI review although the project would be Presumed not to be a DRI under the Statute. The Department does not require developments outside Chapter 28-24's enumeration to undergo DRI review. The Department has never treated petroleum Pipelines as "petroleum storage facilities," or as otherwise subject to DRI review. On Several occasions, the Department has applied the petroleum storage facility guideline and standard to petroleum tank farms without determining whether a pipeline was attached to the tank farm. On one prior occasion, the Department has explicitly stated that Petroleum Pipelines are not subject to DRI review. The Petitioners contend that Department's Position that pipelines are not "petroleum storage facilities" is an invalid policy because it has not been adopted as a rule. There is no dispute the Department's Position on this issue has not been promulgated as a rule. If a facility were represented to be a Petroleum pipeline, but was actually designed as and operating as a petroleum storage facility, the Department would apply the Petroleum storage facility DRI guideline and standard to that facility.
The Issue Whether Petitioner's application for a septic tank permit application should be granted?
Findings Of Fact On July 29, 1987, Petitioner applied for a septic tank permit for a proposed individual sewage disposal system to serve a single family residence on Lot 40, Block P, Killearn Lakes Unit I (Unit 1), in Leon County, Florida. A septic tank system consists of a tank and a drainfield which is wholly or partly underground. The decision of whether to grant a septic tank system permit is greatly influenced by the elevation of the wet season water table in the area where the septic tank system will be located. Under normal circumstances, the elevation of the wet season water table can be determined by taking a boring of the ground in question using an auger. If water is found at the time the boring is conducted, that is an indication of where the water table is located. If no water is found, the elevation of the wet season water table can be determined by examining the soil removed from the ground for signs of mottling. Mottling is the discoloration of the soil caused by the interaction of water with the minerals in the soil. The process of mottling takes place over hundreds of years. Therefore, a rapid change in conditions may cause the elevation of the wet season water table to be different than what would be indicated by mottling. Because of the development of Unit I and the drainage method used in Unit I (sheetflow), the elevation of the wet season water table in Unit I is estimated to be between 12 and 20 inches higher than what is indicated by mottling. On July 7, 1987, a boring was taken on an indeterminate area on Lot 40, by Certified Testing, Inc., a private engineering firm. The evaluation of the boring resulted in mottling being present at a depth of 60 inches. On August 3, 1987, Ms. Teresa A. Hegg, an Environmental Health Specialist with HRS, took two borings on Lot 40. The first boring was taken in an area other than where the septic tank system's drainfield would be located. This boring resulted in mottling being present at a depth of 45 inches. The second boring was taken in the area where the septic tank system's drainfield would be located. This boring resulted in mottling being present at a depth of 22 inches. Based on the boring taken at the proposed site for the septic tank system, showing mottling at 22 inches, and the estimate that the wet season water table in Unit I is from 12 to 20 inches higher than mottling would indicate, the estimated wet season water table for Lot 40 is between 2 to 10 inches below the ground surface. Unit I has a history of septic tank system failures. Unit I was platted prior to January 1, 1972. There exists a very high probability that any septic tank system, even a mound system, installed in Lot P-40 will fail.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that Respondent issue a final order denying Petitioner's application for a septic tank permit. DONE and ENTERED this 28th day of July, 1988, in Tallahassee, Florida. JOSE A. DIEZ-ARGUELLES Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 28th day of July, 1988. APPENDIX TO RECOMMENDED ORDER, CASE NO. 87-4085 The Respondent has submitted proposed findings of fact which are addressed below. Paragraph numbers in the Recommended Order are referred to as "RO ." The Respondent's Proposed Findings of Fact Proposed Finding Paragraph Number in Recommended Order of Fact Number of Acceptance or Reason for Rejection First phrase accepted. Remainder of paragraph supported by competent evidence but unnecessary to the decision reached. First two sentences accepted. Third sentence supported by competent evidence but unnecessary to the decision reached. Accepted. Accepted. 5,6,7,8,9,10 Supported by competent evidence but unnecessary to the decision reached. Accepted. Accepted. 13,14 Supported by competent evidence but unnecessary to the decision reached. 15. First sentence accepted. Second sentence rejected; the wet season water table on Lot P-40 is from 2-10 inches below grade. Third sentence accepted. COPIES FURNISHED: Salvatore A. Carpino, Jr., Esquire One Urban Centre, Suite 750 4830 West Kennedy Boulevard Tampa, Florida 33609 John R. Perry, Esquire Assistant District II Legal Counsel Department of Health and Rehabilitative Services 2639 North Monore Street Suite 200-A Tallahassee, Florida 32303 Sam Power, Clerk Department of Health and Rehabilitative Services 1323 Winewood Boulevard Tallahassee, Florida 32399-0700 Gregory L. Coler, Secretary Department of Health and Rehabilitative Services 1323 Winewood Boulevard Tallahassee, Florida 32399-0700 John Miller, Acting General Counsel Department of Health and Rehabilitative Services 1323 Winewood Boulevard Tallahassee, Florida 32399-0700
The Issue Whether Petitioner is entitled to participate in the Reimbursement Program established under the State Underground Petroleum Environmental Response (SUPER) Act of 1986 for the petroleum terminal owned by Gulf Products Division of BP Oil Company at Port Everglades, Florida.
Findings Of Fact The State Underground Petroleum Environmental Response (SUPER) Act of 1986 provides for the expeditious cleanup of sites contaminated as the result of storage of petroleum or petroleum products. The Reimbursement Program, found in Section 376.3071(12), Florida Statutes, provides for reimbursement of the allowable costs of site rehabilitation contaminated as a result of a discharge related to the storage of petroleum or petroleum products from a storage tank, or its integral piping or dispensing system. The Reimbursement Program does not provide for reimbursement of cleanup costs for discharges related to the transportation or disposal of petroleum or petroleum products. The site at issue in this proceeding is a terminal facility used for the storage of petroleum and petroleum product located at 1500 Southeast 26th Street, Port Everglades, Florida. This facility is referred to as Gulf Facility No. 46888 and DER Facility No. 068732278 (Gulf Terminal). The subject terminal facility is one of fourteen petroleum storage terminals located at Port Everglades, Florida. Petroleum and petroleum products come to the terminal by ship and are pumped from the ship through permanent pipelines to the large aboveground storage tanks located at the facility. The petroleum and petroleum products are stored in these large tanks until it is time for the product to be distributed to the end user. The Gulf Terminal contains eighteen storage tanks whose total capacity is 650,000 barrels of petroleum or petroleum products. These tanks vary in size, with the smallest having a capacity of 10,000 barrels and the largest having a capacity of 80,000 barrels. One barrel equals 42 gallons. The primary activity of the terminals at Port Everglades is to store petroleum or petroleum products. None of the terminals at Port Everglades, including the Gulf Terminal, refines or produces petroleum or petroleum products. Operation of this facility began in 1946. Petitioner, as the successor to the Gulf Oil Corporation, owned and operated the facility until February 1, 1985, when it sold the facility to BP Oil, Inc. As the previous owner of the facility, Petitioner performed an environmental audit which revealed petroleum hydrocarbon contamination at the site. Petitioner is responsible for the cleanup and is entitled to reimbursement of the allowable costs of the cleanup if the site is eligible to participate in the reimbursement program. Any contamination of the soil and groundwater at the site was caused by discharges of petroleum or petroleum products, water contaminated with petroleum or petroleum product or sludges which consist predominately of petroleum or petroleum product constituents. Based on hydrogeological assessment information, Petitioner determined that response action, including ground water cleanup activities, was required at the site. Petitioner hired independent contractors to conduct the response action. In 1986, Petitioner designed a recovery system for petroleum and petroleum product and a ground water treatment system at the site. Through February, 1989, the recovery system had recovered over 12,000 gallons of petroleum or petroleum products, which constitutes the recovery of between 60%- 70% of the total amount in the ground. Through November 1989, Petitioner had expended in excess of $560,000 on its response action at the Gulf Terminal. Petitioner advised Respondent of its response action at the site by letter dated January 6, 1988. Petitioner submitted documentation to Respondent concerning hydrogeological assessment at the site which included field and laboratory work and investigation performed for the site from 1984 to the present. Pursuant to the requirements of SUPER Act, Petitioner notified Respondent of its intention to seek reimbursement for money spent conducting response action in accordance with Chapter 17-70, Florida Administrative Code, with regard to petroleum and petroleum product contamination at the site. Petitioner's notice to Respondent was timely and was procedurally correct. On July 13, 1989, Respondent issued its Order of Determination of Ineligibility concerning Petitioner's request for reimbursement. As stated in this order the initial basis for Respondent's denial of eligibility was: The determination is based on the fact that the contamination was not related to the storage of petroleum or petroleum products. Sources of contamination at this site include tanker trucks, an oil/water separator, a holding pond, and crude oil and tank-bottom sludge disposal pit. These items are not petroleum storage systems as defined in Section 376.301 F.S. therefore (sic), this site is not eligible for reimbursement under the SUPER Act. ... Respondent clarified its Order of Ineligibility by a Notice to Amend and Clarify dated November 14, 1989, which provides, in pertinent part, as follows: The notice of denial provides that the site is being denied due to the fact that the disclosed sources of contamination are not petroleum storage systems. One of the criteria for being a petroleum storage system is that it be used or intended to be used for storage of petroleum or petroleum product. It is the criteria that the Department contends is not met in this case; i.e., that the discharges were not intended for storage. Section 376.3071(4), Florida Statutes, specifically limits the use of the Environmental Protection Trust Fund to incidents of inland contamination related to storage of petroleum or petroleum product. * * * The Department recently became aware that prior to 1983, contaminated water was disposed of directly from tanks at the site with no pretreatment by an oil/water separator. As with the disposal of oil and sludge to a pit, the act of intentionally disposing of contaminants to the ground is not "related to storage" as required by Chapter 376, Florida Statutes. * * * Wherefore, The State of Florida Department of Environmental Regulation hereby requests that the Hearing Officer allow for the amendment of the notice of denial of eligibility to include the following basis for denial: Contamination at the site is related to the disposal of petroleum or petroleum product, or water contaminated with petroleum or petroleum products. Disposal activities including the intentional discharge and disposal of contaminated water and/or fuel from tanks, oil water separators and sump areas, the intentional discharge and disposal of contaminated water to a percolation pond, the intentional discharge and disposal of oil and sludge to a disposal pit, and the intentional discharge and disposal of fuel to the ground at the loading rack. Among the causes of contamination of the Gulf Terminal are accidental overfills of tanks and leaks from an integral pipeline. Absent any other source of contamination, the discharges that occurred at the Gulf Terminal due to these causes would be eligible for the reimbursement. Respondent has determined, however, that the following additional sources of contamination render the entire response action ineligible for reimbursement: Discharges of dissolved hydrocarbon molecules contained in water which accumulated in storage tanks; Discharges of petroleum or petroleum products at the loading rack at the terminal; and The discharge of crude oil and of crude oil tank bottoms. TANK OVERFILL During the operation of the Gulf Terminal, petroleum and petroleum products have been accidentally discharged onto the ground. In 1955, an unknown quantity of petroleum or petroleum products was accidentally discharged onto the ground in the areas of tanks 104 and 105 as a result of these tanks being over- filled. Following this massive spill, between 5,000 - 10,000 barrels of product was recovered, while an unknown quantity could not be recovered. PIPELINE LEAK Since 1955, approximately 15,000 additional barrels of petroleum or petroleum products were leaked from an underground pipeline that is integral to the storage system in an area between the loading rack and tank 101, extending toward the west to between tanks 110 and 102. This is the vicinity where the heaviest free floating petroleum contamination exists. DISCHARGE OF CONTAMINATED WATER Florida has adopted the standard code for the design of aboveground storage tanks prepared by the American Petroleum Institute (API-650). The tanks at the Gulf Terminal are in compliance with API-650. The accumulation of water in storage tanks is a problem associated with the storage of petroleum or petroleum products in the storage tanks at the Gulf Terminal and at the other terminals at Port Everglades. Water accumulates in the storage tanks from rainfall and from condensation. The records of the US Department of Commerce, National Oceanic and Atmospheric Administration for Station 08063163 (Fort Lauderdale, Florida) accurately depict the rainfall levels at the terminal facility. The total annual rainfall levels are as follows: 1980, 69.67 inches; 1981, 57.9 inches; 1982, 82.92 inches; 1983 75.16 inches; 1984, 59.4 inches; 1985, 63.74 inches; 1986, 64.14 inches, 1987, 58.50 inches; 1988 40.66 inches. Because water is heavier than petroleum and petroleum products, the water accumulates at the bottom of the tanks. It is essential to the proper storage of the petroleum or petroleum products that the water be removed for at least three reasons. First, if the water is not removed, the tanks would eventually become filled with water instead of product. Second, the product contaminated by water, particularly fuel for motor vehicles and aircraft, would not meet specifications. Third, water in the tanks speeds the corrosion of the tank. In order to remove this water that accumulates at the bottom of the storage tanks, a water draw-off mechanism located at the bottom of the tank is a design feature of API-650. When water accumulates in the bottom of the tank, the water is drained out through the water draw-off mechanism. The storage tanks located at the Gulf Terminal are equipped with such a water draw-off mechanism. Throughout the existence of the facility, accumulated water in the tanks has been controlled by discharging the water through the water draw-off mechanism. From 1948 to 1980, water was drained out of the tanks through the water draw-off mechanism and on to the ground. Beginning in 1980, the water was taken from the tanks through the water draw-off mechanism and piped to a catch basin where an effort was made to recover petroleum product by skimming the water before the water was discharged into the ground. Since 1985, the water taken from the tanks through the water draw-off mechanism has been treated by an oil/water separator which effectively removes all petroleum product before the water is discharged. The purpose of the oil/water separator is to separate petroleum product from water so that the petroleum product can be returned to the storage tank and the water can be discharged. This process serves to prevent the discharge of petroleum product. Up to 1988, the discharges to the ground from the oil/water separator at the Gulf Terminal accumulated in a holding pond. In 1988, the holding pond was eliminated and the water discharges from the oil/water separator were routed to a holding tank prior to treatment by an air stripper and subsequent discharge into the canal adjacent to the property. At all times since 1983, the water drawn out of the tanks has been the subject of permits issued by Respondent which approve the use of the oil/water separator. While it is necessary for the operation of the storage tanks that water be drawn from the tanks, it is not necessary for the operation of the storage tanks for the contaminated water to be discharged onto the ground. The purpose of discharging the water was to dispose of it. There was no intent to recover the contaminated water after it was discharged. Any water coming out of a storage tank is contaminated with dissolved petroleum. It may have solids in it and floating residue or product on it. Between 1946 and 1980, when this water from the storage tanks was discharged to the ground, any contaminates in the water would be discharged along with it. Water has been drained from tanks numbered 101, 106, 109, 110, 111, 112 113, and 114 on a daily basis. The other tanks are drained after a rainfall. An average of one or two inches of water was drained off each time it rained. Following a rainfall, in excess of 30 barrels of water would be drained from the smaller tanks, while approximately 300 barrels of water would be drained from the larger tanks. The discharge of the water drawn from the storage tanks contributed to the contamination of the groundwater at the Gulf Terminal. This type contamination exists in almost all areas of the site. Petitioner was unable to distinguish the contamination to the groundwater caused by the discharge of contaminated water drawn from the storage tanks from contamination to the groundwater which resulted from other causes. Petitioner failed to establish that the contribution to this contamination to the groundwater by the discharge of the contaminated water drawn from the storage tanks was insignificant. THE LOADING RACK The loading rack at the Gulf Terminal is the apparatus by which the petroleum in the storage tanks is dispensed to tanker truck for distribution to consumers. The loading rack is a series of dispensers which operate much like at a service station except that it fuels tanker trucks rather than automobiles. The loading rack is connected by permanent integral piping to the storage tanks. The purpose of the loading rack is to load the transport trucks. Without the storage tanks at the terminal, there would be no need for a loading rack. Over the years, discharges have occurred in the loading rack, usually as the result of human error. Occasional overfills in the 10-15 gallon range have occurred while a truck was being filled. This type discharge is analogous to a spill which occurs at a service station when an automobile is being fueled and the fuel splashes back or overfills the automobile's fuel tank. The supervisor of Respondent's Reimbursement Section testified that this type discharge, absent other causes, would probably be eligible for reimbursement. This testimony conflicts with the official position taken by Respondent in this proceeding that the cleanup caused by the operation of the loading rack is ineligible for reimbursement. In other incidents, small amounts of product ranging from a teacup to less than a gallon, were occasionally discharged while a truck was being drained of one type of product so that the truck could transport another type of product. The loading rack is an integral part of the storage system because without a means of moving the product out of storage and into the distribution system, the storage tanks could not provide a meaningful function. The discharges which occurred at the loading rack during the course of both loading and unloading trucks are insignificant when compared with the other sources of contamination at the site. TANK BOTTOMS In 1956, a storage tank was emptied for the purpose of switching product from crude oil to diesel fuel. At the time the change in product was made, approximately 1000 barrels of sludge and crude oil were disposed of in a pit adjacent to tank 101. Also disposed of was the tank bottom, a hard tar residue which formed at the bottom of the tank. Oil occasionally oozes to the surface in the vicinity of the pit adjacent to tank 101, but the area around the sludge pit has not been found to be contaminated, and the tank bottom has remained a hardened mass. Each tank on the site also had a pit alongside the tank where a tank bottom was disposed. Although it was necessary to remove the sludge and the tank bottoms to be able to properly operate the storage tanks, it was not necessary for the operation of the storage tanks to dump the sludge and the tank bottoms onto the ground or into the pits. The purpose of discharging the crude oil sludge and the tank bottoms was to dispose of them. There was no intent to recover the crude oil sludge or the tank bottoms water after they were discharged. CONTAMINATION PHASES The contamination at the site exists in three phases, floating petroleum product contamination, dissolved petroleum groundwater contamination, and sludge contamination. The contamination in the form of floating petroleum was caused by discharges of petroleum or petroleum products following the tank overfills, the pipeline leaks, and spills at the loading rack. The dissolved groundwater contamination was caused by two primary sources. First, the dissolved groundwater contamination was caused by floating petroleum product coming into contact with groundwater. Upon such contact, molecules from the floating petroleum would dissolve into the water, causing contamination. Second, the dissolved groundwater contamination was caused by the discharge of the contaminated water that had been drawn off from the storage tanks. Petitioner was unable to distinguish the dissolved groundwater contamination that was caused by accidental discharges of product from the contamination caused by the discharge of the contaminated water. Petitioner was also unable to establish that the dissolved groundwater contamination caused by the contaminated water was insignificant. The sludge contamination was caused by the discharge of crude oil and crude oil tank bottoms. CLEANUP The sludge contamination is capable of being cleaned up separately from the free floating petroleum contamination and the groundwater contamination at the site. The sludge contamination is separate and distinct from the other contamination at the site both as to the location of the contamination and as to the methods that would be employed to clean up that type of contamination. Free floating petroleum contamination is recovered by drawing down the water level in a well by use of a pump so that a cone of depression is created. The cone of depression is a funnel shaped depression that causes the surface of the underground water table to bend down towards the well in all directions. The free floating petroleum which flows on top of the underground water surface is then recovered by use of a second pump. The free floating petroleum is then pumped into a holding tank where the recovery of free floating petroleum is completed. The recovery of free floating petroleum contamination is usually more expensive to accomplish than groundwater cleanup because more equipment is required. Groundwater cleanup usually takes a longer period of time to accomplish than does free floating product cleanup. The same or a similar well used to recover the free floating petroleum can also be used for the cleanup of contaminated groundwater. The contaminated groundwater is pumped from the well into an oil/water separator where the water and dissolved petroleum is separated, water is taken off the bottom, put through an air stripper, and is returned to the ground through an infiltration unit. Respondent has previously found sites eligible for the reimbursement program even though those sites experienced discharges which alone would render a site ineligible for the reimbursement program. The basis for finding these sites eligible was that the ineligible discharges had become indistinguishable from the eligible discharges and were insignificant by comparison. Petitioner has complied with all procedural requirements for seeking eligibility contained in Section 376.3701, Florida Statutes. Respondent has not been denied access to the Gulf Terminal. Respondent has made no determination that there has been gross negligence in the maintenance of the petroleum storage system locate at the Gulf Terminal. Petitioner has not willfully concealed the existence of a serious discharge at the Gulf Terminal. Petitioner has not falsified any inventory records maintained with respect to the Gulf Terminal. Petitioner has not caused any intentional damage to the Gulf Terminal. The Gulf Terminal is not owned by the federal government. Petitioner's challenge to Respondent's order of ineligibility was filed in a timely manner.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is Recommended that Respondent enter a final order which determines that the subject site is eligible to participate in the reimbursement program for the cleanup of the free floating petroleum contamination, but that the subject site is ineligible to participate in the reimbursement program for the cleanup of the sludge contamination and for the cleanup of the groundwater contamination. RECOMMENDED this 20th day of July, 1990, in Tallahassee, Leon County, Florida. CLAUDE B. ARRINGTON Hearing Officer The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 904/488-9675 Filed with the Clerk of the Division of Administrative Hearings this 20th day of July, 1990. APPENDIX TO RECOMMENDED ORDER, CASE 89-4521 The following rulings are made on the proposed findings of fact submitted by Petitioner in its Supplemental Proposed Recommended Order. The proposed findings contained in paragraphs 1-16, 18-25, 27-30, 33, 36-42, 44, 47-50, and 53-54 of the Supplemental Proposed Recommended Order are adopted in material part by the Recommended Order. The proposed findings contained in paragraphs 17, 31-32, 46, and 51-52 of the Supplemental Proposed Recommended Order are rejected as being contrary to the findings made and to the conclusions reached. The proposed findings contained in paragraph 26 of the Supplemental Proposed Recommended Order are adopted in part and are rejected in part as being unnecessary to the conclusions reached. The proposed findings contained in paragraph 34 of the Supplemental Proposed Recommended Order are rejected as not being established by the greater weight of the evidence. The testimony cited by Petitioner in support of these proposed findings do not establish the proposed findings. The proposed findings conflict with the contents of the Report of Ground-Water Quality Assessment accepted into evidence as Respondent's Exhibit 1. The proposed findings contained in paragraphs 35 , 43, and 45 of the Supplemental Proposed Recommended Order are rejected to the extent the proposed findings conflict with the findings made and the conclusions reached. The following rulings are made on the proposed findings of fact contained in Respondent's Proposed Recommended Order and in Respondent's Supplemental Proposed Recommended Order. The proposed findings of fact in paragraphs 1-5, 7-19, 23, 25-31, 33-34, 39- 52, 55-68, and 70-72 of Respondent's Proposed Recommended Order are adopted in material part. The proposed findings of fact in paragraphs 6, 20-22, 24, 32, 35-38, and 69 of Respondent's Proposed Recommended Order are rejected as being subordinate to the findings made or to the conclusions reached. The proposed findings of fact in paragraphs 53 and 54 of Respondent's Proposed Recommended Order are rejected because the testimony referred to by Respondent in support of the proposed findings relates to amounts discharged following rainfalls, not amounts discharged daily. The proposed findings of fact in paragraphs 1-14 of Respondent's Supplemental Proposed Recommended Order are rejected as being subordinate to the findings made or to the conclusions reached. COPIES FURNISHED: E. Gray Early, Esquire Assistant General Counsel Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Robert W. Wells, Esquire Ignacio E. Sanchez, Esquire KELLEY, DRYE & WARREN 2400 Miami Center 201 South Biscayne Boulevard Miami, Florida 33131 Dale H. Twachtmann, Secretary Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Daniel H. Thompson, General Counsel Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400
The Issue Whether Respondent committed the violations as set forth in the Citation for Violation, Onsite Sewage Program/Sanitary Nuisance dated April 28, 2000.
Findings Of Fact Petitioner is authorized and given the jurisdiction to regulate the construction, installation, modification, abandonment, or repair of onsite sewage treatment and disposal systems, including drainfields, by septic tank contractors. At all times material hereto, Respondent was a registered septic tank contractor and, as such, he was authorized to provide septic tank contracting services, including the installation and repair of drainfields. On or about November 2, 1995, Petitioner issued a permit (Permit No. RP648-95) to Wilmar Rodriguez for the repair of a septic tank system at 417-421 Perry Avenue, Greenacres, Florida. The property was a triplex, which was purchased by Mr. Rodriquez in 1981. Mr. Rodriguez has no knowledge as to whether any drainfields were installed or replaced on the property, prior to 1981. The Permit included the installation of a new multi- chambered septic tank, a dosing tank, a lift station, and a new drainfield. The Permit was also for a filled system and called for the drainfield to be 700 square feet. Respondent was indicated as the "agent" on the Permit. Respondent and/or his employees performed the work under the Permit. Respondent was the septic tank contractor for the repair of the septic tank system under the Permit. On November 9, 1995, the construction of the septic tank system was approved by one of Petitioner's inspectors, who was an Environmental Specialist I. Petitioner's inspectors are not present during the entire construction or repair of a septic tank system or drainfield. Usually, inspections are made after the completion of the construction or repair of the septic tank system. Additionally, the inspection of a drainfield is usually performed after the rock has been placed on top of the drainfield. On February 2, 1996, the same inspector performed the inspection after the completion of the construction of the septic tank system, including after the placing of the rock on top of the drainfield. Even though the Permit reflects a filled system, the filled/mound system section on the inspection sheet was crossed out. The inspector considered the system to be a standard system, not a filled or mound system, and, therefore, inspected it as a standard system. In inspecting a drainfield, the inspection by an inspector includes checking to ensure that a drainfield has 42 inches of clean soil below the drainfield. An inspector uses an instrument that bores down through the rock and brings up a sample of the soil, which is referred to as augering. Augering is randomly performed at two locations. For the instant case, the inspector performed the augering in two random locations of the drainfield, which were in the area of the middle top and the middle bottom. The samples failed to reveal anything suspect; they were clean. On February 2, 1996, the inspector issued a final approval for the septic tank system. Final approval included the disposal of "spoil" and the covering of the septic tank system with "acceptable soil". The inspector mistakenly inspected the system as a standard system. He should have inspected the system as a filled system.1 After the repair and installation of the septic tank system by Respondent, Mr. Rodriguez continued to have problems with the septic tank system. He contacted Respondent three or four times regarding problems with the system, but the problems persisted. Each time, Respondent was paid by Mr. Rodriguez. Sewage water was flowing into the street where the property was located and backing-up into the inside of the triplex. Having gotten no relief from Respondent, Mr. Rodriguez decided to contact someone else to correct the problem. Mr. Rodriguez contacted Richard Gillikin, who was a registered septic tank contractor. On October 14, 1999, a construction permit was issued to Mr. Rodriguez for the repair of the septic tank system. Mr. Gillikin was indicated as the agent. Mr. Gillikin visited the property site of the triplex and reviewed the problem. He determined that the drainfield was not properly functioning, but he did not know the cause of the malfunctioning. With the assistance of Petitioner's inspectors, Mr. Gillikin and Mr. Rodriguez attempted to determine the best method to deal with the problem. After eliminating options, Mr. Rodriguez decided to replace the drainfield. To replace the drainfield, Mr. Gillikin began excavating. He began removing the soil cover and the rock layer of the drainfield. Mr. Gillikin also wanted to know how deep he had to dig to find good soil. After digging for that purpose and for 10 to 12 inches, he discovered a drainfield below Respondent's drainfield. The drainfield that Mr. Gillikin discovered was a rock bed 12 inches thick in which pipes were located and, as indicated, 10 to 12 inches below Respondent's drainfield. Mr. Gillikin also dug a hole two to three feet deep, pumped the water out of the hole, and saw the old drainfield. Mr. Gillikin determined that the old drainfield extended the full length of Respondent's drainfield. As a result of Mr. Gillikin's determining that the old drainfield was below Respondent's drainfield, both drainfields had to be removed and the expense of a new drainfield increased. Leon Barnes, an Environmental Specialist II for Petitioner, who was also certified in the septic tank program, viewed the drainfield site. He determined that the old drainfield was below Respondent's drainfield and that, therefore, Respondent had not removed the old drainfield. On or about November 6, 1999, Mr. Barnes' supervisor, Jim Carter, and co-worker, Russell Weaver, who is an Engineer, also visited the drainfield site. Mr. Weaver determined that the old drainfield covered a little more than 50 percent of the area under Respondent's drainfield. On November 8, 1999, a construction inspection and a final inspection of the system installed by Mr. Gillikin were performed. The system was approved. Respondent admits that a new drainfield is prohibited from being installed over an old drainfield. However, Respondent denies that he installed a new drainfield over the old drainfield on Mr. Rodriguez's property. In 1995, Respondent failed to completely remove the old drainfield before he installed the new drainfield. The soil and rocks from the old drainfield, which was not functioning, were contaminated spoil material. Because the old drainfield was not completely removed, the contaminated spoil material remained in the drainfield and was used as part of the material in the installation of the new drainfield. Leaving the contaminated spoil material in the new drainfield, prevented the sewage water from being able to percolate through the ground, which is a method of cleansing the sewage water. Without being able to percolate through the ground, the sewage water remained on the surface of the drainfield, creating a serious sanitary nuisance and health hazard. The sewage water spilled onto the street and backed-up into the triplex. Respondent was issued a Citation for Violation, Onsite Sewage Program/Sanitary Nuisance by Petitioner.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Health, Palm Beach County Health Department, enter a final order: Affirming the Citation for Violation, Onsite Sewage Program/Sanitary Nuisance and finding that Noel Sanfiel violated Section 381.0065, Florida Statutes (1995), and Rule 10D- 6.0571(4), now Rule 64E-6.015(6), and Rule 10D-6.0751(1)(l)1, now 64E-6.022(1)(l)1, Florida Administrative Code. Imposing a fine of $500. DONE AND ENTERED this 13th day of February, 2001, in Tallahassee, Leon County, Florida. ERROL H. POWELL 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 13th day of February, 2001.
