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
The Issue There are three legal issues which remain for determination: (1) Whether Florida Petroleum has standing in this case; (2) Whether proposed rule 62-770.220(3)(b), requiring constructive notice to residents or business tenants of real property into which the temporary point of compliance is allowed to extend is an invalid exercise of delegated legislative authority within the meaning of Section 120.52(8)(c), Florida Statutes; and (3) Whether proposed rule 62-770.220(4), requiring additional constructive notice of the status of site rehabilitation is an invalid exercise of delegated legislative authority within the meaning of Section 120.52(8)(c), Florida Statutes.i
Findings Of Fact On December 23, 2004, the Department published a Notice of Proposed Rulemaking regarding amendments to Florida Administrative Code Chapter 62-770. In particular, proposed rule 62-770.220(3)(b) and (4), provides: Subsequent Notice of Contamination Beyond Source Property Boundaries for Establishment of a Temporary Point of Compliance (TPOC) - Prior to the Department authorizing a temporary extension of the point of compliance beyond the boundary of the source property (i.e., the location from which the contamination originates) in conjunction with Natural Attenuation Monitoring pursuant to Rule 62-770.690, F.A.C., or Active Remediation pursuant to Rule 62-770.700, F.A.C., the PRSP shall provide the following notices: * * * (b) Constructive notice to residents [if different from the real property owner(s) notified pursuant to paragraph 62- 770.220(3)(a), F.A.C.] and business tenants of any real property into which the point of compliance is allowed to extend. Such constructive notice, which shall include the same information as required in the actual notice, shall be provided by complying with the following: * * * Status Update 5-Year Notice - When utilizing a TPOC beyond the boundary of the source property to facilitate natural attenuation monitoring or active remediation, an additional notice concerning the status of the site rehabilitation shall be similarly provided every five years to [the classes of] those persons who received notice pursuant to subsection 62-770.220(3), F.A.C., unless in the intervening time, such persons have been informed that the contamination no longer affects the property into which the point of compliance was allowed to extend. * * * (The language in brackets was added pursuant to the Department's Notice of Change and "those" was deleted.) The proposed rule implements Section 376.3071, Florida Statutes. The specific authority for the proposed rule is Sections 376.303 and 376.3071, Florida Statutes. On February 2, 2005, the Environmental Regulation Commission held a public hearing on the proposed rules and approved the proposed rules with certain amendments. On February 14, 2005, Florida Petroleum filed a Petition for Determination of Invalidity of Proposed Rule (Petition) challenging the validity of proposed amendments to proposed rule 62-770.220(3)(b) and (4). The Petition was filed pursuant to Section 120.56(1) and (2), Florida Statutes, and in each instance, Florida Petroleum alleges that the proposed rule violates Section 120.52(8)(c), Florida Statutes. On March 4, 2005, the Department published a Notice of Change regarding the above-referenced Notice of Proposed Rulemaking. With respect to the pending proceeding, the Notice of Change reflects revisions to language of proposed rule 62- 770.220(4), which are not subject to challenge. See Finding of Fact 1. On May 16, 2005, without objection, official recognition was taken of the Department's Notice of Proposed Rulemaking and Notice of Change. Florida Petroleum is a Florida voluntary, non-profit trade association, which comprise, in part, approximately 194 Marketer Members who own and/or operate petroleum storage system facilities in Florida. Florida Petroleum’s purposes include providing representation on behalf of its members in legislative and regulatory matters before the Florida legislature and agencies. Florida Petroleum routinely represents its members in rule development proceeding and other regulatory matters before the Department of Environmental Protection, Department of Revenue, and Department of Agriculture and Consumer Services. Florida Petroleum’s By-Laws state that its purposes include advancing the business concerns of its members, pooling the energy and resources of its members, and communicating with elected officials at the national, state, and local levels of government. Towards those ends, Florida Petroleum has represented it members before the Florida Legislature in matters relating to the regulation of petroleum facilities under Chapter 376, Florida Statutes, and has appeared before the Department in rulemaking proceedings involving the regulation of petroleum cleanups, and the various state restoration funding assistance programs. The subject matter of the rule at issue is within the general scope of interest and activity of Florida Petroleum, in particular, its marketer members, who own or operate facilities that store petroleum products for consumption, use, or sale. Florida Petroleum submitted oral and written comments, recommendations, objections, and proposed amendments to the Department and the Environmental Regulation Commission in connection with the rules at issue in this case. A substantial number of Florida Petroleum marketer members are "persons responsible" for assessment and remediation of one or more petroleum-contaminated sites. Florida Administrative Code Chapter 62-770, governs the remediation of petroleum-contaminated sites. A substantial number of Florida Petroleum’s marketer members are "persons responsible" for assessment and remediation of sites identified by the Department as "confirmed" or "suspected" sources of contamination beyond the boundary of the facility (i.e., "off-site contamination"). In certain instances, the Department's rules allow for the use of No Further Action with Conditions procedures in cases of petroleum contamination where applicable regulatory requirements are met because the use of conditions, such as institutional and engineering controls, may be more cost- effective than active remediation. As of February 2005, the Department estimated that it had reports of approximately 23,000 petroleum-contaminated sites. In 2004, the Department received an estimated 539 Discharge Report Forms in connection with petroleum storage facilities. As of March 2005, the Department had information indicating that approximately 2,000 "off-site" properties have been affected by contamination. Assessment Reports filed with the Department indicate that a substantial number of these sites may have been affected by discharges of petroleum or petroleum products. Petroleum discharges will in all likelihood continue to occur in the future at petroleum facilities. Petroleum discharges will in all likelihood continue to affect off-site properties in the future.
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.
Findings Of Fact Respondent is a registered septic tank contractor. He is licensed locally to install septic tanks in Lee and Collier counties, where he has installed 250-450 septic tank systems in the past 15 years. He has been a septic-tank contractor for 25 years. He has a good record for performing septic-tank services. In November 1995, Respondent performed work for Charles Allen on Marco Island. The work consisted of drainfield repairs and a septic-tank pumpout. Respondent performed the drainfield repairs and pumped out the liquids from the tank, but failed to pump out the solids from the bottom of the tank. Unaware that the solids had not been removed, Mr. Allen paid Respondent the $1500 price on which they had agreed for all of the work. Three months later, Mr. Allen's septic tank backed up, dumping sewage in his home. This happened late at night, and Respondent was unable to come right over to repair the system. Mr. Allen thus contacted another contractor, who, for $205, pumped out at least eight inches of solids, which were causing the sewage to back up into the house. Since the repairs, Mr. Allen has had no other problems with his system. It is evident that Respondent failed to remove the solids in November, as three months are insufficient time for this kind of build-up and Mr. Allen's system has worked fine since the failure in February. In March 1996, Respondent performed repair work to a drainfield in Bonita Springs. Petitioner rejected the work for final approval on March 27, 1996. The grounds for rejection were that the drainfield was installed 4.8 inches too low, a large amount of the drainfield aggregate was sinking into the drainfield replacement material, and Respondent had added an extension onto the existing drainfield, rather than replace the entire drainfield, as the repair permit had required. Petitioner's inspector informed Respondent of the rejection on March On April 3, the inspector drove by the site and found that Respondent had covered the repaired system without having first called for a reinspection. Circumstances unknown to Respondent, the homeowner, and Petitioner at the time of initial permit rendered almost the entire plan for this repair job unfeasible. Among other factors was the fact that the drainfield was planned for a front yard, sandwiched between a driveway and a landscaped area. Also, Respondent discovered deficiencies in the original drainfield once he uncovered it. However, Respondent was not justified failing to call for a reinspection before covering the system. Respondent was irritated with Petitioner's representative for failing to come immediately to inspect the work, but this is no excuse for covering the repaired system with dirt prior to obtaining a reinspection. Shortly before the final hearing, Respondent dug up the system, installed an entirely new drainfield, and completed the repairs in a satisfactory fashion.
Recommendation It is RECOMMENDED that the Department of Health and Rehabilitative Service enter a final order imposing an administrative fine of $1000 against Respondent for a false payment statement and failure to call for reinspection prior to covering a system. ENTERED on October 10, 1996, in Tallahassee, Florida. ROBERT E. MEALE Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 SUNCOM 278-9675 Fax Filing (904) 921-6847 Filed with the Clerk of the Division of Administrative Hearings on October 10, 1996. COPIES FURNISHED: Susan Mastin Scott Senior Attorney Department of Health and Rehabilitative Services Post Office Box 60085 Fort Myers, Florida 33906 Attorney Michael F. Kayusa Post Office Box 6096 Fort Myers, Florida 33911 Richard Doran, General Counsel Department of Health and Rehabilitative Services 1317 Winewood Boulevard, Room 204 Tallahassee, Florida 32399-0700 Gregory D. Venz, Agency Clerk Department of Health and Rehabilitative Services 1317 Winewood Boulevard Building 2, Room 204X Tallahassee, Florida 32399-0700
Findings Of Fact The Petitioner is the owner of real property located at 726 North Beach Street, Daytona Beach, Florida, also known as DEP Facility No. 64-9100172. The Petitioner has been the owner of this site from 1982 to the present. From approximately 1984 and 1988, it was leased to a Mr. Jack Delaney. Apparently, during that time or before, the site was used as an AAMCO transmission repair shop and automobile repair facility. The Respondent, Department of Environmental Protection (DEP, Department), is an agency of the State of Florida responsible, in pertinent part, for the administration of Florida's Abandoned Tanks Restoration Program. Through an agreement with Volusia County, Florida, the county where the subject site is located, the Department has delegated to the Volusia County Environmental Control Division inspection and regulatory authority for purposes of cleanup of sites contaminated by petroleum, petroleum products or hydrocarbons. The facility in question included two 1,000-gallon underground storage tanks and three 550-gallon underground storage tanks (UST's). All of the tanks, when in service, had contained petroleum products of one form or another. The tanks at the front or "street-side" end of the facility property, tanks one and five, most likely contained gasoline, when in service, although at the time of inspection and remedial action, the tanks were filled with water. All of the storage tanks at the facility were removed under the supervision of the Volusia County environmental regulatory agency. The tanks were properly disposed of by a qualified subcontractor, and the contaminated soil at the site was removed and stored in a segregated, protected fashion, until shipment to a thermal processor to be burned and thus cleansed of its petroleum-related pollutants. The Volusia County Environmental Control Division made an inspection of the subject site and on September 10, 1987, informed Mr. Delaney, the lessee, that a considerable amount of soil contamination, due to petroleum or petroleum products, was present on the site. The Department maintains that the finding by the county agency was that the soil contamination was due to improper surface disposal of used oils. Mr. Ed Smith, who testified for the Petitioner, has been involved as a petroleum de-contamination contractor for such sites hundreds of times and was present throughout the cleanup operations conducted at the subject site. He established that, indeed, there were spillages of used and waste oils and petroleum products at the site but that a great deal of the contamination also resulted from underground leakage from the storage tanks, or some of them. Preponderant evidence was not adduced by the Department, merely through its reliance upon DEP Exhibit 1, Request No. 59, to show that the contamination at the site solely resulted from surface spillage, in consideration of the testimony of Mr. Smith, which is accepted. On or about September 19-20, 1990, five underground storage tanks were removed from the facility site by Hydroterra Environmental Services, Inc., a contractor at the site. Thereafter, an underground storage tank closure report (closure report) for the AAMCO transmission facility was prepared by Hydroterra Environmental Services, Inc. That report is in evidence as the Petitioner's Exhibit 20. The report and testimony reveals that a total of three 550-gallon underground storage tanks were removed from the facility. There were two 550- gallon underground storage tanks located in front of the facility, known as tanks one and five. When those two tanks were removed, both were found to contain water. It is not clear what originally was stored in those tanks, but they were, in all likelihood, utilized for the storage of gasoline. The closure report concerning tank one and tank five reveals that the fuel-dispensing capability of those tanks was discontinued many years ago. One of the tanks, tank one, leaked. It had holes caused by corrosion. An environmental consultant, however, utilizing an organic vapor analyzer (OVA), performed soil-monitoring tests during the excavation and removal of these two 550-gallon UST's, which were thought to have formerly contained gasoline (tank one and tank five). His single OVA reading at that site showed a "0 PPM" (parts per million) for that sampling location associated with the excavation of tank one and tank five near the front of the AAMCO facility. The environmental consultant also obtained a groundwater sample during excavation and removal of those two tanks. The sample was analyzed for the presence of benzene, ethylbenzene, toluene, and xylene (BETX). The parameters for BETX are utilized to determine the presence of petroleum contamination. The analytical results for that sample for the tank one and tank five excavation site indicate that the parameters for those hydrocarbon compounds were all below detectable limits. Analytical results for the water sample, however, did indicate the presence of chlorobenzene. Chlorobenzene is associated with solvents, is an aromatic hydrocarbon compound and is a form of petroleum, that is, it is made from crude oil derivatives. With regard to these two tanks and, indeed, all of the tanks excavated, there was an absence of "free product" on the water table. That is, gasoline, waste oil or other forms of petroleum or petroleum products were not separately identified and existing on the surface of the groundwater table. Upon visual inspection, as shown by the Petitioner's Exhibit 20, the closure report, the testimony of Mr. Smith, as well as the photographs in evidence, tanks one, five, four, and six had multiple holes from small "pinhead size" to one inch in diameter. The tanks thus would have leaked any contents contained therein. Upon excavation of the tanks from the site, they were cleaned, de-commissioned, and transported to Jacksonville, Florida, to a subcontractor for disposal as scrap. Tanks two and three were determined to be intact, with no apparent holes. Tank one had one or more holes. The evidence shows that that tank was suspected of containing gasoline during its useful life, although when it was excavated, it was found to be full of water. The OVA and groundwater tests taken in conjunction with the removal of tanks one and five from the site near the front of the facility do not show excessive contamination, however. This is corroborated by the testimony of Mr. Smith, testifying for the Petitioner, who is a licensed pollutant storage tanks specialty contractor and a general contractor. He has removed hundreds of underground storage tanks and conducted many such cleanup projects. He himself supervised the removal of the tanks and was on site virtually every day. With regard to the removal site for tanks one and five, which were in close proximity to each other, he confirmed that he felt that the site was "clean". Thus, it has not been demonstrated by preponderant evidence that tanks one and five contributed to the contamination of groundwater and soil at the site. In the rear of the AAMCO transmission facility, there were two 1,000- gallon UST's. One of them had been used for storage of waste oil and transmission fluid (tank two). The second 1,000-gallon UST, tank three, had been used for storage of new transmission fluid. Tanks two and three were located on either side of a concrete apron at the rear door of the transmission shop. Tank two was excavated separately from tanks three, four and six. There is no evidence that tanks two and three, the two 1,000-gallon tanks, had holes or other sources of leakage. During the excavation and removal of tank two, an OVA was used to perform the soil monitoring tests. A single reading of 328PPM was recorded for the sampling location associated with the excavation and removal of tank two. A groundwater sample (MW-SB No. 3) was obtained from the tank pit, where tank two was excavated and removed. That sample indicates that there was a "odor of solvents". The analytical results for that groundwater sample indicate an analysis for benzene, ethylbenzene, toluene and xylene, showing that the parameters for benzene and ethylbenzene were below detectable limits. However, the analytical results for that sample indicate that chlorobenzene and 1,4- dichlorobenzene were above detectable limits, with significantly-elevated readings, representing excessive contamination with these constituents. These are consistent with the presence of aromatic solvents. Such compounds are hydrocarbons, being derived from petroleum. The groundwater sample related to tank three also showed very high levels of xylene, chlorobenzene, and 1,4-dichlorobenzene; volatile, aromatic hydrocarbon compounds derived from petroleum. The excavation pit for tank three yielded a groundwater sample of similar quality, in terms of the odor of solvents and elevated levels of the above-mentioned hydrocarbon compounds associated with solvents. Tank six, a 550-gallon tank, was located immediately adjacent to and in close proximity to tank three, between tank three and the concrete apron at the rear door of the transmission shop. It contained water at the time it was excavated and inspected. However, it had been used for storage of petroleum or petroleum products of unknown nature. Because of the nature of the business located at the site, the petroleum products contained in the other nearby tanks and because of the petroleum products saturating the soil in the area immediately surrounding and beneath the tank, it is inferred that the tank contained waste oil, transmission fluid, or solvents at various times and occasions. The excavation for tanks three and six, as well as "tank No. four", which was actually the 55-gallon oil and water separator, was one continuous excavation. The water sample taken with regard to the location of tank six shows significantly-elevated levels of chlorobenzene, 1,4-dichlorobenzene, and xylene. The Department's witness, Mr. Register, acknowledged that elevated levels of pollutants in the pit associated with tanks four, three and six were consistent with the presence of solvents and waste oil or "oils and greases". Mr. Smith, the certified pollution specialty contractor supervising and conducting the project, described in his testimony how one can recognize contaminated soil in the field and that soil is saturated when one can squeeze petroleum compounds out of the soil with the hand. This shows excessive contamination of soils at such a site, as was acknowledged by Mr. Register, the engineer for the Bureau of Waste Cleanup for the Department, who testified. Mr. Smith thus established that the soils in the pit at the rear of the facility were saturated with petroleum or petroleum products. These were derived from waste oils and greases, consisting of waste oil and transmission fluid, as well as solvents. The pollutants leaked from tanks six and four, although Mr. Smith acknowledges in his testimony that tank four is not really considered to be a storage facility but, rather, a 55-gallon drum used as an oil/water separator, connected by a clay pipeline to a catch basin immediately in the rear of the apron and rear door of the building. In summary, through Mr. Smith's testimony, it was established that there was excessive contamination at the site, as shown by the saturation of the soils in the excavation pits from which the tanks were removed, in the manner described above. Under Mr. Smith's supervision, all appropriate remedial action was done at the site, all contaminated soil was removed and cleansed at an appropriate thermal treatment facility. The site was declared "clean" by the county agency referenced above, which had supervision of the project under its agreement with the Department. The initial remedial action task undertaken by the Petitioner, as shown by Mr. Smith's testimony, included removal of excessively-contaminated soils, as defined under Section 62.770.200(2), Florida Administrative Code, concerning the excavations at the rear of the transmission shop. Tank six is the only storage tank shown to have been leaking at the rear of the shop, but the spread or diffusion rate and area of contamination which leaked from that tank through the excavation area is not precisely definable. In any event, a significant portion of the soil in the excavation area at the rear of the transmission shop, including that occupied by tank six, was shown to be excessively contaminated and much of it emanated from tank six, especially evidenced by its central location in the contaminated portion of the site. Removal of that contaminated soil was part of the initial remedial action task. Likewise, the removal of the tanks was part of the performance of the initial remedial action task. In fact, all of the excess contamination could not be removed by removal of the soil without removing the tanks first, to get access to the excessively-contaminated areas beneath the surface grade. There is, however, no evidence that the initial remedial action task, with regard to each tank and tank site, which included removal of the tanks and excessively- contaminated soils, included any necessity to recover "free product" with regard to any of the tanks or tank locations. Finally, it is shown that transmission fluid and waste oil, as well as the other, solvent-related constituents of the contamination at the site, are petroleum or petroleum products. They can be, and are used, as a mixture amounting to a "liquid fuel commodity made from petroleum" and such waste petroleum products are often used in Florida, particularly for boiler fuel to fire industrial-type boilers. These compounds found at the site are both petroleum and petroleum products and are hydrocarbons, as defined in Section 376.301, Florida Statutes. It was thus demonstrated that the contamination at the facility was the result of a discharge of petroleum products, from a petroleum storage system, in the manner and for the reasons delineated more particularly above. On or about January 30, 1991, the Petitioner filed an abandoned tank restoration program application form with the Department. The Department issued the Petitioner an "order of eligibility" under that program for the abandoned tank restoration, which final order was entered on August 16, 1991. That order of eligibility is limited to "contamination related to the storage of petroleum products, as defined in Section 376.301(10), Florida Statutes. On February 14, 1992, the Petitioner filed a reimbursement application for all allowable costs with the Department. On or about April 28, 1993, a "final order of determination of reimbursement" for allowable costs was issued by the Department, which denied all reimbursement of cleanup costs associated with contamination of the property. That action was the result of the Department's position that the contamination resulted from improper disposal of petroleum products at the AAMCO transmission facility and not due to contamination of the site from the storage tank system.
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 RECOMMENDED that a Final Order be entered by the Department of Environmental Protection awarding reimbursement for the cleanup of DEP Facility No. 64-9100172 in accordance with the considerations, findings and conclusions made above. DONE AND ENTERED this 29th day of May, 1996, in Tallahassee, Florida. P. MICHAEL RUFF, 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 29th day of May, 1996. APPENDIX TO RECOMMENDED ORDER CASE NO. 93-3313 Petitioner's Proposed Findings of Fact 1-7. Accepted. 8. Rejected, as constituting argument and not a proposed finding of fact. 9-10. Accepted. 11. Accepted, as to those tanks delineated more particularly in the Hearing officer's findings of fact. 12-13. Accepted. Rejected, as subordinate to the Hearing Officer's findings of fact on this subject matter. Accepted. Respondent's Proposed Findings of Fact 1-2. Accepted. 3. Accepted, but not itself materially dispositive. 4-12. Accepted, but not all of which are materially dispositive. 13-19. Accepted, but not necessarily materially dispositive. 20-23. Accepted. 24-25. Accepted, but not material. 26. Rejected, as subordinate to the Hearing Officer's findings of fact on this subject matter. 27-29. Accepted. 30. Accepted, but not materially dispositive. 31-34. Accepted, but not in themselves materially dispositive. 35-36. Accepted. 37-39. Accepted, but immaterial. 40-45. Accepted, but not in themselves materially dispositive. 46-49. Accepted. 50. Accepted, only as an indication of the Department's position. 51-55. Accepted. 56-64. Rejected, as contrary to the preponderant weight of the evidence and subordinate to the Hearing Officer's findings of fact on this subject matter. 65. Accepted. 66-69. Rejected, as contrary to the preponderant weight of the evidence and subordinate to the Hearing officer's findings of fact on this subject matter, and erroneous as a matter of law. COPIES FURNISHED: Robert J. Riggio, Esquire Owens & Riggio, P.A. 125 North Ridgewood Avenue Daytona Beach, FL 32114 W. Douglas Beason, Esquire Department of Environmental Protection 3900 Commonwealth Boulevard Tallahassee, FL 32399-3000 Virginia B. Wetherell, Secretary Department of Environmental Protection 3900 Commonwealth Boulevard Tallahassee, FL 32399-3000 Kenneth Plante, General Counsel Department of Environmental Protection 3900 Commonwealth Boulevard Tallahassee, FL 32399-3000
The Issue Whether Petitioner, Department of Community Affairs (the Department), is legally precluded in this proceeding from taking agency action to enforce the reporting and fee provisions required pursuant to Chapter 252, Part II, Florida Statutes, against Respondent, Goodson Paving, Inc., for the reporting years of 1989 through 1994, inclusive, by operation and application of Section 95.011 and Section 95.11(3)(f), Florida Statutes (statute of limitations); and, Whether the Department is legally and equitably precluded in this proceeding from taking agency action to enforce the reporting and fee provisions required pursuant to Chapter 252, Part II, Florida Statutes, against Respondent for the reporting years of 1989 through 1994, inclusive, by operation and application of Section 95.11(6), Florida Statutes (doctrine of laches).
Findings Of Fact The Florida Hazardous Materials Emergency Response and Community Right to Know Act (the Act), Part II, Chapter 252, Florida Statutes, was first passed in 1988. The purpose of Act is to provide information to response personnel in an emergency regarding the type of chemicals and substances that might be present at a facility. The outreach program conducted by the Department of disseminating information to facilities which potentially may be required to report was initiated in 1988 and continued into 1989. It included mass mailings to over 100,000 facilities; conduct of regional seminars, which were advertised in newspapers; establishment of an Internet site; publishing a how-to-comply handbook; and working with local communities and other state agencies. There are approximately 15,000 to 16,000 active facilities reporting under various sections of the Act. The Department did not contact Respondent during the outreach program. Respondent has been located at 5855 Industrial Drive, Cocoa, Florida, since April 1989. Respondent reported the following number of employees to the Florida Department of Labor and Employment Security for unemployment compensation tax purposes for the last month of each year, from 1989 through 1998: 1989 24 1990 22 1991 25 1992 30 1993 31 1994 35 1995 37 1996 40 1997 44 1998 45 Respondent is in the business of site contracting and road building/construction and uses diesel fuel which it stores on-site for fueling its trucks and construction equipment. Respondent does not distribute the diesel fuel or offer it for retail sale. The site located at 5855 Industrial Drive, Cocoa, Florida, has been an asphalt plant and road construction office since approximately 1949. Respondent stores on-road diesel fuel and off-road diesel fuel at the site for self-use for completion of contracted projects. The Brevard County Fire and Rescue Department performs annual inspection of Respondent's site at 5855 Industrial Drive, Cocoa, Florida, as well as inspection of the shop, the office, and the storage tanks. Respondent has completed and filed the State of Florida Department of Environmental Protection Storage Tank Registration forms and the State of Florida Environmental Protection Plant Storage Tank System Inspection Report for every year of operation since at least 1991. Respondent completed and filed the State of Florida Department of Environmental Protection Storage Tank Facility Compliance Inspection Report for the year 1999 on September 8, 1999. Respondent received the State of Florida Department of Environmental Protection Storage Tank Placard issued in July of 1999 with an expiration date on June 30, 2000. Respondent is in possession of the requisite State of Florida Storage Tank Third Party Liability and Corrective Action Policy Declarations with an effective date of January 1, 1999. Respondent has maintained uninterrupted insurance for the on-site tanks since 1989. Respondent pays a State of Florida Pollutant Tax on each gallon of diesel fuel purchased through its supplier, Coastal Refining and Marketing, Inc. The tax is collected by the supplier and remitted to the State of Florida. The State of Florida Department of Environmental Protection Storage Tank Facility Compliance Inspection Reports are filed with the State of Florida Department of Environmental Protection in Tallahassee, Florida. The Brevard County Fire and Rescue Department is aware and informed of the chemicals and type of operation located at Respondent's site at 5855 Industrial Drive, Cocoa, Florida. The only chemicals possessed by Respondent at the site at 5855 Industrial Drive, Cocoa, Florida, are the aforementioned diesel fuel tanks, motor oil, hydraulic oil, and four one-gallon cans of paint. Respondent does not manufacture asphalt or maintain liquid asphalt at the site at 5855 Industrial Drive, Cocoa, Florida. Prior to receiving the April 2, 1999, Notice of Violation and Intent to Assess Late Fee, Respondent had not had contact with The Department. Respondent has filed the requisite monthly reports to the State of Florida Department of Revenue and has paid the requisite road and fuel tax to the State of Florida Department of Revenue since incorporation. Respondent, Goodson Paving, Inc., does have a current, valid Occupational License issued by Brevard County, Florida. Respondent's diesel fuel storage containment system is built to the code issued by Brevard County and is approved by the Brevard County Inspectors each year. Prior to receiving the April 2, 1999, Notice of Violation and Intent to Assess a Late Fee from the Department, Respondent, in the previous ten or eleven years, has had annual inspections conducted by the Brevard County Fire and Rescue Department and the other county inspectors; has paid taxes to the State of Florida Department of Revenue; and has had a valid Occupational License. Respondent was not informed of the obligation to report under Part II of Chapter 252, Florida Statutes. On April 8, 1999, Respondent received the Department's Notice of Violation and Intent to Assess a Late Fee dated April 2, 1999. Respondent timely requested an administrative hearing regarding the Department's April 2, 1999, Notice of Violation and Intent to Assess Late Fee, pursuant to Section 120.569, Florida Statutes, and implementing rules. The staff of the Department's Division of Emergency Management Compliance Planning Section who administer the Emergency Planning and Community Right-to-Know Act (EPCRA) and the Act of 1988 are also responsible for assisting the Division's Emergency Operations Center during activations for disasters such as hurricanes or fires. During activations, the routine hazardous materials program duties are subservient to other Division of Emergency Management duties. Respondent suffered no prejudice from the timing of the Department's April 1999 Notice of Violation and Intent to Assess a Late Fee since: (1) the annual inventory forms are required by federal law; (2) Respondent was able to complete the forms based upon available information; and (3) no interest, late fee, or other adverse financial impact will result if the annual fees are timely paid in response to the notice. Respondent is responsible for the fee obligations under the statutes and rules for the years 1989-1998, in the total amount of $832.50.
Recommendation That the Secretary of the Department of Community Affairs enter a final order which holds that: Respondent is responsible for reporting diesel fuel in excess of the threshold planning quantity pursuant to 42 U.S.C. Section 11022 and Sections 252.85 and 252.87, Florida Statutes, for the years 1989-1998 inclusive; and for the fee obligations under Section 252.85, Florida Statutes, and Rule 9G-14.003(3), Florida Administrative Code, for the reporting years 1989-1998, inclusive. Respondent owes the Department annual registration fees totaling $832.50 if the reports and fees are submitted within thirty days of the Department's final order in this matter. Respondent can be assessed additional late fees if all required reports, fees, and late fees are not timely paid, in accordance with Section 252.85(4)(b)3, Florida Statutes. DONE AND ENTERED this 1st day of December, 1999, in Tallahassee, Leon County, Florida. DANIEL M. KILBRIDE 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 1st day of December, 1999. COPIES FURNISHED: Ross Stafford Burnaman, Esquire Department of Community Affairs 2555 Shumard Oak Boulevard, Suite 325A Tallahassee, Florida 32399-2100 Douglas W. Baker, Esquire John H. Evans, P.A. 1702 South Washington Avenue Titusville, Florida 32780 Jim Robinson, General Counsel Department of Community Affairs 2555 Shumard Oak Boulevard, Suite 315 Tallahassee, Florida 32399-2100 Steven M. Seibert, Secretary Department of Community Affairs 2555 Shumard Oak Boulevard, Suite 100 Tallahassee, Florida 32399-2100
The Issue Whether Petitioner's site, Hughes Supply, Inc. located at 2920 Ford Street, Fort Myers, Lee County, Florida is eligible for restoration under Section 376.3072, Florida Statutes.
Findings Of Fact Upon consideration of the oral and documentary evidence adduced at the hearing, the following relevant findings of fact are made: Hughes is a Florida Corporation in good standing and authorized to do business in the State of Florida. The Department's facility no. 36-8519331 (the Facility), owned and operated by Hughes and the subject matter of this proceeding, is located at 2920 Ford Street, Ft. Myers, Lee County, Florida, and is a "Facility" as defined in Section 376.301(5), Florida Statutes. The Facility consisted of (a) two underground storage tanks (USTs), one 4000 gallons UST (gasoline tank) and one 8000 gallons UST (diesel tank), and (b) four monitoring well, and is a "petroleum storage system" as defined in Section 376.301(15), Florida Statutes. At all times material to this proceeding, Hughes held, and was the name insured of, an effective third party pollution liability insurance policy (No. FPL 7622685 - Renewal No. FPL 7621566) applicable to the Facility that was issued in accordance with, and qualified under, Section 376.3072, Florida Statutes. Hughes paid annual premiums exceeding $20,000.00 for the above insurance. In accordance with Sections 376.3072, Florida Statutes, and Chapter 17- 769, Florida Administrative Code; the Department issued to Hughes a Notice of Eligibility pertaining to the Facility and the third party pollution liability insurance referred to in Finding of Fact 4 above. Lee County, Florida has a local program approved by the Department pursuant to Section 376.3073, Florida Statutes, to provide for the administration of the Department's responsibilities under certain sections of Chapter 376, Florida Statutes. Diesel fuel was placed into the diesel tank at the Facility on August 12, 1991, and no diesel fuel has been placed in the diesel tank at the Facility since that date. On Thursday, August 29, 1991, a contractor bidding on the removal of the tanks detected free product in one of the monitoring wells at the Facility and told Larry Carman, the Warehouse Manager for Hughes. Mr. Carman told Phillip Ross, the Branch Manager for Hughes, who in turn informed Gene Kendall, the Operations Coordinator for Hughes. All of this occurred on August 29, 1991. On Friday, August 30, 1991, an employee of IT Corporation, acting upon the request of Gene Kendall, sampled the four monitoring wells at the Facility and found six inches of free product in the northwest monitoring well. On Tuesday, September 3, 1991, Fred Kendall discussed the discharge with Bill W. Johnson, Supervisor, Lee County Storage Tank Local Program. During this discussion, Johnson learned that the diesel tank had not been emptied. Johnson advised Kendall that the diesel tank had to be emptied of its product and placed out of service. On Tuesday, September 3, 1991 Mr. Kendall completed the Discharge Reporting Form (DRF) pertaining to the discharge and mailed the DRF to Johnson on September 4, 1991. The DRF indicated August 30, 1992, the day that IT Corporation confirmed the discharge, as the day of discovery of the discharge. The discharge was diesel fuel as indicated by the DRF and a "petroleum product" as defined in Section 376.3-1(14), Florida Statutes. The discharge reported in the DRF constitutes a "discharge" as defined in Section 376.301(4), Florida Statutes, which constitutes an "incident" as defined in Section 376.3072(2)(c), Florida Statutes, and as described in Rule 17-769.600, Florida Administrative Code. On Wednesday, September 4, 1991, Mr. Kendall also mailed a letter to Johnson stating Hughes' intent to seek restoration coverage for the Facility, pursuant to Policy No. FPL 762285, Renewal No. FPL 7621566. On September 13, 1991 when Hooper, Inspector for the Lee County Storage Tank Local Program, inspected the Facility the diesel tank contained a total of 39 5/8 inches of diesel and water, of which 4 3/4 inches was water. On September 16, 1991 when Hooper again inspected the Facility, the diesel tank contained a total of 36 1/2 inches of diesel and water, of which 4 1/2 inches was water. On this date, Hooper advised Hughes that the diesel tank had to be emptied of its product. The inspection report issued on September 16, 1991 by Hooper advised Hughes that the Facility was not in compliance with Chapter 17-761, Florida Administrative Code. On September 17, 1991, Hughes had the diesel tank emptied of all its product. Although Hughes was in the process of emptying the diesel tank by giving diesel away, at no time between August 30, 1991 and September 16, 1991 was the diesel tank completely empty of its product. Between August 30, 1991 and September 16, 1991 Hughes did not test the diesel tank to determine if the diesel tank was leaking and, if so, to pinpoint the source of the leak. There was no evidence that either the Department or Lee County Storage Tank Local Program personnel ever informed Hughes before September 16, 1991 that there was a time frame within which the diesel tank had to be emptied of all of its product, and placed out of service in order for Hughes to be in compliance and eligible for reimbursement for restoration under the FPLIRP. Likewise, Hughes did not request any information from the Department or the Lee County Local Program personnel concerning any time frames within which the diesel tank had to be tested for leaks or emptied of its contents to prevent any further discharge in order to be eligible for reimbursement for restoration under the FPLIRP. Between August 29, 1991 and September 17, 1991 Hughes bailed the monitoring wells at the Facility on a daily basis, removed the free product from the monitoring wells, and placed the free product in a sealed 55-gallon drum. When the discharge was discovered, Hughes made the decision to close the Facility by tank removal, and at this point did not intend to repair or replace the Facility. As a result of an inspection of the Facility by the Lee County Local Program personnel in May, 1991, Hughes was made aware that the Facility was not in compliance with Chapter 17-761, Florida Administrative Code, since the gasoline tank had not been used in over three years, and there had been no closure of the gasoline tank. This noncompliance with Chapter 17-761, Florida Administrative Code, concerning the gasoline tank was also a portion of the noncompliance report filed by Hooper on September 16, 1991. The gasoline tank comes within the definition of "unmaintained" as defined by Rule 17-761.200(2), Florida Administrative Code. Both the diesel tank and the gasoline tank were removed on October 28, 1991 by a Florida licensed storage tank system removal contractor, and the Facility permanently closed by IT Corporation on October 29, 1991. In December, 1991, Hughes filed a tank closure assessment report pertaining to the removal of the diesel and gasoline tanks from, and closure of, the Facility. The tank closure assessment report was prepared by IT Corporation upon a request made by Hughes to IT Corporation on September 3, 1991 for a tank closure assessment proposal which was submitted by IT Corporation to Hughes on September 4, 1991. In April or May, 1992, Hughes filed with Lee County a contamination assessment report prepared by IT Corporation pertaining to the removal of the USTs from and closure of the Facility. Subsequent to discovery of the discharge. Hughes has expended approximately $60,000.00 as of June 10, 1992, on the Facility in connection with the USTs. Site rehabilitation costs for the Facility have been estimated in a range of $220,000.00 to $245,000.00 as of June 10, 1992. In the early part of 1991 water was present in the diesel tank, and approximately six months before discovering the discharge in August, 1991, Hughes had the water pumped out of the diesel tank. Hughes gave no explanation for the presence of water in the diesel tank. Neither the Department nor the Lee County Local Program personnel were notified of this unexplained presence of water in the diesel tank.
Recommendation Based upon the foregoing findings of fact and conclusions of law, it is recommended that the Department enter a Final Order denying Hughes application for restoration coverage under the Florida Petroleum Liability Insurance and Restoration Program. DONE and RECOMMENDED this 24th day of September, 1992, 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 24th day of September, 1992. APPENDIX TO RECOMMENDED ORDER IN CASE NO. 91-8334 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. Rulings on Proposed Findings of Fact Submitted by the Petitioner 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); 2-3(2); 4-5(3); 6- 8(4); 9(5); 10(6); 11(8,9); 12(10,11); 14(15,22); 15(10); 16(19); 18(10); 19(13); 20-21(7); 22-23(24); 24(21); 25(17); 26-29(20); 30(15); 31(16); 32(22); 33(23); 35(23); 36(7); 37(23); 38(24); 39(25); 40(26); 41(27); 42-43(27); and 44(15,22). Proposed Findings of Fact 13, 17 and 34 are neither material nor relevant to the conclusion reached in the Recommended Order. Rulings on Proposed Findings of Fact Submitted by the Respondent 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:1-2(2); 3(3); 4-6(5); 7(6); 8(22); 9(7); 10(8); 11(9); 12(10); 13-16(11); 17(12); 18(13): 19(18); 20(17); 21-22(14); 23-24(15); 25-26(28); 27(16); and 28(23). COPIES FURNISHED: Scott E. Wilt, Esquire Maguire, Voorhis and Wells 2 South Orange Plaza Orlando, Florida 32801 Brigette A. Ffolkes, Esquire Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Carol Browner, Secretary Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Daniel H. Thompson, Esquire General Counsel Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32399-2400
The Issue Are the Respondents legally liable for petroleum contamination of soil and groundwater at the Economy Tire Service Station, 1858 Main Street, Sarasota, Florida and, if so, should the Respondents be required to perform the Corrective Actions included in the Notice of Violation and Orders for Corrective Action issued on February 19, 1993, by Petitioner, Department of Environmental Protection?
Findings Of Fact Upon consideration of the oral and documentary evidence adduced at the hearing, the following relevant findings of fact are made: The Department is the administrative agency charged with the responsibility of administering and enforcing the provisions of Chapter 376, Florida Statutes, and the rules promulgated thereunder in Title 17, Florida Administrative Code. Bryant A. Meeks, Trustee, is the owner of the property situated at 1858 Main Street, Sarasota, Florida (Property). Meeks is a person within the meaning of Section 376.301(12), Florida Statutes. Stanley M. Butler is the operator of Economy Tire Service (Business) on the Property, and has continually operated the Business on the property, beginning on November 26, 1980. The Property is specifically identified in a Quit-Claim Deed dated September 10, 1980, conveying all of the interest of O. M. Bailey in and to the Property, to Bryant A. Meeks and Jacqueline F. Meeks. The Property is legally described as: "the East one-half of Lot 3 and all of Lot 4, Subdivision of Lot 15, Block H, PLAT OF SARASOTA, as per plat thereof recorded in Plat Book 1, Page 166, Manatee County Records; and being the same property conveyed by Special Warranty Deed dated July 1, 1979, executed by BP Oil Corporation, a Delaware Corp., recorded in Deed Book 1012, Page 1905, Public Records of Sarasota County Florida." On December 1, 1977, SWT, Inc., purchased the Business from William E. Mitchell and Margaret G. Mitchell. Meeks was President of SWT, Inc. 6 After the acquisition of the Business by SWT, Inc., Meeks hired Butler to operate the Business. On July 17, 1979, Meeks, and his wife, Jacqueline F. Meeks, acquired an undivided one-half interest in the Property by Special warranty Deed from American Petrofina Company of Texas. O. M. Bailey acquired the remaining undivided one-half interest in the Property in the same deed. By Quit-Claim Deed dated September 10, 1980, O. M. Bailey conveyed all of his right, title and interest in the Property to Bryant A. Meeks and Jacqueline F. Meeks. On November 26, 1980, SWT, Inc. sold the Business, including fixed assets, inventory and accounts receivable to Butler. The sale included four underground petroleum storage tanks situated on the Property. On December 1, 1980, Stanley M. Butler and Dixie J. Butler leased the Property from Bryant A. Meeks and Jacqueline F. Meeks for a term of ten years, with an option to renew the lease and an option to purchase the Property. The lease was extended for ten years on January 4, 1991. The lease requires Butler to comply with "all statutes, ordinances, rules, orders, regulations and requirements of Federal, State and City Government and any and all their Departments and Bureaus applicable to said premises..." By Trust Deed dated September 23, 1983, Bryant A. Meeks and Jacqueline F. Meeks conveyed their right, title and interest in the Property to Bryant A. Meeks as Trustee, under the Bryant A. Meeks, Jr., Trust dated August 24, 1983. The Property remains under the ownership of Bryant A. Meeks, Trustee. At all times material to this proceeding, the Business on the Property has consisted of automobile service station, selling various grades of gasoline, diesel fuel, tires and automobile repairs. At all times material to this proceeding, there were four 3,000 gallon, carbon steel, underground petroleum storage tanks, one underground waste oil tank of unknown size (Tank Five) and two underground kerosene tanks of unknown size (Tank Six and Tank Seven) The four underground gasoline tanks shall be collectively referred to as "Gasoline Tanks" and individually as Tank One through Tank Four moving in a northerly direction, with Tank One being adjacent to the service bays on the Property and Tank Four being adjacent to Main Street. Tank Five is located just south of the office adjacent to the east side of the service bays. Tank Six and Tank Seven are located south of the pump island and just north of the office and service bays. The Gasoline Tanks have been continuously owned by Butler since Butler first acquired the Business on November 26, 1980. Butler did not purchase Tank Five, Tank Six and Tank Seven at the time he purchased the Business. At all times material to this proceeding, the Gasoline Tanks contained various grades of gasoline including regular leaded, unleaded and premium unleaded gasoline, as well as diesel fuel. At all times material to this proceeding, the Property was a facility within the meaning of Section 376.301(7), Florida Statutes. In the summer of 1978, it was determined that Tank Four was the source of water pumped into a customer's automobile gas tank. Tank Four was tested and found to be leaking. Tank Four was disconnected from service without removing all of the gasoline product. During this time, Butler advised Meeks that Tank Four was leaking, notwithstanding Meeks' testimony to the contrary. When Meeks purchased the undivided one-half interest in the Property in July 1979, Butler again advised Meeks that Tank Four had been disconnected due to a leakage, notwithstanding Meeks' testimony to the contrary. Meeks advised Butler that the Property had been purchased "as is". Since November 26, 1980, Butler has been an Operator of the Facility within the meaning of Section 376.301(10), Florida Statutes. Butler switched suppliers in 1981 and his new supplier, Amoco Oil, offered to fiberglass line Tank Four. The contractor hired by Amoco Oil pumped out the petroleum product left in the Tank Four when it had been disconnected. The contractor determined that Tank Four could not be fiberglass lined due to the holes in the tank. On May 21, 1984, there was a complaint by the Sarasota Fire Department of gasoline odors from the Facility. The gasoline vapors resulted from a leak in the underground air lines in conjunction with gasoline being discharged from Tank Four because of perforations in the tank before it was pumped out in 1981. The Department notified Butler of this finding and requested that Butler perform a hydrologic study to determine the extent of contamination. Apparently, Butler never had this hydrologic study performed. On October 12, 1984, Butler was given a warning notice by the Department that he was in violation of Chapter 403, Florida Statutes, and regulations promulgated thereunder. Additionally, the Department advised Butler to commence an contamination assessment which would require a Contamination Assessment Report to be submitted to the Department. The record does not reflect that a contamination assessment was commenced or that a Contamination Assessment Report was submitted to the Department. The Department has been aware of Meeks' ownership of the Property since October 1984. Butler registered the Gasoline Tanks and the Waste Oil Tank with the Department in March, 1986. In 1989, Butler installed four monitoring wells at the Facility adjacent to the Gasoline Tanks. On July 27, 1989, another complaint concerning gasoline odors was reported. On August 17, 1989, a written notice was mailed to Butler by the Department advising Butler that he was in violation of Chapters 403 and 376, Florida Statutes. There is no evidence that the Department sent Meeks a notice of such violation. During an inspection of the Facility in April 1990, the inspector found that: (a) the Gasoline Tanks had not been upgraded and retrofitted as required by Department rule; (b) the Gasoline Tanks did not have the requisite overfill and overspill protection as required by Department rule; (c) there was petroleum product in all four monitoring wells, with well no. 1 having a high petroleum odor and a detectable petroleum odor in wells nos. 2, 3, and 4; (d) the organic vapor analyzer readings taken in each of the monitoring wells indicated hydrocarbon vapors in excess of 5,000 parts per million and; (d) a tightness test had not been performed at the Facility in accordance with Department rules, and in response to the Discharge Notification Form filed by Butler on November 13, 1989. It was not until the fall of 1990 that Meeks received a notice from the Department concerning the contamination of the Property and that Meeks would be liable for cleaning up the contamination. However, Meeks failed to present sufficient evidence that he had been prejudiced by the Department's delay in notifying him of the contamination due to the unavailability of witnesses or records. There was no showing that Meeks had made any attempt, unsuccessful or otherwise, to secure witnesses and records concerning the condition of the Property before his acquisition in 1979 and 1980. During an inspection of the Facility in February 1991, the inspector found that: (a) one of the Gasoline Tanks was full of water; (b) the Gasoline Tanks had not been upgraded and retrofitted as required by Department rule and; (c) the Gasoline Tanks did not have the requisite overfill and overspill protection as required by Department rule. Amoco Oil removed all of the petroleum product from Tanks One, Two and Three in October 1991. Butler then contracted with Dickerhoof to inspect the Gasoline Tanks and reline them with fiberglass. After inspecting Tank One and Tank Two, Dickerhoof determined that these tanks could not be relined because of their condition. There were pin holes on the inside of the tanks in addition to split seams and perforations in the tops of the tanks. Butler decided not to inspect Tank Three since he could not operate with only one tank. Tank Four had been taken out of service earlier. On October 22, 1991, Eugene Cherno, Environmental Supervisor, Pollution Control Division, Sarasota County Government advised Butler not to return the Gasoline Tanks to service due to their poor condition. During an inspection of the Facility in May 1992, one-half inch of free product with a fairly strong petroleum odor was bailed from the southwest monitoring well. The color and condition of the free product indicated that the petroleum discharge had occurred within one to four years before the free product was removed. There was a slight petroleum odor in the remaining three monitoring wells. In July 1992 Butler contracted with James Nuwer to remove and replace the Gasoline Tanks and gas lines with new underground storage tanks and gas lines. Upon removing the Gasoline Tanks, Nuwer found small holes in Tanks One, Two and Three and somewhat larger holes in Tank Four. All of the Gasoline Tanks were corroded and had perforations on the welded seams. On July 10, 1992, when the Gasoline Tanks were excavated there was a strong petroleum odor permeating the entire area around the facility even though the petroleum product had previously been pumped out of the Gasoline Tanks. The soil removed in the process of excavating the Gasoline Tanks was a porous sand type soil. During the excavation and replacement of the Gasoline Tanks, Environmental Science and Engineering, Inc. (ESE), on behalf of Butler, prepared a UST Closure Environmental Assessment Report (Closure Assessment Report). During the excavation activities, ESE monitored the soils removed from the excavation using an organic vapor analyzer (OVA), equipped with flame ionization detector (FID). The OVA/FID measures total vapors, including methane, in the parts per million (ppm) range. An unfiltered and filtered screening was performed on each sample to evaluate the total organic vapor and methane concentration. The methane concentration was subtracted from the total organic vapor concentration to evaluate the soil for excess soil contamination. Soil vapor screening was performed in accordance with procedures defined in Rule 17-770.200(2), Florida Administrative Code. Twenty-one soil samples were collected for OVA/FID screening. The results of the OVA/FID screening show the total OVA reading in all 21 samples being greater than 1000 ppm. After subtracting the methane reading from total OVA reading, the samples ranged from a total OVA reading of 890 ppm to 1000 ppm. Pursuant to Rule 17-770.200(2), Florida Administrative Code, soils excessively contaminated by gasoline or diesel fuel will cause a total hydrocarbon reading of 500 ppm for gasoline and 50 ppm for diesel fuel using OVA/FID screening. Based on these results, the soil on the Property is excessively contaminated as that term is defined in Rule 17-770.200(2), Florida Administrative Code. ESE collected groundwater samples from monitoring wells nos. 1, 2, and The analytical results indicate the detection of both purgeable aromatic and polynuclear aromatic hydrocarbons in the groundwater samples from monitoring wells 1, 2, and 3. In each groundwater sample the benzene, total volatile organic aromatic (TVOA) and methy-tertiary-butyl-ether (MTBE) are reported in concentration presented as micrograms/liter (ug/L) as follows: MW1 MW2 MW3 Benzene 2,140 ug/L 737 ug/L 732 ug/L TVOA's 3,160 ug/L 2,080 ug/L 1,430 ug/L MTBE's 6,090 ug/L 5,980 ug/L 2,940 ug/L These levels exceed the Site Rehabilitation Levels (SRL's) for benzene, TVOA and MTBE of 1 ug/L, 50 ug/L and 50 ug/L, respectively, established in Rule 17- 770.730(5)(a), Florida Administrative Code. Monitoring well no. 4 was not sampled because free product was observed on the groundwater in the well, demonstrating contamination. ESE was unable to determine the extent of the excessively contaminated soils at the Facility due to limiting site conditions. The excavated excessively contaminated soils were transported to the Sarasota County Landfill for bio-treatment. Tank Five, Tank Six and Tank Seven are unmaintained underground storage tanks on the Property that have not been properly closed. On February 19, 1993, the Department issued a Notice Of Violation And Orders For Corrective Action against Meeks and Butler concerning the contamination of the Property on which the Facility is located. At a meeting on March 26, 1993, with Meeks, Butler and representatives of the Department present, the matter of the cost of cleaning up the contamination was discussed by those present. Meeks contends that at this meeting a Department representative advised those present that the Department would pay for the cleanup of the contamination but would not pay for the removal of the three underground storage tanks remaining on the Property. Meeks further contends, that in reliance on this commitment he did not pursue an eviction action against Butler. Meeks presented no evidence on how his not pursuing the eviction action against Butler was detrimental to him. A second meeting was held on July 14, 1993, where only Meeks and Department representatives were present. Meeks contends that another Department representative advised him that the Department could not honor the previous commitment to pay for the cleanup. There is insufficient evidence to show that a Department representative made a commitment for the Department to pay for the contamination cleanup on the Property. However, assuming that a commitment was made, there is insufficient evidence to show that Meeks' reliance on that commitment resulted in Meeks foregoing his eviction action against Butler. Furthermore, even if Meeks did rely on the commitment to forego his eviction action against Butler, there is insufficient evidence to show that his change in position was detrimental or that his reliance on the commitment for any reason resulted in a change of position that was detrimental to Meeks. There is sufficient evidence to show that a Contamination Assessment should be completed at the Facility to determine the extent of the petroleum contamination on the Property. There is sufficient evidence to show that one or more of the Gasoline Tanks have discharged gasoline or diesel fuel to the soils and groundwater on the Property. There is sufficient evidence to show that Tank One, Tank Two and Tank Three discharged either gasoline or diesel fuel to the soils and groundwater on the Property during the several years before the removal of the petroleum product from those tanks in October 1991. Likewise, there is sufficient evidence to show that Tank Four discharged gasoline to the soils and groundwater on the Property from the summer of 1978, when it was taken out of service, until the remaining gasoline was pumped out in 1981. The Respondents presented no evidence that some or all of the contamination was attributable to someone other than the Respondents. While it might be inferred that the Department incurred expenses and costs while investigating this matter, the Department presented no evidence to support any expenses or costs for its investigation.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is, accordingly, Recommended that the Respondents shall take the following specific corrective actions to address the violations: Respondents shall, within 60 days of receipt of the Final Order, properly close the three unmaintained underground storage tank systems remaining on the Property in accordance with Rule 17-761.800(2), Florida Administrative Code Respondents shall, at time of the closure of the unmaintained underground storage tank systems, conduct a closure assessment in accordance with Rule 17.761.800(3), Florida Administrative Code, and shall submit the closure assessment report to the proper authority within 60 days of the date of the closure. Respondents shall, within 30 days of receipt of the Final Order, initiate a contamination assessment, as required in Rule 17-770.600(1), Florida Administrative Code. Respondents shall conduct a petroleum contamination cleanup in accordance with Rule 17-770, Florida Administrative Code, in the manner and within the time frames specified therein. DONE and ENTERED this 21st day of December, 1994, in Tallahassee, Florida. WILLIAM R. CAVE Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 21st day of December, 1994. APPENDIX TO RECOMMENDED ORDER, CASE NOS. 93-2020 AND 93-6637 The following constitutes my specific rulings, pursuant to Section 120.59(2), Florida Statutes, on all of the proposed findings of fact submitted by the parties in this case. Petitioner's Proposed Findings of Fact; 1. Petitioner's proposed findings of fact 1 through 74 are adopted in substance as modified in Findings of Fact 1 through 50; otherwise they are not supported by the evidence in the record, or are unnecessary or subordinate, or are neither material nor relevant. Respondent Meeks' Proposed Findings of Fact: Respondent Meeks' proposed findings of fact 1 through 14, and 16 through 19 are adopted in substance as modified in Findings of Fact 1 through 50; otherwise they are not supported by the evidence in the record, or are unnecessary or subordinate, or are neither material nor relevant. Respondent Meeks' proposed finding of fact 16 is not supported by the evidence in the record. Respondent Meeks' proposed findings of fact 20 and 21 are not supported by the evidence in the record, but see Findings of Fact 43, 44 and 45. Respondent Butler's Proposed Findings of Fact: Respondent Butler did not file any proposed findings of fact. COPIES FURNISHED: Heidi Davis, Esquire Peter Fodor, Esquire Department of Environmental Protection 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Michael S. Drews, Esquire Richard E. Nelson, Esquire 2070 Ringling Boulevard Sarasota, Florida 34237 Stanley M. Butler, Pro se c/o Economy Tire Service 1858 Main Street Sarasota, Florida 34236 Kenneth Plante, General Counsel Department of Environmental Protection 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Virginia B. Wetherell, Secretary Department of Environmental Protection 2600 Blair Stone Road Tallahassee, Florida 32399-2400
The Issue The issue is whether the application of Petroleum Products Corporation for reimbursement of the cost of assessment and clean-up of soil and groundwater contamination at its site in Broward County, Florida, under the State Underground Petroleum Environmental Response Act of 1986 should be granted.
Findings Of Fact The Legislature provided a system for the clean-up of sites contaminated as the result of the storage of petroleum or petroleum products in the State Underground Petroleum Environmental Response Act of 1986 (Super Act), Chapter 86-159, Laws of Florida, codified primarily as Section 376.3071, Florida Statutes. The Super Act contains a reimbursement program funded by the Inland Protection Trust Fund. Section 376.3071(12), Florida Statutes, permits reimbursement of allowable costs for the rehabilitation of sites contaminated from discharges related to the storage of petroleum or petroleum products. Petroleum Products Corporation owns a parcel of land located at 3130 Southwest 17th Street, Pembroke Park, Florida. From 1959 to 1970 Petroleum Products Corporation operated a facility on that land which collected used oil from service stations and automobile dealerships, processed it, and sold it either as fuel oil or lubricating oil. About 90% of 150,000 gallons of used oil processed monthly at the facility was sold as fuel; the remaining oil was sold as lubricating oil, but even when sold as lubricating oil, it was sometimes burned as fuel because re-refined oil makes good fuel. The storage tanks were located on the southeastern portion of the property, near Carolina Road. The facility used a two-phase distillation process. Used oil was distilled to remove water, after which it could be sold as fuel oil. If processed in the second phase, for sale as lubricating oil, it was distilled further, and treated with sulfuric acid and clay to remove additives and residue, and change color. This phase produced a waste consisting of acid/clay sludge. This sludge is generally very black, and has a pH of approximately 3. It is very viscous, and has the consistency of roofing cement; laymen would describe it as tar. It does not flow easily, but is liquid enough to be pumped. This processing also occurred in the southeast part of the property. While the recycling facility produced lubricating oil using the acid/clay treatment from 1959 to 1970, the acid sludge was hauled to a municipal dump, or placed in pits dug into the ground on the north and east of the plant site. When the pits were dug, they were dug below the water level, and there was water in the pits before the sludge was dumped in them. The disposal of sludge in pits on the recycling site was a prevailing industry practice, and violated no regulatory requirements at the time. Operators considered on-site disposal of sludge preferable to hauling sludge to a landfill. During periods of heavy rain, some of the sludge may have overflown the pits and spread to nearby land, where it would become mixed with the surface soil. Petroleum Products Corporation ceased making lubricating oil in 1970, but continued to process used oil into fuel oil. The local Broward County Pollution Control Agency asked Petroleum Products Corporation to remove the acid/clay sludge from its property, and to refill the pits with other fill material. Petroleum Products Corporation acceeded to this request, and a great volume of sludge, perhaps hundreds of thousands of gallons, was removed from the pits, which were then refilled under the supervision of the Broward County Pollution Authority. Receipts Petroleum Products Corporation produced at the hearing, or thereafter from the custody of the U. S. Environmental Protection Agency, show that more than 150 truck loads of sludge were removed and hauled to landfills operated by Metropolitan Dade County or by the City of Surfside. Some pockets of the sludge remain at the site of the pits because they were not completely emptied. The backfill was clean fill, and the area was then bulldozed so that warehouses could be constructed in the area. This filling and bulldozing changed the contour of the land from what it had been in the past. The Department contends that much of the sludge was spread out over an extended area of the site, and not removed to landfills. The evidence is persuasive that almost all of the sludge from the pits was removed to landfills. The testimony of Mr. Blair denying that the sludge was spread was credible. In addition, on-site spreading of the sludge would have been impracticable. As a tar-like substance, if spread out, it would have been tracked everywhere. It would stick to the tracks or wheels of any vehicles operating on the surface, and was so acidic it would burn or irritate the skin of anyone who came in contact with it. It would be extremely difficult to perform maintenance on equipment used to spread the sludge because of the need to clean the sludge off, so that the mechanic would not be burned. In addition, there are a large number of receipts evidencing the systematic hauling of the sludge to landfills. The logic of Mr. McDonnell's testimony is persuasive: If you have the alternate, which they obviously did, of hauling it away and simply dumping it, no one would go out and deliberately choose to do a very difficult job [spreading the sludge over the property] where there is an easy alternative available to them. (Tr. 285) Although the facility ceased its re-refining of lubricating oil in 1970, it continued to collect, process, and sell used oil as a fuel until 1984. About 150,000 gallons per month of used oil were processed and sold as fuel. The oil was typically crank case engine oil which contained the substances normally found in used oil of that type. There is no persuasive evidence that Petroleum Product Corporation ever received any hazardous waste, or mixed used oil with any hazardous waste. Used oil is not listed as a hazardous waste by the U.S. Environmental Protection Agency or by the Department. The used oil collected and recycled at Petroleum Product's facility was pumped into and stored in above-ground storage tanks. There were, over time, from 10 to 25 tanks, which ranged in size from 12,000 to 20,000 gallons. Normally, the facility stored between 400,000 and 500,000 gallons of used oil. Occasionally, the facility also received virgin oil, but it was processed quickly or sold because of its higher value. At the peak of its operation, the facility had 25 to 35 storage tanks. Recycling operations had slim profit margins and were small operations. Storage tanks, pumps, and other equipment were bought used, often from other businesses dealing in virgin petroleum products. That used equipment was often rusty or deteriorating. Tank bottoms could have holes in them as the result of rust from standing water; tanks were sometimes riveted, and would have side or bottom leaks. The tanks had virtually no overfill protection. When oil was pumped in, it would overflow from the top and run down the sides. Operators were typically not careful with the oil, because it had a very low value, about 2 to 5 cents a gallon. A spill of a few thousand gallons was regarded as an inconsequential matter. The pumps used in storing oil often had leaks in packing seals, or had screw joints which would leak. Tank valves, also usually bought as used equipment, were often installed without new stem packing, and also would leak during operation. Almost no preventive maintenance was done, because it was not cost-effective to do so. Equipment was repaired only if its current state of repair interfered with operations, which usually meant that leaks were not repaired until they created a fire hazard. Leaks and spills from used oil storage tanks, including their pumps, valves, and piping, were common. A great volume of used oil leaked or spilled from Petroleum Products Corporation's tanks, pumps, and piping over its 25 year operation. There were also large oil spills resulting from four or five major fires at the facility in the 1960s. The fire in 1963, which may have been the result of vandalism, caused 40,000 to 60,000 gallons of use oil to spill from storage tanks; 8 or 10 tanks were destroyed. There were no dikes, so that the oil flowed freely. When firemen used water on the fire, the oil was absorbed into the soil. Another major fire occurred in October, 1966 in which three oil storage tanks collapsed spilling about 50,000 gallons of oil. Another 25 foot high oil tank collapsed on a firetruck. There is no way to know, with certainty, the volume of used oil, virgin oil, and lubricating oil which spilled or leaked into the ground on the site. It is reasonable to believe that 9 to 12 gallons of oil would have leaked or spilled each day at the facility, which would have resulted in spill of over 100,000 gallons of oil. This estimate, made by Mr. McDonnell, is credible and is conservative, given the volume of oil also spilled during the fires. Petroleum Products Corporation does not contend that the leaks and spills from process tanks, rather than from storage tanks, are eligible for reimbursement of site assessment and cleanup costs. Oil leaked from both, however, and once in the ground, the oils are indistinguishable. Due to the capacity of the tanks and the years they were in use, however, it is reasonable to assume that 15% or less of the leaks and spills were attributable to process tanks. After processing, most of the oil was burned as fuel. Some was used as a lubricant. The only difference between used oil sold as fuel or lubricant was that the lubricating oil had the additives removed and the color changed. Both burn well. There is an insufficient basis in this record to justify the Department's interpretation excluding this site from eligibility for cleanup because oil processing ocurred at the site to produce lubricating oil. Section 376.3071 does not disqualify all or part of a site from eligibility for cleanup reimbursement because a portion of the used oil stored there was ultimately used as lubricants. In 1984 a Department investigator asked Petroleum Products Corporation to install exploratory wells to determine whether there was contamination at the site. Petroleum Products engaged the firm of Dames & Moore to undertake a preliminary investigation, which revealed that there was groundwater contamination in the form of floating hydrocarbons. On April 1, 1985, the United States Environmental Protection Agency and Petroleum Products Corporation entered into a consent order agreement which required the removal of 17 above-ground tanks leaking used oil into the ground, which constituted a continuing source of contamination. Petroleum Products Corporation contracted with Conversion Technology Corporation to recover and recycle the oil and wastes, with Waldron's tank cleaning services to clean the empty tanks and drum the sludge, with Cuyahoga Wrecking Service to make the tanks inoperable, and with Seven & Seven Transporters to remove the waste to a disposal facility. The employee of the U.S. Environmental Protection Agency who was in charge of the site commended Petroleum Products Corporation for its cleanup effort, and wrote as the OSC [on- scene coordinator] for this EPA-monitored cleanup I may say that [Petroleum Products Corporation] exemplified industrial cooperation and responsibility in combating the vexing problem of hazardous waste management. (Petitioner's Exhibit 9) Petroleum Products Corporation cooperated with the Environmental Protection Agency and with the Department in determining how to deal with the contamination. It has already spent approximately $150,000 to perform remedial action. Contamination at the site is of three types: oil floating in the groundwater, soil contamination, and groundwater contamination. It is not possible to clean any individual phase of the contamination without affecting the other phases. Attempts at remediation must be monitored to prevent an influx of organic contaminants into the aquifer. Similarly, the cost related to the cleanup of an individual phase of contamination cannot be isolated because of the inter-related nature of the cleanup phases. The creation of a cone of groundwater depression is necessary for any recovery of the free or floating oil. The cost of recovery of the free product cannot be separated from groundwater cleanup because it is necessary to treat large quantities of groundwater involved in creating a cone of depression. To the extent that a proportion of the cost might be estimated, the cost associated with the recovery of free product would be a minor portion of the overall cleanup. There is currently a free product recovery effort in place at the site, which is intended to prevent further migration of the product off-site. This ongoing action is not considered an element of the site cleanup. The most feasible method of cleanup for the free product will involve the excavation of the soils to create a trench. The free product and ground water will be recovered as they flow into the trench. During October and November of 1984, Environmental Science and Engineering, Inc., a consulting firm working under contract with the Department, assessed the extent of free floating oil in the groundwater under the Petroleum Product Corporation's site. Those consultants found a free floating layer of oil from 5" to 30" thick under approximately one-half of the one acre site Petitioner still owns. The free product generally mirrors the location of the former recycling facility and its storage tanks. The viscosity of the free product is comparable to about 40-weight engine oil. Environmental Science and Engineering estimates that the floating layer of oil contains 20,000 to 60,000 gallons of recoverable petroleum product. The direction of ground water flow and the migration of contaminants off-site is to the east or southeast. The soil above the oil layer has been saturated with oil because of the fluctuations of the layer with movement of the water table as the area experiences heavy rains or dry spells. Wells drilled in the location of the former sludge lagoons to the north and east of the plant site reveal a heavy slightly liquid type of sludge. The oil in the lagoon sites is immobile, and no free product collects in the wells after 24 hours. One sample collected in the mason jar shows a slight degree of oil separation after 24 hours. This anecdotal evidence of separation is not very informative, and is not persuasive that oil separates from the remaining sludge on-site. See, Finding 32, below. A second assessment of soil and groundwater contamination was done by another consulting firm under contract with the Department, Ecology and Environment, Inc. That study showed free floating product at the site. The only calculation of the amount of free floating oil was that done by Environmental Science and Engineering, Inc., see, Finding 29, estimating that there would be 20,000 to 60,000 gallons of recoverable oil. That calculation understates the amount of oil in the ground. The estimate given by George McDonnell of 103,000 gallons is more persuasive. It is consistent that the large amounts of oil which leaked or spilled at the site over a 25 year period. It is unlikely that any appreciable portion of the approximately 103,000 gallons of floating oil has its genesis in the separation of oil from the acid/clay sludge which had been disposed in the two lagoons for the following reasons: Oil associated with acid/sludge would be quite acidic, and have a pH between 2 and 4. The pH scale is not a linear scale, so differences in pH are quite dramatic as the pH values change. Samples of free product shows a uniform pH of approximately 6 or 7. In almost all 31 monitoring or observation wells the pH is consistent with the characteristics of used oil, (a pH of 6 or 7), not the pH of sludge (a pH of 2 to 4). The only sample which disclosed a low pH was that taken in monitoring well number 3 which was located in the former sludge lagoon site. The groundwater flows to the east or southeast. This does not explain the presence of free product to the west and southwest of the sludge pits nor the absence of free product to the east of the pits. The viscosity of the oil is similar to that of 40-weight engine oil and not highly viscous, as the tar-like sludge would be. The oil in the sludge pits is basically immobile and no free product surfaced in the monitoring well after waiting 24 hours. The pH of the free product is nearly neutral. The Department believes that the sludge was mixed with lime rock or fill and spread over the site to increase the pH of the oil. This is unpersuasive. Mixing with lime rock would increase the pH of the sludge (tend to bring it towards neutral) but it would not cause the dramatic lowering of acidity which would bring the sludge to a pH of 6 or 7. In addition, the viscosity of the sludge would not be so changed by mixing the sludge with fill that its viscosity would become similar to that of 40-weight engine oil. To believe that the free product results from sludge disposal rather than leaks ignores the normal operating practice of used oil recovery facilities in the late 50s and 60s where spills from storage tanks, pumps, and piping were very common. Little of the free product has been recovered through the current remediation efforts. If not recovered, over time the approximately 103,000 gallons of floating oil will spread to adjacent property. To recover this oil by conventional trench or well recovery operations will probably cost $250,000 or more. The capital cost of the groundwater recovery/discharge system, with monitoring wells, will be about $85,000; cost of operating and maintenance are approximately $180,000. The firm of Ecology & Environment, Inc., collected soil samples at 56 locations in two phases in its remedial investigation. Forty-six of the samples were taken at shallow depths (27 at 8 inches, 19 at approximately 10 inches); 10 more samples were taken in the old disposal pit sites at depths between 0 and 35 feet). The two primary classes of contaminants found in the soil were lead and organics (hydrocarbons associated with petroleum products). Both contaminants are found in used oil. The lead and organic contaminants were found in the shallow soils over the southern half of the site. Very little contamination was found beyond the main area of site activity. The soil contamination was concentrated in the plant and former disposal pit areas. Samples with high lead concentrations were found in the former disposal pit sites. Contamination extended to a depth of 25 feet in one soil sample from a former pit, where oily plastic sludge was found with fine sand or clay. The two former pit sites are the only places with documented contamination below a 10 foot depth. Although the organic contamination extended laterally further than the lead contamination, Environment & Ecology concluded that the wider distribution did not reflect contamination from Petroleum Product Corporation's activities. The general area has long been the site of commercial and industrial activities, and there are many other possible sources for contamination including a firing range, which would have been disposing of lead bullets fired at the range, a generator plant, and a former spray-painting facility. Solvents and other chemicals used in these activities would contribute to soil and groundwater contamination. The consultants had been told by area businesses that small scale dumping of industrial chemicals in the vicinity has been common. Soil samples revealed a "great deal of heterogeneity." There was no uniform distribution of soils in the shallow zone. This probably occurs because after the reprocessing operations ended in 1970, the land was cleared and filled, so that many of the warehouses now in the area could be constructed. Most of the upper 8 to 10 feet is fill material. The ground water was monitored by installing 38 wells on the site, most of which were screened at depths of 10 to 12 feet. Five intermediate wells with depths of 50 feet and two deep wells of 100 to 200 feet were also installed. Every sample exhibited a pH of between 6.4 and 7.4. The primary contaminants were lead, organics, and chromium. The evidence does not indicate the source of the chromium. It is unrelated to Petroleum Product Corporation's activities. The groundwater contamination, both metal and organic, was only in the shallow zone. It extends laterally roughly to the same extent of the shallow contamination found in the soil. This suggests that the contaminants in the soil migrated due to seepage from rainfall or fluctuation in the water table into the groundwater. The water table is about five feet below the land surface. The Department has argued that the contaminants in the soil and groundwater were caused by mixing and spreading of the sludge material during the early 1970s over the surface of the area. This hypothesis has already been rejected for the reason stated in Findings 7 and 8, above. It is more likely that the soil contamination resulted from frequent spills and leaks of oil from storage tanks years ago. The soil contaminants are those found in used oil. The area generally is flat. There was no impediment to oil spills flowing over a large surface area, following the contour of the land at that time. Depending on the method used to clean up the site, the cost of rehabilitating the area will range between two and forty-six million dollars. It will cost over one million dollars to recover and treat contaminated groundwater. Approximately 110,000 cubic yards of contaminated soil must be removed and treated, the majority of that coming from the area outside the former sludge pits. The presence of contamination at the site is to be expected, given the site's former use. All of the 8 turnpike facilities and 8 maintenance yards operated by the Florida Department of Transportation report petroleum contamination from tanks, and the Department of Transportation has estimated cleanup cost will range from $20 to $30 million, although DER believes the cost may be $5 million. The cleanup will be funded by the Inland Protection Trust Fund, as would the reimbursement in this case. The cost of rehabilitation is in the range of estimates that the Department has received for other petroleum contamination sites. In summary, the Petitioner's site is contaminated primarily from leak and spills of used and virgin oils processed or unprocessed and from storage tanks, pumps and integral piping. Small spills were continuous and some associated with fires were massive. The only portion of the site not contaminated due to leaks and spills is the residual soil and groundwater contamination from the sludge disposal pits, which is a small part of the overall contamination.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the application of Petroleum Products Corporation fo eligibility to participate in the cleanup program funded by the Inland Protection Trust Fund be granted. DONE and ENTERED this 9th day of July, 1990, at Tallahassee, Florida. WILLIAM R. DORSEY, JR. Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 9th day of July, 1990. APPENDIX Rulings on Findings of Fact proposed the Petitioner: As will be obvious, the proposed order submitted by Petroleum Products Corporation comported closely with the Hearing Officer's view of the evidence, and with some modification was essentially adopted as proposed. Adopted in Finding of Fact 3. Adopted in Finding of Fact 3. Adopted in Finding of Fact 4. Adopted in Finding of Fact 4. Adopted in Finding of Fact 5. Adopted in Finding of Fact 6. Adopted in Finding of Fact 6. Adopted in Findings of Fact 7 and 8. Adopted in Finding of Fact 8. Adopted in Findings of Fact 9 and 10. Adopted in Finding of Fact 10, to the extent necessary. Adopted in Finding of Fact 11. Adopted in Finding of Fact 12. Adopted in Finding of Fact 13. Adopted in Finding of Fact 14. Adopted in Finding of Fact 15. Generally adopted in Finding of Fact 16. Rejected as subordinate. Rejected as unnecessary and subordinate. Adopted in Finding of Fact 17. Adopted in Finding of Fact 18. Adopted in Finding of Fact 19. Adopted in Finding of Fact 20. Generally adopted in Finding of Fact 21. Adopted in Finding of Fact 22. Adopted in Finding of Fact 23. Adopted in Finding of Fact 24. Adopted in Finding of Fact 24. Adopted in Finding of Fact 24. Adopted in Finding of Fact 28. Adopted in Finding of Fact 29. Adopted in Finding of Fact 30. Adopted in Finding of Fact 31. Adopted in Findings of Fact 31 and 32. Adopted in Finding of Fact 33 Rejected as repetitious of Finding of Fact 6. Rejected, see Findings of Fact 25 and 26. Adopted in Finding of Fact 24. Adopted in Finding of Fact 34. Adopted in Finding of Fact 35. Adopted in Finding of Fact 36. Adopted in Finding of Fact 37. Adopted in Finding of Fact 38. Adopted in Finding of Fact 39. Adopted in Finding of Fact 40. Adopted in Finding of Fact 41. The spreading theory is rejected in Findings of Fact 7 and 8. Rejected as unnecessary. Adopted in Finding of Fact 42. Adopted in Finding of Fact 42. See also the stipulation of the parties entered as Exhibit 22. Rejected as unnecessary. Rulings on Findings of Fact proposed by the Department. Adopted in Finding of Fact 1. Adopted as modified in Finding of Fact 2. Discussed in the Conclusions of Law, see page 20. Adopted in Finding of Fact 3. Adopted in Finding of Fact 3. Implicit in Findings of Fact 3 and 6. Adopted in Finding of Fact 6. Adopted in Finding of Fact 5. Adopted in Finding of Fact 4. Adopted in Finding of Fact 4. Rejected as unsupported by the transcript references given. Adopted in Finding of Fact 5. Adopted in Finding of Fact 5. Adopted in Finding of Fact 5 Rejected as unnecessary. Generally rejected; see Finding of Fact 6 concerning the filling of the disposal pits. While some pockets of sludge remain at the site of the pits, the volume is difficult to determine. In an absolute sense, those pockets may contain a substantial amount of sludge, but on a comparative basis, by far the greatest part of the sludge was removed. Rejected as unnecessary. Generally adopted in Finding of Fact 32(1), but see the final sentence of (1). Generally adopted in Findings of Fact 25, 28, and 34. Generally adopted in Finding of Fact 28, since the recycling facility and storage tanks were on the southern part of the property. Rejected as unnecessary. Adopted in Finding of Fact 26. Adopted in Finding of Fact 26. Adopted in Finding of Fact 3. Implicit in Finding of Fact 11. Adopted in Finding of Fact 11. Adopted in Finding of Fact 4. Rejected because the process tanks necessarily store the product being processed, serving as a vessel to contain the product. Rejected, see Finding of Fact 3 with respect to the turnover in the volume of used oil processed at the facility. Only about 10 percent of the oil was reprocessed as lubricating oil. This is more significant than the volume of the tanks. See also Tr. 24 with respect to the storage capacity, and Finding of Fact 11. Rejected as unnecessary. Rejected because the surficial drainage has probably been changed by the filling and regrading of the property in preparation for building the warehouses. See Finding of Fact 6. The current surficial flow says little about the flow when the facility operated in the late 1950's and throughout the 1960's. Adopted in Findings of Fact 15 through 19. Adopted in Findings of Fact 17 and 18. Adopted in Finding of Fact 17. Generally rejected, the evidence is persuasive that about 50,000 gallons of oil were lost in the 1966 fire. (See Tr. 36-37.) Adopted in Finding of Fact 25. Adopted in Finding of Fact 26. Adopted in Finding of Fact 26. Adopted in Finding of Fact 26. Adopted in Finding of Fact 27. Adopted in Finding of Fact 27. Rejected as unnecessary. Adopted in Finding of Fact 27. Adopted in Finding of Fact 27. Adopted in Finding of Fact 27. Adopted in Finding of Fact 27. Adopted in Finding of Fact 27. Rejected, the free product covers approximately one-half acre. Rejected, the more persuasive evidence is the 103,000 gallons estimated by Mr. McDonnell. See Finding of Fact 31. Rejected as unnecessary. Rejected as unnecessary. See Findings of Fact 28 and 34. Rejected because it is unlikely that sludges are separating in the former sludge lagoon. See Finding of Fact 30. The source of the oil is more likely the substantial loss of oil which occurred from the fires and from leaks over the years which is now floating above the ground water. Generally adopted in Finding of Fact 28. Generally adopted in Finding of Fact 28. Rejected as unpersuasive. Rejected, the source of the free product is not leaching from the disposal pit, but the oil from over flows and leaks during operation as well as large inundations during fires. Adopted in Finding of Fact 4. Adopted in Finding of Fact 4. Adopted in Finding of Fact 4. Rejected, see Finding of Fact 30. Rejected because oil does not separate from the sludge. Rejected for the reason given for rejecting Finding of Fact 63. Rejected, the seepage is not the result of separation in the disposal pits, but from the plume of free product in the ground above the ground water. Rejected as unnecessary, but the similarity of the oil seeping from the sludge pit area to waste oil is consistent with its source as leaks and spills inicident to fires. Rejected because the sludge does not separate. Rejected because the sludge does not separate. Rejected because the sludge does not separate, see Finding of Fact 30. Rejected as unnecessary; obviously as there is no more storage, so there is no more source for leaks or spills. 71-73. Discussed in Finding of Fact 30. Rejected because liquid product will not accumulate. Rejected because the sludge does not separate. Adopted in Finding of Fact 32(1). Adopted in Finding of Fact 32(5). Adopted in Finding of Fact 32(1). Rejected for the reason stated in Finding of Fact 32(5). Rejected for the reason stated in Finding of Fact 32(5). Rejected as unnecessary and for the reason stated in Finding of Fact 32(5). Adopted in Finding of Fact 32(1), which is consistent with the source of the free product being used oil rather than separation from sludge remaining onsite. 83-84. Rejected as unnecessary. Rejected as unnecessary. Rejected because the testimony of Mr. McDonnell has been accepted. Rejected as unnecessary. Adopted in Finding of Fact 27. Rejected as redundant. Adopted in Finding of Fact 34. Adopted in Finding of Fact 34. Implicit in the finding that lead is a contaminant found in used oil. See Finding of Fact 34. Adopted in Finding of Fact 4. Rejected as unnecessary. Generally adopted in Finding of Fact 34. Generally adopted in Finding of Fact 34. Adopted in Finding of Fact 35. Rejected as unnecessary. Rejected as unnecessary; see also, Finding of Fact 6. Adopted in Finding of Fact 32(1). Rejected as unnecessary. Rejected as unnecessary. Rejected as unnecessary, although there were disposal pits in the north and eastern parts of the property. Adopted in Finding of Fact 34 with respect to location, but the testimony with respect to spreading of the sludge is rejected. See Finding of Fact 7. It is unlikely that sludge was spread over the site. The more likely explanation for the appearance of sludge in the lithologic logs for the southern end of the site is that the disposal lagoons periodically overflowed after heavy rains and provided a mechanism for the active transport of sludge out of the disposal pits into some areas on the southern end of the site. Apparently the northern area now occupied by the warehouses was higher, because no sludge was found in observation wells 4, 5 and 19. Rejected, page 41 of DER's Exhibit 3 shows no sludge at observation well 5, which the proposed finding implies. 107-112. Generally rejected because the testimony with respect to the surface flow from the tank area being to the south is rejected because the grading of the property as the warehouses were built likely changed the contour of the land. Mr. Levin's testimony was not particularly strong; for example, at page 25 of his prefiled direct testimony he states, "And for the shallow soil contamination I would still have to lean towards the fact that the materials were mixed and spread." 113-114. The sludge contamination is not the predominant or source of contamination. Rather, it is the oils which floated across the land and were carried into the soil and resulted from the leaks and spills. 115-120. Generally accepted in Finding of Fact 36, although subordinate to that finding. 121. Generally accepted, although the soil contamination by lead is attributable to leaks and spills from the used oil. 122-124. Rejected as unnecessary. Accepted in Finding of Fact 25. Accepted in Finding of Fact 38. 127-128. Subordinate to Findings of Fact 36, especially the last sentence, and 38. Subordinate to Finding of Fact 39. Subordinate to Finding of Fact 39, especially the last sentence. Rejected as unnecessary. 132-134. Accepted in Finding of Fact 39. 135. Rejected because the soil contamination is the result of leaks and spills of oil. 136-137. Rejected, it is more likely that the neutral pH of the ground water is the result of the essentially neutral contaminant, the used oil. Rejected as unnecessary. Rejected as unnecessary, although consistent with Finding of Fact 39 that the lateral extent of ground water contamination mirrors the soil contamination which has resulted from leaks and spills. 140-141. The predominant source of contamination is leaks and spills. 142. Rejected, the area affected by the leaks and spills is large, due especially to the fires and consequent loss of large amounts of oil from tanks. See Finding of Fact 41. 143-144. Rejected as irrelevant and unnecessary. 145. Although true, not relevant. 146-148. Rejected, whether the Environmental Protection Agency is correct or not in its assessment is not at issue here. This site was contaminated by used oil. 149-150. Although true, not relevant. Implicitly accepted in that no finding with respect to "bias" has been made. Rejected as legal argument. Rejected because the predominate source of contamination is an eligible source. Rejected, but the source here falls within the statutory directive. Rejected. The site here is predominantly contaminated by used oil, which is eligible. The eligible portion is not a minor part of the entire of the contamination. COPIES FURNISHED: R. L. Caleen, Jr., Esquire OERTEL, HOFFMAN, FERNANDEZ & COLE Post Office Box 6507 Tallahassee, Florida 32314-6507 Gary Early, Esquire Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Dale H. Twachtmann, Secretary Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Daniel H. Thompson, General Counsel Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 =================================================================
