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 At issue in this proceeding is the reasonable cost to be reimbursed Petitioner, under the provisions of Section 376.3071(12), Florida Statutes, for the development of a Monitoring Only Plan (MOP) program for the Dagam Oil Company (DEP Facility No. 138504146), at 331 23rd Street, Miami Beach, Florida.
Findings Of Fact Background Petitioner, Panhandle Industries, Inc., is a Florida corporation engaged in the business of consulting, engineering and construction. George M. Hidle, a professional geologist licensed in the State of Florida, is the president and sole owner of the Petitioner corporation. In September 1992, Dagam Oil Company, doing business as Sierra Fina, employed Petitioner to do environmental assessment work and prepare a Contamination Assessment Report (CAR) under the then existing Rule 17-770.630, Florida Administrative Code, for a site located at 331 23rd Street, Miami Beach, Florida (DEP Facility No. 138504146).4 That CAR was submitted to DERM (Metropolitan Dade County, Department of Environmental Resources Management) July 13, 1993. (Petitioner's Exhibit 1.) Pertinent to this case, the CAR provides the following background or historical information: . . . PHYSICAL SETTING . . . Sierra Fina is located at 331 23rd Street in Miami Beach, Florida . . . The facility is bordered to the north by Collins Canal, to the east by the light commercial properties, and to the south/southeast by property that once contained Chevron and Fina service stations. . . . * * * . . . FACILITY HISTORY AND OPERATION Sierra Fina was built in 1963. The station originally operated as a Sunoco service station with a 3 bay garage. Dagam Oil Company purchased the facility in March 1981 from Charles Rosenblatt. At the time the station had five underground fuel tanks. . . . * * * . . . PREVIOUS INVESTIGATIONS Dagam Oil Company contracted with another environmental company in November 1988 to collect groundwater samples from . . . five monitoring wells at the facility. Groundwater samples were collected on November 9, 1988 and analyzed by EPA Method 602. Monitoring well MW-3 was also analyzed by EPA Method 610. All five of the wells had hydrocarbon contaminant concentrations in excess of state guidelines. . . . A discharge notification form was mailed to the DER and DERM on December 9, 1988, the date of receipt of the analytical results from the November 9, 1988 groundwater sampling event. . . . * * * . . . INITIAL REMEDIAL ACTIONS [IRA] [The F]ive underground storage tanks [and associated piping] were removed from the facility during March and April 1989 [, and replaced with four new cathodically protected underground petroleum storage tanks]. Approximately 400 cubic yards of contaminated soil was also removed at that time. On March 31, 1989 a composite sample of the soil was collected for analysis . . . Because of limited space at the station, the contaminated soil was hauled to a Metro Trucking Inc. storage yard located at 112th Avenue and 143 Street in Miami. The contaminated soil was landfarmed at this Metro Trucking facility for a period of seven months, during which time the soil was spread onto visqueen and tilled on a regular basis. On November 21, 1989 the soil was resampled and analyzed . . . Results of this second round of analyses met clean fill criteria. Also at the time of tank replacement, a sheen of free floating hydrocarbons was observed on water in the tank pit. A vac truck was used to skim this product from the pit prior to tank replacement. Approximately 2100 gallons of oily water were removed, transported, and disposed of by Cliff Berry, Inc. . . . Other than these IRA activities, no other assessment or remediation work had been performed at the facility until Petitioner was employed in September 1992. Petitioner's CAR concluded that: Soil and groundwater at Sierra Fina are contaminated with gasoline and diesel hydrocarbons. Excessively contaminated soil is confined to an area at the western end of the station building that is approximately 20 feet in width by 30 feet in length, extending down to a water table of between 6 and 8 feet below land surface. No free phase floating product is present on the groundwater underlying this facility. However, dissolved hydrocarbon contamination is present in the groundwater. A dissolved hydrocarbon plume is present in the western half of the site. This plume measures 80 feet in length by 60 feet in width and extends to a depth of less than 22 feet below land surface, yielding approximately 134,640 gallons of hydrocarbon contaminated water. Volume calculations are based on an average depth to groundwater of 7 feet below land surface and an effective soil porosity of 25%. The highest benzene (53.3 ppb) and total napthalenes (752 ppb) concentrations were detected in MW-12. * * * Groundwater within the Biscayne Aquifer beneath Sierra Fina is nonpotable because of salt water intrusion from the Atlantic Ocean. For this reason there are no private or public potable wells in the area. Contamination at Sierra Fina is limited onsite to the western half of the station, and poses no threats to sensitive receptors in the area, with the possible exception of Collins Canal. The cause of hydrocarbon contamination was never determined; however, the most probable source, i.e. previous petroleum tanks and lines, were removed in March and April of 1989. Based on these findings and the data presented about or elsewhere in this report, it is known that soil and groundwater contamination does exist at this facility in concentrations that exceed guidelines specified in Section 17- 770.730(5)FAC; however, the levels of contamination may not warrant the need for any extensive remediation activities at this site. Petitioner's CAR was approved by DERM on October 8, 1993, and Petitioner was directed to submit a Remedial Action Plan (RAP) within 60 days.5 At the time, Mr. Hidle (Petitioner) was aware that the levels of contamination were low or near target levels, and that it was likely that the contamination levels would decrease naturally over time. Consequently, Petitioner elected to seek approval of a Monitor Only Plan (MOP), as opposed to a RAP. Such choice was favored based on the nature and location of the contaminants. In this regard, it was observed that the soil contamination consisted of both gasoline and diesel fuel, with much of the contaminated soil abutting or underneath the building. Excavation and removal of the soil was not an alternative because it would undermine the structural integrity of the building. Moreover, given the fuel mix, vapor extraction was not a viable option. Given Petitioner's choice to pursue approval of a MOP, it gave notice to the Department and DERM on October 18, 1993, as well as November 12, 1993, and December 2, 1993, of its intention to undertake groundwater sampling and soil sampling on the site. Groundwater sampling was undertaken by Mr. Hidle between 1:30 p.m., November 30, 1993, and 2:30 a.m., December 1, 1993,6 at which time he drew water samples for laboratory analysis from 10 monitor wells (MW) and one deep well (DW). A duplicate sample was also retrieved at MWs 12R and 14, and equipment blanks were also obtained for laboratory analysis. Between 8:25 p.m., December 4, 1993, and 3:40 a.m. December 5, 1993,7 Mr. Hidle and a senior technician (Martin Hidle) augured 6 soil borings for use in preparing the MOP and collected one soil sample for laboratory analysis. Petitioner delivered the water samples to the laboratory (Envirodyne, Inc.) on December 2, 1993, and the soil sample on December 6, 1993, for analysis. The laboratory completed its analysis of the water samples on December 13, 1993, and of the soil sample on December 14, 1993, and rendered its written reports (analysis) to Petitioner.8 Upon receipt of the laboratory data, Mr. Hidle completed his preparation of the MOP. (Petitioner's Exhibit 4.) That MOP contained the following conclusions and recommendations: The initial dissolved hydrocarbon plume dimensions were based on data from groundwater sampling events of January and February 1993. Laboratory results from a more recent sampling event (11/30/93) indicate that plume size and hydrocarbon compound concentrations therein have decreased substantially (Table 4-2). Maximum groundwater contaminant concentrations decreased as follows: benzene from 53.3 ppb to 11.1 ppb; BTEX from 111.7 ppb to 20.6 ppb; total naphthalenes from 752 ppb to 246.1 ppb. During the contamination assessment program task a small area of contaminated soil was found to be abutting the western end of the station building (CAR, Fig. 3-1, p. 35). Because of the presence of diesel compounds in the groundwater, it was assumed during preparation of the CAR that the soil too was contaminated with diesel. In early December 1993 PI Environmental personnel installed six additional soil borings (Figure 3-1, SB-16 through SB-21) and collected one soil sample for laboratory analyses. The soil borings were augered in the immediate area of the previously defined contaminated soil plume, and soil samples were analyzed in the field by using a Foxboro OVA 128. Soil samples were collected vertically every two feet, beginning at one foot below ground surface and continuing until the water table was encountered. A soil sample was collected from boring SB-17 at a depth of six feet below land surface. A net OVA reading of 160 ppm was observed from a duplicate sample taken from the same depth. The soil sample was tested by EPA Methods 3540/8100 (diesel compounds) and 9073 (TRPH). Laboratory results indicated that all diesel compounds were below laboratory detection limits, and the TRPH concentration was below normal background readings. Soil contamination was reclassified as being gasoline in origin, because no diesel compounds were detected in the soil sample from SB-17. Section 17-770.200(2) Florida Administrative Code defines excessively contaminated soil, associated with gasoline contamination, as those that have a net OVA/FID reading equal to or greater than 500 ppm. From December 1993 sampling event, a maximum net OVA/FID reading of 316 ppm was obtained from a sample that was collected at five fee below land surface in SB-17. Based on these results, no excessively contaminated soil was found during the most recent sampling event. It is the recommendation of PI Environmental Inc. that a Monitoring Only Plan be implemented at Sierra Fina. This recommendation is based on the following findings: 1) Absence in the study area of any potable water wells within the Biscayne Aquifer because of salt water intrusion from the Atlantic Ocean 2) Absence of free phase hydrocarbons 3) Absence of excessively contaminated soil 4) Substantial decrease in concentrations of dissolved hydrocarbon compounds within the groundwater during the last year, and 5) relatively low levels of hydrocarbon contamination in the groundwater, i.e., based on the November 30, 1993 sampling event, maximum benzene of 11.1 ppb, maximum BTEX of 20.6 ppb, and maximum total naphthalenes of 246.1 ppb. It is our recommendation that groundwater from monitoring wells MW-8, MW-12R, MW-6, and MW-17 be sampled on a quarterly basis. Groundwater from the source area wells, MW-8 and MW-12R, should be analyzed quarterly by EPA Methods 602 and 610. Groundwater from the perimeter wells, MW-6 and MW-17, should be analyzed quarterly by EPB Method 602 and semiannually by EPA Methods 602 and 610. Petitioner submitted the MOP to DERM on January 24, 1994. Pertinent to this case, it is observed that the MOP was a brief document, consisting of only 13 pages of textual material, much of which was a restatement of material contained in the CAR. The balance of the report consisted of 5 "Figures" (three of which were contained in the CAR and one of which is an updated version of a CAR Figure); 2 "Tables" (an update of the Water Table Elevation table contained in the CAR to include the November 30, 1993, data, and an update of the Summary of Groundwater Analyses contained in the CAR to include the November 30, 1993, and December 1, 1993, data); 6 "Geologic Log[s]" (a restating of the soil boring results noted in the field notes for December 4 and 5, 1993); copies of the laboratory (Envirodyne, Inc.'s) reports of groundwater analysis; and the laboratory's report on the soil analysis. In all, while apparently adequate and nicely presented, the MOP does not address a complex or unique issue, and does not evidence the expenditure, or need to expend, an inordinate amount of effort to produce. Petitioner's MOP was disapproved by DERM on May 11, 1994, for the following reasons: A complete round of groundwater analyses, no greater than six months old, is required. Therefore, all wells at this site must be sampled for EPA Method 418.1, and monitoring wells numbered MW-6, MW-9, MW-10, MW-11, MW-13, MW-16, and MW-17 must be sampled for EPA Method 610. Because diesel contamination is present at this site, soil OVA readings above 50 ppm are considered to indicate excessively contaminated soil. Based on this OVA readings obtained for your Contamination Assessment Report (CAR) and this MOP, excessively contaminated soil does exist at this site. Since this coil could be a continuing source of contamination, it must be removed prior to the approval of a MOP. Consequently, Petitioner was directed to submit an addendum to the MOP to address those issues. On June 1, 1994, Petitioner gave notice to the Department and DERM of its intent to collect groundwater samples to address issues raised by DERM's MOP review letter. These samples were collected by Mr. Hidle and a technician (Leo Iannone) between 1:15 p.m. and 10:00 p.m., June 15, 1994.9 Petitioner delivered the water samples to the laboratory (Envirodyne, Inc.) on June 16, 1994. The laboratory completed its analysis and delivered its written reports to Petitioner on or about June 23, 1994. Upon receipt of the laboratory data, Mr. Hidle completed the Monitoring Only Plan Addendum (Petitioner's Exhibit 8), and submitted it to DERM on July 5, 1994. The addendum addressed the additional groundwater analysis that was performed, and with regard to the diesel contamination it observed, as follows: Soil analytical results (MOP, Page 62) are below laboratory detection limits for EPA 610 compounds; however, because groundwater at this facility is contaminated with both gasoline and diesel, we are concurring with DERM by reclassifying excessively contaminated soil as any soil that exhibits net OVA/FID readings of 50 ppm or greater, per Chapter 17-770 FAC. OVA/FID soil analyses were performed in accordance to Panhandle Industries, Inc. approved Comp QAP. Net OVA/FID soil results obtained during the CAR program task are shown in Figure 1-5. A maximum net OVA/FID reading of 887 ppm was obtained during CAR soil assessment activities which ended on November 29, 1992. Figure 1-6 shows net OVA/FID results obtained during the MOP program task. These MOP analyses are current through December 5, 1993. A maximum net OVA/FID of 316 ppm was obtained during this latter event. As is shown in comparison of Figures 1-5 and 1-6, it can be seen that the size of the soil contaminant plume and OVA/FID net soil readings therein have decreased significantly since initiation of the CAR. Also, by observing Figure 1-6, which has a scale of 1" = 20', it is evident that very little soil, if any can be excavated without jeopardizing the structural integrity of the station building. Furthermore, there exist the possibility that some soil contamination may underlie the building itself; therefore, soil excavation would most likely result in only partial removal of the contaminated soil plume. The addendum concluded by recommending that the MOP be implemented as originally proposed, but with additional monitoring to assure a continuing decline in contamination. The addendum, like the MOP, was a brief document and contains only 6 pages of textual material. The balance of the addendum contains 6 "Figures" (all of which appeared in the CAR or MOP); 2 "Tables" (an update of the Water Table Elevations table contained in the MOP to include June 15, 1994, data, and an update of the Summary of Groundwater Analyses contained in the MOP to include the June 15, 1994, data); and the laboratory reports of groundwater analyses. As with the MOP, the addendum did not appear to address any complex or unique issues, and did not evidence the expenditure, or need to expend, an inordinate amount of time to produce. On August 16, 1994, and August 26, 1994, DERM and the Department, respectively, approved the "monitoring only" proposal. The request for reimbursement Petitioner submitted its reimbursement application on or about August 23, 1994, and it was apparently complete on or about April 18, 1996. (Petitioner's Exhibit 11). That application sought recovery of the following sums for the items noted: 6. REMEDIAL ACTION PLAN [MOP and MOP Addendum] PREPARATION . . . Personnel 31442.55 Capital Expense Items Rentals 1127.45 Mileage 68.05 Shipping 35.00 Well Drilling Permits Analysis 3680.00 Miscellaneous 1601.25 REMEDIAL ACTION PLAN PREPARATION TOTAL 37954.30 * * * 13. REIMBURSEMENT APPLICATION PREPARATION Supplementary Forms Personnel 795.00 Capital Expense Items Rentals 15.00 Mileage .80 Shipping 86.81 Well Drilling Permits Analysis Miscellaneous 60.75 APPLICATION PREPARATION TOTAL 958.36 CERTIFIED PUBLIC ACCOUNTANT REVIEW FEE 500.00 APPLICATION GRAND TOTAL 39412.66 By letter (Order of Determination of Reimbursement) of June 27, 1996, the Department responded to Petitioner's reimbursement request as follows: We have completed review of your Reimbursement Application for expenses incurred during the Remedial Action Plan/Monitoring Only Plan program task at this site and have determined that $13,198.70 of the total $39,412.66 requested is allowable for reimbursement. This amount will be paid to the person responsible for conducting site rehabilitation when processing is completed by the Comptroller's Office. Some adjustments to the amount of reimbursement requested have been made. The following list details these adjustments. Citations refer to the specific sections of the enclosed Reimbursement Application Summary Sheets: 1. $24,766.25 in Section 6A, $259.95 in Section 6C, $28.20 in Section 6D and $63.25 in Section 6I were deducted because the total personnel hours (413.15 hours) and the total cost of $39,412.66 claimed for performing a limited scope of work consisting of 78.34 hours of field activities, two rounds of analyses (59 samples) and two letter reports have been determined to be excessive. However, actual field activities (including a reasonable amount of preparation), two rounds of analyses and a reasonable amount of personnel time to prepare two letter reports have been allowed. 2. $162.50 in Section 6A, $9.00 in Section 6E and $331.15 in Section 6I were deducted for costs associated with providing backup for the Contamination Assessment reimbursement application. These costs are not reimbursable in this application which is for the Remedial Action Plan/Monitoring Only Plan program task. $184.80 in Section 6A and $394.56 in Section 6I were deducted for field supplies, ice, conducting database modifications and purchasing office supplies, which are considered to be overhead. These costs are not justified in addition to the loaded personnel rates which already include overhead and profit. $11.76 in Section 6I was deducted because the rate for reproduction ($0.99 per page) has been determined to be excessive. However, $0.15 (per page) has been allowed based on the predominant rate claimed in other reimbursement applications for similar rates. $19.56 in Section 13E was deducted for costs added to the application preparation claimed as a markup. Reimbursement for application preparation is limited to actual costs only. $17.02 was added to the application grand total to cover the cost of reproducing the reimbursement application and invoices and shipping the replacements to the Department. (Petitioner's Exhibit 12.) Petitioner filed a timely challenge to contest the Department's decision. That challenge disputed the Department's action, as set forth in paragraphs numbered 1 through 4 of the letter, but Petitioner did not then, or at hearing, dispute the Department's action with regard to the matters contained in paragraphs numbered 5 and 6 of the Department's letter. (Petitioner's Exhibit 13). Subsequently, at hearing, Petitioner withdrew its request for reimbursement regarding the items contained in paragraph 3 of the Department's letter. (Transcript, page 101). The claim for the cost of preparing the reimbursement application Petitioner's claim for the cost of preparation of the reimbursement application totalled $1,458.36 (including the certified public accountant review fee). The Department proposed to deduct $19.56 (in Section 13E), and to add $17.02 to cover certain costs, as noted in the Department's letter. (Petitioner's Exhibits 12 and 13). Petitioner offered no objection to the Department's decision and, therefore, Petitioner should be awarded $1,455.82, without the need for further discussion, as the cost of preparing the reimbursement application. The claim for the cost of preparation of the MOP and MOP Addendum Petitioner's application for reimbursement claimed 413.15 personnel hours ($31,442.55) were dedicated to the development of the MOP (329.42 hours/$25,500.95) and the MOP Addendum (83.73 hours/$5,941.60). (Respondent's Exhibit 7, and Transcript, pages 188-190). In its initial review, the Department approved 55.67 hours ($3,790.45) for the MOP and 41.92 hours ($2,538.55) for the MOP Addendum, for a total award of $6,329.00. Subsequently, the Department resolved to accept as reasonable, 89 hours ($6,308.00) for the MOP and 83.73 hours ($5,941.60) for the MOP Addendum, for a total award of $12,249.60 for personnel costs.10 The 83.73 hours ($5,941.60) agreed to by the Department for the MOP Addendum was the precise amount Petitioner requested in its reimbursement application; however, the 89 hours ($6,308.00) accepted by the Department for the MOP is clearly less than the 329.42 hours ($25,500.95) Petitioner had requested. With regard to the difference, the Department views the request as excessive. In contrast, Petitioner contends the time requested was reasonable. Here, the Department's view has merit. To support the reasonableness of the hours (labor) claimed, Petitioner pointed to the "Daily Time Log[s]" which were contained within the reimbursement application, and which it contended contain an accurate recording of the hours worked and the task performed. (Petitioner's Exhibits 11, and Transcript, pages 29 through 31). According to Mr. Hidle, all employees of the company were required to keep a notepad on which they were to record the job (customer), hours worked, and task performed. At some future date, perhaps up to a week or more, those entries were ostensibly transferred to the "Daily Time Log." (Transcript, pages 29 through 31, and page 84). Consequently, Mr. Hidle contends Petitioner's "Daily Time Log[s]" may be relied upon to accurately reflect the hours actually worked, and that those hours were reasonably expended. Here, considering the record, Mr. Hidle's testimony is rejected as not credible or, stated otherwise, inherently improbable and unworthy of belief. In so concluding, it is observed that there is nothing of record, either in the exhibits or testimony offered at hearing, that could possibly explain the dichotomy between the number of hours claimed for development of the MOP (329.42) and the number of hours claimed for development of the MOP Addendum (83.73). Notably, neither project was particularly complex, and the tasks performed were reasonably alike. Similarly, it is inherently improbable, given the limited field work and the product produced (the MOP), that production of the MOP could require 329.42 hours or, stated differently, eight and one-quarter weeks, at 40 hours per week. Finally, most of the entries for which substantial blocks of time are assigned contain only vague or general terms to describe the task, such as "literature review," "MOP/RAP preparation," "file review," and "schedule/plan/coordinate RAP/MOP." Such practice renders it impossible to determine what work was actually done, whether the work was duplicative, and whether the time was actually expended or reasonable. Given the record, it must be concluded that the proof offered by Petitioner to support the number of hours claimed for development of the MOP is not credible or persuasive, and that it would be pure speculation to attempt to derive any calculation or meaningful estimate based on such proof. In the end, Petitioner must bear the responsibility for such failure. While Petitioner's proof offers no credible basis upon which to derive the number of hours dedicated to the MOP and their reasonableness, Petitioner obviously dedicated time to the MOP, and to the extent the record provides a reasonable basis on which to predicate an award, it is appropriate to do so. Here, given the lack of credibility of Petitioner's "Daily time Log[s]," as well as the testimony of Mr. Hidle, to provide a basis on which to derive the number of hours actually worked, and then test those hours against the standard of reasonableness, the only option is to award the 89 hours or $6,308.00, which the Department agrees were reasonably expended. Finally, with regard to the miscellaneous cost items, as opposed to personnel hours, rejected by the Department's letter of June 27, 1996, it must be resolved that Petitioner failed to offer, at hearing, any compelling proof that the items rejected by the Department were reasonable expenditures incurred in development of the monitor only program. Consequently, the following sections of Petitioner's reimbursement application have been reduced by the sums stated: $295.95 deducted from Section 6C; $28.20 deducted from Section 6D; $9.00 deducted from Section 6E; and $800.72 deducted from Section 6I. The award for reimbursement Given the proof, Petitioner should be awarded the following sums, for the items indicated, as reimbursement for preparation of the MOP and MOP Addendum: Personnel $12,249.60 Capital Expense Items Rentals 867.50 Mileage 39.85 Shipping 26.00 Well Drilling Permits Analysis 3680.00 Miscellaneous 800.53 TOTAL 17,663.48 For expenses involved in preparation of the reimbursement application, Petitioner should be awarded the following sums for the items indicated: Personnel $ 795.00 Capital Expense Items Rentals 15.00 Mileage .80 Shipping 67.25 Well Drilling Permits Analysis Miscellaneous 77.77 APPLICATION PREPARATION TOTAL 955.82 CERTIFIED PUBLIC ACCOUNTANT REVIEW FEE 500.00 TOTAL FOR APPLICATION PREPARATION 1,455.82 In all, Petitioner should be accorded a total reimbursement of $19,119.30.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that a final order be entered which awards Petitioner the sum of $19,119.30, as reimbursable costs. DONE AND ENTERED this 22nd day of February, 1999, in Tallahassee, Leon County, Florida. WILLIAM J. KENDRICK 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 22nd day of February, 1999.
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 =================================================================
The Issue Whether Alachua County Environmental Protection Department discriminated against Tilak B. Shrestha based upon his race or national origin, in violation of Title VII of the Federal Civil Rights Act of 1964 and the Florida Civil Rights Act of 1992, by releasing Mr. Shrestha from his temporary assignment through Temp Force with the Alachua County Environmental Protection Department and by not hiring Mr. Shrestha for the position of Senior Environmental Specialist within the Alachua County Environmental Protection Department.
Findings Of Fact The State of Florida funds the Petroleum Cleanup Program (Petroleum Program) which is focused on removing petroleum contaminants from various sites within the State of Florida. The Department of Environmental Protection (DEP) administers the Petroleum Program, also known as the Underground Storage Cleanup Program. In 12 counties, including Alachua, Florida contracts with the county to manage the Petroleum Program. The Alachua County Environmental Protection Department (Alachua DEP) manages the Petroleum Cleanup sites in Alachua County. Mr. Chris Bird has been the director of the Petroleum Program since 1993. He has worked with Alachua County since 1986. In the 1994-1995 fiscal year, the Florida Legislature was facing a deficit; therefore, the Legislature significantly reduced the funding for the Petroleum Program. As a result, DEP froze the Petroleum Program, and dropped several active sites. The lack of funding resulted in downsizing at both the county and state levels at the beginning of 1995. At the beginning of 1995, the Alachua DEP had three funded positions in the Petroleum Program. Mr. Alex Vieira occupied the position of full-time Professional Engineer. The Alachua DEP also had funding for an administrative position and a full-time Environmental Engineer/Geologist. The Environmental Engineer/Geologist position was vacant at the beginning of 1995. The Alachua DEP originally advertised for the position. However, when the State reduced funding for the Petroleum Program, the Alachua DEP decided not to fill the position with a permanent employee and ultimately froze this permanent position. In order for the Petroleum Program to continue at a minimum level of operation, the Alachua DEP hired temporary employees through Temp Force, a temporary employment agency. Temp Force served as an independent contractor for the Alachua DEP. Temp Force provided Mr. Tilak Shrestha and Mr. Mike Shuler to the Alachua DEP Petroleum Cleanup Program. Mr. Shuler began working at the Alachua DEP through Temp Force two months prior to Mr. Shrestha's Temp Force assignment to the Petroleum Program. At the time of the assignment through Temp Force, Shrestha was not credentialed as a Ph.D. Mr. Shrestha and Mr. Shuler were employees of Temp Force, received their paychecks from Temp Force and acquired no benefits from Alachua County. Mr. Shrestha worked as a Temp Force employee for six months at Alachua DEP and was assigned to various projects at the Alachua DEP. As supervisor for the Petroleum Program, Mr. Vieira assigned projects to both Mr. Shrestha and Mr. Shuler. Mr. Shrestha described his working conditions during his assignment through Temp Force with the Alachua DEP as "good, no complaints," and "good on average." In 1995, the Florida legislature ultimately reduced funding for the Petroleum Program from $1.2 million to approximately $250,000. When the Alachua DEP received notice of these funding cuts, Mr. Bird advised Mr. Vieira that he needed to release one of the Temp Force employees from his assignment with the Alachua DEP. Mr. Vieira retained Mr. Shuler and informed Mr. Shrestha that he would no longer be working on the Petroleum Cleanup assignment through Temp Force. Mr. Shrestha's assignment through Temp Force with the Alachua DEP was terminated on August 10, 1995. During Fall 1995, the legislature substantially changed the law and administration pertaining to the Petroleum Program, both at the county and state levels. In October 1995, Ms. Pegeen Hanrahan became the Petroleum Program supervisor following Mr. Vieira's resignation. Ms. Hanrahan earned a Bachelor's degree in Environmental Engineering and Sociology and a Master's degree in Environmental Engineering. She is a registered Professional Engineer and a certified Hazardous Materials Manager. She began working for Alachua County in 1992 as an Environmental Engineer and later served for three years as Hazardous Materials Program Supervisor for Alachua County. When Ms. Hanrahan became supervisor of the Petroleum Program in Fall 1995, the Petroleum Program had essentially entered a "stand-by" mode. The Alachua DEP declined to send any additional work to its sub-contractors. Therefore, the technical duties involved in the Petroleum Program were reduced and the administrative duties became more important. During the Fall of 1995, there were no permanent employees on staff. Mr. Shuler remained as the only temporary employee in the Petroleum Program and according to Ms. Hanrahan was doing a "perfectly adequate job." Based on the new and reduced Petroleum Program budget for the 1995-1996 fiscal year, the Alachua DEP acted in October 1995 to establish the position of Senior Environmental Specialist in lieu of the Environmental Engineer/Geologist position. The position was advertised in December 1995. The main role of the Senior Environmental Specialist was to assist the Professional Engineer in the area of the administration involved in the Petroleum Program. The duties included filing reports, tracking sites, and submitting task orders and invoices to the office in Tallahassee. Due to the increasing changes in the Petroleum Program, the Alachua DEP required a Senior Environmental Specialist who understood the Petroleum Program's administrative tasks, as well as the State policies pertaining to the Petroleum Program. The Senior Environmental Specialist candidate was required to have a technical background in fields including, but not limited to, engineering, biology or geology. The Professional Engineer, not the Specialist, was assigned the technical review of the Petroleum Program. An applicant's understanding of the technical and administrative duties was necessary. In 1995, the Alachua DEP advertised the position of Senior Environmental Specialist, which included printing an advertisement in the local newspaper, per the County regulations. The Alachua DEP described the administrative tasks of Senior Environmental Specialist to include: preparing reports; making recommendations; receiving and investigating complaints; conducting performance evaluations; counseling, hiring and terminating employees. The Alachua DEP described the knowledge, skills, and abilities of the Senior Environmental Specialist to include: thorough knowledge of the technical methods and procedures involved in the administration of environmental regulations, programs, and policies; knowledge of local, state, and federal rules, regulations, and ordinances related to environmental protection; ability to create concise, clear, and succinct technical reports; and ability to research technical problems, formulate recommendations, and compile related reports. The Alachua DEP described the minimum qualifications for the position of Senior Environmental Specialist as: Bachelor's degree in environmental or natural science, civil or environmental engineering, geology, or hydrology, or related field, and two years' professional level environmental-related experience; or any equivalent combination of related training and experience. The County received 14 applications for the position as Senior Environmental Specialist from applicants, which included Mr. Shrestha and Mr. Shuler. Ms. Hanrahan was supervisor of the Petroleum Program in January 1996 and responsible for the hiring of the Senior Environmental Specialist. She received an Application Referral Document from personnel, stating that each of the applicants met the County's minimum requirements for the position of Senior Environmental Specialist. Upon receipt of the re?sume's and applications, Ms. Hanrahan initially screened the applicants for those who had petroleum-related experience. She narrowed the applicants to four individuals, who included Mr. Shrestha, Mr. Shuler, and two others. On January 22, 1996, Ms. Hanrahan conducted a telephone interview of each of the four applicants who passed the initial screening. The telephone interview was customary hiring practice within the Alachua DEP. During the telephone interview, Ms. Hanrahan asked each applicant the same series of ten questions, designed to test the applicant's level of knowledge regarding technical and administrative aspects of the position of Senior Environmental Specialist. Mr. Shrestha answered five out of a possible eleven answers correctly. This was the second highest score out of the four applicants. Shuler achieved the highest score, answering eight-and-one-half out of eleven answers correctly. Three interview questions specifically addressed administrative issues. Question six asked, "What does RBCA stand for?" Question seven stated, "This year the Florida Petroleum Cleanup Program has adopted a new mechanism for review and approval of work on petroleum contaminated sites. Can you tell me what that program is called?" Question nine stated, "Give two examples of policy decisions under RBCA." Mr. Shrestha failed to answer question six, seven or nine correctly. Mr. Shrestha's failure to correctly answer each of the administrative questions indicated to Ms. Hanrahan that he was unaware of the changes within the Petroleum Program. Another purpose of the telephone interview was to assess the applicants under pressure. Ms. Hanrahan also sought to evaluate how the applicants responded to her authority. During the telephone interview, Mr. Shrestha challenged Ms. Hanrahan regarding the relevance of the questions to the position of Senior Environmental Specialist and she noted his argumentative attitude during the interview. He conceded at the hearing that he did ask her about the relevancy of the questions. Based upon his argumentative tone, Ms. Hanrahan questioned Mr. Shrestha about his ability to accept her supervisory decisions. She decided not to hire Mr. Shrestha for the position of Senior Environmental Specialist based on his limited knowledge of the administration of the Petroleum Program, a factor essential to the position of Senior Environmental Specialist, and his inability to accept her authority as supervisor. Ms. Hanrahan was also aware of critical statements that Mr. Shrestha allegedly had made to female co-workers during his assignment through Temp Force at the Alachua DEP. Ms. Robin Hallbourg is currently employed as Senior Environmental Specialist with the Alachua DEP. Ms. Hallbourg has been with the Alachua County DEP for 15 years. Ms. Hallbourg worked with Mr. Shrestha at the Alachua DEP during Mr. Shrestha's assignment through Temp Force. Ms. Hallbourg testified that Mr. Shrestha told her that "she should be home with her child" and that she "should allow a man to have her job." After this conversation, Ms. Hallbourg discussed his statements with others in the Alachua DEP, including Ms. Hanrahan. Ms. Hanrahan recalled the discussion with her. Ms. Hanrahan hired Mr. Shuler for the position of Senior Environmental Specialist because he proved himself to be the most qualified candidate during the interview process. Ms. Hanrahan kept an interview log on which she noted Mr. Shuler's strong qualifications for the position of Senior Environmental Specialist. She noted his "excellent experience in the Petroleum Cleanup Program and his significant applicable training and experience in program administration." Ms. Hanrahan also noted that his "application and interview showed strong computer skills." Mr. Shuler's Bachelor's degree in Microbiology met the education requirements for the position of Senior Environmental Specialist. Moreover, at the time of Shuler's application, there had been a growing emphasis placed on bi-remediation, which is currently a regularly used process. Given Ms. Hanrahan's education, training,and experience as a Professional Engineer, she determined that a Bachelor's degree in Microbiology was an appropriate background for the position. In addition, Mr. Shuler had the technical knowledge of processes, performance of groundwater sampling, and drilling, as well as other relevant technical knowledge pertaining to the position of Senior Environmental Specialist. Additionally, due to his continued assignment in the Alachua DEP, he was aware of the new administrative duties required of a Senior Environmental Specialist. Ms. Hanrahan had personally observed Mr. Shuler from October 1995 until January 1996, and was extremely satisfied with his performance. As part of the usual hiring process, Ms. Hanrahan submitted her interview log, personnel action form, and applications to the personnel department to support her hiring decision. Mr. Bird approved the hiring decision in his capacity as director, and the personnel department, budget department, and Equal Employment Office then approved the decision. Since his hire, Mr. Shuler has been commended by the Alachua DEP and his supervisors. Ms. Hanrahan informed Mr. Shrestha that he had not been hired for the position during a telephone conversation on January 23, 1996. She did not base her decision to hire Mr. Shuler over Mr. Shrestha on the basis of race or national origin. Ms. Hanrahan is fully aware of Alachua County's Equal Employment Opportunity policy through her position as advisor on the Equal Opportunity Advisory Committee. There is no evidence of any discriminatory hiring decision. In fact, on the same day that Ms. Hanrahan hired Mr. Shuler for the position of Senior Environmental Specialist, she also hired Mr. Gus Olmos for the position of Environmental Engineering Supervisor. Mr. Olmos is from Panama and is Hispanic. Moreover, Dr. Prasad Kuchibhotla is a Professional Engineer with a Bachelor's, Master's and Ph.D. in Chemical Engineering. He is from India and is Asian. Alachua County hired Dr. Kuchibhotla in 1997 and is the current Petroleum Cleanup Program Manager for Alachua DEP. Dr. Kuchibhotla currently has a Senior Environmental Specialist working for him within the Petroleum Program. As was the case in December 1995, the current Specialist's primary duty is to assist him with the detailed administrative tasks involved with the Petroleum Program. On January 27, 1997, Mr. Shrestha filed a formal Charge of Discrimination. The charge was date stamped as received by the Florida Commission on Human Relations on January 30, 1997. Mr. Shrestha is currently employed with Bell South in Atlanta, Georgia. He earns $47,000 per year and receives health benefits.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Florida Commission on Human Relations enter a final order finding that Petitioner, Tilak B. Shrestha is not entitled to any relief relating to his charge of discrimination under Title VII of the Federal Civil Rights Act of 1964 and the Florida Civil Rights Act of 1992. DONE AND ENTERED this 2nd day of August, 2000, in Tallahassee, Leon County, Florida. WILLIAM R. PFEIFFER 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 2nd day of August, 2000. COPIES FURNISHED: Tilak B. Shrestha 3579-C Meadowglen Village Lane Doraville, Georgia 30340 Robert M. Ott, Esquire County Litigation Attorney Post Office Box 2877 Gainesville, Florida 32602 Sharon Moultry, Clerk Florida Commission on Human Relations 325 John Knox Road Building F, Suite 240 Tallahassee, Florida 32303-4149 Dana A. Baird, General Counsel Florida Commission on Human Relations 325 John Knox Road Building F, Suite 240 Tallahassee, Florida 32303-4149
Findings Of Fact Petitioner is the owner of the site known as Union 76 #702 or as Taylor's 76, Inc., located at 9700 East Indigo Street, Perrine, Dade County, Florida. The prior owner of that site was Lawrence Oil Company. There appears to be a commonality of principals between Petitioner TYU, Inc., and its predecessor in title, Lawrence Oil Company. In 1986 the Legislature created the Early Detection Incentive Program (hereinafter "EDI") to encourage early detection, reporting, and cleanup of contamination from leaking petroleum storage systems. Essentially, the Legislature created a 30-month grace period ending on December 31, 1988, for owners of sites with contamination from petroleum storage systems to apply for reimbursement for cleanup expenses due to the contamination, without retribution from the State. The statute also provided several bases for which an applicant would be deemed ineligible. Prior to the December 31, 1988, deadline Petitioner checked the various sites owned by it, including the site which is the subject of this proceeding, to determine whether contamination was present. The subject site had been a service station, selling gasoline for 30 to 35 years. From 1986 forward, however, gasoline was no longer being dispensed at the site although the underground gasoline tanks were still present. It is unknown whether the tanks were emptied at the time that they were taken out of service. Automobile repairs were still performed at the site. By 1989, the site was also occupied by a lawn maintenance company and a pool company. In 1988 and 1989 a 55-gallon drum of used oil was located on the site. The lawn company employees used that oil to lubricate their chain saws. The remainder of the used oil and the solvents from the small parts washer were picked up from that site for recycling. In November or December of 1988, Harry Barkett, president of Lawrence Oil Company, personally visited the site. He sampled the monitoring wells. Because he smelled gasoline in the monitoring wells, he retained Seyfried & Associates, Inc., an environmental consultant, to prepare a report to be submitted to the Department. That report is dated December 15, 1988. Petitioner's application for participation in the EDI program, together with the report of Seyfried & Associates, Inc., was submitted to the Department prior to the December 31, 1988, deadline. At the time, Metropolitan Dade County's Department of Environmental Resources Management (hereinafter "DERM") was performing EDI inspections for the Department pursuant to a contract. On March 22, 1989, a DERM employee who performed only industrial waste inspections went to the subject site. He specifically was not there to inspect the petroleum storage systems, and he did not do so. That employee went into the service bays where the routine auto repair and maintenance services were performed. He noticed the floor drains going from the service bays to the oil/water separator. He then inspected the oil/water separator. He noted that a hole had been cut at the top of the effluent pipe, which breached the system and which might allow oil to flow into either a drain field or a septic tank system. He did not check further to ascertain which. He took three samples from inside the oil/water separator, one for oil and grease, one for phenols, and one for metals, specifically cadmium, chromium, and lead. Not surprisingly, the laboratory analysis of those samples indicated the presence of phenols, oil, and grease. The only sampling done by that employee was of the contents of the oil/water separator. No investigation was made of, and no samples were taken from, the soil or groundwater anywhere on the site. Such sampling was not part of that employee's authority or responsibility. On October 11, 1989, Dade County DERM sent a different employee to perform the EDI inspection at the subject site. To determine the presence of contamination from petroleum or petroleum products, that employee dipped an acrylic bailer into each of the monitoring wells and then "sniffed the bailer" to ascertain if the odor of gasoline could be detected. He did not dip the bailer lower than the top foot of water since he did not wish to bring the bailer up through a column of water before sniffing. Dade County DERM employees no longer "sniff the bailer" due to the health risk involved in such a procedure. In 1989, however, it was the common practice for DERM employees to "sniff the bailer," albeit cautiously. That employee failed to detect the odor of gasoline and did not see any petroleum contamination in the monitoring wells. He issued a report to that effect. He took no samples from the soil or groundwater to determine if there were contamination from petroleum or petroleum products at the site. Based upon the second report indicating the absence of gasoline odor and based upon the first report indicating the presence of oil, grease, and phenols inside the oil/water separator, Dade County DERM recommended to the Department that Petitioner's application for participation in the EDI program be denied. Based upon that recommendation, the Department sent Petitioner a letter dated May 23, 1990, denying Petitioner's application for participation in the EDI program. That letter stated as the two reasons for denial the following: Contamination is not the result of a discharge from a petroleum storage facility as defined in Section 376.301(11), Florida Statutes. Waste oil contamination found on the ground and groundwater was the result of poor maintenance practices by site owner/ operator. Participation in the Early Detection Incentive Program is restricted to contamination from such storage facilities pursuant to 376.3071(9), Florida Statutes. Contamination is a mixture of waste oil, grease and phenolic compounds. Participation in the Early Detection Incentive Program is limited to petroleum or petroleum products as defined in Section 37.301 [sic] (9) and (10), Florida Statutes. That letter further advised Petitioner of its right to request a hearing regarding that determination and advised Petitioner that its failure to timely request an administrative hearing would render that correspondence to be a final Order of Determination of Ineligibility. When Petitioner received that correspondence, one of its employees interpreted the letter to mean that the Department had determined that the site did not have contamination from petroleum or a petroleum product. Viewing that as good news, that employee merely put the letter in a file. No request for an administrative hearing was made by Petitioner, and the correspondence became a final Order of Determination of Ineligibility by its own terms. In 1990 the Legislature determined that all sites which had been declared ineligible by the Department would be re-determined for eligibility. The Legislature established March 31, 1991, as the new deadline by which owners or operators could request the Department to reevaluate eligibility for sites for which a timely EDI application had been filed but which had been deemed ineligible by the Department. The new legislation set forth several circumstances under which the Department would not redetermine the eligibility of a previously denied site. One of those exceptions related to the reason for which a site had initially been denied. Petitioner had remained convinced that the subject site was contaminated by petroleum or petroleum products prior to the original deadline for filing EDI applications. Petitioner was aware of the new legislation and new deadline by which sites determined ineligible could have their eligibility redetermined. Petitioner therefore retained Kiefer-Block Environmental Services, Inc., to do a site analysis to verify Petitioner's belief that the site had a petroleum contamination. That company issued a report indicating that was the case. Petitioner timely filed its application for redetermination before the March 31, 1991, deadline and submitted to the Department the information obtained from Kiefer-Block, the second environmental consultant to verify the presence of petroleum contamination. In reviewing applications for redetermination, the Department established a procedure whereby it simply looked at its original letter denying eligibility to ascertain the reason for denial. If that reason matched one of the exclusions under the new legislation, the Department advised the applicant that it was not eligible to have its site redetermined. The Department did not review the Department's files relating to a site and did no additional inspection. In 1991 the Legislature again amended the statute, this time carving out an exception to those sites excluded from redetermination of eligibility by directing that sites excluded due to an absence of contamination be redetermined for eligibility if contamination had in fact existed. That amendment went into effect July 1, 1991. Accordingly, that amendment was part of the law in effect when the Department made its decision as to whether it would redetermine Petitioner's eligibility. By letter dated September 3, 1991, the Department advised Petitioner that it was not eligible to participate in the redetermination process. That letter specifically provided as follows: This Order is to inform you that this site is not eligible to participate in the eligibility redetermination process pursuant to Section 376.3071(9)(b), F.S., because the original reasons for ineligibility were: Contamination is not the result of a discharge from a petroleum storage facility as defined in Section 376.301(11), Florida Statutes [definition in Section 376.301(15), F.S., current revision]. Waste oil contamination found on the ground and groundwater was the result of poor maintenance practices by site owner/ operator. Participation in the Early Detection Incentive Program is restricted to contamination from such storage facilities pursuant to 376.3071(9), F.S. Contamination is a mixture of waste oil, grease and phenolic compounds. Participation in the Early Detection Incentive Program is limited to petroleum or petroleum products as defined in Section 376.301(9) and (10), Florida Statutes [definitions in Section 376.301(13) and (14), F.S., current revision]. Section 376.3071(9)(b)3.c., F.S., states that redetermination of eligibility is not available to facilities that were denied eligibility due to contamination from substances that were not petroleum or a petroleum product, or contamination that was not from a petroleum storage system. Petitioner timely filed its request for an administrative hearing regarding that letter, contesting the Department's refusal to redetermine Petitioner's eligibility to participate in the EDI program.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that a Final Order be entered: (1) granting Petitioner's application for redetermination of eligibility and (2) finding Petitioner ineligible to participate in the Early Detection Incentive Program. DONE and ENTERED this 26th day of August, 1992, at Tallahassee, Florida. LINDA M. RIGOT 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 26th day of August, 1992. APPENDIX TO RECOMMENDED ORDER DOAH CASE NO. 92-0678 Petitioner's three unnumbered paragraphs contained in its post-hearing submittal have been rejected as not constituting findings of fact but rather as constituting conclusions of law or argument. Respondent's proposed findings of fact numbered 1-3, 5-18, and 20 have been adopted either verbatim or in substance in this Recommended Order. Respondent's proposed finding of fact numbered 4 has been rejected as being unnecessary to the issues involved herein. Respondent's proposed finding of fact numbered 19 has been rejected as not being supported by the weight of the competent evidence in this cause. COPIES FURNISHED: C. Vittorino Special Projects Manager TYU, Inc. 1601 McCloskey Boulevard Tampa, Florida 33605-6710 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, General Counsel Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32399-2400
The Issue The question presented here concerns the Petitioner, State of Florida, Department of Agriculture and Consumer Services' Stop Sale Notice placed against Respondent, Pinner Oil Company under the alleged authority of Section 525.06, Florida Statutes (1980), by the process of requiring a refundable bond in the amount of $471.34, pending the outcome of this dispute in which it is contended that the Respondent supplied gasoline for sale which failed to comply with Rule Subsection 5F-2.01(1)(j), Florida Administrative Code, dealing with the allowed lead content in gasoline.
Findings Of Fact The Petitioner, State of Florida, Department of Agriculture and Consumer Services is an agency of government which has, among other responsibilities, the requirement to establish and enforce standards related to maximum allowable lead content in unleaded gasoline offered for sale to the general public. This regulation is designed to avoid the destruction of catalytic devices found in the exhaust systems of certain cars, in which the destruction of a catalyst would bring about problems, with the exhaust system causing its replacement and more importantly, lead to adverse effects on the environment due to an increase in undesired emission from the exhaust system. The Respondent, Pinner Oil Company of Cross City, Florida, is a jobber which supplies gasoline to retail outlets who in turn sales the gasoline to members of the motoring public. The facts reveal that on October 6, 1980, an official with the Petitioner made a routine inspection of the unleaded gasoline reservoir at the B. F. Goodrich-Texaco at 210 Rogers Boulevard, Chiefland, Florida, a customer of Pinner Oil Company. This gasoline was subsequently analyzed and on October 7, 1989, a Stop Sale Notice was served based upon a determination that the unleaded gasoline found in the reservoir at that station contained more than 0.05 grams of lead per U.S. gallon. The gasoline in question was provided to the B. F. Goodrich outlet by an employee of Pinner Oil Company as a part of his duties with the Respondent. In lieu of the total confiscation of the gasoline found in the reservoir tank at the station In question, the Respondent was allowed to post a refundable bond in the amount of $471.34 which represented the price for the number of gallons sold at a retail price since the time of the prior delivery to that station. (By Stipulation entered into between the parties, it was agreed that a finding of fact would be made to the effect that the Respondent, during the course of the last two years, had not been cited for a violation of the Florida Statutes pertaining to contaminated fuels.)
Findings Of Fact Since 1984, the Department has been the state agency charged with the responsibility to establish rules and regulate underground pollutant storage facilities in Florida. In 1988, the Legislature added the administration of the newly enacted Florida Petroleum Liability and Restoration Program to the Department's duties. The program was to be established on or before January 1, 1989. The Applicant is the owner of a petroleum storage system in Jacksonville, Florida. Since 1984, it has been subject to the rules regarding underground pollutant storage facilities promulgated by the Department. On September 18, 1989, an odor indicative of possible petroleum contamination was discovered at the site during the installation of monitoring wells. A Discharge Notification Form was sent to the Department by the Applicant on October 23, 1989. The form advised that there were no leaks in the system. It was suggested that the odor may have resulted from surface spill at the site over a number of years. In response to the notification, an inspection of the site was completed by the Department on December 5, 1989. The inspection revealed the following on-site violations: Registration requirements were not being met. The forms had not been updated to include the presence of monitoring wells and overfill protection at the facility. Two underground tanks had not been properly abandoned. Inventory and reconciliation records had not been properly maintained, as required by rule since 1987. This violation was reviewed, and discussed in detail with on-site representatives of the Applicant. The monitoring wells were not installed by the time deadlines set forth in the Department's rules regarding stationary tanks. Since the wells were installed in September 1989, samples had not been taken for visual signs of petroleum contamination. The purpose of the system is to allow the owner of the storage tanks to learn if there is a leak in the tanks that can be quickly controlled to limit contamination. The day after the inspection, the Applicant applied for a determination of eligibility for participation in the restoration coverage portion of the new Florida Petroleum Liability Insurance and Liability Program. An affidavit was signed stating that all of the Department's rules regarding stationary tanks were being complied with by the Applicant. Six days after the inspection, the Department sent the Applicant written notice of the results of the inspection. The Applicant was given time frames and instructions for correcting the listed violations that could be corrected. A contamination assessment and clean up were also required in the letter. This letter did not address the issue of eligibility for the restoration funding program because that was a matter unrelated to the inspection results. On March 7, 1990, the Department determined the facility was ineligible for participation in the restoration funding provided by the Florida Petroleum Liability and Coverage Program. The following reasons were given: Failure to properly abandon underground storage tanks, pursuant to Section 17-61.050(3)(c), Florida Administrative Code. Failure to maintain inventory records, reconciliations, and significant loss/gain investigation as per Section 17-61.050(4)(c), Florida Administrative Code. Failure to install monitoring system and overfill protection by the dates set forth in Section 17-61.06(2)(c)2, Florida Administrative Code. Failure to properly monitor leak detection system, pursuant to Section 17-61.050(5)(c), Florida Administrative Code. The 10,000 gallon fuel oil tank and the 3,000 gallon waste oil tank present at the facility were abandoned in March 1990. The notice issued by the Department after its inspection in December 1989, gave the Applicant sixty days after receipt of the notice to properly abandon the tanks. The Applicant substantially complied with this requirement after the written notice was received. Although the Applicant failed to maintain the inventory records, reconciliations, and significant loss/gain investigations required by the Department rules, some of these violations had been corrected prior to the Department's inspection in December 1989. Correct inventory recordkeeping was discussed during the inspection, and the need to immediately implement the proper recordkeeping practices was emphasized in the post-inspection notice of violations. All of the recordkeeping violations were not cured until August 1990. The records kept by the Applicant during the noncompliance period from 1984 to August 1990, did not provide a substantially equivalent degree of information regarding possible leak detection or prohibited discharges as the required recordkeeping procedures. Two underground stationary storage tanks on the site have been part of the Applicant's petroleum storage system since 1970 and 1975, respectively. The monitoring wells and overfill protection for these tanks should have been in place by December 31, 1987. Neither monitoring system was installed until September 1989. The Applicant began the contract negotiations for installation in September 1988. The Applicant did not demonstrate that the facility contained an alternative procedure between December 31, 1987 and September 1989, that provided a substantially equivalent degree of protection for the lands, surface waters, or groundwaters of the state as the established requirement for monitoring wells and overfill protection. In December 1989, the Department's notice advised the Applicant that the monitoring wells should be sampled monthly for visual signs of petroleum contamination. Since April 1990, the Applicant has been completing the monthly sampling in the monitoring wells as part of its leak detection system, as required by the Department's rule regarding underground stationary tanks.
Recommendation Accordingly, it is RECOMMENDED: That the Department enter a Final Order denying Petitioner's application for restoration coverage in the Florida Petroleum Liability and Restoration Program at the Jacksonville location. DONE and ENTERED this 28 day of December, 1990, in Tallahassee, Leon County, Florida. VERONICA E. DONNELLY Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904)488-9675 Filed with the Clerk of the Division of Administrative Hearings this _28_ day of December, 1990. APPENDIX TO RECOMMENDED ORDER The proposed findings of fact submitted by Petitioner are addressed as follows: Rejected. Improper interpretation of law. As for the facts in the first sentence, they are accepted. See HO #8. Rejected. Irrelevant. See HO #9. Rejected. Contrary to fact. See HO #9 and #11. Rejected. Contract to fact. See HO #11. Rejected. Contrary to fact. See HO #12 and #13. Rejected. Contrary to fact. Improper shifting of duty ad legal responsibility. Rejected . Improper application of law. The Respondent's proposed findings of fact are addressed as follows: Accepted. Accepted. Accepted. Accepted. See HO #8. Accepted. See HO #8. Accepted. See HO #3. Accepted. See HO #3. Accepted. See HO #3. Accepted. See HO #5. Accepted. Accepted. See HO #4. Accepted. See HO #4. Accepted. Accepted. See HO #6. Accepted. See HO #4 and #6. Accepted. See HO #4 and #6. Accepted. Accepted. Accepted. See HO #4 and #9. Accepted. Accepted. See HO #4 and #9. Accepted. Accepted. See HO #9. Accepted. See HO #4 and #10. Accepted. Rejected. Contrary to fact. See HO #10. Accepted. Accepted. Accepted. See HO #10. Accepted. See HO #3 and #12. Accepted. Accepted. See HO #13. Accepted. Accepted. See HO #6. Accepted. See HO #4 and #6. Accepted. See HO #6. Accepted. Rejected. Not established by evidence. See HO #6. Accepted. Accepted. Accepted. Accepted. See HO #7. Accepted. Accepted. COPIES FURNISHED: William Chadeayne, Qualified Representative 8933 Western Way, Suite 16 Jacksonville, Florida 32256 Janet E. Bowman, Esquire Assistant General Counsel Department of Environmental Regulation 2600 Blairstone Road Tallahassee, Florida 32399-2400 Dale H. Twachtmann, Secretary Department of Environmental Regulation 2600 Blairstone Road Tallahassee, Florida 32399-2400 Daniel H. Thompson, Esquire General Counsel Department of Environmental Regulation 2600 Blairstone Road Tallahassee, Florida 32399-2400
Findings Of Fact Puckett reported a discharge of used oil at its site when it filed an early detective incentive program notification application with DER. Puckett, thus, advised DER that it would clean up its site and apply for reimbursement of the costs of that cleanup in accordance with Section 376.3071(12), Florida Statutes (Supp. 1986). When it received Puckett's application, DER conducted an investigation of the site and determined that a discharge of used automotive crankcase oil had occurred there. DER was advised by Puckett that the discharge had occurred when used automotive crankcase oil was drained into a service bay floor drain. Puckett and the site operator placed the used oil in the drain in the belief that a storage tank was connected to the floor drain to receive and safely store the used oil. Unknown to Puckett, however, the storage tanks previously connected to that floor drain had been removed by a former site owner or operator. The Recommended Order entered by the Hearing Officer contains findings to the effect that Puckett was unaware that storage tanks did not any longer connect with the floor drain in question, in part, at least, because it is the custom and practice in the service station business that used oil collecting persons or entities collect from such storage tanks after the service station hours of operation. Therefore, it was customary for the operator of a service station not to be aware of when used oil was removed from storage tanks. Upon learning that used oil had been spilled at the site due to the lack of a storage tank, where formerly one had been in place, the subject application was filed. DER conducted its site investigation and after it was concluded, on April 16, 1987, issued an order denying reimbursement eligibility to Puckett. DER took this position because it opined that used oil is not "petroleum" or a "petroleum product", as those terms and substances are defined in Subsections 376.301(9)(10), Florida Statutes (Supp. 1986). Puckett then filed a timely petition for administrative hearing as a result of that denial of eligibility. The cause was duly transmitted to the undersigned Hearing Officer for conduct of a Section 120.57, Florida Statutes, formal proceeding. In the discovery phase of that proceeding, requests for admissions were served by Puckett upon DER, in response to which DER admitted that the sole basis for denial of reimbursement eligibility was the fact that the substance discharged was used oil, which, DER contended was not "petroleum" or a "petroleum product". DER, thus, took the position that the used oil in question was beyond the scope of reimbursement eligibility allowed by the "Super Act," the statutory provisions cited above. The cause was duly scheduled for hearing for September 9-10, 1987. Shortly prior to the hearing, on August 31, 1987, DER filed a motion for continuance seeking an opportunity thereby to have time to explore the question of whether Puckett was "grossly negligent" in the maintenance of its facility, which is a ground for disqualification from Super Act reimbursement eligibility. This was an issue which had not theretofore been raised in the proceeding. See Section 376.3071(9)(b)3., Florida Statutes (Supp. 1986). That motion for continuance was denied, as found and discussed in the Recommended Order in the underlying proceeding. The cause then came on for hearing as scheduled on September 9-10, 1987. A motion in limine filed by Puckett was granted at the hearing so as to preclude DER from raising any issue concerning "gross negligence" at hearing. The basis for the ruling was that DER had known of the circumstances surrounding the discharge for nearly one year, but that during the discovery process, DER assured Puckett that its position was that gross negligence would not be an issue in the proceedings and that the sole basis for its denial of the reimbursement application was that the substance discharged, being used oil, was not, in its view, "petroleum" or a "petroleum product". Following the hearing, the Hearing Officer issued the Recommended Order in question finding that used crankcase oil was, indeed, "petroleum", as well as being a "petroleum product", for the purposes of the definitions in the above- cited statutory provisions. It was thus recommended that Puckett be determined to be eligible to apply to DER for reimbursement of the cleanup costs involved. Puckett, 10 FALR at 5540. Certain findings and conclusions made in the Recommended Order are germane to the question of whether DER's actions with respect to the initial and final denial of Super Act eligibility had a reasonable basis in law and fact at the time the agency action was initiated and finally taken in the Final Order. Those findings include the findings in the Recommended Order that used crankcase oil consists of "petroleum", as that term is defined by Section 376.301(9), Florida Statutes (Supp. 1986), with particular emphasis on those findings and conclusions in the Recommended Order, incorporated by reference herein, concerning crankcase oil coming within the definition of "other hydrocarbons" for the reasons delineated in the Recommended Order. Further, DER's own expert witness admitted, and it was found by the Hearing Officer, that the predominant use of used oil is as a fuel, just as is gasoline, diesel, kerosene and certain other grades of fuel oil, which are specifically included in the statutory definition of "petroleum product". See page 20 of the Recommended Order and the transcript of the proceeding below, pages 362-363. It was also established without question that used oil is a "liquid," a "commodity" and a liquid fuel commodity for the reasons delineated in the Recommended Order. It was established further by the record in the proceeding on the merits, and found in the Recommended Order that used oil has no meaningful similarity to the substances specifically, statutorily excluded from the definition of "petroleum product", and that DER has had a policy encouraging the collection and recycling of used oil as a fuel. This was well-known and accepted by DER's own experts before the "policy makers" at DER, who engendered the subject initial agency action, took the position that used oil did not constitute petroleum or a petroleum product. Used oil has not been otherwise regulated as a hazardous waste. DER's interpretation of the statutory definition of "petroleum product" to the effect that the product, as it was initially produced, must be sold or used as a fuel in order to meet that definition, in fact, imposes an additional inconsistent criteria for determining what types of substances are included within the meaning of the term, which criteria is not enunciated in the statute, either expressly or implicitly. DER's restrictive interpretation of the statute further disregards the language of the Super Act. Sections 376.3071(12)(a) and 376.315, Florida Statutes (Supp. 1986), which requires it to give "such liberal construction to the statute as will accomplish the purposes set forth in this subsection", in other words, to promote the cleanup of as many contamination sites as possible. Further, it was established by the record in the proceeding on the merits and concluded in the Recommended Order that the restrictive interpretation of the statute adopted by DER was inconsistent with existing agency policy which encourages used oil collection and recycling and that the interpretation "is clearly not one expressed or reasonably implied on the face of the statute" and "would frustrate the clear, legislative impetus of the Super Act" and is "illogical". More significantly, DER's policy makers responsible for the initial agency action and decision that used oil is not "petroleum" or a "petroleum product" did not take counsel with certain key expert personnel in DER's own used oil section concerning whether used oil is "petroleum" or a "petroleum product" prior to the initial denial of eligibility and the proceeding and hearing before the Hearing Officer. In fact, the policy makers were apparently unaware of facts critical to the subject determination and to the fact that DER's proposed (and, indeed, final) action was inconsistent with agency policy concerning treatment and definition of used oil, which DER's "in- house" experts had been aware of all along. These findings and conclusions in the Recommended Order demonstrate clearly and in detail why DER's initial agency action and position through the conclusion of the hearing, concerning rejection of Puckett's reimbursement eligibility, did not have a reasonable basis in law and fact. Those findings and conclusions appearing at pages 18-36 of the Recommended Order, which has been stipulated into the record of the instant proceeding, are incorporated by reference and adopted in the findings of fact and conclusions of law in this Final Order. Despite the findings and conclusions in the Recommended Order, DER, in its Final Order, ultimately denied reimbursement eligibility. Puckett at page 5505. DER found in its Final Order that Super Act coverage is limited to "incidents related to storage", as opposed to incidents where a contaminant is discarded. DER also found that because Puckett did not have a "petroleum storage system" at the site, the discharge was not "related to storage", despite the facility operator's proven and found intention and belief, when he dumped the product in the floor drain, that he was "storing" the used oil in question. DER acknowledged the Hearing Officer's granting of Puckett's motion in limine, which precluded denial of reimbursement eligibility on "gross negligence" grounds, but stated that it was not denying eligibility on this ground at page 18 of its Final Order. Although DER acknowledged in its Final Order that its denial of eligibility did not depend on a finding of gross negligence, this acknowledgment, which appears to re- state its position, taken in the discovery phase, that gross negligence would not be raised as an issue by DER, and is an apparent acknowledgment of the ruling on the motion in limine, is somewhat belied by the following language from the Final Order: Although my decision to deny eligibility for reimbursement to Puckett does not depend on a finding of gross negligence on the part of Puckett, any site owner who fails to ascertain whether an oil drain fitting on site is actually connected to an operational used oil system now has clear notice that it allows used oil discharges to that drain fitting only at its own peril. It is not appropriate that state funds be expended to remediate contamination caused by reckless disregard for elementary waste disposal regulations. In the future, the department will continue to deny eligibility to any site where contamination has resulted from used oil discharges to land in the complete absence of a used oil storage system. (emphasis supplied) See pages 18 and 19 of the Final Order. Puckett then appealed that denial of reimbursement eligibility. The District Court of Appeals reversed DER, finding as follows: DER's assertion that Puckett's eligibility for cleanup reimbursement of the used oil discharge was dependent on whether storage was involved and whether the used oil would be reused or recycled was never made until the final agency order was entered. These issues were not raised by the pleadings, were not litigated at the hearing, were not considered by the Hearing Officer, and were not considered by the Hearing Officer's Recommended Order. In addition, the pleadings reflect that DER was asked in a written request for admission to admit the following: 'The Department's only basis for denial of Super Act eligibility for Puckett is that the reported discharge was used oil.' DER admitted that statement. This was the only issue created by the pleadings, and it was the only issue tried and determined by the Hearing Officer. DER cannot raise and decide for the first time in the final agency order issues not previously raised or considered. See Puckett, 549 So.2d at 722 (emphasis in original). The Court then remanded the proceeding to DER for entry of an order determining Puckett to be eligible to apply for reimbursement. Puckett also petitioned the appellate court for appellate attorney's fees pursuant to Section 120.57(1)(b)5., Florida Statutes, arguing that the Final Order was a "gross abuse" of agency discretion, a standard for granting of appellate attorney's fees under that statutory provision. The Court denied that motion on the basis that gross abuse of agency discretion had not been demonstrated. Although reliance on issues improperly raised for the first time in the Final Order may not have been a "gross abuse" of agency discretion supportive of an award of appellate costs and fees pursuant to the above- referenced statutory provision, it is found that DER has not justified as reasonable its rejection of eligibility on additional non-litigated or properly raised grounds in the Final Order. Therefore, DER's reliance on the new issues in the Final Order to deny reimbursement eligibility was not "substantially justified". After issuance of the Court's mandate, Puckett filed a petition for costs and fees pursuant to Section 57.111, Florida Statutes, initiating the instant proceeding. DER filed an untimely response conceding that Puckett was a "prevailing small business party" and the other criteria for award of fees and costs provided for in Section 57.111, Florida Statutes, with the exception that it did not concede that its denial of reimbursement eligibility in the related proceeding was not "substantially justified". DER did not dispute that the reasonable amount of costs and fees incurred by Puckett exceeded $15,000.00 nor did it assert that any special circumstances exist which would make an award of costs and fees unjust nor that it was a nominal party only. Since Puckett's petition was not timely responded to and since its Motion for Summary Final Order thereon was not answered by DER, the Hearing Officer issued a Summary Final Order awarding $15,000.00 in costs and fees to Puckett. DER appealed and the First District Court of Appeals reversed the award and remanded the proceedings to the Hearing Officer to consider DER's position on the issue of award of fees and costs, based generally upon the Court's view that DER's non- timely response to the petition for fees and costs should be excused, as more particularly delineated in the Court's opinion in Department of Environmental Regulation v. Puckett Oil Company, Inc., 16 FLW D.926 (Fla. 1st DCA April 3, 1991). The cause involving fees and costs, thus, became at issue before the Hearing Officer once again. In the prehearing filings, the parties limited the issues to that concerning whether DER's action on the reimbursement eligibility question was "substantially justified". On July 30, 1991, a hearing was held on this matter, during which the parties presented their arguments and stipulated that the record in this proceeding would be the record on appeal, including the Hearing Officer's Recommended Order in the reimbursement eligibility case.
The Issue The issue is whether Florida Petroleum Markers and Convenience Store Association (Florida Petroleum) is entitled to reasonable attorney’s fees and costs pursuant to Section 120.595(2), Florida Statutes, and if so, in what amount.1
Findings Of Fact Introduction Florida Petroleum is the prevailing party in the underlying rule challenge and requests an award of reasonable attorney's fees pursuant to Section 120.595(2), Florida Statutes.2 Florida Petroleum prevailed in DOAH Case No. 05-0529RP on one of two challenged proposed rule revisions to Florida Administrative Code Chapter 62-770, which governs cleanup of petroleum contamination. Proposed rule 62-770.220(3)(b) was held to be an "invalid exercise of delegated legislative authority." Proposed rule 62-770.220(4), was "not an invalid exercise of delegated legislative authority, except insofar as notice must be given every five years to persons other than 'local governments and owners of any property into which the point of compliance is allowed to extend,' as provided in Section 376.3071(5)(b)2., Florida Statutes."3 The Department argues that its actions were "substantially justified" because there was a reasonable basis in law and fact at the time its actions were taken. The proposed rules were approved by the Environmental Regulation Commission (ERC) on February 2, 2005, which is the time when the Department's "actions were taken." The Department does not argue that special circumstances exist that would make the award of fees unjust. Department Contamination Programs The Department's Division of Waste Management is comprised of the Bureau of Petroleum Storage Systems, the Bureau of Waste Cleanup, and the Bureau of Solid and Hazardous Waste. The Bureau of Petroleum Storage Systems administers the state's petroleum contamination cleanup program. This cleanup program encompasses the technical oversight, management, and administrative activities necessary to prioritize, assess, and cleanup sites contaminated by discharges of petroleum and petroleum products from petroleum storage systems. There are approximately 23,000 petroleum-contaminated sites statewide. Florida Administrative Code Chapter 62-770 establishes petroleum contamination site cleanup criteria. These criteria are established for the purposes of protecting the public health and the environment and for determining, on a site-specific basis, the rehabilitation program tasks that comprise a site rehabilitation program and the levels at which a rehabilitation program task and site rehabilitation program may be deemed complete. Fla. Admin. Code R. 62-770.160(8). The petroleum contamination cleanup program incorporates risk-based corrective action (RBCA) principles to achieve protection of human health, public safety, and the environment in a cost-effective manner. The phased RBCA process is iterative and tailors site rehabilitation tasks to site-specific conditions and risks. Fla. Admin. Code R. 62-770.160(8). The Bureau of Waste Cleanup administers the state's drycleaning solvent cleanup program. This program is for the cleanup of property that is contaminated with drycleaning solvents as a result of the operations of a drycleaning facility or wholesale supply facility. Florida Administrative Code Chapter 62-782 establishes drycleaning solvent cleanup criteria, established for the purposes of protecting the human health, public safety and the environment under actual circumstances of exposure and for determining, on a site-specific basis, the rehabilitation program tasks that comprise a site rehabilitation program and the levels at which a rehabilitation program task and site rehabilitation program may be deemed complete. Fla. Admin. Code R. 62-782.150(1). The drycleaning solvent cleanup program, like the petroleum contamination cleanup program, the brownfield site rehabilitation program, and the global RBCA contamination cleanup program mentioned below, incorporates RBCA principles to achieve protection of human health and the environment in a cost-effective manner. Fla. Admin. Code R. 62-782.150(1) and 62-785.150(1). In 2003, the Legislature adopted Section 376.30701, Florida Statutes, which authorizes the Department to adopt rule criteria for the implementation of what is referred to as "global RBCA," which extends the RBCA process to contaminated sites where legal responsibility for site rehabilitation exists pursuant to Chapter 376 or Chapter 403, Florida Statutes. Global RBCA is a cleanup program for contaminated sites that do not fall within one of the Department's other contamination cleanup programs. Department Rulemaking Efforts After the passage of Section 376.30701(2), Florida Statutes, the Department initiated rulemaking to develop Florida Administrative Code Chapter 62-780 (global RBCA). Section 376.30701(2) established July 1, 2004, as the date the Department was to adopt rule criteria to implement the global RBCA contamination cleanup program. At the same time, the Department initiated rulemaking with respect to revisions to Florida Administrative Code Chapters 62-770 (petroleum), Chapter 62-782 (drycleaning solvents), and Chapter 62-785 (brownfields). This decision was predicated on the similarities among the four waste cleanup programs and the Department's desire to ensure a consistent approach across the four programs and pursuant to one large rulemaking effort. As such, the Department sought to include the same notification provisions in each rule for consistency purposes. (T 33-34, 55). However, the Department also recognized at the time that the notice provision for RBCA for petroleum contamination cleanups, i.e., Section 376.3071(5)(b)2., was different from the notice provisions for RBCA cleanups for the drycleaning solvent (Section 376.3078(4)(b)), brownfields (Section 376.81(1)(b)), and global RBCA (Section 376.30701(2)(b)) programs. (T 69, 115, 126-129). In each of these three statutes, the Legislature expressly expanded the class of persons to whom notice is required to be given and expressly referred to a specific type of notice to be given (actual or constructive) depending on the class of persons designated to receive notice. Each of the latter statutes was enacted after, and presumably with knowledge of Section 376.3071(5)(b)2., which was materially amended in material part in 1996 to add, in part, the notice provision. See Ch. 96-277, § 5, at 1131, 1135-1136, Laws of Fla. In May 2004, the Department became aware of concerns with regard to on-going efforts to assess the groundwater contamination at the former American Beryllium plant in Tallevast, Manatee County, Florida. (The party's refer to the city as Tallavast, whereas the Transcript (T 36) and DEP Exhibit 1 refer to the city as Tallevast.) For approximately two years, the owner of the plant, Lockheed Martin, had been conducting an on-going assessment of the extent of the solvent (trichloroethylene) contamination. The Department was concerned that there were residential areas located adjacent to and in the immediate vicinity of the former industrial plant. In May 2004, it became apparent that there were problems with certain assumptions concerning the assessment of the groundwater contamination. First, there had been an erroneous assumption that the contamination plume was small and located predominantly on-site. Second, based on well surveys, there was an assumption that there were no human health exposure points in the form of contaminated off-site potable water wells. Significant concerns arose when it became apparent the contamination plume was more extensive than anticipated and had migrated off-site. These concerns were exacerbated when it became apparent that groundwater contamination was impacting off-site potable water wells. Tallevast residents raised concerns that they were being exposed to contamination and that they were never properly notified by the Department, upon the initial discovery of the groundwater contamination. Tallevast residents were also concerned about whether the Department had failed to properly notify then once it was discovered the groundwater contamination had migrated off-site. The problems experienced at Tallevast emphasized to the Department the need to explore available avenues to enhance public notification procedures as a whole.4, 5 The Department asserted as to a reasonable basis in fact for the proposed rules, that contamination affecting Tallevast residents provided an impetus for the Department in May 2004 to address notification of contamination to affected off-site property owners. The situation in Tallevast arose because well surveys failed to indicate the extent of the contamination plume and that residents were using private wells for potable water. The Department's objective was to make sure that if there was exposure potential, the potentially affected parties should be notified. The Department seems to agree that the failure to discover the contamination of the potable wells in Tallevast occurred during the assessment phase of the cleanup and that it had not yet gotten to the stage of determining the remediation strategy. (T 45-46). The Department's stated concerns regarding Tallevast are not specifically addressed by proposed rule 62-770.220(3)(b) and (4). (T 74-75, 95-96). The Department’s procedure for granting a temporary extension of the point of compliance is that the responsible party will propose such an extension in its remedial action plan. (The four cleanup programs provide for the establishment of a TPOC.) The Department will then issue its notice of intended agency action, notice of the agency action will be provided to the enumerated persons, and the persons receiving notice will have a 30-day comment period. (T 149-155). (Pursuant to proposed rule 62-770.220(3)(a), the person responsible for site rehabilitation (PRSR) "shall provide" actual notice "to the appropriate County Health Department and all record owners of any real property into which the point of compliance is allowed to extend . . . ." In this regard, as Mr. Chisolm testified, the process is "similar to a permit.") Mr. Sole testified that, in the course of rulemaking, Florida Petroleum argued to the Department that the "petroleum statute under 376.3071 is different as it addresses the temporary point of compliance. It's not as prescriptive as the other statutory provisions for Risk-Based Corrective Action and the dry-cleaning, the Brownfields, and now the Global RBCA [statutes]. And their concern was that because it's not as prescriptive, [the Department] should not be establishing these additional notice provisions, such as constructive notice . . . But their fear was or concerns . . . were that you're going to engender a lot of litigation that's unnecessary because, as soon as you say the word 'contamination,' somebody is going to want to sue me . . . . And I understood that position. But at the same time, the lessons that we learned were that failure to provide that notice, unfortunately, can cause exposure and can cause a public health concern; and [the Department] needed to balance the two." (T 63-64, 122). Mr. Chisolm testified, in part, about the development of the constructive notice provision in proposed rule 62- 770.220(3)(b) and explained that the global RBCA, brownfields, and drycleaning solvent statutes required constructive notice to residents and business tenants of impacted properties.6 Mr. Chisolm further explained: So, if you're going to give notice to the legal owners of a piece of property, many cases there are tenants there. And they may not get the word, and they may be the ones that are drinking the water. The same with business tenants. So the idea was let's give notice to the people who are going to be or potentially going to be affected by this contamination, which is, after all, under the property which they may be inhabiting and using. So that was the purpose for the rule change in this case. Let's give notice to everybody who could potentially be affected by the rule, by the contamination beyond the property boundaries . . . . The whole idea behind RBCA, Risk- Based Corrective Actions, is that, if there's no exposure, there's no risk. There's no danger to the individual, to any individual. (T 116-117).
The Issue The issue is whether to approve an application by Respondent, Dan R. Hughes Company, L.P. (applicant or Hughes), for an oil well drilling permit authorizing the drilling of an exploratory oil well in Collier County, Florida.
Findings Of Fact The Parties Mosher resides on a three-acre lot at 4695 26th Avenue Southeast, Naples, Florida. His residence is around 2,500 feet west of the proposed wellsite, but Mosher says that the eastern edge of his lot "might be 2,000 feet" from the drilling site. He has not, however, measured the actual distance to confirm this assertion. Preserve is a Florida non-profit corporation whose purpose is to educate the public on issues affecting the preservation and protection of the environment, particularly the environment of south and southwest Florida. It was formed in response to Hughes' intention to drill for oil in the area. The corporation is not a membership organization; rather, it has around 25 non-member, active volunteers, six member directors, and an unknown number of donors. Excluding Mosher, the other member directors live between three and ten miles away from the proposed wellsite. The record does not show where the 25 volunteers reside. The corporate representative testified that four directors, including Mosher, regularly use the Florida Panther National Wildlife Refuge (Refuge) to observe wildlife and habitat. However, the public access point to the Refuge appears to be at least several miles from the wellsite. Based upon an email survey, he stated that a "substantial number [around 36] of donors and volunteers utilize the panther refuge," but he was unaware of when, or how often, this occurred. About every six weeks, meetings are conducted at Mosher's home, which are attended by some, but not all, of the directors and volunteers. Schwartz's primary residence is in Lake Worth (Palm Beach County) where he serves as the unpaid executive director of the South Florida Wildlands Association.3 He sometimes provides paid tours in the Everglades and Big Cypress Swamp and has led "numerous" free hikes into panther habitat to look for signs of panthers. These hikes are limited to the hiking trails in the southeast corner of the Refuge, which is the only area that can be accessed by the public. He represented himself as an advocate for the protection of wildlife habitat in the greater Everglades, with a particular interest in the Florida panther. Hughes is a Texas limited partnership engaged in the business of oil and gas exploration, which is registered to do business in the State of Florida. Hughes has applied for a permit to drill an exploratory well for oil in Collier County. If the well is commercially viable, Hughes must apply for an operating permit at a later time. The Department has jurisdiction to issue permits for the drilling and exploring for, or production of, oil under part I, chapter 377. Pursuant to that authority, the Department reviewed the oil and gas well drilling permit application. The Application and Project After the application was deemed complete by the Department, it was distributed for comment to a number of local, state, and federal agencies. While some commented on the application, no agency had any unresolved concerns at the end of the application process. Hughes met all rule requirements for performance bonds or securities, and it provided all information required by rule. The proposed site is located on the southeast corner of an active farm field in the Big Cypress Swamp watershed, just north of a speedway now used as a test track. Surface holes for oil wells are commonly located on farm land, and farm fields are compatible with oil wells. Based upon a mineral lease between Hughes and the owner of the land, Collier Land Holdings, Ltd., Hughes has the right to locate and drill the well at the proposed surface hole location. The Refuge was established by Congress in 1989 to protect the Florida panther and its habitat and is located approximately 20 miles east of Naples. Around 98 percent of the Refuge is closed to any public activity. The project is consistent with the comprehensive conservation plan for the Refuge prepared by the United States Fish and Wildlife Service (USFWS), in that the plan recommends "slant drilling" off of the Refuge. Although Mosher and Preserve argue that the drill hole should be moved further east into wetlands, and Schwartz contends that it should be moved further west away from the Refuge, the proposed location of the drilling pad and project site is reasonable with respect to the nature, appearance, and location of the proposed drilling site. Likewise, the location is reasonable with respect to the type, nature, and extent of Hughes' ownership. The proposed activity can best be characterized as a "resource play," where an operator drills toward a known resource. This is distinguished from a wildcat operation, where the operator is drilling in an unproven area. Hughes proposes to target the rubble zone (i.e., the lower zone) within the lower Sunniland formation, a geologic formation thousands of feet below the ground surface that runs through southwest Florida. Hughes will first drill a vertical pilot hole and then drill horizontally from the hole bottom in a southeast direction toward a formerly drilled oil well known as the Tribal Well. In order to increase the probability of locating commercially available petroleum, Hughes plans to proceed from west to east in order to arrive at a perpendicular direction of existing limestone fractures as the drilling approaches the Tribal Well. When that well was drilled vertically into the rubble zone in the 1970s, oil rose to the ground surface. Thus, the indicated presence of oil is sufficient to warrant and justify the exploration for oil at this location. The proposed depth of the pilot hole is 13,900 feet measured depth (MD/13,900 feet true vertical depth (TVD)), which will allow assessment of the upper Sunniland, lower Sunniland, and Pumpkin Bay Formations. If the evaluation determines that the well will likely be commercially productive, Hughes will complete a 4,100-foot horizontal leg in the lower Sunniland rubble zone with a landing depth at 12,500 feet MD/12,064 TVD and a total depth of 16,600 feet MD/12,064 feet TVD. The footprint for the drilling pad will be 225 feet by 295 feet, or 2.6 acres, with a two-foot earthen berm around the perimeter of the operating area to contain all water on the site. A secondary containment area within the perimeter of the site will be covered by high-density polyethylene to contain and collect any accidental spills. A drilling rig, generators, and other drilling equipment will be on the pad during drilling operations. A maximum of 20 persons will be at the site, and then only for one day of operations. At all other times, Hughes anticipates there will be a five-person drill crew plus support personnel on site. After drilling, Hughes will remove its equipment. Once the access road is built and the equipment put in place, the drilling activities will take place 24 hours per day, seven days per week, and will be completed in approximately 60 to 70 days. The on-site diesel generators will run simultaneously 24 hours per day while drilling is taking place. The pad will be illuminated at night with lights on the drilling derrick and throughout the pad. Construction of the drilling pad will require trucking around 12,000 to 14,000 cubic yards of fill to the drilling location. Additional traffic for bringing in fill, piping, and related equipment will occur, but the exact amount of traffic is unknown. The South Florida Water Management District (SFWMD) previously approved an environmental resource permit (ERP) to allow the construction and operation of a surface water management system on Camp Keais. The United States Army Corps of Engineers (USACE) also permitted the same system under the Clean Water Act. The latter permit requires mitigation for wetlands and Florida panther habitat compensation. Based on the proposed wellsite, the SFWMD modified the ERP to allow a culvert and access to the proposed wellsite. In addition to the oil drilling permit application, Hughes has applied for two water well drilling permits from the SFWMD, and an injection well drilling permit. Petitioners and Intervenor's Objections The challengers have raised a number of objections that they assert require denial of the application. Conflicting testimony was presented on these issues, which has been resolved in Respondents' favor as being the more credible and persuasive testimony. Mosher and Preserve Mosher and Preserve raise two broad objections. First, they contend that hydrogen sulfide gas (H2S) is likely to be encountered in the drilling of the proposed well. They further contend that the H2S contingency plan submitted by Hughes is not sufficient to evacuate the public in the event of an incident where H2S is uncontrollably released under pressure. Second, they contend that the Committee did not review the application under the process contemplated by section 377.42(2). Except for these two objections, they agree that no other issues remain. See TR., Vol. I, p. 33. Within the petroleum industry, drilling operators create H2S plans when there is reason to believe that the operator may encounter H2S while drilling. This practice is codified in Florida Administrative Code Rule 62C-27.001(7), which requires a contingency plan only when H2S is "likely" to be encountered while drilling. The plan must "meet generally accepted industry standards and practices," and it must contain measures "for notifying authorities and evacuating civilians in the event of an accident." Id. See also rule 62C-26.003(3), which requires a contingency plan "if appropriate." The plan is prepared for two main users: the personnel working at the drilling site; and local emergency management officials, who must plan and train for the implementation of emergency activities. The parties agree that the "generally accepted industry standards and practices" for the oil and natural gas industry are found in the operating standards and recommended practices adopted by The American Petroleum Institute (API), a trade association for the oil and natural gas industry. Recommended Practice 49 (API 49) is the generally accepted industry standard for oil and gas drilling operations likely to encounter H2S and was relied upon by all parties throughout the hearing. The standard includes guidance on personnel protection measures, personnel training, personnel protection equipment, and community contingency planning. API 49 recommends the use of a community warning and protection plan when atmospheric H2S exposures beyond the well site could exceed potentially harmful exposure levels and could affect the general public. Mosher/Preserve's expert opined that H2S might be encountered at levels as high as 21 percent (210,000 parts per million (ppm)) in southwest Florida, and that "it's quite likely" H2S would be encountered at the proposed wellsite. At the same time, however, he agreed with the assessment of Respondents' experts that the likelihood of encountering H2S at this site was merely "possible," "sporadic," and "unlikely," and that there was "zero" potential of a severe H2S release under high pressure. Florida has two major oil producing areas: the Sunniland Trend in southwest Florida and the Smackover formation near Jay, Florida, in the northwest part of the state. Unlike the Smackover formation which has higher temperatures and pressures and a high concentration of H2S, the Sunniland Trend has normal temperatures and pressures and a sporadic presence of H2S. Less than two percent of wells in southwest Florida have been reported to contain H2S, and those reports relate to production wells where bacteria (biological contamination) was likely introduced into the formation during production. Of over 300 oil wells drilled in southwest Florida, only six were reported to have encountered H2S. Notably, the Tribal Well, located 1.5 miles to the southeast of the proposed site, encountered relatively low pressure during drilling and had no H2S, and another well located 12 miles to the north likewise had no high pressure or H2S. It is unlikely that Hughes will encounter high pressure or H2S if it drills at the proposed site. Even though it is unlikely that high pressure or H2S will be encountered during the drilling of this proposed well, Hughes still submitted an H2S contingency plan as part of the drilling application. The Department determined the plan provided an effective design to detect, evaluate, and control any hazardous release of H2S. In response to public concerns, in January 2014 Hughes revised its plan to provide more protections. The revised plan exceeds the guidance provided in API 49. The revised plan clarifies and adds multiple protections, including implementing the plan at a vertical depth of 9,000 feet, which is 2,700 feet before the zone that Mosher claims could contain H2S; clarifying that an H2S alarm notification at 15 ppm would result in an instant well shut-in (i.e., closure of the well) to prevent the escape of H2S; instituting a reverse 911 call system to allow local officials to notify the public by telephone of any incident; creating an air dispersion model to understand the likelihood of public exposure; and adding H2S scavengers to the drilling mud. Adding H2S scavengers in the mud is a protective measure. Specifically, the zinc oxide scavengers will react with H2S to create benign zinc sulfide and water. Even if H2S is present in the formation, the H2S scavengers will neutralize the H2S before it could reach the surface. The H2S scavengers will effectively eliminate the likelihood of H2S escaping from the well during drilling operations. The drilling plan requires the Trinity C formation (which Hughes estimated will begin at a depth of around 11,850 feet) to be cemented off and sealed once drilled. This formation will not be encountered in the first 15 or 20 days of drilling. Once encountered, the formation will be exposed for only four to six days. Even if H2S were encountered during this short exposed duration, all of the protections included in the revised plan would be in place, including overbalanced drilling mud, H2S scavengers, blowout preventers, H2S monitors, and alarms. When wells are drilled, there are numerous personnel monitoring the drilling fluid, or mud, which is designed not only to carry cuttings to the surface, but more importantly to act as a barrier to keep fluids or gasses in the geologic formation. The mud is weighted with additives to combat reservoir pressures. Drill operators want the same amount of mud pumped into the hole as the amount flowing back up. If more fluid is flowing back up, then the mud is not heavy enough to hold back the fluids or gasses encountered. If this imbalance occurs, the well is shut- in immediately and the mud weight is adjusted. A shut-in can be accomplished in just a few seconds. Anything in a shut-in well will stay in the well. Hughes' normal drilling plan is to slightly overbalance the mud weight. This ensures that nothing unintentionally escapes from the reservoir. Mosher and Preserve contend that if H2S is encountered, dangerous concentrations of H2S would leave the wellsite. In response to this type of concern, as part of the revised plan, Hughes conducted an air dispersion model using the methodology provided by API 49. The API 49 model is a Gaussian model with default values reflecting the worst-case exposures. The peer- reviewed and conservative model calculated by Dr. Walker looked at H2S concentrations of 10, 15, and 100 ppm. At the extreme case, a 100-ppm release at the well would be reduced below 10 ppm within about 20 feet from the well and further reduced to one ppm within 60 feet from the well. Although H2S is unlikely to escape the well, 100 ppm was selected as a precautionary level because this level is an immediate danger to human life and health. Reaching 100 ppm is highly unlikely because at an instantaneous reading of 15 ppm, the well is immediately shut-in. The air dispersion model results demonstrate that atmospheric H2S exposures beyond the wellsite could not exceed potentially harmful exposure levels nor could exposures affect the general public. Thus, even though the plan includes a community warning and protection provision, it is not required under API 49. In an abundance of caution, however, the plan provides for a public notification zone of 2,000 feet in case of an H2S release. This zone is two orders of magnitude beyond the 20- foot, 10 ppm distance dispersion of H2S based on the modeled worse case release and exceeds any required notification zones in other states. The notification boundary is conservative, as compared with industry standards. While Mosher's expert recommended more stringent standards than API 49, he knew of no contingency plan for an oil drilling permit in the United States that included his recommended standards. Mosher's expert testified that based on his review of literature, the lowest observable adverse effect from H2S was at concentrations of 2.1 ppm. Based on a worst case scenario release of 100 ppm of H2S, the gas would disperse to a concentration of 2.1 ppm in less than 40 feet from the well. The property boundary abutting the neighborhood to the west is over 800 feet from the well. API 49 expressly provides that wellsite personnel should be provided protection devices if concentrations of H2S exceed 10 ppm for an eight-hour time-weighted average. The revised plan requires wellsite personnel to don a self-contained breathing apparatus if the monitors encounter an instantaneous reading of 10 ppm H2S. Instantaneous readings are more protective of human health than the time-weighted averages proposed by Mosher's expert. Using an instantaneous trigger is another area where the revised plan exceeds the recommendation of API 49. The greater weight of evidence demonstrates that the H2S contingency plan meets or exceeds guidance of API 49. The revised plan requires hands-on training for public officials and fire/rescue staff before reaching the depth of 9,000 feet. The revised plan further requires hands-on training and drills related to the procedures for use, and location of, all self- contained breathing apparatus and evacuation procedures. The plan is a complete and accurate contingency plan that will assist operators and local emergency management in the unlikely event of an H2S escape. It exceeds the degree of caution typically employed in industry standards. Mosher and Preserve contend that the plan fails to include specific instructions and training for nearby residents in the event of an emergency. However, emergency plans are designed for use by operators at the facility and the local emergency management officials rather than nearby residents. Thus, the Department did not require the applicant to provide specific instructions for those residents. Mosher and Preserve also contend that the plan fails to adequately describe the evacuation routes in the event of an emergency. However, evacuation routes and the potential closure of roads are normally in the domain of local governments, as the operator and Department have no control over this action. Mosher and Preserve contend that the plan does not include complete and accurate information for all property owners in the area. This is understandable since some property owners either failed to respond to inquiries by Hughes when it assembled the information for the plan or were reluctant to provide any personal information. Recognizing this problem, the Department reviewed the website of the Collier County property appraiser to complete the information. To the extent information on certain parcels may not be complete, Hughes can update that aspect of the plan on an on-going basis before operations begin. If a permit is issued, the Department will continue to coordinate with Collier County and other local emergency management officials for the purpose of planning to implement the contingency plan. Based on the foregoing, the evidence establishes that the probability of a dangerous release of H2S beyond the wellsite is highly remote and speculative in nature. The revised contingency plan is consistent with industry standards and satisfies the requirements of the rule. Schwartz Like Mosher and Preserve, Schwartz agreed that except for the concerns expressed in his amended pleading, no other issues remain. Schwartz first contends that Hughes did not demonstrate sufficient efforts to select a proposed location for drilling to minimize impacts as required by rule 62C-30.005. Subparagraph (2)(b)1. requires that drilling sites be located "to minimize impacts on the vegetation and wildlife, including rare and endangered species, and the surface water resources." In particular, Schwartz is concerned about the potential impact on the Florida panther, an endangered species. Hughes selected the proposed site primarily because of its proximity to the Tribal Well, which had a significant show of oil. In order to increase the chances for commercial production, the horizontal segment of the well needs to be perpendicular to the natural fractures in the limestone. In this location, Hughes must drill horizontally from west to east in the direction of the Tribal Well. Hughes was unable to locate the well on the automotive test track directly south of the agricultural field and west of the Tribal Well because of objections by Harley-Davidson, then the owner of the track. A second proposed location just east of the test track was considered but Harley-Davidson would not grant access from the track to the upland sites on the adjacent location. A third option was to construct a lengthy access road from the north to one of the upland sites just east of the test track. However, this alternative would have resulted in significant impacts to wetlands and native vegetation. The proposed site offers the least amount of environmental impact. It is 1.5 miles from the Tribal Well. It has no federal or jurisdictional wetlands on the site, and groundwater modeling submitted with an application for a water use permit demonstrated that the proposed use of water will not adversely affect surrounding wetlands. The proposed access road and drilling pad will not impact any cypress-mixed forest swamps, hardwood hammocks, mangrove forests, archeological sites, or native ceremonial grounds. Nor will they adversely affect known red-cockaded woodpecker colonies, rookeries, alligator holes, research sites, or pine uplands. The evidence establishes that Hughes chose a site that minimized environmental impacts. Schwartz also contends that the wellsite activities will directly decrease the recovery chances of the Florida panther. According to Schwartz, this decrease will occur because the activities involve creating an access road, truck traffic, noise, lights, and vibrations. He also asserts that the proposed wellsite will result in a small amount of direct habitat loss when the cattle field is converted to a drilling pad. The USFWS has developed a panther scientific habitat assessment methodology. It relies upon peer-reviewed studies that found that panthers will select land cover types while avoiding others. The methodology ranks the value of land cover types from zero to ten based on the potential for panther selection. Applying the USFWS' scoring to the proposed wellsite, an improved pasture area has a value of 5.2, which means the land cover is neither actively selected nor avoided by panthers. The areas to the south and east of the proposed wellsite are forested wetlands and forested uplands, which have substantially higher values that range from 9.2 to 9.5. If converted to an open water reservoir under the Camp Keais ERP, the site value would be zero, the land cover type most avoided by panthers. The underlying USACE permit specifically required panther habitat compensation. Hughes' expert established that the proposed site minimizes impacts on wildlife by avoiding habitat selected by panthers such as wetlands, forested uplands, saw palmetto thickets, fresh water marshes, prairies, and native habitats. Based on a dozen visits to the site for the purpose of conducting vegetation mapping and wildlife surveys, the expert concluded there are no panthers currently known to be living, breeding, or denning on the site. A home range for a panther is the area providing shelter, water, food, and the chance for breeding. The typical home range for a male panther is 209 square miles, and female home ranges average around 113 square miles. The evidence establishes the proposed drilling activity will not interfere with the panthers' use of the site. Approval of the permit will not remove or push any panthers out of their home range. Hughes' expert opined that the four male panthers, which historically traversed the area within a mile of the proposed wellsite, would only likely move through the area every 15 or 20 months or longer. The temporary nature of the drilling activities means the panthers may not even be near the location during that time. If a panther is near the location and frightened by any activities, it will avoid the area, but will eventually return. Based on the large home range of the panther, the temporary activities will not increase the likelihood of intraspecies aggression or decrease panther survivability. The more persuasive evidence is that panthers are adaptable. They are habituated to the drilling operations in southwest Florida based on over a hundred thousand telemetry data points taken near 93 oil wells in the primary zone. Panthers are not threatened by the presence of humans. In fact, they live and den in and around residential communities and active agricultural operations. Panthers need prey, water, and shelter. The drilling activities will not adversely affect prey availability or impact water resources. The proposed wellsite's location within a disturbed agricultural field will not impact the panther's ability to shelter. During the permit review process, the Department requested input from the USFWS, the Florida Fish and Wildlife Conservation Commission (FFWCC), and other interested parties regarding the proposed drilling permit. No formal comments were offered by the USFWS, and its biologist for conservation planning indicated informally that the surface impacts from an oil well are "very minor." Likewise, the FFWCC offered no formal comments on the application. The evidence supports a finding that the proposed permit activities will not affect the panther's use of, or travel to and from, the Refuge. The activities will not affect the panthers' availability of prey or increase panther competition for food or home range territory. The drilling will not adversely affect the panther's breeding, survivability, or the recovery of the species. The only other threatened or endangered species found in the vicinity of the proposed site was an eastern indigo snake, which was located two and one-half miles away and would not travel to the proposed wellsite, as its home range is up to a maximum of 450 acres. Schwartz further contends that section 377.242 requires that the permit be denied because the proposed wellsite is within one mile from the seaward (western) boundary of the Refuge. The Refuge is located entirely inland and does not have a seaward boundary, as contemplated by section 377.242(1)(a)3. Therefore, no drilling will be located within one mile of the seaward boundary of any state, local, or federal park, aquatic preserve, or wildlife preserve. This is consistent with the Department's routine and long-standing interpretation of the statute. Big Cypress Swamp Advisory Committee Petitioners and Intervenor initially contended that the permit should be denied because a meeting of the Committee was never convened pursuant to section 377.42. The Committee, however, met on March 11 and 31, 2014. Although a majority of the Committee voted to recommend that the Department deny the permit on various grounds, the recommendation of the Committee is not binding on the Department, and after consideration, was rejected. In their Proposed Recommended Orders, the opponents now contend that the permit should be denied because the Committee did not meet before the Department issued its proposed agency action. For the reasons stated in the Conclusions of Law, this contention is rejected.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department enter a final order issuing Permit No. 1353H, without further modifications. DONE AND ENTERED this 3rd day of June, 2014, in Tallahassee, Leon County, Florida. S D. R. ALEXANDER Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 3rd day of June, 2014.
