The Issue Whether or not the agency may, pursuant to Section 525.06 F.S., assess $390.04 for sale of substandard product due to a violation of the petroleum inspection laws and also set off that amount against Petitioner's bond.
Findings Of Fact Coleman Oil Co., Inc. d/b/a Shell Oil Co. at I-75 and SR 26 Gainesville, Florida, is in the business of selling kerosene, among other petroleum products. On November 15, 1990, Randy Herring, an inspector employed with the Department of Agriculture and Consumer Services and who works under the direction of John Whitton, Chief of its Bureau of Petroleum, visited the seller to conduct an inspection of the petroleum products being offered for sale to the public. Mr. Herring drew a sample of "1-K" kerosene being offered for sale, sealed it, and forwarded it to the agency laboratory in Tallahassee where Nancy Fisher, an agency chemist, tested it to determine whether it met agency standards. The testing revealed that the sampled kerosene contained .22% by weight of sulfur. This is in excess of the percentage by weight permitted by Rule 5F- 2.001(2) F.A.C. for this product. A "Stop Sale Notice" was issued, and on the date of that notice (November 20, 1990) the inspector's comparison of the seller's delivery sheets and the kerosene physically remaining in his tanks resulted in the determination that 196 gallons of kerosene had been sold to the public. Based on a posted price of $1.99 per gallon, the retail value of the product sold was determined, and the agency accordingly assessed a $390.04 penalty. The agency also permitted the seller to post a bond for the $390.04 on November 21, 1990. The assessment is reasonable and conforms to the amount of assessments imposed in similar cases.
Recommendation Upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Agriculture and Consumer Services enter a final order approving the $390.04 assessment and offsetting the bond against it. DONE and ENTERED this 25th day of April, 1991, at Tallahassee, Florida. ELLA JANE P. DAVIS, Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 25th day of April, 1991. COPIES FURNISHED TO: CLINTON H. COULTER, JR., ESQUIRE DEPARTMENT OF AGRICULTURE AND CONSUMER SERVICES 510 MAYO BUILDING TALLAHASSEE, FL 32399-0800 MR. RANDAL W. COLEMAN COLEMAN OIL COMPANY POST OFFICE BOX 248 GAINESVILLE, FL 32602 HONORABLE BOB CRAWFORD COMMISSIONER OF AGRICULTURE THE CAPITOL, PL-10 TALLAHASSEE, FL 32399-0810 RICHARD TRITSCHLER, GENERAL COUNSEL DEPARTMENT OF AGRICULTURE AND CONSUMER SERVICES 515 MAYO BUILDING TALLAHASSEE, FL 32399-0800
The Issue As stated by the Administrative Law Judge in his Recommended Order, the issue presented is: "whether the Petitioner waived its right to a hearing by failing to request a hearing within the period of time described in the Notice to Show Cause."
Findings Of Fact After review of the record in its entirety, it is determined that the Administrative Law Judge's Findings of Fact found in paragraphs 1 through 9 of the Recommended Order are supported by the record and are accepted and incorporated as if fully set forth herein.
Conclusions This proceeding was initiated by a request for a formal administrative hearing filed by Petitioner, SHELL OIL COMPANY (hereinafter SHELL), challenging the Violation and Notice to Show Cause issued by the Respondent, DEPARTMENT OF TRANSPORTATION (hereinafter DEPARTMENT), regarding SHELL'S driveway connection to State Road 7 in Dade County, Florida. This matter was referred to the Division of Administrative Hearings (DOAH) for a formal hearing on October 21, 1997. On October 27, 1997, DOAH issued its Initial Order assigning the case to Michael M. Parrish, a duly appointed Administrative Law Judge, and setting forth the responsibilities of the parties. The hearing was scheduled for January 29, 1998, in Miami, Florida. An Order Granting a Motion for Continuance was issued on December 19, 1997, rescheduling the hearing for March 19, 1998. On March 5, 1998, the hearing was again continued. The hearing was held on May 14, 1998, by telephone. Appearances on behalf of the parties were as follows: For Petitioner: John Lukacs, Esquire Lukacs & Lukacs, P.A. 1825 Coral Way, Suite 102 Miami, Florida 33145 For Respondent: Paul Sexton, Esquire Chief Administrative Law Counsel Brian F. McGrail, Esquire Assistant General Counsel Department of Transportation 605 Suwannee Street, Mail Station 58 Tallahassee, Florida 32399-0458 Stipulated Facts were filed prior to hearing with three exhibits attached. The deposition of Ingrid Birenbaum, the DEPARTMENT'S District Six Permits Engineer at the time the Notice to Show Cause was issued, was filed with DOAH together with exhibits introduced at the deposition. A transcript was prepared and filed subsequent to the hearing. By agreement of the parties, no witnesses were presented and the Stipulated Facts with the three exhibits attached and the deposition of Ingrid Birenbaum constituted the record in this case for the purpose of disposing of the limited issue of timeliness. On June 22, 1998, the DEPARTMENT filed its Proposed Recommended Order and SHELL filed its Findings of Fact, Conclusions of Law and Recommended Order. On July 21, 1998, the Administrative Law Judge issued his Recommended Order. Exceptions to the Recommended Order were filed by SHELL on August 5, 1998, and the DEPARTMENT filed its response to the exceptions on August 17, 1998. Thereafter, SHELL filed a reply to the DEPARTMENT'S response to the exceptions, the DEPARTMENT filed a motion to strike the reply as unauthorized, and SHELL filed a response to the motion to strike.
Appeal For This Case THIS ORDER CONSTITUTES FINAL AGENCY ACTION AND MAY BE APPEALED BY ANY PARTY PURSUANT TO SECTION 120.68, FLORIDA STATUTES, AND RULES 9.110 AND 9.190, FLORIDA RULES OF APPELLATE PROCEDURE, BY FILING A NOTICE OF APPEAL CONFORMING TO THE REQUIREMENTS OF RULE 9.110(d), FLORIDA RULED OF APPELLATE PROCEDURE, BOTH WITH THE APPROPRIATE DISTRICT COURT OF APPEAL, ACCOMPANIED BY THE APPROPRIATE FILING FEE, AND WITH THE DEPARTMENT'S CLERK OF AGENCY PROCEEDINGS, HAYDON BURNS BUILDING, 605 SUWANNEE STREET, M.S. 58, TALLAHASSEE, FLORIDA 32399- 0458, WITHIN THIRTY (30) DAYS OF RENDITION OF THIS ORDER.
The Issue Whether Petitioner's service station site known as Siesta Key Exxon Village, at 5201 Ocean Boulevard, Sarasota, Florida, is eligible for state administered cleanup pursuant to Section 376.3071(9), Florida Statutes.
Findings Of Fact Weeks Oil Company, Inc., owns and operates a service station, Siesta Key Exxon, located at 5201 Ocean Boulevard, Sarasota, Florida. On December 21, 1988, Petitioner applied, pursuant to the Early Detection Incentive Program (EDI), for state assistance due to a suspected discharge of gasoline at the facility. The application indicated that a manual test of a monitoring well, conducted on December 16, 1988, detected contamination. After free product was discovered in the monitoring wells in December, 1988, subsequent monitoring well reports for the months of January - May, 1989, indicated the presence of free petroleum product. The January, 1989, monitoring report indicates six inches of free product; the February, 1989, monitoring report indicates twelve inches of free product; the March, 1989, report failed to indicate the presence of free product; and both the April and May, 1989, monitoring reports indicate the presence of sixteen inches of free product. Purity Well Company, the monitoring well contractor retained by Weeks Oil, bailed free product out of the monitoring wells once a month during the period January through May, 1989. On May 23, 1989, Richard Steele of the Sarasota County Pollution Control Division conducted an Early Detection Incentive Program Inspection at Siesta Key Exxon, 5201 Ocean Boulevard, Sarasota, Florida, DER Facility #588521170. During the inspection, Mr. Steele examined the monitoring well reports for Siesta Key Exxon for the months of January through May, 1989. Evidence of contamination was indicated by each month's monitoring well report, and the amount of free product indicated by the monitoring well reports increased over time. During the May 22, 1989, inspection, Mr. Steele observed a minimum of two feet of free product in monitoring well number three. As part of the Early Detection Incentive Program inspection, Mr. Steele requested inventory records for Siesta Key Exxon, which records were provided on June 7, 1989. Inventory records for January, February, March and April, 1989, indicated a total shortage of 441 gallons of gasoline. Mr. Steele's inspection report of May 22, 1989, indicates that no initial remedial action other than the bailing of monitoring wells occurred subsequent to the December, 1988, EDI application. During the May 22, 1989, inspection, Mr. Steele was neither provided with any evidence of repairs to the petroleum storage system made for the purpose of acting upon monitoring well reports, nor did he visually observe any evidence of repair. By letter dated May 24, 1989, from Richard Steele to Weeks Oil Company, Mr. Weeks was informed of the presence of two feet of free product in monitoring well number three and specifically requested a tank tightness test. The May 24, 1987, letter requested Mr. Weeks to send the results of the tank tightness test to the Sarasota County Pollution Control Office or the Department of Environmental Regulation district office. Mr. Weeks discussed with Steele the fact that the contaminants appeared to come from tanks no longer in service, which tanks were scheduled for relining. Mr. Weeks did not consider it practicable to test tanks scheduled for relining and thought Steele agreed that he could delay the testing until the tanks were refitted. Mr. Steele never made such a commitment, and the tank test was never conducted. On October 20, 1989, the tanks at Siesta Key Exxon were excavated and fiberglass coated. The August 22, 1989 ineligibility determination cites as the reason for denial, the failure of Weeks Oil to conduct a tank tightness test as requested by Sarasota County or otherwise immediately investigate and repair the contamination source as required by Chapter 17-61, Florida Administrative Code, The ineligibility letter concludes that failure to immediately investigate and repair the contamination source as required by Chapter 17-61, Florida Administrative Code, shall be construed as gross negligence in the maintenance of a petroleum storage system, which precludes participation in the Early Detection Incentive Program. A tank tightness test should be performed by the owner or operator of a petroleum storage system where there are any discrepancies in inventory records or monthly monitoring system checks. Rule 17-61.050(4)(c) 3., Florida Administrative Code, requires upon discovery of an inventory discrepancy that investigation of the system "shall not stop until the source of the discrepancy has been found, the tank has been tested, repaired, or replaced, or the entire procedure has been completed." Pursuant to Rule 17-61.050(6), Florida Administrative Code, the owner or operator of a storage system shall test the entire storage system whenever the Department has ordered that such a test is necessary to protect the lands, ground waters, or surface waters of the state. Specifically, the Department may order a tank test where a discharge detection device or monitoring well indicates that pollutant has been or is being discharged. Given the inventory record discrepancy and the amount of free product continually observed in the monitoring wells at Siesta Key Exxon, it was appropriate for Mr. Steele to request a tank tightness test. The bailing of a contaminated monitoring well is not an appropriate method of determining the source of petroleum contamination. The failure of Weeks Oil Company, Inc., to timely conduct a tank test as requested by Sarasota County, acting on behalf of the Department, creates a risk of or the potential for greater damage to the environment because a continual unchecked discharge leads to the release of more petroleum product into the environment.
Recommendation Based on the foregoing, it is hereby RECOMMENDED that the Department of Environmental Regulation enter a Final Order denying the application of Petitioner to participate in the Early Detection Incentive Program. ENTERED this 3rd day of May, 1990, in Tallahassee, Florida. K. N. AYERS, Hearing Officer Division of Administrative Hearings The Desoto Building 1230 Apalachee Parkway Tallahassee, FL 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 3rd day of May, 1990. COPIES FURNISHED: Janet D. Bowman, Esquire Department of Environmental Regulation Twin Towers Office Building 2400 Blair Stone Road Tallahassee, FL 32399-2400 James B. Weeks, Jr. Weeks Oil Company Post Office Box 100 Sarasota, FL 34230 Dale H. Twachtmann Secretary Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400 Daniel H. Thompson General Counsel Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400
The Issue Whether the Petitioners are eligible for restoration coverage under the Abandoned Tank Restoration Program (ATRP) with regard to the remediation of petroleum contamination at DEP Facility No. 588631316, located in Venice, Florida.
Findings Of Fact Upon consideration of the oral and documentary evidence adduced at the hearing, the following relevant findings of fact are made: The Petitioners are the operators of Gulf Car Care (DEP Facility No. 588631316) located at 207 South Tamiami Trail, Venice, Florida. The Department is the agency charged with the responsibility of administering the Abandoned Tank Restoration Program. The Petitioners' ATRP Application was dated May 17, 1992 and received by the Department on June 17, 1992. The Petitioners' ATRP Application indicates that two 2,000-gallon underground storage tanks (UST's) were located at the facility and that one of those tanks was utilized for the storage of diesel fuel while the other tank was utilized for the storage of gasoline. Petitioners' ATRP Application indicates that two 4,000-gallon UST's and two 6,000-gallon UST's were also located at the facility and were utilized for the storage of gasoline. At least some, if not all, of the UST's identified in Petitioners' ATRP Application continued to store petroleum products for consumption, use or sale after March 1, 1990, and in fact, continued to store petroleum products for consumption, use or sale until some time in April, 1990. Petitioner Parr was operated on for colon cancer in late 1989 and Petitioner Homer suffered a heart attack on March 3, 1990. Petitioners contend that because of Petitioner Parr's illness the Petitioners were unable to make a decision to remove the petroleum storage system from service until after March 1, 1990. The petroleum storage system at the facility has been closed in accordance with Department's applicable rules.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is recommended that the Department enter a Final Order denying the Petitioners' application for eligibility or restoration coverage under the Abandoned Tank Restoration Program. RECOMMENDED this day 21st of April, 1994, at Tallahassee, Florida. WILLIAM R. CAVE Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 21st day of April, 1994. APPENDIX TO RECOMMENDED ORDER, CASE NO. 93-6555 The following constitutes my specific rulings, pursuant to Section 120.59(2), Florida Statutes, on all of the proposed findings of fact submitted by the parties in this case. Petitioners, Harold R, Parr and George H, Homer, Sr. Petitioners did not submit any proposed findings of fact per se. However, based on the record, including the testimony of the Petitioners, it does not appear that the Petitioners would disagree with any of the Findings of Fact presented in this Recommended Order. Respondent, Department's Proposed Findings of Fact. 1. The following proposed findings of fact are adopted in substance as modified in the Recommended Order. The number in parenthesis is the Finding(s) of Fact which so adopts the proposed finding(s) of fact: 1(1); 2(3); 3-4(4); 5-6(5); 7- 9(6); 10-11(7) and 12(8). COPIES FURNISHED: Harold R. Parr 913 E. Shanon Court Venice, Florida 34293 George H. Homer, Sr. 3674 Roslyn Road Venice, Florida 34293 W. Douglas Beason, Esquire Department of Environmental Protection Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Virginia B. Wetherell, Secretary Department of Environmental Protection Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Kenneth Plante, General Counsel Department of Environmental Protection Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400
Findings Of Fact Friends of Lloyd, Inc. is a Florida non-profit corporation formed for the purpose of protecting Jefferson County from harmful development. The Council of Neighborhood Associations of Tallahassee/Leon County (CONA) is a non- profit Florida corporation whose members are the neighborhood associations in Leon county; members of those associations reside in 42 Leon County neighborhoods dispersed throughout Leon County. CONA's purposes and goals include protection of the quality of life and environment in Leon County. The Thomasville Road Association's members are principally residents of Leon County. The Association was formed to promote responsible growth management in northern Leon County. None of the Petitioners are owners or "developers" of a Development of Regional Impact within the terms or scope of Chapter 380, Florida Statutes. Rather, Petitioners are members of non-profit organizations interested in the environment and growth management of Leon County. The Department of Community Affairs (the "Department") is the state land planning agency with the power and duty to administer and enforce Chapter 380, Florida Statutes, and the rules and regulations promulgated thereunder. Sections 380.031(18), and 380.032(1), Florida Statutes (1987). Texaco is a business entity that proposes to develop a "tank farm" near the community of Lloyd in Jefferson County, Florida. The Texaco tank farm is a "petroleum storage facility" as that term is used in Rule 28-24.021, F.A.C. Colonial is a business entity that proposes to develop a petroleum pipeline that will connect to the Texaco tank farm. The pipeline is designed to carry and contain petroleum products For purposes of standing, the parties have stipulated that certain environmental hazards can reasonably be expected to occur as a result of the existence of the pipeline/tank farm. No competent evidence was submitted regarding those hazards. As a result of the stipulation, Petitioners have each established injury-in-fact so that they are "adversely affected" by the challenged rule to an extent sufficient to confer upon them standing to maintain this action under Section 120.56, Florida Statutes. On September 7, 1989, one of the Petitioners sent Respondent a letter suggesting that the proposed tank farm development to be built in Jefferson County should be required to undergo review as a DRI. Enclosed with the letter was a proposed circuit court complaint pursuant to Section 403.412(2)(c), Florida Statutes. Petitioner expressed its intention of filing this circuit court action, but first provided Respondent a copy of the proposed complaint in accordance with the provisions of Section 403.412, Florida Statutes. In two letters dated September 8 and 25, 1989, Petitioner supplied additional information to Respondent concerning the tank farm project and contended that in making its determination as to whether the development must undergo DRI review, Respondent should consider the storage capacity of both the tank farm and the pipeline. On October 9, 1989, Respondent answered Petitioner's first letter, and stated that the proposed project was not required to undergo DRI review because the total storage capacity of the tanks was only seventy-eight percent (78%) of the threshold set out in Chapter 28-24, F.A.C. On October 13, 1989, Respondent answered Petitioner's second and third letters, stating that with respect to the pipeline, it has been long standing departmental policy to interpret "storage facilities" as meaning only the tanks, not the pipeline, when determining whether petroleum storage facilities meet the DRI thresholds set out in Chapter 28-24. The proposed tank farm would have nine tanks with a total capacity of 155,964 barrels, which is, as Respondent determined in its letters, approximately seventy-eight percent (78%) of the applicable DRI threshold for "petroleum storage facilities" set forth in Chapter 28-24, F.A.C. The proposed pipeline's capacity over its approximate forty-five mile length from Bainbridge, Georgia to the tank farm is approximately 34,000 barrels. The proposed pipeline's volume flow capacity from the Florida/Georgia state line to the site of the prosed tank farm is approximately 13,500 barrels over approximately 18 miles. If the pipeline's volume capacity from Bainbridge, Georgia is added to the tank farm's volume capacity, the resulting project would be approximately ninety-five percent (95%) of the applicable DRI threshold in Chapter 28-24. If the pipeline's volume capacity from the state line is added to the tank farm's volume capacity, the resulting project would be approximately eighty-five percent (85%) of the threshold. In either instance, the project would exceed the eighty percent (80%) threshold that may require it to undergo DRI review although the project would be Presumed not to be a DRI under the Statute. The Department does not require developments outside Chapter 28-24's enumeration to undergo DRI review. The Department has never treated petroleum Pipelines as "petroleum storage facilities," or as otherwise subject to DRI review. On Several occasions, the Department has applied the petroleum storage facility guideline and standard to petroleum tank farms without determining whether a pipeline was attached to the tank farm. On one prior occasion, the Department has explicitly stated that Petroleum Pipelines are not subject to DRI review. The Petitioners contend that Department's Position that pipelines are not "petroleum storage facilities" is an invalid policy because it has not been adopted as a rule. There is no dispute the Department's Position on this issue has not been promulgated as a rule. If a facility were represented to be a Petroleum pipeline, but was actually designed as and operating as a petroleum storage facility, the Department would apply the Petroleum storage facility DRI guideline and standard to that facility.
Findings Of Fact Prior to July 10, 1984, Son-Mar Propane, Inc. (Son-Mar) was licensed by the Department as a dealer in liquefied petroleum gas, in appliances and in equipment for use of such gas and installation. Virgil Berdeaux was the president of Son-Mar and he and his wife were the sole stockholders. Virgil Berdeaux passed the competency exam which qualified Son-Mar for licensure. Sonny Wade Berdeaux Virgil Berdeaux's son, was the manager of Son-Mar. Son- Mar's business address and place of operation was 16034 U.S. Highway 19 North in Hudson, Florida. Virgil Berdeaux and his wife owned the property located at that address and leased it to Son-Mar. A propane pumping station and a building was located on the property at 16034 U.S. Highway 19. The building housed a pawn shop and supply store for mobile home and RV equipment. Son-Mar operated the pumping station and the stores. It also installed tanks and delivered gas to customers. 1/ On July 10, 1984, a final order was entered by the Department which ordered "[t]hat any and all of [Son-Mar's] licenses issued by the State Fire Marshal Division of Liquefied Petroleum Gas and eligibility to hold said licenses are hereby revoked." The revocation of Son-Mar's licenses was due to its violation of certain safety standards and rules. Specifically, it was found that an employee of Son-Mar, Mr. John Delham, filled a cylinder that had not been recertified, that he lay it horizontally in the customer's van, and that he failed to secure the tank in the van. While the van was still parked at Son-Mar an explosion occurred which destroyed the van and killed its occupant. On July 19, 1984, nine days after Son-Mar's licenses were revoked, Virgil Berdeaux submitted an application for licensure as a dealer in appliances and equipment for use of liquefied petroleum gas, listing the business address as 16034 U.S. Highway 19, Hudson, Florida, and listing the business name as Son- Mar Pawn Shop. On August 3, 1984, twenty-four days after the revocation of Son- Mar's licenses, Sonny Wade Berdeaux submitted an application for licensure as a dealer in liquefied petroleum gas, listing the business address as 16034 U.S. Highway 19, Hudson, Florida. The Department issues several different types of liquefied petroleum gas licenses. A Type 06, Class 02 license, known as a 602 license, is issued to a dealer in appliances and equipment for use of liquefied petroleum gas. The 602 license allows the holder to sell propane appliances and equipment, such as stoves, heaters, and gas grills but it does not permit the holder to install appliances or sell propane gas. A competency examination is not required for this type of license, and there is no inspection of the place of business prior to issuance of the license. Virgil Berdeaux applied for a 602 license. He completed the application and submitted the required fee. The application listed W. C. Johnson, Virgil Berdeaux's son-in-law, as the manager of the business. Bill Johnson had run the pawn shop for Son-Mar. Sonny Wade Berdeaux applied for a Type 06, Class 04 license known as 604 license, which is issued to a dealer in liquefied petroleum gas. This type of license permits the holder to pump liquefied petroleum gas for sale to the public. An applicant for this type of license must pass a competency test and file a surety bond or certificate of insurance. Further, if the licensee has a dispensing station, an inspection of the business location must be performed to ensure that it is in compliance with all safety regulations. Sonny Wade Berdeaux passed the competency examination, filed a certificate of insurance, and submitted the proper fee. Son-Mar held a Type 06, Class 01 license (a 601 license) as a dealer in liquefied petroleum gas, in appliances and in equipment for use of such gas and installation. A 601 license permits the holder to pump liquefied petroleum gas for sale to the public, to sell appliances and equipment for use of liquefied petroleum gas, and to install such appliances and equipment. In essence, it is a combination of a 602 license, a 604 license, and a license to install equipment. Both Sonny Wade Berdeaux and Virgil Berdeaux received letters dated October 8, 1984, which informed them that their applications for licensure had been denied. Both letters referred to the revocation of Son-Mar's licenses and pointed out that the applicants would be operating on the same premises and employing the same staff as Son-Mar. Both letters concluded as follows: Thus, it would appear that your application is seeking licensure for essentially the same entity that has only recently had its liquefied petroleum gas licenses revoked. Therefore, in the interest of public safety, this Bureau cannot permit an Order of Revocation to be obviated by a mere procedural reapplication in your name. The applications for licensure both list the business address as 16034 U.S. Highway 19 in Hudson, Florida. At the time of application Virgil Berdeaux owned that property and Sonny Wade Berdeaux had leased the pumping station. However, on July 1, 1985, the property at 16034 U.S. Highway 19 was sold. The pumping station was moved out along with the inventory that remained in the pawn shop. Neither Virgil Berdeaux or Sonny Wader Berdeaux retained any interest in the property, and at this time neither could operate a business at that location. Although there was testimony concerning the manner in which the business would have been operated and controlled had licensure been granted at the time of applications there was no testimony indicating where or how the business would now be operated. There was no attempt to amend either application to reflect a current business address, and the certificate of insurance entered into evidence lists 16034 U.S. Highway 19, Hudson, Florida, as the location covered. 2/
Recommendation Based on the foregoing findings of fact and conclusions of law; it is RECOMMENDED that a Final Order be entered denying petitioners' applications for licensure. DONE and ENTERED this 21st day of May, 1986, in Tallahassee, Florida. DIANE A. GRUBBS Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 21st day of May, 1986.
Findings Of Fact On March 22, 1977 during a routine inspection of various service stations in Vero Beach, a sample of No. 2 diesel fuel was taken from the pump at English Brothers Truck Stop. Upon analysis at the mobile laboratory the sample was found to be below the minimum flash point for No. 2 diesel fuel and the inspector returned to the station the same day and issued a stop sale notice. (Exhibit 3). Three additional samples were taken, and when analyzed they too were found to be below minimum flash point for this type fuel. Upon receipt of the stop sale notice the station manager notified Respondent. After the fuel had been analyzed at the state laboratory Respondent was notified that since the retail value of the contaminated fuel exceeded $1,000 it could pay $1,000 in lieu of having the fuel confiscated. Respondent owns the fuel at English Brothers Truck Stop until such time as the fuel is removed through the pump for sale. Upon receipt of the notice of the contaminated fuel, which was in one 4,000 gallon tank, Respondent immediately sent three employees to remove the contaminated fuel and clean the tank. Thereafter Respondent attempted to locate the source of the contamination but without success. Since the flash point was lower than allowed for diesel fuel the most likely source of contamination was gasoline which is a higher priced fuel than diesel. Standards used by the Petitioner in determining the required characteristics of fuels are those prescribed by the ASTM. Respondent distributes some 750,000 gallons of diesel fuel per month and this is the first report of contamination of its fuel in the eight and one half years Respondent has been in business.
Findings Of Fact The parties stipulated at hearing to the factual findings set forth in paragraphs 1-5 below. Stipulated Facts The Petitioner has four underground tanks. Two tanks are located at Petitioner's facility in Port Everglades and two tanks are located at Petitioner's facility at Miami International Airport. All four tanks are registered as "stationary tanks" with Respondent. The Petitioner filed a request for reimbursement with the Respondent pursuant to section 376.3071(12)(b), Florida Statutes. The Respondent's denial with regard to the facility at each site was based on "...the fact that this facility is not a petroleum storage system as defined in section 376.301(11), Florida Statutes." Subsequent to the Respondent's denial of the Petitioner's application, the Respondent conducted an additional inspection of the Port Everglades site. The Petitioner timely filed a petition for a formal administrative hearing in response to Respondent's denial. Other Facts Petitioner, Everglades Pipeline Company, is a single, unified pipeline facility. The sole purpose of the system is to transport petroleum product along a route from a receiving pumping station at Port Everglades via a 35 mile pipeline to various terminals and ending at a terminal at the Miami International Airport. The pipeline facility transports 400 to 3000 barrels of petroleum product per hour. The petroleum product transported by Petitioner usually consists of jet A turbine fuel, JP-4 military fuel and railroad diesel fuel. Various pipe lines, not owned or operated by Petitioner, transport petroleum product from major petroleum companies to the Petitioner's receiving station at Port Everglades where the product enters the Petitioner's pipe line facility. The process of placing the petroleum product in the care of Petitioner is known as a "custody transfer." While the product is in Petitioner's custody for purpose of transport to its destination, ownership of the product does not change. At all times, the product remains the property of the company acquiring the Petitioner's transportation service. After transfer to the Petitioner's custody and during the transportation process, tests are constantly performed on the product for the purpose of maintaining quality control. During the testing process, an amount of the petroleum product is withdrawn from the pipeline through a one fourth inch pipe. Samples for testing purposes are then taken from the quantity of the product so removed. The excess of that quantity is channeled to two underground tanks at the Everglades station and temporarily held there for later injection back into the pipeline for delivery, with the same batch of product from which it was drawn, to the recipient at the other end of the pipeline journey. In the Miami station, the same process of withdrawal of a quantity of the product occurs, with two underground tanks there fulfilling the same holding function as that performed by the tanks at the Port Everglades facility. While each of the four tanks have been registered as required by section 376.301(11), Florida Statutes, such registration is not deemed dispositive of whether the tanks are petroleum storage systems since registrations are accepted at face value by the Respondent and no independent verification of registration is made. The two tanks at the Everglades facility have a 2100 gallon, or approximately 50 barrel, capacity. The two tanks at the Miami facility have a 1764 gallon capacity. These four tanks, known as "sump" tanks, perform other functions in addition to temporarily holding amounts of product from which samples are taken. Strainers in the pipeline sometimes become clogged from impurities in the product being transported. When this happens, the product is back washed within the pipeline through the strainers to unclog them. The product used in this back wash operation is then cleansed and placed in the tanks for subsequent re- injection in the pipeline with the batch of product from which it originated. The contaminants are placed in a strainer tank. The strainer tank is necessary for the effective operation of the pipeline. It was conceded in testimony of Petitioner's witness at hearing that this tank is not a petroleum storage system. Maintenance of the system sometimes requires the draining of product from the pipeline into the sump tanks. As soon as the maintenance is completed, the product is re-injected into the pipeline with the batch from which it was drawn. A safe pipeline system requires the existence of the sump tanks to hold maintenance drainage material. The tanks at the Port Everglades station are also used to hold product when pressure builds up in the pipeline system from thermal causes or other conditions which require that pressure in the system be relieved. The product drawn off at these times is re-injected in the pipeline into the batch of product from which it originated. Some form of pressure relief is necessary for safe and effective operation of the pipeline system. The process of reinserting the product back into the pipeline is a manual operation to the extent that personnel are required to open certain valves. The product is not automatically re-injected. However, the sump tanks exist solely to "take care of the individual stations or terminal." While possible to operate the pipeline without the tanks, there is no use or purpose for them except as part of the pipeline facility. An additional tank exists at the Port Everglades station as part of a scavenger system for recovery of product from the ground, but no evidence was presented to show the tank was stationary or registered. The tank is not a petroleum storage system pursuant to section 376.301(11), Florida Statutes. In addition to the two sump tanks, two barrel shaped tanks sit above the ground at the Miami International Airport terminal. These tanks have the capacity to hold 1000 barrels or 42,000 gallons of petroleum product. Neither of these tanks is registered with the Department, nor was evidence introduced that they were otherwise licensed or comply with petroleum storage system requirements of section 376.301(11), Florida Statutes. These barrel tanks were identified at hearing as a relief tank and a settling tank. The relief tank serves the same purpose of providing pressure relief for the system as do the sump tanks at the Port Everglades station. As with the sump tanks, the product is re-injected into the pipeline as soon as the upset condition causing overpressurization is past. The tank also serves to hold certain types of contaminated product until the owner can remove it from the system. The other barrel tank at the Miami station is used as a "settling" tank to filter contaminants from petroleum product. This tank is a treatment or process tank, as opposed to a petroleum storage system. The barrel tanks at the Miami Station, like the sump tanks there and at the Port Everglades station, serve only the product transportation function of the pipeline. They are necessary for safe and effective functioning of that transportation system. Each of the Petitioner's tanks is integrally related to the transportation of product from Port Everglades to Miami. Their sole purpose is the safe and effective functioning of the pipeline. As established by testimony of John Svec, Respondent's expert on petroleum storage facilities, the Petitioner's tanks function for the convenience of the transportation system. The process of taking the product out of the pipe line, holding it, and putting it back into the pipe line is a transportation function. While the Petitioner's tanks temporarily hold petroleum product, they do not store that product in order to provide a supply for future use within the context of that term's use in the field of petroleum marketing. The term "supply" means the buying or selling of product. The Petitioner does not engage in buying and selling. Custody of materials is assumed solely for transportation of that material by the Petitioner's facility. The holding function of the tanks is a part of the overall purpose of the entire pipeline facility to transport petroleum product. Petitioner's exhibit 11 establishes that the original Senate version (Senate Bill 206) of the SUPER Act of 1986 made no mention of pipeline facilities for purpose of inclusion under coverage of the Act. The committee substitute for Senate Bill 206 did include pipelines. This inclusion was carried over to the committee substitute for the committee substitute, only to be deleted from the final enrolled version of the Act.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is RECOMMENDED that a final order be entered denying the Petitioner's application for reimbursement eligibility. DONE AND RECOMMENDED this 17th day of June, 1988, in Tallahassee, Leon County, Florida. DON W. DAVIS Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 17th day of June, 1988. APPENDIX TO RECOMMENDED ORDER, CASE NOS. 87-5374, 87-5305 The following constitutes my specific rulings, in accordance with section 120.59, Florida Statutes, on findings of fact submitted by the parties. PETITIONER'S PROPOSED FINDINGS Included, finding 1 and 6. Included, finding 13. Rejected as unnecessary for result reached. Rejected, unnecessary to result reached. Rejected, unnecessary to result reached. Rejected, unnecessary to result reached. Rejected, unnecessary to result reached. Included in finding 8. Summarily included in finding 11. Summarily included in finding 14. Summarily included in finding 16 with exception of the last two sentences. Testimony on this point indicated holding tanks do provide relief for system pressures. Rejected, unnecessary to result reached. Generally included throughout findings. Not necessary for result reached. Not necessary for result reached. As to manual valves, included in finding 17. Remainder rejected as unnecessary for result reached. Opinion as to tanks rejected as unnecessary to conclusion reached concerning the system. Unnecessary to result reached. Unnecessary to result reached. RESPONDENT'S PROPOSED FINDINGS Unnecessary to result. Unnecessary to result. Unnecessary to result. Included in finding 6. Included in finding 6. Included in finding 6. Included in finding 7. Included in finding 12 and 13. Included in finding 8. Included in finding 14. Included in finding 15. Included in finding 16. Included in finding 17. Included in finding 20. Included in finding 18. Included in finding 19. Included in finding 20. Included in finding 21. Included in finding 23. Included in part in finding 21. Remainder rejected as unnecessary. Included in finding 23. Included in part in findings 23 and 24. Included in finding 24. Included in finding 24. Included in finding 25. COPIES FURNISHED: Richard A. Pettigrew, Esquire Luis R. Figueredo, Esquire 5300 Southeast Financial Center 200 South Biscayne Blvd. Miami, Florida 33131-2339 E. Gary Early, Esquire Department of Environmental Regulation 2600 Blair Stone Road Twin Towers Office Bldg. Tallahassee, Florida 32399-2400 Daniel H. Thompson, Esquire Department of Environmental Regulation Twin Towers Office Bldg. 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Dale Twachtmann Secretary Department of Environmental Regulation Twin Towers Office Bldg. 2600 Blair Stone Road Tallahassee, Florida 32399-2400 =================================================================
The Issue The issue to be determined is whether the applicant, Kanter Real Estate, LLC (Kanter), is entitled to issuance of an Oil and Gas Drilling Permit, No. OG 1366 (the Permit).
Findings Of Fact The Parties Kanter is a foreign limited liability company registered to do business in the State of Florida. Kanter owns 20,000 acres of property in western Broward County, on which it seeks authorization for the drilling of a vertical exploratory well. The exploratory well is to be located on a five-acre site that is subject to an ERP (the Well Site). The Department is the state agency with the power and duty to regulate activities related to the management and storage of surface waters pursuant to chapter 373, Florida Statutes, and to regulate oil and gas resources, including the permitting of activities related to the exploration for and extraction of such resources, pursuant to chapter 377, Florida Statutes. Miramar is a Florida municipal corporation located in Broward County, Florida. Broward County is a political subdivision of the State of Florida with jurisdiction extending to the Kanter property and the Well Site. The Application On July 2, 2015, Kanter submitted its Application for Permit to Drill (Application) to the Department. The proposed Well Site is on land to which Kanter owns the surface rights and subsurface mineral rights. The Application contemplates the drilling of an exploratory well to a depth of approximately 11,800 feet. The Application is not for a production well. The well is to be drilled, and ancillary activities are to be performed on a fill pad of approximately five acres, surrounded by a three-foot high perimeter berm on three sides and the L67-A levee on the fourth. The pad is the subject of an ERP which, as set forth in the Preliminary Statement, is not being challenged. The pad is designed to contain the 100-year, three-day storm. The engineering design incorporates a graded area, berm, and containment with a water control structure and a gated culvert to manipulate the water if necessary. The entire pad is to be covered by a 20 mil PVC liner, is sloped to the center, and includes a steel and concrete sump for the collection of any incidental spills. The pad was designed to contain the full volume of all liquids, including drilling fluid, fuel, and lubricating oil, that are in tanks and containers on the facility. The Application includes technical reports, seismic data, and information regarding the geology and existing producing oil wells of the Upper Sunniland Formation, which Kanter filed for the purpose of demonstrating an indicated likelihood of the presence of oil at the proposed site. The third Request for Additional Information (RAI) did not request additional information regarding the indicated likelihood of the presence of oil at the proposed site. After it submitted its response to the third RAI, Kanter notified the Department of its belief that additional requests were not authorized by law. As a result, the Department completed the processing of the Application without additional RAI’s. On November 16, 2016, the Department entered its Notice of Denial of the Oil and Gas Drilling Permit. The sole basis for denial was that Kanter failed to provide information showing a balance of considerations in favor of issuance pursuant to section 377.241.1/ There was no assertion that the Application failed to meet any standard established by applicable Department rules, Florida Administrative Code Chapters 62C-25 through 62C-30. In particular, the parties included the following stipulations of fact in the Joint Prehearing Stipulation which are, for purposes of this proceeding, deemed as established: The structure intended for the drilling or production of Kanter’s exploratory oil well is not located in any of the following: a municipality; in tidal waters within 3 miles of a municipality; on an improved beach; on any submerged land within a bay, estuary, or offshore waters; within one mile seaward of the coastline of the state; within one mile seaward of the boundary of a local, state or federal park or an aquatic or wildlife preserve; on the surface of a freshwater lake, river or stream; within one mile inland from the shoreline of the Gulf of Mexico, the Atlantic Ocean or any bay or estuary; or within one mile of any freshwater lake, river or stream. The location of Kanter’s proposed oil well is not: within the corporate limits of any municipality; in the tidal waters of the state, abutting or immediately adjacent to the corporate limits of a municipality or within 3 miles of such corporate limits extending from the line of mean high tide into such waters; on any improved beach, located outside of an incorporated town or municipality, or at a location in the tidal waters of the state abutting or immediately adjacent to an improved beach, or within 3 miles of an improved beach extending from the line of mean high tide into such tidal waters; south of 26°00'00? north latitude off Florida’s west coast and south of 27°00'00? north latitude off Florida’s east coast, within the boundaries of Florida’s territorial seas as defined in 43 U.S.C. 1301; north of 26°00'00? north latitude off Florida’s west coast to the western boundary of the state bordering Alabama as set forth in s. 1, Art. II of the State Constitution; or north of 27°00'00? north latitude off Florida’s east coast to the northern boundary of the state bordering Georgia as set forth in s. 1, Art. II of the State Constitution, within the boundaries of Florida’s territorial seas as defined in 43 U.S.C. 1301. 19. The proposed oil well site does not contain Florida panther habitat and is located outside of the primary and secondary habitat zones for the Florida panther. 21. There are no recorded archaeological sites or other historic resources recorded within the area of the proposed oil well site. Kanter submitted a payment of $8,972.00 for its oil and gas permit application on June 30, 2016 pursuant to Rule 62C- 26.002(5)(c), F.A.C. Kanter’s application includes sufficient information and commitments for performance bonds and securities. DEP and Intervenors do not claim that the application lacks the information required in rule 62C-26.002, F.A.C. Kanter’s application includes an organization report that satisfies the requirements of rule 62C-26.003(3), F.A.C. Kanter’s engineering aspects of the site plan for the proposed project site, are appropriate. Kanter’s survey submitted to DEP in support of its application includes a suitable location plat which meets the minimum technical standards for land surveys. Kanter’s application includes an appropriate description of the planned well completion. DEP and Intervenors do not claim that the drilling application lacks the information required by rule 62C-26.003, F.A.C. Kanter’s Application proposes using existing levees to provide access to the proposed Kanter well site. Kanter did not propose to construct additional roads for access. Kanter’s proposed well site is located 332 feet from the L67-A levee, which serves as a roadway for trucks used to perform operations and maintenance on the levees and canals in the area. Kanter’s application does not lack any information required by DEP with respect to the location of roads, pads, or other facilities; nor does it lack any information regarding the minimization of impacts with respect to the location of roads. DEP and Intervenors do not contend that the permit should be denied based upon the proposed “spacing” of the well, or drilling unit, as that term is used in rule 62C-26.004, F.A.C. Kanter’s application includes appropriate plans for the construction of mud tanks, reserve pits, and dikes. Kanter agrees to a reasonable permit condition requiring that if water is to be transported on-site, that it will add additional tanks for the purpose of meeting water needs that would arise during the drilling process. Kanter’s design of the integrated casing, cementing, drilling mud, and blowout prevention programs is based upon sound engineering principles, and takes into account all relevant geologic and engineering data and information. Kanter’s proposed casing plan includes an additional casing string proposed in its response to DEP’s Third Request for Additional Information. This casing plan meets or exceeds the requirements of 62C-27.005, F.A.C. Kanter’s proposed casing and cementing program, as modified, meets or exceeds all applicable statutory and rule criteria.[2/] Kanter’s response and documents provided in response to DEP’s 3rd RAI satisfactorily resolved DEP’s concern regarding the risk of passage of water between different confining layers and aquifers resulting from the physical act of drilling through the layers of water and the intervening soil or earth. Kanter’s application includes a sufficient lost circulation plan. Kanter’s application is not deficient with respect to specific construction requirements which are intended to prevent subsurface discharges. Kanter’s drilling fluids plan is appropriate and is not deficient. Kanter’s blowout prevention equipment and procedures are appropriate and are not deficient. Kanter’s plans for blowout prevention are not insufficient. Kanter’s proposed oil pad is above the 100 year flood elevation and under normally expected circumstances would not be inundated by water if constructed as proposed in Kanter’s application. Kanter’s application includes a Hydrogen Sulfide Safety Plan that includes standards which are consistent with the onshore oil and gas industry standards set forth in the American Petroleum Institutes’ Recommended Practice. DEP and Intervenors do not claim any insufficiencies with respect to Kanter’s Hydrogen Sulfide Gas Contingency Plan, the sufficiency of secondary containment, its construction plans for a protective berm around the drilling site and storage tank areas of sufficient height and impermeability to prevent the escape of pad fluid, its pollution prevention plan, its safety manual, or its spill prevention and cleanup plan. DEP and Intervenors do not contend that the permitting of the well would violate section 377.242(1), F.S., regarding permits for the drilling for, exploring for, or production of oil, gas, or other petroleum products which are to be extracted from below the surface of the land only through the well hole(s). DEP and Intervenors do not contend that Kanter’s application violates the applicable rule criteria for oil and gas permitting set forth in Chapters 62C-25 through 62C-30, Florida Administrative Code. In addition to the foregoing, Kanter is not seeking or requesting authorization to perform “fracking,” and has agreed to a permit condition that would prohibit fracking. As a result of the foregoing, the parties have agreed that the Application meets or exceeds all criteria for an exploratory oil well permit under chapters 62C-25 through 62C-30. The Property Kanter owns two parcels of land totaling 20,000 acres in the area of the proposed Well Site: a northern parcel consisting of approximately 11,000 acres and a southern parcel consisting of approximately 9,000 acres. Kanter assembled its holdings through a series of acquisitions by deeds from 1975 to 1996. The Well Site is to be located within the southern parcel. On August 7, 1944, Kanter’s predecessor in title, Dallas Investment Co., acquired by tax deed all interests in a parcel within the 9,000-acre southern parcel described as “All Section 23 Township 51 South, Range 38 East, 640 Acres,” including, without reservation, the oil, gas, minerals, and phosphate. The evidence of title submitted as part of the Application indicates that a “Kanter” entity first became possessed of rights in Section 23 in 1975. By virtue of a series of transactions extending into 1996, Kanter currently holds fee title to all surface rights, and title to all mineral rights, including rights to oil, gas, and other mineral interests, within Section 23 Township 51 South, Range 38 East. The Well Site specified in the Application is within Section 23, Township 51 South, Range 38 East. Kanter’s property is encumbered by a Flowage Easement that was granted to the Central and Southern Flood Control District in 1950, and is presently held by the South Florida Water Management District (SFWMD). The Flowage Easement guarantees Kanter access to the entire easement property “for the exploration or drilling for, or the developing, producing, storing or removing of oil, gas or other . . . in accordance with sound engineering principles.” Kanter has the legal property right to locate and drill the well, and the exploratory well is consistent with Kanter’s ownership interest. The Well Site is located in a 160-acre (quarter section) portion of the 640-acre tract described above, and is within a “routine drilling unit,” which is the block of land surrounding and assigned to a well. Fla. Admin. Code R. 62C-25.002(20) and 62C-25.002(40). The Kanter property, including the Well Site, is in the historic Everglades. Before efforts to drain portions of the Everglades for development and agricultural uses, water flowed naturally in a southerly direction through land dominated by sawgrass and scattered tree islands. The tree islands were generally shaped by the direction of the water flow. Beginning as early as the late 1800s, dramatically increasing after the hurricane of 1947, and extending well into the 1960s, canals, levees, dikes, and channels were constructed to drain, impound, or reroute the historic flows. Those efforts have led to the vast system of water control structures and features that presently exist in south Florida. The Well Site, and the Kanter property as a whole, is located in Water Conservation Area (WCA)-3. WCA-3 is located in western Broward County and northwestern Miami-Dade County. It was constructed as part of the Central and Southern Florida Flood Control project authorized by Congress in 1948, and was created primarily for flood control and water supply. In the early 1960s, two levees, L67-A and L67-C, were constructed on a line running in a northeast to southwest direction. When constructed, the levees separated WCA-3 into WCA-3A to the west and WCA-3B to the southeast. The Well Site is in WCA-3A.3/ The area between L67-A and L67-C, along with a levee along the Miami Canal, is known as the “Pocket.” There is no water control in the Pocket. Although there is a structure at the south end of the Pocket, it is in disrepair, is rarely -- if ever -- operated, and may, in fact, be inoperable. The Well Site is located within the Pocket, on the southern side of L67-A. L67-A and L67-C, and their associated internal and external canals, have dramatically disrupted sheet flow, altered hydrology, and degraded the natural habitat in the Pocket. Water inputs and outputs are entirely driven by rainfall into the Pocket, and evaporation and transpiration from the Pocket. From a hydrologic perspective, the Pocket is entirely isolated from WCA-3A and WCA-3B. The Pocket is impacted by invasive species, which have overrun the native species endemic to the area and transformed the area into a monoculture of cattails. Vegetation that grows in the Pocket dies in the Pocket. Therefore, there is a layer of decomposing vegetative muck, ooze, and sediment from knee deep to waist deep in the Pocket, which is atypical of a functioning Everglades system. L67-A and L67-C, and their associated internal and external canals, impede wildlife movement, interfering with or preventing life functions of many native wildlife species. The proposed Well Site, and the surrounding Kanter property, is in a rural area where future residential or business development is highly unlikely. The property is removed from urban and industrial areas and is not known to have been used for agriculture. The Department has previously permitted oil wells within the greater Everglades, in areas of a more pristine environmental nature, character, and location than the Pocket. The Raccoon Point wellfield is located 24 miles west of the Proposed Project Site within the Big Cypress National Preserve. It is within a more natural system and has not undergone significant hydrologic changes such as the construction of canals, levees, ditches, and dikes and, therefore, continues to experience a normal hydrologic flow. Mr. Gottfried testified that at Raccoon Point, “you can see the vegetation is maintaining itself because the fact that we don’t have levees, ditches canals, dikes, impacting the area. So you have a diversity of plant life. You have tree islands still. You have the normal flow going down.” The greater weight of evidence shows that the Kanter Well Site is far less ecologically sensitive than property at Raccoon Point on which the Department has previously permitted both exploration and production wells. The Biscayne Aquifer The Biscayne Aquifer exists in almost all of Miami- Dade County, most of Broward County and a portion of the southern end of Palm Beach County. It is thickest along the coast, and thinnest and shallowest on the west side of those counties. The western limit of the Biscayne Aquifer lies beneath the Well Site. The Biscayne Aquifer is a sole-source aquifer and primary drinking water source for southeast Florida. A network of drainage canals, including the L-30, L-31, L-33, and Miami Canals, lie to the east of WCA-3B, and east of the Well Site. Those canals penetrate into the substratum and form a hydrologic buffer for wellfields east of the Well Site, including that operated by Miramar, and isolate the portions of the Biscayne Aquifer near public wellfields from potential impacts originating from areas to their west. The canals provide a “much more hydraulically available source” of water for public wellfields than water from western zones of the Biscayne Aquifer, and in that way create a buffer between areas on either side of the canals. The Pocket is not a significant recharge zone for the Biscayne Aquifer. There is a confining unit comprised of organic soils, muck, and Lake Flint Marl separating the Pocket and the Well Site from the Fort Thompson formation of the Biscayne Aquifer. There is a layer of at least five feet of confining muck under the L67-A levee in the area of the Well Site, a layer that is thicker in the Pocket. The Well Site is not within any 30-day or 120-day protection zones in place for local water supply wells. The fact that the proposed well will penetrate the Biscayne Aquifer does not create a significant risk of contamination of the Biscayne Aquifer. The drilling itself is no different than that done for municipal disposal wells that penetrate through the aquifer much closer to areas of water production than is the Well Site. The extensive casing and cementing program to be undertaken by Kanter provides greater protection for the well, and thus for the aquifer, than is required by the Department’s rules. A question as to the “possibility” that oil could get into the groundwater was answered truthfully in the affirmative “in the definition of possible.” However, given the nature of the aquifer at the Well Site, the hydrological separation of the Well Site and well from the Biscayne Aquifer, both due to the on-site confining layer and to the intervening canals, the degree of casing and cementing, and the full containment provided by the pad, the testimony of Mr. Howard that “it would be very difficult to put even a fairly small amount of risk to the likelihood that oil leaking at that site might possibly actually end up in a well at Miramar” is accepted. The Sunniland Formation The Sunniland Formation is a geologic formation which exists in a region of South Florida known as the South Florida Basin. It is characterized by alternating series of hydrocarbon-containing source rock, dolomite, and limestone of varying porosity and permeability and evaporite anhydrite or mudstone seal deposits. It has Upper Sunniland and Lower Sunniland strata, and generally exists at a depth of up to 12,000 feet below land surface (bls) in the area of the Well Site. Underlying the Sunniland Formation is a formation generally referred to as the “basement.” The basement exists at a depth of 17,000-18,000 feet bls. Oil is produced from organic rich carbonate units within the Lower Cretaceous Sunniland Formation, also known as the Dark Shale Unit of the Sunniland Formation. The oil produced in the Sunniland Formation is generally a product of prehistoric deposits of algae. Over millennia, and under the right conditions of time and pressure, organic material is converted to hydrocarbon oil. The preponderance of the evidence demonstrates that active generating source rock capable of producing hydrocarbons exists in the Sunniland Formation beneath the Kanter property. The preponderance of the evidence also indicates that the oil generated in the Sunniland Formation is at a sufficient depth that it is preserved from microbial degradation, which generally occurs in shallower reservoirs. The Upper Sunniland Formation was formed in the Cretaceous geological period, between 106 and 100 million years ago. Over that period, sea levels rose and fell dramatically, allowing colonies of rudists (a now extinct reef-building clam) and oysters to repeatedly form and die off. Over time, the colonies formed bioherms, which are reef-like buildups of shell elevated off of the base of the sea floor. Over millennia, the bioherms were exposed to conditions, including wave action and exposure to air and rainwater, that enhanced the porosity of the component rudist and oyster shell. Those “patch reefs” were subsequently buried by other materials that formed an impermeable layer over the porous rudist and oyster mounds, and allowed those mounds to become “traps” for oil migrating up from lower layers. A trap is a geological feature that consists of a porous layer overlain by an impervious layer of rock that forms a seal. A trap was described, simplistically, as an upside down bowl. Oil, being lighter than water, floats. As oil is generated in source rock, it migrates up through subterranean water until it encounters a trapping formation with the ability to create a reservoir, and with an impervious layer above the porous layer to seal the trap and prevent further migration, thus allowing the “bowl” to fill. The reservoir is the layer or structure with sufficient porosity and permeability to allow oil to accumulate with its pores. The thickness of the layer determines the volume of oil that the reservoir is capable of retaining. Although rudist mounds are generally considered to be more favorable as traps due to typically higher porosity, oyster mound traps are correlated to producing wells in the Sunniland Formation and are primary producers in the Felda field and the Seminole field. The Lower Sunniland Formation is a fractured carbonate stratum, described by Mr. Aldrich as a rubble zone. It is not a traditional structural trap. Rather, it consists of fractured and crumbling rock thought to be created by basement shear zones or deep-seated fault zones. It has the same source rock as the Upper Sunniland. There is little information on traps in the Lower Sunniland, though there are two fields that produce from that formation. A “play” is a group of prospects or potential prospects that have the same source rock, the same reservoir rock, the same trap style, and the same seal rock to hold in the hydrocarbons. The producing oil fields in the Sunniland Formation, including Raccoon Point, Sunniland, Felda, West Felda, and Lake Trafford are part of a common play known as the Sunniland Trend. The Sunniland Trend is an area of limestone of greater porosity within the Sunniland Formation, and provides a reasonable extrapolation of areas that may be conducive to oil traps. The Sunniland Trend extends generally from Manatee County on the west coast of Florida southeasterly into Broward County and the northwestern portion of Miami-Dade County on the east coast of Florida. The trend corresponds to the ancient Cretaceous shoreline where rudist and oyster bioherms formed as described above. In 2003, the “Mitchell-Tapping” report, named after the husband and wife team, identified two separate trends within the Sunniland Trend, the rudist-dominant West Felda Trend, and the more oyster-based Felda Trend. Both are oil-producing strata. The Felda Trend is more applicable to the Kanter property. Throughout the Sunniland Trend, hydrocarbon reservoirs exist within brown dolomite deposits and rudist and oyster mounds. Dolomite is a porous limestone, and is the reservoir rock found at the productive Raccoon Point oil wellfield. The evidence indicates that a brown dolomite layer of approximately 20 feet underlies the Well Site, and extends in all directions from the Well Site. A preponderance of the evidence indicates that the Kanter property, including the Well Site, is within the Sunniland Trend and its Felda Trend subset.4/ Oil produced from wells in the Sunniland Trend is typically thick, and is not under pressure. The oil does not rise through a bore hole to the surface, but must be pumped. The Raccoon Point Field, which is the closest productive and producing wellfield to the proposed Well Site, is located approximately 24 miles to the west of the Well Site, within the Sunniland Trend. Raccoon Point contains numerous well sites, of which four or five are currently producing, and has produced in the range of 20 million barrels of oil since it began operation in the late 1970s. Cumulative production of oil from proven fields in the South Florida Basin, including fields in the Sunniland Formation, is estimated to be in excess of 160 million barrels. Estimates from the U.S. Geological Service (USGS) indicate that 25 new fields capable of producing five million barrels of oil each are expected to be found within the Lower Cretaceous Shoal Reef Oil Assessment Unit, which extends into the Kanter property. Estimates of the potential reserves reach as high as an additional 200 million barrels of oil. The Dollar Bay Formation Another formation that has potential for oil production is the Lower Cretaceous Dollar Bay Formation, also in the South Florida Basin. The Dollar Bay Formation exists beneath the Kanter property at a shallower depth than the Sunniland Formation, generally at a depth of 10,000 feet in the vicinity of the Well Site. Most of the Dollar Bay prospects are on the east side of the South Florida Basin. Most of the wells in the South Florida Basin are on the west side. Thus, there has not been much in the way of exploration in the Dollar Bay Formation, so there is a lack of data on traps. Dollar Bay has been identified as a known oil-bearing play by the USGS. It is a self-source play, so the source comes from the Dollar Bay Formation itself. Dollar Bay exists both as potential and mature rock. It has known areas of very high total organic content (TOC) source rock; logged reservoir in the formation; and seal rock. There have been three oil finds in the Dollar Bay formation, with at least one commercial production well. Kanter will have to drill through the Dollar Bay Formation to get to the Upper Sunniland formation, thus allowing for the collection of information as to the production potential of the prospect. Although Dollar Bay is not generally the main “target” of the Permit, its potential is not zero. Thus, consideration of the Dollar Bay Formation as a factor in the calculation of risk/success that goes into the decision to drill an exploratory well is appropriate. Initial Exploratory Activities In 1989, Shell Western E&P, Inc. (Shell), conducted extensive seismic exploration in south Florida. Among the areas subject to seismic mapping were two lines -- one line of 36,000 feet mapped along the L67-A levee, directly alongside the Well Site, and the other of approximately 10 miles in length along the Miami Canal levee. The lines intersect on the Kanter property just north of the Well Site. The proposed exploration well is proposed to extend less than 12,000 feet deep. The seismic mapping performed by Shell was capable of producing useful data to that depth. The seismic methodology utilized by Shell produced data with a high degree of vertical and spatial resolution. Given its quality, the Shell data is very reliable. Shell did not use the seismic data generated in the 1980s, and ultimately abandoned activity in the area in favor of larger prospects, leaving the smaller fields typical of south Florida for smaller independent oil companies. The Shell seismic data was purchased by Seismic Exchange, a data brokerage company. In 2014, Kanter purchased the seismic data from Seismic Exchange for the lines that ran through its property. With the purchase, Kanter received the original field tapes, the support data, including surveyors’ notes and observer sheets which describe how the data was acquired, and the recorded data. As a result of advances in computer analysis since the data was collected, the seismic data can be more easily and accurately evaluated. It is not unusual for companies to make decisions on whether to proceed with exploration wells with two lines of seismic data. Mr. Lakin reviewed the data, and concluded that it showed a very promising area in the vicinity of the L67-A levee that was, in his opinion, sufficient to continue with permitting an exploratory oil well. Mr. Lakin described the seismic information in support of the Application as “excellent data,” an assessment that is well-supported and accepted. Mr. Pollister reviewed the two lines of seismic data and opined that the information supports a conclusion that the site is a “great prospect” for producing oil in such quantities as to warrant the exploration and extraction of such products on a commercially profitable basis. Seismic Data Analysis The seismic lines purchased by Kanter consist of line 970, which runs southwest to northeast along the L67-A levee, and a portion of line 998, which runs from northwest to southeast along the Miami Canal levee. The lines intersect at the intersection of the two levees. The data depicts, among others, the seismic reflection from the strata of the Sunniland Trend, and the seismic reflection from the basement. The depiction of the Sunniland Trend shows a discernable rise in the level of the strata, underlain by a corresponding rise in the basement strata. This rise is known as an anticline. An anticline is a location along a geologic strata at which there is an upheaval that tends to form one of the simplest oil traps that one can find using seismic data. In the South Florida Basin, anticlines are typically associated with mounded bioherms. A “closed structure” is an anticline, or structural high, with a syncline, or dip, in every direction. A closed structure, though preferable, is not required in order for there to be an effective trap. Most of the Sunniland oil fields do not have complete closure. They are, instead, stratigraphic traps, in which the formation continues to dip up and does not “roll over.” Where the rock type changes from nonporous to porous and back to nonporous, oil can become trapped in the porous portion of the interval even without “closure.” Thus, even if the “bowl” is tilted, it can still act as a trap. Complete closure is not necessary in much of the Sunniland Trend given the presence of an effective anhydrite layer to form an effective seal.5/ The seismic data of the Kanter property depicts an anticline in the Sunniland Formation that is centered beneath the Well Site at a depth in the range of 12,000 feet bls. Coming off of the anticline is a discernable syncline, or dip in the underlying rock. Applying the analogies used by various witnesses, the anticline would represent the top of the inverted bowl, and the syncline would represent the lip of the bowl. The evidence of the syncline appears in both seismic lines. The Shell seismic data also shows an anhydrite layer above the Sunniland Formation anticline. The same anticline exists at the basement level at a depth of 17,000 to 18,000 feet bls. The existence of the Sunniland formation anticline supported by the basement anticline, along with a thinning of the interval between those formations at the center point, provides support for the data reliably depicting the existence of a valid anticline. A basement-supported anticline is a key indicator of an oil trap, and is a feature commonly relied upon by geophysicists as being indicative of a structure that is favorable for oil production. The seismic data shows approximately 65 feet of total relief from the bottom to the top of the anticline structure, with 50 feet being closed on the back side. The 50 feet of closed anticline appears to extend over approximately 900 acres. There is evidence of other anticlines as one moves northeast along line 970. However, that data is not as strong as that for the structure beneath the Well Site. Though it would constitute a “lead,” that more incomplete data would generally not itself support a current recommendation to drill and, in any event, those other areas are not the subject of the permit at issue. The anticline beneath the well site is a “prospect,” which is an area with geological characteristics that are reasonably predicted to be commercially profitable. In the opinion of Mr. Lakin, the prospect at the location of the proposed Well Site has “everything that I would want to have to recommend drilling the well,” without a need for additional seismic data. His opinion is supported by a preponderance of the evidence, and is credited. Confirmation of the geology and thickness of the reservoir is the purpose of the exploratory well, with the expectation that well logs will provide such confirmation. Risk Analysis Beginning in the 1970s, the oil and gas industry began to develop a business technique for assessing the risk, i.e., the chance of failure, to apply to decisions being made on drilling exploration wells. Since the seminal work by Bob McGill, a systematic science has developed. In 1992, a manual was published with works from several authors. The 1992 manual included a methodology developed by Rose & Associates for assessing risk on prospects. The original author, Pete Rose,6/ is one of the foremost authorities on exploration risk. The Rose assessment method is a very strong mathematical methodology to fairly evaluate a prospect. The Rose method takes aspects that could contribute to finding an oil prospect, evaluates each element, and places it in its perspective. The Rose prospect analysis has been refined over the years, and is generally accepted as an industry standard. The 1992 manual also included a methodology for assessing both plays and prospects developed by David White. The following year, Mr. White published a separate manual on play and prospect analysis. The play and prospect analysis is similar to the Rose method in that both apply mathematical formulas to factors shown to be indicative of the presence of oil. Play and prospect analysis has been applied by much of the oil and gas industry, is used by the USGS in combining play and prospect analysis, and is being incorporated by Rose & Associates in its classes. The evidence is convincing that the White play and prospect analysis taught by Mr. Aldrich is a reasonable and accepted methodology capable of assessing the risk inherent in exploratory drilling. Risk analysis for plays and prospects consists of four primary factors: the trap; the reservoir; the source; and preservation and recovery. Each of the four factors has three separate characteristics. Numeric scores are assigned to each of the factors based on seismic data; published maps and materials; well data, subsurface data, and evidence from other plays and prospects; and other available information. Chance of success is calculated based on the quantity and quality of the data supporting the various factors to determine the likelihood that the prospect will produce flowable hydrocarbons. The analysis and scoring performed by Mr. Aldrich is found to be a reasonable and factually supported assessment of the risk associated with each of the prospects that exist beneath the proposed Well Site and that are the subject of the Application.7/ However, Mr. Aldrich included in his calculation an assessment of the Lower Sunniland Formation. The proposed well is to terminate at a depth of 11,800 feet bls, which is within the Upper Sunniland, but above the Lower Sunniland. Thus, although the Lower Sunniland would share the same source rock, the exploration well will not provide confirmation of the presence of oil. Therefore, it is more appropriate to perform the mathematical calculation to determine the likelihood of success without consideration of the Lower Sunniland prospect. To summarize Mr. Aldrich’s calculation, he assigned a four-percent chance of success at the Well Site for the Dollar Bay prospect. The assignment of the numeric scores for the Dollar Bay factors was reasonable and supported by the evidence. Mr. Aldrich assigned a 20-percent chance of success at the Well Site for the Upper Sunniland play. The assignment of the numeric scores for the Upper Sunniland factors was reasonable and supported by the evidence. In order to calculate the overall chance of success for the proposed Kanter exploratory well, the assessment method requires consideration of the “flip side” of the calculated chances of success, i.e., the chance of failure for each of the prospects. A four-percent chance of success for Dollar Bay means there is a 96-percent (0.96) chance of failure, i.e., that a commercial zone will not be discovered; and with a 20-percent chance of success for the Upper Sunniland, there is an 80-percent (0.80) chance of failure. Multiplying those factors, i.e., .96 x .80, results in a product of .77, or 77 percent, which is the chance that the well will be completely dry in all three zones. Thus, under the industry-accepted means of risk assessment, the 77-percent chance of failure means that there is a 23-percent chance of success, i.e., that at least one zone will be productive. A 23-percent chance that an exploratory well will be productive, though lower than the figure calculated by Mr. Aldrich,8/ is, in the field of oil exploration and production, a very high chance of success, well above the seven-percent average for prospecting wells previously permitted by the Department (as testified to by Mr. Linero) and exceeding the 10- to 15-percent chance of success that most large oil companies are looking for in order to proceed with an exploratory well drilling project (as testified to by Mr. Preston). Thus, the data for the Kanter Well Site demonstrates that there is a strong indication of a likelihood of the presence of oil at the Well Site. Commercial Profitability Commercial profitability takes into account all of the costs involved in a project, including transportation and development costs. Mr. Aldrich testified that the Kanter project would be commercially self-supporting if it produced 100,000 barrels at $50.00 per barrel. His testimony was unrebutted, and is accepted. The evidence in this case supports a finding that reserves could range from an optimistic estimate of 3 to 10 million barrels, to a very (perhaps unreasonably) conservative estimate of 200 barrels per acre over 900 acres, or 180,000 barrels. In either event, the preponderance of the evidence adduced at the hearing establishes an indicated likelihood of the presence of oil in such quantities as to warrant its exploration and extraction on a commercially profitable basis.9/
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Protection enter a final order: Approving the Application for Oil and Gas Drilling Permit No. OG 1366 with the conditions agreed upon and stipulated to by Petitioner, including a condition requiring that if water is to be transported on-site, it will add additional tanks for the purpose of meeting water needs that would arise during the drilling process, and a condition prohibiting fracking; and Approving the application for Environmental Resource Permit No. 06-0336409-001. DONE AND ENTERED this 10th day of October, 2017, in Tallahassee, Leon County, Florida. S E. GARY EARLY 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 10th day of October, 2017.
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