The Issue Whether Gar-Con's revised application for a permit to construct a sewage plant, and soakage trenches to dispose of the effluent, should be granted?
Findings Of Fact Eight to ten miles south of Melbourne Beach and 8.3 miles north of Sebastian Inlet, Gar-Con plans to develop a parcel of land stretching west from the Atlantic Ocean, across Highway A1A, to the Indian River. Gar-Con expects to build a motel and residential complex complete with tennis courts, parking garage, water treatment plant and the sewage treatment facility for which a construction permit is sought in these proceedings. The sewage treatment plant would be built on a site 480 feet west of Highway A1A and 90 feet south of Gar-Con's northern property line, at an elevation of 11 or 12 feet above mean sea level. Ocean Way Water and Sewer Association, Inc. is to be organized as a nonprofit corporation to own and operate the wastewater treatment facility. The Public Service Commission, through the director of its water and sewer treatment, has taken the position that the proposed "sewer system will fall within the exemption described in Section 367.022(7), Florida Statutes." DER's Composite Exhibit A. PACKAGE PLANT PROPOSED The facility Gar-Con proposes is designed to treat 100,000 gallons of sewage daily, which is the estimated "total flow" (T. 75) the sanitary engineer who designed the system anticipates from the development. Sewage generated by the development would flow to the plant, through a bar rack designed to remove rags and other large objects, and into aeration tanks where, over a 24 hour period, interaction with air and a biological mass would supply oxygen and cause the formation of biological floccules. The flocculant sewage would then move to a clarifier hopper. During its five hour stay there, solids which were not earlier segregated as the sewage moved over a weir into the clarifier, would be precipitated and removed. The clear, residual liquid would be pumped through one of two sand filters (each of which would also have granular activated carbon and be capable of filtering 100,000 gallons daily) into one of two chlorine contact chambers where a gas chlorinator would introduce chlorine for an hour. Under ordinary circumstances, the chlorinated effluent would then be pumped into one of two soakage trenches. The soakage trenches, each designed for use every other week, are to be gravel-filled ditches covered over first with felt paper, then with compacted fill. The gravel would lie at least one foot beneath the surface of the ground in a space ten feet wide and three feet deep stretching the 940 foot length of each soakage trench. Punctured like sieves, two six-inch PVC pipes would run through the gravel, sweating effluent from their pores. There is also a plan to dig a percolation pond or grassed swale five feet deep, 120 feet long and 80 feet wide near the wastewater treatment plant, which could serve as a receptacle for effluent, in case of "a 1:10 year storm or when the filters are down and/or if soakage trenches would need repair." Gar- Con's Exhibit 2-A. It would hold about 100,000 gallons. The solids caught by the weir, those extracted in the clarifying process, and those recovered from backwashing the filters would serve as catalyst for the aeration process as needed. Excess sludge, about 3,000 pounds monthly, would undergo "aerobic digestion," before being removed to Brevard County's Central Disposal Facility on Adamson Road, for disposal there. Gar- Con's Exhibit No. 7. Primary and secondary drinking water standards would be met by the effluent as it left the plant (although the engineer who designed the system would not drink the effluent himself), except that, from time to time, nitrate concentrations might reach 12 milligrams per liter, and except in the "event that a homeowner might put some type of [inorganic toxic or carcinogenic] material into the sewer system." (T. 86) The biological oxygen demand (BOD) would be ten milligrams per liter; suspended solids would probably amount to about five milligrams per liter; pH would probably be slightly under seven; nitrates would average approximately eight milligrams per liter but would "peak out at certain times during the year, for maybe extended periods up to two months, at twelve milligrams per liter," (T. 80); and there would be a chlorine residual after 60 minutes of two milligrams per liter. AMBIENT WATERS There would be no direct discharge to the Atlantic Ocean, Indian River or any other body of surface water, nor would any indirect effect on surface waters be measurable. No body of surface water lies within 500 feet of the site proposed for the plant and soakage trenches. Potable groundwater underlies the site; the groundwater table slopes toward the Atlantic Ocean, 9.5 to 12.5 feet below ground. "[D]uring the traditional rainy season," Gar-Con's Exhibit 2B, Attachment, p.3, the groundwater may rise to within seven feet of the surface. The PVC pipes in the soakage trenches are to be placed two and a half feet deep. As effluent percolated through the sandy soil, there would be "mounding" of the groundwater underneath the soakage trenches, and dispersal in all directions. Surface flow is to be diverted from the soakace trenches so that only rainwater falling directly on them would percolate down through the gravel beds. Taking soil characteristics into account, and assuming a "water table depth" of 20 feet, an engineer retained by Gar-Con predicted that "the maximum expected groundwater rises beneath the east and west trenches are 2.4 and 2.1 feet, respectively under a loading of 100,000 gpd for a period of 7 days." Gar-Con's Exhibit No. 3. The water table depth, "the height, the top of the groundwater from the first restrictive layer," (T. 172), is probably more like 40 feet than 20, which accounts in part for the "conservatism" of the mounding predictions. Under very severe weather conditions (a 100 year storm), groundwater would rise as high as the bottom of the trenches making them unavailable to receive effluent, but the effluent would not be forced above ground. In a 100 year flood, water would be expected to rise to seven feet above mean sea level. Under such conditions, people could be expected to evacuate the area. In a 25 year storm, the system could be expected to continue to function. Groundwater to the north and east of the proposed site was sampled, and the samples were analyzed. The water to the north had 380 milligrams of chlorides per liter and the water to the east had 450 milligrams of chlorides per liter. As it left the proposed treatment plant, the effluent would contain approximately 150 milligrams of chlorides per liter. SOUND AND LIGHT Lights like those used as street lights are to be installed at four places in the wastewater treatment plant. A timer, which can be overridden, would turn the lights on at dusk and off at eleven o'clock at night. The lights would illuminate the plant adequately. Pumps would move sewage to and through the proposed plant. Most of the pump motors would be submerged and unable to be heard. Two electric blowers, a flow meter and a totalizer would also have electrical motors. The blowers and the blower motors are to be equipped with insulated fiberglass covers and the blowers would also have intake and double outlet silencers. Four feet from the plant the noise of the motors would be comparable to that of a home air conditioning unit. At the nearest residence the noise level would scarcely exceed background noise. At hearing, Gar-Con revised its application and agreed to install an emergency generator which would also be encased in insulated housing and is to be equipped with a muffler. AEROSOL AND ODOR Unless the proposed plant loses electric power for 24 hours or longer, no offensive odors would emanate from it. The bar rack and weirs would be regularly hosed down. Against the possibility of a power failure, Gar-Con agreed at hearing to install permanently an emergency generator with sufficient capacity to keep both the wastewater treatment plant and the water treatment plant it plans to build operable. No aerosol drift is foreseen. The surface of the liquid In the aeration tanks would be 1.4 feet below the top of the rim. Walkways four feet wide along the inside perimeters of the aeration holding tanks would prevent dispersal of most of aerosol. A decorative hedge around the treatment plant, which would eventually be 15 feet high, is a final fail-safe. WELLS To the north are two shallow wells within 500 feet of the site proposed for the wastewater treatment plant. Both wells belong to Kel Fox, who wrote Gar-Con that he had no objection to their proposed wastewater treatment facility in light of Gar-Con's agreement to furnish drinking water to existing facilities on his property and reimburse him expenses incurred in disconnecting the two shallow wells. Gar-Con's Exhibit 2E. There is a deep well within 500 feet to the south. DER and Gar-Con have entered into the following stipulation, dated September 2, 1983: Existing Wells. Prior to the operation of its waste water treatment plant, Gar-Con will offer to supply drinking water at a reasonable cost to owners of property on which are located operational or approved shallow drinking water wells that are within 500 feet of Gar-Con's land application site. Gar-Con will make this offer to all such owners known to it prior to the operation of its plant. Gar-Con will further offer to provide reasonable compensation to such owners to disconnect their shallow wells. Gar-Con will endeavor to arrange for provision of drinking water to these owners and the disconnection of those wells prior to the operation of its plant. Future Wells. Should nearby individual (non-corporate) property owners propose to construct shallow drinking wells located within 500 feet of Gar-Con's land application site after Gar-Con begins operation of its waste water treatment plant, Gar-Con also will offer to supply them with drinking water at a reasonable cost and to provide reasonable compensation to them to disconnect those wells. However, Gar-Con shall have no obligation to make any such offer to owners of future wells if sampling of monitoring wells located at or near its external property line indicates that the groundwater meets the primary drinking water standards and, after July 1, 1985, the secondary drinking water standards listed in Florida Administrative Code Rule 17-22.104. Gar-Con agrees to record a master notice of restriction barring future owners of lots within the Ocean Way development, which are owned by Car-Con at the time of permit issuance, from installing shallow drinking water wells on such property or otherwise using the shallow aquifer beneath their property as a source for irrigation or for potable water, so long as use of the proposed sewage disposal system continues, and the Department has not found that this restriction is unnecessary. This restriction, which shall be a covenant running with the land, further shall require future owners to purchase water from Gar-Con or any successor owner of the development's water system if Gar-Con or the successor provides water service. These restrictions also shall be contained in all other appropriate documents of title. In addition, Gar-Con plans to create a non-profit water and sewer association to own and control the development's water and sewer system. Gar-Con will include in the Articles of Incorporation of this association a requirement that all property owners served by the system must be members of the Association. Gar-Con is entitled to a zone of discharge extending to its current property line with the exception that the zone of discharge shall not include the area contained within a 100' radius of Gar-Cons's proposed water supply wells. DER Staff concurs that the above conditions, in conjunction with the sewage treatment and disposal system and the groundwater monitoring program proposed by the applicant, to meet the requirements of Chapter 17-4, F.A.C. will provide reasonable assurance that existing and future off-site and on-site property owners will be protected from any adverse effects that might result from the operation of the proposed sewage treatment disposal system. Petitioner's Exhibit No. 10. There are to be a half dozen monitoring wells to allow sampling of the groundwater at strategic points in the shallow aquifer. NATURAL RESOURCES Turtles nest in the general vicinity but off the site of the proposed project. Construction and operation of the proposed waste water treatment facility would have no impact on the turtles apart from making it possible for more people to live closer to where they nest.
The Issue The issue in this case is whether Respondent Laniger Enterprises of America, Inc. (Laniger), is entitled to the renewal of its domestic wastewater facility permit that was denied by Petitioner Department of Environmental Protection (Department).
Findings Of Fact The Parties The Department is the administrative agency of the State of Florida having the power and duty to protect Florida's air and water resources and to administer and enforce the provisions of Chapter 403, Florida Statutes (2005),1 and the rules promulgated in Florida Administrative Code Title 62. Laniger is a Florida corporation that owns and operates the WWTP that is the subject of this case, located at 1662 Northeast Dixie Highway, Jensen Beach, Martin County, Florida. The WWTP is referred to in the Department permit documents as the Beacon 21 WWTP. The WWTP Laniger acquired the WWTP in 1988 in a foreclosure action. At that time, the WWTP was in a "dilapidated" condition and was operating under a consent order with the Department. After acquiring the WWTP, Laniger brought it into compliance with the Department's requirements. Laniger's WWTP is commonly referred to as a "package plant."2 The WWTP's treatment processes are extended aeration, chlorination, and effluent disposal to percolation ponds. The WWTP does not have a direct discharge to surface water. It was permitted to treat 99,000 gallons per day (gpd) of wastewater. Its average daily flow during the past year was about 56,000 gallons. The east side of the WWTP site is adjacent to Warner Creek. On the north side of the WWTP site, an earthen berm separates the WWTP's percolation ponds from a drainage ditch that connects to Warner Creek. Warner Creek is a tributary to the St. Lucie River. The St. Lucie River is part of the Indian River Lagoon System. The Indian River Lagoon Act In 1989, the St. Johns River Water Management District and the South Florida Water Management District jointly produced a Surface Water Improvement and Management (SWIM) Plan for the Indian River Lagoon System ("the lagoon system"). For the purpose of the planning effort, the lagoon system was defined as composed of Mosquito Lagoon, Indian River Lagoon, and Banana River Lagoon. It extends from Ponce de Leon Inlet in Volusia County to Jupiter Inlet in Palm Beach County, a distance of 155 miles. The SWIM Plan identified high levels of nutrients as a major problem affecting water quality in the lagoon system. Domestic wastewater was identified as the major source of the nutrients. The SWIM Plan designated 12 problem areas within the lagoon system and targeted these areas for "research, restoration and conservation projects under the SWIM programs." Department Exhibit 2 at 11-13. Neither Warner Creek nor the area of the St. Lucie River that Warner Creeks flows into is within any of the 12 problem areas identified in the SWIM Plan. With regard to package plants, the SWIM Plan stated: There are numerous, privately operated, "package" domestic WWTPs which discharge indirectly or directly to the lagoon. These facilities are a continual threat to water quality because of intermittent treatment process failure, seepage to the lagoon from effluent containment areas, or overflow to the lagoon during storm events. Additionally, because of the large number of "package" plants and the lack of enforcement staff, these facilities are not inspected or monitored as regularly as they should be. Where possible, such plants should be phased out and replaced with centralized sewage collection and treatment facilities. Department Exhibit 2 at 64. In 1990, the Legislature passed the Indian River Lagoon Act, Chapter 90-262, Laws of Florida. Section 1 of the Act defined the Indian River Lagoon System as including the same water bodies as described in the SWIM Plan, and their tributaries. Section 4 of the Act provided: Before July 1, 1991, the Department of Environmental Regulation shall identify areas served by package sewage treatment plants which are considered a threat to the water quality of the Indian River Lagoon System. In response to this legislative directive, the Department issued a report in July 1991, entitled "Indian River Lagoon System: Water Quality Threats from Package Wastewater Treatment Plants." The 1991 report found 322 package plants operating within the lagoon system and identified 155 plants as threats to water quality. The 1991 report described the criteria the Department used to determine which package plants were threats: Facilities that have direct discharges to the system were considered threats. Facilities with percolation ponds, absorption fields, or other sub-surface disposal; systems located within 100 feet of the shoreline or within 100 feet of any canal or drainage ditch that discharges or may discharge to the lagoon system during wet periods were considered threats. * * * Facilities with percolation ponds, absorption fields, or other sub-surface disposal systems located more than 100 feet from surface water bodies in the system were evaluated case-by-case based on [operating history, inspection reports, level of treatment, and facility reliability]. Laniger's package plant was listed in the 1991 report as a threat to the water quality of the lagoon system because it was within 100 feet of Warner Creek and the drainage ditch that connects to Warner Creek. Laniger's WWTP was not determined to be a threat based on its wastewater treatment performance. There was no evidence presented that Laniger's WWTP had ever had intermittent treatment process failure, seepage to the lagoon system from effluent containment areas, or overflow during storm events. Those were the concerns related to package plants that were described in the SWIM Plan and the Department's 1991 report. Laniger's WWTP was not determined to be a threat based on evidence that it was causing or contributing to excess nutrients in Warner Creek or in that part of the St. Lucie River nearest to Laniger's WWTP. No evidence was presented that there are excess nutrients in Warner Creek or in that part of the St. Lucie River nearest to Laniger's WWTP. The Department's 1991 report concluded that the solution for package plants threats was to eliminate the package plants and connect their wastewater flow to centralized sewage collection and treatment facilities. To date, over 90 of the 155 package plants identified in the Department's 1991 report as threats to the water quality of the lagoon system have been connected to centralized sewage collection and treatment systems. The 1999 Permit and Administrative Order On August 26, 1999, the Department issued Domestic Wastewater Facility Permit No. FLA013879 to Laniger for the operation of its WWTP. Attached to and incorporated into Laniger's 1999 permit was Administrative Order No. AO 99-008- DW43SED. The administrative order indicates it was issued pursuant to Section 403.088(2)(f), Florida Statutes. That statute pertains to discharges that "will not meet permit conditions or applicable statutes and rules" and requires that the permit for such a discharge be accompanied by an order establishing a schedule for achieving compliance. The administrative order contains a finding that the Beacon 21 WWTP is a threat to the water quality of the lagoon system and that the WWTP "has not provided reasonable assurance . . . that operation of the facility will not cause pollution in contravention of chapter 403, F.S., and Chapter 62-610.850 of the Florida Administrative Code." The cited rule provides that "land application projects shall not cause or contribute to violations of water quality standards in surface waters." The administrative order required Laniger to connect its WWTP to a centralized wastewater collection and treatment [facility] "within 150 days of its availability . . . or provide reasonable assurance in accordance with Chapter 620.320(1) of the Florida Administrative Code that continued operation of the wastewater facility is not a threat to the water quality of the Indian River Lagoon System." As a result of an unrelated enforcement action taken by the Department against Martin County, and in lieu of a monetary penalty, Martin County agreed to extend a force main from its centralized sewage collection and treatment facility so that the Laniger WWTP could be connected. The extension of the force main was completed in April 2003. On April 10, 2003, the Department notified Laniger by letter that a centralized wastewater collection and treatment system "is now available for the connection of Beacon 21." In the notification letter, the Department reminded Laniger of the requirement of the administrative order to connect within 150 days of availability. On May 9, 2003, Laniger's attorney responded, stating that the administrative order allowed Laniger, as an alternative to connecting to the centralized wastewater collection and treatment system, to provide reasonable assurance that the WWTP was not a threat to the water quality of the lagoon system, and Laniger had provided such reasonable assurance. Laniger's attorney also stated, "due to the location of Martin County's wastewater facilities, such facilities are not available as that term is defined in the [administrative] order." On September 29, 2003, the Department issued a warning letter to Laniger for failure to connect to the Martin County force main and for not providing reasonable assurance that the WWTP will not cause pollution in contravention of Chapter 403, Florida Statutes. The Department took no further formal action until it issued the NOV in August 2005. Laniger's challenge of the NOV was consolidated with this permit case. The Permit Renewal Application In an "enforcement meeting" between Laniger and the Department prior to the expiration of 1999 permit, the Department told Laniger that it would not renew Laniger's WWTP permit. Later, when Laniger filed its permit renewal application, the Department offered to send the application back so Laniger would not "waste" the filing fee, because the Department knew it was not going to approve the application. Laniger submitted its permit renewal application to the Department on February 15, 2005. The Department considered Laniger's permit application to be complete, but proceeded to prepare the Notice of Denial without any technical review of the application. The Department denied the application on April 6, 2005. The Department's Notice of Permit Denial stated that the permit was denied because Laniger had not connected to the available centralized wastewater collection and treatment system nor provided reasonable assurance that the WWTP "is not impacting water quality within the Indian River Lagoon System." The record evidence showed that the "reasonable assurance" that would have been necessary to satisfy the Department was more than the reasonable assurance the Department usually requires for package plants, and more than the Department would have required if Laniger's WWTP was 100 feet from Warner Creek. Competent substantial evidence was presented that Laniger's WWTP is capable of being operated in accordance with the statutes and rules of Department generally applicable to package wastewater treatment plants. Laniger's 1999 permit expired on August 25, 2004. Laniger has operated the plant continuously since the permit expired. Whether the Martin County Facility is Available As discussed below in the Conclusions of Law, it is concluded that the Department did not have authority to require Laniger to connect the WWTP to the Martin County force main or to require assurance beyond the reasonable assurance generally required for package treatment plants in order to obtain a permit. However, because considerable evidence and argument was directed to whether the force main was available, that issue will be addressed here. The Martin County force main was not extended to the boundary of the Laniger WWTP site. The force main terminates approximately 150 feet north of the Laniger WWTP site and is separated from the WWTP site by a railroad and railroad right-of-way. Laniger presented undisputed evidence that the cost to connect to the Martin County force main would be approximately $490,000 and that cost was prohibitively high, given the relatively small number of households served by the WWTP. The Laniger WWTP is subject to rate regulation by the Public Service Commission (PSC). Laniger presented evidence suggesting that connection to the Martin County force main would result in rates that would not be approved by the PSC. The evidence was speculative and not competent to support a finding regarding PSC action. The evidence does show, however, that PSC rate regulation was not a factor that the Department considered when it determined that the Martin County force main was available. There is no Department rule that defines when a centralized sewage collection and treatment facility is "available." The determination that the Martin County force main was available to Laniger was made informally by members of the Department's compliance staff in the Department's St. Lucie office. Mr. Thiel testified that he considered the force main to be available because it was "in close proximity" to Laniger's WWTP. However, Mr. Thiel admitted that there is a difference of opinion within DEP as to when a facility is available and reasonable persons could disagree about whether a facility was available. Mr. Thiel thought that the cost to connect is a factor to be considered in determining whether a facility is available, but another Department employee did not think cost should be considered. There was no evidence that the Department took into account Laniger's cost to connect in determining that the Martin County force main was available. The Department simply assumed that the Martin County force main was close enough to the Laniger WWTP site that the cost to Laniger would not be prohibitive. In addition, the Department was aware of other package plants that had connected to centralized sewage collection and treatment facilities that were the same distance or a greater from the package plant, and the Department did not hear from the owners of the package plants that the costs were prohibitive. Timothy Powell of the Department stated that force mains are usually made available by extending the force main so that it is "abutting the property as much as possible." He also stated that he assumed that Martin County would extend its force main under the railroad and to the boundary of the Laniger WWTP site after Laniger agreed to connect. However, there was no evidence to show that this is Martin County's intent, and the Department did not tell Laniger that Laniger did not have to connect to the force main unless Martin County brought the line to the boundary of the WWTP site. If the Department had authority to require Laniger to connect to the Martin County force main when it became available, and in the absence of any rule criteria to determine when a centralized sewage collection and treatment facility is available, the determination would have to be based on reasonableness. Reasonableness in this context must take into account the cost of the connection. Cost is the inherent reason that Laniger was not required to connect to the Martin County centralized sewage collection and treatment facility without regard to whether the facility was available. Laniger showed that the cost of connecting to the force main is unreasonably high due to the need to construct a line beneath the railroad. Therefore, Laniger proved by a preponderance of the evidence that the Martin County force main is not available.
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 granting Laniger Enterprises of America, Inc., a renewal of its wastewater treatment plant operating permit. The permit should contain the same conditions as were contained in the 1999 permit, with the exception of those conditions derived from Administrative Order No. AO 99-008- DW43SED. DONE AND ENTERED this 19th day of September, 2006, in Tallahassee, Leon County, Florida. S BRAM D. E. CANTER 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 19th day of September, 2006.
Findings Of Fact On or about December 28, 1987 Hy Kom filed with the Department an application for a permit to construct a .0126 MGD Advanced Waste Water Treatment Plant on Emerson Point, Snead Island in Manatee County. The proposed waste water treatment plant would discharge effluent into the waters of Terra Ceia Bay in Manatee County. The proposed waste water treatment plant would discharge effluent into the waters of Tampa Bay in Manatee County. The proposed waste water treatment plant would discharge effluent into the waters of Manatee River in Manatee County. The waters of Terra Ceia Bay have been designated Outstanding Florida Waters (OFW) by the Department. On or about April 27, 1989 the Department issued a Notice of Permit Denial concerning Hy Kom's permit application. The parties stipulate the Intervenor, Manasota-88, has standing to intervene as a party Respondent and to object to the issuance of the permit. Petitioner's evidence can best be summarized by what was not submitted. First, the expert witness called to identify the application had not prepared any part of the application or verified any of the studies presented therein. Similarly Petitioner's expert on the proposed treatment plant did not testify that Petitioner was committed to using this plant, or that the construction of the plant and the operation of the plant would comply with statutory and rule requirements. The only witness called by Petitioner to testify to the effect the discharge from the proposed advanced waste water treatment plant would have on the receiving waters was also Respondent's expert; and this witness testified that the effluent discharge from this proposed plant would have an adverse effect on the receiving waters, would seriously degrade the receiving waters as a nursery habitat for both crustacea and fishes endemic to the area, and that no reasonable assurances that this would not happen were ever presented by the Petitioner. This witness further testified that no discharge into these receiving waters would be acceptable not only because of the nitrogen level (which was the most significant reason for denying the permit) but also because even a discharge of absolutely pure water would upset the salinity of the receiving waters at the critical time the receiving waters act as a marine nursery.
Recommendation It is RECOMMENDED that a Final Order be entered denying the application of Hy Kom Development Company, for a permit to construct and operate an advanced waste water treatment facility at Emerson Point, Snead Island, Manatee County, Florida. DONE and ORDERED this _15th_ day of September, 1992 in Tallahassee, Leon County, Florida. COPIES FURNISHED: JAMES W. STARNS ESQ 501 GOODLETTE RD SUITE D-100-24 NAPLES FL 33940 W DOUGLAS BEASON ESQ ASST GENERAL COUNSEL K. N. AYERS 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 _15th_ day of September, 1992. DEPT OF ENVIRONMENTAL REGULATION 2600 BLAIRSTONE RD TALLAHASSEE FL 32399 2400 THOMAS W REESE ESQ 123 EIGHTH ST N ST PETERSBURG FL 33701 DANIEL H THOMPSON ESQ GENERAL COUNSEL DEPT OF ENVIRONMENTAL REGULATION 2600 BLAIRSTONE RD TALLAHASSEE FL 32399 2400 CAROL BROWNER SECRETARY DEPT OF ENVIRONMENTAL REGULATION 2600 BLAIRSTONE RD TALLAHASSEE FL 32399 2400
The Issue Whether Permit No. DO19-101251 issued to Mr. Vail on July 11, 1985 to construct and operate an on-site wastewater treatment and disposal system should be revoked?
Findings Of Fact Mr. Vail is the owner and operator of a business called the St. George Inn and Restaurant (hereinafter referred to as the "Inn"). The Inn is located at the southeast corner of the intersection of Franklin Boulevard and Pine Avenue on St. George Island, Florida. In May of 1984 Mr. Vail spoke with an employee of the Department of Health and Rehabilitative Services about obtaining a permit to construct a septic tank on his property for use by the Inn for the treatment and disposal of wastewater. Mr. Vail was instructed to submit a design of the septic tank for approval. Mr. Vail contracted with McNeill Septic Tank Company for the design and construction of the septic tank. The evidence failed to prove when Mr. Vail applied with the Department of Health and Rehabilitative Services for a permit. As of March, 1985, however, Mr. Vail had not received approval or disapproval of his application from the Department of Health and Rehabilitative Services. Mr. Vail, therefore, went to the Governor's office to seek help in getting a response. Shortly after contacting the Governor's office, the Department of Health and Rehabilitative Services informed Mr. Vail that he needed to obtain a permit from the Department and not from the Department of Health and Rehabilitative Services. On or about March 18, 1985, Mr. Vail filed an Application to Operate/Construct Industrial Wastewater Treatment and Disposal Systems (hereinafter referred to as the "Application"), with the Department. The Application was prepared by Brown and Associates Civil Engineers and Land Surveyors, Inc., Mr. Vail's engineering consultant. The Application was certified by Benjamin E. Brown, Professional Engineer. Mr. Vail signed the Application as "owner" and indicated that he was aware of the contents of the Application. In the Application, "St. George Inn Restaurant" is listed as the "Source Name." Under Part II, A of the Application, the applicant is asked to "[d]escribe the nature and extent of the project." In response to this request, the following answer was given: This project will provide a sewage disposal system for a one hundred and fifty (150) seat restaurant on St. George Island. Sizing of the septic tank system is based on 50 GPD/seat and secondary treatment will be provided by the design proposed. Under Part III, A of the Application, the applicant is asked to provide the following information and the following answers were given: Type of Industry Restaurant . . . . 3. Raw Materials and Chemicals Used Food preparation only. Normal Operation 12 hrs/day 7 days/week . . . . If operation is seasonal, explain This restaurant will be used the most during the summer months which corresponds with ocean/beach recreation & the tourist trade. Nowhere in the Application is it indicated that the permit applied for involved anything other than a restaurant. The Application gives no information from which the Department could have known that the proposed wastewater treatment and disposal system would handle waste from guest rooms or an apartment. In the Application Mr. Vail sought approval of a permit to construct and operate a wastewater treatment and disposal system to serve a 150 seat restaurant. In the Application Mr. Vail sought a permit for a system which was to have a design flow of 7,500 gallons per day based on 50 gallons, per seat, per day water usage. An employee of the Department wrote a memorandum dated May 5, 1985, recommending approval of the Application. The Department determined, however, that the size of the property on which the Inn was to be located was not large enough for the drain field necessary to accommodate a 150 seat restaurant. Therefore, Mr. Brown modified the proposed system and resubmitted application data indicating that a 108 seat restaurant would be constructed. The design flow of the new proposal was 2,160 gallons per day based on 20 gallons per seat per day. Mr. Brown had requested that the Department approve a system based upon the newly submitted design flow. The Department and Mr. Brown both agreed that this design flow was adequate; that it was reasonable to anticipate and provide for the treatment and disposal of a maximum of 2,160 gallons per day design flow. The effect of reducing the design flow and the number of seats was to allow a shortened drain field which could be accommodated by the size of the property the Inn was to be located on. On June 27, 1985, Mr. Vail arranged for a notice to be published in the Apalachicola Times. That notice provided, in pertinent part, the following: State of Florida Department of Environmental Regulation Notice of Proposed Agency Action on Permit Application The department gives notice of its intent to issue a permit to Jack Vail to construct a restaurant and on-site wastewater treatment and disposal system [sic] at Franklin Boulevard and Pine Avenue, St. George Island. The treatment consists of grease trap, septic tank, and sand filter followed by disposal into a drainfield. The project meets applicable standards and will not impair the designated use of the underlying ground water. There is no anticipated impact on surface waters or air quality. . . . . This notice was sent to Mr. Vail by the Department and he made arrangements for it to be published. Nowhere in the notice is it indicated that the system to be approved by the Department is for anything other than a restaurant. On July 11, 1985, less than four months after the Application was filed with the Department, the Department issued Permit Number DO19-101251 (hereinafter referred to as the "Permit"). In the cover letter sent with the Permit the Department indicated that the Permit allowed Mr. Vail "to construct and operate a 2,160 gallon per day, on-site wastewater treatment and disposal system serving St. George Inn Restaurant. . . ." The Department also indicates in the Permit that it is for the "St. George Inn Restaurant." The Permit also provides, in pertinent part, the following with regard to the purpose of the Permit: The above named applicant, hereinafter called Permittee, is hereby authorized to perform the work or operate the facility shown on the application and approved drawing(s), plans, and other documents attached hereto or on file with the department and made a part hereof and specifically described as follows: Construct and operate a 108 seat restaurant with an on-site wastewater treatment and disposal system. Wastewater flows shall be a maximum of 2,160 gallons per day generated by domestic facilities and kitchen wastes . . . Construction shall be in accordance with application dated March 18, 1985 and additional information submitted April 29, 1985, specifications and other supporting documents prepared by Brown and Associates and certified by Benjamin E. Brown, P.E. and submitted to the Department on June 5, June 17, and June 20, 1985. The Permit also contains the following "General Condition" number 2 and "Specific Condition" number 15: . . . . 2. This permit is valid only for the specific processes and operations applied for and indicated in the approved drawings and exhibits. Any unauthorized deviation from the approved drawings, exhibits, specifications, or conditions of this permit may constitute grounds for revocation and enforcement action by the department. . . . . 15. The Department shall be notified and prior approval shall be obtained of any changes or revisions made during construction. . . . . The Permit provides the following with regard to the effect of the conditions of the Permit: The terms, conditions, requirements, limitations, and restrictions set forth herein are "Permit Conditions", and as such are binding upon the permittee and enforceable pursuant to the authority of sections 403.161, 403.727, or 403.859 through 403.861, Florida Statutes. The permittee is hereby placed on notice that the Department will review this permit periodically and may initiate enforcement action for any violation of the "Permit Conditions" by the permittee . . . . During the week after the Permit was issued, Mr. Vail obtained a building permit from Franklin County for the construction of the "inn." In February, 1986, after construction of the Inn had begun, Department inspectors went to the construction site of the Inn. The Permit authorized this inspection and other inspections carried out by the Department. The Department determined that the Inn being constructed by Mr. Vail included a restaurant, an apartment on the third floor of the Inn with two bathrooms, and eight guest rooms on the second floor, each containing a bathroom. This was the first time that the Department knew that Mr. Vail's facility was to include guest rooms and living quarters in addition to containing a 108 seat restaurant. In March of 1986, the Department sent a warning letter to Mr. Vail notifying him of the violation of the General Conditions of his Permit: the use of the approved system for the treatment and disposal of wastewater from the ten bathrooms in the guest rooms and the two bathrooms in the apartment in addition to the 108 seat restaurant. On April 1, 1986, Department personnel met with Mr. Vail and Mr. Brown. The Department reminded Mr. Vail and Mr. Brown that the Permit requested and approved by the Department was for a 108 seat restaurant only. The Department had not authorized a system which was to be used for a 108 seat restaurant and ten additional bathrooms. Pursuant to General Condition 14, the Department informed Mr. Vail that it needed an engineer's evaluation of the ability of the system which had been approved to handle the additional flow which could be expected from the additional ten bathrooms. By letter dated April 1, 1986, the Department memorialized the meeting and indicated that Mr. Vail could operate a 100 seat restaurant and the apartment during the interim. By letter dated May 8, 1986, Mr. Brown asked for additional time to submit the evaluation requested by the Department. The Department approved this request by letter dated May 14, 1986. By letter dated May 16, 1986, Mr. Brown submitted an engineering evaluation which proposed modifications to the approved system to handle the additional ten bathrooms. By letter dated June 13, 1986, the Department indicated that the evaluation was generally acceptable" but requested additional information. In January, 1987, before the additional information was submitted, Mr. Brown died in an airplane accident. No evidence was presented to explain why the information requested by the Department in June of 1986 had not been submitted before January, 1987. In March, 1987, the Department inspected Mr. Vail's facility again. In April, 1987, the Department informed Mr. Vail that the Department would take action to revoke the Permit. Before the Administrative Complaint was issued, the Department requested that certain information be provided on behalf of Mr. Vail by an engineer in an effort to resolve the dispute. Mr. Vail did not, however, obtain the services of an engineer. Instead, Mr. Vail sent the Department information purporting to show the amount of water which had been used at the Inn. That information failed to prove the ability of the system that the Department had approved to handle the maximum wastewater which could be expected from maximum use of the 108 seat restaurant and ten additional bathrooms. At best, the information submitted by Mr. Vail is partial proof that the system is capable of handling the wastewater that has been generated at the Inn for the period of time for which the information relates. No competent substantial proof has been submitted to indicate that the system is capable of handling the maximum wastewater flows which may be experienced or even that the system is adequately handling the current flow. All that has been proved is that there is no apparent problem with the system in handling the current flow. In September, 1987, the Department issued the Administrative Complaint. Pursuant to this Complaint, the Department has sought the revocation of the Permit and prescribed certain orders for corrective action. No application has been submitted by or on behalf of Mr. Vail to the Department to construct and operate a wastewater treatment facility designed to accommodate the sewage flows which may be generated by the Inn as it has been constructed. Although the Department of Health and Rehabilitative Services and other agencies were aware that the Inn includes a restaurant and guest rooms, the Department was never so informed.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department issue a Final Order requiring that Mr. Vail comply with all of the corrective orders, except Paragraph 18, contained in the Administrative Complaint. DONE and ORDERED this 11th day of March, 1988, in Tallahassee, Florida. LARRY J. SARTIN 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 11th day of March, 1988. APPENDIX TO RECOMMENDED ORDER, CASE NUMBER 87-4242 The parties have submitted proposed findings of fact. It has been noted below which Proposed findings of fact have been generally accepted and the paragraph number(s) in the Recommended Order where they have been accepted, if any. Those proposed findings of fact which have been rejected and the reason for their rejection have also been noted. The Department's Proposed Findings of Fact Proposed Finding Paragraph Number in Recommended Order of Fact of Acceptance or Reason for Rejection 1 Conclusion of law. 2 1. 3 6. 4 10. 5 12 and 13. 6 14. 7 15. 8 18. 9 19. 10 20. 11-12 16. 13 21. 14 23. 15 24. 16 25. 17 26. 18-19 27. 20 28. 21 29 22 Hereby accepted. Mr. Vail's Proposed Findings of Fact 1A 15. Not supported by the weight of the evidence and irrelevant. Hearsay and irrelevant. Although technically true, this is not the issue in this case. The evidence did not prove that the system "can in actuality handle three times the amount permitted." Not supported by the weight of the evidence and irrelevant. 2A Not supported be the weight of the evidence. Exhibit 6 indicates that the Department was aware that the Inn included "hotel rooms" but not the number. Irrelevant. The evidence did not prove that the Department was aware of the scope of the project. Not supported by the weight of the evidence. 3A Irrelevant. Not supported by the weight of the evidence and irrelevant. Even if this were true, the fact remains that the Department was unaware that the Inn included guest rooms or an apartment. Irrelevant. 4A-B Irrelevant. 5A-B Irrelevant. 6A 2-4. B 5. 6 and 11. Not supported by the weight of the evidence. See 12. 13 and 15. Not supported by the weight of the evidence and irrelevant. Not supported by the weight of the evidence. 7A-C Not supported by the weight of the evidence and irrelevant. 8A-D Not supported by the weight of the evidence and irrelevant. 9A-B Not supported by the weight of the evidence and irrelevant. 10-12 Not supported by the weight of the evidence and irrelevant. COPIES FURNISHED: Richard L. Windsor, Esquire State of Florida Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Mr. John Vail St. George Inn Post Office Box 222 St. George Island, Florida 32328 Dale Twachtmann, Secretary State of Florida Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Daniel H. Thompson, Esquire General Counsel State of Florida Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400
The Issue Whether General Water Use Permit (WUP) Number 20012185.000 (Permit) meets the conditions for issuance as established in Section 373.223, Florida Statutes, and Rule 40D-2.301, Florida Administrative Code, and should be issued to Farmland Hydro Limited Partnership and Frank T. Basso, Jr. and Redland Growers Exchange, Inc.
Findings Of Fact The Parties DCAP is not-for-profit corporation incorporated in the State of Florida. Behrens is the President of DCAP. See also Findings of Fact 63-77. Farmland Hydro is a Delaware Limited Partnership authorized to transact business in Florida, and is the owner of the property leased by Basso/Redland, which is the subject of this WUP. Frank T. Basso, Jr., is a third generation farmer, who operates as Redland Growers Exchange, and seeks a General WUP to authorize groundwater withdrawals for crop irrigation. The District is the administrative agency charged with the responsibility to conserve, protect, manage, and control water resources within its boundaries pursuant to Chapter 373, Florida Statutes, and the rules promulgated thereunder as Chapter 40D, Florida Administrative Code. The Proposed Water Use An Application for a General WUP was submitted by Farmland Hydro and Basso, as co-applicants, and received by the District on April 11, 2001. After receipt of additional information, the Application was deemed complete on October 22, 2001. The Applicants seek a General WUP to authorize a new water use for the irrigation of 140 acres for the production of both Spring and Fall row crops, using a seepage-with-mulch irrigation system.1 Basso plans to grow tomatoes and/or peppers in the Spring, and squash and/or cucumbers in the Fall. Crop planting for both seasons will be phased-in over a one-month period. Water allocation quantities are calculated on a weekly phase-in basis of approximately 35 acres for each planting date. The total time that the parcel will be in use for farming, to include planting and harvesting for each crop, is approximately six months per year. The subject parcel is part of a 250-acre tract known as the Brushy Creek Tract and is located in Hardee County approximately two miles south of the town of Ona; approximately two miles south of the intersection of U.S. Highway 64 and County Road 663; and is within the Southern Water Use Caution Area (SWUCA). The subject parcel currently does not contain a water well. The Brushy Creek Tract is a larger parcel of approximately 1,230 acres leased from Farmland Hydro by Redland and also by Parker Farms for cattle grazing, farming, and hunting. The subject parcel is used for cattle grazing and is surrounded by land owned by Farmland Hydro and used for either cattle grazing or agricultural row crops. Farmland Hydro also operates an additional approximately 1,941 acres of property near the subject parcel, which is used for citrus groves. Farmland Hydro has consumptive WUPs for this property. The closest existing legal user to the proposed Basso well site is another well on the Farmland Hydro property. As is generally done with vegetable crop production in Florida, vegetable crops grown on the Farmland Hydro property are grown in rotation with pasture, and have been rotated in this manner for many years. Typically, farmers have farmed a piece of land for one, two or three years and then, to avoid the buildup of insects and diseases, have allowed the land to revert to pasture and have moved on to another field for crop production. The subject parcel for which the WUP is being sought will be similarly treated. Crop rotation is an important agricultural best management practice that is used to address pest management, soil conservation, and maximizing nutrients for obtaining favorable crop production. Soil conservation is important to Basso, notwithstanding that there is a response in the Application that no approved Soil Conservation Service plan exists for the operation included in the Application. If the WUP is issued and the subject parcel is placed into crop production, another parcel of land will be taken out of crop production by Basso, resulting in the discontinuation of another permitted well. As a result, the issuance of this WUP will not result in a "water use change." Determination of Reasonable Demand/Allocated Quantities In determining whether a proposed water use is reasonable-beneficial and in the public interest, the District calculates the appropriate permit quantities for the particular water use, which is a function of demonstrated need, or demand for water; efficiency of the water treatment and distribution systems; whether water is sold or transferred to other entities; whether acceptable water can be acquired from lower quality sources; and whether conservation practices are employed. District Basis of Review (BOR), page B3-1. The reasonable need for agricultural water use is generally composed of one or more demand components, depending upon the specific agricultural use. "Typically, the reasonable need for irrigation water uses is equal to the supplemental crop requirement divided by the system efficiency or the system design capacity, whichever is less." "The supplemental crop requirement is the amount of water needed for a particular crop beyond the amount of water provided by effective rainfall." The supplemental crop requirement is generally determined by using the Agricultural Water Use Calculation Program (AGMOD) Version 2.1, which is based on the modified Blaney-Criddle method. This program takes into account site specific information such as crop type, growing period, evapotranspiration rate, soil type, rainfall, irrigation method and number of irrigated areas. "In most cases, the supplemental irrigation requirement is determined for a 2 in 10-year drought condition." The AGMOD program determines an inch-application rate which, when applied to the number of acres to be irrigated, results in a calculation of total annual average and peak monthly quantities for the proposed water use. District BOR, pages B3-4 and 3-5. See also District Water Use Design Aids, pages C4-1 through C4-7. In determining the allocated quantities, or reasonable demand for water, the District seeks to avoid both over- allocating water and under-allocating water for the specific crop intended, to ensure that the permitted amount is sufficient for the "2 in 10-year drought condition." Consequently, the allocated quantities arrived at by District staff through use of the AGMOD methodology may be different from the quantities indicated on an applicant's initial application, which are generally estimated without benefit of an agricultural water use calculation program. The AGMOD program was used to calculate water use quantities for the proposed water use. The allocated quantities for Basso's proposed use are 454,000 gallons per day (gpd) on an annual average basis and 1,241,000 gpd, as a peak month quantity. No quantities were requested or allocated for crop protection. See Finding of Fact 52. Modeling for Simulated Impacts As part of the application review process, the District evaluates potential impacts to existing legal uses of water, the water resources and environmental features that may result from the proposed groundwater withdrawals. To assist in the review process, analytical and numerical models, which incorporate best available hydrogeologic parameters for the area being considered for a permit, are used to simulate drawdowns for the withdrawal of the proposed quantities. The results of these simulations are used in the evaluation of potential impacts to assess whether the application meets the conditions for issuance. The District undertook simulation modeling of the potential effects of the proposed water withdrawals to be authorized by the permit. The allocated quantities were entered into the MODFLOW 387 groundwater flow model, which is a three- layer model developed by the U.S. Geological Survey and is the generally accepted model for this purpose. Model layers were set up to represent the surficial, intermediate, and Upper Floridan aquifers. (The Applicants seek to pump water solely from the Upper Floridan Aquifer.) There are limitations to the model in that the model assumes a homogeneous isotropic aquifer, with no preferred flow direction. In actuality, there is variability in the geology of the area. Modeling is intended to serve as a screening tool for assessing localized impacts anticipated from a proposed water use and is based upon the best available information. As distance from the proposed withdrawal site increases, the reliability of the modeling decreases, due to the variability in the geology and other parameters or boundary conditions that can affect the model. Use of the MODFLOW groundwater model allows the District to look at potential impacts at the site, and in the proximity of the site, and assists the District in assessing possible cumulative impacts associated with a proposed use. To assist in assessing potential impacts from the proposed use, a Peak Month modeling simulation was undertaken by the District, which simulates the effect of pumping the proposed Peak Month withdrawal rate of 1,241,000 gpd for 90 consecutive days, with no recharge to the aquifer systems. The model essentially presents a worst case scenario that is a more severe prediction than what is actually likely to occur from the permitted use under normal conditions. Simulating the period of greatest demand on the hydrologic system is likely to provide maximum protection to existing legal water users and the water resources. The Peak Month simulation undertaken by the District predicts drawdowns in the potentiometric surface of the Upper Floridan Aquifer of approximately 2.6 feet at the proposed withdrawal site; less than 1.4 feet at the nearest property boundary (approximately 1,250 feet from the proposed withdrawal site); and less than 1.2 feet at the nearest existing legal user (a Farmland Hydro well approximately 3,500 feet from the proposed withdrawal site). These numbers did not raise a concern for District staff. ("Potentiometric surface" is "a surface defined by the level to which water rises in an open pipe that is constructed into or all the way through an artesian aquifer. This is measured in feet relative to NGVD or sea level. The level to which water rises inside this open pipe is a function of the pressures on the water in the artesian aquifer." District BOR, page B-xii.) The Peak Month simulation predicts drawdowns in the intermediate aquifer of approximately 0.9 feet at the proposed withdrawal site, and less than 0.9 feet at the property boundary, and at the nearest existing legal user. The Peak Month simulation predicts drawdowns in the water level of the surficial aquifer (water table) of approximately 0.01 feet or less at the proposed withdrawal site, property boundary and nearest existing legal user. Based upon the Peak Month simulations, the District reasonably determined that further cumulative impact modeling was not necessary in order to assess localized cumulative impacts resulting from the proposed use. To assess regional cumulative impacts, the District evaluated Regional Observation Monitoring Program (ROMP) data and found no significant trends in withdrawals in recent years, other than a slight decline attributed to the recent drought. Conditions of Issuance of the Proposed Permit In order to obtain a water use permit, an applicant must establish that the proposed use of water is a reasonable- beneficial use, will not interfere with any existing legal use of water, and is consistent with the public interest, by providing reasonable assurance, on both an individual and cumulative basis, that the water use meets the conditions for issuance as specified in Section 373.223(1), Florida Statutes, and Rule 40D-2.301, Florida Administrative Code. A permit must be obtained from the District prior to withdrawing water, where the withdrawal is from a well having an outside diameter of six inches or more at land surface, where the annual average withdrawal from all sources is 100,000 gpd or greater, or where the total combined withdrawal capacity from all sources is greater than or equal to 1 mgd. The proposed water use falls within these parameters. Rule 40D-2.041(1)(b) and (c), Florida Administrative Code. The quantities allocated for the proposed use have been determined by the District to be necessary to fulfill a certain reasonable demand, for the reasons specified herein. To assist in assessing impacts, the District utilizes a network of ROMP wells to obtain basic groundwater monitoring data over time and to help characterize the lithology, stratigraphy, aquifer depths, water levels and, in some cases, water quality for the various water resources. Data obtained from the ROMP and other wells is compiled to ascertain aquifer characteristics within the District and is also integrated into the District's modeling efforts pertaining to proposed water uses. ROMP well No. 31 is located just off the northeast corner of the Basso site. Having a ROMP well adjacent to the Basso site increases confidence in the specific geological information being used in the groundwater model to assess potential impacts from the proposed uses. ROMP well No. 17 is located approximately 1/2 mile from DCAP member Behren's well. Data from both wells were considered in assessing potential impacts from the proposed water use. Based on available information, the possible sources of groundwater for the proposed use at the Basso site are the surficial aquifer, intermediate aquifer, and the Upper Floridan Aquifer systems. To ensure sufficient quantities of water for the proposed use and to avoid potential impacts to environmental features, such as wetlands and surface waters, the District will require the proposed use to limit withdrawals to solely the Upper Floridan Aquifer. By examining stratigraphic cross sectional information generated from the ROMP wells, particularly ROMP No. 31 well, which is in close proximity to the Basso site, District staff were able to determine, with reasonable certainty, the approximate depths of the aquifers at the Basso well site. To ensure that the well will be open solely to the Upper Floridan Aquifer, the permit requires the Basso well to have a minimum of 400 feet of casing, with an estimated well depth of 1,000 feet. Based upon available information concerning the construction of other wells in the vicinity of the proposed Basso well, the District is reasonably assured that a well cased for a minimum of 400 feet will draw water only from the Upper Floridan Aquifer and will minimize the potential for water to move between the aquifers through the well. The well construction requirements imposed for Basso's well are in line with the best available stratigraphic information and with known construction of wells in the area. By casing the well to a depth of 400 feet and due to the extremely low leakage of the intermediate confining unit, the intermediate and surficial aquifers will be buffered from impacts associated with the proposed use. The District will deny a water use permit application if the proposed withdrawal of water, together with other withdrawals, would cause an unmitigated adverse impact on a legal water withdrawal existing at the time of the application. The District considers an adverse impact "to occur when the requested withdrawal would impair the withdrawal capacity of an existing legal withdrawal to a degree that the existing withdrawal would require modification or replacement to obtain the water it was originally designed to obtain." District BOR, page B4-14. Based upon an assessment of individual and cumulative regional information, there are no existing legal uses of water that will be adversely impacted as a result of the proposed withdrawals. Based upon an assessment of individual and cumulative regional information, no quantity or quality changes that adversely impact the water resources, including both surface and groundwaters, are anticipated from the proposed withdrawals. The District requires that consideration be given to the lowest water quality available, which is acceptable for the proposed use. Lower quality water includes reclaimed water, collected stormwater, recovered agricultural tailwater, saline water or other sources. District BOR, page B4-12. For the proposed water use, there is no viable lower quality water source and no reclaimed water available near the site to use as an alternative to groundwater pumping. The Applicants are proposing to use the lowest quality water that is available. There are no known concerns regarding the quality of water in the Upper Floridan Aquifer at this location in Hardee County. Restricting the proposed water use to the Upper Floridan Aquifer will not cause water quality concerns or result in pollution to any of the aquifers. Simulated drawdowns to the Upper Floridan Aquifer of approximately 2.6 feet at the proposed withdrawal site, less than 1.4 feet at the nearest property boundary, and less than 1.2 feet at the nearest permitted well, provide reasonable assurance that adverse impacts will not occur from the proposed water use. Simulated drawdowns to the intermediate aquifer of 0.9 feet at the proposed withdrawal site, and less as the distance from the proposed withdrawal site increases, provide reasonable assurance that adverse impacts will not occur from the proposed water use. Simulated drawdowns to the surficial aquifer of 0.01 feet or less at the proposed withdrawal site, and less as the distance from the proposed withdrawal site increases, constitute a nearly undetectable impact to the surficial aquifer, which is not an adverse impact. The modeling simulations demonstrate that the proposed withdrawals will have no significant effect on the surficial aquifer and, therefore, will not cause adverse impacts to environmental features such as wetlands, lakes, streams, fish and wildlife, or other natural resources. None of the simulated drawdowns are considered to be predictions of adverse impacts, not even in the localized vicinity of the well site. Mr. Jackson explained that because the localized modeling simulations were small or insignificant and showed no adverse impacts, cumulative modeling is not considered necessary. Reasonable assurance on a cumulative basis is determined by assessing the potential localized impacts in conjunction with existing cumulative data for the region, such as the available ROMP data and hydrographs, which depict the existing regional condition, taking into account, on a cumulative basis, all existing uses as well as rainfall conditions and climate. Based on an assessment of the cumulative data and the modeling for individualized impacts, and applying professional judgment, District staff reasonably concluded that the proposed water use presents no concerns that it will cause, on either an individual or a cumulative basis, adverse impacts to the water resource or existing legal uses. Minimum flows and levels have not been established by the District for the area where the proposed use is located. (The parties stipulated that the District has not established minimum flows and levels pursuant to Section 373.042, Florida Statutes, for the Southern Water Use Caution Area (SWUCA)). Therefore, Rule 40D-2.301(1)(d), Florida Administrative Code, (requirements for minimum flows and levels), is not applicable to the proposed permit. The proposed use presents no concerns for saline water intrusion. The proposed use raises no concerns regarding causing pollution to the aquifer. There are no offsite land uses that will be adversely impacted as a result of this permit. Basso currently uses best management practices for water conservation in his ongoing farming operations, and intends to use such practices with the new farming operation authorized under the permit. In keeping with such practices, irrigation is stopped when the water reaches the end of the watering ditch. Basso uses seepage irrigation and tries to regulate the ditches so that there is a minimum, if no, runoff. Also, a watering cycle generally lasts from three to seven days before irrigation has to be resumed. Any runoff goes into "filtering ponds, before reaching ditches or creeks" in its raw content. Basso does not intend to farm during months of likely frost so no separate allocation for frost/freeze protection was requested or needed. Given these irrigation practices, water is not reasonably expected to be wasted. All necessary and feasible agricultural water conservation activities will be implemented upon issuance of the WUP. In addition, Specific Condition No. 3 of the proposed WUP requires the incorporation of best water management practices in all irrigation practices. The proposed use presents no concerns that it will otherwise be harmful to the water resource. The Applicants have met all the requirements for issuance of a WUP. Southern Water Use Caution Area The proposed water use site is located within the SWUCA. The District established the SWUCA as a means of addressing on a regional scale concerns about long-term impacts to the water resource. Water use caution areas were created in recognition of regional water concerns. There have been drought conditions in the area which have caused reduced aquifer levels. The proposed water use site is not within the "Most Impacted Area" (MIA), which is located approximately 18 miles to the west of the site in Manatee County, nor within the "East Tampa Bay Water Use Cautionary Area" (ETB WUCA), which is approximately six miles to the west of the proposed site, also in Manatee County. (The SWUCA includes the MIA and ETB WUCA.) Pending final adoption of rules for the SWUCA, the District will continue to issue WUPs for proposed water uses that meet the conditions for issuance. The District cannot treat new uses and existing renewal uses any differently when considering the issuance of a permit. Once SWUCA rules and minimum flows and levels are established, the District expects to rely on a more regional approach to address long-term cumulative impacts over the entire use caution area, instead of relying on a permit-by-permit basis to address regional concerns. Standard Condition No. 9 of the proposed WUP requires the permittee to cease or reduce withdrawals as directed by the District, if water levels in the aquifers fall below the minimum levels established by the District Governing Board. The proposed withdrawal will use a seepage with mulch irrigation method, which has a 50 percent efficiency level. See footnote 1. This is the minimum efficiency level currently required for agricultural WUPs within the SWUCA, which approve the use of this irrigation method. As SWUCA rules come into effect, a higher percentage efficiency level probably will be required, as is now required in the Eastern Tampa Bay Water Use Caution Area and also in the Highlands Ridge Water Use Caution Area. Consequently, Standard Condition No. 11 of the proposed WUP requires that, when SWUCA rules are implemented, the permittee must comply with any higher efficiency level or other special regulation that may be required for the SWUCA area. DCAP's Challenge to the Proposed WUP DCAP does not keep official membership records. It does not maintain any list of current members. According to Behrens, there are five members of the board of directors. DCAP does not hold corporate meetings, annual meetings or maintain corporate records. Members do not meet. There are no means to document the existence of members for this organization. Behrens is a member of DCAP. He has owned five acres adjoining the west side of Horse Creek (in DeSoto County) since 1985. Behrens complains that the District does not look at the cumulative effect on his well and other people he knows, such as George Chase. Behrens is concerned with any lowering of the water level in the area, including Horse Creek. He believes that approval of wells in the area, including the proposed well, is the straw that is breaking the camel's back. Mr. Chase shares this view. Behrens relies on an artesian free-flowing, two-inch diameter well, for domestic water use, located in the intermediate aquifer, approximately 150 feet deep. (Behrens' well is approximately 18-20 miles from the proposed Basso well.) For most of the time he has lived there, the well had an electric pump for obtaining water. Approximately one year ago, the pump went bad, and a replacement system has not been installed. Currently, Behrens has no pump on the well, and in dry periods, has to obtain water for domestic uses from nearby Horse Creek, which is low during the dry season. (Behrens depends on Horse Creek to pursue his recreation, wildlife, and aesthetic values.) Having a flowing artesian well will enable him to obtain water from the well without having to install an electrical pump, a situation which is desired by Behrens, in part, because the property is in a flood plain and experiences frequent flooding and electrical outages. Not all artesian wells flow. Artesian wells are completed into confined aquifers in which the water in a tightly cased well, will rise to a level above the formation being measured. Water would have to rise above the land surface to be a flowing well. For a well to be artesian, the well must be under confined pressure. For a well drawing water from a confined aquifer, such as the intermediate or the Upper Floridan Aquifer systems, the measured water level in the well is a reflection of the amount of potentiometric pressure in the well. This level can be affected just as much by the amount of recharge as it can by the amount of water withdrawals. There is no evidence that the proposed water use will adversely impact the flowing nature of either Behrens' or Chase's well. The evidence demonstrates that the proposed water use will not adversely impact Behrens' well. George Chase is a member of DCAP. Mr. Chase lives in Arcadia, DeSoto County, Florida. His property is adjacent to the Peace River. Mr. Chase's well is a two-inch diameter well, believed to be about 150 feet deep and equipped with a 12-volt DC solar-powered pump. Mr. Chase has in the past relied on artesian pressure within the confined intermediate aquifer to supply water to his solar-powered home. The solar-powered pump assists in supplying water to the home. In recent years, Mr. Chase has experienced low water pressure in his well. In Spring 2000, Mr. Chase contacted the District to complain that when an adjacent citrus grove was irrigating the groves, it appeared to affect the water level in his well such that the well's ability to flow was impacted. (According to Mr. Chase, his neighbors have had problems obtaining sufficient water from their wells and reaching water with standard pumps.) This citrus grove is an existing legal user of water that pre-existed Mr. Chase's well. In recent years, numerous domestic wells have been constructed in the vicinity of the Chase home that are large diameter wells utilizing submersible pumps with 110-volt AC power. These wells are more efficient at producing water than the type of well and pump being used by Mr. Chase, are located within a few hundred feet of Mr. Chase's well, and are open to the intermediate aquifer as is the Chase well. Based upon the District's experience in other areas, where there is a cluster of domestic wells drawing from the same intermediate aquifer, such adjacent wells have a much greater impact on each other than do other more distant wells, such as the previously discussed citrus irrigation wells, that are open solely to the confined Upper Floridan Aquifer System. This conclusion is based upon monitoring of the ROMP sites in the affected areas. Mr. Chase's well is approximately ten miles from the proposed withdrawal site. There is no basis to conclude that the proposed water use will cause any adverse impacts to Mr. Chase's well. DCAP members' interests are not affected any differently by the proposed use than are the interests of the general public. DCAP has produced no evidence to support its assertion that the issuance of this permit will result in lowered water levels in the Horse Creek and Peace River or other surface waters. DCAP has produced no evidence to support its assertion that the permit will cause adverse impacts to surface water flows or surface waters or to environmental features such as vegetation, fish, and wildlife. DCAP has produced no evidence that its substantial interests are affected by the proposed agency action.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that Southwest Florida Water Management District enter a final order: Determining that Farmland Hydro Limited Partnership and Frank T. Basso, Jr. and Redland Growers Exchange, Inc., have satisfied the requirements of Section 373.223, Florida Statutes, and Rule 40D-2.301, Florida Administrative Code, regarding conditions for issuance of WUPs;3 Issuing proposed General Water Use Permit No. 20012185.000, as set forth in District Exhibit No. 4; and Finding that DCAP lacks standing to challenge the issuance of the permit. DONE AND ENTERED this 3rd day of June, 2002, in Tallahassee, Leon County, Florida. CHARLES A. STAMPELOS 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 3rd day of June, 2002.
The Issue Whether the Petitioner's applications for (1) a general permit to operate a used oil refining facility and 2) an operation permit to operate an industrial waste water treatment system, at the same facility, in conjunction with the used oil refining operation, should be granted.
Findings Of Fact Sometime in the 1950's George Davis, the owner and operator of Davis Refining Corporation, became interested in used oil recycling and refining. From that time on, Mr. Davis worked towards his dream of operating a used oil recycling and refining center by gradually accumulating the land and equipment to operate such a facility. In order to further his goal, Mr. Davis acquired property located at 2606 Springhill Road in Tallahassee, Florida. Eventually, Mr. Davis applied for a permit to construct an industrial waste water treatment system in conjunction with a used oil refining facility on the Springhill Road property. On January 21, 1986, the Department issued a construction permit to the Petitioner to modify and construct an industrial waste water treatment system. The construction permit was subsequently extended on three different occasions. The last extension, granted May 30, 1989, extended the construction permit to its full statutory limit of five (5) years. The final expiration date of the construction permit was January 20, 1991. Petitioner was notified of the expiration date by the Department. During the time of the construction permit, Mr. Davis constructed an industrial waste water treatment system and an oil recycling and refining facility on his property on Springhill Road. Less than sixty days prior to expiration of the construction permit for the industrial waste water treatment system, the Petitioner submitted an application for renewal of an operation permit. The Department received the application on January 10, 1991. Unfortunately, the application for renewal of an operation permit was not the correct form since the Petitioner never had an operation permit. The application was rejected by the Department because it was the incorrect form and did not have the required permit fee. In March of 1991, after the expiration of Petitioner's industrial waste water treatment construction permit, Petitioner filed the correct application for an industrial waste water treatment operation permit and submitted the required fee. The industrial waste water operation permit application was denied by the Department because it was incomplete and lacked the required reasonable assurances that the system would not be a source of pollution in violation of water quality standards or contrary to the public interest. On October 29, 1990, Petitioner submitted a Used Oil Recycling Facility General Permit Notification to the Department. By letter dated November 28, 1992, the Department timely denied use of a general permit to operate a Used Oil Recycling Facility because the application lacked the requisite reasonable assurances that the proposed operation of the facility would not discharge, emit, or cause pollution so as to violate water quality standards or be contrary to the public interest. Even though the construction permit has expired and no additional permits have been issued by the Department the Petitioner continues to accept used oil and oily industrial waste water from outside sources for treatment. Currently, the facility consists of a used oil refining plant, industrial waste water treatment system, and separator (coalescer) system and water treatment pond. Munson Slough separates the facility into two parts. The used oil refining portion of the facility together with the industrial waste water treatment system input and separator (coalescer) system are located on the east side of Munson Slough. The refining portion of the facility is immediately adjacent to the slough. The industrial waste water treatment pond is located on the west side of Munson Slough. The industrial waste water treatment pond is likewise immediately adjacent to the slough. The industrial waste water treatment system is an integral part of the used oil recycling operation. Used oil and oily waste water are accepted from outside sources and are put through the separator system to separate the oil from the water and other contaminants. The separated oil is then re-refined at the refinery. The remaining industrial wastewater contains oily materials, solids, and volatiles. The separated water is pumped through a pipe underneath Munson Slough to the industrial waste water treatment pond. Additionally, the surface and stormwater runoff from the refining facility on the east side of Munson Slough also goes through the same industrial waste water treatment system and is pumped into the waste water treatment pond. Runoff from the refinery contains various pollutants as well as pollutants from any spills occurring at the refinery. Both the general permit for the refining facility and the operation permit for the industrial waste water treatment system depend on the ability of the waste water treatment system and pond to adequately handle the waste water and runoff water from the refining facility without permitting leaks of the wastewater into the environment. The industrial waste water treatment pond is lined with soil cement. Soil-cement is not a common material used in the construction of industrial waste water pond liners and the Department's personnel is not familiar with the material and its ability to function as an adequate liner for an industrial waste water pond. The soil-cement is a sand-cement mix (10 percent). The sand-cement was intended to be layered to a depth of six inches on the sides and bottom of the pond. The evidence showed that portions of the liner achieve a six inch depth. However, the evidence did not show that the soil-cement's depth is consistent throughout the liner since no as-built plans or certification for the facility were submitted to the Department and the engineer for the project at the time of its construction was not called to testify on whether the pond was constructed according to the construction plans. The sand cement liner overlays a high clay content pond bottom. The estimated (not established) permeability rate of the sand-cement pond liner is 1/100,000,000 centimeters per second and is within the Department's parameters for the adequacy of a lining material if that material is shown to actually have such a permeability rate by the time the operation permit is applied for. No materials data was submitted to the Department which demonstrated that the sand- cement liner of the pond actually achieved the permeability rate of 1/100,000,000 centimeters per second or the deterioration rate of such a liner. Likewise, no expert witness was called to establish such facts. The small amount of information given the Department on the sand-cement liner in Petitioner's application for its construction permit for the facility is inadequate to establish the actual performance of the sand-cement liner for purposes of the operation permit. Water from the industrial waste water treatment pond is discharged to the City of Tallahassee's waste water treatment system. The City of Tallahassee requires the industrial waste water treatment pond water to be tested for water quality prior to discharge to the City's waste water treatment system. The City requires that the waste water pond be aerated for approximately four (4) hours before discharge to the City waste water treatment system. One function of the aeration is to "blow off" the volatile contaminants from a used oil refining operation which might be present in the ponds water prior to aeration. However, the results of one water quality test indicated the presence of volatile substances and nonvolatile substances consistent with petroleum product contamination. Unfortunately, the results of only one water quality test were presented at the hearing. No conclusions either for or against the Petitioner can be drawn from the results of one testing period. Therefore, such test results cannot be used to affirmatively establish reasonable assurances that the pond is not leaking. In an unprecedented effort to aid the Petitioner in getting approval of his applications, the Department agreed to accept Petitioner's submittals and assertions regarding the integrity of the pond's liner as reasonable assurance if several soil borings and their subsequent analyses did not reveal any indication of contamination from the pond to soil or ground water. One soil boring was obtained by Dr. Nayak and six soil borings were obtained jointly by Dr. Nayak and the Department from locations around the industrial waste water treatment pond for chemical analysis. Unfortunately, chemical analysis of the soil borings revealed the presence of contaminants consistent with contamination parameters for waste oil recyclers. Therefore leakage or improper discharge from the pond could not be ruled out and it fell to the Petitioner to demonstrate that the contamination found in the soil was not the result of leaks or discharge from the pond. Petitioner points to the fact that the pond is supposedly setting on an impermeable layer of clay. However, it is not unusual for the geological features of a site such as the one upon which the treatment pond is located to vary within the limited site area. The different sites of the soil borings around the pond revealed that the substrata differed between the bore sites. The Department's geological expert testified that, based upon his observation at the site, including observing and participating in the taking of soil samples from the borings, that groundwater contamination was likely. In short, it is impossible to determine the geological composition of the entire site by the one soil boring taken by Dr. Nayak or even by the six borings performed jointly by the parties. Dr. Nayak's testimony that he is able to determine the geological features of the pond site with one boring is not credible nor is Dr. Nayak qualified to make such an assessment even if such were an acceptable scientific method for making such determinations. Therefore, the evidence failed to demonstrate that the waste water pond is sited over an impermeable layer of clay. Moreover, even if it were, then any contaminated water improperly discharging through the bottom layer of the pond would migrate along the top of the clay until it reached Munson Slough and still be a pollution problem for water quality purposes. The Petitioner has not, at any time prior to or during the hearing, obtained any environmental background of the site. Nor was any such information introduced at the hearing. The on-site observation of the taking of soil bores, visual inspection of the site, and the chemical analysis of the soil samples taken from the borings are consistent with petroleum contamination resulting from the industrial waste water pond. There are procedures and courses of action which the Petitioner can pursue to address the apparent contamination problems and to demonstrate the reasonable assurances necessary to qualify for the required Department permit to operate the used oil recycling facility. The Department has made many suggestions to the Petitioner as to various methodologies that the Petitioner might employ in order to endeavor to provide reasonable assurances that the waste water treatment pond does not leak. These suggestions include emptying the pond and examining the liner, performing a materials balance calculation, or performing more soil borings sampling and testing, together with assembling additional hydrological data. However, other than chemical analysis of the soil borings, the Petitioner has not opted to pursue any suggested procedure for obtaining the desired permit and did not submit sufficient competent, substantial evidence of any credible or scientifically reasonable alternative explanations for the presence of indicator chemicals in the soil borings. In short, The Petitioner has not submitted sufficient evidence nor provided any reasonable assurance that the operation of the used oil recycling facility will not discharge, emit or cause pollution. The Petitioner also has not provided reasonable assurance that the operation of the used oil recycling facility will not violate water quality standards or be contrary to the public interest. Similarly, there was insufficient evidence and no reasonable assurance submitted or offered by the Petitioner that the industrial waste water treatment system could be operated without violating water quality standards or being contrary to the public interest. Therefore Petitioner is not entitled to either a general permit for a used oil recycling facility or an operation permit for the industrial waste water treatment system used in conjunction with the used oil facility.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is accordingly, RECOMMENDED that a Final Order be entered denying the Petitioner both the general permit to operate a used oil recycling facility and the operation permit for the industrial waste water treatment system without prejudice to reapplying for such permits. DONE and ENTERED this 9th day of September, 1993, in Tallahassee, Florida. DIANE CLEAVINGER 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 9th day of September, 1993. APPENDIX TO RECOMMENDED ORDER, CASE NO. 91-5140 and 92-1560 The facts contained in paragraphs 1, 2, 3, 4, 5, 6, 7, 8, 9, 12, 13, 14, 16, 17, 18, 19, 20, 21, 22, 23, 24, 25, 26, 28, and 29 of Respondent's Proposed Findings of Fact are adopted in substance insofar as material. The facts contained in paragraphs 11, 15, 27 and 30 of Respondent's Proposed Findings of Fact are subordinate. The facts contained in paragraph 10 of Respondent's Proposed Findings of Fact were not shown by the evidence. Paragraphs 1 and 2 of the Petitioner's Proposed Findings of Fact were introductory and did not contain any factual matters. The facts contained in the 1st, 2nd and 7th sentences of paragraph 4 of Petitioner's Proposed Findings of Fact were not shown by the evidence. The remainder of the paragraph is subordinate. The facts contained in the 4th, 5th, 6th and 7th sentences of paragraph 5 of Petitioner's Proposed Findings of Fact are subordinate. The remainder of the paragraph was not shown by the evidence. The facts contained in paragraphs 3, 6, 7, 10, 12 and 13 of Petitioner's Proposed Findings of Fact were not shown by the evidence. The facts contained in the 3rd and 5th sentences of paragraph 8 of Petitioner's Proposed Findings of Fact were not shown by the evidence. The remainder of the paragraph is subordinate. The facts contained in the last sentence of paragraph 11 of Petitioner's Proposed Findings of Fact were not shown by the evidence. The remainder of the paragraph is subordinate. COPIES FURNISHED: Virginia B. Wetherell, Secretary Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Daniel H. Thompson, Esquire General Counsel Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Dr. S. K. Nayak 3512 Shirley Drive Tallahassee, Florida 32301 Candi Culbreath, Esquire Assistant General Counsel Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400
The Issue The issues to be resolved in this proceeding concern whether the Petitioner is entitled to a permit permitting installation of an on-site sewage disposal system (OSDS) on his property located in Dixie County, Florida, in the vicinity of the Suwannee River and whether he is entitled to seek a variance from the statutes and rules concerning permitting of such systems.
Findings Of Fact The department hereby adopts and incorporates by reference the findings of fact set forth in the Recommended Order.
Recommendation Having considered the foregoing Findings of Fact and Conclusions of Law, the evidence of record, the candor and demeanor of the witnesses and the pleadings and arguments of the parties, it is therefore RECOMMENDED: That a Final Order be entered denying the Petitioner's application for an OSDS permit, without prejudice to the applicant applying for and seeking a variance from the statutory and rule requirements related to permitting for the reasons found and concluded above, and without prejudice to applying for and pursuing an OSDS permit application should the applicant, at a later time, be able to demonstrate that alternative methods of treatment and disposal of the sewage effluent at issue can feasibly be performed, within the bounds of the standards enunciated in the above-cited statutes and rules concerning on- site sewage disposal permitting. DONE and ENTERED this 21st of December, 1990 in Tallahassee, Leon County, Florida. P. MICHAEL RUFF Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 21st day of December, 1990. APPENDIX TO THE RECOMMENDED ORDER IN CASE NO. 90-2487 PETITIONER'S PROPOSED FINDINGS-OF FACT Accepted. Accepted. 5-14. Accepted. RESPONDENT'S PROPOSED FINDINGS OF FACT 1-7. Accepted. COPIES FURNISHED: Sam Power, Agency Clerk Department of HRS 1323 Winewood Boulevard Tallahassee, FL 32399-0700 Linda K. Harris, Esquire General Counsel Department of HRS 1323 Winewood Boulevard Tallahassee, FL 32399-0700 John K. McPherson, Esquire 22 South Main Street Gainesville, FL 32601 Frances S. Childers, Esquire Assistant District III Legal Counsel Department of HRS 1000 Northeast 16th Avenue Gainesville, FL 32609 =================================================================
Findings Of Fact Trans/Circuits is a manufacturer of electronic printed circuit boards located at 210 Newman Way, Lake Park, Florida. Trans/Circuits' manufacturing operation involves the deposition of copper on plastic boards and the use of a lead or tin etch resist in order to create an electrically conducting circuit board. In the course of the manufacturing process, rinsewaters are used which become contaminated with copper and lead from the manufacturing process. These rinsewaters undergo chemical treatment to remove the metals and other contaminants, and are then discharged into an unlined percolation pond located behind Trans/Circuits' facility. About 36,000 gallons of effluent are discharged into the pond every day. The percolation pond discharges into ground water underlying Trans/Circuits' facility which groundwaters contain less than 3000 milligrams per liter (mg/l) of total dissolved solids. Trans/Circuits uses a Havviland brand wastewater treatment system. The system at present does not provide treatment sufficient to remove copper, fluoride, and lead from the wastewater effluent in compliance with the DER class G-II groundwater standards for these metals, i.e., 1.0 mg/l of copper, 1.5 mg/l of fluoride, and .05 mg/l of lead. Trans/Circuits has exceeded the effluent limitations for copper and lead at almost all times since at least June 1984. Trans/Circuits is not likely to comply with those standards for at least six months, by Trans/Circuits' own admission. The Operating Permit Application, Case No. 83-3676 Trans/Circuits requested a hearing to contest the DER Notice of Intent to Deny the application for an operating permit. The burden of proof and burden of going forward is therefore on Trans/Circuits to show that it is entitled to issuance of the operating permit. In this regard, Trans/Circuits did not introduce into the case any evidence relating to the operating permit application and did not introduce the application, itself. Further, Trans/Circuits did not present any evidence that its installation will abate or prevent pollution, or that it can provide reasonable assurances that the system which it seeks to operate will not discharge, emit or cause pollution. The Trans/Circuits facility has never been in compliance with DER standards and cannot provide assurances that it will be in compliance at anytime in the foreseeable future. Further Trans/Circuits has been operating without an operating permit at least since October 1983. The Month-to-Month Authorization, Case No. 84-0191 On September 17, 1982, DER issued a Notice of Violation and Orders for Corrective Action (NOV) to Trans/Circuits. The NOV alleged that Trans/Circuits violated provisions of Chapter 403, Florida Statutes, and DER rules in operation of its industrial waste water treatment and disposal system. Trans/Circuits requested and received an informal conference to discuss the allegations of the NOV, which conference was held on October 20, 1982. At the informal conference, DER and Trans/Circuits reached agreement on a resolution of the issues raised by the NOV. On November 4, 1982, a Consent Order was issued by DER, setting forth the parties' agreement and requiring Trans/Circuits to perform certain corrective actions. In the consent order, Trans/Circuits agreed not to discharge industrial wastewaters into waters of the state "without an appropriate and valid permit authorizing such discharge or having otherwise obtained Department authorization." At the time the consent order was issued, Trans/Circuits was operating pursuant to a DER construction permit which was issued for the purpose of allowing Trans/Circuits to make certain modifications to its treatment system to bring the system into compliance with DER effluent standards. The construction permit expired in January 1983, but Trans/Circuits continued to operate. About one month after the construction permit expired, DER notified Trans/Circuits that it was violating the consent order by operating without DER authorization. The parties met to discuss the matter, and agreed that Trans/Circuits would cease operation for one week to conduct bench-scale testing to identify problem areas and possible corrective actions. Trans/Circuits did cease operation and conduct the testing as agreed. Trans/Circuits presented the data resulting from their bench scale testing to DER, and represented that it had identified problem areas that needed correction. DER evaluated the data and agreed to allow Trans/Circuits to operate for a limited time to gather plant effluent quality data which would form the basis for DER's decision whether to allow operation to continue. DER did not take enforcement action to have Trans/Circuits cease operation at that time because DER wanted to give Trans/Circuits time to show that it could comply with the effluent standards as it claimed it could. On March 23, 1983, DER notified Trans/Circuits that there had been a significant improvement in the plant's ability to produce effluent of acceptable quality, and DER authorized Trans/Circuits to make modifications in order to improve effluent quality. DER at that time gave Trans/Circuits authorization to operate for an indefinite period, with the condition that DER would rescind its approval if the program of sampling and system approval did not continue. Trans/Circuits accepted the authorization on DER's terms. On April 12, 1983, DER granted Trans/Circuits' month-to-month authorization to operate ". . . provided continued improvement is made in your system's operation and the Department can reasonably anticipate system compliance." This authorization was in response to a request from Trans/Circuits for 90-day temporary operating approval in order to demonstrate that the system could comply with state standards. By letter dated October 5, 1983, DER withdrew its authorization for month-to-month operation of Trans/Cirouits' facility because it believed that compliance with state standards could no longer be reasonably anticipated. Despite Trans/Circuits' best efforts, the facility was not in compliance and DER had no assurance that continued operation would bring the facility into compliance within a reasonable amount of time. Trans/Circuits has never ceased operation since DER withdrew its month-to-month operating approval. Trans/Circuits has not had a DER permit for construction or operation of the facility since the expiration of their last construction permit in January, 1983. At a meeting on December 1, 1983, Trans/Circuits' general manager admitted that he was aware that Trans/Circuits' was in violation of the terms of the consent order by continuing to operate without DER authorization. Analysis of Trans/Circuits' plant effluent for April 1983, shows that average lead levels were 0.21 parts per million (ppm) (or mg/l), average fluoride levels were 2.45 ppm, while average copper levels were 0.51 ppm. These were the effluent levels existing when Trans/Circuits was granted its month-to- month approval for operation. Since the month-to-month authorization was granted, the majority of Trans/Circuits' effluent samples have not complied with the DER standards for lead, copper, and fluoride. Since April 16, 1984, five percent or less of Trans/Circuits' effluent samples have complied with the effluent standards for lead and copper. In the week or two prior to hearing, the majority of effluent samples contained lead at a concentration of 0.2 to 0-5 ppm (with some higher), and contained copper at a concentration of between 2 and 3.5 ppm (with some higher). The most recent data available indicate that Trans/Circuits is not in compliance with the effluent standards for lead, copper and fluoride. Daily average effluent concentrations for lead and copper are significantly greater now than they were when DER issued its month-to-month authorization. Groundwater samples just outside Trans/Circuits' property show violations of the DER standards for lead. The evidence shows that Trans/Circuits effluent quality has not improved since April 1983. Effluent concentrations of lead and copper have actually increased significantly since October 1983, when DER withdraw its month-to-month authorization. Trans/Circuits does not even expect to know before December 1984, whether its present system can attain compliance with effluent standards. The Construction Permit Application On March 8, 1984, Trans/Circuits applied to DER for a permit to construct modifications and improvements to the existing Havviland wastewater treatment system. Although the stated purpose of the requested construction was to upgrade the system to achieve compliance with the Riviera Beach Sewer Use Code so as to allow a sewer tie-in, Trans/Circuits had abandoned that purpose by the time of the hearing. Trans/Circuits now seeks to upgrade the systems so that the effluent can comply with the applicable standards for discharge to ground water. When DER received the application, it was reviewed by a DER engineer to see if it was complete. The engineer determined it was not complete, and notified Trans/Circuits on April 6, 1984, that additional information was needed to complete the review process, all of which information was necessary to determine whether a permit should be issued for the requested construction. Trans/Circuits' general manager objected to the request for additional information, claiming that all the requested information was not necessary to review the application. However, at the request of Trans/Circuits' counsel, a meeting was held between representatives of Trans/Circuits and DER to discuss the request for information that was needed for review of the application. Trans/Circuits thereafter, withdrew their objections, and agreed to provide the requested information. Trans/Circuits responded to DER's request for additional information on June 27, 1984, at 3:30 P.M. the day prior to hearing. Trans/Circuits delivered a packet of information to DER at that time that purported to be the requested information. Also at that time, however, Trans/Circuits told DER that it had already performed some of the construction for which a permit was sought, and that it was not sure what, if any, of the remaining construction would be undertaken. The information that was submitted to DER was not all of the information requested by DER. No flow diagram was submitted and waste effluent analysis was lacking. Without this information, it is impossible to determine whether or not reasonable assurance has been provided by Trans/Circuits that DER standards will be met. Even if all of the requested information had been submitted, DER could not issue a construction permit to Trans/Circuits because its future construction plans are now only speculative. Trans/Circuits does not know what modifications it intends to construct, or when exactly such modifications will be made. All that is certain is that Trans/Circuits does not intend any longer to construct the modifications for which it made application. DER evaluates applications to determines whether all proposed modifications works as a system. Trans/Circuits is the applicant for this permit and has the burden of showing that it is entitled to issuance of the permit. Here Trans/Circuits failed to present any evidence of what construction it actually plans to do, let alone that the purposed construction meets the criteria and that it is entitled to the permit.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED: That a Final Order be entered by the State of Florida Department of Environmental Regulation: Denying Trans/Circuits application for an operation permit; Denying Trans/Circuits application for a construction permit; and Withdrawing the month-to-month authorization for Trams/Circuits' operation. DONE and ENTERED this 19th day of September, 1984, in Tallahassee, Florida. DIANE K. KIESLING 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 19th day of September, 1984.
Findings Of Fact Kearney is engaged in the development of real property in and around Hillsborough County, Florida, and is located in Tampa, Florida. Corrugated is a Louisiana Corporation which maintains a local headquarters in Tampa, Florida, and is presently seeking a business outlet in Hillsborough County for the assembly and distribution of metal buildings. At all times material hereto, Kearney and Corrugated have been parties to a real estate transaction concerning certain real property located at 1920 U.S. Highway 301 in Tampa, Hillsborough County, Florida. The subject property consists of .82 acres of undeveloped land which is located in an area of rapid commercial and industrial growth. Under the Hillsborough County Zoning Code, the subject property is designated M-1, which authorizes commercial and industrial uses. Corrugated is the purchaser of the subject property, and proposes to establish an assembly and distribution center for pre-painted sheet metal buildings. Corrugated does not propose to engage in any activity which will generate industrial wastewaters of any kind, and in particular, will not generate wastes or wastewaters of a "hazardous" or "toxic" nature. No centralized public wastewater service has been available to this property, and septic tanks with drainfields are utilized by both adjacent properties for their domestic and other wastewater needs. Kearney and Corrugated have determined that the property in question is suitable for the intended uses in all other respects, including water, electricity, and transportation. In September, 1988, Kearney and corrugated sought approval from Respondent of a permit to install an onsite sewage disposal system (septic tank and drainfield) for the sole purpcse of providing toilet services to employees of the company. The site plan and preliminary construction drawings for the on- site system were reviewed by the Department of Environmental Regulation (DER) to determine whether the project posed unusual wastewater problems or relied upon inadequately designed facilities. The DER had no objection to the installation of the septic tank and drainfield to serve the proposed system because of the non-hazardous character of the business, and the absence of floor drains in the proposed work areas. The Hillsborough County Health Department, however, gave immediate verbal denial of a septic tank permit based solely upon the industrial zoning of the property, and set forth its denial, in writing, on October 14, 1988. Following the County Health Departnent's denial, Kearney and Corrugated, based upon consultation with Respondent's officials in Tallahassee, assembled additional information to provide further assurance that the site would not generate industrial or hazardous wastes which could be disposed of via the septic tank. They provided detailed descriptions of each process to be performed by Corrugated, in substantiation of its claim that no wastewaters would be generated at the site. They also obtained the agreement of the Hillsborough County Building Department to subject any future building permit applications at the site to particular wastewater scrutiny, in addition to formal deed restrictions which they proposed for the subject property. Notwithstanding these additional representations, the Environmental Health Director of the Hillsborough County Health Department continued to reject the application on the sole ground that the property was zoned for industrial uses. On October 14, 1988, Petitioners submitted an application for a variance to the Hillsborough County Health Department and the Respondent, accompanied by supporting material setting forth the regulatory history referred to above, as well as the written representations and assurances, including proposed deed restrictions, which they had previously tendered to the County Environmental Health Director. They appeared before the Variance Advisory Review Board on November 3, 1988, to substantiate the specific measures which they proposed in order to ensure that no toxic or hazardous substances would be introduced into the septic tank system. These proposals were received by the Advisory Board without objection, and members observed that Petitioners had done everything they could do to provide the comfort margin which the agency sought. However, denial of the variance was recommended based upon the failure of Hi1sborough County to adopt a local ordinance providing for future inspections or controls by local officials to prevent future toxic or hazardous wastes from being disposed into the on- site sewage disposal system. Without such a local ordinance, the Advisory Board members expressed the view that it did not matter what the applicant presented to the Board. On December 2, 1988, the Respondent formally informed the Petitioners, in writing, that their application for a variance had been disapproved. This denial had the effect of formally denying Petitioners' permit application. Thereupon, Petitioners timely sought review of this decision by filing a petition for formal administrative hearing.
Recommendation Based upon the foregoing, it is recommended that the Respondent issue a permit for an onsite sewage disposal system to the Petitioners. DONE AND ENTERED this 18th day of May, 1989 in Tallahassee, Florida. DONALD D. CONN Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 Filed with the Clerk of the Division of Administrative Hearings this 18th day of May, 1989. COPIES FURNISHED: Charles G. Stephens, Esquire Bayport Plaza - Suite 460 6200 Courtney Campbell Causeway Tampa, Florida 33607 Raymond Deckert, Esguire W. T. Edwards Facility 4000 W. Buffalo 5th Floor, Room 500 Tampa, Florida 33614 John Miller, General Counsel 1323 Winewood Blvd. Tallahassee, Florida 32399-0700 Gregory Coler, Secretary 1323 Winewood Blvd. Tallahassee, Florida 32399-0700 Sam Power, Clerk 1323 Winewood Blvd. Tallahassee, Florida 32399-0700 =================================================================
