The Issue The ultimate issue to be resolved in this proceeding is whether the Department should issue a permit allowing the construction of a wastewater treatment and disposal system as requested in the modified application filed by Thomas E. Wasdin. The applicant and the Department contend that reasonable assurances have been given that the proposed facility will not result in violations of any of the Department's rules or regulations. The Petitioner contends that the proposed facility is located too near to existing shallow water drinking wells and that the facility otherwise fails to comport with the Department's rules and regulations.
Findings Of Fact Petitioner is the president of Beach Woods of Brevard County, Inc. The corporation is the developer of "Beach Woods," a 376-unit planned unit development located in Melbourne Beach, Brevard County, Florida. One hundred eighty of the units have already been developed. Existing regional sewage treatment facilities operated by Brevard County are not adequate to accommodate the total number of units that the applicant proposes to develop. It appears that 24 more hookups are all that the existing facilities will tolerate. Beyond that number, a sewer moratorium is in effect, and unless the applicant can make some other arrangement for disposing of sewage, the development cannot be completed. The county has approved the planned unit development. In order to meet sewage treatment needs of the proposed development, the applicant is proposing to construct a "package sewage treatment plant" to accommodate waste that exceeds quantities that can be handled by existing regional facilities. Once the regional facilities are upgraded so that the development's sewage treatment needs can be accommodated, the applicant proposes to disassemble the package plant and utilize the regional facilities. The proposed plant would be a 50,000 gallons per day contact stabilization sewage treatment plant. Initially, it would be operated as a 5,000 to 15,000 gallons per day aeration plant. Once loads reach 18,000 gallons per day, it would become a contact stabilization plant. The Present collection and transmission system for sewage that exists at Beach Woods includes an 8-Inch collection station from which sewage flows to an existing lift station that pumps effluent via 6-inch pipes to the regional plant. When the proposed plant is completed, a computerized system would be set up to send effluent to the new plants when the limits that the regional plant can accommodate are met. Once the regional plant is upgraded to sufficient capacity, the bypass to the proposed plant would be eliminated, and all units would then be connected to the original collection system. The proposed treatment plant is based upon proven technology that has been in existence for more than 50 years. The plant should operate reliably, and proper consideration has been given to odor, noise, lighting, and aerosol drift. In close proximity to the plant, it is likely that there would occasionally be a "earthy smell" that would be noticeable, but not objectionable. Outside of the immediate proximity, no odor would be noticeable. Large fans would be operated in connection with the plant, and some noise would result. It does not, however, appear that the noise would be excessive or bothersome, even in the immediate vicinity of the plant. The plant would be lighted by street lights and would not result in any more excessive lights than normal street lights. The plant is not of the sort that aerosol drift is a likely problem. Adequate considerations have been given to providing emergency power to the plant in the event of a power outage. The plant could sit for at least 20 hours without power before any emergency would exist. If there was a power outage in excess of that period, emergency power sources are available. Consideration has been given to the 100-year flood plain. The plant has been placed at an elevation that keeps it outside of the 100-year flood plain. The land application system proposed by the applicant would utilize drain fields that would be alternately rested. Groundwater flows from the area of the proposed drain fields are in a southwesterly direction toward the Indian River. The Indian River in the location of the proposed facility is a "Class III surface water." Groundwater in the area of the proposed facility might be classified as either "G-I" or "G-II." Reasonable assurance has been given that the proposed sewage treatment plant would not operate in such a manner as to degrade surface or ground waters to the extent that any of the Department's specific water quality parameters set out in Chapter 17, Florida Administrative Code, would be violated. The proposed sewage treatment plant comports with local requirements and has been approved by Brevard County. The Allans Subdivision is a residential development that is located directly to the north of the Beach Woods development. Petitioner utilizes a shallow water well as a source of drinking water. The proposed land application site of the sewage treatment plant is located within 500 feet of the Petitioner's well. There are at least two other shallow water wells that serve as drinking water sources located within 500 feet of the proposed land application site. The applicant indicated a willingness to move the proposed facility so that no part of it would be located within 500 feet of the shallow drinking water wells. The evidence establishes that the plant could be moved to accomplish that. No specific plan, however was presented. Potential factual issues could exist respecting appropriate buffer zones for any relocation of the facility, even a minor relocation. The applicant is proposing to develop areas within 100 feet of the proposed facility. The applicant does not, however, propose to locate any public eating, drinking, or bathing facilities within 100 feet of the proposed plant or land application area. No map was presented during the course of proceedings before the Department of Environmental Regulation that preceded the formal administrative hearing or during the hearing itself to establish present and anticipated land uses within one mile of the boundaries of the proposed facility. The facility of such a size that it could not inhibit any conceivable present or proposed future land uses except within 500 feet of the proposed facility. Evidence was offered at the hearing from which it could be concluded that the Department has, in the past, issued permits for sewage treatment plants located within 500 feet of existing shallow drinking water wells. The testimony was that this has occurred despite a requirement in the Department's rules that there be a 500-foot buffer zone between any such plant and a shallow drinking water supply. No specific evidence was presented as to why the Department has allowed such a breach of its rules or why it should be allowed in this proceeding.
The Issue The issue posed herein is whether or not the Respondent, Arthur M. Jones, Jr.'s Wastewater Treatment Plant Operator's license should be suspended or revoked based on conduct set forth hereinafter in detail based on allegations as set forth in the Petitioner's Administrative Complaint filed January 31, 1979.
Findings Of Fact Based upon my observation of the witnesses and their demeanor while testifying, the arguments of counsel and the documentary evidence received, the following relevant facts are found. Respondent, Arthur M. Jones, Jr., is a duly certified Class C Wastewater Treatment Plant Operator, certified pursuant to Chapter 17-16, Florida Administrative Code. Respondent holds license No. 793 originally issued by the Florida Department of Health and Rehabilitative Services on May 13, 1971. The responsibility for certification of wastewater treatment plant operators was transferred to the Florida Department of Pollution Control by Executive Order 72-75. The Florida Department of Environmental Regulation is the successor agency to the Florida Department of Pollution Control by virtue of Chapter 75- 22, Laws of Florida, and is authorized by Section 403.101, Florida Statutes, to issue and revoke operators' certificates pursuant to its rules and Chapter 120, Florida Statutes. At all times material to this complaint, Respondent was employed by the Duval County School Board in Jacksonville, Florida. At all times material, Respondent was employed by the School Board as a School Sewer/Water Plant Mechanic, a position requiring certification by the Department as a Wastewater Treatment Plant Operator. In his capacity as a School Sewer/Water Plant Mechanic and Class C Operator, Respondent was responsible for the operation, supervision, maintenance and collection of influent and effluent samples from various Duval County schools. Persons responsible for the operation, supervision, maintenance and collection of influent and effluent samples must be licensed and certified by the Department as a Wastewater Treatment Plant Operator. Additionally, Respondent, in his capacity as a School Sewer/Water Plant Mechanic and Certified Class C Wastewater Treatment Plant Operator, was responsible for the proper collection of composite samples of raw sewage and the treated effluent from each such plant. According to instructions given the Respondent, a composite sample was to be taken by filling one-third of a sample bottle at two-hour intervals until the bottle was full. The composite sample of raw sewage was to be taken from the influent line and the composite sample of treated final sewage was to be taken from the effluent line. After the collection process, Respondent was responsible for properly and accurately labeling the composite samples and for depositing them in a refrigeration unit at School No. 98. The composite samples are then picked up at School No. 98 by authorized personnel for laboratory analysis to determine whether sewage is being adequately treated. The complaint, in summary fashion, alleged that the Respondent on or about February 15 and March 15, 1978, completely filled a raw sample bottle from the filter bed rather than from the influent line of the plant at School No. 94. That sample was submitted as a composite sample and placed in the refrigeration unit for pickup and analysis by laboratory personnel. Additionally, the complaint alleges that on February 15, 1978, at School No. 82, Respondent filled raw and final sample bottles for Schools Nos. 82, 64, 83 and 153, none of which were a proper composite sample. The samples, it is alleged, were all taken from School No. 82. The complaint alleges that similar acts occurred on March 15, 1978; on April 4, 1978 and April 11, 1978, all of which acts "constitute gross neglect and fraud in the performance of duties as an operator of a wastewater plant." Based thereon, the Petitioner seeks revocation of the Respondent's Class C Wastewater Treatment Plant Operator's license. L. L. Masters is Respondent's foreman and is in charge of the wastewater treatment plant facilities. Masters is Respondent's immediate supervisor. On March 15, 1978, Foreman Masters assigned Respondent the duties of taking composite samples of Schools 94, 64, 83, 82 and 159. Evidence reveals that Foreman Masters arrived at School 82 at 9:00 o'clock a.m. and departed at 2:00 p.m. Evidence also reveals that Foreman Masters had a clear view of the entire wastewater treatment plant and that it was impossible for the Respondent to enter and leave the treatment plant in a manner whereby composite samples could be collected without Foreman Masters seeing him. In this regard, Respondent's work orders reflect that he reported having arrived at School 82 at 10:40 a.m. and departed at 12:10 p.m. (Petitioner's Exhibits 5, 6, 7 and 8.) On April 4, 1978, Respondent was assigned to collect composite samples from Schools 72, 233, 76 and 208. (Petitioner's Exhibit 9.) Foreman Masters observed Respondent on April 4, 1978, with employee Carl Casey. Masters went to School 77 at 8:30 and Respondent was not there, although he had given a dispatcher a routing which would have taken him to School 76. When Foreman Masters noted that Respondent had not arrived at School 76 by 8:30 a.m., he took employee Carl Casey to School 233 and left Casey at School 233 while he returned to School 76. The Respondent was not there and Masters drove to School 208 where the Respondent arrived at approximately 9:30 a.m. It suffices to say that the Respondent then left for School 233 and arrived there at 10:30. From approximately 10:45 to 11:45, the Respondent was in the wastewater treatment area of School 233 and took three samples from the effluent line and three samples from the influent line at School 233 from the period 10:30 a.m. through 11:45 a.m. (Petitioner's Exhibits 9, 10 and 11.) Employee Pat Wilson testified that he accompanied Respondent on February 15, 1978, and that all samples were taken from the filter beds of Schools 98 and 82. Detective Jack C. Adams of the Jacksonville Police Department was assigned to the surveillance of Respondent on April 11, 1978. Detective Adams credibly testified that the Respondent did not take composite samples from the assigned schools as reflected by the work orders submitted by Respondent Respondent appeared and testified that one of the events for which he had been charged occurred as alleged; however, he testified that inasmuch as he questioned the procedures, he was of the opinion that since no harm was done, and since no school experienced problems, he is not guilty of gross neglect and fraud in the performance of his duties as an operator of a wastewater treatment plant as alleged. The evidence herein reveals that the Respondent was instructed as to the proper procedures for testing, collecting and preserving composite raw and final samples from wastewater treatment plants by his employer. He testified that he had attended a seminar wherein the instructions for such procedures were outlined to him and that he was given a manual on the methods for collecting raw and final samples. Barry McAlister, a certification officer for the Department, testified that Class C operators are instructed as to the proper procedures for collecting samples. Additionally, he testified that the submitting agencies rely heavily on the operators to properly collect samples which are submitted for analysis. Chapters 17-19.04, Florida Administrative Code, additionally set forth the sampling and testing methods for collection and preservation of composite samples. Although there was some conflicting testimony respecting the adherence to the procedures uniformly by the various wastewater treatment plant operators employed by the School Board, the undersigned is of the opinion that the Respondent was not at liberty to select and choose the manner within which he would collect composite samples for analysis by his employer in view of outstanding instructions which were in effect during his employment.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is hereby, RECOMMENDED: That the Respondent, Arthur M. Jones, Jr.'s license as a Class C Wastewater Treatment Plant Operator be suspended for a period of two (2) years. RECOMMENDED this 28th day of September, 1979, in Tallahassee, Florida. JAMES E. BRADWELL, Hearing Officer Division of Administrative Hearings Room 101, Collins Building Tallahassee, Florida 32301 (904) 488-9675 COPIES FURNISHED: Silvia Morell Alderman, Esquire Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Reed Tallahassee, Florida 32301 Joseph S. Farley, Jr., Esquire Mahon, Mahon & Farley 350 East Adams Street Jacksonville, Florida 32202
The Issue Whether Pasco County should be granted operating permits for Embassy Hills Wastewater Treatment Plant (WWTP) (Case 92-2489); Hudson WWTP (Case 92-2489); Hudson WWTP (Case 92-2488); and 8 Rapid Rate Infiltration Basins (RRIB) in Northwest Pasco County (Case 93-3091); whether the permit for RRIB should be granted to construct 10 RRIBs rather than 8 (Case 93-3641); whether these facilities can be operated without damage to the area potable and ground water systems; and whether the operating permit should include the provisions of a settlement agreement entered into between Matis, Pasco County and DER dated December 7, 1987. Whether the challenge to these permits was timely filed by Petitioner was resolved prior to the hearing and will not be revisited.
Findings Of Fact (Findings 1-80 below are from the prehearing stipulation submitted by the parties) The County is a political subdivision of the State of Florida, and owns and operates a wastewater collection, treatment, and disposal system in Pasco County, Florida. The Department is a state agency created pursuant to Section 20.261, Florida Statutes, and is responsible for protecting Florida's air and water resources in accordance with Chapter 403, Florida Statutes, and Chapter 17, Florida Administrative Code. Matis owns and resides at 11220 Denton Avenue, Hudson, Pasco County, Florida; her property is approximately 330 acres in size. In 1987, Matis filed a petition for formal administrative hearing against the Department and the County, in which she challenged the Department's proposed agency action to approve the County's applications for construction permits concerning the Embassy Hills WWTP (Permit Number DC51-128933) and the Hudson WWTP (Permit Number DC51-130307). That case was subsequently assigned DOAH Case No. 87-4781. Case No. 87-4781 was resolved by virtue of the 1987 Settlement Agreement. Matis, the County, and the Department were each parties to the 1987 Settlement Agreement. Paragraph 1(c) of the 1987 Settlement Agreement states: That the Respondent, Pasco County, will modify the permit application No. DC51-128933 as follows: . . . (c) The County agrees to reduce the number of ponds constructed at the Embassy disposal site located on Denton Avenue from fourteen (14) to nine (9) ponds by eliminating the five (5) most easterly ponds depicted on the County's construction plans; . . . The County subsequently modified its application for Permit Number DC51-128933 so as to delete the five most easterly ponds referred to in paragraph 1(c) of the 1987 Settlement Agreement. The Department subsequently issued Permit Numbers DC51-128933 and DC51- 130307, authorizing construction of the Embassy Hills and Hudson facilities, respectively. Permit Number DC51-128933 did not include authorization to construct the five ponds referred to in paragraph 1(c) of the 1987 Settlement Agreement. The County has not violated that portion of Section 2 of the Stipulated Settlement Agreement between the County, the Department and Matis which requires the County to construct a Floridian Aquifer and shallow aquifer monitor well cluster at the Hudson WWTP site at a location acceptable to Matis. The County has not violated that portion of Section 2 of the Stipulated Settlement Agreement which requires the County to monitor effluent discharged from the Hudson WWTP on a quarterly basis for the parameters specified in EPA Methods 601 and 602. The County has not violated Section 10 of the Stipulated Settlement Agreement. The County has not violated Section 13 of the Stipulated Settlement Agreement. The County has not violated Section 14 of the Stipulated Settlement Agreement. If the County and the Department comply with the 1987 Settlement Agreement, Matis will not be adversely affected by the proposed operation permits for the Embassy Hills and Hudson WWTPs (Permit Numbers DO51-203667 and DO51-203666). The County applied for Permit DO51-203666 (Hudson WWTP) on appropriate Department forms. The County applied for Permit DO51-203667 (Embassy Hills WWTP) on appropriate Department forms. The County's application for Permit DO51-203666 (Hudson WWTP) was certified by a professional engineer registered in the State of Florida. The County's application for Permit DO51-203667 (Embassy Hills WWTP) was certified by a professional engineer registered in the State of Florida. The County's application for Permit DO51-203666 (Hudson WWTP) was accompanied by a written certification by the permittee on Form 17-600.910(2) that an appropriate operation and maintenance manual is available at a specified location for the Hudson WWTP and the on-site percolation pond system. The County's application for Permit DO51-203667 (Embassy Hills WWTP) was accompanied by a written certification by the permittee on Form 17- 600.910(2) that an appropriate operation and maintenance manual is available at a specified location for the Embassy Hills WWTP and each associated disposal site. The Hudson WWTP is a Type I facility. The Embassy Hills WWTP is a Type I facility. The Hudson WWTP is enclosed with a fence or otherwise designed to discourage the entry of animals and unauthorized persons. The Embassy Hills WWTP is enclosed with a fence or otherwise designed to discourage the entry of animals and unauthorized persons. The Hudson WWTP's on-site percolation pond system is a Type I facility. The Denton Avenue Percolation Pond System is a Type I facility. The proposed Northwest RRIBs project is a Type I facility. The Hudson WWTP's on-site percolation pond system is a rapid rate land application system, as that term is defined in 17-610.510. The Denton Avenue Percolation Pond System is a rapid rate land application system as that term is defined in Rule 17-610.510, Florida Administrative Code. The Northwest RRIBs project is a rapid rate land application system, as that term is defined in Rule 17-610.510, Florida Administrative Code. There are no storage or holding ponds incorporated in the Hudson WWTP's on-site percolation pond system. There are no storage or holding ponds incorporation in the Denton Avenue Percolation Pond System. There are no storage or holding ponds proposed for the Northwest RRIBs project. The Hudson WWTP's on-site percolation ponds are designed to provide at least three feet of freeboard. The Denton Avenue Percolation Ponds are designed to provide at least three feet of freeboard. The Northwest RRIBs are designed to provide at least three feet of freeboard. Signs or other type of notice are posted around the Hudson WWTP's on- site percolation pond system, which designate the nature of the project area. Signs or other type of notice are posted around the Denton Avenue Percolation Pond site, which designate the nature of the project area. Signs or other type of notice will be posted around the Northwest RRIBs site, which designate the nature of the project area. There is fencing around the Hudson WWTP's percolation ponds on-site. There is fencing around the percolation ponds at the Denton Avenue Percolation Ponds site. There will be fencing around the percolation ponds at the Northwest RRIBs site. There is a set back distance of at least 500 feet from the edge of the percolation ponds at the Denton Avenue Percolation Pond site to any potable water supply well. There will be a set back distance of at least 500 feet from the edge of the percolation ponds at the Northwest RRIBs site to any potable water supply well. There is a set back distance of at lest 500 feet from the edge of the Hudson WWTP's percolation ponds on-site to any Class I Water. There is a set back distance of at least 500 feet from the edge of the percolation ponds at the Denton Avenue Percolation Pond site to any Class I Water. There will be a set back distance of at least 500 feet from the edge of the percolation ponds at the Northwest RRIBs site to any Class I Water. There is a set back distance of at least 500 feet from the edge of the Hudson WWTP's percolation ponds on-site to any Class II Water. There is a set back distance of at least 500 feet from the edge of the percolation ponds at the Denton Avenue Percolation Pond site to any Class II Water. There is a set back distance of at least 500 feet form the edge of the percolation ponds at the Northwest RRIBs site to any Class II Water. There is a set back distance of at least 100 feet from any Hudson WWTP wastewater transmission facility to any public water supply well. There is a set back distance of at least 100 feet from the Denton Avenue Percolation Pond site to any public water supply well. There is a set back distance of at least 100 feet from the Northwest RRIBs site to any public water supply well. Matis does not object to or challenge that portion of proposed Permit Number DO51-203667 (Embassy Hills WWTP) which relates to the Fox Hollow Percolation Pond System. Matis does not object to or challenge that portion of proposed Permit Number DO51-203667 (Embassy Hills WWTP) which relates to the Beacon Woods Golf Course Reuse System. Matis does not object to or challenge that portion of proposed Permit Number DO51-203667 (Embassy Hills WWTP) which relates to the Beacon Woods East Golf Course Reuse System. Matis does not object to or challenge that portion of proposed Permit Number DO51-203667 (Embassy Hills WWTP) which relates to the Timber Oaks Golf Course Reuse System. On December 23, 1992, the Department's Intent to Issue Permit Number DC51-214670 was published in the Pasco Times. On December 23, 1992, Matis saw and read an Intent to Issue Permit Number DC51-214670 published in the Pasco Times. Matis' property receives wastewater service from a septic tank located on the east side of her house. Matis' septic tank was installed in 1965, and it has not been replaced or serviced since that time. Since Matis' septic tank was installed in 1965, she has never had any wastewater removed from it. Matis is not aware of any water quality or contamination problems on her property. All water quality analyses which Matis has performed on her well water has revealed no contamination. Matis has never experienced an inability to pump water from her wells. Matis is not aware of any land collapse or sinkhole problems on her property. Matis' property includes approximately 240 to 250 acres of planted pine trees. Matis has had cattle operations on her property since around 1967. Presently, Matis has approximately 30 head of cattle on her property. Matis is not aware of any adverse affects to her agricultural operations caused by the historical operations of the County's wastewater facilities. Matis is not aware of any adverse affects to her property caused by the historical operations of the County's existing wastewater facilities. Matis is not an expert in the field of engineering, geology, hydrology, hydrogeology, wastewater system design, wastewater system operation, wastewater treatment methods, wastewater disinfection, sinkhole formation, biology, botany, ecology, groundwater modeling, water quality analysis, or air quality analysis. By letter dated November 17, 1992, Attorney William Deane requested the Department to provide his client (Respondent Marie Cook Matis), through his office, actual notice of the proposed agency action regarding the Northwest RRIBs construction permit application. On December 22, 1992, the Department furnished Matis (via her attorney, Mr. Deane) a telephonic facsimile copy of an Intent to Issue Permit Number DC51-214670 for the Northwest RRIBs. On December 23, 1992, the County (as permit applicant) had an Intent to Issue Permit Number DC51-214670 published in the Pasco Times. On December 23, 1992, the Pasco Times was a newspaper of general circulation in the area affected by the Northwest RRIBs project. On December 29, 1992, the Department's Southwest District Office hand delivered a copy of the Intent to Issue Permit Number DC51-214670 to Matis. On or about January 5, 1993, Mr. Deane's associate (i.e., Attorney Charles Hinton) sent the Department's attorney, Francine Ffolkes, a letter which stated: RE: Construction Permit Number DC51-214670 Northwest Pasco Rapid Infiltration Basins Notice of Intent Dear Ms. Ffolkes: This is to confirm our conversation this morning regarding the above referenced permit. Pursuant to that conversation, it is our understanding that Ms. Matis received actual notice of the above-referenced Notice of Intent on December 29, 1992. Accordingly, Ms. Matis has until January 12, 1993 to file a motion or objection to this permit. If this is in anyway incorrect, please contact my office immediately. Sincerely, /s/ Charles D. Hinton Charles D. Hinton Sent by facsimile this 5 day of January, 1993. Mr. Hinton did not send a copy of the foregoing letter to the County or otherwise advise the County regarding his conversation with Ms. Ffolkes. On January 12, 1993, Matis' Petition for Formal Administrative Hearing concerning the Northwest RRIBs construction permit (Permit Number DC51-214670) was received by the Department's Office of General Counsel. Matis' sole objection to the proposed operating permits for Embassy Hills WWTP and Hudson WWTP is that they do not incorporate the terms of the 1987 Settlement Agreement. No evidence was submitted that Pasco County is not complying with the terms of this settlement agreement or that the operation of these plants will in any wise affect Matis' property. The evidence is unrebutted that these plants have been operating for over two years without violations and that the effluent from these plants meets all statutory and regulatory requirements. So far as practicable the treated wastewater from these plants (and other WWTPs operated by Pasco County) is reused for irrigating golf courses, orange groves, and for residential irrigation. It is only during rainy periods when irrigation is not called for that this effluent is discharged through the infiltration basins. Both of these plants are Type I conventional activated sludge with anoxic denitrification wastewater treatment plants and meet the limitations for ph, BOD, nitrates, chlorine, sodium and dissolved solids contained in the proposed operating permit conditions. Although these operating limits for BOD, TSS and nitrates in the proposed operating permit exceed those in the construction permit and the Settlement Agreement, the proposed permit meets all statutory and regulatory requirements which the Department is called upon to enforce. The actual operation of these WWTPs meet the elevated standards of 15BOD, 5TSS, and 10 nitrates contained in the construction permit and Settlement Agreement. Accordingly, Pasco County is in compliance with the Settlement Agreement. Pasco County, like much of central Florida, is a Karst area subject to sinkholes. To insure the proposed rapid rate infiltration basins will not constitute a threat to the aquifer below the sites selected for these RRIBs, transects were taken, and the U.S. Department of Agriculture, Soil Conservation Service was engaged to conduct ground penetrating radar (GPR) studies of these areas. For any of those areas showing a possibility of below ground caverns or other evidence of potential sinkhole, borings were taken to determine the conditions below the surface of the ground. The GPR survey coupled with these "truth" borings revealed that the sites selected for these RRIBs are safe and appropriate for use as infiltration basins to receive the treated effluent from these plants. Five of the proposed RRIBs located closest to Matis' property were removed from the 1987 Pasco County construction permit application as a result of the Settlement Agreement. That Agreement did not preclude Pasco County from later seeking authorization to construct these RRIBs. It is the construction of these five RRIBs that Matis here protests. Matis' property is upgrade from these RRIBs and from the WWTPs here involved. Accordingly, it is virtually impossible for effluent from these RRIBs to reach Matis' property or her potable water well. In fact, the most likely source of contamination of Matis' potable water well is Matis' septic tank which is located upgrade from her potable water well. Pasco County currently reaches about 80 percent utilization of the effluent from its WWTPs as reused water for irrigation of golf courses, orange groves, residences, etc. It is seeking 100 percent utilization of its treated effluent for reuse. This will conserve potable water from the aquifers and better enable Pasco County to supply adequate potable water to its increasing population. To accomplish better reuse of treated effluent from its WWTPs Pasco County intends to install a master reuse plan wherein wastewater effluent from all the WWTPs in the county would feed into a single looped system. This system would intermingle all of the wastewater and then dispose of this wastewater at all of the county's reuse points. When the reuse points cannot absorb the wastewater due to rain or high water conditions, the wastewater would be discharged into the RRIBs. Although the construction of the additional five RRIBs to which Matis objects exceed the minimal disposal capacity required by the Department, having this excess disposal capacity reduces the possibility of contamination of surface waters from the treated wastewater from these WWTPs.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that Permit Number DO51-203666 be issued for the operation of Hudson WWTP; that Permit Number DO51-203667 be issued for the operation of Embassy Hills WWTP; and that Permit Number DC51-214670 be issued for construction of the ten Northwest Pasco County RRIBs. DONE AND ENTERED this 22nd day of October, 1993, in Tallahassee, Leon County, Florida. 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 22nd day of October, 1993. APPENDIX TO RECOMMENDED ORDER, CASE NO. 92-2488 Proposed findings submitted by Petitioner are accepted except as noted below. Those neither accepted nor noted below were deemed unnecessary to the conclusions reached. 16. Rejected in part. Matis saw the Notice of Intent to issue the permits here at issue published in the Pasco Times on December 23, 1992, and on December 22, 1992, Matis' attorney was furnished a facsimile copy of this notice. A copy was personally delivered to Matis by a DER representative on December 29, 1992. 24. Rejected. 30-32. Rejected as irrelevant. Rejected. DER adopted the proposed findings submitted by Pasco County. Those findings are accepted. Proposed findings submitted by Pasco County and not included in the Hearing Officer's findings were deemed unnecessary to the conclusions reached largely because Petitioner Matis challenged only the refusal of DER to include the provisions of the Settlement Agreement in the operation permit for the WWTPs and to grant construction permits for the five RRIBs withdrawn from the petition in 1987 as a result of the Settlement Agreement. COPIES FURNISHED: William W. Deane, Esquire Charles D. Hinton, Esquire Deane & Hinton, P.A. Post Office Box 7473 St. Petersburg, Florida 33734 David M. Caldevilla, Esquire Post Office Box 172537 Tampa, Florida 33672 Francine M. Ffolkes, Esquire Keith Hetrick, Esquire Department of Environmental Protection 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Virginia B. Wetherell, Secretary Department of Environmental Protection 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Kenneth Plante, General Counsel Department of Environmental Protection 2600 Blair Stone Road Tallahassee, Florida 32399-2400
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
Findings Of Fact On or about October 30, 1984, Lawrence E. Bennett, a consultant engineer for Peninsula, forwarded to DER's domestic waste engineering section an application to construct/operate a domestic wastewater treatment and disposal system along with the appropriate plans and a check for the fee. The package included proposals for construction of a 300,000 gpd splitter box and addition of a 100,000 gpd contact stabilization plant. Thereafter, on May 22, 1985, Mr. Bennett submitted a revised copy of the application pertaining to the 100,000 gpd expansion initially submitted as above. The revised application reflected Peninsula's proposed outfall to the Halifax River which was applied for under separate permit. By application dated October 7, 1983, as revised on May 15, 1985, Peninsula proposed to construct an outfall discharge into the Halifax River from the secondary treatment plant. By letter dated October 29, 1984, Mr. Bennett advised DER, inter alia, that the discharge rate would be an ADF of 1.25 mgd. The application for the additional 100,000 gpd plant and splitter box also provided for a chlorination facility. This expansion was needed because 200,000 gpd capacity is already committed to serve current residents and customers of the utility. The new construction is designed to accommodate established future demand. In Mr. Bennett's opinion, the design of this facility will accommodate all DER criteria and standards. The outfall facility proposed in the second project will be a pvc forced main for a part of the distance with iron pipe for the remainder and a lift station attached to pump the effluent to a point in the river selected where the river is deep enough to meet DER water criteria. The initial permit application on this project called for discharge into a portion of the river which did not meet water quality standards. As a result; DER suggested discharge point closer to the center of the river, and this change is now planned. At this point, the outflow will meet DER standards. Intents to issue the permits, as modified, were issued in August 1985. Peninsula has also filed for permits with the Florida Public Utilities Commission, the United States EPA, and the U.S. Army Corps of Engineers for these projects. The plans are based on the estimated population expansion called for in the next few years. Peninsula is fully capable, financially, of providing and paying for the projected improvements. In the past, it has always provided sufficient funding to do that which is called for under its permits and which is necessary. The waters in question here are Class III waters of the State, mainly recreational. There is no shellfish harvesting in the area because of the pollution of the Halifax River, condition which has existed since at least 1941. Results of tests conducted by experts for Peninsula show the quality of the water presently coming out of the treatment plant is cleaner than that currently existing in the Halifax River. The outfall pipe in question will have the capability of handling approximately 1,200,000 gpd. Latest reports from the water treatment plant indicate that the current average daily flow is 150,000 gpd representing approximately 75% of capacity. The design estimated for this project was based on a 250 gpd per unit use rate multiplied by the estimated number of units presently existing and to be constructed in the period in question. It is estimated however, that within two to three years even this project will be insufficient and Peninsula will have to file an additional request for expansion. Construction will have no detrimental environmental effect on the waters of the Halifax River. Mr. Bennett recommends discharge into the river rather than pumping the effluent backup to Port Orange because the local dissipation rate into the Halifax River, which is called for under these projects, is much quicker than that at Port Orange. Studies run on siting of the outfall pipe location which is close to Daggett Island included studies relating to dilution calculation and water quality of the effluent versus water quality of the river near the outfall. The project was, therefore, sited in such a manner as to provide for the least possible detrimental effect. Those studies, however, were for the original outfall location, not the present location as proposed by DER which is approximately 150 to 200 feet away. In the experts' opinion, however, there is very little difference in the two sites. The Daggett Island site is not unique in any way. It is a mangrove swamp of approximately 3 to 4 acres with nothing on it. Once the pipe is buried, it will be difficult to know that it is there. Even during construction, there would be little detrimental effect or disruption to the river ecology. Mr. Bennett's conclusions are confirmed by Mr. Miller; a DER engineer specializing in wastewater facility permits who has reviewed the plans for expansion of the plant for completeness and adequacy and found that they were both. The approval of the outfall pipe initially was made in Tallahassee based on the original siting. He reviewed it again, however, and determined that both projects are environmentally sound and conform to the DER standards. Rule 17-6, Florida Administrative Code, requires surface water discharge to have secondary treatment activity prior to discharge and the discharge cannot exceed 20% 80D and suspended solids. According to DER studies; the secondary treatment afforded the water at this location was adequate with the caveat that the District might want to require an extension of the outfall to the main channel of the river to promote tidal flushing of the effluent. It was this change which was; in fact, made by the District office. Without the change, the incoming tide would take the wastewater up into Daggett Creek. By moving it as suggested, west of the point of Daggett Island, the tide would go up river rather than into the creek taking the effluent with it. Concern over the creek is due to its limited natural flushing as opposed to the greater natural flushing of the river. It was the intent of all parties to achieve the desired result and move the outfall point; if at all possible, at no increase in cost. Consequently, the pipeline was moved at the same length with a slight possible addition to take the outlet to the same depth and this change became a condition to the issuance of the permit. The Peninsula will also need a dredge and fill permit in order to accomplish the work in question. The outfall plans (both construction and discharge) meet the requirements set forth in the pertinent provisions of Rule 17-6, Florida Administrative Code. DER evaluated post- construction, concluding that the new point source discharge would not violate these standards. However, prior to approval of these projects, DER did not perform a biological, ecological, or hydrographic survey in the area. As a result, it cannot be said that the criteria outlined in Rule 17-4.29(6), Florida Administrative Code, will not be adversely affected by the outfall pipe. Nonetheless, these surveys were not deemed necessary here. EPA denial of the NPDES (National Pollution Discharge Elimination System) permit, would have no impact on DER's intent to issue the instant permits. NPDES permits have no bearing on the state permitting process. If the NPDES permit is denied, the utility cannot discharge its effluent into the river. The state permit merely authorizes the construction. The NPDES permit applies to the outfall portion of the project, not to the treatment plant. Only if it could be shown there was a longstanding adverse effect on the water quality so as to bring it below standards, would this construction not be permitted. The depth of the water in the proposed area of the outfall is five feet. A 12-inch pipe would extend below the soil with an upturn to exit into the bottom of the river. Short term impacts of actual construction are not relevant to the permitting process. If there are any, they would be related to and considered in the dredge and fill permitting process. This conclusion is supported by the testimony of Jan Mandrup-Poulsen, a DER water quality specialist who, in his analysis of the instant projects, first looked at the plans for the outfall just a week before the hearing. By this time, the water quality section of DER had previously considered the project and he is familiar with the suggested change in the outfall location. In November 1985, he spent several days on a boat on the Halifax River in this area collecting data. His inquiry and examination showed that in the area in question, there are no grass beds, oyster beds, or anything significant that would be adversely affected by the location of the pipe and the outlet. The pipe outlet, as suggested, is far enough out into the river to keep it under sufficient water at all times to promote adequate flushing. In his opinion, the proposed discharge will be quickly diluted and will not violate the standards or other criteria set out in Section 17-3.121, Florida Administrative Code. In contrast to the above, Mr. Richard Fernandez, a registered civil engineer with a Master's Degree in environmental engineering, who did a study of these projects for TPI, indicated that the County 201 plan relating to this area, mandated by the federal government, calls for the eventual closing of all independent wastewater treatment plants with ultimate delivery of all wastewater to the Port Orange facility. If implemented, this plan calls for the conversion of the Peninsula facility to a pump station for the transmittal of effluent to Port Orange. In his opinion, the proposed discharge standard, as evaluated here, for the secondary treatment facility, is very high for such a facility. He feels the surface water discharge content of dissolved oxygen and suspended solids should be lower. In addition, he is of the opinion that the degree of treatment of discharged water required by the facilities in question here is too low and lower than typical secondary discharge points elsewhere in the area. Nonetheless, Mr. Fernandez concludes that while the intended facility here would probably not lower the quality of river water below standards, it is not in the public interest to construct it. Having considered the expert testimony on both sides, it is found that the construction requested here would not create sufficient ecological or environmental damage to justify denial. The proposals in the 201 plan calling for the transmittal of all effluent to Port Orange would not be acceptable to DER. The cost of such a project and the ecological damage involved would be so great as to render the project not even permittable. The currently existing percolation ponds used by the facility at Port Orange are not adequate to serve current needs and leech pollutants into the surrounding waterway. While the exact transmission routes called for under the 201 plan are not yet set, there would be substantial ecological problems no matter what routing is selected. There would be substantial damage to bird habitat, mangrove, and other protected living species unless some way were found to get the pipe across the river in an environmentally sound fashion. Consequently, DER has taken the position that the current proposals by Peninsula are superior to any plan to transmit waste to Port Orange.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is, therefore RECOMMENDED THAT DER: Enter an order dismissing with prejudice Volusia County's Petition in DOAH Case No. 85-3029 and, Issue permits to Peninsula Utilities, Inc., for the construction of a 100,000 gpd expansion to its existing wastewater treatment plant and to construct a river outfall line as was called for in the amended specifications listed in the application for this project. RECOMMENDED this 25th day of April, 1986, in Tallahassee, Florida. ARNOLD H. POLLOCK, Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32399 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 25th day of April, 1986. COPIES FURNISHED: Martin S. Friedman, Esquire Myers, Kenin, Levinson & Richards 2544 Blairstone Pines Drive Tallahassee, Florida 32301. Deborah Getzoff, Esquire Assistant General Counsel Department of Environmental Regulation 2600 Blair Stone Rd. Tallahassee, Florida 32301 Lester A. Lewis, Esquire Coble, McKinnon, Rothert, Barkin, Gordon, Morris and Lewis, P.A. P. O. Drawer 9670 Daytona Beach, Florida 32020 Ray W. Pennebaker, Esquire Assistant County Attorney P. O. Box 429 Deland, Florida 32720 Victoria Tschinkel Secretary Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32301 APPENDIX The following constitutes my specific rulings pursuant to Section 120.59(2), Florida Statutes, on all of the Proposed Findings Of Fact submitted by the parties to this case. Rulings on Proposed Findings of Fact Submitted by Petitioner, TPI 1-2. Accepted in paragraph 17. 3-4. Rejected as contra to the weight of the evidence. Rulings on Proposed Findings of Fact Submitted by Peninsula 1-13. Accepted in the Findings of Fact of the Recommended Order. Rulings on Proposed Findings of Fact Submitted by Respondent, DER 1. Accepted and incorporated in Finding of Fact 1 and 2. 2-3. Accepted and incorporated in Finding of Fact 5. 4-5. Accepted and incorporated in Finding of Fact 20 and 21. 6. 7. Accepted in Finding of Fact 19. 8. Accepted in Finding of Fact 14. 9. Accepted in Finding of Fact 9. 10. Accepted in Finding of Fact 8 and 21. 11. Accepted in Finding of Fact 14 and 17. 12-13. Accepted in Finding of Fact 14 and 17. 14-15. Rejected as a statement of evidence and not a Finding of Fact. Accepted in Finding of Fact 17. Recitation of Mr. Miller's testimony is not a Finding of Fact. The conclusions of Mr. Mandrup- Poulsen's testimony is not a Finding of Fact. Recitation of Mr. Mandrup-Poulsen's testimony testimony is not a Finding of Fact. Accepted in Finding of Fact 23. Recitation of testimony is rejected as not a Finding of Fact. Conclusions drawn from that testimony accepted in Finding of Fact 24.
Findings Of Fact In December, 1993, Suwannee Farms, through one of its partners, Robert Wight, applied to the Department of Environmental Protection for a wastewater treatment facility permit to be constructed on part of its property in Suwannee County, Florida. The Department of Environmental Protection requested clarification or amendment of the initial application. Suwannee Farms amended its initial application and the Department determined that the applicant had provided reasonable assurances of compliance with Florida Statutes and the Department's rules and regulations. The permittee listed on the initial application is Robert Wight. Suwannee Farms is a partnership consisting of Robert Wight and Joseph Hall. The permit is to be issued in the name of Suwannee Farms. Issuance in the name of the partnership is within the scope of the Department of Environmental Protection's authority. On January 25, 1994, the Department issued its Intent to Issue the permit. The intent to issue provided in part: Pursuant to Section 403.815, F.S. and DER Rule 17-103-150, Florida Administrative Code, you (the applicant) are required to publish at your own expense the enclosed Notice of Intent to Issue Permit. The Notice shall be published one time only within 30 days, in the legal ad section of a newspaper of general circulation in the area affected. For the purpose of this rule, "publication in a news- paper of general circulation in the area affected" means publication in a newspaper meeting the requirements of Sections 50.011 and 50.031, F.S., in the county where the activity is to take place. Where there is more than one newspaper of general circulation in the county, the newspaper used must be one with significant circulation in the area that may be affected by the permit. If you are uncertain that a newspaper meets these require- ments, please contact the Department at the address or telephone number listed below. The applicant shall provide proof of publication to the Department, at Northeast District Office, 7825 Baymeadows Way, Suite B-200, Jacksonville, Florida 32256-7577, within seven (7) days of the publication. Failure to publish the notice and provide proof of publication within the allotted time may result in the denial of the permit. The Notice Of Intent to Issue was published in the Gainesville Sun on February 5, 1994. Proof of publication was timely filed with the Department. The Gainesville Sun is a daily newspaper printed in Alachua County, Florida. The paper is available for purchase by the general public in Suwannee County, Florida and is sold to the general public at newspaper racks. Additionally, the Sun is available to residents of Suwannee County, including the area of the proposed project, through subscription and delivery via newspaper carrier "tubes." The Gainesville Sun is the only newspaper of general circulation delivered on a daily basis to homes in the area affected by the proposed permit. The Gainesville Sun contains national, state and local news stories, including local events in Suwannee County. Additionally, the Sun contains a legal ad section. The information in the Sun is of a public character and of interest and value to the residents of Suwannee County.dd The Sun has been published for more than a year in both Alachua and Suwannee Counties. At least twenty-five percent of the words in the Sun are in the English language and is entered as second class mail at the post office. There is no question that the Gainesville Sun meets the legal requirements of the Department for publication of Notices of Intent to Issue Permits in Suwannee County. Therefore, publication of the Intent to Issue Permit for the proposed wastewater facility involved in this case was appropriate. Through discovery and after an order compelling such answers, the Petitioner listed her objections to the issuance of the permit generally as noncompliance with nitrate level regulations, noncompliance with fencing regulations, noncompliance with set-back regulations and noncompliance with excessive noise and odor regulations. The evidence at the hearing demonstrated that the proposed wastewater treatment facility and land application meet the requirements of Florida Statutes and the Department's rules in the areas specified by the Petitioner as well as other areas of the statutes and rules. Suffice it to say that Petitioner offered no evidence which even remotely demonstrated that the Suwannee Farms permit did not meet these requirements or in some way failed to reasonably assure the Department that the requirements for a wastewater treatment permit with rapid rate land application would be met. Indeed, the only evidence in this case demonstrated that the technology proposed for the wastewater plant and rapid rate land application has been in use for a long time and has historically either met or exceeded the Department's requirements for nitrates (not to exceed 12 milligrams per liter), noise, odor and fecal coliform. There was no evidence submitted that would cause one to conclude that the technology for this facility would not perform as it has in the past at other locations. The plans of the facility clearly show adequate fencing and that the percolation ponds will be set-back at least 500 feet from any wells and at least 100 feet from any property line. Both fencing and pond location meet the requirements of Florida Statutes and Departmental rule. Given these facts, Petitioner has shown its entitlement to a construction permit for its proposed project.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is recommended that the Department of Environmental Protection issue a Final Order granting the application of Suwannee Farms for a wastewater treatment facility and rapid land application permit. DONE and ENTERED this 4th day of May, 1995, in Tallahassee, Florida. DIANE CLEAVINGER 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 4th day of May, 1995. APPENDIX TO RECOMMENDED ORDER, CASE NO. 94-2800 1. The facts contained in paragraphs 1, 2, 3, 4, 5, 6, 7, 8, 9, and 10 of Respondent's Proposed Findings of Fact are adopted in substance, insofar as material. COPIES FURNISHED: Stephen C. Bullock P. O. Box 447 Jacksonville, FL 32201 Thomas I. Mayton, Jr. Assistant General Counsel D E P 2600 Blair Stone Rd. Tallahassee, FL 32399-2400 Frederick L. Koberlein P. O. Drawer 2349 Lake City, FL 32056-2349 Virginia B. Wetherell, Secretary D E P 2600 Blair Stone Rd. Tallahassee, FL 32399-2400 Kenneth Plante General Counsel D E P 2600 Blair Stone Rd. Tallahassee, FL 32399-2400
The Issue Whether SFP's revised application for a permit to construct a sewage treatment plant with percolation ponds should be granted or, for failure of SFP to give reasonable assurances that the plant will not cause pollution significantly degrading the waters of Gator Cove, be denied?
Findings Of Fact About 1,500 feet from Santa Fe Lake's Gator Cove, SFP proposes to build an extended aeration package sewage treatment plant to serve a "private club with restaurant and overnight accommodations," SFP's Exhibit No. l, to be built between the plant and the lake, on the western shore of Santa Fe Lake, just south of the strait or pass connecting Santa Fe Lake and Little Santa Fe Lake. The site proposed for the waste water treatment plant lies at approximately 177 or 178 feet above sea level, north of Earleton on county road N.E. 28 near State Road 200A, some three miles north of State Road 26, in unincorporated Alachua County, Section 33, Township 8 South, Range 22 East. SFP's Exhibit No. 1. Santa Fe Lake, also called Lake Santa Fe, and Little Santa Fe Lake, also called Little Lake Santa Fe, are designated outstanding Florida waters by rule. Rule 17-3.041(4)(i), Florida Administrative Code. Lake Santa Fe "is . . . the sixth largest non-eutrophic lake in the State of Florida . . . [and] the last remaining large non-eutrophic lake in Alachua County." (0.367). Recreation is a "beneficial use" of these waters. The Lakes Santa Fe are at an elevation of approximately 140 feet above sea level, and their level varies within a range of four feet. Input The proposed plant is to treat sewage generated by staff, by diners at a 150-seat restaurant, and by inhabitants of 150 lodge or motel rooms, comprising 100 distinct units. On the assumptions that 150 rooms could house 275 persons who would generate 75 gallons of sewage a day for a daily aggregate of 20,625 gallons, and that a 150-seat restaurant would generate 50 gallons of sewage per seat per day, full occupancy is projected to engender 28,125 gallons of sewage per day. This projection is based on unspecified "D.E.R. criteria; (5.35) which the evidence did not show to be unreasonable. Full occupancy is not foreseen except around the Fourth of July, Labor Day and on other special occasions. An annual average flow of between 15 and 20,000 or perhaps as low as 13,000 gallons per day is envisioned. (S.38) The proposed plant is sized at 30,000 gallons per day in order to treat the peak flow forecast and because package plants are designed in 5,000 gallon increments. Sluice-gate valves and baffling are to permit bypassing one or more 5,000 gallon aeration units so plant capacity can be matched to flow. The composition of the sewage would not be unusual for facilities of the kind planned. As far as the evidence showed, there are no plans for a laundry, as such, and "very little laundry" (S.37) is contemplated. The health department would require grease traps to be installed in any restaurant that is built. Gravity would collect sewage introduced into 2,000 feet of pipe connecting lodging, restaurant and a lift station planned (but not yet designed) for construction at a site downhill from the site proposed for the water treatment plant. All sewage reaching the proposed treatment plant would be pumped 3,000 feet from the lift station through a four-inch force main. Influent flow to the treatment plant could be calculated by timing how long the pump was in operation, since it would "pump a relatively constant rate of flow." (S.39) Treatment Wastewater entering the plant would go into aeration units where microorganisms would "convert and dispose of most of the incoming pollutants and organic matter." (S.40) The plant would employ "a bubbler process and not any kind of stirring-type motion . . . [so] there should be very little:; aerosol leaving the plant," (S.42) which is to be encircled by a solid fence. Electric air blowers equipped with mufflers would be the only significant source of noise at the proposed plant, which would ordinarily be unmanned. If one blower failed, the other could run the plant itself. A certified waste water treatment plant operator would be on site a half-hour each week day and for one hour each weekend. SFP has agreed to post a bond to guarantee maintenance of the plant for the six months' operation period a construction permit would authorize. (0.63) The proposed plant would not "create a lot of odor if it's properly maintained." Id. The specifications call for a connection for an emergency portable generator and require that such a generator be "provide[d] for this plant. . . ." (S. 43). The switch to emergency power would not be automatic, however. A settling process is to follow extended aeration, yielding a clear water effluent and sludge. Licensed haulers would truck the sludge elsewhere for disposal. One byproduct of extended aeration is nitrate, which might exceed 12 milligrams per liter of effluent, if not treated, so an anoxic denitrification section has been specified which would reduce nitrate concentrations to below 12 milligrams per liter, possibly to as low as 4 or 5 milligrams per liter. Before leaving the plant, water would be chlorinated with a chlorinator designed to use a powder, calcium hypochlorite, and to provide one half part per million chlorine residual in the effluent entering the percolation ponds. A spare chlorine pump is to be on site. The effluent would meet primary and secondary drinking water standards, would have 20 milligrams or less per liter of biochemical oxygen demand or, if more, no more than ten percent of the influent's biochemical oxygen demand, and total suspended solids would amount to 20 milligrams or less per liter. (5.294- 295). Half the phosphorous entering the plant would become part of the sludge and half would leave in the effluent. Something like ten milligrams per liter of phosphorous would remain in the effluent discharged from the plant into the percolation ponds. (5.202). Although technology for removing more phosphorous is available (S.298, 0.170-171), SFP does not propose to employ it. Allen flocculation treatment followed by filtration could reduce phosphorous in the effluent to .4 milligrams per liter, but this would increase the cost of building the treatment plant by 30 to 40 percent; and operational costs would probably increase, as well, since it would be necessary to dispose of more sludge. (0.170-172). SFP did agree to accept a permit condition requiring it to monitor phosphorous levels in groundwater adjacent to the proposed plant. (0.63). Land Application Three percolation ponds are planned with an aggregate area of 30,000 square feet. At capacity, the plant would be producing a gallon and a half of effluent a day for each square foot of pond bottom in use. The ponds are designed in hopes that any two of them could handle the output of effluent, even with the plant at full capacity, leaving the third free for maintenance. The percolation ponds would stand in the lakes' watershed, in an area "of minimal flooding, (S.30) albeit outside the 100-year flood plain. Santa Fe Lake, including Gator Cove, and Little Santa Fe Lake are fed by groundwater from the surficial aquifer. All effluent not percolating down to levels below the surficial aquifer or entering the atmosphere by evapotranspiration would reach the lake water one way or another sooner or later. If percolation through the soils underneath the percolation ponds can occur at the rate SFP's application assumes, effluent would not travel overland into Lake Santa Fe except under unusually rainy conditions, which would dilute the effluent. Whether the planned percolation ponds would function as intended during ordinary weather conditions was not clear from the evidence, however. In the event the ponds overflowed, which, on SFP's assumptions, could be expected to happen, if peak sewage flaw coincided with weather more severe than a 25-year rainfall, effluent augmented by rainwater would rise to 179.87 NGVD (S.34), then overflow a series of emergency weirs connecting the ponds, flow through an outfall ditch, drain into a depression west of the ponds, enter a grassed roadside ditch, and eventually reach Lake Santa Fe after about a half a mile or so of grass swales. (5.69). Sheet flow and flow through an ungrassed gulley in the direction of Gator Cove (0.154) are other possible routes by which overflowing waters might reach the lake. (0.263). Since the facilities the plant is designed to serve are recreational, wet weather would discourage full use of the facilities and therefore full use of the water treatment system. Effluent traveling over the surface into Gator Cove would wash over vegetation of various kinds. Plants, of course, do take up phosphorous, but they don't do it forever, and if you leave a plant system alone, it will come to a steady state in which there is no net storage of phosphorous in the plant material. (0.166) Whether by sheet flow or by traversing swales, overland flow would reach Gator Cove within hours. Effluent traveling through the surficial aquifer would not reach the lake for at least five years. (S.238-9). It could take as long as 45 years. (0.316). In the course of the effluent's subterranean passage, the soil would take up or adsorb phosphorous until its capacity to do so had been exhausted. In addition, interaction with certain chemicals found in the soil, primarily calcium, precipitates phosphorous dissolved in groundwater. As between adsorption and precipitation, the former is much more significant: "[W]ith a three-meter distance you can expect at least 70 to 80 percent removal of phosphorous just by a a[d] sorption alone." (0.21). Precipitated phosphorous does not return to solution, unless the soil chemistry changes. (0.19) Adsorption, however, is reversible, although not entirely, because of the "hysteresis phenomenon." (0.19) Eventually, a kind of dynamic equilibrium obtains to do with the binding of the phosphorous to soil constituents, binding or precipitation of phosphorous. At some point . all of the binding sites become saturated . [and] the amount of phosphorous leaving, into the lake really, will be equal to the amount of phosphorous going into the the system. When there is no more place to store the phosphorous in the ground, then the output is equal to the input and that is called the steady state. (0.161) Although precipitation of phosphorous would not reach steady state under "conditions that render the phosphorous-containing compound insolu[]ble," (0.168) these conditions were not shown to exist now "much less . . . on into perpetuity." Id. Spring Seep A third possible route by which the effluent might reach lake waters would begin with percolation through the sand, which is to be placed on grade and on top of which the percolation ponds are to be constructed. Underground, the effluent would move along the hydraulic gradient toward the lake unless an impeding geological formation (an aquiclude or aquitard) forced it above ground lakeward of the percolationi ponds. In this event, the effluent would emerge as a man-made spring and complete its trip to Gator Cove, or directly to the lake, overland. The evidence demonstrated that a spring seep of this kind was not unlikely. Relatively impermeable clayey soils occur in the vicinity. A more or less horizontal aquitard lies no deeper than four or five feet below the site proposed for the percolation ponds. Conditions short of an actual outcropping of clayey sand could cause effluent mounding underground to reach the surface. Nor did the evidence show that an actual intersection between horizontal aquitard and sloping ground surface was unlikely. Such a geological impediment in the effluent's path would almost surely give rise to a spring seep between the pond site and the lakes. In the case of the other percolation ponds in this part of the state that do not function properly, the problem is n [U] sually an impermeable layer much too close to the bottom of the pond," (S.179), according to Mr. Frey, manager of DER's Northeast District. Phosphorous in effluent travelling by such a mixed route would be subject to biological uptake as well as adsorption and precipitation, but again a "steady state" would eventually occur. On Dr. Bothcher's assumptions about the conductivity of the clayey sand (or sandy clay) lying underneath the topsoil, the effluent would accumulate as a mound of groundwater atop the clay unit, and seep to the surface in short order; and "after a matter of probably weeks and maybe months, it would be basically of the quality of the water inside of the percolation pond." (0.278). More Phosphorous in Gator Cove The total annual phosphorous load from all existing sources "to the lake" has been estimated at 2,942 kilograms. Assuming an average effluent flow of 17,000 gallons per day from the proposed plant, "the total phosphorous load [from the proposed plant] will be 235 kilograms per annum," (0.16), according to Dr. Pollman, called by SFP as an expert in aquatic chemistry. Even before any steady state condition was reached, 20.75 to 41.5 kilograms of phosphorous, or approximately one percent of the existing total, would reach the lake annually from the proposed plant, on the assumptions stated by Dr. Pollman at 0.22-23 (90 to 95 percent removal of phosphorous in the soils and average daily flow of 30,000 gallons). Santa Fe Lake is more than two miles across and two miles long, and Little Santa Fe Lake, which may be viewed as an arm of Santa Fe Lake, is itself sizeable, with a shoreline exceeding two miles. But Gator Cove is approximately 200 yards by 100 yards with an opening into Santa Fe Lake only some 50 to 75 yards wide. (0.154). On a site visit, Dr. Parks observed "luxuriant growth of submerged plants" (0.154), including hydrilla, in Gator Cove. If a one percent increase in phosphorous were diffused evenly throughout the more than eight square miles Santa Fe Lake covers, there is no reason to believe that it would effect measurable degradation of the quality of the water. Some nutrients are beneficial, and the purpose of classifying a lake is to maintain a healthy, well-balanced population of fish and wildlife. It's hard to see how 1.4 percent increase would lower the ambient quality. But . . . seepage into Gator Cove, which is a much more confined place [100 by 200 yardsj [would make it] quite probable that there would be a lowering of ambient water quality in the site . R] educed dispersion . . . in this cove would allow . . . phosphorous to build up. (0.156) Overland effluent flow to Gator Cove would increase concentrations of phosphorus there, with a consequent increase in the growth of aquatic plants, and the likely degradation of waters in the Cove, unless rapid and regular exchange of lake and cove waters dispersed the phosphorous widely, promptly upon its introduction Except for testimony that wind-driven waves sometimes stir up phosphorous laden sediments on the bottom, the record is silent on the movement of waters within and between Lake Santa Fe and Gator Cove. The record supports no inference that phosporous reaching Gator Cove would be dispersed without causing eutrophic conditions significantly degrading the water in the Cove. Neither does the record support the inference, however, that effluent moving underground into the lakes would enter Gator Cove. On this point, Dr. Bottcher testified: [T]he further away from the lake that you recharge water the further out under a lake that the water will be recharging into the lake; gives it a longer flow . . . it's going to migrate and come up somewhat out into the lake. (0.281-2) Phosphorous in the quantities the treatment plant would produce, if introduced "somewhat out into the lake" would probably not degrade water quality significantly, notwithstanding testimony to the contrary. (0.349, 354). Sands and Clays DER gave notice of its intent to deny SFP's original application because SFP proposed to place the pond bottoms approximately two and a half feet above an observed groundwater table. Placement in such proximity to groundwater raised questions about the capacity of the ground to accept the effluent. In its revised application, SFP proposes to place sand on the existing grade and construct percolation ponds on top of the sand. By elevating the pond bottoms, SFP would increase the distance between the observed groundwater table and pond bottoms to 5.2 feet. (S.256, 257). This perched water table, which is seasonal, is attributable to clayey sand or sandy clay underlying the site proposed for the percolation ponds. Between January 9, 1985, and January 17, 1985, "following a fairly dry antecedent period," (S.229) Douglas F. Smith, the professional consulting engineer SFP retained to prepare the engineering report submitted in support of SFP's permit applications, conducted six soil borings in the vicinity of the site proposed for the plant. One of the borings (TB 5) is in or on the edge of a proposed percolation pond and another (TB 4) is slightly to the north of the proposed pond site. Three (TB 1, 2 and 3) are east of the proposed pond site at distances ranging up to no more than 250 feet. The sixth is west of the proposed site in a natural depression. Mr. Smith conducted a seventh test boring under wetter conditions more than a year later a few feet north of TB 4. Finally, on September 5, 1986, during the interim between hearing days, Mr. Smith used a Shelby tube to obtain a soil sample four to six feet below grade midway between TB 4 and TB 5. 1/ The sites at which samples were taken are at ground elevations ranging from 173 to 178 feet above sea level. From the original borings and by resort to reference works, Mr. Smith reached certain general conclusions: The top four feet or so at the proposed pond site consists of silty sand, 17 percent silt and 83 percent quartz sand. This topsoil lies above a two-foot layer of clayey sand, 20 percent clay, 6 percent silt and 74 percent sand. Below the clayey sand lies a layer some eight feet thick of dense, silty sand, 23 percent silt, 7 percent clay and 70 percent sand, atop a one and one-half foot layer of clayey sand, separating loose, quartz sands going down 40 feet beneath the surface from what is above. These formations "are very heterogeneous, in the sense of the position and occurrence of the clay layers or the sandy layers . . .," (0.230) and all occur within the surficial aquifer. "There are layers of clay within it, and so perched water tables are rather common." (0.225). In March of 1986, the regional water table was some 17 feet down. SFP Exhibit 1B. Below the surficial aquifer lie the Hawthorne formation and, at a depth of 110 feet, the limestone of the Floridan aquifer. The soils above the Hawthorne formation are not consolidated. (S.254, 255). Conductivity Measurements The applicant offered no test results indicating the composition or conductivity of soils lying between the easternmost test boring and Gator Cove, some 1,200 feet distant. No tests were done to determine the conductivity of the deeper layer of clayey sand beneath the site proposed for the ponds. Tests of a sample of the topsoil in TB 7 indicated horizontal permeability of 38.7 feet per day and vertical permeability of six feet per day. On the basis of an earlier test of topsoil in TB 3, "hydraulic conductivity of the surface soils was measured to be 8.2 feet per day. . . ." SFP's Exhibit No. 1B. From this measurement, vertical hydraulic conductivity was conservatively estimated at .82 feet (9.84 inches) per day. Id. The design application rate, 2.41 inches per day, is approximately 25 percent of 9.84 inches per day. Id. The initial test done on a sample of the clayey sand, which lay beneath the topsoil at depths of 3.5 to 5.5 feet, indicated a permeability of 0.0001 feet per day. Thereafter, Mr. Smith did other testing and "made some general assumptions" (S. 235) and concluded that "an area-wide permeability of this clayey sand would be more on the order of 0.0144 feet per day." (S. 234). Still later a test of the sample taken during the hearing recess indicated hydraulic conductivity of 0.11 feet per day. SFP's Exhibit No. 10. The more than thousandfold increase in measured conductivity between the first laboratory analysis and the second is attributable in some degree to the different proportions of fines found in the two samples. The soil conductivity test results depend not only on the composition of the sample, but also on how wet the sample was before testing began. Vertical Conductivity Inferred On March 6, 1986, ground water was observed on the site about two and a half feet below the surface. SFP's expert, Mr. Smith, concluded that it was "essentially a 1.5 foot water table, perched water table over the clay." (0.422). There was, however, groundwater below, as well as above, the clay. On March 12, 1986, the water table at this point had fallen six inches. In the preceding month rainfall of 5.9 inches had been measured in the vicinity, after 5.1 inches had been measured in January of 1986, but in November and December of 1985 "there was a total of 0.6 inches of rainfall." (0.421). Later in the year, notwithstanding typically wet summer weather, no water table was measured at this point. From this Mr. Smith concluded that, once the clayey sand layer is wetted to the point of saturation, conductivity increases dramatically. If that were the case, a more or less steady stream of effluent could serve to keep the clayey sand wetted and percolation at design rates should not be a problem. But Dr. Bottcher, the hydrologist and soil physicist called as a witness for the Association, testified that the six- inch drop over six days could be attributed, in large part, to evapotranspiration. He rejected the hypothesis that the clayey sand's conductivity increased dramatically with saturation, since "the actual water table was observed . about three weeks after the very heavy rainfall had stopped" (0.290) and had probably been present for at least a month; and because the soil survey for Alachua County reports that perched water tables ordinarily persist for two months (0.227) in this type of soil. Certain soils' hydraulic conductivity does diminish with dessication, but such soils usually regain their accustomed conductivity within hours of rewetting. Dr. Bottcher rejected as unrealistically optimistic the assumption SFP's expert made about the conductivity of the clayey sand on grounds that "the conductivity that . . . [SFP] used, if you went out there you couldn't perch a water table for a month." (0.277). In these respects, Dr. Bottcher's testimony at hearing has been credited. In the opinion of the geologist who testified on behalf of the Association, Dr. Randazzo, a minimum of seven or eight additional augur borings in "definitive patterns to the northeast and to the northwest" (0.240) to depths of 15 to 20 feet, with measurements within each augur boring every two feet, are necessary to determine "how permeable the soils are and how fast the waters would move through them." (0.240). This testimony and the testimony of the soil physicist and others to the same general effect have been credited, and Mr. Smith's testimony that no further testing is indicated has been rejected. Wet Ground In the expert opinion of a geologist who testified at hearing, "it is reasonable to assume that saturation conditions of the surficial aquifer in this area can be achieved," (0.238) even without adding effluent from a wastewater treatment plant. The evidence that soils in the vicinity of the site have a limited capacity to percolate .water came not only from engineers and scientists. Charles S. Humphries, the owner of the property 150 feet from the proposed percolation site, "put a fence post line . . . every ten feet, and every ten feet [he] hit clay." (0.372). Three quarters of an inch of rain results in waters standing overnight in neighboring pastures. In parts of the same pastures, rain from a front moving through "will stay for a week or so." (0.373). It is apparent that the area cannot percolate all the rainfall it receives. This is the explanation for the gully leading down toward Gator Cove. Six-feet deep (0.377), "the gully is a result of natural surface runoff." (0.263).
Findings Of Fact The Parties. Respondent, Roland Tardif, is the owner of Pond View Mobile Home Park (hereinafter referred to as "Pond View"). Pond View is located in Lake City, Columbia County, Florida. Respondent, the Florida Department of Environmental Protection (hereinafter referred to as the "Department"), is an agency of the State of Florida with responsibility for, among other things, regulating wastewater treatment facilities. The Petitioner, Jeffrey Hill, is the owner of real property located adjacent to the northern boundary of Pond View. Mr. Hill has witnessed fluids flowing from Pond View onto his property. Those fluids, while not identified as to substance or source, came from the direction of a wastewater treatment facility on Pond View. It is possible, therefore, that a discharge from the wastewater treatment facility on Pond View could flow onto Mr. Hill's property. Mr. Hill is also the owner of sixty percent of the stock of a corporation which owns real property adjacent to the western boundary of Pond View. The corporation is not, however, a party to this proceeding. Pond View's Wastewater Treatment Facility. Pond View is served by a 0.009 MGD extended aeration (activated sludge) wastewater treatment plant (hereinafter referred to as the "Treatment Facility"). The Treatment Facility is located on the property at Pond View and is the subject of this proceeding. The Treatment Facility includes two percolation ponds where final treatment and disposal of chlorinated wastewater effluent takes place. The percolation ponds, if operating properly, should hold all effluent until it percolates into the groundwater. Viable operation of the Treatment Facility depends, in part, upon proper maintenance of the percolation ponds. The Treatment Facility was operated by Mr. Tardif pursuant to a permit issued by the Department (hereinafter referred to as the "Operation Permit"). The Operation Permit expired in 1991. Pursuant to the Operation Permit, Mr. Tardif was allowed to discharge effluent to an unnamed ditch and wetland area which connects with Alligator Lake. Alligator Lake is a Class III waterbody. Class III waterbodies are designated for use as recreational waters. Mr. Tardif's Application for Renewal of the Operation Permit. In November of 1991, Mr. Tardif applied to the Department for a renewal of the Operation Permit. Due to modifications in the Department's rules relating to wetlands made since the Operation Permit had been issued, the practice of discharging effluent into wetlands was no longer acceptable. Therefore, the Department denied Mr. Tardif's application for renewal of the Operation Permit. Mr. Tardif's Application for a Temporary Operation Permit. On September 3, 24 and 28, 1992, Department field inspections were conducted of the Treatment Facility. The field inspectors determined that there was excessive vegetation growing on the berms of the two percolation ponds of the Treatment Facility. Excessive vegetation makes it difficult to inspect the ponds to determine if improper discharges are taking place. The Department's field inspectors also determined that the distance between the effluent level in the percolation ponds and the top of the berms, which is referred to as "freeboard", was inadequate. Adequate freeboard is required to help insure that the ponds have sufficient volume capacity to contain facility effluent and rainwater without discharging effluent from the ponds. One effluent line adjacent to one of the ponds was observed discharging to a ditch. The discharge was considered a discharge to surface waters. Because of the condition of the percolation ponds, the Department was concerned about the operation and maintenance of the percolation ponds and their ability to perform properly. On or about October 8, 1992, the Department issued a Warning Letter to Mr. Tardif. The Warning Letter informed Mr. Tardif of the problems with the operation of the Treatment Facility found during the September of 1992 inspections. Mr. Tardif was also informed that the Treatment Facility was being operated without a valid permit in violation of Rule 17-4.030, Florida Administrative Code. On or about November 19, 1992, Mr. Tardif applied to the Department for a temporary operation permit (hereinafter referred to as a "TOP"), to operate the Treatment Facility. On or about May 14, 1993, the Department issued a notice of intent to issue a TOP (hereinafter referred to as the "Proposed TOP"). A copy of the Proposed TOP was attached to the notice of intent to issue. Specific condition 18 of the Proposed TOP provided as follows: This permit is issued to allow time for the facility to demonstrate full compliance with Department rules, demonstrate satisfactory evaporation/percolation pond performance and investigate alternate land application methods if necessary. The submitted schedule for compliance is as follows: Date when planning is expected to be complete: January 1, 1994. Date when design will be complete: January 1, 1995. Date construction permit application will be submitted to upgrade or eliminate the existing discharge: July 1, 1995. Date construction will begin: October 1, 1995. Date construction is to be completed: May 1, 1996. Date that full compliance with Chapter 403, Florida Statutes, and rules of the Department will be achieved: May 1, 1997. Mr. Tardif did not challenge any part of the Department's decision to issue the Proposed TOP. On or about May 28, 1993, Mr. Hill filed a Petition for Formal Administrative Hearing challenging the Department's decision to issue the Proposed TOP. Mr. Hill alleged that the Proposed TOP would allow the Treatment Facility to discharge treated and untreated wastewater onto his property. Mr. Hill also alleged that Mr. Tardif had failed to demonstrate that the Treatment Facility would comply with all applicable statutes and rules governing its operation. The Department's Decision to Modify the Proposed TOP. Subsequent to the filing of this matter with the Division of Administrative Hearings, the Department caused the Treatment Facility to be inspected. Those inspections took place in August and September of 1993. The Department discovered that the berms of the percolation ponds were still covered with excessive vegetation and that the freeboard in the ponds was still inadequate. Additionally, the Department discovered during the August and September of 1993 inspections that the ponds were covered with duckweed. Duckweed, if not removed, will die and drop to the bottom of a percolation pond, reducing the ability of water to percolate into the soil. Duckweed also reduces the volume capacity of percolation ponds. The Department was already concerned about the adequacy of the soil conditions and the water table where the Treatment Facility is located. In a properly functioning percolation pond, water percolates quickly and the pond dries out. If the soil contains too much clay and/or the water table is high, percolation will occur at a slower rate. Percolation at the Treatment Facility was slow. The Department's concern about the inadequacy of the soil conditions and water table in the area where the Treatment Facility is located, coupled with the continued lack of maintenance of the percolation ponds, caused the Department to become more concerned with the potential for surface water discharges from the Treatment Facility. The Department's concern became greater as a result of reports of actual discharges from the Treatment Facility it received in September of 1993. On September 8, 1992, Sergeant Henry Grimes, a wildlife officer with the Florida Game and Freshwater Fish Commission, inspected property adjacent to the western boundary of Pond View and the percolation ponds in response to a complaint about the Treatment Facility. Sergeant Grimes witnessed fluids being discharged from a pipe on Pond View property and an area saturated with a sludge-like substance that almost topped his boots when he stepped in it. The sludge-like substance was also located on property located immediately adjacent to the western boundary of Pond View. Mr. Tardif informed Sergeant Grimes that the discharge would be directed to a retention pond when the pond was completed. Discharges from the percolation ponds was a further indication that the percolation ponds are not operating properly. Such discharges may flow directly into wetlands through the ditch running from near Pond View to Alligator Lake. These discharges threaten the quality of the waters of Alligator Lake. Potentially harmful constituents in effluent which are of concern include bacteria, chlorine, phosphorus, nitrogen and ammonia. Effluents may also have a negative impact on biological oxygen demand. Based upon the foregoing events and concerns, the Department notified Mr. Tardif on or about October 8, 1993, that it intended to modify the Proposed TOP. The Department's Modification of the Proposed TOP. The Department decided to modify specific condition 18 of the Proposed TOP (hereinafter referred to as the "Modified TOP"). Specific condition 18 of the Modified TOP, with the modifications emphasized, provides as follows: There shall be no discharge from the ponds. This permit is issued to allow time for the facility to demonstrate full compliance with Department rules, demonstrate satisfactory evaporation/percolation pond performance and provide land application methods if a discharge occurs. The Schedule for providing alternate land application methods is as follows: Immediately upon the effective date of this Permit, if a discharge occurs, the Permittee shall notify the Department orally within 24 hours, of the discharge and its cause. Oral notification shall be followed by a written report within 72 hours. The report shall describe the nature and cause of the discharge and the steps being taken or planned to be taken to temporarily correct the problem. Upon any discharge, a construction permit application will be submitted to upgrade or eliminate the existing discharge within 45 days of the discharge occurrence in accordance with the following schedule: The Permittee shall within 45 days of the pond discharge, have a qualified professional engineer, ("Engineer"), registered in the State of Florida, submit to the Department a completed domestic waste application for construction of an approved land application site, which includes Department form No. 17-610.910(1) to meet the current requirements of the Department. If the Department determines that the Permittee's application is incomplete, the Permittee shall have 15 days, or such longer period as provided and approved by the Department, from the date of receiving notice from the Department, to submit the required information to the Department to complete the application. Upon issuance of the Department permit, the Permittee shall comply with all permit conditions. If the Permittee fails to submit and/or complete the application within the time frame specified above in Specific Condition 18(a)(1) of this Permit, the Permittee shall cease all discharges to ground and/or surface water within 20 days of receiving such notice from the Department. The Permittee shall cease all discharges from the facility by either closing the facility and the appurtenant sewage collection lines or by daily removal of effluent from the treatment plant by a licensed hauler and having said effluent taken to a Department approved site until the facility is in compliance with the requirements of the Department Permitting Section and a Department operation permit has been issued for the facility. If the Permittee ceases discharge at any time, the Permittee shall orally notify the Department within 24 hours of the start of the cessation. Within 72 hours of oral notification, the Permittee shall submit to the Department a report describing and certifying compliance with this paragraph. Date construction will begin: within 4 months of issuance of construction permit. Date construction is to be completed: within 6 months of issuance of construction permit. Date that full compliance with Chapter 403, Florida Statutes, and rules of the Department will be achieved: within 18 months of the discharge occurrence. If any event occurs which causes delay, or the reasonable likelihood of delay, in achieving full compliance with Chapter 403, Florida Statutes, and rules of the Department within 18 months of the discharge occurrence, the Permittee shall have the burden of proving that the delay was, or will be, caused by the circumstances beyond the permittee's reasonable control and could not have been or cannot be overcome by due diligence. Economic circumstances shall not be considered circumstances beyond the control of the Permittee, nor shall the failure of a contractor, subcontractor, materialman or other agency (collectively referred to as "contractor") to whom responsibility for performance is delegated to meet contractually imposed deadlines be a cause beyond the control of the Permittee, unless the cause of the contractor's late performance was also beyond the contractor's control. Upon occurrence of an event causing delay, or upon becoming aware of a potential for delay, the Permittee shall notify the Department orally within 24 hours and shall, within seven days of oral notification to the Department, notify the Department in writing of the anticipated length and cause of the delay, the measures taken, or to be taken, to prevent or minimize the delay, and the timetable by which the Permittee intends to implement these measures. If the parties can agree that the delay or anticipated delay has been, or will be, caused by circumstances beyond the reasonable control of the Permittee, the time for performance hereunder shall be extended for a period equal to the agreed delay resulting from such circumstances. Such agreement shall adopt all reasonable measures necessary to avoid or minimize delay. Failure of the Permittee to comply with the notice requirements of this paragraph in a timely manner shall constitute a waiver of the Permittee's right to request an extension of time for compliance with the requirements of this Permit. Special condition 18 of the Proposed TOP did not clearly address the Department's concerns about the adequacy of the Treatment Facility. While the Proposed TOP specified that there will be "no discharge to the surface waters" and imposed upon Mr. Tardif the obligation to undertake remedial activities, the Proposed TOP was vague as to what exactly must occur before Mr. Tardif was required to undertake the remedial activities. Special condition 18 of the Proposed TOP also provides, in part, that "[t]his permit is issued to allow time for the facility to demonstrate full compliance with Department rules, demonstrate satisfactory evaporation/percolation pond performance and investigate alternative land application methods if necessary. . . ." [Emphasis added]. This requirement is vague and caused uncertainty as to whether Mr. Tardif was required to take any action before it was determined to be "necessary" and, if so, what events would cause such action to be considered "necessary." Special condition 18 of the Modified TOP identifies a specific event which will require Mr. Tardif to modify the Treatment Facility: any discharge from the percolation ponds. This requirement eliminates the uncertainty of the original special condition 18 and reduces the possibility of a dispute arising between the Department and Mr. Tardif as to whether remedial actions are required. Special condition 18 of the Proposed TOP also allowed Mr. Tardif until May 1996 to complete construction of alternative land application methods and until May 1997 to bring the percolation ponds into full compliance regardless of whether a discharge occurred today. Special condition 18 of the Modified TOP reduces the time period after a discharge when the percolation ponds must be brought into compliance to 18 months from the date of the discharge. The changes to special condition 18 reflect the Department's concern about the adequacy of the percolation ponds. These concerns have, in part, been caused by Mr. Tardif's lack of action to maintain the percolation ponds. Special Condition 18 of the Modified TOP is Reasonable. Mr. Tardif failed to prove that the percolation ponds can be operated without discharge. Mr. Tardif has failed to prove that the Modified TOP, with the changes to special condition 18, is not reasonable. In fact, the evidence proved that special condition 18, as modified, is reasonable and desirable to protect the quality of surface waters of the State. Mr. Tardif failed to prove that he is entitled to the issuance of the Modified TOP.
The Issue The issue in this case is whether Respondent Laniger Enterprises of America, Inc. (Laniger), is liable to Petitioner Department of Environmental Protection (Department) for penalties and costs for the violations alleged in the Department's Notice of Violation, Orders for Corrective Action, and Administrative Penalty Assessment (NOV).
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, 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."3 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 the water quality of 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 St. Lucie River area near Laniger's WWTP 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. The Department notified Laniger that its WWTP was listed as a threat to the water quality of the lagoon system soon after the 1991 report was issued. The Department's 1991 report concluded that the solution for package plants threats was to replace them with centralized sewage collection and treatment facilities. To date, over 90 of the 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 [sic] 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." Most of the parties' evidence and argument was directed to the following requirements of the administrative order: Beacon 21 WWTP shall connect to the centralized wastewater collection and treatment within 150 days of its availability and properly abandoned facility [sic] or provide reasonable assurance in accordance with Chapter 62-620.320(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 and will not cause pollution in contravention of chapter 403, F.S. and Chapter 62-610.850 of the Florida Administrative Code. * * * (3) Beacon 21 WWTP shall provide this office with semi annual reports outlining progress toward compliance with the time frames specified in paragraph 1 of this section, beginning on the issuance date of permit number FLA013879-002-DW3P. The administrative order contained a "Notice of Rights" which informed Laniger of the procedures that had to be followed to challenge the administrative order. Laniger did not challenge the administrative order. 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. The 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. Correspondence Regarding Compliance Issues On August 21, 2001, following an inspection of the Laniger WWTP, the Department sent Laniger a letter that identified some deficiencies, one of which was Laniger's failure to submit the semi-annual progress reports required by the administrative order. Reginald Burge, president of Laniger and owner of the WWTP, responded by letter to William Thiel of the Department, stating that, "All reports were sent to the West Palm Beach office. Copies are attached." Mr. Thiel testified that the progress reports were not attached to Laniger's letter and he informed Laniger that the reports were not attached. Mr. Burge testified that he subsequently hand-delivered the reports. At the hearing, it was disclosed that Laniger believed its semi-annual groundwater monitoring reports satisfied the requirement for progress reports and it was the monitoring reports that Mr. Burge was referring to in his correspondence and which he hand-delivered to the Department. Laniger's position in this regard, however, was not made clear in its correspondence to the Department and the Department apparently never understood Laniger's position until after issuance of the NOV. 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, the Department received a response from Laniger's attorney, 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. It was also stated in the letter from Laniger's attorney that "due to the location of Martin County's wastewater facilities, such facilities are not available as that term is defined in the [administrative] Order."4 On May 29, 2003, the Department replied, pointing out that the administrative order had found that reasonable assurance was not provided at the time of the issuance of the permit in 1999, and Laniger had made no "improvements or upgrades to the facility." The Department also reiterated that the progress reports had not been submitted. On September 29, 2003, the Department issued a formal 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 progress reports were not mentioned in the Warning Letter. The Department took no further formal action until it issued the NOV in August 2005. Count I: Failure to Timely File for Permit Renewal and Operating Without a Permit Count I of the NOV alleges that Laniger failed to submit its permit renewal application at least 180 days prior to the expiration of the 1999 permit, failed to obtain renewal of its permit, and is operating the WWTP without a valid permit. The date that was 180 days before the expiration of the 1999 permit was on or about February 27, 2004. Laniger did not submit its permit renewal application until February 15, 2005. In an "enforcement meeting" between Laniger and the Department following the issuance of the warning letter in September 2003, the Department told Laniger that it would not renew Laniger's WWTP permit. It was not established in the record whether this enforcement meeting took place before or after February 27, 2004. When Laniger filed its permit renewal application in February 2005, 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 requested that the Department to act on the permit application, and 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." Laniger filed a petition challenging the permit denial and that petition is the subject of DOAH Case 05-1599, which was consolidated for hearing with this enforcement case. Laniger's permit expired on August 25, 2004. Laniger has operated the plant continuously since the permit expired. Count II: Failure to Submit Progress Reports Count II of the NOV alleges that Laniger failed to comply with the requirement of the administrative order to provide the Department with semi-annual reports of Laniger's progress toward connecting to a centralized sewage collection and treatment facility or providing reasonable assurances that continued operation of the WWTP would not be a threat to the water quality of the lagoon system. Laniger maintains that its groundwater monitoring reports satisfied the requirement for the semi-annual progress reports because they showed that the WWTP was meeting applicable water quality standards. The requirement for groundwater monitoring reports was set forth in a separate section of Laniger's permit from the requirement to provide the semi-annual progress reports. The monitoring reports were for the purpose of demonstrating whether the WWTP was violating drinking water quality standards in the groundwater beneath the WWTP site. They served a different purpose than the progress reports, which were to describe steps taken by Laniger to connect to a centralized sewage collection and treatment facility. Laniger's submittal of the groundwater monitoring reports did not satisfy the requirement for submitting semi-annual progress reports. There was testimony presented by the Department to suggest that it believed the semi-annual progress reports were also applicable to Laniger's demonstration of reasonable assurances that the WWTP was not a threat to the water quality of the lagoon system. However, the progress reports were for the express purpose of "outlining progress toward compliance with the time frames specified in paragraph 1." (emphasis added) The only time frame mentioned in paragraph 1 of the administrative order is connection to an available centralized wastewater collection and treatment facility "within 150 days of its availability." There is no reasonable construction of the wording of this condition that would require Laniger to submit semi-annual progress reports related to reasonable assurances that the WWTP is not a threat to the water quality of the lagoon system. Count III: Department Costs In Count III of the NOV, the Department demands $1,000.00 for its reasonable costs incurred in this case. Laniger did not dispute the Department's costs.
The Issue The issue in this case is whether the application of Respondents Falkner to transfer and modify a Water Use Permit should be approved.
Findings Of Fact The Southwest Florida Water Management District (District) is responsible for regulation and protection of water resources in the geographic area involved in this proceeding. Since 1994, John Falkner has owned the property in Hillsborough County which is the subject of this proceeding. The Falkner property is farmed by Christopher Falkner, the owner's brother. Prior to purchasing the land, the Falkners farmed the property, also known as the Rogers farm, through a lease arrangement with the previous owner. Rose Ann DeVito owns property to the south of the Falkner property. In the time since Ms. DeVito purchased the property, the elevation of Sumner Road has been raised and culverts were replaced. A fish farm was constructed in close proximity to her property. The result of this and other development has been to direct all the water flow from the surrounding area into the stream adjacent to the DeVito property. Drainage patterns in the area of Ms. DeVito's property have been altered since she first occupied the property. A ditch along Sumner Road which used to handle runoff from her property has been blocked by a neighbor's driveway. Maintenance on the ditch, allegedly a county responsibility, is described as poor. The ditch at the rear of Ms. DeVito's property handled water flow to Bullfrog Creek until the water flow became blocked, and the water diverted onto her property. The effect is that Ms. DeVito's property often contains a large amount of water. A substantial amount of sand is visible on her property, allegedly deposited by water flow. According to Ms. DeVito, both the county and the District have blamed the Falkner farm for the water-deposited sand. Charles and Diana Booth own property adjacent and to the south of the Falkner property. From 1992 to 1994, the Booths suffered from water running off the Falkner/Rogers farm and flooding the Booth property. A flood of the Booth property in the Fall of 1994 was not caused by irrigation but was related to a ten inch rainfall event at the Falkner farm. A ten inch rainfall exceeds a 25 year storm event and would likely result in widespread flooding. The Booths' pasture, top soil and driveway were eroded by the flooding. During the two years of flooding, Mr. Booth complained on several occasions about the flooding to the Falkners' foreman, "Cleo." The complaints were not relayed to Mr. Falkner. In October 1994, Mr. Booth reported the problem to the Southwest Florida Water Management District. Soon after the complaint was made, a representative of the District inspected the property and determined that a ditch needed maintenance. Shortly thereafter, the ditch was cleaned and a berm was installed to redirect runoff away from the Booth property. There has been no further flooding of the Booth property. In October 1995, Mr. Booth became concerned that a ditch was filling with sand and would not continue to handle the runoff. After voicing his concern, a water diverter was installed in the ditch and appears to have remedied the situation. At the time the Falkners began to lease the Rogers property, an existing water use permit, numbered 206938.01, had been issued and was valid for the farm. The Falkners have applied to transfer the existing water use permit from the previous property owner. The Falkners also seek to modify the permit, increasing the total quantities which can be pumped by transferring previously approved quantities from another permit the Falkners currently hold. All of the relevant wells are within the District's Most Impacted Area (MIA) of the Tampa Bay Water Use Caution Area. The District allows a permit holder within the MIA to increase withdrawals from a well by transferring the quantities from another permitted well within the MIA. The other Falkner farm (the "301 farm") from which the quantities would be transferred is located approximately one-half mile to the south of the Rogers farm and is within the MIA. The District reviewed the application and, on September 29, 1995, issued its Proposed Agency Action to Issue Water Use Permit No. 206938.03. The proposed permit includes special conditions requiring monthly pumping reports, water quality reports, adherence to District irrigation allotments (irrigation levels established by the AGMOD computer model) and crop reporting. In reviewing the application the District utilized the criteria set forth in Florida Administrative Code, and the Basis of Review, incorporated into the code by reference. In order to obtain a Water Use Permit, an applicant must demonstrate that the water use is reasonable and beneficial, is in the public interest, and will not interfere with any existing legal use of water. Additionally, the applicant must provide reasonable assurances that the water use: will not cause quantity or quality changes which adversely impact the water resources, including both surface and ground waters; will not adversely impact offsite land uses existing at the time of the application; will not cause water to go to waste; and will not otherwise be harmful to the water resources within the District. The uncontroverted evidence establishes that the water use is reasonable, beneficial and is in the public interest. The Falkners irrigate farmland to produce agricultural products. The production of food is in the public interest. The proposed use is reasonable and beneficial. Further, uncontradicted evidence and opinions of expert witnesses establish that the proposed use will not interfere with any existing legal use of water. The applicant must provide reasonable assurances that the water use will not cause quantity or quality changes which adversely impact the water resources, including both surface and ground waters. The evidence establishes that pumping from the Falkner wells will not adversely affect the quality of water within the aquifers from which the water is drawn. Mr. Booth asserted that he is having water quality problems, specifically with rust in his well. The Booth well is approximately 25 years old. There is no evidence that the rust is related to the Falkner pumping. The DeVito and Booth wells draw from the Intermediate aquifer. Review of the potentiometric surface map of the intermediate aquifer indicates that there is a water level variation of 17 feet between the rainy and dry seasons. The result of the variance can be "dry" wells. There are two wells on the Falkner/Rogers property relevant to this proceeding. The first (District ID number 1) is 770 feet deep, is cased to a depth of 160 feet, and opens to the Floridan aquifer. The second (District ID number 2) is 1100 feet deep, is cased to a depth of 140 feet, and opens to the Intermediate and the Floridan aquifers. A cased well does not withdraw water from the formations through which the casing is placed. For example, a well cased to a depth of 160 feet draws no water from the top of the casing (at approximately ground level) to the bottom of the casing at 160 feet. The Intermediate aquifer releases water at a much slower rate than the Floridan aquifer. Based on the type and location of the Falkner wells, the vast majority of the water pumped by the Falkners comes from the Floridan aquifer. Impacts on existing wells are calculated through computer modeling. The "MOD" flow model demonstrates impacts that will occur after 90 days of pumping at peak month levels with no recharge to the aquifer. The MOD flow model results in a conservative "worst case" projection. The MOD flow model calculation projects the drawdown at Falkner well number 1 to be approximately .9 feet. The MOD flow model calculation projects the drawdown at Falkner well number 2 to be approximately 1.4 feet. The MOD flow model calculation projects the drawdown at the Booth well to be approximately one-half foot. The impact on the DeVito well will not exceed that projected at the Booth well. District permitting criteria allow for projected MOD flow model drawdown impacts of less than five feet at existing wells. The impact possible after approval of this application falls well within the District's guidelines. The impact of pumping if the application at issue in this proceeding is approved will result in a maximum variation of one-half foot at the Booth well. The evidence fails to establish that any problems related to water quantity encountered by the Booths are related to agricultural pumping at the Falkner farms. The evidence also establishes that, based on the existing retention and drainage system, the proposed use will not adversely impact surrounding surface water bodies. A system of swales and ditches is utilized to retain the water on the farm property. The evidence fails to establish that runoff from the Falkner/Rogers farm will adversely impact surrounding surface waters if this application is approved. The applicant has provided reasonable assurances that the water use will not adversely impact offsite land uses existing at the time of the application. The evidence establishes that the runoff from the Falkner farm does not discharge directly to the stream at the rear of the DeVito property. Other agricultural property discharges into the stream adjacent to the DeVito property. There is a steady waterflow through the stream at all times, whether or not the Falkner pumps are operating. Ms. DeVito's property consists of Myakka soil, which has little capacity to absorb rainfall and generates large amounts of runoff. The altered drainage patterns in the area have resulted in substantial water on her property. The evidence in insufficient to establish that the Falkner farm pumping has resulted in flooding on Ms. DeVito's property. The evidence fails to establish that approval of the application at issue in this proceeding will cause adverse impact to the DeVito property or will result in water quality or quantity problems. The Booths are concerned that the existing drainage system will not be maintained and that increased pumping will result in their land being flooded again. The evidence fails to establish a substantial likelihood that the Falkner farm drainage system will not be maintained. The applicant has provided reasonable assurances that the water use will not cause water to go to waste. The Falkners use a semi-enclosed seep irrigation system at the Rogers farm. Irrigation is only used when necessary. Mushroom compost, humates, and plastic mulch retain moisture in the soil. A special condition of the permit requires the Falkners investigate the feasibility of tail water recovery and reuse. The applicant has provided reasonable assurances that the use will not otherwise be harmful to the water resources within the District. The permit application results in no increased withdrawal of water than is allowed under the existing permits for the Rogers and the "301" farms.
Recommendation Based on the foregoing, it is hereby RECOMMENDED that the Southwest Florida Water Management District enter a Final Order granting the Falkner application and issuing permit number 206938.03. DONE and ENTERED this 26th day of April, 1996 in Tallahassee, Florida. WILLIAM F. QUATTLEBAUM, Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 26th day of April, 1996. APPENDIX TO RECOMMENDED ORDER, CASES NO. 95-5763 and 95-5764 To comply with the requirements of Section 120.59(2), Florida Statutes, the following constitute rulings on proposed findings of facts submitted by the parties. Petitioners Booth The Petitioners Booth proposed findings of fact fail to comply with the requirements of Rule 60Q-2.031(3), Florida Administrative Code, which requires citations to the record of hearing. The proposed findings are rejected as irrelevant or not supported by the greater weight of the evidence except where they are consistent with the Findings of Fact set forth herein. Respondents The Respondents' joint proposed findings of fact are accepted as modified and incorporated in the Recommended Order except as follows: 15. Rejected, cumulative. 28-29. Rejected, subordinate. 33. Rejected, subordinate. COPIES FURNISHED: Rose Ann DeVito, pro se 11001 Sumner Road Wimauma, Florida 33598 Diana P. and Charles B. Booth, pro se 10812 Sumner Road Wimauma, Florida 33598 Patricia Petruff, Esquire Dye and Scott, P.A. 1111 Third Avenue West Bradenton, Florida 34206 Martin Hernandez, Esquire Southwest Florida Water Management District 2379 Broad Street Brooksville, Florida 34609-6899 Peter G. Hubbell, Executive Director Southwest Florida Water Management District 2379 Broad Street Brooksville, Florida 34609-6899
