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MARIE COOK MATIS vs PASCO COUNTY UTILITIES DEPARTMENT AND DEPARTMENT OF ENVIRONMENTAL REGULATION, 92-002488 (1992)
Division of Administrative Hearings, Florida Filed:New Port Richey, Florida Apr. 24, 1992 Number: 92-002488 Latest Update: Jul. 31, 1995

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

Florida Laws (3) 120.57120.68403.088
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TOM VISCONTI vs NORTH PENINSULA UTILITIES CORPOTRATION AND DEPARTMENT OF ENVIRONMENTAL PROTECTION, 94-000082 (1994)
Division of Administrative Hearings, Florida Filed:Tallahassee, Florida Jan. 06, 1994 Number: 94-000082 Latest Update: May 02, 1996

The Issue Whether or not Petitioners should be ordered to pay reasonable costs and attorney's fees to the Respondent North Peninsula Utilities Corporation, and, if so, the determination of the amounts of costs and attorney's fees.

Findings Of Fact A brief background of the parties' history is important to disposition of the attorney's fees and costs motion. Petitioner Thomas Visconti is a resident of Seabridge Subdivision and is provided with wastewater treatment service by Respondent NPU. His property is not adjacent to NPU's treatment facility and the record does not establish that Mr. Visconti owns or operates any potable water wells within the vicinity of NPU's facility. See Finding of Fact 19, infra., concerning absence of any potable wells that could be affected by rerating the percolation pond. SCA is a homeowner's corporation which does not own property adjacent to the NPU facility, but which allegedly has members who do. The authority of the SCA vice-president to file the initial petition in November 1993 is subject to some conjecture, since the way this was done was because the SCA president informally delegated all duties to the vice-president while the president was out of state and all or most of the members signed the petition. There is no evidence the SCA bylaws permitted either such a delegation or the act of filing the Section 120.57(1) F.S. petition. Although an amended petition months later cured the "authority to file" problem, no evidence ever established which, if any, association members owned property adjacent to the NPU facility. Respondent NPU has owned and operated its Seabridge wastewater treatment plant since 1989. At that time, the plant had been rated at .9 MGD because of the previous owner's decision to economize by using an extended aeration form of treatment rather than contact stabilization method for which the plant had been designed. If the previous owner had utilized the contact method, the facility would have been rated at .157 MGD. The capacity of the plant percolation ponds at the time NPU acquired the facility was .157 MGD. In 1991, NPU applied for and received a Department of Environmental Regulation (DER, predecessor agency to DEP) permit to expand the facility to a treatment capacity of .210 MGD. Legal and appropriate notice of the Department's Intent to Issue was provided to the public. It was never formally challenged pursuant to Section 120.57(1) F.S., and the DER permit became final. Mr. Visconti and SCA felt abused by the agency and by NPU because they, Visconti and SCA, had missed that window of opportunity to challenge the 1991 plant expansion permit. Thereafter, they proceeded to fight NPU on the expansion and every other issue in whatever forum was available, notably before the Volusia County Commission and the Florida Public Service Commission. Mr. Visconti, acting as head of the SCA Sewer Committee, wrote a March 10, 1993 letter to DEP that stated, in pertinent part, as follows: Seabridge Civic Association, Inc. (hereafter "SCA") wishes to apprise you that SCA hereby intends to petition the DER for an administrative hearing(s) upon your giving any Notice of Intent to Issue any further permits, particularly any future 0.210 MGD Operating Permit, for the "Seabridge Subdivision" Sewer Treatment Plant. The letter, confirmed by Mr. Visconti's and Mr. Tyde's oral testimony, shows that Mr. Visconti and SCA intended to oppose any permit NPU applied for, regardless of its purpose, and that they knew of the original .210 MGD permit at that time. It goes on to protest sewer connections and previously finalized old permits. Mr. Visconti also wrote a July 2, 1993 letter to DEP, limiting communication, which stated, in pertinent part, as follows: Effective after today, please be advised that the official single point communication link between DER and SCA is with SCA President Charles Dassance. NPU's consulting engineer submitted "as-built" plans of the expansion in early 1993 after the NPU plant expansion construction had been completed. The percolation pond had been expanded to a lesser degree than that authorized by the 1991 DER permit because NPU had had to accommodate Volusia County setback requirements which eliminated approximately 11,000 square feet of pond bottom. NPU's engineer timely made the Department aware of the discrepancy and discussions occurred with the Department as to how to resolve it. NPU's engineer commissioned a groundwater engineering company to prepare a report to justify effluent disposal capacity of the percolation pond at the rate of .210 MGD, which was done on April 12, 1993 by PSI/Jammal & Associates ("the April Jammal report.") Not satisfied that the model used by Jammal for the April report could be verified by computer means available to the Department, DEP required a corroborating mounding analysis which was submitted on July 23, 1993 ("the July Jammal report.") In the meantime, DEP limited the percolation pond loading rate to .151 MGD until the applicant could justify a higher loading rate. NPU's 1991 construction permit for .210 MGD had expired in July of 1993. Needing a vehicle by which the review of the applicant's request to rerate the pond could take place, DEP required submittal of a construction permit application, which NPU subsequently filed on August 11, 1993 at the Department's Orlando office. To demonstrate reasonable assurance for the rerating authorization, NPU submitted the July 23 mounding analysis and showed that the loading rate would not be greater than 5.6 gallons per day per square foot. Percolation is considered to be excellent at the Seabridge treatment plant site because of the soil types underlying it, and the 5.6 figure is within the parameters of DEP's current rules. On October 26, 1993, DEP issued its Notice of Intent to issue the rerating permit for .181 MGD, calculated by multiplying the pond bottom area by the loading rate of 5.6 gpd2, which constituted a reduction from the 1991 .210 MGD loading rate approval. The Notice was published on November 11, 1993, and both Petitioners received individual Notice of the Intent to Issue. On November 22, 1993, SCA filed its petition challenging the proposed rerate authorization. Petitioner Visconti timely filed his petition on November 26, 1993. To establish substantial interests, Petitioners generally alleged that the noise, odor, and unsightliness of the plant would be increased if the rerating were to be approved. They also alleged adverse effects to property values, disparities in the technical information NPU had provided in support of its rerating application, and improper procedures employed by DEP in that it had not coordinated with Volusia County. Petitioners' asserted that their "proper purpose" for filing their petitions was that they had seen a 1993 letter of the DEP Regional Director to the effect that the pond was only licensed for .151 MGD and they assumed a new permit application for .181 MGD would constitute a dangerous increase. This assertion is spurious because both Mr. Visconti and Mr. Tyde admitted they had not even seen the rerate application before filing their petitions and that they did not know what the rerate application said until well into the formal administrative hearing process. Assuming, arguendo that the prior letter and DEP's Notice of Intent on its face could have misled Petitioners into believing there would be an increase from .151 MGD to .181 MGD instead of a decrease from .210 MGD to .181 MGD, that, alone, does not demonstrate a proper purpose in light of all the contrary and clarifying information available to Petitioners upon reasonable inquiry and which they chose to ignore. Because of the allegations of technical disparity and improper procedure, Visconti's petition was sustained against NPU's motion to dismiss with one paragraph struck. The SCA petition was dismissed for lack of showing of substantial interest and the amended SCA petition was challenged by NPU on the same basis, with ruling reserved for the recommended order. (See, the April 8 and June 6, 1994 orders, discussed supra.) After acknowledging on June 15, 1994 that NPU could demonstrate reasonable assurances, Petitioners presented evidence with regard to whether they had conducted a "reasonable inquiry" prior to filing the November 1993 petitions, but presented no proof as to their allegations of substantial interest contained in their petitions. Based on the evidence, it is found that neither Petitioner had any substantial interest which gave them standing to proceed with their challenges. Prior to filing their petitions, neither Petitioner had looked at NPU's August 1993 permit application. Between the Notice of Intent to Issue and filing their petitions, neither Petitioner contacted either DEP or NPU, nor conducted any review of the DEP files for data in support of their contention that the rerate authorization had been improperly granted by DEP. Petitioner SCA relied entirely on research conducted by Mr. Visconti when he had been chairman of SCA's Sewer Committee prior to July 2, 1993. Mr. Visconti's last review of NPU's files at the Department had been in June 1993, two months before the rerate application was even filed. Mr. Visconti ostensibly filed his petition upon his own opinion that the pond capacity was being increased from .151 to .181 instead of decreased from .210 to .181. His testimony was evasive or obstructionist in replying to reasonable questions concerning his area of expertise for forming his opinion, except to say that as a management consultant for unspecified high technology companies on how to manage their programs for federal, state, and local governments, he could interpret rules as well as anybody. As to his interpretation of DEP rules, however, he testified that he did not know precisely what the DEP capacity rules were; he did not ask any questions of DEP after the notice of intent to grant was issued, and he relied on hearsay from other SCA members. He never contacted NPU or their engineers after the rerate application. He opposed NPU's entitlement to the rerate permit even if NPU met all DEP rules, and he intended that his petition would cause the plant to go back the way it was before the 1991 expansion. He knew that the F.A.C. standard had changed to permit 5.6 GPDs, but he still objected to granting the permit on the terms contained in the rule. Mr. Visconti further testified that he knew in 1991 that a permit for .210 capacity had been issued and that the 1991 assessment was that percolation was excellent at the site. Although he had not seen the new permit application before filing his petition, he testified that he would not have cared if the application had said it reduced from .210 to .181, because he would still believe it was an increase. He never checked to see if the Intent to Issue had reconciled his pre-application concerns. He told himself the rerate would possibly increase pollutants. He did not know if June 1993 letters he relied on concerning a permit expiring and a .151 capacity of the pond had anything to do with the new permit application; he did not ask anybody, but just decided that they did. He admitted he intended to contest any and every permit NPU ever applied for regardless of what the permit was for. Despite the fact that the percolation pond has no equipment in it, he felt it was just "logical" that noise would increase. He admitted that he has never even looked over the fence, and so his petition's complaint of unsightliness was based solely on the already completed plant expansion, not the 1993 rerate application for the percolation pond which his petition challenged. He never asked DEP or any lawyer if noise, odor and aesthetics constitute pollution concerns; he assumed DEP personnel were incompetent; he decided DEP was withholding information from him because DEP did not keep all old permits for one facility or site in a single file and because papers he had seen in Public Service Commission and Volusia County files were not always in DEP files. He did not verify if the allegation in his petition that NPU did not own the land had been resolved before he filed his petition. He did not know that it had been resolved. Mr. Visconti left town for the entire five months immediately after filing his petition, with no concern as to how this might affect litigation. Mr. Tyde, now president of SCA, also testified that he filed the SCA petition because he believed there was to be an expansion of the plant. He specifically testified that he relied on Mr. Visconti's old research, except that he massaged some figures of his own based on standards of the Department of Health and Rehabilitation so as to compare that agency's condominium connection requirements with single family dwelling connections. Apparently, SCA opposes the influx of condominiums to its area. However, this subject matter has no real nexus to the gallonage one NPU percolation pond can accommodate under DEP rules, and it only goes to the Petitioners' belief that any change, starting with the 1991 expansion permit, impacts on property values and plant capacity and is simply a bad thing. Mr. Tyde filed SCA's initial petition without knowing if the SCA by-laws permitted him to do so. He decided there was expansion solely on the basis of a DEP letter that had been written before the current application was made. He believed erroneously that the words "rerating" and "increase" are synonymous. He never contacted anybody at DEP to verify his analysis; he filed the petition within nine days of the Notice of Intent to Issue, concentrating not upon the validity of the allegations but upon format. He knew there were no potable wells that would be affected by the plant so that paragraph six of SCA's amended petition drafted to further explain the disparities which were alleged environmental dangers could not possibly be correct. The intent of the SCA petition was not to challenge the pond rerating but to revert the area to what it had been before NPU's completed 1991-1993 expansion, and it was filed with the knowledge that NPU had spent a lot of money to complete that construction and would have to spend more to litigate the pond rerate application. When Petitioners admitted on the day scheduled for formal hearing on the merits that NPU and DEP would be able to show reasonable assurance for granting the permit, they thereby admitted that their petitions' allegations of disparities in the technical information NPU had provided could not be substantiated. Evidence at the fees hearing showed their allegations about data disparities were irrelevant to the pond rerate permit because the "disparities" the Petitioners were concerned about related to the collection or treatment processes of the plant, the permit for which had long-ago become final, or they were irrelevant because they were related to potential enforcement actions if something went wrong at the plant or if NPU operations violated DEP rules. The so-called "disparities" did not concern the percolation pond's capability. No reason to file any violation/enforcement action against NPU existed at the time the petitions were filed. Because the NPU facility was never involved in a DEP enforcement proceeding and was in constant touch with DER per the procedures outlined in Findings of Fact 5, and 7-9 and 20 supra, it is found that the "as built" construction of the pond at less than the originally authorized maximum capacity did not provide evidence that DEP had not followed its own rules for processing NPU's 1993 permit application and for its Intent to Issue. With regard to the procedure (mounding calculations) employed by DEP in approving the rerate, it was shown that Mr. Visconti waited until February 1994 to discuss his 1993 materials with a college professor of geology, another professor, and a professional engineer. Only in February 1994, three months after filing the petitions, did Mr. Visconti present these "experts" with the 1993 data, and even then he asked them about hypothetical flows from values he made up. When they could not give him any definitive answers, he claimed that DEP had withheld information and moved to continue the administrative proceeding. In considering the evidence, the candor and demeanor of all the witnesses has been weighed and the issue of whether or not DEP impeded Petitioners' access to agency files at any time is resolved against Petitioners and in favor of the agency. In so doing, consideration has been given to the evidence that SAC allowed Mr. Visconti to "take the point" on all investigations instead of doing anything on its own. That Petitioners, as laymen, may have been confused by DEP's use of discreet files for each of the successive permits applied for by NPU and granted or denied by the agency has been considered. The undersigned also appreciates that Mr. Visconti never understood that after some permits were granted, only microfilm copies of certain preliminary items remained. However, even so, Mr. Visconti's own testimony is to the effect that he was so fixated on the idea of a "conspiracy" or "collusion" between DEP and NPU that he rejected all explanations by DEP personnel and persisted in the ideation that DEP's failure to copy him with copies of all correspondence between the applicant and the agency pointed to collusion. He assumed, without good legal cause, that if something he had previously seen or thought should be in the agency file was not, in fact, in the agency file, he therefore had a right to file a petition against any permit application. Likewise, he decided, also without good legal cause that if there were anything in the agency file that caused him "concern" or which was different than the current permit application papers but which applied to any prior permit, he had a right to challenge the current permit application. The single instance of lack of cooperation and courtesy by one DEP employee as related by Ms. McCarthy concerning one telephoned question is accepted, but that single incident is not enough to swing the balance and absolve Petitioners of making a reasonable investigation before they filed their petitions. There is no evidence that the single question related to this permit; it was asked before the application for this permit was made and before the Intent to Issue was published; and the question apparently was never repeated. None of this evidence established any proper purpose in Petitioners for alleging data disparities or procedural irregularities, however defined. NPU presented evidence it had employed its attorney and agreed to pay certain fees and that its attorney's fees and costs are reasonable with the exception of the billings between October 5 and October 29, 1993. The allowable amount totals $24,690.00 in attorney's fees and $2,434.83 in costs. Petitioner Visconti established no evidence with regard to his counter motion for attorney's fees upon any legal theory whatsoever. DEP established no independent motion, entitlement, or amount of fees and costs.

Florida Laws (2) 120.57120.68
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FLORIDA WILDLIFE FEDERATION vs. GORDON V. LEGGETT, MOSELEY COLLINS, ET AL., 82-002235 (1982)
Division of Administrative Hearings, Florida Number: 82-002235 Latest Update: Jun. 21, 1991

The Issue Whether the applicants own the property in question? Whether the project would comply with the criteria of the South Florida Water Management District contained in Basis of Review for Surface Water Management Systems, specifically Sections 3.1.3 and 3.2? Whether flood protection would be inadequate or septic tanks unsuitable or whether the public health and safety would be compromised or the ultimate purchasers be deprived of usage of the property due to inundation in violation of Chapter 373, Florida Statutes (1981), or Rule 40E-4.301(1), Florida Administrative Code?

Findings Of Fact Ms. Williamson and Messrs. Leggett and Collins hold in fee simple a triangular 117.24-acre parcel in Okeechobee County as tenants in common under a warranty deed executed in their favor by one W. C. Sherman. They propose to develop the property as a trailer park (complete with airstrip) large enough to accommodate 109 trailers. To this end, soil would be dug up from the center of the property and used to raise the elevation of the surrounding land above the 100-year floodplain. (T. 47) The applicants have a dredging permit from the Department of Environmental Regulation authorizing them to excavate 629,889 cubic yards. They are proposing to dig to a depth of 76 feet below ground. This would create an 18-acre body of water ("Poe's Lake") which would overflow a V-notched weir into a county canal. The county canal would take the water to C- 38, one of the large canals to which the Kissimmee River has been relegated, at a point about 18 miles upstream from Lake Okeechobee. Runoff would wash over residential lots and roadways; the site would be graded to assure drainage into Poe's Lake. The minimum road crest elevation would be 30 feet NGVD ("[a]round twenty-nine feet" T.52), as compared to the control elevation for surface waters of 28.5 feet NGVD. WATER QUALITY The developers plan septic tanks for wastewater treatment. At the close of all the evidence, counsel for the applicants stated that sanitary sewers could be installed instead. Respondents' Proposed Recommended Order, p. With all the housing units in use, at least 10,900 gallons of effluent would seep into the ground from the tanks daily. There would be some evapotranspiration, but all the chemicals dissolved in the effluent would eventually end up in the groundwater. During the dry season, septic tank effluent would cause mounding of the groundwater and some groundwater movement toward, and eventual seepage into, Poe's Lake. The eventual result would be eutrophication and the growth of algae or macrophytes on the surface of Poe's Lake. This would cause dissolved oxygen violations in Poe's Lake. Discharges from the lake would inevitably occur, aggravating the situation in C-38, which already experiences dissolved oxygen levels below 5.0 milligrams per liter in the rainy summer months. Some fraction of the nutrients in the effluent from the septic tanks would ultimately reach Lake Okeechobee itself. The sheer depth of the excavation would create another water quality problem. Under the anaerobic conditions that would obtain at the bottom of Poe's Lake, bacteria acting on naturally occurring sulfates would produce hydrogen sulfide, ammonia and various other reduced organic nitrogen compounds. These substances are toxic to human beings and would, in some indeterminate quantity, enter the groundwater from Poe's Lake. This would affect the taste and perhaps the potability of water from any well nearby. It would be "possible to design a better system where there would be nutrient removal and a greatly reduced probability of violation of the dissolved oxygen criterion and obviation of the potential for ground water contamination." (T. 200) Installation of a baffle on the weir would serve to prevent buoyant debris from entering surface waters of the state. BASIS OF REVIEW Official recognition was taken of the "Basis of Review for Surface Water Management Permit Applications Within the South Florid Water Management District," parts of which all parties agree pertain in the present proceedings. Among the criteria stated in this document are: 3.1.3 Waste and Wastewater Service - Potable water and wastewater facilities must be identified. The Applicant for a Surface Water Management Permit must provide information on how these services are to be provided. If wastewater disposal is accomplished on-site, additional information will normally be requested regarding separation of waste and storm systems. 3.2.1.4 Flood protection - Building floors shall be above the 100 year flood elevations, as determined from the most appropriate information, including Federal Flood Insurance Rate Maps. Both tidal flooding and the 100 year, 3 day storm event shall be considered in determining elevations. b. Commercial and industrial projects to be subdivided for sale are required to have installed by the permittee, as a minimum, the required water quality system for one inch of runoff detention or one half inch of runoff retention from the total developed site. State standards - Projects shall be designed so that discharges will meet State water quality standards, as set forth in Chapter 17-3, Retention/detention criteria - Retention and/or detention in the overall system, including swales, lakes, canals, greenways, etc., shall be provided for one of the three following criteria or equivalent combinations thereof . . . Wet detention volume shall be provided for the first inch of runoff from the developed project, or the total runoff from a 3-year, 1-hour rainfall event, whichever is greater. Dry detention volume shall be provided equal to 75 percent of the above amounts computed for wet detention. Retention volume shall be provided equal to 50 percent of the above amounts computed for wet detention. 3.2.4.1 Discharge structures should include gratings for safety and maintenance purposes. The use of trash collection screens is desirable. Discharge structures shall include a "baffle" system to encourage discharge from the center of the water column rather than the top or bottom. 3.2.4.4.2 b. Control elevations should be no higher than 2 feet below the minimum road centerline elevation in the area served by the control device in order to protect the road subgrade. Simply detaining runoff before discharging it offsite will not insure that the water quality standards set forth in Chapter 17-3 will be met. Whether the standards are met depends on, among other things, the composition of the runoff. FWF'S INTEREST Among the purposes of the FWF, as stated in its charter, Shall be to further advance the cause of conservation in environmental protection, to perpetuate and conserve fish and wildlife, oil, water, clean air, other resources of the State and so manage the use of all natural resources, that this generation and posterity will receive the maximum benefit from the same. (T. 248-9) Four or five thousand Floridians belong to FWF. FWF members "make use" (T. 250) of the waters of Lake Okeechobee, the Kissimmee River and specifically of the waters in C-38. PROPOSED FINDINGS CONSIDERED The applicants and FWF filed post hearing memoranda and proposed recommended orders including proposed findings of fact which have been considered in preparation of the foregoing findings of fact. They have been adopted, in substance, for the most part. To the extent they have been rejected, they have been deemed unsupported by the weight of the evidence, immaterial, cumulative or subordinate.

Recommendation Upon consideration of the foregoing, it is RECOMMENDED: That SFWMD deny the pending application for surface water management permit. DONE and ENTERED this 29th day of November, 1983, in Tallahassee, Florida. ROBERT T. BENTON II, Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 29th day of November, 1983. COPIES FURNISHED: Dennis J. Powers, Esquire Gunster, Yoakley, Criser & Stewart 400 South County Road Palm Beach 33480 Terrell K. Arline, Esquire 325-C Clematis Street West Palm Beach, Florida 33401 Irene Kennedy Quincey, Esquire 3301 Gun Club Road West Palm Beach, Florida 33406 Charles P. Houston, Esquire 324 Datura Street, Suite 106 West Palm Beach, Florida 33401

Florida Laws (2) 120.57120.60 Florida Administrative Code (1) 40E-4.301
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SHELLEY MEIER vs KELLY ENDRES, IFRAIN LIMA, AND DEPARTMENT OF ENVIRONMENTAL PROTECTION, 20-002994 (2020)
Division of Administrative Hearings, Florida Filed:Tallahassee, Florida Jul. 01, 2020 Number: 20-002994 Latest Update: Dec. 25, 2024

The Issue The issue in this case is whether the Respondents, Kelly Endres and Ifrain Lima (Endres/Lima), are entitled to an Environmental Resource Permit (ERP) that would allow use of 0.535 acres of previously impacted wetlands for the construction of a single-family residence and associated structures, a 30' x 30' private dock with a 4' access walkway, and a 12' wide boat ramp (Project) at 160 Long Acres Lane, Oviedo, Florida (Property).

Findings Of Fact The following Findings of Fact are based on the stipulations of the parties and the evidence adduced at the final hearing. The Parties The Department is the administrative agency of the state statutorily charged with, among other things, protecting Florida's air and water resources. The Department administers and enforces certain provisions of chapter 373, part IV, Florida Statutes, and the rules promulgated, thereunder, in the Florida Administrative Code. Under that authority, the Department determines whether to issue or deny applications for ERPs. Respondents Endres/Lima own the Property and are the applicants for the ERP at issue in this consolidated proceeding. Petitioner Meier is a neighboring property owner to the south of the Property. Petitioner Meier's property includes a single-family residence with accessory structures and is located on Long Lake. Petitioner Meier is concerned that the NOI provides inadequate environmental protections and that there will be flooding on adjacent properties from the Project. Petitioner Hacker is the neighboring property owner adjacent to the south of the Property. Petitioner Hacker's property includes a single-family residence with accessory structures and is located on Long Lake. He is concerned with the completeness of the application for the Project, the calculation of wetland impacts, that reasonable assurances were provided, and that the Department's NOI ignores willful negligence and allows disparate treatment of Respondents Endres/Lima. Petitioner Kochmann is a property owner with a single-family residence and accessory structures located on Long Lake. She is concerned that the NOI is based on a misleading application and provides no evidence that the Respondents Endres/Lima made reasonable efforts to eliminate and reduce impacts detrimental to the environment. History of the Project and Application On April 12, 2018, Respondents Endres/Lima applied for an ERP for proposed wetland impacts associated with a planned single-family home on the Property. This was the first ERP application for the Property. The Department sent a Request for Additional Information (RAI) on April 24, 2018, and a second RAI on November 2, 2018. Respondents Endres/Lima provided a Mitigation Service Area Rule Analysis for "As If In-Basin" for the Lake X Mitigation Bank for the St. Johns River Water Management District Basins to the Department via email on May 10, 2018. Respondents Endres/Lima submitted revised plans to the Department on September 19, and October 30, 2018. On January 7, 2019, the Department denied the ERP application. The Department and Respondents Endres/Lima, on July 18, 2019, entered into a Consent Order (CO). The Department found, and Respondents Endres/Lima admitted, that approximately 0.80 acres of jurisdictional wetlands were dredged and filled without a valid ERP from the Department; and was done with improperly installed erosion and sedimentation controls. On August 22, 2019, Respondents Endres/Lima submitted a second ERP application. The Department sent an RAI on September 20, 2019, to which Respondents Endres/Lima responded on December 19, 2019. In addition, Respondents Endres/Lima reserved 0.60 of forested Uniform Mitigation Assessment Method (UMAM) wetland credits from the Lake X Mitigation Bank and provided the Department with an updated site plan and Lake X Mitigation Bank credit reservation letter. The Department issued an NOI on February 7, 2020, which was timely published in the Sanford Herald on February 9, 2020. Respondents Endres/Lima provided timely proof of publication to the Department on February 13, 2020. Consent Order and Compliance A warning letter was issued to Respondents Endres/Lima on January 30, 2019, for the dredging and filling of approximately 0.80 acres of forested wetlands and improper installation of erosion and sedimentation control. The CO, executed on July 18, 2019, required Respondents Endres/Lima to cease any dredging, filling, or construction activities on the Property, submit an application for an Individual ERP within 30 days, and pay $5,599.00 in penalties and the Department's costs and expenses. After the issuance of an ERP, Respondents Endres/Lima were also required to implement the restoration actions outlined in the CO. Respondents’ Endres/Lima’s application, dated August 19, 2020, was submitted to the Department on August 22, 2020. Respondents Endres/Lima paid the CO's penalties and costs, and had multiple meetings with the Department to complete the requirements of the CO. Respondents Endres/Lima’s expert, Mr. Exner, testified that he began working on a restoration plan for the Property, which will be provided to the Department once an ERP is issued. Permitting Criteria The Department reviewed the complete application and determined that it satisfied the conditions for issuance under Florida Administrative Code Rule 62-330.301, and the applicable sections of the ERP Applicant's Handbook Volume I (AH Vol. I). The Department also considered the seven criteria in rule 62-330.302 and section 373.414(1)(a), and determined that implementing the Project would not be contrary to the public interest. Water Quantity, Flooding, Surface Water Storage and Conveyance Respondents’ Endres/Lima's civil engineering expert, Mr. Herbert, testified that according to the drainage design, the Property would have swales on either side of the proposed residence to slope water away from the residence. There would also be a conveyance swale on the north property boundary to convey water from the street area and front yard toward the restoration and wetland areas with ultimate discharge to Long Lake. He stated that the elevation of the road at the front of the Property would be at 47.4 feet, and the elevation at the terminus of the swale would be at 45 feet. This would allow a 2.4-foot vertical fall for the swales to convey water to the lake. The design would preserve pre-development surface water flow over the Property to Long Lake, which is the lowest elevation in the area, and will ensure that storm water does not flood adjacent properties. Mr. Herbert also testified that the Project design would maintain pre-development water storage capacity. The imported fill that is currently on the Property in the flood plain would be removed and reshaped so that the lake elevation would be maintained and water can flow correctly. Elimination or Reduction of Impacts and Mitigation Respondents Endres/Lima provided the Department with design modifications to reduce impacts associated with the Project. These included a 15-foot restoration buffer along the lake front's northern shoreline, an elevated access walkway five feet above the wetland restoration area to the proposed dock, limiting the width of the access walk to four feet, and limiting the boat ramp width to a single-lane. In June 2015, an informal wetlands determination was conducted for the Property. The informal determination concluded that the entirety of the Property were wetlands. However, this was an informal determination and was not binding. In October 2016, before the first permit application was submitted, Mr. Exner did a wetlands delineation flagging prior to the Property being cleared or disturbed. Mr. Exner testified that, in his opinion, the Property was not all wetlands because large pines near the road had no high water marks, adventitious growth around the bases, or evidence of pine borer beetles along with other indicators of upland habitat. This wetland delineation was part of the permit submittal, was shown on the plans, was accepted by the Department, and was used for the preparation of the UMAM scoring. Mr. Exner's wetland delineation line was used by the Department to help determine and map the wetland impacts identified in the CO. The direct impact area was assessed at 0.54 acres with a secondary impact area of 0.02 acres for a total impact of 0.56 acres, and a functional loss score of 0.364. Respondents Endres/Lima reserved 0.6 forested UMAM mitigation credits, almost double the amount of functional loss under the UMAM assessment, agreed to purchase 0.46 credits. The excess mitigation bank credits implement part of a plan that provides regional ecological value and greater long-term ecological value than the area of wetland adversely affected. Secondary and Cumulative Impacts The Project's UMAM analysis assessed 0.02 acres, or 870 square feet, of secondary impacts. These impacts would be fully offset by the mitigation proposed for the Project. Petitioners' expert, Mr. Mahnken, noted three areas where he thought the application was incomplete. The first was that the site plan did not call out the location of the secondary impacts. However, Part III: Plans of Section B of the application, does not require that the site plan show the location of the secondary impacts. The application requirements for "plans" requires only the boundaries and size of the wetlands on the Property and provide the acreages of the upland areas, wetland impact areas, and the remaining untouched area. Second, Mr. Mahnken questioned the calculation performed to determine the secondary impact acreage. However, Mr. Mahnken read the information incorrectly and stated that the secondary impact area was 0.002 acres, or 87 square feet, when the UMAM score sheet clearly showed that the secondary impact area is 0.02 acres, or 870 square feet. In addition, the Department's witness, Ms. Warr, testified that even if the Department were to use Mr. Mahnken's analysis, the result would have been the same, i.e., the requirement to purchase 0.46 mitigation credits. Thus, Petitioners failed to support their claim that the Project would have adverse secondary impacts. Third, Mr. Mahnken asserted that cumulative impacts were not adequately addressed. He testified that the assessment for the Property using spill over benefits, in his opinion, was not enough to fully offset the impacts of the Project. Mr. Mahnken acknowledged, however, that his opinion was open to debate, and that he had not conducted any rigorous hydrologic evaluation in reaching his opinion. Respondents Endres/Lima had submitted a report prepared by Breedlove, Dennis & Associates (BDA Report) with their application in order to demonstrate compliance with section 10.2.8, ERP AH Vol. I, regarding cumulative impacts. The BDA Report utilized peer-reviewed hydrologic data that was reviewed and approved by the South Florida Water Management District, and was accepted by the Department pursuant to section 373.4136(6)(c). This was consistent with the Property's location within the mitigation service area for the Lake X Mitigation Bank. The Project is located within the Econlockhatchee River drainage basin, which is a nested basin within the larger St. Johns River [Canaveral Marshes to Wekiva] drainage basin. The Lake X Mitigation Bank is located outside of the Econlockhatchee River drainage basin, but the Project is located within the Lake X Mitigation Bank service area. The BDA report determined that: In summary, the Lake X Mitigation Bank is a regionally significant mitigation bank site that has direct hydrological and ecological connections to the SJRWMD basins, to include the cumulative impacts basin in which the subject property is located (i.e., SJRWMD Basin 19). The size, biodiversity, and proximity of the mitigation bank site to the SJRWMD basins, and the regionally significant hydrological connection between the mitigation bank site and the contiguous SJRWMD mitigation basins, supports the use of this mitigation bank site “as if in basin” mitigation for the Lima/Endres Wetland Fill Project. Additionally, the evaluation of factors, to include connectivity of waters, hydrology, habitat range of affected species, and water quality, demonstrates the spillover benefits that the Lake X Mitigation Bank has on the St. Johns River (Canaveral Marshes to Wekiva) mitigation basin, which includes the Econlockhatchee River Nested basin, and demonstrated that the proposed mitigation will fully offset the impacts proposed as part of the Lima/Endres Wetland Fill Project “as if in-basin” mitigation. The Lake X Mitigation Bank will protect and maintain the headwaters of two regionally significant drainage basins [i.e., the Northern Everglades Kissimmee River Watershed and the Upper St. Johns River Watershed (to include the nested Econlockhatchee River basin)], and will provide resource protection to both river systems (SFWMD Technical Staff Report, November 29, 2016). Furthermore, the permanent protection and management of the Lake X Mitigation Bank will provide spillover benefits to the SJRWMD basins located within the permitted MSA. Mr. Mahnken stated that his review of the Project did not include a hydrologic study and only looked at basic flow patterns for Long Lake. By contrast, the BDA Report included an extensive hydrologic study, looked at all required factors in section 10.2.8(b), ERP AH, Vol. I, and determined that the Project would be fully offset with the proposed mitigation. Thus, Respondents Endres/Lima provided reasonable assurance that the Project will not cause unacceptable cumulative impacts. Water Quality Rule 62-330.302(1)(e) requires that Respondents Endres/Lima provide reasonable assurance that the Project will not adversely affect the quality of receiving waters such that the state water quality standards will be violated. The conditions of the ERP would require the use of best management practices including a floating turbidity curtain/barrier, soil stabilization with grass seed or sod, and a silt fence. Respondent Endres/Lima's experts, Mr. Herbert and Mr. Exner, testified that there is an existing turbidity barrier in the lake around the property and a silt fence around the east half of the Property. While these items are not required by the Department until construction of the Project, part of the silt fence and the turbidity barrier are already installed on the Property and will be required to be repaired and properly maintained in accordance with the conditions of the ERP and Site Plan SP-2. Mr. Herbert testified that the Property will be graded in a manner that will result in a gentle sloping of the lake bank in the littoral zone, which would allow revegetation of the lake bank. Outside of the restoration area and the undisturbed wetlands, the backyard would be covered with grass to prevent migration of sand and soil discharging into the lake. Mr. Exner testified that the grass swales proposed for the Project would provide a considerable amount of nutrient uptake and filtration of surface water on the Property. Also, in the restoration area next to the lake, the restoration plan includes a dense planting plan with native species that have good nutrient uptake capability. Impacts to Fish and Wildlife Rule 62-330.301(1)(d) requires that Respondents Endres/Lima provide reasonable assurance that the Project will not adversely impact the value of functions provided to fish and wildlife and listed species by wetlands and other surface waters. Mr. Exner testified that, in his review of the Property, he did not identify any critical wildlife habitat. He visited the Property multiple times and he did not see any osprey nests, deer tracks, animal scat, gopher tortoises, or sand hill cranes. The Department's Ms. Warr testified that the Florida Fish and Wildlife Conservation Commission database was reviewed, and did not show any listed species in the area. Publication of Notice Petitioners argued that the notice published in the Sanford Herald on February 9, 2020, did not meet the requirements of section 373.413(4). Despite the notice having no effect on their ability to timely challenge the proposed ERP, Petitioners argued that the published notice was insufficient because the notice itself did not provide the name of the applicants or the address of the Project, only a link to the Department's permit file. Unlike the notice required in section 373.413(3), where a person has filed a written request for notification of any pending application affecting a particular designated area, section 373.413(4) does not specify the contents of the published notice. Section 373.413(4) does not require the published notice to include the name and address of the applicant; a brief description of the proposed activity, including any mitigation; the location of the proposed activity, including whether it is located within an Outstanding Florida Water or aquatic preserve; a map identifying the location of the proposed activity subject to the application; a depiction of the proposed activity subject to the application; or a name or number identifying the application and the office where the application can be inspected. In response to the published notice, the Department received approximately ten petitions challenging the NOI, including the petitions timely filed by Petitioners. Therefore, Petitioners were not harmed by any information alleged to have been left out of the published notice. Ultimate Findings Respondents Endres/Lima provided reasonable assurance that the Project will not cause adverse water quantity impacts to receiving waters and adjacent lands; will not cause adverse flooding to on-site or off-site property; and will not cause adverse impacts to existing surface water storage and conveyance capabilities. Respondents Endres/Lima provided reasonable assurance that the Project complied with elimination and reduction of impacts, and proposed more than adequate mitigation. Respondents Endres/Lima provided reasonable assurance that the Project will not cause adverse secondary impacts to water resources; and unacceptable cumulative impacts to wetlands and other surface waters within the same drainage basin. Respondents Endres/Lima provided reasonable assurance that the Project will not cause adverse water quality impacts to receiving water bodies. Respondents Endres/Lima provided reasonable assurance that the Project will not adversely impact the value of functions provided to fish and wildlife, and listed species by wetlands, or other surface waters. Petitioners failed to prove lack of reasonable assurance by a preponderance of the competent substantial evidence.

Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department enter a Final Order granting Respondents’ Endres/Lima's ERP application. DONE AND ENTERED this 1st day of December, 2020, in Tallahassee, Leon County, Florida. S FRANCINE M. FFOLKES Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us COPIES FURNISHED: Filed with the Clerk of the Division of Administrative Hearings this 1st day of December, 2020. Jay Patrick Reynolds, Esquire Department of Environmental Protection 3900 Commonwealth Boulevard, Mail Station 35 Tallahassee, Florida 32399 (eServed) Neysa Borkert, Esquire Garganese, Weiss, D'Agresta and Salzman 111 North Orange Avenue Post Office Box 398 Orlando, Florida 32802 (eServed) Tracy L. Kochmann 249 Carolyn Drive Oviedo, Florida 32765 (eServed) Shelley M. Meier 208 Long Acres Lane Oviedo, Florida 32765 (eServed) Brian Hacker 170 Long Acres Lane Oviedo, Florida 32765 (eServed) Lea Crandall, Agency Clerk Department of Environmental Protection Douglas Building, Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399 (eServed) Justin G. Wolfe, General Counsel Department of Environmental Protection Legal Department, Suite 1051-J Douglas Building, Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399 (eServed) Noah Valenstein, Secretary Department of Environmental Protection Douglas Building 3900 Commonwealth Boulevard Tallahassee, Florida 32399 (eServed)

Florida Laws (7) 120.52120.569120.57120.68373.413373.4136373.414 Florida Administrative Code (2) 62-330.30162-330.302 DOAH Case (5) 11-649512-257420-299320-299420-2995
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LEE MADDAN vs DEPARTMENT OF ENVIRONMENTAL PROTECTION, 03-001499 (2003)
Division of Administrative Hearings, Florida Filed:Shalimar, Florida Apr. 28, 2003 Number: 03-001499 Latest Update: Nov. 24, 2003

The Issue The issues for determination in this case are: 1) whether the Department of Environmental Protection (DEP) has dredge and fill permitting jurisdiction over a certain body of water known as Lake Blake in Okaloosa County, Florida; 2) if DEP's dredge and fill permitting jurisdiction is established, whether Petitioner qualifies for an exemption from DEP's dredge and fill permitting jurisdiction; and 3) if not otherwise exempt from DEP's dredge and fill permitting jurisdiction, whether Petitioner's application No. 46-0199306-001-EE, seeking to place a modular home on a fill pad in Lake Blake, should be approved by DEP.

Findings Of Fact Parties DEP is the agency of the State of Florida vested with the power and duty to enforce the provisions of Chapters 373 and 403, and the rules promulgated in Chapter 62, Florida Administrative Code. DEP is the only agency involved in these proceedings. Lee Maddan (Maddan) is a long-time resident of Okaloosa County, and the Petitioner in Case No. 03-1499. Maddan is a Respondent in Case No. 03-2040. Maddan has personally observed activities occurring at the Lake Blake property for more than 38 years, including the excavation of the lake. Santa Rosa Three, Inc. (the Corporation), is a Respondent in Case No. 03-2040, and holds fee simple title to the property containing Lake Blake, which is located in unincorporated Okaloosa County between Lewis Street and Clifford Street in Sections 2 and 3, Township 2 South, Range West. Santa Rosa II is also Respondent in Case No. 03-2040, and is a corporate predecessor in interest to the Corporation. Maddan holds equitable title to the Lake Blake property and is in the process of purchasing the fee simple title to the property from the Corporation. Maddan is and was at all material times hereto authorized by the Corporation to enter upon the Lake Blake property, to proceed to develop the land, to obtain permits in his name and to do other acts to prepare the property for Maddan's purchase. History of Lake Blake Lake Blake is an artificially created water body in unincorporated Okaloosa County, having a water surface area slightly less than six acres. There is a small island in the center of the lake. The property surrounding Lake Blake presently consists of both uplands and wetlands. No other water body is visible from Lake Blake. For DEP jurisdictional determination purposes, Lake Blake is located in the Northwest District of Florida. The oldest records of the Lake Blake property dating to 1826, indicate that the property was flat land with natural vegetation dominated by palmetto and galberry. The property historically had no flowing streams. In the 1950's the then owner of the property began excavating a borrow pit on the property. The excavations continued until approximately 1979. As the borrow pit excavations continued a lake formed due to the intrusion of underground water as well as collected rainfall. During the excavation period, and until approximately 1976, the land around the borrow pit was primarily pasture land with no trees or other vegetation. Up to 1976, there was no wetland vegetation growing on the property. Prior to 1960, the natural stormwater flow from the property was to the southwest toward Cinco Bayou, a defined water body of the State of Florida which on a direct line is located approximately one-quarter mile from the property. Cinco Bayou is the body of water of the State nearest to Lake Blake. During the 1960's, a road known as Lewis Street (also known as Mayflower Avenue) was constructed along the southern boundary of the property. At the time of the construction of Lewis Street, the borrow pit was separated into two parts, an eastern and western section. A concrete culvert divided the sections of the borrow pit. At the time of the Lewis Street construction, a stormwater discharge pipe was installed by Okaloosa County and excess water flowed out of the borrow pit only at certain times in direct response to rainfall. The installation of the stormwater discharge pipe on Lewis Street was intended to drain excess rainfall from the borrow pit. Okaloosa County never acquired ownership of the borrow pit for use as a stormwater retention pond. The water body that formed in the borrow pit would come to be called Lewis Street Pond, or Blake Lake, and eventually Lake Blake. The natural flow of the stormwater from the property was further altered in the 1970's when a public elementary school was constructed by Okaloosa County on Lewis Street. The public school is located between the property and Cinco Bayou. Borrow pit operations formally ceased in September of 1980 when DEP's predecessor agency, the Department of Environmental Regulation (DER), entered an order requiring the cessation of mining operations. The physical operations had actually ceased a few years before the DER order. Lake Blake originally resulted from collected rainfall, as well as underground water intrusion in the borrow pit. Over the subsequent years and at the present time, additional diverted stormwater runoff collected in the lake as a result of Okaloosa County's stormwater drainage system. Lake Blake today is an artificial body of water owned entirely by one person. Residential housing is located on property surrounding Lake Blake. The lake is occasionally utilized for recreational purposes, including fishing. The property surrounding the lake is not open to the general public, and the entrances to the property are fenced. For purposes of this proceeding, there are no threatened or endangered plants on the property. Okaloosa County Stormwater Drainage System Okaloosa County has constructed a stormwater drainage system that runs through the Lake Blake drainage area. As part of this stormwater drainage system, Lake Blake collects diverted stormwater discharge from surrounding areas which have been previously developed. Residential neighborhoods are close to the area, specifically the Berkshire Woods Subdivision. Indeed, as a condition for the development of the Berkshire Woods Subdivision in 1976, the Okaloosa County Planning Commission required that a former owner of the property, Ron Blake, excavate the lake and have it made ready for stormwater drainage from the proposed development of the Berkshire Woods Subdivision. In addition to the residential areas and the public school to the south, there is a private school to the north across the road on Clifford Street which also diverts water to the lake from its campus and parking lots Okaloosa County has installed several pipes which carry stormwater from the surrounding developed areas into Lake Blake. The only drainage out of Lake Blake is via the stormwater discharge pipe located at the southern boundary of the property on Lewis Street which was installed by Okaloosa County in the 1960's. Okaloosa County's stormwater discharge system serving Lake Blake is integrated into a series of interconnecting underground stormwater pipes which route the flow of the water for approximately one-half mile before ultimately discharging water into Cinco Bayou. Okaloosa County's stormwater discharge system which ultimately connects Lake Blake with Cinco Bayou is composed of buried pipes. DEP considers buried pipes or culverts which convey stormwater as excavated water bodies. The installation of Okaloosa County's stormwater discharge system required the excavation of land. Under DEP's interpretation of its rules, specifically Rule 62-312.030(2), Florida Administrative Code, the underground installation of stormwater pipes is sufficient to establish a series of excavated water bodies which connect Lake Blake to Cinco Bayou. Prior to the installation of Okaloosa County's stormwater discharge pipe on Lewis Street in the 1960's, there was no dredge and fill permitting jurisdiction which applied to the property containing Lake Blake. The stormwater discharge pipe has continuously existed on the southern boundary of the property since its installation in the 1960's to the present. Lake Blake was not originally designed, constructed, nor permitted as a stormwater treatment or retention pond. Lake Blake incidentally resulted from the borrow pit excavations. Okaloosa County, however, has at least since 1976 utilized Lake Blake as part of its stormwater drainage system. Okaloosa County never acquired title to Lake Blake. In 1981, the Okaloosa County Board of Commissioners (who were not the owners of the property) applied for, and were issued by DER, a Construction Permit (No. RC-46-80-2031, dated May 27, 1981, which expired November 27, 1981), for "Blake Lake Modifications," which permit stated it was "to modify an existing stormwater drainage system." This permit allowed for, among other items, construction of "two earthen berms in Blake Lake" and "the diversion of lake flow from the western lake to the eastern lake." Although attempts were made to construct the two earthen berms, due to the white clay composition of the soil the berms were not successfully established. In 1984 DER issued another Construction Permit (No. 460853421 dated August 20, 1984, which expired August 15, 1987) to the Okaloosa County Board of Commissioners (who again were not the owners of the property) for the purpose constructing "two drainage channels . . . from a berm separating East and West Blake Lake." The drainage channels were thereafter completed and the east and west portions of the lake were eventually connected. On August 14, 1984, Okaloosa County also filed a Notice of New Stormwater Discharge with DER which proposed a re-routing of an existing stormwater drainage system which then diverted stormwater from the Candlewood Subdivision and Navy Street into Lake Blake. The stated purpose of the re-routing of the stormwater drainage system away from Lake Blake was to address flooding problems in the Candlewood Subdivision. By letter dated August 21, 1984, DER informed Okaloosa County that "the stormwater discharge is exempt from stormwater permitting requirements of the Department pursuant to Florida Administrative Code Rule 17-25.03(2)(c)." DER came to this conclusion in 1984 because the proposed project was "the modification of an existing County stormwater management system not serving a new development or increasing pollution loading." Although Lake Blake was utilized by Okaloosa County as part of the existing Okaloosa County stormwater drainage system, which in 1984 qualified for a DER stormwater permitting exemption, nothing pertaining to this stormwater permitting exemption supports a finding that Lake Blake was originally constructed, permitted or designed solely for the purpose of stormwater treatment so as to qualify for an exemption from DEP's dredge and fill jurisdiction under Rule 62-312.050(4), Florida Administrative Code. Dredge and Fill Permitting Jurisdiction Prior to the installation of Okaloosa County's stormwater discharge pipes on the property in the 1960's, there was no dredge and fill permitting jurisdiction which applied to the property and Lake Blake. Under current law, the Northwest District of Florida is governed by separate jurisdictional determination provisions. In order to initially establish DEP's dredge and fill permitting jurisdiction over wetlands and surface waters in the Northwest District, DEP must demonstrate that the wetlands and surface waters are connected to the surface waters of the State. Since 1995, isolated wetlands in all the rest of the State of Florida are regulated by DEP without regard to any connection to the surface waters of the State. In the Northwest District under Rule 62-312.030(2), Florida Administrative Code, "surface waters of the state are those waters listed below and excavated water bodies, except for those exempted by Section 62-312.050(4), F.A.C., which connect directly or via an excavated water body or series of excavated water bodies . . ." to waters of the State. Under Rule 62- 312.045, Florida Administrative Code, however, "[i]solated wetlands that infrequently flow or otherwise exchange water with a described water body are not intended to be included within the dredge and fill jurisdiction of the Department." By letter dated April 24, 2001, DEP advised Santa Rosa II, Inc., that the Lake Blake property was not subject to DEP's dredge and fill jurisdiction. The letter was sent in response to an application seeking to fill 2.5 acres of the southeastern portion of the lake for the construction of an apartment complex. The letter was issued by DEP's Northwest District, and signed by Martin Gawronski on behalf of Larry O'Donnell, the Environmental Manager for Permitting Section of the Northwest District. The letter was issued after a visit to the property by one or more DEP employees, and based on an informal determination that Lake Blake was not connected to the waters of the State. In May of 2001, the United States Army Corps of Engineers determined that the Lake Blake property was not within its jurisdiction. Subsequent to the issuance of the April 24, 2001, non- jurisdictional letter, certain employees of Okaloosa County (not specifically named in these proceedings) contacted DEP seeking reconsideration of DEP's decision. These Okaloosa County employees thereafter met with DEP employees at the property and communicated by telephone with DEP employees while DEP considered a re-determination of its non-jurisdictional decision. The property owners were then notified that DEP was in the process of re-evaluating its non-jurisdictional decision. By letter dated October 24, 2001, DEP advised Santa Rosa II, Inc., that DEP had made a "correction" to the letter of April 24, 2001, and had determined that the property was in fact subject to DEP's dredge and fill permitting jurisdiction, because the "pond" was "connected to jurisdictional waters" of the State. The October 24, 2001 letter, like the previous letter, was issued from DEP's Northwest District signed by Martin Gawronski on behalf of Larry O'Donnell. Between April 24, 2001, and October 24, 2001, there were no man-made alterations made to the Lake Blake property. Between March and April 2002, Maddan filled in a portion of the lake and lacustrine wetlands. Maddan also built two pedestrian footbridges over the lake to the small island in the middle of the lake. DEP asserted its dredge and fill permitting jurisdiction based upon the existence of a series of underground pipes installed by Okaloosa County as part of its stormwater drainage system that conveys excess stormwater from Lake Blake to Cinco Bayou. Installation of the underground pipes required excavation. Neither the April 24, 2001 letter, nor the subsequent October 24, 2001, letter issued by the Northwest District, is binding determination of DEP's dredge and fill permitting jurisdiction over the wetlands and surface waters of Lake Blake. The authority to make a binding DEP dredge and fill permitting jurisdictional determination is vested in Dr. John Tobe, Environmental Administrator of the Wetland Evaluation and Delineation Section and his staff. DEP's Site Inspections/Jurisdictional Determination In April of 2002, Stacy Owens, DEP Environmental Specialist, received a telephone call from Chuck Bonta with the Okaloosa County Code Enforcement Department, and an unnamed homeowner, complaining that Lee Maddan had built two unpermitted pedestrian footbridges at Lake Blake and was also filling in part of Lake Blake. Ms. Owens initially investigated whether DEP had issued any permits for the placement of fill in Lake Blake or the surrounding wetlands, and determined that no permits had been issued. Ms. Owens further discovered that a prior Notice of Violation and Orders for Corrective Action had been issued by DER in 1980 against the Okaloosa County Board of Commissioners and Lloyd D. Junger (a lessor conducting mining operations). The 1980 case pertained to the discharge of turbidities from the Lewis Street Pond into Cinco Bayou. A final order in that case was entered on January 5, 1981, requiring Okaloosa County to make payment to DER and take corrective action. On April 23, 2002, Ms. Owens followed up on these complaints by performing a site visit to Lake Blake. At this time Ms. Owens observed two unpermitted pedestrian footbridges, unpermitted fill in a finger of Lake Blake, and unpermitted fill within a 20-foot by 25-foot lacustrine wetland area. On April 25, 2002, Maddan came to Ms. Owens' office to discuss whether permits were necessary for the placement of fill at Lake Blake. At that time Maddan showed Ms. Owens the previous letters of April 24, 2001, and October 24, 2001, which had been sent from the Northwest District of DEP. Maddan stated that in his opinion no dredge and fill permit was needed because Lake Blake was not within the jurisdiction of DEP. Ms. Owens was then informed by employees of Okaloosa County that there were underground pipes connecting Lake Blake to Cinco Bayou. She obtained from Gary Bogan of Okaloosa County an aerial map of the drainage area for Lake Blake which identified the location of the culvert on Lewis Street which conveys excess flow from Lake Blake to Cinco Bayou. On April 30, 2002, Ms. Owens performed another site inspection at Lake Blake. During this site inspection, she tracked the connection from Lake Blake to Cinco Bayou by personal observation. After her second site inspection, Ms. Owens e-mailed her findings to Dr. Tobe, and inquired whether the underground pipes satisfied the DEP requirements for connection to a water body of the State for the purpose of establishing DEP's dredge and fill permitting jurisdiction. Dr. Tobe replied to Ms. Owens that an underground pipe connection would satisfy DEP's jurisdictional requirements. On June 25, 2002, Dr. Tobe, Ms. Owens, and a DEP wetland delineation team visited the Lake Blake property for the purpose of making a jurisdictional determination. Maddan also accompanied Dr. Tobe and his team on the day of the site inspection. As a result of this inspection, Dr. Tobe completed and filed a Field Report for Lake Blake, Okaloosa County, dated June 25, 2002. As indicated in his Field Report, Dr. Tobe and his wetland delineation team determined that for jurisdictional purposes, Lake Blake was connected to the waters of the State by reason of the culvert on Lewis Street that ultimately discharges into Cinco Bayou. At the time of his inspection on June 22, 2002, Dr. Tobe did not observe water flowing from Lake Blake into the Lewis Street culvert. Dr. Tobe attributed this to abnormal drought conditions the area was then experiencing. Maddan, who has observed this area for many years, testified that the lake was near or slightly less than its normal water level on that date. Dr. Tobe conducted a further examination of the area to determine the ordinary high water line, and concluded that Lake Blake would at ordinary high water level flow into the Lewis Street culvert on a sufficiently regular frequency into Cinco Bayou, a water body of the State, in order to establish DEP's dredge and fill jurisdiction. In determining whether water exchange frequency is sufficient to establish jurisdiction, there is a DEP Interoffice Memorandum of October 31, 1988, setting out 25-year, 24-hour criteria which is used as guidance, but the criteria stated in this Memorandum have not been adopted as a rule, and are not singularly determinative of DEP's jurisdiction. At this time, Dr. Tobe and his team also performed a wetland boundary delineation. Dr. Tobe found hydric soils and wetland plants dominating the area. The wetland delineation boundary was determined by the continual interpretation of vegetation, soils, and hydrologic indicators. As a result of his inspection and wetland boundary delineation, Dr. Tobe concluded that unpermitted fill had been placed within the surface waters of the State, and in lacustrine wetlands.. Thereafter on July 18, 2002, DEP sent Maddan a Warning Letter (DF-SO-46-022) requesting that Maddan cease dredging, filling or construction activities at Lake Blake without obtaining a permit. Subsequent to DEP's sending Maddan the Warning Letter of July 18, 2002, Stacy Owens visited the Lake Blake site on numerous occasions beginning in October of 2002, and continuing through July of 2003. On most of these site visits Ms. Owens observed water flowing from Lake Blake through the Lewis Street culvert. Ms. Owens documented water flowing from Lake Blake through the Lewis Street culvert on October 29, 2002, November 5, 2002, May 20, 2003, June 20, 2003, June 23, 2003, June 27, 2003, and July 8, 2003. The area was not experiencing abnormally excessive rainfall events at the times that Ms. Owens documented water flowing from Lake Blake into the Lewis Street culvert. Maddan testified that in his personal observation over many years, Lake Blake generally discharges excess stormwater into the Lewis Street culvert only as a result from a significant rainfall event. Lake Blake discharges water into the Lewis Street culvert at regular intervals. The water discharged from Lake Blake ultimately is released through the Okaloosa County stormwater drainage system into the surface waters of Cinco Bayou, a water body of the State of Florida. The Okaloosa County stormwater drainage system connecting Lake Blake to Cinco Bayou is a series of excavated water bodies. Lake Blake is connected to the surface waters of Cinco Bayou, and regularly exchanges water with Cinco Bayou. Exemptions from DEP's Jurisdiction To assert dredge and fill permitting jurisdiction over this property, not only must Lake Blake be connected to the waters of the State, but the property must not be otherwise exempt from dredge and fill permitting jurisdiction under either statute or rule. On August 29, 2002, under the authority of the Corporation, Maddan filed a "Joint Application for Works in the Waters of Florida" with DEP requesting an exemption from DEP's dredge and fill permitting jurisdiction under Rule Chapter 17- 312, re-codified as Rule Chapter 62-312. Rule 62-312.050, Florida Administrative Code, sets out the recognized exemptions to DEP's dredge and fill permitting jurisdiction. Maddan primarily relies on Rule 62-312.050(4) which provides that "[n]o permit under this chapter shall be required for dredging or filling in waters which are contained in those artificially constructed stormwater treatment and conveyance systems designed solely for the purpose of stormwater treatment and that are regulated by the Department or the water management district." Lake Blake, however, is the result of excavations in a borrow pit. Because of surrounding development, Lake Blake receives stormwater runoff; however, the lake was not "designed solely for the purpose of stormwater treatment," and cannot therefore qualify for this exemption. Maddan also cites Rule 62-312.050(1)(g), Florida Administrative Code, which provides an exemption for the "construction of seawalls or riprap, including only that backfilling needed to level land behind the seawalls or riprap, in artificially created waterways where such construction will not violate existing water quality standards, impede navigation or adversely affect flood control." Even assuming that the filling of the finger of Lake Blake meets the test of construction of a seawall, there is no evidence that such filling of Lake Blake was ever subjected to appropriate water quality tests, much less meeting such water quality tests as well as the other requirements of this exemption. In addition to the exemptions established by Rule 62- 312.050, Maddan cites statutory exemptions. The definition of "waters" which are regulated under Chapter 403 as set forth in Section 403.031(13), provides in pertinent part that "[w]aters owned entirely by one person other than the state are included only in regard to possible discharge on other property or water." Although Lake Blake is owned entirely by one person, this provision does not exempt Lake Blake because the lake actually discharges on the surface waters of Cinco Bayou. Maddan also cites Section 403.812, which provides that "[t]he department shall not require dredge and fill permits for stormwater management systems where such systems are located landward of the point of connection to waters of the state and are designed, constructed operated and maintained for stormwater treatment, flood attenuation, or irrigation." Although Lake Blake has been utilized by Okaloosa County's stormwater drainage system which is located landward of Cinco Bayou, the lake was not designed nor constructed for stormwater treatment, flood attenuation or irrigation, and it is not being operated nor maintained for stormwater treatment, flood attenuation or irrigation. Lake Blake does not qualify for an exemption from DEP's dredge and fill permitting jurisdiction. Dredge and Fill Permit Denial On September 30, 2002, Maddan was notified of DEP's denial of his application to place a modular home on a fill pad in Lake Blake. Because Maddan took the position that DEP did not have dredge and fill jurisdiction over Lake Blake, or alternatively that Lake was exempt from DEP's jurisdiction, an analysis of whether Maddan's application might be approved under Rule 62- 312.060(5), Florida Administrative Code, has not been done. DEP has not performed any analysis of water quality standards nor public interest assessment required by the rule, and Maddan offered no evidence which would be necessary to make such determinations.

Recommendation Based upon the foregoing findings of fact and conclusions of law, it is recommended that a final order be entered upholding denial of Maddan's Permit Application No. 46-0199306- 001-EE. DONE AND ENTERED this 10th day of October, 2003, in Tallahassee, Leon County, Florida. S RICHARD A. HIXSON Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 10th day of October, 2003. COPIES FURNISHED: Charles T. Collette, Esquire Department of Environmental Protection The Douglas Building, Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 James E. Moore, Esquire Post Office Box 746 Niceville, Florida 32588 Robert W. Stills, Jr., Esquire Department of Environmental Protection The Douglas Building, Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 Teri L. Donaldson, General Counsel Department of Environmental Protection The Douglas Building, Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 Kathy C. Carter, Agency Clerk Department of Environmental Protection The Douglas Building, Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000

Florida Laws (7) 120.57373.4145373.4211403.031403.121403.812403.813
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RONALD E. DOWDY vs. DEPARTMENT OF ENVIRONMENTAL REGULATION, 79-000219 (1979)
Division of Administrative Hearings, Florida Number: 79-000219 Latest Update: Sep. 04, 1979

Findings Of Fact Based on the testimony of the witnesses and their demeanor while testifying, the documentary evidence introduced, the proposed findings of facts and recommended orders filed by the parties' counsel, and the arguments and citations of authority cited therein, the following relevant facts are found. 1/ This action concerns a parcel of land owned by Ronald E. Dowdy and his wife, Mary Ellen Dowdy, located at 7630 Lake Marsha Drive, Orlando, Florida. The Department does not claim, other than regulatory authority, ownership to the land in question. On March 15, 1978, Petitioner submitted to the Department a dredging and fill permit application, file No. 48-8093-4E., to deposit 200 cubic yards of fill material waterward of the line of ordinary high water, adjacent to Petitioner's upland property on Lake Marsha. The area proposed to be filled measured 150 feet along the shoreline, 55 feet between the line of ordinary high water and ordinary low water, and 12 inches deep. (Petitioner's Exhibit 2; D.E.R. Exhibit 9.) On June 15, 1978, the Department gave notice of its intent to deny Petitioner's permit application, stating with particularity the specific ground on which the denial was based and allowing Petitioner fourteen (14) days in which to petition for a hearing on the denial. Within thirty (30) days of the filing of the petitioner's application, he was advised that clearance and/or approval was necessary from the Department of Natural Resources. A Final Order denying application for permit was issued June 23, 1978. Petitioner did not file a petition pursuant to Chapter 120, Florida Statutes, seeking review of either the intent to deny letter or the Final Order until January 15, 1979. The Department waived the time requirement for filing the petition. On or about August 3, 1978, Petitioner caused to be deposited large quantities of fill in excess of the 200 cubic yards applied for along approximately 380 feet of shoreline between the line of ordinary high water and ordinary low water adjacent to his upland property. (Petitioner's Exhibit 2 and D.E.R. Exhibits 1 and 2.) Although Petitioner did not obtain a permit from the Department prior to commencement of the fill work described above, Orange County issued a permit (see Petitioner's Exhibit 2) which specified that the Department permit would have to be obtained prior to commencement of the fill work. The county permitted the Petitioner to fill an area along 150 feet of shoreline while the petitioner filled the entire length of the shoreline, i.e., 380 feet. As of the hearing date, Petitioner had not filed an application for a permit from either the county or the Department for the excess fill. Prior to the time that the Petitioner undertook the filling project, he met with employees of the Department who advised that a permit would be necessary prior to commencing the fill work. Department employees suggested that the State would look favorably on a reduced fill project of somewhere between 50 to 75 feet along the lake shoreline. (D.E.R. Exhibit 8.) The bulk of the fill area as completed, lies below the ordinary high water line of Lake Marsha, i.e., below the elevation line of 127 feet. (Petitioner's Exhibit 2.) Mr. Robert Day, a pollution control specialist employed by the Department as an enforcement investigator, observed the filling activity as it was taking place from the movement of fill by bulldozer to the sodding of the newly created fill area. (D.E.R. Exhibits 1 and 2.) Upon discovery of the Petitioner's filling activity without a permit, the Department attempted to notify him of the violation by means of a warning notice sent by U.S. Mail, certified, return receipt requested, which Petitioner did not claim. The Department thereafter sent Petitioner a telegram which resulted in a meeting in the Department's office in Orlando. (D.E.R. Exhibits 3, 4 and 5.) Richard Hoffman, district conservationist with the U.S. Department of Agriculture, Soil Conservation Service, was qualified as an expert in the collection and identification of soil core samples. Mr. Hoffman testified at length on a series of core samples taken on the Dowdy property confirming the fact that the Petitioner had placed fill on vegetated muck and that all but one of the core samples were below the high water line. (Petitioner's Exhibit 2 and D.E.R. Exhibit 7.) James Morgan, an environmental specialist of the Department, was qualified as an expert witness in the processing and appraisal of dredge and fill permit applications and their impact on water quality and wetlands ecology. Mr. Morgan advised the Petitioner on February 14, 1978, several months before the actual filling activity, that it was necessary to obtain a permit from the Department pursuant to Chapter 17-4, Florida Administrative Cede. Again, on March 16, 1978, at a meeting with Petitioner, Mr. Morgan advised the Petitioner of the necessity to obtain a permit before any filling was done. Additionally, he advised and suggested to Petitioner that with respect to his proposed activity, the Department would look favorably upon a modified application requiring a fill area of 50 to 75 feet of the lake's shoreline. Upon receipt of Petitioner's application, Mr. Morgan conducted a permit application appraisal (D.E.R. Exhibit 9) and found that the area proposed to be filled contained deep muck deposits and was dominated by the vegetation, maidencane, with a lesser abundance of arrowhead, pickeral weed and pennywort. The dominant species was maidencane, which along with arrowhead and pickeral weed, are species found in the vegetative index for submerged lands as set forth in Section 17-4.02(17), Florida Administrative Code. (See D.E.R. Exhibits 9 and 10.) Approximately 50 percent of the shoreline of Lake Marsha has been developed with the consequent elimination of marsh and wetland vegetation fringes of the lake. The aquatic vegetation found on the Dowdy property prior to filling performed functions of assimilating nutrients and filling deleterious substances from the waters of Lake Marsha and provided wildlife habitat. This assimilation process enabled and assisted the shoreline plants ability to absorb water containing dissolved pollutant substances which are utilized for plant food. The aquatic vegetation also filters suspended solids from the lake water. This assimilation and filtration process helps preserve water quality in a fresh water lake by both filtering runoff from the upland and cleansing the water of substances found in the water body itself. (D.E.R. Exhibit 9.) This process is commonly referred to as the "kidney effect". The fill which has been placed in the submerged land aquatic community will, as testified by the Department's witnesses, totally eliminate portions of the kidney of Lake Marsha and has been replaced with sod which carries the potential for causing further pollution of the waters of Lake Marsha. Testimony reveals that the fill will increase the nutrient load in the lake and dramatically decrease its ability to cope with the increased load. It is predicted by the Department's witnesses that the impact of the fill on the water quality of the lake will be significant as a substantial portion of the lake's littoral zone has been substantially eliminated. This, according to witness Morgan, can lead to the eutrophication of Lake Marsha end a resultant lower equilibrium based on poor water quality. (D.E.R. Exhibit 11.) According to Morgan, the parameters which are expected to be violated by the fill and the resultant elimination of a submerged land aquatic plant community include phosphorous and nitrogen which are classified as nutrients under Section 17-3.061(2)(i), Florida Administrative Code, and turbidity, under Section 17-3.061(2)(g) Florida Administrative Code. (D.E.R. Exhibit 9, part 2.) Testimony reveals that a correlation exists between the degree of shoreline development of Central Florida lakes and the water quality of such lakes. This correlation is direct and reveals that the greater the degree of shoreline development, the greater the reduction of the lake's ability to compensate for nutrient load going into the lake and, thus, lower water quality. (Testimony of Morgan and Hulbert, T.R. pp 138-139; 177-180.) Witness Morgan testified that by restoration of the Petitioner's fill site to its original contours and elevation, the aquatic vegetation which once thrived on the site will reestablish itself and the consequent restoration of the lake's "kidney effect". James Hulbert, a Department District Biologist qualified as an expert in the area of water pollution biology and wetlands ecology, confirmed witness Morgan's testimony regarding the impact of water quality based on Petitioner's filling, the value of the wetland vegetational community which was, according to him, destroyed by the filling, including protection of uplands and its role as a source of food and shelter for the lake's aquatic life. Witness Hulbert also confirmed the testimony of witness Morgan to the effect that a direct correlation exists between the degree of shoreline development in central Florida lakes and the lowering of water quality in such lakes. Witness Hulbert testified further that submerged lands such as the ones filled by Petitioner assimilate nutrients for preserving fisheries of fresh water lakes. Mr. Hulbert also testified that dissolved oxygen levels are expected to be degraded with severe fluctuations which would result in the dissolved oxygen levels of as low as 0.0, below the standards of Chapter 17-3, Florida Administrative Code. This increased nutrient load will, according to Mr. Hulbert, result in proliferation of such existing exotic plant species such as hydrilla and water hyacinths, and an acceleration of the lake's eutrophication. Mr. Hulbert summarized the long- range impact of the fill as both measurable and substantial and concluded that the degradation process will be steady and gradual. Robert Bell, a real estate appraiser licensed in the State of Florida as a broker, indicates that there are other valuable uses of Petitioner's property other than filling the entire shoreline. Such uses, according to Bell, include the construction of a boardwalk, a deck, gazebo, a boat house, and even partial filling of the shoreline area for access to the water. The Department incurred expenses and costs in preparation of this proceeding for purposes of tracing, controlling, and abating the pollution sources created by the Petitioner's dredge and fill activities in the amount of $201.88. (D.E.R. Exhibits 14 and 15.)

Recommendation Based on the foregoing findings of fact and conclusions of law, it is hereby

Florida Laws (5) 120.57403.031403.121403.141403.161
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THOMAS A. DRISCOLL vs SOUTHWEST FLORIDA WATER MANAGEMENT DISTRICT, ENGLE HOMES AND LAKE BERNADETTE, INC., 01-002471 (2001)
Division of Administrative Hearings, Florida Filed:Tampa, Florida Jun. 25, 2001 Number: 01-002471 Latest Update: Dec. 03, 2001

The Issue The ultimate legal and factual issue in this matter is whether Engle Homes, Inc., and Lake Bernadette, Inc. (Permittees), have provided the Southwest Florida Water Management District (District) with reasonable assurances that the activities they propose to conduct pursuant to Management and Storage of Surface Water (MSSW) General Construction Permit No. 49005837.017 (the Permit) meet the conditions for issuance of permits established in Rules 40D-4.301, 40D-4.302, and 40D- 40.302, Florida Administrative Code. In particular, the issues of fact to be litigated are whether the Project will cause adverse water quality impacts to receiving waters and adjacent lands; whether the Project will cause adverse flooding of on-site or off-site property; whether the Project will cause impacts to existing surface water storage and conveyance capabilities; and whether the Project will adversely affect the property of others.

Findings Of Fact The Parties Engle Homes, Inc., and Lake Bernadette, Inc., are corporations licensed to operate in the State of Florida. The District is the administrative agency charged with the responsibility to conserve, protect, manage, and control water resources within its boundaries pursuant to Chapter 373, Florida Statutes, and the rules promulgated thereunder as Chapter 40D, Florida Administrative Code. Driscoll resides at 35716 Welby Court, Zephyrhills, Florida 33541, Lot 14, within the Timber Creek 2 Subdivision (Subdivision). Driscoll requested this hearing to show the District that there is a drainage problem on Lots 13 and 14, and the adjacent Geiger property to the south, which should be fixed at this time and as part of the Project. Driscoll wants "Engle Homes to propose a new solution to fix the entire Welby Court Geiger property problem," i.e., from Lots 4 through 14, and not a piecemeal solution as proposed in the Permit modification. The Subdivision Engle Homes, Inc., and Lake Bernadette, Inc., developed the Timber Creek 2 Subdivision. Lots 15 through 25 run east to west and are north of Welby Court. Lots 15 and 16 are located north of the cul-de-sac, on the eastern portion of Welby Court. Lots 3 through 14 run west to east, south of Welby Court. Lots 13 and 14 are south of the cul-de-sac on the eastern portion of Welby Court and are across the street and the cul-de-sac from Lots 16 and 15, respectively. Residences exist on Lots 5, and 7 through 14. Driscoll owns Lot 14, a corner lot, which is the southeastern most lot of the Subdivision. Don Geiger (Geiger) owns the land (approximately five acres) south of the property lines of Subdivision Lots 5 through Geiger's northern driveway, essentially a dirt road, runs parallel to Lots 5 through 14. Subsequent to the original construction activity involving the Subdivision, the developer realized that there was an "existing depression" (referenced on Engle Exhibit number 1), south of Lots 7 and 8, and on Geiger's property. Geiger complained to the District about standing water in this area. This depression area is approximately 90 feet long and 30 feet wide which needed to be "drained off" according to Geiger. The depressed area on Geiger's property was most likely caused when Lots 7 through 14 were graded and sodded, which raised the "lots up a few inches" above Geiger's driveway/property. Water is trapped during a storm event between the back yards and the depressed area. As a result, the southern end of the back yards, particularly Lots 7 and 8, and the driveway remain constantly wet. The Project On January 16, 2001, Engle Homes, Inc., and Lake Bernadette, Inc., filed MSSW Permit Application No. 49005837.017 with the District, to address the problems with the rear lot grading and the adjacent property. The actual Project area for the permit modification1 includes the southern portions of Lots 4 through 9 and south of the property lot line including Geiger's property. See Finding of Fact 5. The modified permit does not address the drainage area including the back yards of Lot 13 and Driscoll's Lot 14, and the other portion of Geiger's property/driveway to the south. On April 5, 2001, the District issued MSSW Permit No. 49005837.017 to Engle Homes, Inc., and Lake Bernadette, Inc., under the provisions of Chapter 373, Florida Statutes, and Chapter 40D-40, Florida Administrative Code, for the modification of a surface water management system to serve the Project area. The proposed Project will involve the construction of a concrete inlet box with a safety grate, storm sewers, and grass swales. Specifically, the project is intended to solve the drainage problems associated with the "existing depression" south of the boundary line for Lots 7 and 8 on Geiger's property (although Lots 4 through 9 ("area 1") are included within the Project area), and the back yards of Lots 7 and 8. A catch basin is proposed to be located south and on the lot line between Lots 8 and 9, which is expected to drain off the water in the depression area to the modified surface water management system. The inlet box will be placed in the corner between Lots 8 and 9. The collected water in the inlet box will be routed underground through a series of 18-inch storm sewer pipe straight north through a drainage easement between Lots 8 and 9 to Welby Court. The underground pipe ties into an existing pipe in front of Lot 9 on the street, then runs east along the Welby Court right-of-way and then north between Lots 19 and 20, and eventually north into a large permitted retention pond, located to the north of the Subdivision which will handle the stormwater. Driscoll's Alleged Drainage Problem There is another distinct drainage area, i.e., "area 2," which includes Geiger's property and the southern portions of Lots 13 and 14, where water drains from south to north into a roadside ditch to Geiger Cemetery Road ("area 3"), which runs south to north and east of Lots 14 and 15. During a September 2001 tropical storm, there was standing water on Geiger's driveway, directly south of Lots 13 and 14, which was present for more than 3 days. This was referred to by Mr. Barrett as a "small drainage problem that could easily be corrected." On the other hand, Geiger says that there is standing water on his driveway, south of Lots 13 and 14, "all the time." This caused Geiger to move his driveway "50 or 60 feet" south. According to Geiger, the berm, which runs across Lots 10 through 14, should be lowered and the backyards reconfigured. But this would be quite disturbing to the neighbors. Therefore, Geiger recommends the placement of drains south of Lots 13 and 14, which would direct the water out to the ditch at Geiger Cemetery Road and away from Driscoll's Lot 14. The modified Permit is not intended to solve this problem, although Driscoll wants this problem fixed. It is not necessary to resolve Driscoll's issue regarding whether there is a drainage problem in and around Driscoll's lot. The two drainage areas 1 and 2 discussed herein are not connected, although they are close in proximity. The solution to the first problem has no impact on the second, and there is no cited statutory or rule requirement that both issues must be addressed in this Permit application. This is Driscoll's quandary. Compliance with Rules 40D-4.301 and 40D-4.302, Florida Administrative Code The Project will not impact wetlands or surface waters. The Project will not adversely impact the value of functions provided to fish and wildlife, and listed species, including aquatic and wetland-dependent species, by wetlands or other surface waters and other water-related resources. The Project will not adversely impact the quality of receiving waters such that the water quality standards will be violated. The Project will not cause adverse secondary impacts to the water resources. The Project will not adversely impact the maintenance of surface or groundwater levels or surface water flows established pursuant to Section 373.042, Florida Statutes. The Project will not cause adverse impacts to a work of the District. The Project is capable, based on generally accepted engineering and scientific principles, of being effectively performed and of functioning as proposed. The Project will be conducted by an entity with financial, legal, and administrative capability of ensuring that the activity will be undertaken in accordance with the terms and conditions of the permit, if issued. The Project will comply with any applicable special basin or geographic area criteria established pursuant to Chapter 40D, Florida Administrative Code, by the District. The Project will not adversely affect the public health, safety, or welfare. The Project will not adversely impact the conservation of fish and wildlife, including endangered or threatened species, or their habitats. The Project will not adversely affect navigation. The Project will not cause harmful erosion or shoaling. The Project will not adversely affect fishing or recreational values or marine productivity in the vicinity of the Project. The Project will not adversely affect significant historical and archeological resources. The Project will not cause unacceptable cumulative impacts upon wetlands and other surface waters. The Project area is less than 100 acres. The Project does not require dredging or filling of wetlands, or construction of boat slips. The Project is not contrary to the public interest. The Project will not cause adverse water quantity impacts to receiving waters and adjacent lands, and will not adversely affect or impact the property of others, including Driscoll's property, Lot 14. "Area 1," between Lots 4 and 9, is a separate drainage area, and the water from this area does not drain to Lot 14. Driscoll's property is not within the Project area, and the Project was not intended to resolve his alleged drainage problem. The Project will not cause adverse flooding to on-site or off-site property. The Project will not cause adverse impacts to existing surface water storage and conveyance capabilities. Rather, the project is expected to improve the conveyance of water and drainage for "area 1" and the Project area.

Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Southwest Florida Water Management District enter a final order issuing Management and Storage of Surface Water General Construction Permit No. 49005837.017. DONE AND ENTERED this 24th day of October, 2001, in Tallahassee, Leon County, Florida. CHARLES A. STAMPELOS Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 24th day of October, 2001.

Florida Laws (2) 120.569373.042
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CAHILL PINES AND PALMS PROPERTY OWNERS ASSOCIATION, INC. vs DEPARTMENT OF ENVIRONMENTAL PROTECTION, 95-004377 (1995)
Division of Administrative Hearings, Florida Filed:Key West, Florida Aug. 31, 1995 Number: 95-004377 Latest Update: Jan. 29, 1997

Findings Of Fact On July 19, 1991, the Petitioner, Cahill Pines and Palm Property Owners Association, Inc. (Cahill), filed a permit application with the Department of Environmental Resources, predecessor to the Respondent, Department of Environmental Protection (Department), for a permit to remove two earthen plugs in the Cahill canal system, located in Big Pine Key, Monroe County, Florida. The plugs were to be removed to a depth of -5.5 feet N.G.V.D. Kenneth Echternacht, a hydrologist employed by the Department, had performed a hydrographic review of the proposed project and reduced his findings to writing in a memorandum dated June 25, 1993. Mr. Echternacht recommended that the project not be permitted. On August 20, 1993, the Department issued a notice of its intent to deny Cahill's application to remove the plugs. The notice included six proposed changes to the project which would make the project permittable. Cahill requested an administrative hearing on the Department's intent to deny the permit. On March 3 and 4, 1994, an administrative hearing was held on the issue of whether a permit should be issued. The hearing officer entered a recommended order on May 9, 1994, recommending that a final order be entered denying the permit. The Department issued a final order on June 8, 1994, adopting the recommended order of the hearing officer and denying the permit. See Cahill Pines and Palm Property Owners Association v. Department of Environmental Protection, 16 F.A.L.R. 2569 (DER June 8, 1994). In the final order the Department found that the following findings of Mr. Echternacht were "scientifically sound and credible conclusions": The estimated flushing for the presently open portion of the waterway was calculated to be 14.5 days. The flushing for the open section exceeds the 4 day flushing criterion by approx- imately 3.6 times. Clearly, the open portion poses a potential problem to the maintenance of acceptable water quality. For the presently closed sections of the waterway, the calculated flushing time was found to be 38.6 days. Again, this system would pose a significant potential for contamination to adjacent open waters if opened for use. The waters behind the barrier that presently appear to pose no problem would clearly become a repository for contaminants associated with boat usage. Because of the exceptionally long flushing time, contaminants would build up over time. Below standard water quality throughout the waterway would be expected and, associated with this, below standard water would be exported into adjacent clean water on each ebbing tide. The final order also found the following facts: 13. Neither the water in the open canals nor the water in the closed canals is presently of substandard quality. * * * Petitioner's plug removal project will also spur development in the Cahill subdivision and lead to an increase in boat traffic in the Cahill canal system, as well as in the adjacent waters of Pine Channel. Such activity will result in the discharge of additional contaminants in these waterways. As Echternacht stated in his June 25, 1993, memorandum that he sent to O'Connell, '[b]ecause of the [canal system's] exceptionally long flushing time, [these] contaminants would build up over time' and result in a significant degradation of the water quality of not only the Cahill canals, but also of Pine Channel, into which Cahill canals flow. This degradation of water quality will have an adverse effect on marine productivity and the conservation of fish and wildlife that now inhabit these waterways. Consequently, in the long run, the removal of the plugs will negatively impact fishing opportunities in the area. On the other hand, the project will have a beneficial effect on navigation and recreational boating and related activities. It will have no impact on historical and archaeological resources. On April 10, 1995, Cahill submitted a permit application to the Department to remove portions of the two canal plugs. Cahill proposed to leave an island in the center of each plug. The islands would be stabilized with riprap, and mangrove seedlings would be planted in the riprap. By letter dated April 21, 1995, the Department returned the April 10 permit application to Cahill along with the $500.00 processing fee. The Department advised Cahill that the application was not substantially different from the 1991 permit application which was denied by final order. The Department further advised that Cahill could resubmit the application and application fee if it wanted the permit to be processed but the Department would deny the application on the basis of res judicata. On May 17, 1995, Cahill submitted a revised permit application along with the processing fee. A circulation culvert had been added to the project. Ken Echternacht performed a hydrographic review of the proposed project. In a memorandum dated May 25, 1995, Mr. Echternacht recommended that the permit be denied for the following reasons: The proposed 24-inch culvert connection would not be expected to be visible hydraulically. A 24-inch diameter culvert, length 181 ft would be expected to have a friction factor several orders of magnitude greater than the adjacent canals. As such, water would not be expected to pass through the connector unless there were a sizeable head to drive the flow. No studies and/or supporting documentation have been provided to support the design in terms of the documenting the amplitude and repeatability of the flow driving force. Cutting holes through embankments do not necessarily result in flushing relief. As stated in 1, above, any and all proposed design modifications to the proposed waterway must be accompanied by adequate design justifi- cation based on hydrographic modeling supported by site specific data support. The culvert design proposed does not meet the above require- ment. The proposal is nothing new. In the hearing, ideas such as the above were suggested. However, as was stated in the hearing any and all such proposals must be supported by proper engineering study. On July 7, 1995, the Department issued a Notice of Permit Denial, denying the May, 1995 permit application on the basis of res judicata, stating that the May 1995 permit was not substantially different from the 1991 permit application which had been denied and that no studies had been submitted by Cahill that would support that the use of the islands and culvert would increase the flushing rate to the four day flushing criterion established in the hearing on the 1991 permit application. At the final hearing counsel for Cahill stated for the record that the use of the islands and the culvert would not increase the flushing rate to four days.

Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that a Final Order be entered denying Cahill Pines and Palms Property Owners Association, Inc.'s application for a permit to remove two plugs separating the open and closed canal sections of the Cahill canal system, placing an island in the center of each plug, and adding a 24 inch culvert connection. DONE AND ENTERED this 31st day of July, 1996, in Tallahassee, Leon County, Florida. SUSAN B. KIRKLAND 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 31st day of July, 1996. APPENDIX TO RECOMMENDED ORDER, CASE NO. 95-4377 To comply with the requirements of Section 120.59(2), Florida Statutes (1995), the following rulings are made on the parties' proposed findings of fact: Petitioner's Proposed Findings of Fact. Paragraphs 1-7: Accepted in substance but not necessary to be incorporated in the recommended order. Paragraph 8: The evidence presented showed that there is a dispute of whether the waters are now of substandard quality. For the purposes of this hearing, it is not necessary to determine whether the water quality is presently substandard. Based on the assumption that the water quality is not substandard, Petitioner has failed to show that the change in the design of the project is sufficient to warrant the rejection of the applicability of the doctrine of res judicata. Petitioner has failed to show that the addition of islands and a culvert will eliminate the potential for future contamination of the waters. The second sentence is accepted in substance but not necessary to be incorporated in the recommended order. Paragraphs 9-11: Accepted in substance but not necessary to be incorporated in the recommended order. Paragraphs 12-15: Accepted in substance to the extent that for the purposes of this hearing the water quality is assumed not to be substandard. Paragraph 16: Rejected as unnecessary. Paragraphs 17-27: Rejected as subordinate to the finding that for the purposes of this hearing the present water quality is assumed not to be substandard. Paragraphs 28-30: Accepted in substance. Paragraph 31: Accepted in substance to the extent that the changes in the design will not increase the flushing rate to four days. Paragraphs 32-33: Accepted to the extent that they were findings in the final order on the 1991 application. Paragraphs 34-35: Accepted to the extent that the slow flushing rate is one of the criteria to be considered. The increase of development and boat traffic are also contributors to the potential of contamination building up. Petitioner has not demonstrated that the use of islands and a culvert will eliminate the potential for contamination. Respondent's Proposed Findings of Fact. Paragraphs 1-10: Accepted in substance. Paragraphs 11-14: Rejected as unnecessary. Paragraph 15: Accepted in substance. Paragraph 16: Accepted in substance as corrected. Paragraph 17: Accepted. Paragraphs 18-21: Accepted in substance. Paragraph 22: Accepted. Paragraph 23: Rejected as unnecessary. COPIES FURNISHED: David Paul Horan, Esquire Horan, Horan and Esquinaldo 608 Whitehead Street Key West, Florida 33040-6549 Christine C. Stretesky, Esquire John L. Chaves, Esquire Department of Environmental Protection 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 Kenneth J. Plante, General Counsel Department of Environmental Protection 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 Virginia B. Wetherell, Secretary Department of Environmental Protection 3900 Commonwealth Boulevard, Douglas Building Tallahassee, Florida 32399-3000

Florida Laws (1) 120.57
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BERNARD M. CAMPBELL AND BESSIE H. CAMPBELL vs SOUTHERN HY POWER CORPORATION AND DEPARTMENT OF ENVIRONMENTAL PROTECTION, 99-000307 (1999)
Division of Administrative Hearings, Florida Filed:Inglis, Florida Jan. 22, 1999 Number: 99-000307 Latest Update: May 17, 2000

The Issue Whether Southern Hy Power Corporation (Hy Power) has provided reasonable assurance, based on plans, test results, or other information, that its proposed hydroelectric facility will comply with the Management and Storage of Surface Water (MSSW) statutes and rules of Southwest Florida Water Management District (SWFWMD) and the Wetland Resource Management permit (WRM)/water quality certification statutes and rules of the Florida Department of Environmental Protection (DEP).

Findings Of Fact By Joint Prehearing Stipulation the parties agreed to the following description of the parties and the project: PARTIES: The Department of Environmental Protection (the Department) is a government agency in the State of Florida existing by virtue of Section 20.255, Florida Statutes, and operating pursuant to Chapters 253, 373, 376, and 403, Florida Statutes, and Title 62, Florida Administrative Code. Under an interagency agreement with SWFWMD, the Department also implements Title 40D, Florida Administrative Code. The Department is located in Tallahassee, Florida, and it has a district office in Tampa, Florida, which district includes Levy County. Southern Hy Power Corporation is a Florida Corporation whose principal offices are located at 7008 Southwest 30th Way in Gainesville, Florida. Betty Berger is an interested party with a mailing address of Post Office Box 83, Inglis, Florida. The Campbells are an interested party with a mailing address of 245 Palm Street, Inglis, Florida. Hy Power applied on August 31, 1993, to the Department for a WRM permit/water quality certification to construct a hydroelectric facility on the Inglis By-Pass Channel. The project is located in Section 12, Township 17 South, Range 16 East, within the town of Inglis in Levy County. The facility consists of a powerhouse located on the south side of the channel measuring about 28 feet wide by 115 feet long, drawing water from the Inglis By-Pass Channel, passing it through a single-pit type turbine and discharging downstream of the Inglis By-Pass Spillway Dam. Hy Power applied on August 4, 1998, to the Department for a MSSW permit for the same proposed hydroelectric facility on the Inglis By-Pass Channel. DESCRIPTION OF PROPOSED PROJECT The project involves the construction of an intake structure, powerhouse, and tailrace on a 0.61-acre area located on the south side of the existing Inglis By-Pass Spillway. The facility will take advantage of the existing hydrostatic head that exists on either side of the Spillway Dam, to generate electricity. The powerhouse will be constructed below grade and will contain a single megawatt turbine and generating unit. The intake structure will divert flows from the upstream side of the Spillway Dam through the powerhouse and back into the By-Pass Channel. A small one-story control building and low profile substation will be constructed above grade within the boundaries of the project area. The hydroelectric project is considered to be a "Run of the River" type of facility because it can only use that water which flows down the existing channel. The geometry of the channel restricts flow to a certain amount, therefore the project cannot create or use flows above those that the By-Pass Channel can provide. The overall authority for control of water levels in Lake Rousseau and flow to the lower Withlacoochee River will remain with the DEP. Lake Rousseau was created in 1909 when the Inglis Dam was constructed across the Withlachoochee River for the purposes of hydroelectric generation. The dam impounds over 11 miles of the Withlachoochee River and forms a lake approximately 3,000 to 4,000 acres in size. Prior to construction of the Barge Canal, water released from the Inglis Dam would flow down the lower portion of the Withlachoochee River about 10 miles before entering into the Gulf of Mexico. In the mid to late 1960's the Army Corps of Engineers (ACOE) built a portion of the Cross Florida Barge Canal between the Gulf of Mexico and Lake Rousseau. The canal severed the Withlachoochee River downstream of the Inglis Dam causing its flow to be diverted into the Barge Canal and then into the Gulf. In order to maintain the flow of freshwater from Lake Rousseau to the lower segment of the River, the 8,900-foot long Inglis By- Pass Channel and Spillway were constructed. The resulting downstream flow ensures navigation in the lower portion of the River and sustains its freshwater and estuarine environment. The water level in Lake Rousseau is generally maintained at an elevation of 27.5 feet above mean sea level (msl) by a combination of the Inglis Dam, the Inglis Lock, which is located in the Barge Canal, and the By-Pass Channel Spillway. These water control features are known collectively as the Inglis Project Works. The water levels in the lower Withlachoochee River immediately to the west of the By-Pass spillway are close to sea level. The resulting head provides the potential energy needed to drive the proposed generator turbine. Under normal conditions the majority of water released from Lake Rousseau flows over the Spillway Dam into the lower segment of the River. According to the DEP Office of Greenways and Trails (OGT), the maximum capacity of the existing By-Pass Channel Spillway is 1,540 cubic feet per second. The hydroelectric project will divert whatever flow is allowed around the existing spillway through the turbine and back into the channel. When the Cross Florida Barge Canal project was cancelled in the 1990's, the ACOE transferred ownership of the property to the State of Florida Board of Trustees, who in turn has leased the property to the DEP for use as the Cross Florida Greenbelt State Recreation and Conservation Area. Management of this property, the control of river flow and lake levels, and operation of the Inglis Project Works are exercised by the DEP's OGT. The OGT utilizes a document entitled "Water Control Plan for Inglis Project Works," dated September 1994, as a guide to operating the structures. The Water Control Plan is incorporated as part of the MSSW intent to issue. On or about April 25, 1995, the Governor and Cabinet, sitting as the Board of Trustees of the Internal Improvement Trust Fund ("Trustees"), approved a request from Hy Power to sublease 0.61 acres of Greenway property at the project site for the purpose of providing electric power. The request was challenged by Berger and the Campbells, and resulted in an administrative hearing held on November 3, 1995. As a result of the hearing, Administrative Law Judge Larry Sartin entered a Recommended Order on July 12, 1996, that the Board enter an order approving execution by the DEP of the proposed sublease and dismissing the petition of Berger and the Campbells. The Recommended Order was approved by the Trustees in its entirety in a Final Order dated April 12, 1996 ("Final Order"). Berger v. Southern Hy Power Corporation et al., Case No. 95-3589. A copy of the Final Order is listed as an exhibit to this Stipulation, and the Findings of Fact and Conclusions of Law contained therein are adopted herein. As previously ruled by the undersigned, the previous Final Order is res judicata as to Petitioners in this case, who are collaterally estopped from challenging any of the findings of fact or conclusions of law contained in the previous Final Order. Petitioners reserve the right to litigate issues of fact and law not addressed in the Findings of Fact or Conclusions of Law contained in that Final Order with regard to the permittability of this project under the WRM and MSSW permitting proposals, and to raise objections as to relevance to this proceedings of any of the Findings of Fact or Conclusions of Law in the Final Order. On February 21, 1995, Hy Power filed application with the Federal Energy Regulatory Commission (FERC) for a conduit exemption from the licensing requirements of Part I of the Federal Powers Act (FPA) for the proposed project. Petitioners and various other persons filed protests with FERC in opposition to the project. On April 21, 1997, FERC issued an Order Granting Conduit Exemption, a copy of which is listed as an exhibit to this Stipulation. Petitioners in this case are collaterally estopped from challenging any of the findings or conclusions contained in that Order Granting Conduit Exemption. Petitioners reserve the right to litigate issues of fact and law not addressed in the Findings of Fact or Conclusions of Law contained in that Order Granting Conduit Exemption with regard to the permittability of this project under the WRM and MSSW permitting proposals, and to raise objections as to relevance to this proceedings of any of the findings or conclusions in the Order Granting Conduit Exemption. FACTS ADDUCED AT HEARING OUTLINE OF PROJECT The proposed project calls for the construction of a water retention structure along the existing By-Pass spillway, the excavation of a large hole in which the powerhouse and turbine would be constructed "in-the-dry" south of the existing dam, and a millrace below the proposed project to return the water back into the existing water course. Conflicting testimony was received regarding the facts surrounding the construction of the project. These included: whether the proposed project will touch the existing wing walls of the existing dam; whether the water retention structure is a coffer dam; whether the proposed water retention structure will safely retain the water; whether the powerhouse and turbine have sufficient negative buoyancy to stay in the ground; whether the proposed excavation will weaken the existing dam; and whether the de-watering of the excavation site will adversely impact ground and surface water. PROJECT DESIGN AND ENGINEERING Engineering for the project was directed by witness Richard A. Volkin, a professional engineer and president and CEO of Engineering Company, Inc., based in Canton, Massachusetts. Mr. Volkin has extensive national and international experience in the design, management, and operation of hydroelectric facilities. Other engineers in Mr. Volkin’s firm worked on the project under Mr. Volkin’s direct supervision, including John May, who became registered as a professional engineer in Florida in order to sign and seal the engineering drawings for the project, which he initially did around 1994. Mr. May became ill and retired in 1998. Because of the length of time the application process has taken and the fact that Mr. May retired, there was a time while the application was pending, when Hy Power's design team was without a registered Florida engineer. When this was brought to the attention of Hy Power, Hy Power substituted Steven Crockett for Mr. May as the Florida-registered professional engineer of record for the project. DEP routinely accepts an applicant’s changing its engineer of record during the course of permit application or construction. Mr. Crockett is a civil and structural engineer who has considerable experience in preparing dam structural designs. Mr. Crockett independently reviewed and evaluated the engineering drawings for the project. Mr. Crockett resealed the drawings by using his drawn seal and signing the plans because his embossed seal was not readily available and time was of the essence. Mr. Crockett has advised DEP that he is now engineer of record for the project, using the appropriate DEP forms. Mr. Volkin’s firm performed all of the studies required by the various agencies, including a geotechnical study of the area, a 50-year analysis of water flow in and out of the Lake Rousseau regime, and water quality evaluations of water in the By-Pass Channel. The ACOE performed deep hole borings of the soils (approximately 36-40 feet below sea level) in the area of the project site to determine soil stabilization conditions at the site when they were constructing the Inglis Project Works. The soil conditions found can reasonably be expected to be similar today. Mr. Volkin’s company also took its own eight-foot deep surface core samples. The purpose of those samples was to verify the ACOE data. The new core samples verified the original core samples. Mr. Volkin also reviewed the ACOE’s engineering drawings developed from construction of the Spillway Dam. These show that the dam is founded on limestone bedding that has been stabilized with concrete. The hydroelectric facility will be constructed adjacent to and south of the dam structure and adjacent to and north of the barge canal. The same type of limestone bedrock is found in the area of the proposed construction. The facility design includes an intake channel on the upstream channel and a tailrace downstream. Those are the only structures that will be constructed next to the By-Pass Channel. The construction of the facility itself will be "in the dry." Hy Power will use coffer dams to seal off the construction site from the By-Pass Channel, so that there will not be water leakage from the Channel into the construction site. Water from the By-Pass Channel will enter the power plant when the coffer dams are lifted and the water is allowed to flow into the facility. The Petitioners presented the testimony of Bill Edwards, an individual with considerable experience in the construction of bridges, cofferdams, and similar concrete structures in aquatic and semi-aquatic conditions. Mr. Edwards is a former hard-hat diver who worked all over the world and worked in Florida for many years prior to his retirement. Based upon his experience and expertise in construction related to projects of this type, his testimony is credible and worthy of consideration. Mr. Edwards pointed out that if the proposed water retention structure did not touch the wing wall of the existing dam, it could not keep the water out and would not have the strength that it needed to retain the water. Hy Power’s witnesses explained that the retention structure would be set close enough to the existing wing wall that waterproofing materials could be placed between the two structures to keep the water out. Further, that the existing plans did not show interior bracing which would be included for structural strength and integrity. In sum, the retention structure will be in contact with existing dam’s wing wall, but will be free standing and not dependent upon the strength of the wing wall for its strength. Mr. Edwards pointed out that a cofferdam by definition has walls on all sides of the structure. The structure proposed by Hy Power did not have walls all the way around the proposed excavation. In rebuttal, Hy Power presented evidence that its plans were conceptual, design drawing and not construction plans. Hy Power represented that in actuality it would put as many walls as were necessary to keep the water out of the hole it intended to excavate. Trash racks will be constructed at the intake structures to protect aquatic life and make sure that trash and vegetation do not enter the intake structure or go down river. The trash rack bars will be two inches on center, which the U.S. Fish and Wildlife Service has determined as the appropriate size for the protection of fish. The turbine blades are "double regulated," and operate generally between 60 and 90 revolutions per minute. The design enables the turbine to operate at a constant speed to generate a consistent flow of electricity, notwithstanding the fact that the flow of the water may vary. The blade speed is not very fast, and the 2.5-meter blades provide a two to three-foot opening. This design acts to prevent fish mortality. There are four ways to shut off the flow of water through the proposed structure: close the pitch of the blades, close the wicket gates, allow the counter balance to the wicket gates to kick in and automatically close the gates, and close off the main gates. This is a fail safe system ("four level redundancy") designed to work upon any failure. Once water goes through the generator, its velocity is reduced to no greater than its intake rate which is a maximum of three feet per second. This prevents the water being discharged from the tailrace from causing erosion. If the head of water in the dam produces a flow exceeding three feet per second, it can be diverted over the other dams which will be functional. The power plant will be encased in concrete, except for a small access way that enables a person to go down a set of stairs to the plant. It will be a sealed, waterproof structure, as required by FERC and the ACOE. This will prevent penetration of groundwater, or flood waters in the event a massive flood overtops the plant. The only water entering the powerhouse will be through the turbine tunnel for power generation purposes. Mr. Edwards pointed out that the powerhouse was a closed structure and as such would have positive buoyancy, that is, it would float. Mr. Edwards pointed out that the proposed site is between the barge canal and By-Pass spillway and there is a great deal of groundwater and potentiometric pressure in the existing water table. In sum, there is a unlimited supply of groundwater at the site, and powerhouse could float out of the ground just like an empty swimming pool. Hy Power presented rebuttal evidence that the weight of the building, the turbine, and the water flowing through the turbine would be close to negative buoyancy, and they would add additional weight to the structure as necessary to keep it in place. The project is designed to generate three megawatts of electric power which is enough electricity to serve between 300 and 3000 homes, depending on usage. The project is designed to be unmanned. This is common for facilities such as this. The plant can be operated by remote control, unlike the existing controls at the By-Pass Dam, which are operated manually. DEP can access, monitor, and control remotely the generator's operation to include shutting the facility down at any time. There will be remote sensors to monitor water elevations. Flood protection will improve because of the ability of DEP to manage water flow from a remote location. If there is any major disruption, the plant will shut itself down. The project is classified as "green power." In other words, it generates natural energy without any disruption to the environment. The project will have minimal to no impact on the environment. There will be no significant changes in water quality compared to existing conditions as a result of either construction or operation of the facility. WRM Permit Criteria Hy Power has provided reasonable assurances that the proposed project will not cause a violation of state water quality standards of Section 403.918(a), Florida Statutes (1991). The parties stipulated that turbidity and dissolved oxygen were the two surface water quality issues of concern in this proceeding. The receiving water body is the Inglis By-Pass Channel. The Inglis By-Pass Channel is a Class III surface water. The project is not located in a OFW. While the lower Withlacoochee River is an OFW, the OFW designation runs up the natural river itself, and does not include the Spillway Dam, tailrace, or the remainder of the By-Pass Channel. There would be no degradation of water quality at the point of contact with the Withlacoochee River OFW. The DEP and FERC looked specifically at potential for turbidity and dissolved oxygen in determining whether the project would violate state water quality standards. The standards for turbidity and dissolved oxygen will not be violated. Because the By-Pass Dam is an under flow structure, a minimum of oxygenation currently occurs as water flows through the existing dam. The proposed project runs the water underground through the generator; however, Hy Power will measure the dissolved oxygen below the dam in the Lower Withlacoochee River. In the event there is any lowering of dissolved oxygen, Hy Power can install a "sparge ring" to reoxygenate the water going through the turbine so that dissolved oxygen remains at current levels. No turbidity will be added to the receiving water as a result of the project, because water velocity is low and the structure is encased in concrete and rip-rap. The only other potential for turbidity would occur when the coffer dams are removed after construction is complete. The coffer dams can be removed with the generator closed to permit any turbidity to settle. The amount of siltation that might occur when the generator is opened would be insignificant. Where a project is not in a OFW, an applicant must provide reasonable assurance that the project will not be contrary to public interest. See Section 403.918(2), Florida Statutes (1991). Hy Power has provided such assurances. The project will not directly affect public health, safety or welfare, or the property of others. See Section 403.918 (2)(a)1., Florida Statutes. There are concerns relating to the structural integrity of the proposed facility and adjacent structures which are discussed extensively below. The project will have no adverse impact upon the conservation of fish and wildlife, including threatened and endangered species and their habitat. See Section 403.918 (2)(a)2., Florida Statutes. While manatees are not likely to be found at the project site, the installation of the trash racks will eliminate any potential adverse impact on manatees. In fact, the racks will be an improvement over the current unprotected Spillway Dam. DEP procedures require a specific manatee control plan be implemented to deal with site specific concerns. The project will not adversely affect navigation or the flow of the water or cause harmful erosion or shoaling. See Section 403.918(2)(a)3., Florida Statutes. The project will not adversely affect fishing or recreation values or marine productivity in the vicinity of the project. See Section 403.918(2)(a)4., Florida Statutes. The permanent project and its construction will cause no significant environmental impacts. See Section 403.918(2)(a)5., Florida Statutes. There will be no adverse impacts to significant historical and archeological resources. Section 403.918(2)(a)6., Florida Statutes. With regard to the impact on current conditions and relative value of functions being performed by the areas affected by the proposed activity, there will be no negative impacts. See Section 403.918(2)(a)7., Florida Statutes. Improvement will result from better control of water flow at the project site, installation of trash racks and implementation of green power. THE FORESEEABLE ADVERSE SECONDARY OR CUMULATIVE IMPACTS Potential adverse secondary impacts related to power transmission are addressed through the fact that there is an existing power line corridor that can be used to transmit the electricity. Any need to change the corridor could be addressed by subsequent DEP permitting. Cumulative impacts are not at issue. Mr. Gammon, with Florida Power, acknowledged that the current electric company, presumably Florida Power, would be required by FERC to transport the electricity generated by Hy Power over its existing corridor and poles. No final decision has been made regarding how to access the site with equipment during construction. Several feasible construction options exist, and there are several ways of accessing the site with heavy equipment vehicles and without impacting wetlands. Any final decision would be subject to DEP approval. Since the project meets the public interest criteria of Section 403.918(2)(a), Florida Statutes, and wetland impacts are minimal, the project is permittable without the need for mitigation. See Section 403.918(2)(b), Florida Statutes. The ACOE has issued a permit for the facility. The permit varies slightly from the DEP intent to issue in the use of reinforced concrete rather than rip-rap on the bottom half of the intake channel. This is to comply with ACOE preference, but the variation has only an environmental benefit. Counsel for Petitioners sought to elicit testimony from Linda Sloan, Executive Director of the Withlacoochee Regional Planning Council, with regard to compliance of the proposed project with the Town of Inglis Comprehensive Plan and Land Development Code. Such compliance is not relevant to this proceeding. At any rate, Ms. Sloan conceded that any prohibition that might apply in the Land Development Code to construction of the proposed facility could potentially be alleviated by exemption or variance provisions in the Code. MSSW PERMIT CRITERIA The project will provide adequate flood protection and drainage in the conventional sense. See Rule 40D-4.301(1)(a), Florida Administrative Code. Because the amount of impervious area is minimal, runoff from the project will not in any way contribute to increased flooding or adversely impact drainage patterns. The total amount of impervious area of the facility is less than that of a single-family residence. SWFWMD rules do not even require MSSW permits for single-family residences because the impact is not significant. The only purpose for requiring a MSSW permit for the project is to review the project’s potential downstream impacts to the watershed, not stormwater runoff from the facility itself. The project will not cause adverse water quality or water quantity impacts on adjacent lands in violation of Chapter 373, Florida Statutes, or cause a discharge that violates state water quality standards. See Rule 40 D-4.301(1)(b), Florida Administrative Code. As indicated by the WRM water quality findings above, the project will not generally violate state surface water quality standards. See Rule 40 D-4.301(1)( c), Florida Administrative Code. The project will not generally cause adverse impact on surface or groundwater levels or flows. See Rule 40 D- 4.301(1)(d), Florida Administrative Code. Since the project is a run-of-the-river, it will not diminish the capability of a lake or other impoundment to fluctuate through the full range established for it under Chapter 40D-8, Florida Administrative Code. The project will not cause adverse environmental impacts, or adverse impacts to wetlands, fish, and wildlife or other natural resources. The project can be effectively operated and maintained. See Rule 40D-4.301(1)(g), Florida Administrative Code. The project is a slow speed, low maintenance facility. The design concept is well established and has been successfully used for many years. Possible adverse affects to public safety are discussed below. The project is consistent with the requirements of other public agencies. See Rule 40D-4.301(1)(i), Florida Administrative Code. Potential harm to water resources within the SWFWMD are discussed below. See Rule 40D-4.301(1)(j), Florida Administrative Code. The proposed project generally will not interfere with the legal rights of others. See Rule 40D-4.301(1)(k), Florida Administrative Code. The proposed project is not against public policy. See Rule 40D-4.301(1)(l), Florida Administrative Code. The project complies with the requirements contained in the Basis of Review. See Rule 40D-4.301(2), Florida Administrative Code. There is a dispute as to whether the project was within or at the edge of the 100-year flood plain. This dispute is related to how one interprets the rule as it relates to the millrace and the location of the facility which is under ground. In the conventional sense, the project is not in the flood plain. Further, the project is designed in such a way, that it is waterproof if it were topped with water. While in the past SWFWMD may have had concerns that the project might cause downstream flooding, SWFWMD currently has no such concerns, given the run-of-the-river status of the proposed project. The operation of the project will not cause downstream flooding. The DEP included in its intent to issue, conditions contained in the sublease between Hy Power and the DEP in order to ensure that the facility would remain run-of-the-river, would comply with the water control plan, and would otherwise comply with the terms of the sublease. The DEP has final control over water flow and can revoke the permit or otherwise take enforcement action against Hy Power if Hy Power fails to comply with the water control plan. GROUNDWATER IMPACTS Operation of the project will not cause groundwater contamination or otherwise have adverse groundwater impacts. Some concerns about groundwater during excavation of the construction site were raised. The conflicting evidence received regarding them is discussed below. An area of concern was the de-watering plan for the project. Everyone agrees there will be some water seepage into the construction site that will have to be pumped out. The parties disagree regarding the amount of water that will have to be removed. Their estimates of amount of water to be removed vary because their estimates of size and over-all depth of the site vary. Petitioners presented credible evidence that a potential exists for the construction site to have a large quantity of water because of its location between two sources of surface water (the By-Pass Channel and Barge Canal), because of the makeup of the subsurface, and because of the depth of the construction. Hy Power credibly represents that if excessive groundwater is found, it can address the adverse impacts through its de-watering plan that would have to be filed with FERC and DEP. The technology exists to address the de-watering of the project. Such plans are routinely considered by DEP after a construction permit is issued and before de-watering occurs. There is very little evidence of sinkhole activity in the project area, and the construction activities are not expected to cause any sinkhole activity. NOISE POLLUTION Mr. Bitter expressed concerns that FERC would require the facility to install a very loud siren that would result in sudden noise adverse to the well-being of neighbors. Mr. Bitter is unfamiliar with FERC siren requirements at run-of the-river hydroelectric facilities. In contrast, Mr. Volkin, who has substantial experience in this area, testified that the only alarm device that would be required would be for the protection of the workers during construction. The purpose of the alarm is to warn persons below a dam spillway of a change in the volume of water being let out of the impoundment. In the case of a run-of-the-river facility, the volume is near constant, changing only gradually. Therefore, even if a warning siren had to be installed its use would be limited to significant changes in flow or testing. This would not constitute a nuisance. Further, the facility is located in the vicinity of the Crystal River Nuclear Power Plant which has its own warning sirens. It would be prudent to make any warning devices required for this structure significantly different from those at the nuclear plant and to limit their use. DAM SAFETY AND FERC REVIEW In reviewing whether Hy Power’s applications complied with the relevant permitting criteria, the DEP took into consideration the review of the facility already performed by FERC. FERC will also be responsible for reviewing the project as it is being constructed. Mr. Edwards also raised concerns about the structural stability of the By-Pass Dam itself. This has been a subject of concern by those responsible for the dam, and a survey of the structure was conducted in 1993, referred to as the Greiner Report. The Greiner Report identified specific maintenance problems that have been and are being addressed by the DEP. However, DEP’s maintenance plan does not address specifically the possibility that the weight of the dam over time has caused some shifting in the dam. Hy Power has only a few core borings and only one at the location of the generator. Hy Power is using the ACOE’s original borings, as confirmed by several new ones, to develop its preliminary plans. The DEP considered FERC and the ACOE as responsible agencies for determining the structural integrity of the dam. DEP has taken FERC’s review of this facility into consideration as part of DEP’s own permitting review. It is normal for DEP to rely on outside sources and agencies for assistance in determining compliance with DEP permitting criteria such as public health and safety, and it is reasonable for DEP to do so in this instance. Most states do not have the full capability to evaluate dam safety, and so they rely on FERC and ACOE. On April 21, 1997, the project received a conduit exemption from FERC. The application process is illustrated in Hy Power Exhibit 11. Hy Power submitted to DEP detailed information about the dam, the associated structures and the proposed project which had been reviewed by FERC and the ACOE, the two agencies in the United States who are responsible for dam structure design, control, and administration. Included in the package was the Greiner Report and Hy Power’s review of it. FERC evaluated the project, the Inglis By-Pass Dam structure, and the proximity of the project to the Dam in relation to structural impact, upstream and downstream impacts, water quality, and environmental issues. Mr. Edwards raised concerns regarding the ability of the limestone bedrock to sustain additional construction in the area of proposed construction. This is a material issue in the controversy which impacts several aspects of the proposed construction. Mr. Edwards pointed out that the barge canal channel was constructed with the use of explosives that caused a fracturing of limestone bedrock. He pointed out that the steel panels, which Hy Power proposes to drive into the bedrock to construct the water retention structure necessary to excavate the hole into which the turbine and powerhouse would be placed, will further fracture this bedrock. This creates two potential dangers. It could permit water to move under and around the bottoms of the panels, potentially scouring the loosened material from the base of the panels and making them unstable and subject to failure. It could weaken the entire southern wing of the existing spillway dam. Mr. Edwards opined that this could result in catastrophic failure of the dam or the coffer dam. Such a failure would cause major destruction and loss of life to those persons living and working in and along the lower Withlacoochee River. Hy Power presented rebuttal evidence that it could and would, if necessary, inject concrete into the limestone to stabilize it and avoid the concerns raised by Mr. Edwards. FERC specifically evaluated concerns raised by project opponents over the poor physical condition of the By-Pass Channel Spillway structures, relying particularly on the 1993 Greiner Report. FERC noted that the DEP had entered into a contract to correct any deficiencies listed in the Greiner Report, which "did not conclude that the deficiencies at the By-Pass Spillway threaten downstream life and property." The FERC review concluded that the dam was safe. To ensure safety, FERC is requiring that Hy Power do a complete stability analysis of the dam prior to any construction. Articles 301 and 302 of the FERC exemption ensure that all final drawings and specifications be submitted to FERC prior to construction, along with a supporting design report consistent with FERC’s Engineering Guidelines; that FERC can require changes to assure a safe and adequate project; and that Hy Power must also submit approved coffer dam construction drawings and specifications at least 30 days prior to starting construction. FERC has its own engineering staff who will go to the site and do their own analysis, along with the ACOE, of the dam and structures, prior to any construction commencing. This is a detailed design review evaluation so that the latest information on the dam will be made known immediately prior to construction, and will prevent any catastrophic event from happening. Under FERC procedures, FERC requires the applicant to obtain the DEP permits prior to requiring applicant to submit more detailed construction designs for FERC's consideration. These more detailed designs in turn will be subject to further review by DEP and FERC. It is assumed that Hy Power will comply with the post- permitting procedures and requirements, and will present complete, detailed construction drawings for FREC and DEP approval. Hy Power’s failure to complete the process would result in denial of a construction permit.

Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law set forth herein, it is RECOMMENDED: That the DEP enter a Final Order that issues the two permits challenged in this proceedings, WRM Permit No. 38-237096-3.001 and MSSW Permit No. 38-0129249-002, subject to the conditions contained in the Intents to Issue in the respective WRM and MSSW Permits and as described in the Recommended Order. DONE AND ENTERED this 2nd day of March, 2000, in Tallahassee, Leon County, Florida. STEPHEN F. DEAN Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 2nd day of March, 2000. COPIES FURNISHED: Daniel H. Thompson, Esquire Berger Davis & Singerman 215 South Monroe Street, Suite 705 Tallahassee, Florida 32301 Andrew Zodrow, Esquire Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 John S. Clardy, III, Esquire Crider Law Firm Plantation Point 521 West Fort Island Trail, Suite A Crystal River, Florida 34429 Teri Donaldson, General Counsel Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 Kathy Carter, Agency Clerk Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 Bernard M. Campbell Bessie H. Campbell 245 Palm Street Post Office Box 159 Inglis, Florida 34449 Sarah E. Berger Post Office Box 83 Inglis, Florida 34449

Florida Laws (6) 120.5720.255267.061373.026373.414471.025 Florida Administrative Code (6) 40D -4.30140D-4.09140D-4.30161G15-27.00162-4.08062-4.242
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