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LAKE REGION AUDUBON SOCIETY vs SOUTHWEST FLORIDA WATER MANAGEMENT DISTRICT AND SPANISH OAKS OF CENTRAL FLORIDA L.L.C., 05-002606 (2005)
Division of Administrative Hearings, Florida Filed:Bartow, Florida Jul. 20, 2005 Number: 05-002606 Latest Update: Jan. 09, 2009

The Issue The issues in this case are: whether the Petitioner, Lake Region Audubon Society (LRAS), a not-for-profit corporation, has filed a petition challenging the issuance of Environmental Resource Permit (ERP) No. 44025789.001 to Spanish Oaks of Central Florida, L.C.C. (Spanish Oaks); whether LRAS has standing to challenge the ERP; whether the Southwest Florida Water Management District (District, or SWFWMD) should issue the ERP to Spanish Oaks; and whether Spanish Oaks should be awarded attorney's fees and costs.

Findings Of Fact Application and ERP On or about January 23, 2004, Spanish Oaks submitted to SWFWMD an application for an ERP to construct a surface water management system (the System) to serve a 30.878-acre, 47-lot single-family residential development in the vicinity of Lakeland, Polk County, Florida. SWFWMD requested additional information on February 20, 2004, to which Spanish Oaks responded on or about February 27, 2004. The application was deemed complete on March 26, 2004. On April 27, 2004, SWFWMD issued the Spanish Oaks ERP. The Spanish Oaks ERP describes the System as follows: The proposed surface water management system includes storm drains with associated piping and three interconnected retention ponds (Pond A, Pond B, and Pond C). The system is designed to accommodate the runoff from the activities associated with the construction of the 47-lot subdivision with paved roads. The project site is located on the south side of State Road 33, just east of Lake Luther Road in Polk County. The project is located within a hydrologically closed drainage basin. The consultant utilized a design storm based on a 100-year, 24-hour rainfall event of 10.0 inches. The ponds are designed to retain the post-development runoff volume for the 100-year, 24-hour rainfall event without surface discharge. Project runoff will be conveyed to the proposed retention ponds. . . . No adverse off-site/on-site water quantity impacts are expected. Compliance with Chapter 40D-4, F.A.C., water quality requirements is assured; the retention ponds will treat the first one- half inch of runoff from the contributing drainage area and recover this volume through natural infiltration within 72 hours. This is consistent with Part B, Environmental Resource Permitting Information Manual Section 5.2(c). No adverse on-site/off-site water quality impacts are expected. There is 0.11 acre of herbaceous wetlands within the project area. Permanent wetland impacts are proposed to the 0.11 acre herbaceous wetland. No mitigation is required for this impact. LRAS' Amended Petition On June 6, 2005, LRAS filed a Petition signed by Paul Anderson, Mae Hartsaw, Carrie Plair, and Chuck Geanangel. SWFWD dismissed the Petition without prejudice. On July 11, 2005, an Amended Petition was filed, clarifying that LRAS was orally informed about the Spanish Oaks ERP by one of its members, since identified as Donna Stark, on May 10, 2005. The Amended Petition was signed by LRAS Steering Committee/Acting President Carrie Plair. The District determined that the Amended Petition was timely filed and substantially complied with the requirements for a petition. The Amended Petition alleged the following as disputed issues of material fact: the Permit allows construction of a retention pond in a sinkhole in the southeast portion of the site; construction of a retention pond in a sinkhole creates a danger to public health and safety; and Spanish Oaks failed to notify SWFWMD that it was beginning construction of the clay cores of certain berms surrounding the retention ponds, as required by a permit condition so that SWFWMD could inspect during the construction.3 The Amended Petition asserted that LRAS member Donna Stark observed firsthand a sinkhole collapse that allegedly occurred in the southeast portion of Spanish Oaks site during construction of Retention Pond A. The Amended Petition alleged that on January 25, 2005, Donna Stark, along with a state employee (since identified as Timothy King), observed a "very large cone-shaped depression with smooth steeply-sloping sides – so steep that Donna Stark was nervous that the front-end loader driving up and down the slopes could end up in the aquifer if he lost traction in the loose unconsolidated sands. In the center of the depression was a lake perhaps 50 feet in diameter." The Amended Petition further alleged that “Donna Stark judged the distance from the top of the ground surface to the water surface to be about 15 feet.” The Amended Petition also asserted that “[o]n November 13, 2004, LRAS member Donna Stark was informed by a man who had worked on the Spanish Oaks site that the retention ponds were 30 feet deep.” As to any specific rules or statutes requiring reversal or modification of the proposed agency action, LRAS’ Amended Petition asserted that the Spanish Oaks development violates Chapter 62, Florida Administrative Code,4 which, LRAS contends, disallows the use of a sinkhole to discharge contaminated water, citing Rule 62-522.300(1) and (3). See Conclusion 90, infra. Standing LRAS did not allege or present any evidence to prove that the substantial interests of a substantial number of its members would be affected by issuance of the ERP to Spanish Oaks. The Amended Petition alleged that, if LRAS failed to oppose the ERP, it would not "fulfill it's [sic] objectives and hence adversely affect the corporation and disappoint it's [sic] membership." But LRAS did not present any evidence at the final hearing to prove that its own substantial interests would be affected by the ERP. LRAS alleged that it has standing under Section 403.412(6), Florida Statutes. See Conclusions 74, infra. LRAS was formed as a Florida not-for-profit corporation in 1962. The evidence was sufficient to prove that LRAS has at least 25 current members residing in Polk County, where Spanish Oaks' ERP is proposed. Not only was there testimony in the depositions introduced into evidence as Spanish Oaks Exhibits 1, 2 and 3 that there were over 500 members of LRAS, most of whom would reside in Polk County, exhibits attached to those depositions included a partial membership list with at least 25 current members residing in Polk County,5 in addition to other members residing in Polk County who testified during the final hearing. Article II of LRAS' Articles of Incorporation states that LRAS was formed "to promote an understanding and interest in wildlife and the environment that supports it and to further the cause of conservation." It also includes language generally empowering the corporation to "have and exercise all of the powers of like corporations not for profit and to do all and everything necessary, suitable or proper for the accomplishment of any of the purposes, the attainment of any of the objects or the furtherance of any of the powers herein set forth, . . . and to do every other act or acts, thing or things incident or pertinent to or growing out of or connected with the aforesaid objects, purposes or powers or any of them." Finally, it includes the admonition that enumeration of specific "powers and objects . . . shall not in anyway be construed as any limitation or derogation of any power or object herein specifically named or any general power which this corporation might otherwise have." Spanish Oaks6 contends that LRAS has no standing in part because the Petition and Amended Petition was "ultra vires"-i.e., that, although there was no evidence that LRAS was dissolved or otherwise not in good standing as a duly- organized not-for-profit corporation, the signers did not have the legal authority to sign or file either the Petition or the Amended Petition on behalf of LRAS under its articles of incorporation and by-laws. At the time of its formation in 1962, LRAS had eleven charter members, six officers, and ten directors. Article VI of the Articles of Incorporation provided, in pertinent part: The affairs of the corporation shall be managed by a board of directors of "not less than five members of the officers provided for in this charter and the Board of Directors shall elect a president, a first vice president, a second vice president, a secretary and a treasurer. The number of directors shall be fixed by the by-laws of the corporation, but in no instance shall the number of directors be less than five. The Board of Directors may establish an Executive Committee from the members of the Board of Directors by resolution and may provide for the setting up of advisory boards or councils. The Board of Directors shall be elected from the voting members of the corporation at an annual meeting to be held in June of each year at a date to be determined by the Board of Directors at least fifteen days prior to such meeting. A quorum for the purpose of transacting business shall consist of those present. The officers and directors herein provided for shall serve until the next general election of the corporation, provided, however, that in the event of any vacancies prior to that time the Board of Directors may fill such vacancies by majority vote. There was no evidence of any amendment to those provisions in the articles of incorporation. Article I of LRAS' By-Laws, as last revised on April 7, 2002, provided for a president to: "(a) preside at meetings of the Society and of the Board of Directors; . . . ; (c) decide all questions of order, and act as judge in elections and declare the results; (d) appoint, subject to the Executive Committee's approval, the chairmen of the Standing Committee, and the chairmen of such special committees as may be authorized by the Board; (e) perform such other duties as the Board or the By-Laws may from time to time assign." It also provided for: a first vice-president, who was to preside and perform the duties of the president in the absence or inability of the president; a second vice-president, who was to preside and perform the duties of the president in the absence or inability of the president and first vice- president; a third vice-president to coordinate all field activities; a fourth vice-president to coordinate all membership activities; a fifth vice-president to be the newsletter editor; a recording secretary to keep an accurate record of all meetings, act as secretary of the board of directors, keep a record of attendance at meetings of the board of directors, and act as custodian of all records and papers; a corresponding secretary, who was to perform the duties of the recording secretary in the absence or inability of the recording secretary; and a treasurer. Article II of the By-Laws provided for the board of directors to "be composed of all officers and committee chairmen, and other members who may be appointed by the President." It also provided that the board of directors had the "power to fill vacancies in the list of officers." It also provided: "A majority of officers shall have the power to carry on the affairs of the Society in the event of emergency, between Board Meetings." Article III of the By-Laws provided for committees to be established by the president as deemed necessary as well as apparently for appointment of individuals with special responsibilities. Article IV provided for elections, including: "A Nominating Committee, consisting of a Chairman and two other members appointed by the President and announced at the January Board Meeting, shall submit a slate of officers at the March meeting for approval by the Board, to be voted on at the Annual Meeting of the Society in April. . . . A majority of the votes cast shall constitute an election. If there are no nominations from the floor, the slate of officers shall stand as presented." It also provided: "Elected officers shall be elected for a term of one year, and shall hold office until their successors have been elected." The president was limited to two consecutive terms, or a third consecutive term upon majority vote of the board of directors. Article V of the By-Laws provided for: open meetings of the board of directors to be held on the second Wednesday of each month September through May, unless changed on ten days notice to each board member; special meetings at the call of the president or written request of five members, with "due notice"; and one annual meeting to be held in April, unless changed by direction of the board. Article VI provided that a majority of the board would constitute a quorum, provided at least two officers were present, and that 15 members, including at least four Board members, would be a quorum for the annual meeting. Article VIII provided that membership in National Audubon, Florida Audubon or LRAS would constitute membership in all three levels for anyone living within the LRAS area. As indicated above, there are inconsistencies between the Articles of Incorporation and the By-Laws. For example, the Articles of Incorporation provide for an annual meeting in June, while the By-Laws provide for the annual meeting to take place in April, unless changed by the board of directors. In addition, the By-Laws provide for more officers than the Articles of Incorporation. Finally, the Articles of Incorporation provide that a quorum at the annual meeting shall consist of those present, while the By-Laws provide for a quorum of a majority of the board, provided at least two are officers, and that 15 members, including at least four board members, would be a quorum for the annual meeting. Under Section 617.0206, Florida Statutes, by-laws must be consistent with the articles of incorporation. Even allowing for the inconsistencies between the Articles of Incorporation and the By-Laws, the evidence suggested that, notwithstanding the formal and detailed (if somewhat inconsistent) provisions in the Articles of Incorporation and By-Laws, LRAS has operated less formally and with less attention to those details at least in recent years, in part because it is a totally-volunteer organization and seems always to be looking for members to share in the tasks of continued operation. Any member who expresses interest in the business of the organization is welcome to volunteer to be on the board of directors. Any volunteer is virtually assured of becoming a board member. There certainly are no contested elections. Spanish Oaks questions whether the process used results in the legitimate election of members of the board of directors and appointment of officers in accordance with the Articles of Incorporation and By-Laws. The evidence presented by Spanish Oaks as to status of LRAS' board of directors and officers was unclear. It consisted of the deposition testimony of Paul Anderson, Carrie Plair, and Chuck Geanangel, along with minutes attached as exhibits to the Anderson deposition. In addition, while not actually introduced in evidence at the final hearing, the minutes of the May 2005 meeting of the board of directors were attached to and formed part of the basis for the Motion for Summary Recommended Order which was filed by Spanish Oaks and joined by SWFWMD. In addition, the PRO filed by Spanish Oaks cited to these attachments to the Motion for Summary Recommended Order.7 The evidence indicates that, notwithstanding provisions in the Articles of Incorporation and By-Laws, for the last two years LRAS has operated using a five-member steering committee (also referred to as an executive board) instead of a president. Designed to relieve the burden on long-serving volunteer president, Pat Herbert, the idea was that the steering committee would rotate responsibility for conducting board meetings, so that each committee member would conduct two meetings a year. Anderson and Plair testified that they were on the LRAS Steering Committee, along with Geanangle, Bill Karnofsky and Mae Hartsaw. Plair testified that all members of the Steering Committee are members of the board of directors, along with all other officers. Anderson also named several other officers from memory--Liz Purnell, Paul Fellers (a vice- president), Gary McCoy (membership chair), and Herman Moulden (newsletter editor). He deferred to a list of board members, which he did not have with him and which was not placed in evidence. Plair named a few other board members--Bob Snow, Gina Lucas, Gil Lucas--along with Fellers. The minutes placed in evidence by Spanish Oaks all state that they are minutes of board of directors meetings and do not refer to an annual general membership meeting. However, Anderson testified that a board of directors meeting is combined with the annual general membership meeting. He believed it was in December but was not sure. Geanangel testified that the annual general membership meeting was in the spring, which was consistent with Plair's recollection, and was noticed as such. Plair testified that there generally were meeting agendas for all board of directors meetings (one of which, according to the testimony, would be the annual general membership meeting). No notices or agendas of meetings were placed in evidence. The minutes placed in evidence started with the September 2003 meeting of the board of directors. According to the minutes, Karnofsky conducted the meeting and also presented a treasurer's report, indicating that he also was the Treasurer at the time. Herbert, Louise Lang, Hartsaw, Plair, Paul and Janet Anderson, Ann Pinner, Gil and Gina Lucas, Paul Fellers, and Rae Bourqueim also attended. Bourquein announced a newsletter deadline. Pinner was looking for volunteers. Under old business, the rotation for conducting the next several meetings was announced: Karnofsky for October 2003, Plair for November and December 2003, Paul Anderson in January and February 2004, and Hartsaw in March and April 2004. Janet Anderson was congratulated on the job she was doing as "Publicity Chairperson." A December 2003 Christmas party was announced. Motions were made or seconded by Gil Lucas, Paul Anderson, Bourqueim, Fellers, and Hartsaw (suggesting that they were members of the board of directors). The minutes were recorded by Gina Lucas, as "Secretary Pro Tem." There was no other indication in those minutes as to who the officers and board members were. The minutes of the October 2003 meeting indicate that the meeting was conducted by Herbert, not Karnofsky, who was unable to attend due to illness. Nine others attended, including the Andersons, Plair, the Lucases, Fellers, Bourquein, Herbert, and Purnell, who was the Recording Secretary. The November 2003 minutes indicate that Plair conducted the board meeting. Hartsaw, Bourquein, Geanangel, Karnofsky, the Lucases, Fellers, Marvel Loftus, the Andersons, Ron Butts, Herbert, and three others also attended, along with Purnell, the Recording Secretary. Motions were made or seconded by Paul Anderson, Hartsaw, Fellers, Herbert, Geanangel, and Janet Anderson. The minutes of the January 2004 meeting of the board of directors indicate that Paul Anderson conducted the meeting, Karnofsky presented a treasurer's report, and Purnell was the Recording Secretary. Hartsaw and Geanangel attended the meeting, along with the Andersons, the Lucases, Herbert, Lang, Loftus, and two others. A motion was made by Herbert and seconded by Loftus. According to the minutes of the February 2004 meeting of the board of directors, it was conducted by Paul Anderson again, again included Karnofsky's treasurer's report, and again was recorded by Purnell. Janet Anderson, Lang, Plair, Hartsaw, the Lucases, Geanangel, and three others also attended. The minutes indicate that Chuck Geanangel would conduct the March 2004 meeting. They also included the reports of several others, including Plair and Hartsaw, without specifying whether they were officers. The minutes indicated that the slate of candidates would be the same as the current officers, but they do not specify who the current officers were, or whether the reference to "officers" was meant to include board members. The minutes of the March and April 2004 meetings, which were conducted by Geanangel and also attended by Hartsaw, the Andersons, Bourquein, Karnofsky, Purnell, Loftus, Pinner, Plair, Fellers, and others. Motions were made or seconded by Herbert, Paul Anderson, Hartsaw, and Loftus. These minutes do not reveal any more information about who the officers were but do reflect that Ron Butts was willing to be on the board of directors and would be contacted about the position. The minutes indicate that a board of directors meeting was held on May 12, 2004, and that it was conducted by Anderson again and was attended by 13 people, including Plair, Hartsaw, Butts, and Geanangel. The minutes do not mention its being a general membership meeting, do not mention any voting, and do not mention any nominations from the floor for membership on the board of directors. They indicate that a new membership chair volunteer was called for and that Karnofsky would be asked to conduct the next meeting in September 2004. Motions were made or seconded by Hartsaw, Butts, Geanangel, and Loftus. The September 2004 minutes indicate that the board meeting was conducted by Geanangel, not Karnofsky, who was absent and did not present his treasurer's report. Plair, the Andersons, Butts, and Ann Pinner attended. Motions were made or seconded by Janet Anderson, Geanangel, Butts, Plair, Paul Anderson, and Pinner. A House Interior Committee was formed, with Plair, Susie Brantley, and Gina Lucas as members. Janet Anderson recorded the minutes in Purnell's absence. According to the minutes, Geanangel also conducted the October 2004 meeting of the board, which was also attended by Bourquein, Karnofsky (who gave the treasurer's report), Pinner, Plair, the Andersons, Paul and Donna Fellers, Butts, the Lucases, and Purnell, the Recording Secretary. Gina Lucas reported for the House Interior Committee. Motions were made or seconded by Butts, Loftus, and Paul Fellers. According to the minutes, Plair conducted the November 2004 meeting of the board, which was also attended by Karnofsky (who gave the treasurer's report), Pinner, the Andersons, Hartsaw, Butts, one other person, and Purnell, the Recording Secretary. It was announced that Bourquein was resigning from her position as Newsletter Editor. There was no replacement yet. The next minutes were for a board meeting in January 2005. Paul Anderson conducted the meeting, which also was attended by Geanangel, Plair, Karnofsky (who gave the treasurer's report), Hartsaw, Gary McCoy, Pinner, Paul Fellers, the Lucases, Butts, one other person, and Purnell, the Recording Secretary. McCoy was introduced as the new Membership Chairman, and it was announced that Herman Moulden had accepted responsibility for the newsletter and website. Geanangel reported on Polk County's desire to use the Saddle Creek property owned by Audubon of Florida for water storage, flow, and quality purposes. Leadership vacancies for Nature Faire and Corresponding Secretary were announced. A motion was made by Pinner and seconded by Hartsaw. According to the minutes, the February 2005 meeting was conducted by Paul Anderson. Plair, Karnofsky, Butts, McCoy, Hartsaw, the Andersons, Moulden, Geanangel, Pinner, Paul Fellers, and Purnell attended. Moulden solicited articles for the newsletter. It was suggested that an invitation to serve on the board be extended to Bob Snow. Motions were made or seconded by Butts, Janet Anderson, Plair, and Pinner. Purnell recorded the minutes. According to the minutes, the March 2005 meeting was conducted by Hartsaw. The Andersons, Paul Fellers, Moulden, McCoy, Butts, Karnofsky, Plair, Geanangel, and one other person also attended. McCoy presented a membership report, and Moulden reported on the newsletter. Geanangel reported on negotiations with Polk County on the Saddle Creek property. Motions were made or seconded by Paul Anderson, Fellers, and Karnofsky. Hartsaw would chair the April meeting. Paul Anderson recorded the minutes in Purnell's absence. According to the minutes, the April 2005 meeting was conducted by Hartsaw. Pinner, McCoy, Karnofsky, the Andersons, Moulden, the Lucases, Butts, Plair, Paul Fellers, Purnell (the Recording Secretary), and one other person also attended. Karnofsky gave his treasurer's report, Moulden asked for newsletter articles, and a nominating committee was appointed, consisting of Paul Anderson, Karnofsky, and Plair. A motion was made by Karnofsky and seconded by Loftus. The real need for a corresponding secretary was discussed. According to the minutes,8 the May 11, 2005 meeting was conducted by Karnofsky. Plair, Butts, the Andersons, Pinner, McCoy, Moulden, Geanangel, Purnell (the Recording Secretary), Donna Stark, and one other person also attended. Motions were made by Paul Anderson and seconded by Pinner. The minutes reflect a nominating committee report which included: a five-member Steering Committee of Karnofsky, Hartsaw, Geanangel, Plair, and Paul Anderson; Hartsaw as Vice- President for Programs; Geanangel as Vice-President for Conservation; Paul Fellers as Vice-President for Field Trips; McCoy as Vice-President for Membership; Moulden as Vice- President for News Letter; Karnofsky as Treasurer; and Purnell as Recording Secretary. Also nominated as members of the board of directors were: Janet Anderson, Louise Lang, Marvel Loftus, the Lucases, Butts, McCoy, Moulden, Snow, Pinner, and six others. No voting or nominations from the floor are reflected in the minutes. While the evidence was not clear, it appears from the testimony and minutes that all those attending the board of directors meeting on May 11, 2005, except for Donna Stark and one other person, were officers or otherwise members of the board of directors under the Articles of Incorporation and the By-Laws. The minutes of the February 2004 board meeting state that the "LRAS Candidate slate will be the same as the current officers." It appears that they included at least Karnofsky, Bourqueim, and Purnell and that Karnofsky, Plair, Paul Anderson, Hartsaw, and Geanangel were on the steering committee. Assuming the use of the word "officers" in the minutes meant to include the current board members who were not officers, it appears that they also would have included Herbert, Lang, Janet Anderson, Pinner, the Lucases, Fellers, Loftus, and Butts. There are no minutes mentioning a noticed general membership meeting or election of the board of directors in the spring of 2004. If there was one, the minutes do not indicate that there were nominations from the floor. If there was a noticed general membership meeting for purposes of electing the board of directors, with a quorum, and there were no nominations from the floor, either the slate of current officers (and, probably, directors) "stood," or the officers and board of directors would continue to serve until the next general election, under Article VI of the Articles of Incorporation. In either case, vacancies prior to that time could be filled by the board of directors by majority vote, and it would appear that, at the beginning of the board meeting on May 11, 2005: the officers included at least Karnofsky, Purnell, McCoy, and Moulden; the steering committee still consisted the same five; and other board members included at least Lang, Janet Anderson, Pinner, the Lucases, Fellers, Loftus, and Butts. Only 12 individuals appearing to be board members attended the meeting on May 11, 2005. While this would not be a quorum under the By-Laws, it would be a quorum under the Articles of Incorporation, which would control over inconsistent By-Laws.9 Assuming the May 2005 meeting was the noticed general membership meeting, since the minutes do not reflect any nominations from the floor, the slate stood as presented under Article IV of the By-Laws. If not, (or if the By-Laws established the necessary quorum), under Article VI of the Articles of Incorporation, the current officers and board of directors would serve until the next general election. In either case, it appears that authorized officers and directors were in place and in attendance at the board meeting on May 11, 2005, and that there was a quorum for transacting business under the Articles of Incorporation. In any event, Spanish Oaks did not prove the contrary. According to the May 2005 minutes, as well as the testimony at the final hearing, Donna Stark made a presentation asserting that Spanish Oaks was using at least three sinkholes to collect runoff water, instead of digging retention ponds, contrary to legal requirements and polluting the underlying aquifer. She asked LRAS to consider filing an administrative challenge to the ERP. After the presentation, the board decided that the Steering Committee would continue to investigate and make a decision as to what role LRAS should have in the future. Although the minutes do not reflect a vote on a resolution, the assigned task of the Steering Committee was like the role of the "Executive Committee" referred to in Article VI of the Articles of Incorporation. The Steering Committee reviewed the information presented by Starks, decided to file a challenge, and invited Starks to help draft the Petition, which was signed by four members of the Steering Committee between May 31 and June 2, 2005, as well as the Amended Petition signed by "LRAS Steering Committee/Acting President Carrie Plair" on July 6, 2005. Starks actually drafted almost all of the Petition and Amended Petition. The subject of the challenge in the Petition and Amended Petition is virtually identical to a challenge to Spanish Oaks' ERP that was filed by Starks on behalf of her not-for-profit corporation, Central Florida EcoTours, in early May 2005 but was time-barred and dismissed because Starks and Ecotours got mailed notice of the issuance of the ERP to Spanish Oaks. Spanish Oaks implied that Starks told LRAS about the fate of the EcoTours challenge and asked LRAS to file its Petition and Amended Petition at her behest to block the Spanish Oaks development for her ulterior motives. But those allegations were denied by LRAS and were not proven. Alleged Sinkholes The principal concern raised by LRAS, both in its Amended Petition and at hearing, is that one or more of the retention ponds constructed on Spanish Oaks is located over a sinkhole. LRAS is of the view that this alone should mandate that the ERP application be denied. Retention ponds are often located in depressional areas since these land features are generally the lowest spots on a property and allow the engineers designing a surface water management system to utilize the land’s natural drainage configuration. A relic sinkhole, as contrasted to an active sinkhole, has either been sealed or has self-sealed, so that there is no connection between the sinkhole and the underlying aquifer. An active sinkhole provides a direct connection-- referred to by both LRAS’ and Spanish Oaks' experts as a “good communication”--between the surface and the aquifer. Retention ponds are intended to allow infiltration of water through the soils underlying the pond bottom. This infiltration through soil layers provides water quality treatment, and it is necessary to ensure that the bottom surface of a retention pond is sufficiently separated by soils from the top of the aquifer. If an active sinkhole develops in a retention pond, SWFWMD requires that some corrective action be taken. Generally, this involves refilling the cavity formed by the sinkhole. However, because retention ponds are designed to allow infiltration through the pond bottoms, care must be taken to ensure that any fill does not impede this infiltration function. The bottoms of the retention ponds at Spanish Oaks are approximately seven feet below natural grade. The Floridan Aquifer in the Spanish Oaks vicinity is approximately 75 feet below grade. The separation between the pond bottoms and the limestone that is part of the aquifer is sufficient to provide adequate water quality treatment. Soil borings done around the perimeter of each of the ponds indicate the presence of clays and clayey sands between the pond bottoms and the aquifer. These soil layers act as an aquitard that impedes the migration of water into the bedrock (and upper soils into lower cavities, voids, or ravel zones, which are areas of loose, unconsolidated soils capable of further downward subsidence). In each instance, the depth at which the aquitard occurs is below the bottom depth of the retention ponds. There was no competent evidence admitted at hearing to suggest that there are active sinkholes in or under any of the three retention ponds on Spanish Oaks. To the contrary, the SWFWMD personnel who have been on the site testified that they saw nothing on the site that indicated the presence of an active sinkhole. Contractors and engineers who were on the site prior to and during construction of Spanish Oaks stated that they were not aware of any active sinkholes. Nonetheless, because LRAS made the allegation that there were sinkholes on the site, Spanish Oaks retained a geotechnical engineer with expertise in sinkholes, Sonny Gulati, to conduct a sinkhole investigation of the three retention ponds. Mr. Gulati used testing protocols that are generally utilized to determine whether sinkhole activity has caused damage to a building or other structure. Mr. Gulati observed no damage to the retention ponds and his investigation revealed no sinkhole activity onsite. (LRAS’ expert also was unaware of any damage to the retention ponds.) Mr. Gulati used both ground penetrating radar (GPR) and standard penetration testing (SPT) during his investigation. GPR makes use of repetitive, short-duration, electromagnetic waves, which are deflected back to a receiver by interfaces between materials. GPR detects subsurface features such as sinkholes and voids through the reflected radar signal. GPR must be conducted with the transmitter in contact with the ground surface. It cannot be used over a water surface. Mr. Gulati took GPR readings around each of the three retention ponds, in two circles, one contained within the other. GPR data collected on the Spanish Oaks site revealed no subsurface anomalies. SPT is described in Mr. Gulati’s report as: a widely accepted method of in-situ testing of foundation soils (ASTM D-1586). A two- foot long, two-inch outside diameter, split barrel (“spoon”) sampler, attached to the end of drilling rods, is driven 18.0 inches into the ground by successive blows of a 140-pound hammer freely dropping 30.0 inches. The number of blows needed for each six (6) inches of penetration is recorded. The sum of the blows required for penetration of the second and third six-inch increments of penetration constitutes the test result or N-value. LRAS Exhibit 5, p. 23. An N-value of less than 2 indicates the presence of a ravel zone, a subsurface area with voids or loose soils into which soils from upper strata can travel and which acts as a conduit between strata. An N-value of less than 4, in combination with a loss of drilling fluid,10 may also indicate a ravel zone. Solutioned calcareous ravel zones are those ravel zones that occur in the limestone that forms the top of the Floridan Aquifer. Based on his investigation, Mr. Gulati concluded as follows: Our investigation did not reveal the existence of specific conditions such as cavities or voids, solutioned calcareous ravel zones, or the presence corroded bedrock conditions located above the dense bedrock stratum indicative of sinkhole activity at the subject site. Based on the interpretations of our recent subsoil investigation, site reconnaissance, available background and geologic data, it is our opinion that the subject site has not been impacted by a sinkhole related activity. In our professional opinion, the scope of work included in this analysis is of sufficient scope to eliminate sinkhole activity at the subject site within a reasonable professional probability. LRAS-5 at 18 (emphasis in original). SWFWMD's expert agreed that there is no direct connection to the Floridan Aquifer. Marc Hurst, a geologist who testified for LRAS, opined that Mr. Gulati’s sinkhole investigation was insufficient to demonstrate whether or not the Spanish Oaks retention ponds were constructed over sinkholes.11 However, Mr. Hurst offered no opinion as to whether the retention ponds are located over active sinkholes. Nor did Mr. Hurst specifically disagree with Mr. Gulati’s conclusion that the Spanish Oaks retention ponds have not been impacted by active sinkholes.12 To the contrary, Mr. Hurst admitted that the retention ponds were holding water on the day that he observed them--indicating that to him that the ponds were not acting as a strong conduit to the aquifer. Mr. Gulati also noted the significance of the presence of water in the ponds, stating that, if there were active sinkholes in the ponds, they would not hold water.13 The only suggestion of any sinkhole-related damage to the retention ponds came from Donna Stark, who testified that George Wilt--a heavy equipment operator at the site incorrectly identified by Ms. Stark as “an employee of Spanish Oaks”--told her that there had been a sinkhole collapse during the excavation of Pond A. This hearsay testimony was directly contradicted by Mr. Wilt himself, who testified that he made no such statement. Despite the allegation in LRAS’ petition regarding observations of collapse of sinkhole by Donna Stark, Ms. Stark herself admitted at hearing that she did not witness any actual collapse. Rather, she testified that, on January 25, 2005, she saw what she believed to be the aftermath of a sinkhole collapse. Stark may have been confused by the amount of excavated material being stored on the ground surface around the pond. 43,906 cubic yards of dirt was excavated from Pond A alone and was stacked to a height of 8-10 feet higher than the natural ground elevation. Others who observed the site on January 25, 2005, saw no evidence of a sinkhole collapse. Tim King, a Florida Fish and Wildlife Conservation Commission employee who was with Ms. Stark on January 25, 2005, merely reported seeing pond excavation in process. Laura Howe, a SWFWMD employee who inspected the site on that date, observed that “[i]t appears depth of ponds are [p]robably close to permitted depth.” Moreover, Ms. Stark admits that, on February 10, 2005, she observed the ponds to be “[s]even and a half feet, or six and a half, whatever it should be.” Ms. Stark’s suggestion that the collapse was filled in between January 25 and February 10, 2005, is belied by testimony that repairing a sinkhole collapse of the size suggested by Ms. Stark would have required much more material than was available. (No dirt was imported onto the site.) The evidence admitted at hearing requires a finding that there was no sinkhole collapse onsite. Spanish Oaks provided reasonable assurance that the System was designed and constructed to include sufficient separation between the pond bottoms and the Floridan Aquifer to prevent groundwater contamination. Construction of Berms LRAS contended in its Amended Petition that Spanish Oaks failed to give notice prior to constructing clay cores in some of the berms onsite, as required as a condition of the ERP, and that this failure constituted failure to provide reasonable assurances.14 The interconnection of the three ponds that are part of the System will allow them to function as one pond, while a perimeter berm around the entire Spanish Oaks project will ensure that surface water runoff is retained onsite and directed toward the ponds. Ponds A and C are located, respectively, at the southeast and northeast corners of Spanish Oaks.15 The design plans submitted with the ERP application indicated that the berms alongside the eastern side of Ponds A and C are to include clay cores, a design feature that was included as a specific condition in the ERP. The purpose of the clay cores was to prevent offsite impacts caused by lateral movement of water. The specific conditions of the ERP also required that Spanish Oaks notify SWFWMD's "Surface Water Regulation Manager, Bartow Permitting Department [William Hartmann], at least 48 hours prior to commencement of construction of the clay core, so that District staff may observe this construction activity." LRAS proved that Mr. Hartmann did not personally receive a phone call prior to the construction of the clay cores, as required by the ERP, and that SWFWMD staff did not observe the construction. Mr. Hartmann explained that this constituted a permit condition compliance issue which would prevent the ERP from being transferred to the operation phase until SWFWMD was assured that the clay core was, in fact, constructed as required. To confirm proper construction of the clay core, Spanish Oaks undertook soil borings. SWFWMD staff engineer Sherry Windsor was onsite to observe the soil borings. Spanish Oaks also submitted a report from its engineering consultant certifying that the clay cores had been properly constructed in accordance with the ERP. SWFWMD typically relies on a project engineer’s signed and sealed certifications of compliance matters. SWFWMD staff observations and the certification provided by the Spanish Oaks engineer satisfactorily resolved the issue of proper clay core construction. Failure to notify Mr. Hartmann prior to construction, as required by the ERP, does not undermine Spanish Oaks' provision of the necessary reasonable assurance for issuance of the ERP.

Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that SWFWMD issue a final order approving the issuance of ERP 44025789.001 to Spanish Oaks. Jurisdiction is retained to consider Spanish Oaks’ Motion for Attorney's Fees under Sections 57.105, 120.569(2)(e), and 120.595(1)(a-e), if renewed within 30 days after issuance of the final order. DONE AND ENTERED this 10th day of November, 2005, in Tallahassee, Leon County, Florida. S J. LAWRENCE JOHNSTON 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 November, 2005.

Florida Laws (9) 120.52120.569120.57403.41257.105617.0206617.0304617.0801617.0803
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IN RE: GEORGE BLAKE vs *, 05-000571EC (2005)
Division of Administrative Hearings, Florida Filed:Live Oak, Florida Feb. 16, 2005 Number: 05-000571EC Latest Update: May 01, 2006

The Issue The issue is whether Respondent violated Section 112.313(6), Florida Statutes, during January through March 2003.

Findings Of Fact Pursuant to Article II, Section 8, Florida Constitution, and Section 112.320, the Commission is empowered to serve as the guardian of the standards of conduct for the officers and employees of the state. Pursuant to Sections 112.324 and 112.317, the Commission is empowered to conduct investigations and to issue a Final Order and Public Report recommending penalties for violations of the Code of Ethics for Public Officers and Employees (Code of Ethics). Respondent George Blake (Mr. Blake) is subject to the Code of Ethics. Mr. Blake, at the time of the hearing, had served continuously as a town councilman of the City of Live Oak, Florida, for approximately 15 years. The City of Live Oak is a small North Florida town governed by a five-member City Council having one member designated by the Council as President. It has an elected Mayor who has no vote in Council matters. The Council governs Live Oak through a City Administrator. The Council has the authority to hire and discharge city employees although it generally defers to the City Administrator to accomplish those duties. The City Council of Live Oak, like governing bodies in many small towns, is more intimately involved in the day-to-day operations of the municipality than is the case in a large city. Michael Christensen (Mr. Christensen) resides in Umatilla, Florida, and resided there at all times pertinent to this case. In January 2003 he held a Building Code Administrator's license issued by the State of Florida and was a registered architect. He also held a general contractor's license. He had never before been a municipal employee at any municipality. Mr. Christensen was hired as the Building Official for the City of Live Oak by Myron Holmes, the Live Oak City Administrator. Mr. Holmes believed that Mr. Christensen was highly qualified for the job. Mr. Christensen began work on January 13, 2003. Willard Hewett, the Public Works Director for Live Oak, was Mr. Christensen's immediate supervisor. Mr. Christensen was hired pursuant to an agreement that he would work Monday through Thursday each week. According to the City Personnel Policy and Procedure Manual, all employees except police and fire personnel must work five days per week, eight hours per day. Only the Council could approve a variance and in the case of Mr. Christensen, the Council was never asked to approve this deviation from the Manual. Prior to Mr. Holmes' decision to hire him, Mr. Christensen met with the Council. The Council, including Mr. Blake, was aware that a condition of employment was that he be allowed to work a four-day week. Mr. Blake did not object to the four-day work week schedule that was proposed. The City Counsel made a unanimous recommendation to Mr. Holmes that Mr. Christensen be hired. A four-day work week was critical to Mr. Christensen's employment with the City until his house in Umatilla was sold. He was also finishing up some work in Umatilla. It is 150 miles from Umatilla to Live Oak. On January 14, 2003, Mr. Christensen began the review of plans submitted by Julie Ulmer for a house to be built for Mr. Blake. Ms. Ulmer is Mr. Blake's daughter. Mr. Christensen noted 26 items on the plans which did not comply with the Florida Building Code (FBC). The builder, Jeremy Ulmer, Ms. Ulmer's husband, resubmitted the plans. Mr. Christensen found additional deficiencies on the resubmitted plans. Mr. Christensen and Mr. Ulmer had a discussion with regard to the deficiencies in Mr. Christensen's office on February 4, 2003. Mr. Ulmer exhibited hostility toward Mr. Christensen. Mr. Christensen met twice with Gary Gill, the Professional Engineer who had "sealed" the plans. Eventually Mr. Christensen determined that, after modification, the plans met the FBC and, on February 7, 2003, he issued a building permit for the construction of the Blake residence. He also became aware that Mr. Blake was unhappy with him. During the time that Mr. Christensen served as Building Official he conducted plan reviews on a total of ten plans and, at least initially, rejected all ten. On Tuesday, February 11, 2003, at the regularly scheduled Council meeting, Mr. Blake attempted to cause the Council to consider Mr. Christensen's performance as Building Official. It is unusual for the performance of a city employee to be considered during a Council meeting, although not without precedent. Don Boyette, the president of the Council, recessed the meeting to February 18, 2003, when the matter of Mr. Christensen was to be discussed further. By Thursday, February 13, 2003, City Administrator Holmes was aware that Mr. Blake was angry with Mr. Christensen and believed he had embarked on a course of action designed to visit harm upon Mr. Christensen's employment status. City Administrator Holmes thought the matter had become, "extremely heated." At some point, Mr. Blake had stated to Mr. Holmes that the plan changes to his house had cost him a lot of money. Also on February 13, 2003, Mr. Blake attended a meeting of the Builders' Association of Suwannee County at the Farm Bureau Building and individual complaints regarding Mr. Christensen were made to him by Sam Carter, Lynn Fletcher, Dan Murray, and Harvey Carroll who are all involved in the construction business. On one other occasion he received a complaint from J.D. Brown who is in the construction business. The complaints against Mr. Christensen centered primarily around his attitude, and these complaints were legitimate. His ability to deal with builders in Live Oak was hampered by his imperious attitude. The prior building official was considered strict, like Mr. Christensen, but he was able to obtain compliance without greatly irritating people. This propensity to irritate people was observed by Chad Croft, the Live Oak Fire Chief. Chief Croft had for many years accomplished his Life Safety inspections on commercial buildings in company with the Live Oak Building Official. This was done as a matter of convenience to the person whose business was being inspected. He continued this practice when Mr. Christensen became the Building Official. However, after a few of these inspections he discontinued the practice because he objected to being present during Mr. Christensen's unpleasant interactions with contractors. Mr. Croft opined that Mr. Christensen lacked people skills and was harsh with people. On Friday, February 14, 2003, Mr. Christensen entered upon the property on which Mr. Blake's house was being constructed for the purpose of inspecting the footer, which is part of the foundation. He asked Pat Sura, the Suwannee County Building Official, to accompany him because he believed that Mr. Blake was seeking retribution because of the changes in the building plans. Mr. Sura had been a building official for many years and was more experienced than Mr. Christensen. Mr. Christensen and Mr. Sura both found the footer forms constructed on the Blake property to be deficient because of root obstruction. Mr. Christensen decreed that the roots would have to be removed before concrete could be poured. Mr. Sura thought that it would be permissible for the footer to be poured and the roots removed subsequently. Because Mr. Sura was present in an advisory capacity, it was Mr. Christensen's opinion that prevailed, based on FBC 23-1.2, which clearly says that vegetation must be removed before the footer may be poured. Mr. Christensen returned to his office to obtain his copy of the FBC and then returned to the building site. When he returned he found that Mr. Ulmer had come to the site. Mr. Ulmer was unhappy when he learned he could not pour the footers absent additional work. Mr. Ulmer said to him, "If you don't pass my inspection, there will be consequences." Ultimately, Mr. Hewitt authorized the contractor to pour concrete into the footer as scheduled. On Monday, February 17, 2003, Mr. Christensen met with City Attorney Ernie Sellers at his office. Also attending were Willard Hewett and Myron Holmes. Mr. Christensen stated that he believed Mr. Blake was trying to intimidate him. Although Mr. Blake had never spoken to Mr. Christensen about this matter, Mr. Christensen drafted a letter to the State Attorney requesting prosecution and a letter of guidance to the Council. He did not mail this letter after having been advised that the State Attorney was the incorrect venue for his complaint. On Tuesday, February 18, 2003, at the Council meeting which was a continuation of the February 11, 2003, meeting, referred to as a "recessed meeting," several people testified. Julie Ulmer, Tom Smith, who is an architect, and Sam Carter who is a draftsman, all complained about Mr. Christensen's performance. Prior to this time only a few people in the construction business, other than the Ulmers, had complained about Mr. Christensen to Mr. Hewitt. The complaints addressed to Mr. Hewitt were routine disagreements between contractors and Mr. Christensen, and Mr. Hewitt was concerned with Mr. Christensen's absence one day a week. Mr. Christensen solicited and obtained a letter of recommendation from Jimmy Worth who was building a large building that was being inspected by Mr. Christenson on a routine basis. This letter was presented to the Council during the "recessed meeting." Mr. Christensen spoke at the meeting and he and Mr. Blake had a heated exchange of words. During the meeting Mr. Blake stated that he did not believe that Mr. Christensen could work with people and that if he could get two more votes he would have Mr. Christensen fired. Despite this, both Mr. Hewett, Mr. Christensen's immediate supervisor, and Mr. Holmes, the City Administrator, remained satisfied with Mr. Christensen's performance. The day after the "recessed meeting," on February 19, 2003, Mr. Blake told City Administrator Holmes that he wanted Mr. Christensen to work a five-day work week, in accordance with the City Personnel Policy and Procedure Manual. Mr. Blake, having failed to have Mr. Christensen terminated by the Council, wrote the County Coordinator on February 21, 2003, and requested that Suwannee County building officials inspect the construction of his home pursuant to an existing inter-local agreement. This resulted in the county building official doing the inspection. All citizens of Live Oak are permitted to request that the Suwannee County building department inspect their construction and such requests are routinely granted. By February 21, 2003, Mr. Christensen had already drafted his ethics complaint. Mr. Blake sought a legal opinion from City Attorney Sellers, as to whether he had to abstain from any vote to discharge Mr. Christensen. In a letter dated February 28, 2003, Mr. Sellers correctly noted that Mr. Blake had a personal issue with Mr. Christensen related to the home Mr. Blake was having built and that Mr. Blake had received complaints from others addressing Mr. Christensen's performance. Mr. Sellers opined, "It is my opinion that firing or not firing the building inspector is not reasonably calculated to afford you any special private gain or loss and that there will be no conflict involved in your voting on the above state [sic] issue." At a meeting of the Council on March 11, 2003, Mr. Blake moved to abolish the City's building inspection activity and to contract with Suwannee County for the purpose of building inspections. This motion failed with three members voting in opposition and two in favor. Mr. Blake then moved to require Mr. Christensen to work five days a week, in accordance with the City Personnel Policy and Procedure Manual. This motion passed. The requirement to work a five-day week resulted in the constructive termination of Mr. Christensen because he could not comply with this requirement due to his personal financial situation. Accordingly, on March 17, 2003, Mr. Christensen submitted his letter of resignation. Mr. Blake put a copy of Mr. Christensen's letter of resignation in each councilperson's box, and the Mayor's box, and loudly announced that he was not through with Mr. Christensen and that he would sue him. Mr. Christensen, prior to his employment, and subsequently, has been on the Internet advocating for the removal of city councilmen who intimidate building officials. The record does not reveal why, but it is clear that Mr. Christensen was a pistol with a hair-trigger, waiting for an elected official to pull it. He found that official in Mr. Blake. It was proved by clear and convincing evidence that Mr. Blake had a personal vendetta against Mr. Christensen and that he used his position as a City Councilman to try to intimidate him. It was proved by clear and convincing evidence that Mr. Blake used his position to ultimately effect his resignation. It was also proved that there were others in the community who desired to have Mr. Christensen's employment come to an end, and that in part, Mr. Blake was representing their interests in his efforts to have Mr. Christensen discharged.

Recommendation Based upon the Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Commission on Ethics issue a Final Order and Public Report finding that George Blake did not violate Section 112.313(6), Florida Statutes, and dismissing the complaint filed against him. DONE AND ENTERED this 25th day of January, 2006, in Tallahassee, Leon County, Florida. S HARRY L. HOOPER 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 25th day of January, 2006. COPIES FURNISHED: Linzie F. Bogan, Esquire Advocate for the Florida Commission on Ethics Office of the Attorney General The Capitol, Suite Plaza-01 Tallahassee, Florida 32399-1050 Kaye Starling, Agency Clerk Florida Commission on Ethics Post Office Drawer 15709 Tallahassee, Florida 32317-5709 George W. Blow, III, Esquire Law Offices of George W. Blow, III 106 White Avenue, Suite C Live Oak, Florida 32064 Bonnie J. Williams, Executive Director Florida Commission on Ethics Post Office Drawer 15709 Tallahassee, Florida 32317-5709 Philip C. Claypool, General Counsel Florida Commission on Ethics Post Office Drawer 15709 Tallahassee, Florida 32317-5709

Florida Laws (7) 104.31112.313112.317112.320112.322112.324120.57
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SPANISH OAKS OF CENTRAL FLORIDA, LLC vs LAKE REGION AUDUBON SOCIETY, INC., 05-004644F (2005)
Division of Administrative Hearings, Florida Filed:Tallahassee, Florida Dec. 20, 2005 Number: 05-004644F Latest Update: Jan. 09, 2009

The Issue The issue in this case is whether sanctions, including attorney's fees and costs, should be assessed against Respondent, the Lake Region Audubon Society, Inc. (LRAS), and awarded to Petitioner, Spanish Oaks of Central Florida, LLC (Spanish Oaks), under Sections 57.105, 120.569(2)(e), and 120.595(1), Florida Statutes,1 after LRAS unsuccessfully challenged the Southwest Florida Water Management District's (SWFWMD's) issuance of Environmental Resource Permit (ERP) Number 44025789.001 to Spanish Oaks.

Findings Of Fact LRAS' Amended Petition SWFWMD issued ERP 44025789.001 to Spanish Oaks on April 27, 2004. On May 11, 2005, Donna Stark, a member of LRAS, made a presentation to the LRAS board of directors asserting that Spanish Oaks was using one-to-three sinkholes to collect runoff water, instead of digging retention ponds, contrary to legal requirements and was polluting the underlying aquifer. She asked LRAS to consider filing an administrative challenge to the ERP. After the presentation, the LRAS board decided that its five-member Steering Committee--which took the place of a president, rotated responsibility for conducting board meetings, and functioned like an executive committee--would continue to investigate and make a decision as to what role LRAS should have in the future. The Steering Committee reviewed the information presented by Starks, decided to file a challenge, and invited Starks to help draft a Petition for Administrative Proceeding (LRAS Petition), which was signed by four members of the Steering Committee between May 31 and June 2, 2005, and was filed with SWFWMD on June 6, 2005. Because the timeliness of the LRAS Petition could not be ascertained from the allegations, SWFWD dismissed the Petition without prejudice. On July 11, 2005, an Amended Petition was filed, clarifying that LRAS was orally informed about the Spanish Oaks ERP by one of its members, later identified as Donna Stark, on May 10, 2005. The Amended Petition was signed by LRAS Steering Committee/Acting President Carrie Plair on July 6, 2005, and filed with SWFWMD, which determined that the Amended Petition was timely filed and substantially complied with the requirements for a petition and referred it to DOAH, where it was given DOAH case number 05-2606 and scheduled for a final hearing on September 22-23, 2005. The Amended Petition alleged in ¶5: The following evidence of the karst nature of the site is submitted: On February 3, 2005, in a meeting of Donna Stark, a member of [LRAS], with Sherry Windsor and biologist Jeff Whealton, the District personnel called in their geologist Tom Jackson for his professional opinion on this issue. Based on his training in karst geology and years of field observation at this site (prior to current ownership), Mr. Jackson referred to this structure as a fracture (an elongate sinkhole). Another individual who has graduate training in karst topography and who has studied this site for several years also has informed [LRAS] that this sinkhole has a vertical pipe and was an active "surface-to- ground water system" (Affidavit of Charles Cook - Ex. 8) Petitioners have consulted professionals who specialize in geological and geotechnical engineering and who are well recognized for their work in the state. Based on the available information they have expressed concern and have indicated that a thorough and detailed investigation consisting of geophysical and geotechnical methods should be performed to address the concerns of this Petition. Donna Stark, a member of [LRAS], observed first-hand the sinkhole in the southeast portion of Spanish Oaks collapsed during construction of the retention pond (perhaps due to heavy equipment or due to heavy rains of the fall 2004 hurricanes). Refer to Affidavit - Ex. 9. Paragraph 5. iv) of the Amended Petition continued and asserted that “[o]n November 13, 2004, LRAS member Donna Stark was informed by a man who had worked on the Spanish Oaks site [later identified as George Wilt] that the retention ponds were 30 feet deep.” It also asserted that LRAS member Donna Stark observed firsthand a sinkhole collapse that allegedly occurred in the southeast portion of Spanish Oaks site during construction of Retention Pond A. The Amended Petition alleged that on January 25, 2005, Donna Stark, along with a state employee (later identified as Timothy King), observed a "very large cone- shaped depression with smooth steeply-sloping sides – so steep that Donna Stark was nervous that the front-end loader driving up and down the slopes could end up in the aquifer if he lost traction in the loose unconsolidated sands. In the center of the depression was a lake perhaps 50 feet in diameter." The Amended Petition further alleged that “Donna Stark judged the distance from the top of the ground surface to the water surface to be about 15 feet.” It also asserted: "On February 4, 2005, Donna Stark went to the District office in Bartow to discuss this issue with the engineer in charge of the project, Sherry Windsor, biologist Jeff Whealton and geologist Tom Jackson. The engineering worksheet in the file shows a required depth of 6.5 feet from pond bottom elevation (136.5') to top of bank elevation (143.0')[.] It was suggested by one of the District scientists that the retention pond had collapsed during construction to create the observed depth. This is the only logical explanation in the opinion of Petitioner since [that would be a violation and grounds for revocation, as well very expensive, and would serve no useful purpose]." It also alleged that, "[w]hen Donna Stark returned on February 10, 2005, the area had been filled with sand to the required elevation and was flat-bottomed." On the clay core issue, paragraph 5. iv) of the Amended Petition alleged: "When Donna Stark spoke to William Hartmann, [SWFWMD] Surface Waters Regulation Manager, on April 21, 2005 he indicated that he had received no phone call from Permittee and that District staff had not inspected the clay core construction. At that time, the 'As-Built' inspection had been requested." The "Concise Statement of Ultimate Facts Alleged" included the statement: "Permittee also did not inform the District, as required, when (and if) a clay core was constructed in the berms. Serious impacts on adjacent property may be expected if the clay cores were not properly constructed." The Amended Petition in ¶6 alleged the following as disputed issues of material fact: the Permit allows construction of a retention pond in a sinkhole in the southeast portion of the site; construction of a retention pond in a sinkhole creates a danger to public health and safety; Spanish Oaks failed to notify SWFWMD that it was beginning construction of the clay cores of certain berms surrounding the retention ponds, as required by a permit condition so that SWFWMD could inspect during the construction; and Spanish Oaks failed to follow SWFWMD rules by neglecting to provide for permanent erosion control measures. LRAS’ Amended Petition asserted in ¶7. ii) that the Spanish Oaks development violated Florida Administrative Code Rule 62-522.300(1) and (3),2 which provided in pertinent part: (1) . . . [N]o installation shall directly or indirectly discharge into ground water any contaminant that causes a violation in the . . . criteria for receiving ground water as established in Chapter 62-520, F.A.C., except within a zone of discharge established by permit or rule pursuant to this chapter. * * * (3) Other discharges through wells or sinkholes that allow direct contact with Class G-I, Class F-I, or Class G-II ground water shall not be allowed a zone of discharge. It was alleged that this violation required reversal or modification of the proposed agency action. It was later revealed that the professionals referred to in paragraph 5. iii) of the Amended Petition included three engineers, one named Larry Madrid, and "many, many professionals of different government agencies." The attached "affidavit" (actually, an unsworn statement) of Charles Cook set out the basis of his knowledge of karst geology in general, and the Spanish Oaks site in particular, and his "conclusion that three depressional features existed on the subject parcel and I personally explored a subterranian [sic] void in a depressional sinkhole located in the southern part of the parcel in question, and believe it was an active recharge conduit connecting with subsurface aquifers." The attached "affidavit" (actually, an unsworn statement) of Donna Stark included the statement: "I hereby certify that the information submitted to [LRAS] concerning Spanish Oaks is true and accurate to the best of my knowledge." It also repeated some of the allegations in the Amended Petition and gave her "qualifying credentials for the above observations and interpretations" including: Ph.D. in Ecology from the University of Minnesota - 1971 with thesis title "Paleolimnology of Elk Lake, Itasca State Park, Northwestern Minnesota" Post-doctoral Research at Limnological Research Center, University of Minnesota 1972-1973 - published 1976 Science teaching at Southeastern College in Lakeland 1973-1974. Full Professor. The Amended Petition also was buttressed with citations cited to several scientific publications about karst geology, sinkholes, and stormwater retention ponds. It is clear that LRAS relied heavily on Donna Stark and her educational background and scientific knowledge, her alleged personal knowledge, and her alleged discussions with various professionals, including District personnel. Starks actually drafted almost all of the Petition and Amended Petition for the LRAS Steering Committee. Proceedings in Case 05-2606 LRAS was represented in Case 05-2606 by Paul Anderson, a member of LRAS' Steering Committee. By letter filed July 27, 2005, LRAS requested that the ALJ enter an order requiring a halt to all work on Spanish Oaks. On August 1, 2005, Spanish Oaks filed a Motion to Dismiss, or in the Alternative, Motion to Strike. The grounds were that there was no jurisdiction to enforce compliance with permit conditions, which the prayer for relief in the Amended Petition seemed to seek, and that allegations of non-compliance with ERP conditions should be stricken as irrelevant to issuance of the ERP. Discovery was initiated in Case 05-2606. In addition, in response to concerns expressed in the Amended Petition, Spanish Oaks hired Sonny Gulati, a professional engineer and expert in the field, to undertake a sinkhole investigation on the Spanish Oaks property using ground penetrating radar (GPR) and standard penetration testing (SPT). Mr. Gulati concluded that there were no active sinkholes on the site and prepared a report to that effect. Spanish Oaks presented the report to LRAS in August 2005; Spanish Oaks also served LRAS with a Motion for Attorney's Fees under Sections 57.105, 120.569(2)(e), and 120.595(1)(a-e), Florida Statutes (Motion), and informed LRAS that Spanish Oaks would file the Motion within 21 days if LRAS did not drop its opposition to the ERP. The Motion specifically alleged the impropriety of the sinkhole and clay core issues raised in the Amended Petition but did not mention the erosion control issue. LRAS' first attempt at discovery was defective in that its interrogatories and requests for production were directed to witness Tom Jackson instead of SWFWMD. SWFWMD moved for a protective order, which was granted on August 17, 2005. LRAS promptly served interrogatories and requests for production on SWFWMD and Spanish Oaks. Also on August 17, 2005, an Order was entered explaining to LRAS the procedure for obtaining qualified non- attorney representation, and an Order on Motion to Dismiss or Strike and Request for Stop-Work Order was entered. The latter Order recognized that the peculiar procedural posture of the case (namely, that LRAS' Amended Petition was timely even though it challenged an ERP purportedly issued in April 2004) contributed to the incorrect wording of LRAS' prayer for relief; placed a gloss on LRAS' prayer for relief as seeking denial, not revocation, of the ERP; and declined to strike allegations of non-compliance with the ERP, as they could be relevant to LRAS' challenge to the provision of reasonable assurance by Spanish Oaks. The stop-work request was denied for lack of jurisdiction to give injunctive relief in an enforcement matter. (Unbeknownst to the ALJ, on July 22, 2005, SWFWMD approved the transfer of the ERP to the operation phase, with responsibility for future operation and maintenance transferred to the Spanish Oaks of Central Florida Homeowners Association (HOA), notwithstanding the requirement of Section 120.569(2)(a), Florida Statutes, that SWFWMD take no further action on the ERP except as a party litigant.) By letter dated August 26, 2005, LRAS requested that Spanish Oaks allow its retained engineer to enter, inspect, and conduct investigations on the Spanish Oaks site. Spanish Oaks denied this request. At the end of August and in early September 2005, the parties exchanged hearing exhibits and witness lists in accordance with the Order of Pre-Hearing Instructions. When LRAS followed the procedure for obtaining approval of qualified, non-attorney representation by Mr. Anderson, Spanish Oaks objected to Mr. Anderson's qualifications. On September 7, 2005, an Order Authorizing Qualified Representation was entered. It recognized the short- comings in Mr. Anderson's qualifications, and the possibility that representation by a Florida attorney would benefit LRAS and make the proceeding fairer to all (including LRAS). Also on September 7, 2005, Spanish Oaks filed its Motion for Attorney's Fees under Sections 57.105, 120.569(2)(e), and 120.595(1)(a-e), Florida Statutes. Cf. Finding 14, supra. On September 12, 2005, LRAS filed a request for permission to add Mr. Madrid to its witness list. On September 14, 2005, an Order Denying, without Prejudice, Request to Add Witness was entered because the request did not indicate whether LRAS had conferred with the other parties. On September 15, 2005, Spanish Oaks filed a Response in Opposition to Request for Entry upon Land for Inspection and Other Purposes and Motion for Protective Order. Spanish Oaks asserted that it no longer had control over the retention ponds, which were controlled by the HOA, and that home construction was in progress, making timing and coordination of the request problematic, if not impossible. Spanish Oaks also asserted that, if the inspections were allowed, multiple issues would have to be addressed, including potential liability and insurance issues, and that more detail would be required to ensure that LRAS' inspection, which could include drilling sample borings in the retention ponds, would not compromise the integrity of the stormwater system and retention ponds. By letter dated September 19, 2005, LRAS requested that Spanish Oaks agree to the addition of Mr. Madrid as a witness. By another letter dated September 19, 2005, LRAS requested that Spanish Oaks produce back-up documentation supporting Mr. Gulati's sinkhole investigation report, including site maps of GPR test locations, the uninterpreted GPR raw data, the GPR strip charts, as well as the actual SPT soil borings, because LRAS' retained expert geologist, Marc Hurst, had advised LRAS that the information was necessary for him to determine the reliability of Mr. Gulati's report and conclusions. A telephone hearing was held on September 20, 2005, on LRAS' requests to add Mr. Madrid to its witness list, for Mr. Hurst to be allowed entry on the Spanish Oaks site to inspect and investigate, and for Mr. Hurst to be allowed to review the back-up documentation and SPT borings supporting Mr. Gulati's report. No party ever requested a continuance of the final hearing (set to begin in just two days), and the request to add Mr. Madrid as a witness was denied as too late. It is not known what Mr. Madrid's testimony would have been. LRAS dropped its request for entry on land in the face of the opposing arguments from Spanish Oaks. As to the back-up documentation supporting Mr. Gulati's report, Mr. Gulati was required to bring the documents to the final hearing but Spanish Oaks was not required to produce the SPT borings, which were represented to be numerous and a large quantity of soil. Immediately before the start of the final hearing, Spanish Oaks filed both a Motion in Limine, which was denied, and a Motion for Summary Recommended Order. Ruling on the pending motions was deferred. Spanish Oaks' Motion for Summary Recommended Order Motion was based on arguments that LRAS' filing of the Amended Petition was "ultra vires" and that LRAS had no standing. These issues (which ultimately were resolved in favor of LRAS and against Spanish Oaks) were the focus of much of the effort of Spanish Oaks in discovery and in the final hearing, as reflected in the Recommended Order in the case. Recommended and Final Orders in Case 05-2606 After the final hearing, Spanish Oaks filed a proposed recommended order suggesting that jurisdiction to rule on its Motion for Attorney's Fees under Sections 57.105, 120.569(2)(e), and 120.595(1)(a-e), Florida Statutes, should be retained. A Recommended Order that ERP 44025789.001 be issued to Spanish Oaks was entered in Case 05-2606 on November 10, 2005. Jurisdiction was retained to consider Spanish Oaks’ Motion for Attorney's Fees under Sections 57.105, 120.569(2)(e), and 120.595(1)(a-e), if renewed within 30 days after issuance of the final order. On November 30, 2006, SWFWMD entered a Final Order adopting the Recommended Order in its entirety and issuing ERP 44025789.001 to Spanish Oaks. As to the ERP criteria, the Recommended Order found in pertinent part: Alleged Sinkholes * * * Marc Hurst, a geologist who testified for LRAS, opined that Mr. Gulati’s sinkhole investigation was insufficient to demonstrate whether or not the Spanish Oaks retention ponds were constructed over sinkholes.11 However, Mr. Hurst offered no opinion as to whether the retention ponds are located over active sinkholes. Nor did Mr. Hurst specifically disagree with Mr. Gulati’s conclusion that the Spanish Oaks retention ponds have not been impacted by active sinkholes.12 To the contrary, Mr. Hurst admitted that the retention ponds were holding water on the day that he observed them--indicating that to him that the ponds were not acting as a strong conduit to the aquifer. Mr. Gulati also noted the significance of the presence of water in the ponds, stating that, if there were active sinkholes in the ponds, they would not hold water.13 EN. 11 - Notably, Mr. Hurst has only participated in four sinkhole investigations and reviewed the reports of approximately six other such investigations, while Mr. Gulati has conducted between 700 and 800 during the past ten years. EN. 12 - The anecdotal testimony of Charles Cook and Tom Jackson regarding their observations of depressions and “cracks” at the site several years earlier did not support a finding that there is an active sinkhole. Mr. Jackson, a geologist for SWFWMD, was not willing to draw such a conclusion. EN. 13 - Mr. Gulati acknowledged that, in areas where the aquifer is under artesian pressure, an active sinkhole will hold water. However, that aquifer condition does not exist in the vicinity of Spanish Oaks. T. 358. The only suggestion of any sinkhole- related damage to the retention ponds came from Donna Stark, who testified that George Wilt--a heavy equipment operator at the site incorrectly identified by Ms. Stark as “an employee of Spanish Oaks”--told her that there had been a sinkhole collapse during the excavation of Pond A. This hearsay testimony was directly contradicted by Mr. Wilt himself, who testified that he made no such statement. Despite the allegation in LRAS’ petition regarding observations of collapse of sinkhole by Donna Stark, Ms. Stark herself admitted at hearing that she did not witness any actual collapse. Rather, she testified that, on January 25, 2005, she saw what she believed to be the aftermath of a sinkhole collapse. Stark may have been confused by the amount of excavated material being stored on the ground surface around the pond. 43,906 cubic yards of dirt was excavated from Pond A alone and was stacked to a height of 8-10 feet higher than the natural ground elevation. Others who observed the site on January 25, 2005, saw no evidence of a sinkhole collapse. Tim King, a Florida Fish and Wildlife Conservation Commission employee who was with Ms. Stark on January 25, 2005, merely reported seeing pond excavation in process. Laura Howe, a SWFWMD employee who inspected the site on that date, observed that “[i]t appears depth of ponds are [p]robably close to permitted depth.” Moreover, Ms. Stark admits that, on February 10, 2005, she observed the ponds to be “[s]even and a half feet, or six and a half, whatever it should be.” Ms. Stark’s suggestion that the collapse was filled in between January 25 and February 10, 2005, is belied by testimony that repairing a sinkhole collapse of the size suggested by Ms. Stark would have required much more material than was available. (No dirt was imported onto the site.) The evidence admitted at hearing requires a finding that there was no sinkhole collapse onsite. Spanish Oaks provided reasonable assurance that the System was designed and constructed to include sufficient separation between the pond bottoms and the Floridan Aquifer to prevent groundwater contamination. Construction of Berms LRAS contended in its Amended Petition that Spanish Oaks failed to give notice prior to constructing clay cores in some of the berms onsite, as required as a condition of the ERP, and that this failure constituted failure to provide reasonable assurances.14 EN. 14 - The Amended Petition actually alleged that this was a permit condition violation requiring revocation of the ERP. However, it was ruled prehearing that "the Petitioner's request for revocation actually is a request for a final order denying Spanish Oaks' application for a permit" and that "the allegations of non- compliance with permit conditions should not be stricken but instead should be considered only as they might relate to Spanish Oaks' provision of required reasonable assurances for issuance of a permit." See Order on Motion to Dismiss or Strike and Request for Stop-Work Order, entered August 17, 2005. The interconnection of the three ponds that are part of the System will allow them to function as one pond, while a perimeter berm around the entire Spanish Oaks project will ensure that surface water runoff is retained onsite and directed toward the ponds. Ponds A and C are located, respectively, at the southeast and northeast corners of Spanish Oaks.15 The design plans submitted with the ERP application indicated that the berms alongside the eastern side of Ponds A and C are to include clay cores, a design feature that was included as a specific condition in the ERP. The purpose of the clay cores was to prevent offsite impacts caused by lateral movement of water. EN. 15 - Pond B is centrally located in the Spanish Oaks’ interior. The specific conditions of the ERP also required that Spanish Oaks notify SWFWMD's "Surface Water Regulation Manager, Bartow Permitting Department [William Hartmann], at least 48 hours prior to commencement of construction of the clay core, so that District staff may observe this construction activity." LRAS proved that Mr. Hartmann did not personally receive a phone call prior to the construction of the clay cores, as required by the ERP, and that SWFWMD staff did not observe the construction. Mr. Hartmann explained that this constituted a permit condition compliance issue which would prevent the ERP from being transferred to the operation phase until SWFWMD was assured that the clay core was, in fact, constructed as required. To confirm proper construction of the clay core, Spanish Oaks undertook soil borings. SWFWMD staff engineer Sherry Windsor was onsite to observe the soil borings. Spanish Oaks also submitted a report from its engineering consultant certifying that the clay cores had been properly constructed in accordance with the ERP. SWFWMD typically relies on a project engineer’s signed and sealed certifications of compliance matters. SWFWMD staff observations and the certification provided by the Spanish Oaks engineer satisfactorily resolved the issue of proper clay core construction. Failure to notify Mr. Hartmann prior to construction, as required by the ERP, does not undermine Spanish Oaks' provision of the necessary reasonable assurance for issuance of the ERP. Endnote 3 at Finding of Fact 4 in the Recommended Order in Case 05-2606 stated: "The Amended Petition also alleged that Spanish Oaks failed to follow SWFWMD rules by neglecting to provide for permanent erosion control measures, but no evidence was presented by LRAS on this issue, which appears to have been abandoned." As to the ERP criteria, the Recommended Order concluded in pertinent part: The applicable criteria for the issuance of a standard general ERP for the Spanish Oaks project are set forth in Rules 40D-4.301 and 40D-4.302, as well as SWFWMD's Basis of Review (BOR), which is made applicable pursuant to Rule 40D-4.301(3). LRAS’ challenge to the ERP alleges the presence of a sinkhole or a sinkhole collapse in one or more of the retention ponds for the Spanish Oaks subdivision, and the impact that such alleged sinkhole or sinkhole collapse would have on conditions for issuance relating to groundwater quality. LRAS’ case reflects a basic misperception of the permitting criteria applicable to surface water management system retention ponds. Section 6.4.1.b. of the BOR, which establishes specific design criteria for retention areas, requires as follows: Depth – The detention or retention area shall not be excavated to a depth that breaches an aquitard such that it would allow for lesser quality water to pass, either way, between the two systems. In those geographical areas of the District, where there is not an aquitard present, the depth of the pond shall not be excavated to within two (2) feet of the underlying limestone which is part of a drinking water aquifer. As found, the Spanish Oaks retention ponds comply with this criterion. LRAS also contends that the Spanish Oaks retention ponds violate Rule 62- 522.300, a rule which, in LRAS’ view, prohibits the location of a stormwater retention pond in or over a sinkhole. LRAS’ reading of the rule is incorrect. Rule 62- 522.300(1), with certain exceptions not relevant here, provides that no installation shall directly or indirectly discharge into ground water any contaminant that causes a violation in the . . . criteria for receiving ground water as established in Chapter 62-520, F.A.C., except within a zone of discharge established by permit or rule pursuant to this chapter. The purpose of a zone of discharge is to provide a mixing zone “extending to the base of the designated aquifer or aquifers, within which an opportunity for the treatment, mixture or dispersion of wastes into receiving ground water is afforded.” Fla. Admin. Code R. 62-520.200(23). No evidence introduced at hearing suggests that the surface water runoff that infiltrates through the bottom surfaces of the Spanish Oaks retention ponds, and then travels approximately 70 feet through soil before reaching the Floridan aquifer, will exceed applicable ground water criteria when it reaches the aquifer. For that reason, the Spanish Oaks retention ponds do not need a zone of discharge. Rule 62-522.300(3) provides that Other discharges through wells or sinkholes that allow direct contact with Class G-I, Class F-I, or Class G-II ground water shall not be allowed a zone of discharge. (Emphasis supplied). Classes F-1, G-1, and G-II groundwaters are designated for potable use and are located within an aquifer. Fla. Admin. Code R. 62-520.410. “Aquifer” is specifically defined as “a geologic formation, group of formations, or part of a formation capable of yielding a significant amount of ground water to wells, springs or surface water." Fla. Admin. Code R. 62- 520.200(2). Unless the alleged sinkholes allowed "direct contact" with the Floridan Aquifer, a zone of discharge would be permitted, assuming one were needed. No evidence introduced at hearing suggests that discharges from the retention ponds will come into direct contact with Class G-1, Class F-1, or Class G-II groundwaters. Instead, the discharges from the Spanish Oaks ponds only indirectly contact a drinking water aquifer, after infiltrating through tens of feet of separating soil layers. LRAS has not identified any applicable rule that prohibits the location of a retention pond in or over a relic sinkhole. Indeed, the record establishes that the presence of a sinkhole in or under a retention pond is problematic only if sinkhole activity affects the approved design of the retention pond. See Findings 47 and 49, supra. LRAS’s assertion of a sinkhole collapse at Spanish Oaks during the time frame alleged is contrary to the greater weight of the evidence, which established that the ponds have been constructed and are operating as designed and that there is no active sinkhole on the Spanish Oaks site that adversely affects the quality of receiving waters such that state water quality standards would be violated, or that otherwise affects Spanish Oaks’ ability to provide reasonable assurance of meeting applicable permitting conditions. LRAS offered no evidence to establish that water percolating through the Spanish Oaks retention ponds will come into direct contact with a drinking water aquifer or that a state water quality standard would be violated by the project. The greater weight of the evidence established that the Spanish Oaks retention ponds comply with the applicable construction requirement as stated in BOR Section 6.4.1.b. There is more than sufficient soil underlying the Spanish Oaks retention ponds to assure compliance with this requirement. As found, Spanish Oaks' failure to notify Mr. Hartmann before beginning construction of the clay core berm does not prevent Spanish Oaks from providing reasonable assurance that permit criteria will be met. As a result, Spanish Oaks has met its burden of proof and persuasion that all conditions for issuance of the permit have been satisfied and that it is entitled to the requested ERP. As suggested in the proposed recommended order filed by Spanish Oaks in Case 05-2606, the Recommended Order retained jurisdiction to consider Spanish Oaks’ Motion for Attorney's Fees under Sections 57.105, 120.569(2)(e), and 120.595(1)(a-e), if renewed within 30 days after issuance of the final order. Spanish Oaks "renewed" the motion by filing its Petition in this case. SWFWMD's Final Order adopted the Recommended Order in its entirety. Petition in Case 05-4644F The Petition in this case asserts essentially that LRAS had no competent substantial evidence: that there was an active sinkhole under the retention ponds on the Spanish Oaks site; that the required clay core was not installed; or that erosion control measures were not used. As to the sinkhole allegations, Spanish Oaks asserts that, even if there were a reasonable basis for filing the Amended Petition in Case 05- 2606, it should have been withdrawn upon receipt of Mr. Gulati's report and Spanish Oaks' Motion for Attorney's Fees under Sections 57.105, 120.569(2)(e), and 120.595(1)(a-e), Florida Statutes. As indicated in the findings of fact and conclusions of law in Case 05-2606, Donna Stark and Charles Cook did not testify precisely as LRAS had been led to believe from their "affidavits" in the Amended Petition that they would. Likewise, the testimony of Timothy King and George Wilt was not supportive of Donna Stark's "affidavit" as to a sinkhole collapse during construction on the site, or her testimony as to Mr. Wilt's statements to her. The testimony of Tom Jackson and Charles Cook also did not completely support Donna Stark's "affidavit" as to the existence of sinkholes on the site. But while the use of "discovery" to establish the testimony of those individuals before the hearing certainly might have alerted LRAS to problems with the "affidavits" it was relying on, it was not incumbent on LRAS to undertake such "discovery" in order to avoid sanctions. It is not found that LRAS's prosecution of its Amended Petition in reliance on those "affidavits" was frivolous, for an improper purpose, or to needlessly increase the costs to Spanish Oaks of having its ERP approved. LRAS' prosecution of the Amended Petition after receiving Mr. Gulati's report and notice of Spanish Oaks' intention to file its Motion for Attorney's Fees under Sections 57.105, 120.569(2)(e), and 120.595(1)(a-e), Florida Statutes, also was not proved to be frivolous, for an improper purpose, or to needlessly increase the costs to Spanish Oaks of having its ERP approved. LRAS attempted to follow up on Mr. Gulati's report so as to enable its retained expert, Mr. Hurst, to verify whether it should be accepted as conclusive proof of the hydrogeology of the site, and perhaps assure LRAS that its Amended Petition could be withdrawn, but LRAS' attempts were unsuccessful. As a result, LRAS was left to presentation of Mr. Hurst's testimony based on the information he had. Mr. Hurst testified to the likely existence of at least three sinkholes at the site. He based this testimony on his knowledge of the area's stratigraphy, aerial photographs and topographical maps showing unexplained surface depressions, and evidence reported in Mr. Gulati's report. In addition, there are two documented sinkholes in the "immediate vicinity" of the site and about a dozen more within two-to-three miles. Based upon his review of all of the pertinent data, Mr. Hurst testified that the surface depressions on the site probably are part of a "lineament"--i.e., a fracture in the limestone formation below the earth's surface along which sinkholes tend to form. While he was unable to testify that an active sinkhole existed at the site, he maintained that the information presented to him was insufficient to disprove the existence of an active sinkhole at the site. He also testified to his opinion that relic sinkholes probably existed under the retention ponds. As found in the Recommended Order in Case 05- 2606: A relic sinkhole, as contrasted to an active sinkhole, has either been sealed or has self-sealed, so that there is no connection between the sinkhole and the underlying aquifer. An active sinkhole provides a direct connection--referred to by both LRAS’ and Spanish Oaks' experts as a “good communication”--between the surface and the aquifer. Mr. Hurst testified that, even if no active sinkhole existed at the site, the likely relic sinkholes made it more likely that active sinkholes would open there and create a direct conduit to the aquifer. At the final hearing and in its proposed recommended order in Case 05-2606, LRAS argued that the Spanish Oaks retention ponds violated Rule 62-522.300, even if they were not constructed over active sinkholes but rather only over relic sinkholes. As concluded in the Recommended Order and Final Order in Case 05-2606, such an interpretation of the Rule would be "incorrect" and a "misperception." But LRAS' primary argument was that Spanish Oaks did not provide reasonable assurance that there were not active sinkholes at the site, and the "fall-back" argument was not unreasonable to make based primarily on Mr. Hurst's testimony. The Petition also asserted that LRAS had no evidence in support of its allegation that the required clay core was not installed, or that required erosion control measures were not provided. But facts supported a finding that Spanish Oaks did not notify SWFWMD, as required, which was ruled to be relevant to the provision of reasonable assurance in general, and the erosion control issue was a minor feature of the Amended Petition, and the Motion for Attorney's Fees under Sections 57.105, 120.569(2)(e), and 120.595(1)(a-e), Florida Statutes, filed in Case 05-2606 did not mention it. Evidence was presented during the final hearing in Case 05-2606 that the challenge in LRAS' Petition and Amended Petition was virtually identical to a challenge to Spanish Oaks' ERP that was filed by Donna Starks on behalf of her not-for- profit corporation, Central Florida EcoTours, in early May 2005 but was time-barred and dismissed because Starks and Ecotours received mailed notice of the issuance of the ERP to Spanish Oaks on April 27, 2004. Spanish Oaks implied during the final hearing in Case No. 05-2606 that Donna Starks told LRAS about the fate of the EcoTours challenge and asked LRAS to file its Petition and Amended Petition at her behest to block the Spanish Oaks development for leverage to accomplish her ulterior motive- -namely, purchase of the property by EcoTours. But those allegations were denied by LRAS and were not proven during the hearing in Case 05-2606.

Florida Laws (7) 120.52120.56120.569120.57120.595120.6857.105
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ANDY D. ANDREWS, D/B/A A. D. ANDREWS NURSERY vs P. S. L. LANDSCAPE SERVICES, INC. AND CUMBERLAND CASUALTY AND SURETY COMPANY, 02-000215 (2002)
Division of Administrative Hearings, Florida Filed:Tallahassee, Florida Jan. 14, 2002 Number: 02-000215 Latest Update: Jun. 18, 2002

The Issue Is Petitioner entitled to compensation for the sale of agricultural products, and, if so, how much?

Findings Of Fact On or about August 28, 2001, Petitioner sold F.O.B. (Free on Board) at Petitioner's farm to P.S.L. Landscape Services Inc. (hereafter, PSL), 16 Crepe Myrtle trees 14 feet tall and 5 Live Oak trees 2.5 -3.0 inches in Diameter Breast High for a total costs, including tax, of $4,208.20. These trees were dug and wrapped in accordance with the standards of the American Association of Nurseryman in the afternoon of August 30, 2001. The tree roots balls were 40 inches in diameter, and the root balls were placed in wire baskets lined with burlap. The trees were placed upon a flatbed truck with the tops of the trees resting on a rack, and the entirety of the trees, except the roots, covered with a plastic screening material used for this purpose to keep the leaves from becoming wind burned in transit. The trees were transported overnight to PSL where they were received Broward County the following morning at 8:00 a.m. The trees were received and signed for by a representative of PSL, Randy Smith. The documents accompanying the shipment were introduced as part of Petitioner's Composite Exhibit 1. The first of these documents signed by Smith states: Attention: We do not replace trees. If trees are not in satisfactory condition when received, do not accept them. So please take care of your trees. Refer to watering guide in our catalog. The second document signed by Smith provides in bold type at the bottom of the page: DO NOT REFUSE TO UNLOAD THE TRUCK. If there is a serious problem and you question the merchandise, call our office immediately. Our number is 352 493 2496. PSL provided the freight company two checks, one to the freight handler for the freight and the other for 4,208.20 to Petitioner. This check was delivered to the Petitioner by the freight company and deposited by the Petitioner in due course. The Petitioner was notified several days later that a stop payment order had been received on the check for $4,208.20 by PSL. This was the first time the Petitioner was aware of a problem with the merchandise. PSL had not contacted the Petitioner about any problem with the shipment. When Mr. George Kijewski of PSL was contacted regarding the stop payment order, he responded that the trees had wilted. He wrote a letter dated December 21, 2001, to the Department of Agriculture in which he stated: Our firm ordered material from A.D. Andrews Nursery for one of our projects. Two Live Oaks were not number one as ordered. The Crepe Myrtle came in bone dry, not wet as the nursery states. The nursery dug up the plant material ordered and left items in the field until they were loaded onto truck for delivery. They never went to holding area prior to loading to get watered or hardened off. When we got them they were wilting . . . [.] Mr. Deming was present when the trees were prepared. Mr. Kijewski was not present when the trees were prepared. Mr. Deming described the manner in which the trees were dug, prepared for shipment, and shipped. The Crepe Myrtles were dug using a tree spade; the root balls were placed in burlap- lined wire baskets; and the trees placed on the trailer bed where they were secured and covered with a plastic screen to protect them from wind in transit. The Oaks were handled in a similar manner. The trees were not watered; however, the area had received approximately 1.5 inches of water in the seven days prior to shipment. The roots were wet enough to cause the burlap to be damp. The shipping documents do not reflect any wilting or problems although the documents, as quoted above, advised that product should not be received if not in good shape. No notes were made upon receipt reflecting the alleged poor condition of the trees. The trees were sold F.O.B. at Chiefland, and were the property of PSL when loaded.

Recommendation Based upon the foregoing findings of fact and conclusions of law, it is RECOMMENDED: That the Department enter a final order adopting these findings and conclusions of law, directing PSL to pay to Petitioner $4,208.20 within 14 days of receipt of its final order; and, if PSL fails to abide by the Department's order, directing the surety to make good on its bond in the amount of $4,208.20. DONE AND ENTERED this 30th day of April, 2002, 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 30th day of April, 2002. COPIES FURNISHED: Andy D. Andrews A. D. Andrews Nursery Post Office Box 1126 Chiefland, Florida 32644 Brenda D. Hyatt, Bureau Chief Department of Agriculture 541 East Tennessee Street Tallahassee, Florida 32308 George Kijewski P.S.L. Landscaping Services, Inc. Post Office Box 9421 Port St. Lucie, Florida 34985 Deborah A. Meek Cumberland Casualty & Surety Company 4311 West Waters Avenue Suite 401 Tampa, Florida 33614

Florida Laws (7) 672.103672.105672.201672.401672.602672.606672.710
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CHARLES H. GRIFFIN vs ST. JOHNS RIVER WATER MANAGEMENT DISTRICT, 98-000818 (1998)
Division of Administrative Hearings, Florida Filed:Orlando, Florida Feb. 19, 1998 Number: 98-000818 Latest Update: Jul. 12, 2004

The Issue Live Oak Plantation No. 1, Ltd. (Live Oak) through Stanford Development Group filed application number 4-117-0464AC-ERP with the St. Johns River Water Management District (SJRWMD) in April 1997, seeking a conceptual approval environmental resource permit. After SJRWMD issued its notice of intent to grant the permit, the Petitioners filed their petitions challenging the intended agency action. The central issue in this proceeding is whether the permit should be issued pursuant to Chapter 373, Florida Statutes, and Chapters 40C-4, 40C-41 and 40C-42, Florida Administrative Code, including specific provisions of the Applicant's Handbook adopted by rule and identified in the parties' prehearing stipulation filed July 8, 1998.

Findings Of Fact The Parties Michael D. Rich is a former resident of Seminole County who lived on the property contiguous to the Live Oak site. He is the legal representative of his mother who still resides on the property and he is president of C-RED. C-RED is a Florida non-for-profit corporation with members from the City of Oviedo and unincorporated areas of Seminole County who are interested in assuring that development is done without improper impact on the taxpayers and the rural character of the area. Mr. Griffin is a resident of Seminole County living on Horseshoe Lake, which adjoins the Live Oak site. Live Oak is a Florida Limited Partnership which intends to develop the project that is the subject of this proceeding. SJRWMD is a special taxing district created by Chapter 373, Florida Statutes, and charged with responsibility for various permitting programs, including the one at issue here. The Project Live Oak proposes to develop a large multi-phased single family project with two small commercial sites. The project, to be known as "Live Oak Reserve," will be on approximately 1,041 acres on the south side of county road 419 in southeastern Seminole County in the City of Oviedo. The project site is located near the confluence of the Econlockhatchee River (Econ River) and Little Econlockhatchee River. The Live Oak Reserve property includes approximately half of Horseshoe Lake, as well as a small creek, Brister Creek, which flows from Horseshoe Lake across the property to the Econ River. The Econ River, a class III water and designated an Outstanding Florida Water (OFW), crosses the southwestern corner of the Live Oak Reserve property. The Econ River is the receiving water body of Live Oak Reserve. The Live Oak Reserve property is located within the Econlockhatchee River Hydrologic Basin. A portion of the Live Oak Reserve property lies within the Econlockhatchee River Riparian Habitat Protection Zone (RHPZ). The Live Oak property lies within a 1,500 acre drainage basin; approximately 450 acres off-site drain through Live Oak Reserve. Horseshoe Lake has approximately 500 acres that drain through it, then through the wetlands and into the Econ River. Historically, the Live Oak Reserve property has been used for agricultural practices, including siliviculture and cattle production. Some areas of the property have been logged and some areas have been converted to pasture. Cattle have grazed in wetlands, thereby decreasing the amount and diversity of groundcover vegetation on portions of the property. Additionally, on-site drainage ditches have had a major impact on the hydrological characteristics of the wetlands on the property, including the reduction of surface water elevations. The Live Oak Reserve property is currently vacant and undeveloped. The Application Process In April 1997, Live Oak submitted to the SJRWMD an Environmental Resource Permit Application, N4-117-0464AC-ERP, for conceptual approval of a master stormwater and floodplain management system for the development of Live Oak Reserve. A conceptual permit is utilized in complex multi-phased projects which are expected to have a longer build-out period than a single phase project. A conceptual permit does not allow any construction activity, but provides the outline for final engineering calculations and construction drawings. Further permits are required before any sitework or construction is undertaken. In conjunction with its permit application Live Oak submitted detailed technical information, including but not limited to charts, maps, calculations, studies, analyses and reports necessary to show that the conceptual development plan was consistent with the permitting criteria of the SJRWMD found in Chapter 40C-4, Florida Administrative Code, and the Applicant's Handbook. The master plan for the Live Oak project was designed by Donald W. McIntosh Associates, Inc.(McIntosh) using input from: (a) land planners who were required to consider issues related to the comprehensive plans, open space requirements and related issues; (b) landscape architects who were responsible for the proposed park systems and landscape treatments throughout the project; (c) geotechnical engineers responsible for evaluating the soil and groundwater conditions; and (d) environmental consultants, Modica and Associates, who were responsible for wetland delineation and flagging and wildlife surveys. The first version of the Live Oak Reserve site plan prepared for the project by McIntosh included development of all upland areas and filling several portions of the mixed forested wetlands to maximize lot yield. This included development of the upland adjacent to the Econ River and development of an upland parcel on the west side of the river. After much consideration and revision by the developer and its consultants, a site plan was developed which minimizes impacts to wetlands and other surface water functions, particularly as it relates to the Econ river, and maximizes the benefits to wildlife by establishing a series of wildfire corridors across the site. The final plan submitted to the SJRWMD at the time of the application includes the preservation of the entire Econ River floodplain and two adjacent developable upland areas, a large mixed hardwood forested wetland which traverses the site from the northeast to the southwest, and upland and wetland areas in the southern portion of the site that provide a corridor between a large undeveloped parcel to the east and the Econ River to the west. After submission of its application, Live Oak participated in a review process with SJRWMD staff to further eliminate and reduce wetland impacts. Specifically, SJRWMD requested changes to the site plan which included reductions in impacts to various wetlands and additional buffers to other wetlands. Several changes to the site plan were made to accommodate the SJRWMD's concerns relating to reducing impacts to wildlife, particularly the Florida sandhill crane. The reductions in wetland impacts and other design changes resulted in a revised site plan which the SJRWMD staff recommended to the district's governing board for approval. The staff recommendation of approval, with associated conditions, is set forth in Technical Staff Report dated February 10, 1998. On July 14 and 16, 1998, the SJRWMD revised the technical staff report to reflect changes to the project design and mitigation plan, as well as to add conditions inadvertently omitted from the earlier technical staff report. Condition no. 8 was mistakenly added to the July 16 technical staff report and by stipulation of all the parties, this condition was removed from the technical staff report. (See transcript, page 521) Stormwater Analysis McIntosh utilized information from different sources in preparing the stormwater calculations submitted to the SJRWMD. The developer provided information regarding proposed lot sizes and types so as to determine the impervious surface area for developable lots. The geotechnical consultants, Universal Engineering Sciences, (Universal) provided McIntosh with preliminary, interim, and final geotechnical reports, soil boring logs, and groundwater table estimates. The input from Universal primarily involved the establishment of seasonal high and seasonal low groundwater elevations for the pre-development and post-development conditions on the site. The estimated seasonal high and seasonal low groundwater levels refer to the range of levels the groundwater is expected to attain on the site during the wetter (high) and dryer (low) periods of a normal year. These elevations were then utilized in the stormwater calculations prepared by McIntosh. Topography on Live Oak Reserve consists of elevations ranging from 48 feet to 25 feet NGVD. In its pre-development condition, Live Oak Reserve has 6 distinct drainage patterns. Off-site drainage basins also contribute runoff to the property. The conceptual post-development design will modify the project's on-site drainage patterns into 28 drainage basins. At the request of the SJRWMD, Live Oak prepared seasonal high and seasonal low groundwater elevation contour maps. Live Oak performed approximately 200 borings on the Live Oak Reserve property. From the borings, Live Oak determined the soil types present and the existing groundwater elevations. Live Oak also used the borings to assist in establishing the estimated seasonal groundwater elevations. With the exception of several shallow borings in wetland areas, all borings were taken by split spoon sampling. Seventy-nine piezometers were installed next to bore holes to measure groundwater levels. In establishing the seasonal high groundwater levels, Live Oak evaluated the groundwater level at the time of boring; the time of year the groundwater level was measured; the time span of the investigation and its relationship to normal rainfall patterns; soil indicators such as coloration, mottling, and particle size; site specific topography; USGS quadrangle maps depicting site topography; Soil Conservation Service (NSCS) estimates of the expected seasonal high groundwater levels; and vegetative indicators. It is not essential to evaluate rainfall data when determining the seasonal water levels because the historical seasonal water levels are recorded in the soils. The estimated seasonal high groundwater level can be determined during the dry season. The range of the estimated seasonal high groundwater level on the Live Oak Reserve property is from standing water on the ground to five feet below the existing grade. In evaluating Live Oaks estimated seasonal groundwater levels, the District reviewed Live Oak's submittals, and also reviewed the NSCS soil survey to confirm that the estimated seasonal groundwater levels were reasonable. Wetland seasonal surface water levels were estimated using biological indicators such as lichen lines, buttressing, water lines, and sand lines. Lichen lines were apparent on the Live Oak Reserve properly and reflective of normal rainfall conditions. Seasonal high water levels are expected at the end of September. Seasonal low water levels are expected in May. The wetland surface water levels encountered in January 1997, when the seasonal levels were estimated, were neither exceptionally low nor exceptionally high. The water levels were representative of a period of normal rainfall. Water quantity attenuation and stormwater treatment will be accomplished through wet detention ponds and vegetative natural buffers. Due to the location of Live Oak Reserve in the Econlockhatchee River Hydrologic Basin, special basin criteria apply this project. The special basin criteria, also known as the "Econ Rule," is more stringent than the stormwater management criteria set forth in Applicant's Handbook sections 9 and 10. The special basin criteria, as it relates to the surface water management systems, requires Live Oak to control its discharge from two design storms: the mean-annual design storm, and the 25-year, 24-hour design storm. A design storm is a hypothetical storm with a predetermined rainfall amount, a predetermined intensity and 24 hour-duration. Designing the system to control the peak discharge during the mean-annual storm will prevent erosive velocities that would be harmful to Brister Creek and the Econ River. The conceptually proposed system is designed to limit peak rates of discharge to those of pre-development for the mean-annual and the 25-year, 24-hour design storm events. The system, as conceptually proposed, will limit post-development discharge rates to the same as or lower than the pre-development discharge rates. Each stormwater management area will pre-treat its respective post-development basin's pollution volume prior to discharge downstream. Live Oak proposes to use vegetative natural buffers for a portion of the rear lots within the post- development condition to fulfill treatment requirements. Live Oak Reserve is designed for the retention of the first inch of runoff from the total area of the post-development basins or the total runoff from 2.5 inches times the post- development basin's impervious area, whichever is greater. Furthermore, because Live Oak Reserve conceptually discharges to the Econ River, an OFW, the system is designed to provide an additional 50 percent of treatment. For discharges to an OFW the system must treat to a 95 percent removal standard. The outfall structures within each wet detention system are designed to draw down one-half the required treatment volume between 60 to 72 hours following storm event, but no more than one-half of this volume will be discharged within the first 60 hours. Each wet detention pond is designed with a permanent pool with a 31.5-day residence time during the wet season. Residence time is the time that the water within a pond will stay in the pond prior to discharge. The residence time includes the 14-day residence time required of all wet detention systems, an additional 50 percent residence time (7 days) for discharging into an OFW, for a total of 21 days. In addition, each system has been designed to provide an additional 50 percent residence time (10.5 days) because Live Oak has elected not to plant littoral shelves within each pond. As conceptually designed, Live Oak reserve's post- development drainage pattern will have no effect on the drainage patterns of Lake Eva or Horseshoe Lake. As conceptually designed, Live Oak Reserve's post-development drainage pattern will reduce the rate of flow during the storm events, which is a positive effect on the drainage pattern of Brister Creek. The reduction in flow velocity reduces the erosiveness of the storm. Live Oak has demonstrated that the 25-year and 100- year, 24-hour storm events' post-development peak stages for Lake Eva and Horseshoe Lake are not changed as a result of this conceptual project. Based upon Live Oak's calculations, the Live Oak Reserve project will not cause any restriction to the flow of water as it outfalls from Horseshoe Lake to Brister Creek. The conceptual wet detention systems within Live Oak Reserve are proposed to have a maximum depth of 12 feet. However, Live Oak requested consideration at the time of final engineering for each phase of development to maximize selected stormwater management areas for maximum depths of up to 25 feet. That consideration will be made in subsequent application review and is also subject to the City of Oviedo's approval. The conceptual wet detention ponds are designed with an average length to width ratio of two to one, and are configured to minimize the occurrence of short circuiting. As such, they will meet the criteria of the applicable rules. Tailwater conditions for the project were based on published flood elevations. Live Oak analyzed the tailwater condition for the mean-annual, 25-year 24-hour, and the 100-year 24-hour design storms. Live Oak completed a 100-year flow analysis for Live Oak reserve. Pre-development floodplain elevations for Lake Eva, Horseshoe Lake, and the Econ River were referenced from previous studies (Seminole County) and the Federal Emergency Management Agency. Live Oak determined that the 100-year floodplain elevations effecting Live Oak Reserve to be 40.2 feet NGVD from Horseshoe Lake, 45.0 feet NGVD for Lake Eva, and 32.5 feet NGVD for the Econlockhatchee. The U.S. Geological Survey (USGS) has produced a map of flood prone areas which indicates that the elevation delineating the flood prone area for Horseshoe Lake is 40.14, not 40.2, and for Lake Eva is 43.38, not 45.0. Therefore, the area indicated by USGS as the flood prone area is included in the 100-year floodplain analysis of Live Oak. Live Oak, in its conceptual design, has demonstrated that it will provide compensating storage for any encroachments into the 100-year floodplain. Live Oak has conceptually proposed to fill approximately 18.69 acre- feet within the 100-year floodplain. Live Oak will compensate the filling of the floodplain by providing a cut with the 100-year floodplain of approximately 27.09 acre-feet. By meeting the criteria in the "Econ Rule" the project conceptually meets all other relevant standards for stormwater management as the basin rule is more stringent. Live Oak has provided reasonable assurance that the development will not affect surrounding property or raise stagewater elevations of any surrounding property; the development will not displace the 100- year flood plain area; and the development will not restrict or impede the natural flow from Horseshoe Lake. Wetland and Wildlife Impacts Approximately 430 acres of wetlands cover the project site. Two general types of wetlands on found on the Live Oak reserve property: herbaceous wetlands and forested wetlands. Twenty-three herbaceous wetlands are classified as freshwater marshes. These wetlands range in size from 0.2 acre to over 8 acres. Wetlands 10 and 16, the largest on the property, are mixed hardwood forested wetlands. Approximately 525 acres of the Live Oak Reserve property are located within the RHPZ. Of this area, approximately 410.5 acres are wetlands, and the remainder are uplands that are predominantly pine flatwoods and xeric scrub. A few of the wetlands on site are considered RHPZ wetlands, not "isolated," solely because they are connected to floodplain wetlands by ditches. These wetlands and 50 feet of the uplands surrounding them are considered part of the RHPZ. The wetlands within the RHPZ are intact with little disturbance, especially in the Econ River corridor that is a part of wetland 16. Wetland 10 has been logged and the species composition in that wetland has changed. Wetlands 12 and 14 have ditch connections to the Econ River, but these ditch connections do not appear to have adversely impacted the wetlands hydrologically. Wetlands 2,3, and 8 have ditch connections to the Econ River. These wetlands have been adversely affected (drained) by the ditching. The RHPZ uplands are in good condition and provide very valuable habitat, except for 12 acres that are adjacent to upland cut drainage ditches. These 12 acres have no habitat value. The portion of the Live Oak Reserve property within the RHPZ provides good habitat important to fish and wildlife, and is part of the Econ River floodplain. The upland areas outside the RHPZ on the Live Oak Reserve property primarily consist of pine flatwoods and pasture. The pine flatwoods have been logged and are overgrown. The pasture appears to have been cleared many years ago and planted with bahia grass. Twenty-two isolated wetlands, which total approximately 17.9 acres, are located on the Live Oak reserve property. The isolated wetlands are intact and in good condition, except for temporary impacts due to cattle grazing and logging. The isolated wetlands provide habitat for wading birds, frogs, toads, and other wildlife. Ephemeral wetlands are wetlands that are seasonally inundated, but not necessarily inundated every year. Ephemeral wetlands provide important functions to wildlife, including gopher frogs and other amphibians for breeding, wading birds and sandhill cranes for foraging, and invertebrates. Ephemeral wetlands or "seasonal" wetlands occur on the Live Oak Reserve property. Although Live Oak did not separately address any of the wetlands as ephemeral, the value and functions of ephemeral wetlands were assessed by SJRWMD staff-person, David Eunice. While several small ephemeral wetlands are being impacted by the proposed development, several others are being preserved. Live Oak conducted wildlife surveys of the Live Oak Reserve property in accordance with the Florida Game and Fresh Water Fish Commission's approved Wildlife Methodology Guidelines. Based on the surveys, Live Oak determined that three listed species occurred on-site: the Florida sandhill crane, the gopher tortoise, and the Sherman's fox squirrel. The Florida sandhill crane is a threatened species. Live Oak found no evidence that the property hosts Florida panthers. Although the wildlife surveys did not identify gopher frogs, a species of special concern, the SJRWMD recognized the potential for the gopher frog to use the wetlands, including the ephemeral or seasonal wetlands, on the Live Oak Reserve property. Florida sandhill cranes have been observed foraging in a few areas on the Live Oak reserve property. In the spring of 1997, Live Oak identified two active nests in freshwater marshes (wetlands 21 and 29). There is no evidence that the sandhill cranes are currently nesting in wetland 29; however, Florida sandhill crane nests have been located in wetlands 14 and 21 this year. The typical critical nesting habitat for Florida sandhill cranes is a large, isolated marsh, generally either dominated by maidencane or pickerel weed. The marsh must maintain a surface water level between 12 and 24 inches so that the birds can construct a suitable nesting platform in the marsh. Nesting success, in part, depends upon wetland type used and water depths. The Florida sandhill crane also requires a certain amount of pasture-like upland habitat in which to forage. However, the crane forages in both uplands and wetland. Upland pasture is the sandhill crane's preferred foraging habitat. The sandhill crane's second most preferred foraging habitat is freshwater marsh. When the sandhill cranes have chicks and fledglings, the birds forage in the wetlands. After a period of three to four months, the juvenile and adult sandhill cranes will move to open pasture to forage. The Econ River floodplain wetlands and their associated upland habitats on the Live Oak reserve property are regionally ecologically significant. Overall, the Live Oak Reserve property provides good ecological value. It is part of the river corridor, has a tributary that runs through it and has uplands that have had little disturbance. Live Oak has eliminated certain wetland impacts and reduced others during the design of the Live Oak Reserve project. Live Oak eliminated some road crossings, and redesigned the pond configuration to eliminate or reduce encroachments into wetlands. Live Oak's site plan that was submitted as part of the initial April 14, 1997, application reflects Live Oak's initial attempts to eliminate or reduce impacts. Live Oak, in its application, proposed a project design with 46 acres of wetland impacts. The site plan has changed since Live Oak made the initial application to the SJRWMD. The initial project design called for the removal of the southern one-half of wetland 29 for the construction of a stormwater pond. Live Oak redesigned the project to preserve wetland 29 with a 50-foot upland buffer around it to eliminate direct impacts to the sandhill cranes nesting there. Live Oak further reduced impacts by preserving wetlands 14 and 15, and by placing upland buffers around them to protect sandhill crane habitat. The revised design of the surface water management system reduced wetland impacts by approximately 7 acres. The SJRWMD February 10, 1998, technical staff report includes the design plans reducing impacts by 7 acres. After the SJRWMD issued its February 10, 1998, technical staff report, Live Oak once again redesigned the project to preserve wetland 12. This redesign reduced wetland impacts by an additional 3 acres. In this case, SJRWMD staff worked with Live Oak to reduce or eliminate its impacts. Nonetheless, staff believed Live Oak's proposed mitigation qualified for the exception under Section 12.2.1.2b, that is, the on-site preservation of the Econ River floodplain and associated uplands, in concert with Live Oak's contribution to acquiring a conservation easement over the Yarborough parcel, discussed below, provides regional ecological value and provides greater long term ecological value then the areas impacted. Live Oak proposes practicable design alternatives, but it is not required to reduce or eliminate all impacts. Some design alternatives, such as whether to use a bridge or culverts for the Brister Creek crossing, must be addressed and considered at a later permit application stage and not at this conceptual permit stage. The proposed design includes dredging or filling of approximately 35.9 acres of wetlands and construction in approximately 38 acres of RHPZ uplands. Of these 35 wetlands on the Live Oak Reserve property, Live Oak will completely impact 23 of the wetlands (17.64 acres of wetland impact); partially impact 5 wetlands (18.28 acres of wetland impacts out of 370.15 acres of wetlands); and will avoid impacts to 7 wetlands (40.63 acres). The impacts are mostly limited to the small isolated wetlands, the upland/wetland transitional edges of the floodplain wetlands, and portions of RHPZ already degraded by a ranch roadway and ditch placement. Live Oak focused its impacts on areas, including wetlands, that were historically disturbed. SJRWMD staff considered that the isolated wetlands less than 0.5 acre were used by sandhill cranes and other threatened or endangered species. Therefore, staff required Live Oak to offset impacts to the small isolated wetlands. In addition to physical impacts to wetlands and RHPZ, the habitation of the proposed subdivision, which will result in noise and intrusion into wildlife habitat by humans and their pets, will cause secondary impacts. Those secondary impacts are offset in part by the upland buffers proposed by the applicant (a total of 10 acres of 25 foot buffers and 47.86 acres of 50- foot buffers.) After considering the type of impact proposed; past, present and future activities that may occur in the Econ River Hydrologic Basin; and that Live Oak off-site mitigation of adverse impacts is located within the same hydrologic basin; SJRWMD staff appropriately determined that Live Oak Reserve would not have an adverse cumulative impact. Mitigation Live Oak's mitigation plan consists of both on-site and off-site preservation. The proposed on-site component of the mitigation plan entails the preservation of 19.3 acres of herbaceous marsh, 373.2 acres of forested wetlands, and 124.9 acres of uplands. The mitigation plan preserves approximately 5.65 acres of isolated wetlands on-site, and approximately 386.86 acres of RHPZ wetlands on-site. The cornerstone of Live Oak's on-site mitigation is the preservation of the Econ River forested floodplain swamp, as well as two upland areas, in the southwestern corner of the property. One of the upland areas is a 15-acre upland scrub island on the east side of the river that is surrounded by forested wetlands. The other upland area is 24 acres of uplands located near the Econ River on its west side. Portions of both uplands are within the RHPZ. Both the forested floodplain and the associated upland areas provide habitat of regional ecological significance. The forested floodplain wetlands and the uplands that are part of the RHPZ are protected to a large degree by SJRWMD regulations. These regionally significant wildlife communities, however, can be temporarily, but chronically, impacted, if not permanently degraded, by timbering and other activities that are relatively unregulated. Live Oak proposes to protect and preserve these areas by placing them in a conservation easement. Placing Econ River forested floodplain wetlands and the upland RHPZ areas in a conservation easement will provide a greater level of protection and assurance that they will mature to an "old growth" condition, which will benefit many wildlife species. The Econ River floodplain wetlands, the upland scrub island and the small isolated wetland in the scrub island will accommodate the smaller wildlife species that currently use the Live Oak Reserve property. Live Oak has preserved most of the larger isolated wetlands with high ecological value. The large isolated wetlands preserved on-site will continue to maintain a high level of ecological function even with the surrounding development. Wildlife, such as frogs, toads, snakes, and wading birds will continue to use those wetlands. The on-site portion of the mitigation plan preserves approximately 71.87 acres of upland buffers, of which 2.04 acres are located in 25-foot buffers and 69.83 acres are located in 50- foot RHPZ buffers. The buffer areas will be placed in a conservation easement. The wildlife values of the uplands on this property that are not within the RHPZ are protected to some degree by local government regulations; they are, however, largely unprotected by the existing regulations of SJRWMD. Without the proposed conservation easements, this habitat may be developed or significantly degraded by other activities. As a component of its on-site sandhill crane nesting site management plan, Live Oak preserves a 6.83-acre upland buffer next to wetland 21, which hosts a sandhill crane nest. Additionally, Live Oak provides enhancement of 3.88 acres on the southside of wetland 21 within the 6.83-acre buffer area by converting this area to improved pasture for sandhill crane foraging habitat. The mitigation plan sufficiently offsets the impacts to the smaller isolated wetlands, even if these wetlands have more than a typical resource value. When evaluating impacts and mitigation, Applicant's Handbook Section 12.2.3.7 requires the SJRWMD to evaluate the predicted ability of the wetland or other surface water to maintain their current functions as part of the proposed system once the project is developed. Many of the smaller isolated wetlands, when located in a natural setting such as a pine flatwood, are very critical and provide very high ecological value. However, once a project is developed and the small isolated wetland is surrounded by homes, the resource value of the small isolated wetland is diminished. Many of the smaller wildlife species, such as frogs and snakes, will be extirpated from the developed area of property, whether or not the smaller isolated wetlands remain. SJRWMD considered the value of the off-site mitigation to offset the adverse impacts to the smaller isolated wetlands. In determining the adequacy of the preservation component of the mitigation plan, SJRWMD staff did not rely upon any specific rule, regulation, or comprehensive plan of the City of Oviedo. However, the staff did consider the overall protections afforded by the regulatory and comprehensive plan requirements of the city and determined that preservation of the mitigation areas by conservation easement provided greater assurance that these areas will be protected than the local government rules, regulations, and comprehensive plan. The off-site component of the mitigation plan is the contribution of $160,525 towards participation in the SJRWMD acquisition of a conservation easement over the 3,456 acre Yarborough parcel. The Yarborough parcel is located in the northeastern corner of the Econ River Hydrologic Basin. The Yarborough parcel encompasses property north and south of the Econ River. A portion, mostly sovereign lands, lies within the Puzzle Lake/Upper St. Johns River Hydrologic Basin. The Yarborough parcel is part of a large working ranch. The parcel contains improved and unimproved pasture, significant cabbage palm hammocks, pine flatwood communities, and freshwater marsh. Live Oak's participation equates to the acquisition of a conservation easement over 200 acres of the Yarborough parcel. However, Live Oak is not purchasing any particular 200 acres with the Yarborough parcel. Live Oak's contribution is applied to 200 acres of the Yarborough parcel within the Econ River Hydrologic Basin. SJRWMD estimates that of the 200 acres, 165 acres are wetlands and 35 acres are uplands. This assessment is based on the composition of wetlands and uplands on the Yarborough property within the Econlockhatchee River Hydrologic Basin. SJRWMD has purchased development rights over the Yarborough parcel. Yarborough is authorized to continue its cattle operation on the Yarborough parcel for 20 years in accordance with the conditions of the conservation easement. However, Yarborough is not permitted to increase the amount of improved pasture or further develop the parcel. On the contrary, the conservation easement requires Yarborough to decrease the number of cattle on the parcel over the next 20 years. Purchase of the conservation easement over the working ranch has positive environmental benefits. The conservation easement will protect the wildlife species that use the ranch. This environmental benefit can be used to offset adverse impacts on the Live Oak Reserve property. To participate in this type of mitigation, the acquisition must be imminent so that the SJRWMD is reasonably assured that the purchase will go forward. Participation is precluded for a parcel after its acquisition is concluded. Live Oak's mitigation plan, with its on-site and off- site components, offsets Live Oak Reserves adverse impacts. SJRWMD calculates the mitigation ratio and compares it to the guidelines in the Applicant's Handbook to determine if mitigation is adequate. SJRWMD however, is not required to adhere to any set ratio. The upland preservation ratio (area preserved to area impacted), excluding the 12 acres of uplands along the upland cut ditches and the Yarborough parcel uplands, is 6 to one. The rule guidelines for upland preservation is from 3 to one to 20 to one. The wetland preservation ratio is 15.5 to one. The rule guidelines for wetland preservation is from 10 to one to 60 to one. Public Interest Criteria Live Oak Reserve will not have any effect on the public health, safety or welfare or property of others. Because the mitigation plan adequately offsets all adverse impacts, Live Oak reserve will not adversely affect the conservation of fish and wildlife, including endangered or threatened species or their habitats. Because of the benefits of lowering the discharge rates in the post-development condition and reducing the velocity of stormwater in Brister Creek, Live Oak Reserve will reduce the potential for erosion. Live Oak Reserve will not have any affect on the fishing or recreational values or marine productivity in the vicinity of the site. Live Oak Reserve will be of permanent nature. However, its adverse impacts have been offset by mitigation. The permanence of the project is beneficial in that it provides treatment of untreated off-site runoff from county road 419 by the Live Oak surface water management system and it reduces the discharge rate of stormwater down Brister Creek. Therefore, the permanence of the project is not contrary to the public interest. In accordance with Section 373.414, Florida Statutes, the Florida Department of State Division of Historical Resources determined that the Live Oak Reserve project will have no possible impact to historic properties listed, or eligible for listing, in the National Register of Historical Places, or otherwise of historical or architectural value. Furthermore, the Division of Historical Resources determined that the project is consistent with Florida's Coastal Management Program and its historic preservation laws and concerns. The current condition and relative value of functions being performed by the various vegetative communities on the Live Oak Reserve property is good. However, there is no guarantee that the value and functions would remain good if the property is not managed for species like the sandhill crane or if agricultural and silvicultural practices continue to occur on the property. The mitigation plan, preserving regionally ecologically significant wetland and upland communities on both the Live Oak Reserve and Yarborough parcel by conservation easement, should provide a greater protection of those communities than what currently exists.

Recommendation Based on the forgoing, it is RECOMMENDED That a final order be entered granting Live Oak's application for a conceptual approval environmental resource permit with the conditions set forth in the SJRWMD technical staff report dated July 16, 1998, with the exception of condition 8, deleted by stipulation. DONE AND ENTERED this 2nd day of November, 1998, in Tallahassee, Leon County, Florida. MARY CLARK 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 Filed with the Clerk of the Division of Administrative Hearings this 2nd day of November, 1998 COPIES FURNISHED: Henry Dean, Executive Director St. Johns River Water Management District Post Office Box 1429 Palatka, Florida 32178-1429 Scott M. Price, Esquire J.A. Jurgens, P.A. 505 Wekiva Springs Road Longwood, Florida 32779 Charles H. Griffin, pro se 250 West 7th Street Chuluota, Florida 32766 Michael L. Gore, Esquire Meredith A. Harper, Esquire Ken W. Wright, Esquire Shutts and Bowen, LLP 20 North Orange Avenue Suite 1000 Orlando, Florida 32801 Anthony J. Cotter, Esquire St. Johns River Water Management District Post Office Box 1429 Palatka, Florida 32178-1429

Florida Laws (4) 120.569120.572.04373.414 Florida Administrative Code (5) 40C-4.04140C-4.30140C-4.30240C-4.38140C-41.063
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BAYSHORE HOMEOWNERS ASSOCIATION, INC., ET AL. vs. DEPARTMENT OF ENVIRONMENTAL REGULATION AND GROVE ISLE, LTD., 84-002639 (1984)
Division of Administrative Hearings, Florida Number: 84-002639 Latest Update: Feb. 25, 1985

Findings Of Fact Procedural History This matter has a long history. The full itinerary of this matter's arduous journey through the Administrative Procedure Act and the appellate courts may be glimpsed from the opinions of the District Court of Appeal in Grove Isle, Ltd. v. Bayshore Homeowners Association, Inc., 418 So.2d 1046 (Fla. 1st DCA 1982), Doheny v. Grove Isle, Ltd., 442 So.2d 966, reh. granted, 442 So.2d 977 (Fla. 1st DCA 1983), and Grove Isle, Ltd. v. State, Department of Environmental Regulation, 454 So.2d 571 (Fla. 1st DCA 1984). These cases may be referred to as Grove Isle I, Grove Isle II, and Grove Isle III, respectively. In 1978 Grove Isle submitted its initial application to DER for construction of the marina which is now the subject matter of this proceeding. Grove Isle's initial application was challenged by the same Petitioners who now challenge Grove Isle's "reapplication." In the first case the hearing officer, applying Class III standards for water quality, entered an order on February 22, 1980, recommending that the permit be issued. DER remanded the case to the hearing officer to determine whether the standards of the Outstanding Florida Waters (OFW) rule, Rule 17- 4.242(1)(a), F.A.C., should apply, and if so, whether Grove Isle had satisfied those requirements. On remand, the hearing officer entered a recommended order finding that the OFW rule did apply, that Grove Isle had provided reasonable assurances that the proposed marina would not lower existing ambient water quality, and that the proposed marina was not clearly in the public interest. Accordingly, the hearing officer recommended that the permit be denied. On December 29, 1980, DER entered a final order denying the permit because the project was not "clearly in the public interest" and it was uncertain whether ambient water quality would be lowered. DER found that, unless a "restricted mixing zone" was applied for, ambient water quality was to be measured within the project site, not in the small cove in which the marina was to be located as found by the hearing officer. On appeal, the court affirmed DER's denial of the permit. While DER's denial was affirmed because Grove Isle had failed to establish that the project was "clearly in the public interest," the court found that DER had failed to establish a record foundation which would permit it to substitute its conclusion that ambient water quality should be measured within the project site, as opposed to the small cove as found by the hearing officer. Grove Isle, Ltd. v. Bayshore Homeowners Association, Inc., supra. On May 18, 1981, while Grove Isle I was pending in the appellate court, Grove Isle filed the "reapplication" which is the subject matter of this case. The design and location of the marina were identical to Grove Isle's initial application. However, in an effort to satisfy the OFW rule Grove Isle proposed to add riprap and plant mangrove seedlings in an effort to satisfy the public interest criteria, and requested a mixing zone in conformity with DER's final order in Grove Isle I. DER initially entered a final order denying the application because: This project was reviewed previously... and was determined not to be clearly in the public interest pursuant to Section 17-4.242, F.A.C. No further evidence, upon resubmittal, has been provided to clearly demonstrate that this project is in the public interest. Furthermore, the requested mixing zone exceeds that allowable pursuant to Section 17-4.244,F.A.C., and can be applied only during the con- struction period, pursuant to Section 17.4.242, F.A.C. During the operation of this facility ambient water quality is expected to be degraded in violation of Section 17-4.242, F.A.C. Thereupon, Grove Isle filed a petition for a hearing pursuant to Section 120.57(1), Fla.Stat., and sought a default permit. The hearing officer entered a recommended order that the default permit issue, and DER entered a final order granting the default permit. On appeal the court reversed and remanded the case to DER for further proceedings. The predicate for its remand was: Even though Grove Isle was not entitled to a default permit, it does not follow that DER was justified in entering its earlier ... (order denying the applica- tion) ... without first informing Grove Isle that it had found its application to be deficient, specifying such deficiencies and allowing time for corrections.... Doheny v. Grove Isle, Ltd., supra, at 975. Appellant Doheny had asserted that Grove Isle's reapplication could not be further considered by reason of the doctrine of res judicata or estoppel by judgment. This was, essentially, DER's position in its denial of the "reapplication." The court held, however: Inasmuch as this Court affirmed the denial of Grove Isle's first application on the grounds of the applicant's failure to show that the proposal was clearly in the public interest and since it was determined that the first application was properly denied even though the applicant satisfied the other criterion regarding ambient water quality, it would appear that the reapplication should be denied unless the applicant could demonstrate some change or modification which would show that the project was clearly in the public interest. However ... I am of the view that it would be premature for us to hold that Grove Isle's second application is barred by either doctrine. Whether Grove Isle, after a Rule 17-4.07(2) notification by DER as contemplated above, would be able to remedy the existing deficiency in its present application remains to be seen. New facts, changed conditions or additional submissions by the applicant may materially affect the ultimate applicability of res judicata or estoppel by judgment. Doheny v. Grove Isle, Ltd., supra, at 975. While Grove Isle's "reapplication was pending on remand before DER, Grove Isle filed a rule challenge contesting the validity of Rule 17-4.242, F.A.C. The hearing officer upheld the validity of the rule, but the appellate court held that the "public interest" requirement was an invalid exercise of delegated legislative authority. Grove Isle, Ltd. v. State, Department of Environmental Regulation, supra. Following the decision of Grove Isle III, Grove Isle's attorney, by letter dated March 21, 1984, responded anew to DER's June 18, 1981, completeness summary. That letter provided, in pertinent part: With regard to water quality, that issue has been determined in a prior proceeding and is res judicata on the parties. In response to your request for additional information the enclosed information is submitted. Permit application DOAH Hearing Officer's Recommended Order of February 22, 1980 DOAH Hearing Officer's Recommended Order on Remand of November 20, 1980 DER's Final Order of December 29, 1980 Decision in Grove Isle v. Bayshore Homeowners Associ- ation, 418 So.2d 1046 (Fla. 1st DCA 1982) The decision in David A. Doheny v. Grove Isle, Ltd., and the State of Fla., DER, Case NO. AM476 This submittal contains the necessary information on which to determine com- pliance with the applicable water quality standards and criteria. On June 25, 1984, DER issued its Notice of Intent to Issue the permit. The notice provided, in pertinent part: The Department intends to issue the permit for the following reasons: No significant immediate or long term negative biological impact is anticipated and State water quality standards should not be violated as a result of the pro- posed construction. This intent is based on information supplied by the applicant that the proposed project will not violate existing ambient water quality standards and on the cases of Grove Isle, Ltd. v. Bayshore Homeowners Association, 418 So.2d 1046(Fla. 1st DCA 1982) and Doheny v. Grove Isle, Ltd., 442 So.2d 996 (Fla. 1st DCA 1983)(sic). Petitioners timely filed their Petition for Administrative Hearing pursuant to Sections 120.57(1), Fla.Stat. The petition was referred to the Division of Administrative Hearings and assigned Case No. 84-2639. The Marina The permit sought by Grove Isle would allow it to construct six concrete fixed piers, five "T" shaped, one "L" shaped, with a boat docking capacity of 90 pleasure boats. The piers will extend a maximum of 165 feet offshore from an existing concrete bulkhead on the west side of Grove Isle. The width of the piers will be eight feet from the bulkhead to a point 41 feet offshore, and then increase to a width of 10 feet. A sewage pumpout facility is also proposed. DER's June 25, 1984, Letter of Intent proposed to issue the permit subject to the following conditions: Adequate control shall be taken during construction so that turbidity levels beyond a 50 foot radius of the work area do not exceed 50 J.C.U.'s as per Sec- tion 24-11 of the Metropolitan Dade County Code. During construction, tur- bidity samples shall be collected at mid-depth twice daily 50 feet upstream and 50 feet downstream of the work area. The contractor shall arrange to have turbidity sample results reported to him within one hour of collection. Turbidity monitoring reports shall be sub- mitted weekly to the Department of Environmental Regulation (DER) and the Metropolitan Dade County Environmental Resources Management (MDCERM). If turbidity exceeds 50 J.C.U.'s beyond a 50 foot radius of the work area, turbidity curtains shall be placed around the work area and MDCERM notified immediately. Tur- bidity samples shall be collected as per specific Conditions No. 2 no later than one hour after the installation of the turbidity cur- tains. If turbidity levels do not drop below 50 J.C.U.'s within one hour after installation of the curtain, all construction shall be halted. Construction shall not be resumed until the contractor has received authorization from MDCERM. No liveaboard vessels (per- manent or transient) shall be docked at this facility unless direct sewage pumpout connections are pro- vided at each liveaboard slip. A permanent pumpout station shall be installed and maintained for the removal of sewage and wastes from the vessels using this facility. Compliance with this requirement will entail the applicant contacting the Plan Review Section of MDCERM for details con- cerning connection to an approved sewage disposal system. Boat traffic to the shallow 30 foot wide dense seagrass area which parallels the shoreline shall be restricted by the placement of wooden piles on six foot centers along the entire shoreline facing the marina. The channel from this marina to deeper water in Biscayne Bay shall be marked to prevent boats from straying into adjacent shallow areas. This will prevent habitat destruction. A chemical monitoring program shall be established to determine the affect of this marina on the water quality of this section of Biscayne Bay. Surface and mid-depth samples shall be collected at three points in the project area and at one back- ground station. Parameters shall include, but not be limited to, dissolved oxygen, pH, salinity, tempera- ture, total coliform and fecal coliform, and fecal streptococci bacteria, oil and grease, biochemical oxygen demand and turbidity. Background samples shall be collected prior to construction and quarterly for a minimum of one year after 90 percent occupancy of the marina. In addition to the chemical monitoring program, a bethnic community monitoring program is to be established. Samples of the bethnic seagrass community within and adjacent to the project area are to be collected prior to construction and quarterly for a minimum of one year after 90 percent occupancy of the marina. Should either monitoring program detect dissimilar changes at its monitoring and control stations, DER and MDCERM shall be notified and the results of the programs(s) evaluated. The monitoring program shall be reviewed and approved by the DER and the MDCERM prior to implementation. Monitoring reports shall be submitted to the DER and the MDCERM and the U.S. Army Corps of Engineers on a regular basis. Warning signs shall be posted in the marina area advising marina users that manatees frequent the area and caution should be taken to avoid collisions with them. Issuance of this permit does not relieve the applicant from securing all applicable construction permits including, but not limited to, general construction, electrical, plumbing, etc. The planting of mangroves and the placement of boulder riprap shall be generally constructed as outlined in report number THI-004-005/84 by Melvin S. Brown for Grove Isle, Inc. The mangrove/ riprap site shall be staked by the appli- cant and approved by the Department or MDCERM. Such construction shall not take place in areas vegetated by sea- grasses. Mangrove seedlings (four leaf stage or older) shall be planted with a density of approximately one plant per-square meter. Seedlings shall be replaced in order to maintain 80 percent survival until such time as the Department determines that establishment of the mangroves is reasonably assured (approximately two years). At that time the Department shall notify the permittee of the termination of the revegetation respon- sibilities. Grove Isle has agreed to comply with all the conditions established by the DER Letter of Intent and, additionally, agreed at final hearing to employ a full-time dock master, prohibit the pumping of bilges and sewage from boats docked at the marina, make the sewage pumpout facility available to the public, limit the ownership and use of the boat slips to condominium owners at Grove Isle, and provide additional channel markings from the Grove Isle marina to the Deering Channel. The location and design of the proposed marina has not changed since Grove Isle's initial application. The conditions attached to DER's Letter of Intent, with the exception of Conditions 11 and 12, are the same as previously applied to Grove Isle. The Marina Site Grove Isle is a spoil bank in Biscayne Bay located approximately 700 feet east of the Florida mainland. It is linked to the mainland by a two-lane concrete bridge. The island is currently under development for a 510-unit condominium community with associated facilities such as a restaurant, hotel, and the proposed marina. The island is surrounded by a concrete bulkhead constructed many years ago. No changes in the bulkhead line are proposed. Grove Isle proposes constructing the marina on concrete piles driven in the bay bottom from a shallow draft barge. During construction there would be some turbidity caused from the disruption of the Bay sediment. This can, however, be adequately controlled by the use of turbidity curtains during construction. The construction will not require any filling. In the immediate marina site the most significant biota are a 20-30 foot wide bed of seagrasses running parallel to the seawall. There are no other important biota because at one time the area was extensively dredged to create the island. There are no oyster or clam beds nearby. The water depth in the area ranges from one foot near the island bulkhead to 12 feet offshore to the west of the island. This particular seagrass bed consists primarily of turtle grass (thalassia testudinum) with some Cuban Shoal Weed (Halodule Wrightii). Protection for these grasses will be provided by a buffer zone between the island and the boat slips. The grassy zone will be bordered by a row of dolphin piles to exclude boat traffic. Because the grass requires sunlight for photosynthesis and therefore life, the six piers will have grated walkways where they pass over the grass. This will allow sunlight to reach below. In addition to the small grass bed on the west of the island, there are extensive beds to the northeast, east and south of the island that extend several hundred yards from the island in water depths of three to ten feet. If boat traffic in the vicinity is markedly increased due to the existence of the marina, it is conceivable that the number of propeller scars in these shallow beds could increase. At the present time the beds are already traversed by boats, some of which are owned by Petitioners' members. There are already, for example, approximately 50 craft which operate from the nearby mainland or from Pelican Canal directly across from the island. Grove Isle's assurance that ownership and use of the boat slips at the marina will be limited to those persons who own condominium units at Grove Isle will assure that boat traffic generated by the marina will be no different in kind nor more frequent than that generated by existing craft in the area. Potential damage, from existing craft and those which will occupy the marina, to the seagrasses on the north, east, and south of the island will be eliminated or minimized by the planned installation of navigation markers by Grove Isle. These markers will channel boats into water of a navigable depth and lessen the number of groundings and near groundings which cause the scarring. There is evidence that boats by their very existence and operation are potential pollution sources. Anti-fouling bottom paints by their very nature leach minute amounts of metals such as copper or tin into the waters. These deposits, however, would not be measurable. Further, the marina site has adequate flushing to disperse any pollutants which may be generated by the marina operation. Petitioners also suggest that turbidity, caused by the operation of the marina, could cause a degradation of water quality and affect the biota in the area. Petitioners' assertion must be rejected for two reasons. First, this question was raised and rejected in Grove Isle I. No changed conditions or new facts which were not available at the time of final hearing in Grove Isle I were presented. Second, in the four years that have intervened since the first hearing, these waters have been extensively used by the public, including Petitioners, for such activities as waterskiing and fishing. In that time period there has been no degradation of water quality, or harm to the biota. In fact, the biota have expanded. The fueling of boats and sewage discharge are additional pollution sources generally associated with marinas. However, the proposed marina will have no fueling or maintenance facilities, and all craft docked at the marina will be prohibited from pumping bilges and sewage into the waters. The foregoing findings of fact are, without significant exception, identical to those in Grove Isle I. Grove Isle IV Only three areas of inquiry were present in this case which may not have existed in Grove Isle I. First, Petitioner asserted that Grove Isle's application was incomplete because of its failure to secure the approval of the Department of Natural Resources (DNR) for use of the bay bottom, and that, therefore, Part VIII, Chapter 403, Florida Statutes, the "Warren S. Henderson Wetlands Protection Act of 1984" (Wetlands Act) was applicable to these proceedings. Contrary to Petitioner's assertion, Grove Isle secured and exhibited its consent to use the submerged lands in question. Grove Isle received the requisite consent from DNR in connection with its first application. Pursuant to Rule 16Q-18.03(2), F.A.C., that consent to use remains binding. Further, DNR was noticed of Grove Isle's "reapplication" and evidenced no intention to withdraw its previous consent to use. Grove Isle complied with Section 253.77, Fla.Stat. Consequently, Grove Isle's application was complete prior to October 1, 1984, and the Wetlands Act is not applicable to this case. The second issue presented in this case which Petitioners assert was not present in Grove Isle I, is Grove Isle's request for a mixing zone. Although its "reapplication" did request a mixing zone in accordance with DER's Final Order of December 29, 1980, Grove Isle objected to its necessity since the proper geographic area within which to measure ambient water quality, according to it, was a subject matter of the pending appeal in Grove Isle I. The mixing zone applied for in its "reapplication" was somewhat smaller, but did not significantly differ from the area adopted by the hearing officer in Grove Isle I. In Grove Isle I the parties had differed with regard to the proper geographic area within which to measure ambient water quality. The hearing officer adopted as the appropriate geographic area that part of Biscayne Bay to the west of Grove Isle, to the north of the Grove Isle bridge, to the east of the Miami mainland, and to the immediate south of the Mercy Hospital landing facing Grove Isle. DER's Final Order of December 29, 1980, rejected the hearing officer's conclusion because Determination of compliance with water quality standards is made within the project area itself unless a mixing zone is applied for and granted by the Department. Section 17-4.242(1) (a)2b, Florida Administrative Code, specifically states that ambient water quality standards may not be lowered unless such a lowering is temporary in nature (i.e., not more than 30 days) or unless the "lowered water quality would occur only within a restricted mixing zone approved by the Department..." (EmphasisSupplied.) The record does not show that a "restricted mixing zone" was applied for by the applicant or granted by the Department. Therefore, the hearing officer was not at liberty to apply a mixing zone in this case. In Grove Isle I DER's witness, Larry O'Donnell-- Supervisor of the Dredge and Fill Section of DER's West Palm Beach office--testified that ambient water quality was to be measured within the project site--the specific area occupied by the marina circumscribed by the bulkhead line and out the length of the piers (165 feet). On appeal, the court held that DER erred in rejecting the hearing officer's conclusion, and stated DER offered no expert testimony or evidence, other than conclusory allegations, that ambient water quality must be measured within the project site rather than within the reasonably contiguous area used by the hearing officer. Absent such record foundation, DER is not free to substitute its conclusions for those of the hearing officer. Grove Isle, Ltd. v. Bayshore Homeowners' Assoc., Inc., supra, at 1049. In the instant case the testimony of Mr. O'Donnell was clear that DER accepted the opinion of Grove Isle I as demonstrating satisfaction of ambient water quality under the OFW rule. Consequently, DER has acceded that ambient water quality is to be measured not only within the project site but also within a reasonably contiguous area of the project site, as found by the hearing officer in Grove Isle I. Petitioners took exception to DER's decision. To support their position, Petitioners offered the testimony of Suzanne Walker, DER's Chief of Permitting. Ms. Walker's opinion was that ambient water quality had to be satisfied everywhere, including the marina site proper, and that a mixing zone, except on a temporary basis during construction, was not permitted under Rule 17-4.242, F.A.C. Accordingly, the question of where ambient water quality is to be measured is presented anew. Ambient water quality is to be measured within the area established by the hearing officer in Grove Isle I for three reasons. First, the issue was presented in Grove Isle I and the doctrine of res judicata or estoppel by judgment bars relitigation of this same issue. Second, the testimony of Ms. Walker was of no greater substance than that rejected by the court in Grove Isle I. Finally, Ms. Walker's opinion is questionable since she also testified that a mixing zone, except on a temporary basis during construction, was not permissible in Outstanding Florida Waters. The OFW rule, Rule 17- 4.242(1)(a)2.b, F.A.C., clearly contemplates and authorizes a mixing zone for purposes other than construction. The record is silent as to whether DER granted Grove Isle's request for a mixing zone. It is clear, however, that DER accepted the geographic area established in Grove Isle I as the proper area within which to measure ambient water quality. Accordingly, it is not necessary to pass on Grove Isle's request for a mixing zone. The final matters not litigated in Grove Isle I concern Grove Isle's agreement to (1) add riprap and plant mangrove seedlings, (2) employ a full-time dock master to provide additional assurance that operation of the marina will be ecologically sound, (3) prohibit the pumping of bilges and sewage from boats moored at the marina, (4) make the pumpout facility available to the public, (5) limit the ownership and use of the boat slips to the owners of the condominium units at Grove Isle, and (6) mark a channel from Grove Isle to the Deering Channel so that a deep water channel to open waters will be available. While these additional assurances were not presented in Grove Isle I, and consequently did not affect the hearing officer's recommendation that the permit be granted, each of these matters are of positive benefit to the ecology, and demonstrate Grove Isle's commitment to sound marina design and operation.

Florida Laws (2) 120.57253.77
# 7
MICHAEL D. RICH, COALITION FOR RESPONSIBLE ECONLOCKHATCHEE DEVELOPMENT, INC. vs ST. JOHNS RIVER WATER MANAGEMENT DISTRICT, 98-000819 (1998)
Division of Administrative Hearings, Florida Filed:Orlando, Florida Feb. 19, 1998 Number: 98-000819 Latest Update: Jul. 12, 2004

The Issue Live Oak Plantation No. 1, Ltd. (Live Oak) through Stanford Development Group filed application number 4-117-0464AC-ERP with the St. Johns River Water Management District (SJRWMD) in April 1997, seeking a conceptual approval environmental resource permit. After SJRWMD issued its notice of intent to grant the permit, the Petitioners filed their petitions challenging the intended agency action. The central issue in this proceeding is whether the permit should be issued pursuant to Chapter 373, Florida Statutes, and Chapters 40C-4, 40C-41 and 40C-42, Florida Administrative Code, including specific provisions of the Applicant's Handbook adopted by rule and identified in the parties' prehearing stipulation filed July 8, 1998.

Findings Of Fact The Parties Michael D. Rich is a former resident of Seminole County who lived on the property contiguous to the Live Oak site. He is the legal representative of his mother who still resides on the property and he is president of C-RED. C-RED is a Florida non-for-profit corporation with members from the City of Oviedo and unincorporated areas of Seminole County who are interested in assuring that development is done without improper impact on the taxpayers and the rural character of the area. Mr. Griffin is a resident of Seminole County living on Horseshoe Lake, which adjoins the Live Oak site. Live Oak is a Florida Limited Partnership which intends to develop the project that is the subject of this proceeding. SJRWMD is a special taxing district created by Chapter 373, Florida Statutes, and charged with responsibility for various permitting programs, including the one at issue here. The Project Live Oak proposes to develop a large multi-phased single family project with two small commercial sites. The project, to be known as "Live Oak Reserve," will be on approximately 1,041 acres on the south side of county road 419 in southeastern Seminole County in the City of Oviedo. The project site is located near the confluence of the Econlockhatchee River (Econ River) and Little Econlockhatchee River. The Live Oak Reserve property includes approximately half of Horseshoe Lake, as well as a small creek, Brister Creek, which flows from Horseshoe Lake across the property to the Econ River. The Econ River, a class III water and designated an Outstanding Florida Water (OFW), crosses the southwestern corner of the Live Oak Reserve property. The Econ River is the receiving water body of Live Oak Reserve. The Live Oak Reserve property is located within the Econlockhatchee River Hydrologic Basin. A portion of the Live Oak Reserve property lies within the Econlockhatchee River Riparian Habitat Protection Zone (RHPZ). The Live Oak property lies within a 1,500 acre drainage basin; approximately 450 acres off-site drain through Live Oak Reserve. Horseshoe Lake has approximately 500 acres that drain through it, then through the wetlands and into the Econ River. Historically, the Live Oak Reserve property has been used for agricultural practices, including siliviculture and cattle production. Some areas of the property have been logged and some areas have been converted to pasture. Cattle have grazed in wetlands, thereby decreasing the amount and diversity of groundcover vegetation on portions of the property. Additionally, on-site drainage ditches have had a major impact on the hydrological characteristics of the wetlands on the property, including the reduction of surface water elevations. The Live Oak Reserve property is currently vacant and undeveloped. The Application Process In April 1997, Live Oak submitted to the SJRWMD an Environmental Resource Permit Application, N4-117-0464AC-ERP, for conceptual approval of a master stormwater and floodplain management system for the development of Live Oak Reserve. A conceptual permit is utilized in complex multi-phased projects which are expected to have a longer build-out period than a single phase project. A conceptual permit does not allow any construction activity, but provides the outline for final engineering calculations and construction drawings. Further permits are required before any sitework or construction is undertaken. In conjunction with its permit application Live Oak submitted detailed technical information, including but not limited to charts, maps, calculations, studies, analyses and reports necessary to show that the conceptual development plan was consistent with the permitting criteria of the SJRWMD found in Chapter 40C-4, Florida Administrative Code, and the Applicant's Handbook. The master plan for the Live Oak project was designed by Donald W. McIntosh Associates, Inc.(McIntosh) using input from: (a) land planners who were required to consider issues related to the comprehensive plans, open space requirements and related issues; (b) landscape architects who were responsible for the proposed park systems and landscape treatments throughout the project; (c) geotechnical engineers responsible for evaluating the soil and groundwater conditions; and (d) environmental consultants, Modica and Associates, who were responsible for wetland delineation and flagging and wildlife surveys. The first version of the Live Oak Reserve site plan prepared for the project by McIntosh included development of all upland areas and filling several portions of the mixed forested wetlands to maximize lot yield. This included development of the upland adjacent to the Econ River and development of an upland parcel on the west side of the river. After much consideration and revision by the developer and its consultants, a site plan was developed which minimizes impacts to wetlands and other surface water functions, particularly as it relates to the Econ river, and maximizes the benefits to wildlife by establishing a series of wildfire corridors across the site. The final plan submitted to the SJRWMD at the time of the application includes the preservation of the entire Econ River floodplain and two adjacent developable upland areas, a large mixed hardwood forested wetland which traverses the site from the northeast to the southwest, and upland and wetland areas in the southern portion of the site that provide a corridor between a large undeveloped parcel to the east and the Econ River to the west. After submission of its application, Live Oak participated in a review process with SJRWMD staff to further eliminate and reduce wetland impacts. Specifically, SJRWMD requested changes to the site plan which included reductions in impacts to various wetlands and additional buffers to other wetlands. Several changes to the site plan were made to accommodate the SJRWMD's concerns relating to reducing impacts to wildlife, particularly the Florida sandhill crane. The reductions in wetland impacts and other design changes resulted in a revised site plan which the SJRWMD staff recommended to the district's governing board for approval. The staff recommendation of approval, with associated conditions, is set forth in Technical Staff Report dated February 10, 1998. On July 14 and 16, 1998, the SJRWMD revised the technical staff report to reflect changes to the project design and mitigation plan, as well as to add conditions inadvertently omitted from the earlier technical staff report. Condition no. 8 was mistakenly added to the July 16 technical staff report and by stipulation of all the parties, this condition was removed from the technical staff report. (See transcript, page 521) Stormwater Analysis McIntosh utilized information from different sources in preparing the stormwater calculations submitted to the SJRWMD. The developer provided information regarding proposed lot sizes and types so as to determine the impervious surface area for developable lots. The geotechnical consultants, Universal Engineering Sciences, (Universal) provided McIntosh with preliminary, interim, and final geotechnical reports, soil boring logs, and groundwater table estimates. The input from Universal primarily involved the establishment of seasonal high and seasonal low groundwater elevations for the pre-development and post-development conditions on the site. The estimated seasonal high and seasonal low groundwater levels refer to the range of levels the groundwater is expected to attain on the site during the wetter (high) and dryer (low) periods of a normal year. These elevations were then utilized in the stormwater calculations prepared by McIntosh. Topography on Live Oak Reserve consists of elevations ranging from 48 feet to 25 feet NGVD. In its pre-development condition, Live Oak Reserve has 6 distinct drainage patterns. Off-site drainage basins also contribute runoff to the property. The conceptual post-development design will modify the project's on-site drainage patterns into 28 drainage basins. At the request of the SJRWMD, Live Oak prepared seasonal high and seasonal low groundwater elevation contour maps. Live Oak performed approximately 200 borings on the Live Oak Reserve property. From the borings, Live Oak determined the soil types present and the existing groundwater elevations. Live Oak also used the borings to assist in establishing the estimated seasonal groundwater elevations. With the exception of several shallow borings in wetland areas, all borings were taken by split spoon sampling. Seventy-nine piezometers were installed next to bore holes to measure groundwater levels. In establishing the seasonal high groundwater levels, Live Oak evaluated the groundwater level at the time of boring; the time of year the groundwater level was measured; the time span of the investigation and its relationship to normal rainfall patterns; soil indicators such as coloration, mottling, and particle size; site specific topography; USGS quadrangle maps depicting site topography; Soil Conservation Service (NSCS) estimates of the expected seasonal high groundwater levels; and vegetative indicators. It is not essential to evaluate rainfall data when determining the seasonal water levels because the historical seasonal water levels are recorded in the soils. The estimated seasonal high groundwater level can be determined during the dry season. The range of the estimated seasonal high groundwater level on the Live Oak Reserve property is from standing water on the ground to five feet below the existing grade. In evaluating Live Oaks estimated seasonal groundwater levels, the District reviewed Live Oak's submittals, and also reviewed the NSCS soil survey to confirm that the estimated seasonal groundwater levels were reasonable. Wetland seasonal surface water levels were estimated using biological indicators such as lichen lines, buttressing, water lines, and sand lines. Lichen lines were apparent on the Live Oak Reserve properly and reflective of normal rainfall conditions. Seasonal high water levels are expected at the end of September. Seasonal low water levels are expected in May. The wetland surface water levels encountered in January 1997, when the seasonal levels were estimated, were neither exceptionally low nor exceptionally high. The water levels were representative of a period of normal rainfall. Water quantity attenuation and stormwater treatment will be accomplished through wet detention ponds and vegetative natural buffers. Due to the location of Live Oak Reserve in the Econlockhatchee River Hydrologic Basin, special basin criteria apply this project. The special basin criteria, also known as the "Econ Rule," is more stringent than the stormwater management criteria set forth in Applicant's Handbook sections 9 and 10. The special basin criteria, as it relates to the surface water management systems, requires Live Oak to control its discharge from two design storms: the mean-annual design storm, and the 25-year, 24-hour design storm. A design storm is a hypothetical storm with a predetermined rainfall amount, a predetermined intensity and 24 hour-duration. Designing the system to control the peak discharge during the mean-annual storm will prevent erosive velocities that would be harmful to Brister Creek and the Econ River. The conceptually proposed system is designed to limit peak rates of discharge to those of pre-development for the mean-annual and the 25-year, 24-hour design storm events. The system, as conceptually proposed, will limit post-development discharge rates to the same as or lower than the pre-development discharge rates. Each stormwater management area will pre-treat its respective post-development basin's pollution volume prior to discharge downstream. Live Oak proposes to use vegetative natural buffers for a portion of the rear lots within the post- development condition to fulfill treatment requirements. Live Oak Reserve is designed for the retention of the first inch of runoff from the total area of the post-development basins or the total runoff from 2.5 inches times the post- development basin's impervious area, whichever is greater. Furthermore, because Live Oak Reserve conceptually discharges to the Econ River, an OFW, the system is designed to provide an additional 50 percent of treatment. For discharges to an OFW the system must treat to a 95 percent removal standard. The outfall structures within each wet detention system are designed to draw down one-half the required treatment volume between 60 to 72 hours following storm event, but no more than one-half of this volume will be discharged within the first 60 hours. Each wet detention pond is designed with a permanent pool with a 31.5-day residence time during the wet season. Residence time is the time that the water within a pond will stay in the pond prior to discharge. The residence time includes the 14-day residence time required of all wet detention systems, an additional 50 percent residence time (7 days) for discharging into an OFW, for a total of 21 days. In addition, each system has been designed to provide an additional 50 percent residence time (10.5 days) because Live Oak has elected not to plant littoral shelves within each pond. As conceptually designed, Live Oak reserve's post- development drainage pattern will have no effect on the drainage patterns of Lake Eva or Horseshoe Lake. As conceptually designed, Live Oak Reserve's post-development drainage pattern will reduce the rate of flow during the storm events, which is a positive effect on the drainage pattern of Brister Creek. The reduction in flow velocity reduces the erosiveness of the storm. Live Oak has demonstrated that the 25-year and 100- year, 24-hour storm events' post-development peak stages for Lake Eva and Horseshoe Lake are not changed as a result of this conceptual project. Based upon Live Oak's calculations, the Live Oak Reserve project will not cause any restriction to the flow of water as it outfalls from Horseshoe Lake to Brister Creek. The conceptual wet detention systems within Live Oak Reserve are proposed to have a maximum depth of 12 feet. However, Live Oak requested consideration at the time of final engineering for each phase of development to maximize selected stormwater management areas for maximum depths of up to 25 feet. That consideration will be made in subsequent application review and is also subject to the City of Oviedo's approval. The conceptual wet detention ponds are designed with an average length to width ratio of two to one, and are configured to minimize the occurrence of short circuiting. As such, they will meet the criteria of the applicable rules. Tailwater conditions for the project were based on published flood elevations. Live Oak analyzed the tailwater condition for the mean-annual, 25-year 24-hour, and the 100-year 24-hour design storms. Live Oak completed a 100-year flow analysis for Live Oak reserve. Pre-development floodplain elevations for Lake Eva, Horseshoe Lake, and the Econ River were referenced from previous studies (Seminole County) and the Federal Emergency Management Agency. Live Oak determined that the 100-year floodplain elevations effecting Live Oak Reserve to be 40.2 feet NGVD from Horseshoe Lake, 45.0 feet NGVD for Lake Eva, and 32.5 feet NGVD for the Econlockhatchee. The U.S. Geological Survey (USGS) has produced a map of flood prone areas which indicates that the elevation delineating the flood prone area for Horseshoe Lake is 40.14, not 40.2, and for Lake Eva is 43.38, not 45.0. Therefore, the area indicated by USGS as the flood prone area is included in the 100-year floodplain analysis of Live Oak. Live Oak, in its conceptual design, has demonstrated that it will provide compensating storage for any encroachments into the 100-year floodplain. Live Oak has conceptually proposed to fill approximately 18.69 acre- feet within the 100-year floodplain. Live Oak will compensate the filling of the floodplain by providing a cut with the 100-year floodplain of approximately 27.09 acre-feet. By meeting the criteria in the "Econ Rule" the project conceptually meets all other relevant standards for stormwater management as the basin rule is more stringent. Live Oak has provided reasonable assurance that the development will not affect surrounding property or raise stagewater elevations of any surrounding property; the development will not displace the 100- year flood plain area; and the development will not restrict or impede the natural flow from Horseshoe Lake. Wetland and Wildlife Impacts Approximately 430 acres of wetlands cover the project site. Two general types of wetlands on found on the Live Oak reserve property: herbaceous wetlands and forested wetlands. Twenty-three herbaceous wetlands are classified as freshwater marshes. These wetlands range in size from 0.2 acre to over 8 acres. Wetlands 10 and 16, the largest on the property, are mixed hardwood forested wetlands. Approximately 525 acres of the Live Oak Reserve property are located within the RHPZ. Of this area, approximately 410.5 acres are wetlands, and the remainder are uplands that are predominantly pine flatwoods and xeric scrub. A few of the wetlands on site are considered RHPZ wetlands, not "isolated," solely because they are connected to floodplain wetlands by ditches. These wetlands and 50 feet of the uplands surrounding them are considered part of the RHPZ. The wetlands within the RHPZ are intact with little disturbance, especially in the Econ River corridor that is a part of wetland 16. Wetland 10 has been logged and the species composition in that wetland has changed. Wetlands 12 and 14 have ditch connections to the Econ River, but these ditch connections do not appear to have adversely impacted the wetlands hydrologically. Wetlands 2,3, and 8 have ditch connections to the Econ River. These wetlands have been adversely affected (drained) by the ditching. The RHPZ uplands are in good condition and provide very valuable habitat, except for 12 acres that are adjacent to upland cut drainage ditches. These 12 acres have no habitat value. The portion of the Live Oak Reserve property within the RHPZ provides good habitat important to fish and wildlife, and is part of the Econ River floodplain. The upland areas outside the RHPZ on the Live Oak Reserve property primarily consist of pine flatwoods and pasture. The pine flatwoods have been logged and are overgrown. The pasture appears to have been cleared many years ago and planted with bahia grass. Twenty-two isolated wetlands, which total approximately 17.9 acres, are located on the Live Oak reserve property. The isolated wetlands are intact and in good condition, except for temporary impacts due to cattle grazing and logging. The isolated wetlands provide habitat for wading birds, frogs, toads, and other wildlife. Ephemeral wetlands are wetlands that are seasonally inundated, but not necessarily inundated every year. Ephemeral wetlands provide important functions to wildlife, including gopher frogs and other amphibians for breeding, wading birds and sandhill cranes for foraging, and invertebrates. Ephemeral wetlands or "seasonal" wetlands occur on the Live Oak Reserve property. Although Live Oak did not separately address any of the wetlands as ephemeral, the value and functions of ephemeral wetlands were assessed by SJRWMD staff-person, David Eunice. While several small ephemeral wetlands are being impacted by the proposed development, several others are being preserved. Live Oak conducted wildlife surveys of the Live Oak Reserve property in accordance with the Florida Game and Fresh Water Fish Commission's approved Wildlife Methodology Guidelines. Based on the surveys, Live Oak determined that three listed species occurred on-site: the Florida sandhill crane, the gopher tortoise, and the Sherman's fox squirrel. The Florida sandhill crane is a threatened species. Live Oak found no evidence that the property hosts Florida panthers. Although the wildlife surveys did not identify gopher frogs, a species of special concern, the SJRWMD recognized the potential for the gopher frog to use the wetlands, including the ephemeral or seasonal wetlands, on the Live Oak Reserve property. Florida sandhill cranes have been observed foraging in a few areas on the Live Oak reserve property. In the spring of 1997, Live Oak identified two active nests in freshwater marshes (wetlands 21 and 29). There is no evidence that the sandhill cranes are currently nesting in wetland 29; however, Florida sandhill crane nests have been located in wetlands 14 and 21 this year. The typical critical nesting habitat for Florida sandhill cranes is a large, isolated marsh, generally either dominated by maidencane or pickerel weed. The marsh must maintain a surface water level between 12 and 24 inches so that the birds can construct a suitable nesting platform in the marsh. Nesting success, in part, depends upon wetland type used and water depths. The Florida sandhill crane also requires a certain amount of pasture-like upland habitat in which to forage. However, the crane forages in both uplands and wetland. Upland pasture is the sandhill crane's preferred foraging habitat. The sandhill crane's second most preferred foraging habitat is freshwater marsh. When the sandhill cranes have chicks and fledglings, the birds forage in the wetlands. After a period of three to four months, the juvenile and adult sandhill cranes will move to open pasture to forage. The Econ River floodplain wetlands and their associated upland habitats on the Live Oak reserve property are regionally ecologically significant. Overall, the Live Oak Reserve property provides good ecological value. It is part of the river corridor, has a tributary that runs through it and has uplands that have had little disturbance. Live Oak has eliminated certain wetland impacts and reduced others during the design of the Live Oak Reserve project. Live Oak eliminated some road crossings, and redesigned the pond configuration to eliminate or reduce encroachments into wetlands. Live Oak's site plan that was submitted as part of the initial April 14, 1997, application reflects Live Oak's initial attempts to eliminate or reduce impacts. Live Oak, in its application, proposed a project design with 46 acres of wetland impacts. The site plan has changed since Live Oak made the initial application to the SJRWMD. The initial project design called for the removal of the southern one-half of wetland 29 for the construction of a stormwater pond. Live Oak redesigned the project to preserve wetland 29 with a 50-foot upland buffer around it to eliminate direct impacts to the sandhill cranes nesting there. Live Oak further reduced impacts by preserving wetlands 14 and 15, and by placing upland buffers around them to protect sandhill crane habitat. The revised design of the surface water management system reduced wetland impacts by approximately 7 acres. The SJRWMD February 10, 1998, technical staff report includes the design plans reducing impacts by 7 acres. After the SJRWMD issued its February 10, 1998, technical staff report, Live Oak once again redesigned the project to preserve wetland 12. This redesign reduced wetland impacts by an additional 3 acres. In this case, SJRWMD staff worked with Live Oak to reduce or eliminate its impacts. Nonetheless, staff believed Live Oak's proposed mitigation qualified for the exception under Section 12.2.1.2b, that is, the on-site preservation of the Econ River floodplain and associated uplands, in concert with Live Oak's contribution to acquiring a conservation easement over the Yarborough parcel, discussed below, provides regional ecological value and provides greater long term ecological value then the areas impacted. Live Oak proposes practicable design alternatives, but it is not required to reduce or eliminate all impacts. Some design alternatives, such as whether to use a bridge or culverts for the Brister Creek crossing, must be addressed and considered at a later permit application stage and not at this conceptual permit stage. The proposed design includes dredging or filling of approximately 35.9 acres of wetlands and construction in approximately 38 acres of RHPZ uplands. Of these 35 wetlands on the Live Oak Reserve property, Live Oak will completely impact 23 of the wetlands (17.64 acres of wetland impact); partially impact 5 wetlands (18.28 acres of wetland impacts out of 370.15 acres of wetlands); and will avoid impacts to 7 wetlands (40.63 acres). The impacts are mostly limited to the small isolated wetlands, the upland/wetland transitional edges of the floodplain wetlands, and portions of RHPZ already degraded by a ranch roadway and ditch placement. Live Oak focused its impacts on areas, including wetlands, that were historically disturbed. SJRWMD staff considered that the isolated wetlands less than 0.5 acre were used by sandhill cranes and other threatened or endangered species. Therefore, staff required Live Oak to offset impacts to the small isolated wetlands. In addition to physical impacts to wetlands and RHPZ, the habitation of the proposed subdivision, which will result in noise and intrusion into wildlife habitat by humans and their pets, will cause secondary impacts. Those secondary impacts are offset in part by the upland buffers proposed by the applicant (a total of 10 acres of 25 foot buffers and 47.86 acres of 50- foot buffers.) After considering the type of impact proposed; past, present and future activities that may occur in the Econ River Hydrologic Basin; and that Live Oak off-site mitigation of adverse impacts is located within the same hydrologic basin; SJRWMD staff appropriately determined that Live Oak Reserve would not have an adverse cumulative impact. Mitigation Live Oak's mitigation plan consists of both on-site and off-site preservation. The proposed on-site component of the mitigation plan entails the preservation of 19.3 acres of herbaceous marsh, 373.2 acres of forested wetlands, and 124.9 acres of uplands. The mitigation plan preserves approximately 5.65 acres of isolated wetlands on-site, and approximately 386.86 acres of RHPZ wetlands on-site. The cornerstone of Live Oak's on-site mitigation is the preservation of the Econ River forested floodplain swamp, as well as two upland areas, in the southwestern corner of the property. One of the upland areas is a 15-acre upland scrub island on the east side of the river that is surrounded by forested wetlands. The other upland area is 24 acres of uplands located near the Econ River on its west side. Portions of both uplands are within the RHPZ. Both the forested floodplain and the associated upland areas provide habitat of regional ecological significance. The forested floodplain wetlands and the uplands that are part of the RHPZ are protected to a large degree by SJRWMD regulations. These regionally significant wildlife communities, however, can be temporarily, but chronically, impacted, if not permanently degraded, by timbering and other activities that are relatively unregulated. Live Oak proposes to protect and preserve these areas by placing them in a conservation easement. Placing Econ River forested floodplain wetlands and the upland RHPZ areas in a conservation easement will provide a greater level of protection and assurance that they will mature to an "old growth" condition, which will benefit many wildlife species. The Econ River floodplain wetlands, the upland scrub island and the small isolated wetland in the scrub island will accommodate the smaller wildlife species that currently use the Live Oak Reserve property. Live Oak has preserved most of the larger isolated wetlands with high ecological value. The large isolated wetlands preserved on-site will continue to maintain a high level of ecological function even with the surrounding development. Wildlife, such as frogs, toads, snakes, and wading birds will continue to use those wetlands. The on-site portion of the mitigation plan preserves approximately 71.87 acres of upland buffers, of which 2.04 acres are located in 25-foot buffers and 69.83 acres are located in 50- foot RHPZ buffers. The buffer areas will be placed in a conservation easement. The wildlife values of the uplands on this property that are not within the RHPZ are protected to some degree by local government regulations; they are, however, largely unprotected by the existing regulations of SJRWMD. Without the proposed conservation easements, this habitat may be developed or significantly degraded by other activities. As a component of its on-site sandhill crane nesting site management plan, Live Oak preserves a 6.83-acre upland buffer next to wetland 21, which hosts a sandhill crane nest. Additionally, Live Oak provides enhancement of 3.88 acres on the southside of wetland 21 within the 6.83-acre buffer area by converting this area to improved pasture for sandhill crane foraging habitat. The mitigation plan sufficiently offsets the impacts to the smaller isolated wetlands, even if these wetlands have more than a typical resource value. When evaluating impacts and mitigation, Applicant's Handbook Section 12.2.3.7 requires the SJRWMD to evaluate the predicted ability of the wetland or other surface water to maintain their current functions as part of the proposed system once the project is developed. Many of the smaller isolated wetlands, when located in a natural setting such as a pine flatwood, are very critical and provide very high ecological value. However, once a project is developed and the small isolated wetland is surrounded by homes, the resource value of the small isolated wetland is diminished. Many of the smaller wildlife species, such as frogs and snakes, will be extirpated from the developed area of property, whether or not the smaller isolated wetlands remain. SJRWMD considered the value of the off-site mitigation to offset the adverse impacts to the smaller isolated wetlands. In determining the adequacy of the preservation component of the mitigation plan, SJRWMD staff did not rely upon any specific rule, regulation, or comprehensive plan of the City of Oviedo. However, the staff did consider the overall protections afforded by the regulatory and comprehensive plan requirements of the city and determined that preservation of the mitigation areas by conservation easement provided greater assurance that these areas will be protected than the local government rules, regulations, and comprehensive plan. The off-site component of the mitigation plan is the contribution of $160,525 towards participation in the SJRWMD acquisition of a conservation easement over the 3,456 acre Yarborough parcel. The Yarborough parcel is located in the northeastern corner of the Econ River Hydrologic Basin. The Yarborough parcel encompasses property north and south of the Econ River. A portion, mostly sovereign lands, lies within the Puzzle Lake/Upper St. Johns River Hydrologic Basin. The Yarborough parcel is part of a large working ranch. The parcel contains improved and unimproved pasture, significant cabbage palm hammocks, pine flatwood communities, and freshwater marsh. Live Oak's participation equates to the acquisition of a conservation easement over 200 acres of the Yarborough parcel. However, Live Oak is not purchasing any particular 200 acres with the Yarborough parcel. Live Oak's contribution is applied to 200 acres of the Yarborough parcel within the Econ River Hydrologic Basin. SJRWMD estimates that of the 200 acres, 165 acres are wetlands and 35 acres are uplands. This assessment is based on the composition of wetlands and uplands on the Yarborough property within the Econlockhatchee River Hydrologic Basin. SJRWMD has purchased development rights over the Yarborough parcel. Yarborough is authorized to continue its cattle operation on the Yarborough parcel for 20 years in accordance with the conditions of the conservation easement. However, Yarborough is not permitted to increase the amount of improved pasture or further develop the parcel. On the contrary, the conservation easement requires Yarborough to decrease the number of cattle on the parcel over the next 20 years. Purchase of the conservation easement over the working ranch has positive environmental benefits. The conservation easement will protect the wildlife species that use the ranch. This environmental benefit can be used to offset adverse impacts on the Live Oak Reserve property. To participate in this type of mitigation, the acquisition must be imminent so that the SJRWMD is reasonably assured that the purchase will go forward. Participation is precluded for a parcel after its acquisition is concluded. Live Oak's mitigation plan, with its on-site and off- site components, offsets Live Oak Reserves adverse impacts. SJRWMD calculates the mitigation ratio and compares it to the guidelines in the Applicant's Handbook to determine if mitigation is adequate. SJRWMD however, is not required to adhere to any set ratio. The upland preservation ratio (area preserved to area impacted), excluding the 12 acres of uplands along the upland cut ditches and the Yarborough parcel uplands, is 6 to one. The rule guidelines for upland preservation is from 3 to one to 20 to one. The wetland preservation ratio is 15.5 to one. The rule guidelines for wetland preservation is from 10 to one to 60 to one. Public Interest Criteria Live Oak Reserve will not have any effect on the public health, safety or welfare or property of others. Because the mitigation plan adequately offsets all adverse impacts, Live Oak reserve will not adversely affect the conservation of fish and wildlife, including endangered or threatened species or their habitats. Because of the benefits of lowering the discharge rates in the post-development condition and reducing the velocity of stormwater in Brister Creek, Live Oak Reserve will reduce the potential for erosion. Live Oak Reserve will not have any affect on the fishing or recreational values or marine productivity in the vicinity of the site. Live Oak Reserve will be of permanent nature. However, its adverse impacts have been offset by mitigation. The permanence of the project is beneficial in that it provides treatment of untreated off-site runoff from county road 419 by the Live Oak surface water management system and it reduces the discharge rate of stormwater down Brister Creek. Therefore, the permanence of the project is not contrary to the public interest. In accordance with Section 373.414, Florida Statutes, the Florida Department of State Division of Historical Resources determined that the Live Oak Reserve project will have no possible impact to historic properties listed, or eligible for listing, in the National Register of Historical Places, or otherwise of historical or architectural value. Furthermore, the Division of Historical Resources determined that the project is consistent with Florida's Coastal Management Program and its historic preservation laws and concerns. The current condition and relative value of functions being performed by the various vegetative communities on the Live Oak Reserve property is good. However, there is no guarantee that the value and functions would remain good if the property is not managed for species like the sandhill crane or if agricultural and silvicultural practices continue to occur on the property. The mitigation plan, preserving regionally ecologically significant wetland and upland communities on both the Live Oak Reserve and Yarborough parcel by conservation easement, should provide a greater protection of those communities than what currently exists.

Recommendation Based on the forgoing, it is RECOMMENDED That a final order be entered granting Live Oak's application for a conceptual approval environmental resource permit with the conditions set forth in the SJRWMD technical staff report dated July 16, 1998, with the exception of condition 8, deleted by stipulation. DONE AND ENTERED this 2nd day of November, 1998, in Tallahassee, Leon County, Florida. MARY CLARK 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 Filed with the Clerk of the Division of Administrative Hearings this 2nd day of November, 1998 COPIES FURNISHED: Henry Dean, Executive Director St. Johns River Water Management District Post Office Box 1429 Palatka, Florida 32178-1429 Scott M. Price, Esquire J.A. Jurgens, P.A. 505 Wekiva Springs Road Longwood, Florida 32779 Charles H. Griffin, pro se 250 West 7th Street Chuluota, Florida 32766 Michael L. Gore, Esquire Meredith A. Harper, Esquire Ken W. Wright, Esquire Shutts and Bowen, LLP 20 North Orange Avenue Suite 1000 Orlando, Florida 32801 Anthony J. Cotter, Esquire St. Johns River Water Management District Post Office Box 1429 Palatka, Florida 32178-1429

Florida Laws (4) 120.569120.572.04373.414 Florida Administrative Code (5) 40C-4.04140C-4.30140C-4.30240C-4.38140C-41.063
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DEPARTMENT OF ENVIRONMENTAL REGULATION vs. WILLIAM A. ROMAINE AND B AND W MARINE CONSTRUCTION, INC., 87-003138 (1987)
Division of Administrative Hearings, Florida Number: 87-003138 Latest Update: Mar. 02, 1988

The Issue The following issues have been raised by the Department: Did the Respondents carry out any dredge, fill and bulkhead activities on Mr. Romaine's land within the "waters of Florida"; if so, to what extent? If dredge, fill and bulkhead activities took place within the waters of Florida, did they cause any damage to the natural resources the Department is charged with protecting; and, if so, to what extent? If such activities took place within the waters of Florida, what actions would be appropriate to remedy the violations and the damage caused? What is the amount of expense and damage, if any, which the Respondents should be required to pay to the Department?

Findings Of Fact Mr. Romaine and his wife Purchased land along the shore of the St. Johns River on December 10, 1984. The property was purchased from Milton C. and Cheri A. Rosberg and was secured by mortgage from James L. Tison, Jr., and Frances S. Tison. The land purchased by the Romaines (hereinafter referred to as the "Property") is located on the westerly bank of the St. Johns River in Clay County, Florida. The Property is more particularly described in the copy of the Warranty Deed accepted into evidence as the Department's exhibit 1. The property immediately to the north of the Property is owned by Mr. Rosberg. The property immediately to the south of the Property is owned by Mr. and Mrs. Tison. The Tisons have resided on the property to the south of the Property for approximately 27 years. The Tisons formerly owned the Property. Mr. Tison mowed the grass on the Property and otherwise maintained the Property prior to its sale. The Tisons are familiar with the shoreline of the St. Johns River along the Property both before and after December of 1985. During the latter part of 1985, Mr. Romaine contracted with B & W for the construction of a bulkhead along the western border of the Property and the St. Johns River. From approximately December 3, 1985, to December 7, 1985, a bulkhead was built along the portion of the Property fronting on the St. Johns River. No application for dredge and fill or bulkhead activities was filed with the Department with regard to the activity on the Property, and no such permit was issued by the Department. Mr. Romaine relied upon B & W to obtain any permits required for the construction of the bulkhead on the Property. The Department was not asked whether a permit was required for the construction of the bulkhead on the Property. Other State and federal agencies were consulted concerning their jurisdiction over the construction of the bulkhead on the Property. In addition to the portion of the bulkhead constructed on the Property, approximately 31 feet of bulkhead was constructed from the border of the Property with Mr. Rosberg's property north to a dock located on Mr. Rosberg's property. Mr. Rosberg gave Mr. Romaine permission to use the dock in exchange for the construction of this portion of the bulkhead. For purposes of presenting evidence, the Department divided the bulkhead constructed along the Property into two sections: Area "A" and Area "B." Area A consists of a portion of the bulkhead which begins at the border of the Property and Mr. Rosberg's property and runs in a relatively straight line to the south for approximately 48.2 feet. The bulkhead then begins a gradual, then more pronounced, curve to the west. This is the end of Area A. The bulkhead in Area B goes almost perpendicular to the tangent of the curve in a southern to southwesterly direction in a straight line for approximately 23 feet. The bulkhead then makes a sharp turn to the west and proceeds in a straight line for approximately 12.5 feet where it intersects with the Property's southern boundary. Areas A and B are shown on the Department's exhibit 2 and Romaine exhibit 8. The designation of Areas A and B on these exhibits was not prepared by a licensed surveyor; the designation was intended only as an approximate drawing of portions of the Property. A wetland area is an area which experiences flooding or inundation of water often enough for the area to become defined by species of plants and soils characteristic of areas subject to flooding or inundation of water. Wetlands are potentially the most important part of a water body. Wetlands can maintain water quality, acting as the "kidneys" of a water body, provide habitat not found elsewhere, act as a flood storage area, protect against erosion and play an essential role in the life cycle of aquatic plant and animal life. Water quality will deteriorate if wetlands are destroyed. The wetlands that border the St. Johns River act as a flood plain where water is stored during periods when the River is high. The determination of the extent, if any, of the Department's jurisdiction over the bulkhead built on the Property, is more difficult in this case than in a case where a permit is applied for because of the inability of the Department's experts to examine the Property in its natural, undisturbed state. Because of the changes to the natural state of the Property, including filling activities, many of the natural indicators used to determine the Department's jurisdictional line on the Property have been eliminated or altered. If there is insufficient physical or other evidence to the contrary, the landowner should be given the benefit of any doubt the Department has in setting the Department's jurisdictional line and a line of restoration where property is examined after it has been altered. In determining the extent of the Department's jurisdiction in this case, the starting point is the St. Johns River itself. The open water of the St. Johns River is a water body over which the Department has jurisdiction pursuant to the Florida Administrative Code. Area B used to be a wetlands area prior to the placement of the bulkhead on the Property and the placement of fill behind the bulkhead. This finding of fact is supported, in part, by the location of a large cypress tree, which is a wetlands tree. This tree is the first tree encountered behind the bulkhead in Area B and is the dominant upper canopy vegetation. This tree has been marked by a red "X" on the Department's exhibits 2, 3 and 7. Additionally, the area to the east and south of the bulkhead (between the bulkhead and the St. Johns River) still remains as wetlands. Because of the alteration of Area B by the bulkhead and the placement of fill behind the bulkhead, it is not possible to determine exactly how far the Department's jurisdictional line goes landward from the shore of the St. Johns River. At a minimum, the area between the dashed line and the bulkhead on the Department's exhibit 3 constitutes wetlands and lands within the Department's jurisdiction. By filling the area identified in the Department's exhibit 3 as within the Department's jurisdiction, wetlands of the St. Johns River have been destroyed. This has resulted in the elimination of an area which served the functions of wetlands as explained in findings of fact 10-12. To ignore the fact that the construction of the bulkhead was completed without a permit or to now grant a permit could affect other bulkhead and fill projects along the St. Johns River. Even though the effect of the filling of Area B may be small, the cumulative impact of the destruction of multiple small areas of wetland would have an overall negative effect on the quality of the St. Johns River. In order to remedy the damage in Area B the original status quo of the area should be restored. This requires the removal of the bulkhead in Area B and all fill added behind the bulkhead in Area B down to the original contour of the land and revegetating the area with indigenous wetland vegetation. During this process, steps must be taken to control turbidity and to prevent pollution of adjacent waters. Additionally, it would be appropriate to require that numbered paragraphs 5c, 6, 7, 8 and 9, in the Department's exhibit 10, be complied with in restoring Area B. The Department's experts were unable to say where the Department's jurisdictional line was located in Area A of the Property because there was no physical evidence remaining after construction of the bulkhead from which it could be determined where the natural shoreline of the St. Johns River was located at the time of the Department's examinations. Despite the inability of the Department's experts to precisely locate the Department's jurisdictional line based upon the current condition of Area A, other evidence supports a finding of fact that the bulkhead in Area A was built within the jurisdiction of the Department. In particular, the testimony of Mr. and Mrs. Tison and the Department's exhibits 12A-12D, support a finding that the portion of the bulkhead constructed in Area A of the Property extends into the waters of the St. Johns River to the east of the former shoreline of the Property. Fill was then placed into the River between the bulkhead and the former shoreline. Mr. Tison drew a line in red on the Department's exhibit 11. This line represents the approximate former shoreline of the St. Johns River prior to the construction of the bulkhead on the Property. The area between this red line and the bulkhead is within the Department's jurisdiction. B & W used a Case 410 tractor backhoe to construct the bulkhead. This tractor had outside wheels eighty-two inches apart and it weighed approximately 14,000 pounds. A bucket at the end of the tractor was used for digging. The bucket was approximately two feet wide and the arm, when fully extended, could perform work approximately eight feet away from the body of the tractor. After digging a trench where the bulkhead was to be placed in Area A, a water jet was used to sink four-by-six posts five feet apart. Two-by-eight boards were then stacked between the posts six boards high. The backhoe was used to dig a hole approximately twelve feet behind each post where a deadman was sunk or a tieback was attached to each post. The Department's exhibits 12A-12D are Photographs of Area A during the construction of the bulkhead. They all show water of the St. Johns River between the posts to the west where the shoreline of the St. Johns River was located. Based upon the size of the backhoe, Mr. Woodyard's testimony that the backhoe's wheels, while the backhoe straddled the bulkhead area to dig the trench, were on dry land is not credible. The Department's exhibits 12A and 12D show a leaning cypress tree in the waters of the St. Johns River. The bulkhead posts pictured in these exhibits are several feet into the River. In Romaine's exhibits 3 and 4, and the Department's exhibit 4 the same leaning cypress tree is several feet landward of the bulkhead. The Department's exhibit 12C shows the bucket of the backhoe totally submerged in the waters of the St. Johns River. This further supports a finding that dredging and filling occurred in the waters of the St. Johns River. When the Department's exhibits 12A-12D (photographs of the bulkhead construction in Area A) are compared with Romaine exhibits 3 and 4 and other photographs taken after construction of the bulkhead in Area A, it is evident that fill was placed between the bulkhead and the former shoreline of the St. Johns River. The construction of the bulkhead in Area A has caused the same damage that the construction of the bulkhead in Area B caused. The same remedy suggested for Area B would also be appropriate for Area A. The Department incurred $730.17 in its investigation of this matter and the preparation for the formal hearing of this case.

Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that a Final Order be issued finding that the Respondents have violated Section 403.161(1)(a) and (b), Florida Statutes (1987). It is further RECOMMENDED that the Final Order provide that the Respondents, jointly and severally, must pay $730.17 to the Department within twenty (20) days from the date of the Final Order in this case in reimbursement of the Department's expenses. Payment shall be made by cashiers check or money order and shall be payable to the Department of Environmental Regulation. Payment shall be sent to the Department of Environmental Regulation, Northeast District, 3426 Bills Road, Jacksonville, Florida 32207. It is further RECOMMENDED that the Final Order Provide that the Respondents are to restore the areas of the Property described in this Recommended Order within Sixty (60) days from the date of the Final Order as follows: All of the vertical bulkhead located on the Property shall be removed; All fill material within the jurisdiction of the Department shall be removed and placed upland of the Department's jurisdiction as described in this Recommended Order (the portion of Area A between the St. Johns River and the line drawn in red on the Department's exhibit 11 and the portion of Area B between the St. Johns River and the dashed line on the Department's exhibits 2, 3 and 7. The area from which the fill material is removed shall be restored to the elevation which existed prior to the violation; and During restoration of the Property, adjacent areas within the jurisdiction of the St. Johns River shall not be disturbed unless otherwise approved by the Department in writing. It is further RECOMMENDED that the Final Order provide that the Respondents shall carry out the activities described in paragraphs 5c, 6, 7, 8 and 9 of the Department's exhibit 10. It is further RECOMMENDED that the Final Order Provide that the Respondents are not to undertake any additional dredge and fill activities within the waters of Florida, other than the restoration measures described in the Final Order, without obtaining a permit or written notice that the work is exempted from permitting from the Department. It is further RECOMMENDED that the Final Order provide that the Respondents are to allow authorized representatives of the Department access to the Property at reasonable times for purposes of determining compliance with the Final Order in this case and with Chapter 403, Florida Statutes, and the Department's rules promulgated thereunder. DONE and ENTERED this 2nd day of March, 1988, in Tallahassee, Florida. LARRY J. SARTIN Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 2nd day of March, 1988. APPENDIX The parties have submitted proposed findings of fact. It has been noted below which proposed findings of fact have been generally accepted and the paragraph number(s) in the Recommended Order where they have been accepted, if any. Those proposed findings of fact which have been rejected and the reason for their rejection have also been noted. Petitioner's Proposed Findings of Fact: Proposed Finding Paragraph Number in Recommended Order of Fact of Acceptance or Reason for Rejection 1 Hereby accepted. 2 1. 3 3 and 9. 4 13. 5 These proposed findings are not necessary. They affect the weight to be given to some of the evidence. 6 10. 7 11. 8 12. 9 14. The portion of this proposed finding after the first sentence constitutes proposed conclusions of law. 10. Hereby accepted. 11 13. 12 20. The portion of this proposed finding after the first two sentences constitutes proposed conclusions of law. 13-15 These paragraphs are not proposed findings of fact. They are summaries of testimony. See 15-17. 16 This paragraph is not a proposed finding of fact. It is a summary of testimony concerning law. 17-19 These paragraphs are not proposed findings of fact. They are summaries of testimony. See 18-19 and 28. These proposed findings are not necessary. They affect the weight to be given to some of the evidence. Summary of testimony. 22 6. 23 29. 24-26 Summary of testimony. See 3 and 21. The weight of the evidence did not support a finding that the fill in Area A extended into the St. Johns River approximately 20 feet at its widest point. 27 5 and 7. 28 8. 29 Hereby accepted. 30 22. 31-32 Summary of testimony. See 23-25. 33 25. Not Supported by the weight of the evidence. 26. The last sentence is not supported by the weight of the evidence. Cumulative and unnecessary. 37 27 38-39 Conclusions of law and argument. 40-41 Hereby accepted. Mr. Romaine's Proposed Findings of Fact: The first paragraph under the Findings of Fact portion of Mr. Romaine's proposed recommended order does not contain any relevant findings of fact. Summary of testimony and irrelevant proposed findings of fact. Summary of evidence. The following numbers correspond to the numbers of the sentences contained in Mr. Romaine's "Procedural Statement." 1 and 3. 4 and 7. Hereby accepted. Irrelevant. 5-6 Not supported by the weight of the evidence. See 5 and 6. 7-17, 19-27 32-39 and 42 Irrelevant or not supported by the weight of the evidence presented at the formal hearing. 18, 28-31 and 40-41 Hereby accepted. COPIES FURNISHED TO: JOHN P. INGLE, ESQUIRE STATE OF FLORIDA DEPARTMENT OF ENVIRONMENTAL REGULATION TWIN TOWERS OFFICE BUILDING 2600 BLAIR STONE ROAD TALLAHASSEE, FLORIDA 32399-2400 WILLIAM A. ROMAINE 2127 WINTERBOURNE, WEST ORANGE PARK, FLORIDA 32073-5621 ROBERT E. WOODYARD, PRESIDENT B & W MARINE CONSTRUCTION, INC. 4611 LAKESIDE DRIVE JACKSONVILLE, FLORIDA 32210 DALE TWACHTMANN, SECRETARY STATE OF FLORIDA DEPARTMENT OF ENVIRONMENTAL REGULATION TWIN TOWERS OFFICE BUILDING 2600 BLAIR STONE ROAD TALLAHASSEE, FLORIDA 32399-2400 DANIEL H. THOMPSON, ESQUIRE STATE OF FLORIDA DEPARTMENT OF ENVIRONMENTAL REGULATION TWIN TOWERS OFFICE BUILDING 2600 BLAIR STONE ROAD TALLAHASSEE, FLORIDA 32399-2400

Florida Laws (5) 120.57403.031403.061403.121403.161
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WEST COAST REGIONAL WATER SUPPLY AUTHORITY vs. SOUTHWEST FLORIDA WATER MANAGEMENT DISTRICT, 87-004644 (1987)
Division of Administrative Hearings, Florida Number: 87-004644 Latest Update: Feb. 22, 1998

The Issue The issue in this case is whether the Southwest Florida Water Management District (District) should approve applications to renew consumptive use permits filed on behalf of the West Coast Regional Water Supply Authority (Authority), Pinellas County (County), and Freeman F. Polk (Polk), and if so, what conditions should be included in the permits. The District proposes to issue renewed permits to these applicants with specified conditions, but Polk seeks certain additional condition; to the permits sought by the Authority and the County, and similarly, the Authority and County seek the imposition of additional conditions on Polk's permit. The parties seek these additional conditions to insure that the permitted uses will not interfere with any legal use of water existing at the time of the applications, and will also not cause the water table to be lowered so that lake stages or vegetation are adversely and significantly affected on lands other than those owned, leased or controlled by the applicants.

Findings Of Fact The following findings are based upon relevant stipulations of the parties: The Authority is a special taxing district of the State of Florida encompassing Pasco, Pinellas and Hillsborough Counties, which was created by interlocal agreement on October 25, 1974. It is responsible for the design, construction, operation and maintenance of facilities in locations, and at times, necessary to insure that an adequate supply of water will be available to all persons residing within its boundaries. The District is an agency of the State of Florida which is charged with regulating consumptive uses of water in a sixteen county area, including Pinellas, Pasco and Hillsborough Counties. It has implemented a permitting program that requires all persons seeking to withdraw water in excess of an annual average daily rate of 100,000 gallons, and a maximum daily rate of 1,000,000 gallons, to obtain a consumptive use permit. The Cypress Creek Wellfield is located on a 4,895 acre site in central Pasco County, lying east of U.S. 41 between State Roads 52 and 54. The District owns 3,623 acres of this Wellfield, and the remaining 1,272 acres are owned by the City of St. Petersburg. Construction on the Cypress Creek Wellfield commenced in 1974, and it currently consists of thirteen production wells, numerous monitor wells, several thousand feet of transmission lines, two 5 gallon storage tanks, a pump station and several buildings. The City of St. Petersburg, Pinellas and Pasco Counties, and the District have transferred their rights and privileges in this Wellfield, as well as the Wellfield facilities, to the Authority by contracts entered into in November, 1973, and August 1974. Water produced at the Cypress Creek Wellfield is sold at cost by the Authority to users which include the City of St. Petersburg and Pinellas County. The water produced at this Wellfield comprises 29% of the County's total water system demand (20 million gallons a day), and 25% of the City of St. Petersburg's total system demand (10 million gallons a day). These water systems serve approximately 470,000 and 330,000 persons, respectively. In March 1978, the District issued a six-year consumptive use permit to the Authority, the City of St. Petersburg, and the County authorizing an annual average and maximum daily withdrawal of 30 million gallons a day from the Cypress Creek Wellfield. The Authority also began a detailed ecological monitoring program in, and around, this Wellfield in 1978. A three-year permit was then issued to the Authority in December, 1982, authorizing withdrawals of 30 million gallons a day, annual average, and 40 million gallons a day, maximum daily, from the Wellfield. The District determined by Order No. 82-28, dated December 1, 1982, that an average annual daily rate of withdrawal of 30 million gallons, and a maximum daily rate of withdrawal of 40 million gallons from the Cypress Creek Wellfield was a reasonable-beneficial use, was consistent with the public interest, and would not interfere with any legal use of water existing at the time of that application. An application for renewal of the Cypress Creek Wellfield consumptive use permit at the quantities permitted in 1982 was filed with the District on November 7, 1985, by the Authority, the County and the City of St. Petersburg. The continued withdrawal of water from the Cypress Creek Wellfield at an annual average daily rate of 30 million gallons, and a maximum daily rate of 40 million gallons is needed in order to meet the water supply demands of the residents of Pinellas and Pasco Counties, is in the interest of residents of Pinellas County, and will not cause the rate of flow of a stream or other watercourse to be lowered below the minimum rate of flow established by the District. The regulatory level of the potentiometric surface established by the District for the Cypress Creek Wellfield has never been exceeded by prior withdrawals of water at permitted rates. Continued withdrawal of water from the Cypress Creek Wellfield at an annual average daily rate of 30 million gallons, and a maximum daily rate of 40 million gallons will not cause the potentiometric surface level to be lowered below sea level, or any regulatory level established by the District, will not cause the surface level of water to be lowered below any minimum established by the District, and will not significantly induce salt water encroachment. The Cross Bar Ranch Wellfield is located on a 8,060 acre site in north central Pasco County, lying approximately one mile south of the Pasco-Hernando County line, and immediately east of U.S. 41. The Cross Bar Ranch Wellfield property has been owned by Pinellas County since 1976. Wellfield construction was completed in 1981. By agreement entered into on April 11, 1979, the Authority is obligated to sell the County water produced from the Cross Bar Ranch Wellfield, but any excess not currently being used by the County may be sold to other members of the Authority. A significant amount of water produced at Cross Bar Ranch is pumped to the Cypress Creek Wellfield where it is combined with that Wellfield's water, and then distributed to Pinellas and Hillsborough Counties, as well as the City of St. Petersburg, for further distribution. The water produced at these two Wellfields in combination accounts for about 60% of the County's total water system demand. Following pump tests performed from 1977 to 1979, as well as an ecological monitoring program, the District issued a modified consumptive use permit to the Authority by Order 80-9, dated February 6, 1980, for Cross Bar Ranch Wellfield. The District determined that withdrawals at an average daily rate of 30 million gallons, and a maximum daily rate of 45 million gallons from Cross Bar Ranch Wellfield was a reasonable beneficial use, was consistent with the public interest, and would not interfere with any legal use of water existing at the time of that application. On November 7, 1985, the Authority and County jointly applied to the District for renewal of the consumptive use permit for Cross Bar Ranch Wellfield at the current permitted quantities of an annual average daily rate of 30 million gallons, and a maximum daily rate of 45 million gallons. These withdrawal rates are needed in order to meet present and future water supply demands of the residents of Pinellas, Pasco and Hillsborough Counties, provide water for environmental mitigation, and make up water when one or more production facilities cannot pump at their permitted levels. The withdrawal of water from Cross Bar Ranch Wellfield at permitted rates will not cause the level of the potentiometric surface to be lowered below sea level, or any regulatory levels established by the District, and will not significantly induce salt water encroachment. Jumping Gully is the only stream or watercourse in the vicinity under the influence of this Wellfield, and the District has not established a minimum rate of flow for Jumping Gully. Hydrologic data collected from monitor wells located at the Cross Bar Ranch Wellfield show the potentiometric surface has been above mean sea level during the operation of this facility. The District has renewed consumptive use permits for a period of ten years for the City of St. Petersburg, and the City of Lakeland Power Plant. The Authority owns, leases or otherwise controls the area within both the Cypress Creek and Cross Bar Ranch Wellfields. Polk owns, leases or otherwise controls the property identified in his amended permit application of July 26, 1988. Both the Authority's and Polk's permit applications were filed on the proper forms, and otherwise comply with the District's procedural requirements for consumptive use permits. Each party has standing to participate in this case. The proposed uses of water which are the subject of these proceedings are reasonable beneficial uses, and in the public interest. The only permit criteria that remain at issue in this case are set forth in Rules 40D-2.301(1)(c) and (2)(e), Florida Administrative Code. The following findings of fact are based upon the evidence presented at the hearing: Polk was first issued a consumptive use permit for Ft. King Ranch in August, 1981, after both the Cypress Creek Wellfield and Cross Bar Ranch Wellfield had each been permitted to withdraw 30 million gallons per day. Polk's permit authorized him to withdraw ground water at an average annual rate of 420,000 gallons per day, and a maximum rate of approximately 1.94 gallons per day for irrigation of pasture grass and citrus, and cattle drinking water. A temporary consumptive use permit issued to Polk in August, 1981, was signed by him and states on its face that these additional groundwater withdrawals were necessary because of drought conditions. A modified permit was issued to Polk by the District in July, 1982, authorizing him to increase his withdrawals to an average annual rate of approximately 1.94 gpd, and a maximum rate of 5.9 gpd. Polk's wells are not metered. Prior to August, 1981, Polk did not have man made surface or groundwater withdrawal on his property. As it relates to this proceeding, the property owned, leased or otherwise controlled by Polk is known as the Ft. King Ranch, which is generally located between the Cross Bar Ranch and Cypress Creek Wellfields, and consists of approximately 6,000 acres. The Ft. King Ranch is comprised of five tracts which were separately acquired by Polk commencing in January, 1969, and ending in 1984. By 1978, Polk had acquired two of these five tracts. He leased a third tract beginning in 1971, before acquiring an ownership interest in 1981. These three tracts were designated parcels A, B, and C, and are located in the eastern and northern portion of the Ranch. These three parcels were the only tracts owned, leased or otherwise controlled by Polk at the time the first Cypress Creek and Cross Bar Ranch Wellfield permits were issued in 1978. The western tracts were acquired in 1982 and 1984, and were also referred to as the AL-BAR Ranch at hearing. Polk uses the Ft. King Ranch for a cow-calf operation, and also sod farming and seeding. From 1969 to approximately 1978, there was sufficient surface water on the Ft. King Ranch for these farming activities to be carried out without irrigation or wells. Water holes used by cattle were always wet, and lakes on the property were used for swimming and fishing. His pasture, hay, seed and sod grasses received moisture solely from rainfall. However, Polk did not establish the amounts of water used in his operations prior to the issuance of Wellfield permits. In 1976, parcels A, B, and C were used for these purposes, although Polk has frequently changed the specific size and location of acreages devoted to these land uses. In order to correct flooding that occurred on portions of the Ft. King Ranch during times of heavy rainfall, Polk sought the advice of the Soil Conservation Service in the mid-1970's. He was advised to construct a series of dikes and swales to control the flow of surface water on his property. During 1980 and 1981, Polk constructed a network of swales and ditches to divert and control the flow of surface water from portions of the Ranch needing less water to those requiring wetter conditions, such as his sod and seed operation. The swales interconnect lakes and ponds on his Ranch. He also constructed a levee on the property, and installed a lift pump. These activities have converted most of the eastern portion of his ranch to improved pasture and sod grasses, and virtually eliminated native vegetation. Polk had no professional help in the construction of his ditch-swale systems, or the levee. Beginning in approximately 1980, drier conditions were experienced at the Ranch. One of the ten driest years on record in this area occurred in 1980, and continued drought conditions in 1981 caused the District's Governing Board to declare a water shortage, and impose water conservation measures throughout the District. Some lakes and cypress swamps dried completely and failed to recharge to pre-1980 levels after rainfall. Due to reduced water availability since 1980, including drought conditions in 1985, Polk's calf weights have decreased, while the number of non-breeding cows has increased. Feed bills have increased due to reduced hay and grass production at the Ranch. Polk's bahia seed and sod crops have also declined since 1980 due to reduced surface water levels. Adequate and stable moisture is essential for seed production, and while such conditions did exist on the Ft. King Ranch prior to 1980, they have been absent since 1980. Due to the drier conditions which he noted in 1980 and 1981, Polk filed a formal complaint with the District in 1981. A site visit and pump test were conducted, and the District concluded that the Wellfields were causing less than a one foot drawdown in the Ft. King Ranch water table, and that dry conditions at his ranch were due primarily to drought. In 1985, Polk complained to the District again, and requested that it augment two lakes within the Ranch. After review of surrounding lake conditions, the District declined his request since Polk's lakes had not experienced water level declines atypical of lakes well beyond the influence of the Authority's Wellfields. Studies of water level elevations in the area indicate that the effect of Cypress Creek Wellfield pumpage is quite small when compared to natural changes in water levels due to variable rainfall and evapotransporation. Rainfall in this region is variable, and there has been a significant negative trend over time in surficial and potentiometric water levels that predates Wellfield pumpage. According to J. B. Butler, who was accepted as an expert in hydrology, the swales, dikes and levees constructed by Polk have not caused the water table or surface water level reductions experienced since late 1981. Rather, these are an attempt to divert and retain water on the property, and even in their absence, there would be no significant flow of surface water across Ft. King Ranch from an east to west direction. In addition, Butler testified that a fence line berm constructed along the northern border of the Ranch is an insignificant obstacle to the flow of surface water from the north to south across the Ranch when compared to topographic features, and has had no impact on the water tables of the Ranch. However, evidence introduced at hearing established that as early as 1981, the staff of the District concluded that the swales and elevated fence lines could be aggravating low water conditions by increasing evaporation and leakance, and by excluding surface water which would have entered the Ft. King Ranch from the north. The Authority offered competent substantial evidence to rebut the Butler testimony. Thomas Schanze, who was accepted as an expert in agricultural engineering, testified that Polk's elevated berm along his northern fence line has significantly restricted the flow of surface water onto Ft. King Ranch, and has contributed to the eastern portion of the Ft. King Ranch becoming a closed watershed. Between 1984 and 1986, approximately 700 million gallons of surface water have been excluded by Polk's water control and diversion activities. This exclusion has resulted in a diminished water table within the Ft. King Ranch of about one half foot compared with the water table on the northern side of the berm. Surface water cannot flow onto Polk's property until water levels immediately north reach flood stage. Aerial photographs of the Ft. King Ranch and surrounding properties show that the Polk property is significantly drier than surrounding properties, which include predominant wetlands. If the dry conditions experienced by Polk had been due to pumpage, the same dry conditions should be observed on surrounding properties and lands nearer the Wellfields. However, aerial photos show that lands closer to the Wellfields than Ft. King Ranch are less dry than the Ranch itself. This supports the position of the District and the Authority that Polk's own activities have had a significantly greater impact than pumpage on surface and groundwater levels. The reduction in productivity of Polk's farming activities is reasonably related to his northern berm which serves as a dike, preventing water from flowing onto Ft. King Ranch, as well as drought conditions existing in 1980, 1981 and 1985. The cumulative effect of water excluded from this property and dry weather conditions is significant, and accounts for decreased production. It was not established through competent substantial evidence that Polk's decreased production has resulted from any hydrologic impact of Wellfield pumpage. The District's expert in hydrology and ground water modeling, Robert G. Perry, concluded that significant water table declines on Ft. King Ranch due to pumping from Cypress Creek and Cross Bar Ranch Wellfields could not be confirmed. Through groundwater flow modeling and statistical analysis, he concluded that a one foot water table drawdown contour resulting from withdrawals at the rate of 30 mgd for 30 days without any recharge would not reach the Ft. King Ranch. Even in a worse case scenario of 120 days without recharge and pumpage at Cypress Creek of 30 mgd for 30 days, then 40 mgd for 30 days, and finally 30 mgd for 60 days, Perry concluded that the one foot water table drawdown contour would not reach Polk's Ranch. There is some evidence that under a worse case condition, pumpage at the Cross Bar Ranch Wellfield could result in the one foot water table drawdown contour intersecting a small portion of the western tract of the Ft. King Ranch, but this tract was not owned or leased by Polk in 1978, when the first Wellfield permits were issued. Conflicting evidence based upon steady state modeling by Craig Hutchinson of the United States Geological Survey was introduced on behalf of Polk to establish that the cumulative impact of the Wellfields could induce a significant drawdown in the water table in the area between the Wellfields, including the Ft. King Ranch. However, this evidence is rejected as less credible than the analysis conducted by Park and Phillip Davis, who was also accepted as an expert in hydrology and groundwater flow modeling. The steady state approach used by Hutchinson is inappropriate for analyzing the effects of wellfield withdrawals on the water table, because the water table is a dynamic system which is never at steady state. The transient groundwater simulation model used by the District is better suited for an analysis of impacts to the water table, although it does tend to overpredict such impacts, since it accounts for changes in rainfall. The Hutchinson analysis is also unreliable since it is based upon artificially derived antecedent water levels, rather than observed levels. Finally, he did not have required predevelopment water table data, and thus, could not verify water table predictions derived from his steady state model. A transient groundwater flow computer model used by Terry Bengtsson to estimate greater potentiometric surface and water table declines due to withdrawals from the Wellfields than predicted by Park or Davis was discredited, and shown to be unreasonable, by the results of a 28 day pump test in September and October, 1988. According to Rick Stebnisky, who was called on behalf of Polk and accepted as an expert in groundwater hydrology, the combined effect of pumping at the Cross Bar Ranch and Cypress Creek Wellfields has resulted in a significant reduction in water table and potentiometric surface levels at Ft. King Ranch, with such reductions being greater in the southern areas than northern portions of Polk's property. He testified that drawdowns have been noted since pumping began at Cypress Creek in April, 1976, with greater drawdowns occurring closest to the Wellfields, and for this reason drawdowns appear to be related to pumping rather than drought conditions. However, Stebnisky's conclusions were drawn from an overly simplistic hydrographic analysis which ignored factors other than pumpage, such as reduced rainfall, regional trends, surface drainage and non-wellfield pumpage, according to Robert G. Perry, an expert in hydrology and groundwater modeling. Stebnisky was not accepted as an expert in groundwater flow modeling. It was also established that some of the basic assumptions used by Stebnisky in predicting drawdowns were inaccurate, and not based upon accepted hydrologic principles. Therefore, when weighed and considered against other expert testimony, including that of Perry and Dr. J. I. Garcia-Bengochea, Ph.D., an expert in hydrology and environmental engineering, the testimony of Stebnisky is found to lack credibility. While Dr. Garcia-Bengochea agreed with the testimony of Stebnisky that the potentiometric surface and water table levels on the Ft. King Ranch had been somewhat reduced due PAGE 18 MISSING individual well meters, regardless of whether on-site wetlands are being augmented, and is sufficiently accurate for use in evaluating the impact of withdrawals on the water table and Floridan Aquifer. As a condition for renewal of the Authority's permits, the District has required that flow measuring devices or methods be installed for each augmentation discharge point, although generally augmentation of lakes and wetlands within wellfields is not metered. The allowable drawdown levels of potentiometric surface for the Cypress Creek Wellfield established by the District have never been reached. The lowest levels occurred during severe drought conditions in 1981 and 1985. However, even during these times, the lowest potentiometric surface level was 8.53 feet above regulatory levels. Notwithstanding the testimony of Philip Waller, an expert in hydrology, pumping from Polk's irrigation Wellfields have not had a significant impact on the Cypress Creek Wellfield because Waller's model assumptions are extreme, according to Robert G. Perry, whose field of expertise includes groundwater modeling. These unrealistic assumptions included that Polk would operate his irrigation wells at maximum capacity for 120 days, and that there would be no recharge, even though irrigation, like rainfall, would be expected to result in some recharge. Even under these extreme assumptions, Waller's modeling only produced a one foot drawdown at Cypress Creek Wellfield, which would still be well within regulatory levels established by the District, based upon data for the drought years of 1981 and 1985. Since 1979, Cypress Creek Wellfield has averaged approximately 30 million gallons per day, with the maximum withdrawal occurring in May, 1983, when it averaged 34.2 mgd. From 1981 to 1985, the average withdrawals from Cross Bar Ranch Wellfield remained stable at 13 mgd, but since 1986, the pumpage has increased to over 15 mgd due, in part, to the use of water from Cross Bar to compensate for contaminated wells shut down at the Eldridge-Wilde Wellfield. For purposes of Rule 40D-2.301(1)(c), Florida Administrative Code, the District does not consider the use of water that occurs naturally, without pumping or diversion, for use on crops or other agricultural purposes to be, an existing legal use of water, because it does not require a permit. The District does not apply Rule 40D-2.301(2)(e) to protect agricultural crops, but rather to protect naturally occurring vegetation. When an application to renew a consumptive use permit is reviewed by the District, and that renewal does not seek an increase in the quantity of water withdrawals, "legal users" are those present prior to the original permit. On May 17, 1988, a Final Order was entered in DOAH Case No. 88-0693R declaring the District's Rules 40D-2.301(3)(b), (c), and (d), Florida Administrative Code, which otherwise would apply in this proceeding, to be an invalid exercise of delegated legislative authority. The Authority's applications were declared complete by the District on June 18, 1987, and the District staff recommended issuance of these permits on August 14, 1987. Modifications to the draft permit were made by the District on December 28, 1988, and these modified draft permits are acceptable to the Authority. The latest draft permits contain stated conditions which include the requirement that the Authority directly measure the amount of water it uses to augment the water level of on-site wetlands. On February 22, 1989, the Authority and the District filed a Joint Notice of Settlement in Case Number 87- 4644 by which they settled their dispute as to the duration of consumptive use permit renewals for the Wellfields, and provided for a ten year permit for Cypress Creek, and a six year permit for Cross Bar Ranch Wellfield. Polk submitted his original permit application on April 13, 1987, and then amended his request on July 26, 1988. The District has proposed to issue a draft permit to Polk, with stated conditions.

Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is recommended that the Southwest Florida Water Management District enter a Final Order approving the consumptive use permit applications of the West Coasts Regional Water Supply Authority and Pinellas County for the Cross Bar Ranch and Cypress Creek Wellfields, with conditions proposed by the District, and also approving the consumptive use permit application of Freeman F. Polk, with conditions proposed by the District. DONE AND ENTERED this 10th day of July, 1989, in Tallahassee, Florida. 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 10th day of July, 1989. APPENDIX TO RECOMMENDED ORDER, CASE NOS. 87-4644, 87-4645, 87-4647, & 88-1169 Rulings on the District's Proposed Findings of Fact: Adopted in Findings 6, 21. Rejected as unnecessary. Adopted in Finding 6. Adopted in Finding 38. Adopted in Finding 21. Adopted in Finding 11. Adopted in Finding 38. 8-11. Adopted in Finding 20. 12. Adopted in Finding 21. 13-14. Adopted in Finding 22. Adopted in Finding 27. Adopted in Finding 25. 17-19. Adopted in Findings 25, 26. 20-22. Adopted in Findings 26, 28. 23-48. Adopted in Findings 31 through 35. 49-60. Adopted in Findings 28 through 30. 61-64 Adopted in Finding 36. 65-68. Adopted in Finding 37. Rulings on the Authority's Proposed Findings of Fact: Adopted in Finding 1. Adopted in Findings 4, 10. Adopted in Finding 2. 4-6. Adopted in Finding 39. Adopted in Finding 18. Adopted in Findings 21, 22. Adopted in Finding 40. 10-11. Adopted in Finding 3. 12-14. Adopted in Finding 36. Adopted in Findings 6, 38. Adopted in Finding 5. 17-19. Adopted in Findings 6, 21. 20. Adopted in Findings 7, 16. 21-23. Adopted in Finding 41. 24-25. Adopted in Finding 9. 26-27. Adopted in Finding 36. Adopted in Findings 11, 38. Adopted in Finding 10. Adopted in Finding 11. 3132 Adopted in Findings 11, 21. 33. Adopted in Findings 12, 16. 34-36. Adopted in Finding 41. Adopted in Finding 21. Adopted in Finding 24. Adopted in Finding 29. Adopted in Finding 24. 41-42. Adopted in Finding 22. 43-45. Adopted in Finding 25. Adopted in Finding 26. Adopted in Finding 25. Adopted in Finding 26. Adopted in Findings 26, 28. 50-53. Adopted in Finding 20. Adopted in Findings 20, 21. Adopted in Finding 20. Adopted in Finding 37. Rejected as not based on competent substantial evidence. Adopted in Finding 41. Rejected as unnecessary. 60-62. Adopted in Finding 35. 63. Adopted in Finding 36. 64-70. Adopted in Findings 34, 35. 71-76. Adopted in Findings 33 through 35. 77-78. Rejected as unnecessary and irrelevant. 79-80. Adopted in Finding 34. 81-87. Adopted in Finding 32. 88-91. Adopted in Findings 26 through 35. 92-96. Adopted in Findings 29, 30, but otherwise Rejected as unnecessary and cumulative. Adopted in Finding 28. Adopted in Finding 29. 99-100. Adopted in Finding 30. 101-102. Adopted in Finding 37. Rejected as unnecessary and cumulative. Adopted in Finding 37. Rejected in Finding 37. Adopted and Rejected in part in Finding 37 Ruling on Pinellas County's Proposed Finding of Fact: (The County also adopted the Authority's Proposed Findings.) 1. Rejected since the statement proposed by the County is not a finding of fact, but simply a statement on the evidence. Evidence which was not admitted at hearing has not been considered. Rulings on Polk's Proposed Findings of Fact: Adopted in Finding 3. Adopted in Findings 9, 10. Adopted in Finding 21. Rejected in Findings 6, 11, 21. Adopted in Finding 22. Adopted and Rejected in part in Findings 25 through 27. 7-8. Rejected in Findings 25 through 27. Adopted in Finding 25. Adopted in Finding 24. 11-13. Rejected in Findings 24, 29, 30. Adopted in Finding 37. Rejected as argument on the evidence and not a proposed finding of fact. COPIES FURNISHED: Edward P. de la Parte, Jr., Esquire Douglas M. Wyckoff, Esquire 705 East Kennedy Boulevard Tampa, Florida 33602 Thomas E. Cone, Jr., Esquire 202 Madison Street Tampa, Florida 33602 John T. Allen, Jr., Esquire Chris Jayson, Esquire 4508 Central Avenue St. Petersburg, Florida 33711 Bram D. E. Canter, Esquire 306 North Monroe Street Tallahassee, Florida 32302 Peter G. Hubbell, Executive Director Southwest Florida Water Management District 2379 Broad Street Brooksville, Florida 34699-6899

Florida Laws (5) 120.57373.019373.219373.223373.226 Florida Administrative Code (1) 40D-2.301
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