Findings Of Fact On April 23, 1980, the county applied to DER for a permit to place approximately 334,000 cubic yards of sand along the southern 2.4 miles of the eastern shoreline of Key Biscayne to create an additional recreational beach for public use and to control beach erosion. The northern limit of the Project area is the southern boundary of Crandon park, the southern limit is the Cape Florida Lighthouse, and the seaward limit is the "design toe of fill", which results in establishing a new mean highwater line at approximately the 1913 shoreline. No fill will be placed along a 1600-foot area along the shore between 1500-feet and 3100-feet north of the lighthouse, where accretion has occurred since 1913. The re-nourished beach is proposed to average approximately 100 feet in width. On October 15, 1980, DER issued a letter of Intent to deny the requested permit. There are approximately 45 acres of sea grass within the Project Area which are proposed to be covered with sand as a result of the project. Sea grass is a major marine resource in Florida, and the anticipated loss of these 45 acres is one of the primary reason DER proposed to deny the permit application. Transects made by the County in December of 1977, and March of 1978, showed that the sea grass in the Project Area varies in density from "sparse" in approximately half of the Project Area to "dense" in approximately ten percent of the Project Area, with the remainder being considered being "medium" in density. Approximately 25 percent of the area to be filled is barren bottom. Sea grasses serve several important functions in the marine ecosystem. They are a vital and productive link in the marine food chain. By cycling energy from the sun into digestible plant material, sea grasses provide food for various organisms which, in turn, are eaten by other organisms in the food chain. Sea grasses assist in maintaining good water quality by causing a baffling effect which improves clarity, and by assimilating the potentially harmful nutrients from the water column. Sea grass roots bind sediments on the sea bottoms, thereby detering erosion. Additionally, sea grass beds function as prime nursery habitat for juvenile fish and other young marine animals as well as spawning grounds for various marine species. Sea grass beds further provide areas for concealment protection and feeding for all types of marine-creatures. Two types of marine sea grasses predominate in the area off Key Biscayne: Syringodium filiforme, or "manatee grass", and Thalassia testudinum, or "turtle grass". The sea grass beds proposed to be filled by this project are dominated by Syringodium filiforme, a long, slender grass which, when compared to turtle grass, offers less refuge to smaller marine animals because its leaves are slender and round and it does not occur in dense groups. In addition, Syringodium filiforme is not as good a soil stabilizer as turtle grass, due primarily to its root structure. It also offers comparatively less surface area for the attachment of epiphytes and algae. A significant portion of the sea grasses in the northern part of the Project Area are ephemeral: that is, they have grown in since 1967, and could very likely be destroyed during a major storm event. It is unlikely that they will be in place for sufficient periods of time to become a major influence on the grain size of the sand in the area, nor will they have a major influence on the long-term sediment dynamics of the area. The 45 acres of sea grass in the Project Area constitute only about two percent of the approximately 2,000 areas of sea grass habitat located immediately to the east of the Project Area. In addition, there are approximately 150,000 acres of sea grass beds lying within that portion of Biscayne Bay in Dade County, Florida. There is an almost solid belt of turtle grass beginning on the offshore or ocean-side of Key Biscayne extending southward of Key West out to the Merquesas Islands and, with a slight break, to the Dry Tortugas. Unlike Syringodium filiforme, turtle grass serves as a true nursery ground for marine organisms in their early life stages. The portion of the sea grass community proposed to be filled in the Project Area is not a good nursery ground, primarily because of the small amount of turtle grass present. The turtle grass beds present in the Project Area do not constitute a mature stable community comparable to those located slightly farther offshore Key Biscayne. These better turtle grass beds have longer blades that do not show wear from wave action and are covered with epiphytes and other marine organisms. Further, unlike the turtle grass in the Project Area, these beds are dense, with little open space between them, and have little or no other plants growing with them. The sea grass beds in the Project Area are simply not qualitatively as rich as these adjacent beds. These offshore sea grass beds serve as true nursery grounds for marine life. Shrimp and certain game and commercial fish, as examples, are located primarily in nursery grounds in Biscayne Bay and Hawk Channel, where there are more mature and stable turtle grass communities. In light of the extent and condition of the sea grasses in the fill area and the associated sea grass communities both inshore and offshore Key Biscayne, taken together with the design of the overall project as hereinafter described, the total effect of the proposed fill on marine life should be inconsequential. The sand to be placed in the Project Area will be dredged from a borrow area located approximately one mile south of Key Biscayne. This site was selected by the United States Army Corps of Engineers. A consultant retained by the County has recommended that certain portions within this borrow area not be used, and that other areas adjacent thereto be utilized if necessary. This modified borrow area falls within the area described in the County's permit application for the source of the fill material. The depth of the sand above the substrate in the borrow area ranges from 1.0 to 9.5 feet, with a substantial portion of the area having in excess of a five-foot depth of sand. Assuming sand will be removed to a depth of five feet, the sand will be taken from approximately a 2,000 by 1,000-foot site. If done in this manner, only about one-third of the borrow area designated by the Corps of Engineers and modified by the County's consultant will be utilized. The entire borrow area designated by the Corps of Engineers contains approximately one million cubic yards of sand. There are no known corals or hard-bottom communities within the proposed borrow area. In addition, there appear to be very few benthic organisms in this area, which is comprised primarily of shifting sand. The benthic organisms that do exist in the area will, of course, be removed during dredging. However, the borrow area can reasonably be expected to repopulate with these organisms as soon as the dredging operation is concluded. Further, the area from which the fill is proposed to be obtained is well removed from any areas of persistent sea grass cover. There are only five or six patches of sea grass in the borrow area, the largest being approximately 12 feet across. These patches do not contain turtle grass and may be easily avoided during dredging. The record in this case clearly establishes that use of the sand from the borrow area should not have an adverse impact on the environment surrounding that area. The sand proposed to be placed on the beach is similar in grain size and composition to the sand that is on the existing beach, owing probably to the fact that it was at one time located on the beach and has been removed through the process of erosion. This sand is of such quality that there should be only minimal turbidity occurring during the dredging operations. There are very small quantities of fine material within the borrow area, and the chemical and physical composition of the sand there closely matches the chemical and physical composition of the sand on the beach. As stipulated by the parties, it is not anticipated that any turbidity problems will result from a physical or chemical breakdown of the material after it is deposited on the beach, and it is also not anticipated that significant long-term turbidity will result from the actual fill being placed on the beach because of the small quantity of fine material contained in the fill. The sand is proposed to be dredged from the borrow area by means of a hydraulic dredge, and transported in a sand/water mixture via pipeline to the Project Area. The sand will be placed on the beach by a method known as longitudinal diking, which permits most of the sand to precipitate before the water returns to the ocean, thereby keeping most of the sand in the Project Area and reducing the impact on receiving waters. The 45 acres of sea grass in the Project Area discussed above will not be covered immediately by fill. This acreage figure represents the total area of sea grass that will be covered after the fill has reached the "theoretical- toe of fill". The theoretical design profile of the beach cannot be achieved immediately because it is not possible to operate the necessary equipment below the waterline. The project design calls for fill to be placed on the beach in a different configuration than will ultimately be obtained, and allows natural wave action to reshape the sand to achieve the design profile. It is anticipated that the entire process will take approximately two years. This is not a unique process, in that the Crandon Park beach immediately north of the Project Area was renourished in a similar fashion in 1969. The Crandon Park design profile was achieved in 1971, and the record establishes that sea grasses offshore Crandon Park were not adversely affected by the sand placed on that beach. Further, no additional fill has been placed on Crandon Park beach since its original renourishment in 1969, and that beach is still very close to the original design profile. The design profile for Crandon Park beach is identical to that proposed for the Project Area. Accordingly, once the design profile for this project is achieved, the greater weight of the evidence in this cause establishes that the sand in the renourished area should not migrate beyond the design toe of fill. A rock structure referred to as the "terminal groin" is proposed to be constructed in connection with the project at the lighthouse at the southern extremity of the beach. The purpose of the terminal grain is to retain the sand placed along the beach. This structure will extend seaward approximately 350 feet, with a top width of seven feet, and top elevations ranging from plus 2.6 feet mean low water at the most seaward location, to plus 7.0 feet mean low water at the beach. The County proposes to modify the slope of the groin to create additional intertidal and subtidal habitat by placing native limestone boulders along the entire 350-foot length of the south side of the groin. By making this modification, approximately 7,000 square feet of subtidal rock habitat will be provided. In addition, this modification will create approximately 36,750 cubic feet of void space for potential marine habitat. The approximate cost of this structure is $200,000. The terminal groin will provide a type of rocky habitat which naturally existed in the Biscayne Bay area, but which has been largely eliminated by man-made improvements. This type of habitat, of course, will not duplicate the type currently provided by the 45 acres of sea grass proposed to be covered by fill. Specifically, rocky habitat does not serve the nursery and breeding functions which sea grasses provide. Further, it neither contributes food stuff by way of primary productivity nor cycles energy into the marine ecosystem in the same manner as sea grasses. The County, in fact, had at one time considered replanting sea grass to mitigate for the loss of the grass communities in the Project Area, but abandoned that alternative in view of the existing large areas of sea grass adjacent to the project, and the fact that the barren bottoms in the Project Area and in adjacent areas have occurred as a result of high wave energy. As a result, it was felt that any attempt to replant the sea grasses by way of mitigating the effect of the proposed project would be unsuccessful. With a properly designed terminal structure, the renourished beach should last approximately 30 years. The rate of erosion on the beach when the project is concluded should approximate 15,000 cubic yards per year. Accordingly, it is unlikely that the beach would require renourishing in less than ten years following the project. As noted above, the Crandon Park beach was restored in excess of 12 years ago, has not been renourished, and still is very close to the original design profile. Sea turtles nest at Bill Baggs State Park and at Crandon Park. The record in this case establishes that these turtle nests can be fairly easily found and relocated. The Corps of Engineers has a turtle protection program with the U.S. Fish and Wildlife Service under which contractors on beach renourishment projects are required to relocate turtle nests, utilizing persons licensed by the Florida Department of Natural Resources. Dade County also has a turtle relocation program which is currently being utilized in Crandon Park. The record in this case does not establish that the proposed beach renourishment project will adversely affect the nesting of sea turtles within either the Project Area or areas adjacent thereto. Extensive erosion has occurred on the beaches on the eastern shore of Key Biscayne. It is currently not possible, for example, to walk from one end of the beach on Key Biscayne to the other without climbing seawalls and jetties, since portions of the beach are completely under water at all times except during extremely low tidal periods. A substantial portion of the project Area is completely submerged even during low tide. The Hearing Officer personally viewed the extent of the erosion in the Project Area. The placement of fill in the northern 1.2 miles of the project will create public access between Bill Baggs State Park and Crandon Park, which is maintained by Dade County. The project will also create a public beach where currently none exists eastward of the proposed erosion control line for the northern 1.2 miles of the project. Beach renourishment will provide support for and stabilize the restored beach on Crandon Park, thereby enabling that beach to last longer, and will also provide erosion control for the entire length of the eastern shoreline of Key Biscayne. The project, as designed, will protect against a ten-year storm of 24-hour duration, thereby helping to diminish serious injury to property and persons by reason of violent storms. Additional protection will also be provided to the Cape Florida lighthouse, a State historical landmark. Although not a hurricane surge protection project, the beach renourishment program will provide some degree of protection from hurricanes. More protection is provided to upland structures by increasing the distance between them and adjacent water bodies. Pursuant to Section 161.053, Florida Statutes, the Department of Natural Resources has determined that severe beach erosion has occurred along the southern 2.4 miles of Key Biscayne, and that the beach either has been or will be destroyed in the immediate future unless a publicly financed program is undertaken. In 1978, and in 1979, the Florida Legislature appropriated funds for the project, and additional funding has also been approved by the Governor and Cabinet. Tourism is Florida's largest industry. In 1980, approximately 35.9 million visitors spent $17 billion in the State of Florida, generating $785 million in tax revenues and supplying employment for 535,000 people directly employed in the tourist industry. There are primarily four reasons that visitors come to the State of Florida: (1) rest and relaxation; (2) beaches; (3) climate; and (4) other attractions, primarily manmade. Over 60 percent of the visitors to Florida have indicated that beaches are their primary reason for visiting the State of Florida. In 1980, 12.6 million tourists visited Dade County. Of these, 10.3 million were domestic tourists, and 2.3 million were international tourists. these tourists spent a total of $9.5 billion in Dade County, making the tourist industry by far Dade County's largest single industry, directly accounting for 25 percent of employment in Dade County. In 1950, over $4.77 million were collected in the taxable areas of Dade County by imposition of a resort tax of two percent on hotels and motels for transients. Tourism on Key Biscayne contributed approximately $300,000 to the Dade County resort tax collection, which is 6.2 percent of the total tax collection for 1980. 57.2 percent of the domestic tourists in Dade County came to Dade County because of the beaches. Tourists visiting other sections of Dade County used the beaches on Key Biscayne because they are very convenient and pleasing. During the course of this proceeding, the deposition of Dr. Anitra Thorhaug was taken by Petitioners, and the parties have requested that the Hearing Officer, pursuant to the provisions of Rule 28-5.208, Florida Administrative Code, and Rule 1.390, Florida Rules of Civil Procedure, determine a fair and reasonable expert witness fee to be paid to Dr. Thorhaug for her deposition. Having considered the submissions of the parties on this issue, including the actual time spent in deposition of two hours and 55 minutes, and the total time of 4.5 hours devoted by Dr. Thorhaug to the taking of her deposition, it is determined that a reasonable fee for her services is $350.
Findings Of Fact Ramchandra Jakhotia and Rashmi Jakhotia, his wife, acquired the King Cole Motel at 401 East Shore Drive, Clearwater, Florida in 1983 and have owned the property since that time. At the time of acquisition and for some time prior thereto the property included a commercial marina with 22 slips. In 1985 the City of Clearwater revised its Development Code effective October 13, 1985 and, incident thereto, effective July 7, 1988, enacted Section 114.05, Live-Aboard Vessels as Ordinance 4597, Clearwater City Code. That enactment provided, in part, that: Prohibited; exceptions: It shall be unlawful for any person to moor any live-aboard vessel at any location within or upon the navigable waters in the City for any period of time in excess of seventy-two (72) hours, except as follows: At a marina facility for which conditional use approval has been obtained, or a marina facility in existence as of October 13, 1985 for which conditional use approval would otherwise be required;... In January 1986 a survey was taken of all marinas within the City of Clearwater to determine the number of live aboard vessels coming within the purview of the revised Development Code. At this survey eight live aboard vessels were occupying berths at the King Cole Motel marina and this was the number determined to be grandfathered for which no conditional use approval would be required. In 1988 King Cole Motel applied for conditional authorization to utilize 14 additional berths for live aboard vessels. This conditional use was approved subject to the applicant installing a pump-out facility and meeting the parking requirements. Although the parking requirements for a commercial marina, i.e., 0.5 parking space per slip, is the same as the parking requirement at marinas for live aboard vessels, the latter generally place a greater demand on parking spaces than does non-live aboard vessels. To change the approved use from commercial marina without live aboards to live aboards is a change in the use and requires conditional use approval. Before conditional use approval can be granted the applicant must comply with all code requirements, such as required parking spaces, at the time of the change in use. At the time Appellant acquired the King Cole Motel the 22 commercial slips were grandfathered as an authorized use without any parking being provided. Accordingly, as a 22-slip commercial marina Appellant did not have to provide parking. When the eight slips used for live aboards were counted in 1986 they too were grandfathered in without the need for parking spaces. However, when Appellant applied in 1988 for authorization to use 14 other slips for live aboard vessels, the code required the applicant to provide seven parking spaces. To his credit Appellant obtained the use of seven parking spaces down the road from the marina but those spaces were not contiguous to Appellants' marina as required by the code. Therefore, Appellants' use of the additional slips for live aboards did not meet the parking requirement in his conditional use approval. In 1992 Appellant applied for a variance of the seven parking spaces required to allow the use of these additional slips by live aboard vessels. This hearing was held before the Development Code Adjustment Board on February 11, 1993 and it is from the denial of this variance that this appeal is taken. The Board denied the variance requested because the Appellant failed to demonstrate that the standards established by Section 45.24 Land Development Code were met. In these proceedings Appellant presented no additional evidence to support the variances requested than was submitted to the Board.
The Issue Whether the specifications set forth in Respondent's Invitation To Bid for Lease No. 590:2029 are in accordance with law.
Findings Of Fact Upon consideration of the oral and documentary evidence adduced at the hearing, the following relevant facts are found: The Department of Health and Rehabilitative Services (Department) determines space need annually pursuant to a letter of agency staffing, primarily generated as a result of legislatively allocated new positions. Based on the letter of agency staffing showing the need for additional office space in the Inverness, Florida service area of the Department's District Three, the Department caused an ITB to be advertised regarding Lease No. 590:2029 seeking some 19,373 square feet of office space, plus of minus 3%. The Petitioners presently lease office space to the Department in the Inverness, Florida, District Three service area. This office space is located within the preferred zone set forth in Attachment B to the ITB. In addition to the presently leased space, the Petitioner intends to offer additional space within the preferred area. The Department's Leasing Manual HRS M 70-1 (Manual) sets out the procedure to be followed when the Department is seeking to lease office space of 2,000 square feet or more in privately owned buildings. Within this manual are the forms to be utilized for this purpose and, among other forms, is an ITB packet that contains a Bid Submittal Form (BSF) and, within the BSF is a page entitled Evaluation Criteria. The Department followed the procedure set forth in the manual in advertising for competitive bids on Lease No. 590:2029 for office space in Inverness, Florida service area of District Three and, in doing so, used the ITB packet that contains the BSF with the Evaluation Criteria page. The BSF, including the Evaluation Criteria page, is a slightly modified version of the Department of General Services' (DGS) Request For Proposal Submittal Form - BPM 4136, incorporated by reference in Rule 13M-1.015(3)(e), Florida Administrative Code, as a suggested format. The Evaluation Criteria page of the Department's BSF contains nine of the eleven evaluation criteria set forth on the evaluation criteria page of the BPM 4136, but does not place any limit on the weight of award factors as does BPM 4136 on two of the same criteria used by the Department. The Evaluation Criteria set out in paragraph C. 2. and 4. of BPM 4136 which corresponds to paragraph 1(a) and 2(c) of the Department's Evaluation page, provide that award factors for these two criteria should not exceed ten, whereas the Department does not place a limit on the award factors for any of the criteria. The two Evaluation Criteria on BPM 4136 that do not appear on the Department's Evaluation Criteria page address the availability of dining facilities and proximity of offered space to other Department activities and public services. Both the BSF and BPM 4136 are used in bidding for space in existing facilities and, therefore, require a scaled floor plan showing present configuration, with measurements that equate to the net rentable square footage using the Standard Method of Space Measurement. The BSF does not attach a "floor plan for suggested configuration of offices and rooms" as does the BPM 4136 but does provide the number, types and sizes of rooms to be placed in the existing facility. Both forms leave the final configuration of the floor plan to the successful bidder and the lessee. The Department's reasoning for not including a "suggested floor plan" is that this may reduce the number of prospective bidders due to the varied configuration of existing facilities in the bid area. The majority of the clients to be served by the Department in Citrus County, Florida reside within the preferred zone shown as Attachment B. However, there may be other areas where a lesser concentration of clients may be served by "outposting". That is, servicing those clients on a regular scheduled basis at other smaller facilities within an area outside of the preferred zone. The Department no longer requires the facility to be under one roof but how co-location is accomplished is important to the efficient utilization of services and supervision of staff. Elderly and handicapped clients experience difficulty in utilizing needed services (when more than one service is needed) because of distance between buildings. Department clients frequently utilize the services of more than one program and such multi-service utilization is projected to increase in the future. Public transportation in Citrus County, Florida is partially funded by the Department to assist its clients and is uniformly available to the clients in the Inverness services area. The Department did not prepare any studies of functional space needs, staff space needs, client needs, client demographics or client transportation needs before or after the ITB was advertised. The Evaluation Criteria did not include a factor for future expansion even though the Department's caseload is projected to increase. In accordance with the procedure set forth in the Manual an Evaluation Committee (Committee) was appointed to determine, among other things, the award factor or weight to be placed on the nine Evaluation Criteria set forth on the Evaluation Criteria page of the BSF. The committee determined the significance of the nine criteria on the Evaluation page to the Department's needs in regard to Lease No. 590-2029 and awarded a weight factor in accordance with the significance of the criteria. Those criteria most significant to the Department's needs received the highest weight. These award factors were added to the Evaluation page of the BSF at the time the ITB was advertised. No additional Evaluation Criteria were used by the Committee. There was insufficient evidence to show that Committee's action in determining the weight to be given the nine criteria was arbitrary or capricious or unlawful even though different weights had been placed on some of the same criteria in the 1988 ITB. Likewise, there was insufficient evidence to show that any of the specifications set forth in the ITB did not promote fair competition or otherwise reflect normal policy or, that the criteria were designed to favor a specific location or prospective bidder within the preferred zone. The procedure and the forms set forth in the Manual and used by the Department, including the procedure followed by the Evaluation Committee in putting together the ITB for Lease No. 590:2029, comports substantially with all substantive provisions of Chapter 13M-1, Florida Administrative Code, and more specifically with Rule 13M-1.015, Florida Administrative Code. The differences, such as they are, are not substantial, nor is there any extrinsic or intrinsic divergence from the substance of the rule such as to mislead any potential bidder who sought to address the ITB.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is, accordingly, RECOMMENDED that a Final Order be entered by the Department dismissing Petitioners' Formal Notice of Written Protest. DONE and ENTERED this 2nd day of October, 1990, in Tallahassee, Florida. WILLIAM R. CAVE Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, FL 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 2nd day of October, 1990. APPENDIX TO THE RECOMMENDED ORDER IN CASE NO. 89-6017BID The following constitutes my specific rulings pursuant to Section 120.59(2), Florida Statutes, on the Proposed Findings Of Fact submitted by the parties in this case. Specific Rulings on Proposed Findings of Fact Submitted by the Petitioner Adopted in Finding of Fact 1. - 3. Covered in the Preliminary Statement 4. 6. Adopted generally in Findings of Fact 4 - 11, otherwise not material or a restatement of testimony and stated as a finding of fact. 7. - 8. Not material or relevant. 9. - 22. Adopted generally in Findings of Fact 4 - 11, 15, 17 and 18, otherwise not material or a restatement of testimony and not state as a finding of fact. 23. - 24. Not material or relevant. 23. - 24.*Covered in the Conclusions of Law, otherwise not material or a restatement of testimony and stated as a finding of fact. 25. - 27. Adopted in Findings of Fact 2 and 16. 28. - 31. Not material. Adopted in Finding of Fact 16, otherwise a restatement of testimony and not stated as a finding of fact. - 37. Not material or a restatement of testimony and stated as a finding of fact. Specific Rulings on Proposed Findings of Fact Submitted by the Respondent 1. Adopted in Finding of Fact 1. 2. - 3. Not material. 4. 6. Adopted in Findings of Fact 14, 15 and 13, respectively. 7. - 9. Not material. 10. - 12. Adopted in Findings of Fact 11, 12 and 13. 13. - 15. Rejected as not being supported by substantial competent evidence in the record. 16. Adopted in Finding of Fact 13. 17. Not material. 18. Adopted in Finding of Fact 11. 19. - 22. Not Material COPIES FURNISHED: Thomas V. Infantino, Esquire Post Office Drawer 30 Winter Park, FL 32609 Arthur R. Shell, Esquire 1000 Northeast 16th Avenue Gainesville, FL 32601 Sam Powers, Agency Clerk Department of Health and Rehabilitative Services 1323 Winewood Blvd. Tallahassee, FL 32399-0700 Linda Harris, General Counsel Department of Health and Rehabilitative Services 1323 Winewood Blvd. Tallahassee, FL 32399-0700 Case No. - 89-6017BID
The Issue Whether Respondent, Florida Housing Finance Corporation’s (“Florida Housing”), decision to award funding, pursuant to Request for Applications 2017-111 (“the RFA”), to HTG Sunset, LLC (“Sunset Lake”); HTG Creekside, LLC (“Oaks at Creekside”); and Harper’s Pointe, LP (“Harper’s Pointe”), is contrary to its governing statutes, rules, or the RFA specifications; and, if so, whether the decision is clearly erroneous, contrary to competition, arbitrary, or capricious.
Findings Of Fact Petitioner Madison Oaks is the Applicant entity for a proposed affordable housing development to be located in Osceola County, Florida. Petitioner Sterling Terrace is the Applicant entity for a proposed affordable housing development to be located in Hernando County, Florida. American Residential and Sterling Terrace are Developer entities as defined by Florida Housing in Florida Administrative Code Rule 67-48.002(28). Sunset Lake, Oaks at Creekside, and Harper’s Pointe are all properly registered business entities in Florida in the business of providing affordable housing. Florida Housing is a public corporation organized pursuant to chapter 420, Part V, Florida Statutes, and, for the purposes of these proceedings, an agency of the State of Florida. Through the RFA, Florida Housing proposes to award an estimated $10,978,942 in Housing Credit Financing for Affordable Housing Developments located in medium and small counties (“affordable housing tax credits”). The RFA outlines a process for selecting developments for funding. Section Five B. outlines the Selection Process, and subsection 2. is the Application Sorting Order. On November 5, 2017, Florida Housing received 167 applications in response to the RFA. Madison Oaks, Sterling Terrace, Sunset Lake, Oaks at Creekside, and Harper’s Pointe timely submitted applications seeking funding to assist in the development of multi-family housing in medium counties. Florida Housing selected a review committee to score all submitted applications. The review committee issued a recommendation of preliminary rankings and allocations, and the Board of Directors of Florida Housing approved these recommendations on May 4, 2018. The Board found that the parties to this proceeding all satisfied the mandatory and eligibility requirements for funding, but awarded funding to Intervenors based upon the ranking criteria in the RFA. If Sterling Terrace can demonstrate that any two of the three Intervenors should not have been recommended for funding, it and Blue Sunbelt, LLC, will displace them as applications selected for funding. If Madison Oaks can demonstrate that all three Intervenors should not have been recommended for funding, Sterling Terrace and Blue Sunbelt, LLC, will displace them as applications selected for funding. Sunset Lake Section Four A.5.e.(3) of the RFA allows applicants to receive up to four points for proximity to certain community services. The RFA provides that applicants in medium counties must receive at least seven points to be eligible for funding, and at least nine points to be eligible for a Proximity Funding Preference. One of those community services is public schools, which are defined as follows: A public elementary, middle, junior and/or high school, where the principal admission criterion is the geographic proximity to the school. This may include a charter school, if the charter school is open to appropriately aged children in the radius area who apply, without additional requirements for admissions such as passing an entrance exam or audition, payment of fees or tuition, or demographic diversity considerations. Additionally, it must have been in existence and available for use by the general public as of the Application Deadline. (emphasis added). Sunset Lake identified the Jewett School of the Arts (“Jewett School”) as a public school, received four points for proximity, and as a result, was eligible for the Proximity Funding Preference. The Jewett School is a magnet school within the Polk County Florida School District. The Jewett School was in existence and available for use by the general public as of the application deadline. Petitioners maintain the Jewett School does not meet the definition of “public school.”4/ If the Jewett School does not meet the definition of a “public school,” Sunset Lake would not be entitled to four points for proximity to community services. As a result, it would have a total of seven points for proximity, and while it would remain eligible, it would lose the Proximity Funding Preference. As a result, Sunset Lake would not have been ranked as highly and would not have been recommended for funding. The Jewett School does not meet the RFA definition of “public school” because geographic proximity to the school is not the principal admission criterion. Although a student must live in Polk County Schools’ Magnet Zone B to apply for admission to the Jewett School, the principal admission criteria is a random lottery process. Geographic location within the Polk County magnet school zones is a threshold issue which qualifies a student to apply for admission. However, the magnet school decision-making process entails a subsequent elaborate demographic diversity analysis, sorting based on the outcome of that analysis, and, ultimately, a random lottery drawing which determines final admission. The Jewett School admission process is contrary to Florida Housing’s primary purpose of awarding proximity points to proposed housing developments--to ensure the intended residents can, in fact, use the services in proximity to the development. Sunset Lake is not entitled to four points for proximity to community services and should not be awarded Proximity Funding Preference. As a result, Sunset Lake should not have been ranked as highly and should not have been recommended for funding. Oaks at Creekside Oaks at Creekside identified the Manatee Charter School (“Manatee School”) as a public school, received three points for proximity, and, as a result, was eligible for funding but not for the Proximity Funding Preference. The Manatee School is a charter school located in Bradenton, Florida. The Manatee School was in existence and available for use by the general public as of the application deadline. Petitioners maintain the Manatee School does not meet the definition of a “public school.”5/ If the Manatee Charter School does not meet that definition, then Oaks at Creekside is not entitled to three points for proximity. As a result, it would have only six total proximity points, and would not be eligible for funding. Florida Housing maintains that a charter school must meet both parts of the definition of a public school in order for a proposed development to receive proximity points based on proximity to that school. That means a charter school must (1) use geographic proximity as the primary admission criteria, and (2) be “open to appropriately aged children in the radius area who apply, without additional requirements for admissions such as passing an entrance exam or audition, payment of fees or tuition, or demographic diversity considerations.” Geographic proximity is not the primary admission criterion for the Manatee School. On the contrary, the Manatee School is open for admission regardless of geographic proximity thereto. The Manatee School operates pursuant to a contract with the Manatee County School Board, and is “open to any student residing in the Manatee County School District, students covered in an interdistrict agreement and students as provided for in Section 1002.33(10), Florida Statutes (2010).”6/ The Manatee School operates a “controlled open enrollment” process. The application period opens in early January and closes at the end of February, and the School accepts students from any school district in the state whose parent or guardian can provide transportation to the school, if the school has not reached capacity. This process is sometimes referred to as “school choice” and is mandatory pursuant to section 1002.31, Florida Statutes.7/ The Manatee School has enrolled students throughout Manatee County, as well as from adjoining Sarasota County. Historically, the Manatee School has not reached capacity. Once the School reaches capacity in any one grade level or class, students will be selected by a system-generated, random lottery process. The term “radius area” is not defined in the RFA or in Florida Housing’s rules. Florida Housing introduced no evidence regarding the meaning of the term “radius area” within the definition of “public school.” When questioned about the meaning, Marisa Button, Florida Housing’s Director of Multifamily Allocations, stated she did not know, but “[I] assume it means if the charter school has a radius area. I don’t know.”8/ The term “radius” is defined as “a bounded or circumscribed area.” Merriam-Webster Online, www.merriam- webster.com (2018). The bounded or circumscribed area for admission to the Manatee School is the Manatee County School District, pursuant to its contract. The Manatee School is open to appropriately-aged children in the radius area who apply. The Manatee School does not apply additional requirements for admission, such as passing an entrance exam or audition, payment of fees or tuition, or demographic diversity considerations.9/ The Manatee School does provide admissions preferences to students of active duty military personnel, siblings of a student already enrolled, siblings of an accepted applicant, children of an employee of the School, and children of a charter board member. Each of these preferences is authorized pursuant to section 1002.33(10)(d). The preferences are not additional requirements for admission to the Manatee School. The Manatee School meets the second part of the definition of “public school” for purpose of qualifying Oaks at Creekside to receive proximity points pursuant to the RFA. Harper’s Pointe Madison Oaks argues Harper’s Pointe is ineligible for funding pursuant to the RFA because the Harper’s Pointe development site is a “scattered site,” and Harper’s Pointe did not identify the site as such and comply with the RFA requirement to designate latitude and longitude coordinates for both sites.10/ Rule 67-48.002(105) defines “scattered sites” as follows: (105) “Scattered sites,” as applied to a single Development, means a Development site that, when taken as a whole, is comprised of real property that is not contiguous (each such non-contiguous site within a Scattered Site Development, is considered to be a “Scattered Site”). For purposes of this definition “contiguous” means touching at a point or along a boundary. Real property is contiguous if the only intervening real property interest is an easement, provided the easement is not a roadway or street. All of the Scattered Sites must be located in the same county. Section Four A.5.c. of the RFA states: “The Applicant must state whether the Development consists of Scattered Sites.” Section Four A.5.d. of the RFA requires that applicants provide latitude and longitude coordinates for the Development Location Point and any scattered sites. Section Five A.1. provides that “only items that meet all of the following Eligibility Items will be eligible for funding and consideration for funding selection.” Among the items listed are “Question whether a Scattered Sites Development answered” and “Latitude and Longitude Coordinates for any Scattered Site provided, if applicable.” Harper’s Pointe did not state in its application that the development consists of scattered sites, and did not provide separate latitude and longitude coordinates for scattered sites. Harper’s Pointe’s proposed development site, as identified in its Site Control Documents, consists of land located within a platted tract of property. The plat recorded in Alachua County indicates that the site is bisected by a platted 50-foot street easement running east/west through the property. The parties stipulated the street has never been constructed. Although portions of the east/west easement area show signs of having been improved at some time in the past, the easement area has never been paved, and is currently impassible by car or truck due to vegetation in the easement area. Even if the easement area were improved, there is no roadway to the west of the property to which it would connect. A fence runs along the property line and the property beyond the fence is platted residential lots accessed by Northeast 22nd Street. An existing roadway, Northeast 23rd Avenue, terminates at the eastern property line just south of the east/west easement. The City has placed barriers at that property line prohibiting access to the property from Northeast 23rd Avenue. If the platted street is a “roadway or street” as those terms are used in rule 67-48.002(105), the site would meet the definition of a “scattered site.” Ms. Button testified on behalf of Florida Housing that the property meets the definition of a scattered site because “there is an easement that is a road or a street” that bisects the property. Ms. Button first testified that Florida Housing’s determination did not depend on whether a roadway or street is actually constructed within the easement, but rather, “it goes back to the easement, whether there is an easement that is a roadway or street.” Ms. Button’s testimony seemed logical enough. If the easement were a street easement, access between the northern and southern portions of the development site would be constrained. By contrast, if the easement were a conservation or utility easement, there would be no impairment of access between portions of the development site. However, on cross examination, Ms. Button testified that, in making the determination whether an easement for a road or street existed, Florida Housing would consider a number of other factors, including whether a roadway was actually constructed within the easement, whether there were physical obstructions preventing access to the “prospective” roadway or street, and whether the public had a right to use the “prospective” roadway or street. Ms. Button did not testify with specificity what factors she considered in making the determination that the easement, in this case, was “a roadway or street.” Ms. Button’s direct-examination testimony was conclusory: “Based on the documentation we received, there is an easement that is a road or street.” On direct examination, her determination appeared to be based solely on the plat designation of a street easement. On cross-examination, however, Ms. Button testified that “a street designated . . . on a plat could be evidence of the existence of a scattered site.” (emphasis added). Moreover, Ms. Button testified that Florida Housing could consider whether a roadway or street was actually constructed, whether there were obstructions to its use, and whether the public had a right to use the purported roadway. Ms. Button’s testimony that the Harper’s Point development site was a scattered site was equivocal, and the undersigned does not accept it as either reliable or persuasive.11/ There is no physical roadway or street constructed within the easement. While there is some evidence that some portions of the easement area were improved in the past, said improvement was at least 25 years old. The current condition of the property is fairly heavily wooded. To the extent a “path” exists on the property, it is not passable by a standard four- wheeled vehicle. Moreover, there are physical barriers preventing vehicular access to the property from the adjoining street to the east. There is no access to the property from the residential development to the west of the property. There is not an improved area preventing access from the northern to the southern portion of the development site. There is no structure built within the easement which would have to be demolished in order to build the project on the development site as a single parcel. Based on the entirety of the reliable evidence, the Harper’s Pointe development site is not a “scattered site” as defined in the RFA. Madison Oaks failed to prove that Florida Housing’s initial determination to award tax credits to Harper’s Pointe, pursuant to the RFA, was incorrect.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that Florida Housing issue a final order finding (1) that its initial scoring decision regarding Sunset Lake was erroneous, and awarding funding to the applicant with the next highest lottery number; and (2) awarding funding to Oaks at Creekside and Harper’s Pointe, pursuant to its initial scoring decision. DONE AND ENTERED this 23rd day of August, 2018, in Tallahassee, Leon County, Florida. S SUZANNE VAN WYK Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 23rd day of August, 2018.
Findings Of Fact Counsel for the respective parties stipulated to the following facts: Quayside Associates, Ltd., is a Florida limited partnership whose address is 10670 N.E. Quay Plaza, North Miami, Florida 33134. Respondent is the Department of Environmental Regulation, an agency of the State of Florida as defined in Section 120.52(1), Florida Statutes. This Petition relates to the Department's File No. DF13-28371-6E. Petitioner was the applicant for the subject permit and will, as applicant, be directly affected by a denial thereof. On February 28, 1980, Petitioner applied to the Department for approval of its Phase II Docking Facility which included an elevated walkway with wave break panels, nineteen (19) new wet slips and twenty-five (25) davits. (Exhibit "1") On March 6, 1980, a completeness review form was sent to the applicant's representative by the Department. (Exhibit "2") On March 6, 1980, the applicant's representative responded to the comments of the Department and completeness summary by letter from J. Frederic Blitstein to the Department's Subdistrict Office. (Exhibit "3") As shown by the Department letter of May 29, 1980, response to the completeness summary were received by the Department from the applicant on March 7 and 11, 1980, with final Department of Natural Resources clearance, as requested by the completeness summary, received by the Department of March 14, 1980 (see Exhibit 4). The response of the Depart- ment of Natural Resources is attached hereto as Exhibit "5". On March 20, 1980, the representative of the Department made an on-site visit to the site as shown by the Departmental Summary Permit Processing Worksheet attached as Exhibit "6". On April 9, 1980, the Department received the comments and recommendations of the Dade County Department of Environmental Resources Management which indicated that it had "no objection to the issuance of the Permit" subject to certain stipulations and conditions. (Exhibit "7") On June 25, 1980, the Department held its scheduled Biscayne Bay Aquatic Preserve Hearing in Miami, Dade County, Florida. On July 2, 1980, the Department issued a completion notice to the applicant indicating completion of the application on June 25, 1980. (Exhibit "8") On September 9, 1980, the Department issued its Letter of Intent to Deny which gives rise to the subject proceeding. (Exhibit "9") This Petition ensued and was filed with the Department on September 24, 1980. The State of Florida, Division of Administrative Hearings has jurisdiction over this matter and has jurisdiction to make an Interlocutory Ruling regarding same. This Stipulation may be utilized for interlocutory purposes or for all subsequent purposes.
Findings Of Fact Harbor Course South is a one hundred and seventy two lot real estate development which is a portion of the Ocean Reef Club located at the extreme northern end of Key Largo, Monroe County, Florida. The Harbor Course South property was acquired in approximately 1964 along with over 1200 acres of adjoining property for approximately 1.5 million dollars. Driscoll Properties, Inc. ("Driscoll"), a Florida Corporation, is the developer of Harbor Course South. Driscoll Foundation, Inc., (the "Foundation") is a non-profit Florida corporation which owns a portion of the Harbor Course South property. (Driscoll and the Foundation are collectively referred to as the "Intervenors" or the "Permittees.") The Ocean Reef Club is a one thousand two hundred unit development encompassing approximately eight hundred acres including at least two eighteen hole golf courses, a marina and an air strip. Nine holes of golf are located in Harbor Course South. These nine holes were leased to the Ocean Reef Club in 1974-1975 pursuant to an agreement providing for creation of golf course lots and lake-front lots in Harbor Course South. The nine holes of the golf course located in Harbor Course South were in place by at least 1978 and have been in use since that time. In order to install those nine holes, some roads were cut through the property and the lakes were dredged. Thirty-eight of the one hundred and seventy-two lots in Harbor Course South were originally platted in 1978 or 1979. These thirty eight lots are referred to as Section 1 of Harbor Course South. All of lots in Section 1 have been sold to individual purchasers for an average price of $34,210.00 per lot. The thirty-eight lots in Section 1 were all sold prior to 1988. In approximately 1979, some roads were cleared and paved on the Harbor Course South property in order to provide access to the thirty-eight originally platted lots in Section 1. A number of the lots in Section 1 have been permitted for construction by Monroe County and houses have been constructed on several of them. No individual lot owner in Section 1 has been denied a permit for clearing at least some of his land for a homesite. Both the United States Fish and Wildlife Services ("U.S.F.W.S.") and the Florida Game and Fresh Water Fish Commission (the "Commission") have determined that the clearing and/or development of the lots in Section 1 will not require permits for the taking of endangered or threatened species or their nests. In 1985, the Intervenors, in conjunction with the Ocean Reef Club, sought a determination as to the extent of their vested development rights with respect to the Harbor Course South property by initiating a vested rights hearing before Monroe County. These proceedings were initiated under Chapters 380 and 120, Florida Statutes and resulted in a Joint Stipulation on February 23, 1988 recognizing that the Intervenors have vested rights to develop the Harbor Course South plats. (The Joint Stipulation is referred to as the "Vested Rights Determination.") The Vested Rights Determination recognized that the Intervenors and the Ocean Reef Club had incurred obligations and expenditures based upon the approval of the master plan for development of Ocean Reef in 1977 in accordance with the then-existing regulations of Monroe County. The expenses and improvements upon the property included the construction of roadways, water main extensions, medical facilities, and golf courses. As a result of these expenditures, the Vested Rights Determination established that the Intervenors were authorized to continue development under the master development plan for the Ocean Reef Club, notwithstanding the enactment of a comprehensive land use plan and development regulations by Monroe County on September 15, 1986. No appeal of the Vested Rights Determination was filed by the Florida Department of Community Affairs or any other party. The remaining one hundred thirty-four lots in Harbor Course South were subdivided into three plats in 1986. These plats have been designated Ocean Reef Plat Numbers 17, 18 and 19 (also referred to as Sections 2, 3 and 4 respectively of Harbor Course South.) The Intervenors were not required to obtain a permit from the U.S.F.W.S. or the Commission prior to subdividing and/or selling lots of the Harbor Course South property. Most of the infrastructure for development of Plats 17, 18 and 19 is in place. Paved roads were completed in 1987-1988. The electrical lines and sewer lines are in place and operational in all three plats. The water lines are in place and connected in Plat 17. The waterlines are also in place, but not connected, in Plats 18 and 19. The total area of Sections 2, 3 and 4 of Harbor Course South is 134.09 acres. The remaining one hundred thirty-four lots occupy approximately 53.66 acres of this total. The lots in the area are priced at an average of $127,000 each. The Intervenors have begun selling the lots in Plat 17 (Section 2 of Harbor Course South). This plat consists of twenty-five lots. No competent substantial evidence was offered to establish the exact number of lots sold or houses constructed in this area, but it appears that ten to twelve lots were sold between July 1, 1989 and December 13, 1989. At least one house has been constructed on this plat and three building permits are pending before Monroe County. Prior to selling the lots in Plat 17, the Intervenors reached an informal agreement with the U.S.F.W.S. and the Commission as discussed in more detail in Findings of Fact 33 below. In accordance with that agreement and because there was no indication of the presence of endangered or threatened species on these lots, it was determined that none of the lots sold in Plat 17 would require the issuance of a permit from the Commission before land clearing could take place. The sales of the lots in Plat 17 were not completed until after the issuance of a Proposed Permit by the Commission for the "incidental taking" of endangered and threatened species with respect to the entire Harbor Course Property. (This Proposed Permit is discussed in more detail in Findings of Fact 44.) After the Proposed Permit was issued and this challenge was filed, the titles to the lots sold in Plat 17 were transferred to the purchasers. As indicated above, some of these lot owners have proceeded with the development of their property without the need of a permit from the U.S.F.W.S. or the Commission. None of the lots in Plats 18 and 19 (Sections 3 and 4) have yet been offered for sale. The natural vegetation of North Key Largo, including the Harbor Course South property, consists largely of tropical hardwood hammock. The quality of the vegetation varies widely throughout the area. Development of the Ocean Reef Club has largely supplanted the hardwood hammock in that area. The golf course which is located on the Harbor Course South property was placed in the midst of the hammock. The golf course and the infrastructure for development of Harbor Course South have fragmented the hammock in Plats 17, 18 and 19. The hardwood hammock of North Key Largo is a unigue flora to North America, being extremely tropical in character. It is characterized by vegetation more commonly found on the tropical islands of the Carribean and is different from the tropical hammocks of mainland South Florida because of a difference in hydrology, i.e., the Florida Keys are substantially drier and have a lower water table. The hammock of North Key Largo has a very high species diversity with one hundred and five species of trees and shrubs and fifteen species of woody vines in the hammock vegetation. The ecology of a hardwood hammock is cyclical. Over the years, the hammock has demonstrated its ability to regenerate naturally. Thus, while much of North Key Largo was used as agriculture land in the late nineteenth and early part of the twentieth century, the hammock has recovered in those areas where it has been allowed to naturally regenerate. The species of plants in the hardwood hammock are well-adopted for colonizing. The trees are "good at getting their seeds into places where they will grow." Many of the species of hammock trees and shrubs have fruits that are attractive to birds and some animals such as raccoons. These animals, birds, and raccoons eat the fruit, do not digest the seeds, but pass them in their fecal material which helps spread the vegetation. Tree growth in a young hammock is initially rapidly vertical before spreading out to provide larger coverage. A mature hammock provides a "closed canopy" of branches which affords protection and transportation for many animals including woodrats and cotton mice. As the hammock matures, there is an accumulation of humis and leaf litter on the ground beneath the trees. This humis layer serves as a seed bed for new growth and accumulates over the years. The humis layer is an important factor in assessing the quality of a hammock as habitat for endangered species. It takes decades for a hammock to fully mature to the point that it provides habitat and food sources for woodrats and similar creatures. Because of the biological richness of the hardwood hammock, as well as to protect the off-shore coral reefs from the detrimental effects of run-off from development, the State of Florida, through the Conservation and Recreational Land Acquisition program, ("CARL") has designated much of area of North Key Largo at the top of the acquisition priority list. The area slated for acquisition under the CARL program extends approximately twelve miles from the point where U.S. Highway 1 enters Key Largo northeastward to the southern boundary of Harbor Course South. The State of Florida has already acquired large tracks of North Key Largo under the CARL program. These tracks include a large portion of the land on the east side of State Road 905 from Port Bougainville to the southern border of the Ocean Reef Club (Harbor Course South.) Moreover, the Foundation is currently negotiating with the State regarding the acquisition of approxiately twelve hundred acres immediately adjacent to Harbor Course South. The federal government has established the Crocodile Lake National Wildlife Refuge which embraces most of the land lying west of State Road 905 from Card Sound Road (near and west of the Ocean Reef Club) south to Lake Surprise, a distance of approximately twelve miles. In sum, a large portion of the property in North Key Largo outside the Ocean Reef Club and Harbor Course South does not have vested development rights. A vast majority of this property is, or will likely become in the near future, publicly owned for conservation purposes. Thus, large quantities of high quality tropical hardwood hammock habitat have been, or are in the process of being, acquired in the immediate vicinity of the Harbor Course South property. The hardwood hammocks of North Key Largo are inhabited by certain endangered and threatened species. The Commission has the authority to determine endangered species within the area of its jurisdiction under the Endangered Species Act of 1973, 35 U.S.C.A. 1531, et seq. The Key Largo woodrat (neotoma floridana smalli) and the Key Largo cotton mouse (peromystus gossypinus allapaticola) are animals which can be found in the secondary growth and mature tropical hardwood forests of North Key Largo. Both the woodrat and cotton mouse as well as the Schaus' swallowtail butterfly (heraclides aristodemus ponceana,) have been listed as endangered species in Rule 39-27.003, Florida Administrative Code. The hardwood hammock of North Key Largo also serves as a habitat for the Eastern Indigo snake (drymarchon corais couperi), which has been listed as a threatened species by the Commission pursuant to Rule 39-27.004, Florida Administrative Code. Rock piles, tree roots, mounds, piles of sticks, holes in the rock substrate, holes in the humis layer beneath the trees and similar hiding areas all serve as nests or "refugia" for the woodrat. A mature hammock provides an ideal habitat for the woodrat. Destruction of the habitat of the woodrat has been a key factor in the woodrat becoming an endangered species. The Key Largo cotton mouse occupies much of the same habitat as the woodrat. Although the density of the population has not been established, there is no dispute that some portions of the Harbor Course South property are populated with woodrats and cotton mice. The quality of the habitat varies significantly throughout the property. There is only limited evidence of the presence of the Schaus' swallowtail butterfly on the Harbor Course South property. There have been a few citings of the species in the vicinity of Harbor Course South, but it does not appear that this property is an important habitat for the Schaus' swallowtail butterfly. There is no specific evidence of the presence of the Eastern Indigo snake on the subject property. Before a lot owner in Harbor Course South can clear his homesite, the Monroe County Code requires the owner to secure a habitat analysis which must be prepared by an accredited biologist approved by the County. That analysis determines the quality of the hammock on the lot, which in turn determines the amount of vegetation which the County will allow the lot owner to clear. This requirement was in place for the first thirty eight lots that were originally platted in Section 1. Under the existing Monroe County Land Clearing Regulations, only twenty percent of a lot with high quality tropical hardwood hammock can be cleared; forty percent of a lot with medium quality hammock can be cleared and forty to eighty percent of a lot with low quality hammock can be cleared. As of the date of the hearing in this case, all lot owners in Harbor Course South who have applied for a building permit were allowed to clear at least a portion of the lot for construction of a homesite. It does not appear that any lot owner was permitted to clear more than forty percent of his lot. As indicated above, no permits from the Commission or the U.S.F.W.S. were necessary in order to clear the lots and commence building on the thirty- eight lots in Section 1. Likewise, the Commission determined that the habitat quality in the area of Plat 17 was sufficiently low that a permit would not be required for development on that Plat. However, the Intervenors were aware of the presence of endangered and threatened species in this area. Around the time that the Vested Rights Determination was obtained, the Intervenors entered into discussions with the U.S.F.W.S. and the Commission in an attempt to obtain an overall permit for Plat 17, 18 and 19 with respect to endangered and threatened species. During these negotiations, the Intervenors received permission from the U.S.F.W.S. and the Commission to proceed with development in Plat 17 even before a permit was issued. The Commission determined that the Intervenors could proceed with the development of Plat 17 without obtaining a permit because of the relatively low habitat value of most of the parcel and the apparent absence of any endangered species in this area. As part of the negotiations regarding this authorization, the Intervenors agreed to seek a permit with respect to the remaining one hundred and nine lots in the subdivision. The negotiations were prompted, at least in part, by an agreement between the U.S.F.W.S. and the Florida Keys Aqueduct Authority (which provides water to the area) that established certain requirements before water connections could be made to new residential property in North Key Largo. This agreement requires that, before water connections can be made to an area inhabited by endangered or threatened species of wildlife, a permit must be obtained by the U.S.F.W.S. During the negotiations, the U.S.F.W.S. indicated to the Intervenors its desire to address the conflict between the endangered species on North Key Largo and development interests in "one big conflict rather than having to handle it land owner by land owner." The Commission agreed with this approach feeling it could better protect the subject species through required mitigation by the developer which would probably not be possible or practical when dealing with individual lot owners. Although the Intervenors questioned the legality of the requirements imposed as a result of the agreement between the U.S.F.W.S. and the Florida Keys Aqueduct Authority, the Intervenors decided to try and work with both the federal and state agencies and attempt to meet their concerns rather than engage them in a legal battle over their authority to impose mitigation requirements on new developments. A permit from the U.S.F.W.S. or the Commission is not necessary for the Intervenors to sell the lots in Plats 17, 18 and 19. The Intervenors sought permits from the Commission and the U.S.F.W.S. in a good faith attempt to cooperate with the agencies responsible for enforcing the Endangered Species Act and to eliminate obstacles to the clearing and development of the lots by individual lot purchasers. The U.S.F.W.S. has developed specific rules and procedures for protecting the habitat of endangered species and issuing "incidental take" permits for activities that may impact on the species or their habitat. The Commission has not adopted any rules that specifically protect the habitat of endangered species other than a prohibition against molesting or harming their nests. Similarly, the Commission has no specific rules regarding "incidental take" permits. The Intervenors filed an application with the U.S.F.W.S. on March 13, 1989 seeking a permit for covering all of Plats 17, 18 and 19. Attached as exhibits to the application were copies of the pleadings from the proceedings whereby Intervenors received their Vested Rights Determination, a summary of a proposed revegetation project to be undertaken in connection with the permit; the Harbor Course Subdivision construction plans together with construction details; a report prepared by Dr. Earl Rich regarding North Key Largo endangered rodent preservation measures; a report by Dr. Jack Stout setting forth the results of woodrat and cotton mice trapping in the subject area; and an aerial photograph of the subject area. The application sought a "permit for the incidental taking of endangered species in connection with completion of development of a residential subdivision and related site improvements surrounding an existing golf course. The area to be cleared may include habitat for the Key Largo woodrat, cotton mice, or Schaus' swallowtail butterfly." A permit has not been issued by the U.S.F.W.S. with respect to Plat 17, 18 and 19. The Intervenors' application for a permit has been transmitted to the Commission. It is not clear how the application filed with U.S.F.W.S. came before the Commission for consideration. The Commission has no direct agreement with the Florida Keys Aqueduct Authority regarding water connections. The Commission's authority for asserting jurisdiction over the development is not based on any existing rules or statutes regarding "incidental take" permits. The U.S.F.W.S. has apparently agreed to defer to the Commission with respect to the issuance of a permit for the Harbor Course South development. The U.S.F.W.S. has been kept abreast of the negotiations and terms of the Proposed Permit and has suggested various changes during the negotiation process in an effort to coordinate the conditions of the two permits. By letter dated July 24, 1989, the Commission set forth conditions for the issuance of a permit to the Intervenors which would authorize them to take the nests and habitat of woodrats and cotton mice, to harm or molest Schaus' swallowtail butterflies, and to take Eastern Indigo snakes, "incidental to land clearing operations and building construction of single family and cluster homes" on Plat 17, 18 and 19. The permit does not authorize the killing of woodrats, cotton mice or Schaus' swallowtail butterflies. The Commission stated that the permit was being issued pursuant to Rules 39-27.002(1) and 39- 27.002(2), Florida Administrative Code. (The July 24, 1989 letter setting forth the conditions for the permit will be referred to as the "Proposed Permit.") The Proposed Permit states that the permit will inure to the benefit of the Intervenors and their "successors in title or their agents." In other words, purchasers of lots from the Intervenors would be covered by the Permit and no additional permit would be necessary to take the nests and habitat of woodrats and cotton mice, to harm or molest Schaus' swallowtail butterflies, or to take the Eastern Indigo snakes incidental to the development of their lots. The terms and conditions of the Proposed Permit were prepared after several meetings and discussions between Commission personnel, the Intervenors' expert biologist Dr. Stout and the developers themselves. The Proposed Permit requires both on-site mitigation and off-site mitigation. The on-site mitigation requires the permanent dedication in the form of a conservation eastment of 5.94 acres in Tract E of Harbor Course South, Section 3 ( Ocean Reef Plat 18) to provide perpetual protection for the habitat for the species listed in the Proposed Permit. The exact provisions of this conservation easement are not speficified in the Proposed Permit and were not established in this proceeding. The Permit also requires specific habitat enhancement of Tract E by planting torchwood seedlings as a means to attract Schaus' swallowtail butterflies in the area of an old service road on Tract E, revegetation in accordance with specific planting instructions of another road that bisects Tract E and the placement of ten piles of rocks and logs of at least four cubic yards each in the old roadway. A ten thousand dollar surety bond or letter of credit is required to ensure compliance with the planting and debris placement provisions within three years of the date of the issuance of the permit. The Intervenors had intended to subdivide Tract E into ten additional lots to be sold as homesites. While Petitioner contends that the development of lots in Tract E may have been prohibited because of the high quality hammock on some of these lots, the evidence established that most, if not all, of the lots in Tract E will be sold and developed as individual homesites if the area is not set aside as a conservation area pursuant to the terms of the Proposed Permit. The establishment of a conservation area in Tract E will help preserve a continuous habitat area for the endangered species. Tract E is adjacent to a large track of property that has been or is in the process of being acquired by the state for conservation purposes. By requiring the Intervenors to provide rubble and debris piles and revegetation on Tract E, the Proposed Permit will further enhance the quality of the habitat in this area. The Proposed Permit requires the existing dirt road which currently cuts through Tract E to be closed and revegetated. There is no requirement that the fill installed for the road bed be removed. While Petitioners contend that such a condition is necessary for the development of this tract into high quality habitat for the endangered species, the natural regeneration of the hammock will be enhanced by the revegetation plan and this area will ultimately develop into high quality habitat. Planting torchwood in the area of Tract E, which is close to the golf course and areas that will be developed, may actually harm the survival potential of the Schaus' swallowtail butterfly. The butterflies are extremely susceptible to chemical insecticides. Planting torchwood in areas where insecticides will be used may create an attractive nuisance to the butterflies. Therefore, the requirement for planting should be moved to an off-site area that is remote from the development to guard against this problem. The area of the old service road should be revegetated pursuant to a schedule similar to the one used for the other revegetation area. Off-site mitigation is to be provided through the enhancement of hammock succession on five, one acre segments of the right-of-way of Old State Road 905 or an alternative similar site approved by the Commission with an area of enhancement to equal five acres. The amount of off-site mitigation was baseed upon a calculation of the amount of road surface in Harbor Course South. The Proposed Permit requires the old road bed and asphalt to be removed and the road restored to original grade. The enhancement of the site is to be accomplished by planting tropical hardwood vegetation from a specified vegetation list, adherence to specific planting instructions governing phase of planting, survival rate and watering conditions, placement of twenty rock and debris piles, (each four cubic yards in volume), removal of exotic plant species semi-annually for a five year period and removal of weedy species of trees and shrubs in an area within a radius of three feet around each planted tree over a similar time period. Four lots in Plat 18 are to be set aside as an assurance against failure to complete the planting or failure to provide an alternative site. A surety bond or letter of credit in the amount of $50,000.00 is also required to ensure compliance with the planting requirements. Old State Road 905 is currently owned by the Florida Department of Transportation. There are plans to convey this right-of-way to Monroe County which in turn plans to abandon the road, remove the road bed and asphalt, and cooperate with the restoration. Thus, it appears that Monroe County may assume responsibility for removing the asphalt road along Old State Road 905. The Proposed Permit requires the Intervenor to ensure that this removal is accomplished. Old State Road 905 is utilized by some utility companies to service their utility lines. At this point, it is not clear whether the utility easements will preclude the revegetation required by the Proposed Permit from becoming effective. The Proposed Permit provides adequate procedures for selecting alternative sites in the event that Old State Road 905 can not be effectively used for a mitigation area. With respect to both the on-site and off-site mitigation, the revegatation requirements in the Proposed Permit are reasonably related to the Commission's goal of enhancing the long term survival of woodrats and cotton mice on North Key Largo. While the diversity of the flora in a natural hammock is greater than that called for in the proposed mitigation, the revegetation will accelerate the development of the mitigation areas into high quality habitat for the endangered species. While a hardwood hammock has a natural capability to regenerate on its own, the regeneration can be enhanced by planting trees in a scarified area. The revegetation required pursuant to the Proposed Permit will be placed mainly in corridors replacing old road ways. This placement will hasten the redevelopment of these areas into high quality habitat. The Intervenors are required to ensure a two year, seventy five percent survival rate for trees planted. Any trees that die are to be replaced by the species with the highest survival rate. The evidence established that the most effective way to enhance the revegetation process is to plant those species of trees that are slow to seed or that are relatively rare. It is not clear whether the planting schedule and sucession procedures attached to the Proposed Permit have taken this fact into consideration. While the diversity of species detailed in the attachments to the Proposed Permit could be reallocated between species to further enhance the revegetation process, the proposed schedules are adequate except for the requirement of planting torchwood on Tract E. Torchwood is an important habitat and food source for Schaus' swallowtail butterflies and should not be placed in an area where chemical insect control efforts are likely. As indicated above, the Proposed Permit requires a survival rate of 75% for the planted trees within two years of the initial planting. The Intervenors are also required to inspect the revegetation sites semi-annually for five years and to remove invasive exotic plants. In addition, Intervenors are required to remove weeding trees, shrubs and vines within a radius of 3 feet around each planted tree for a period of five years. Semiannual reports must be filed with the Commission for the first five years after planting to advise as to the presence of such species. There are no enforcement mechanisms in the Proposed Permit to ensure that the monotoring and removal of exotic species requirements will be completed. The bond requirements of the Proposed Permit only apply to the plantings and installation of debris piles. The requirement for removal of exotic species will help ensure that those exotic species cannot invade the mitigation sites and prevent or retard the natural hammock regeneration process. This requirement will enhance the development of a high quality hammock which will hopefully provide habitat for the endangered species. It is important that an enforcement mechanism be provided in the permit with respect to this requirement. The State Department of Natural Resources has a program for the removal of exotic plants from state lands. DNR is currently preparing a major management plan for North Key Largo and DNR employees are currently involved in removing exotic species from the right-of-way of Old State Road 905. The requirements of the Proposed Permit will augment the on-going efforts of DNR and free-up resources to focus on the removal of exotic species in neighboring areas. The Proposed Permit does not impose qualifications on the individuals who will be responsible for removing the exotic species. The permit should require the Intervenors to retain qualified people to identify the exotic species. The spacing, watering and survival rate aspects of the revegetation plan were based, in part, upon the experiences with revegetation at a previous mitigation site (the Budd Post site discussed below) and represent a reasonable effort for enhancing the revegetation of the hammock. While there is no requirement that the planted trees survive longer than two years after the initial planting, the 75% survival requirement during the first two years provides reasonable assurance that the revegetation will be done properly and with a high probability of success. General Condition 1 of the Proposed Permit indicates that the Commission will review the Permit periodically and "may initiate enforcement or revocation action for any violation of the Permit Conditions by the Permittee, its agents, its employees, or representatives." There is no provision for enforcement or revocation of the permit for violations of the permit conditions by purchasers of lots or other third parties who obtain title to the property from the Intervenors. This enforcement mechanism will become essentially obsolete if and when the Intervenors transfer their interests in the property. General Condition 2 of the Proposed Permit indicates that the Permit is valid "only for the specific processes and operations applied for and indicated in the approved drawings or exhibits." This provision is meaningless since there are no "specific processing operations applied for" and there have been no approved drawings or exhibits other than the planting schedules which are part of the revegetation aspect of the mitigation requirements. There are certain provisions of the Proposed Permit which are vague and/or ambiguous. Special Conditions 4(b) indicates that the requirements of Specific Condition 3(j) are applicable to the restoration of Tract E. Special Condition 3(j) requires the placement of twenty debris piles. However, Specific Condition 4(c) only requires a placement of ten such piles in Tract E. This ambiguity should be clarified. Special Condition 4(d) indicates that there are utility lines in the revegetation area which will have to be maintained. Under this provision, the applicant is allowed to maintain, using hand tools only, a clear path of up to eight feet wide over each utility line. It is not clear from the evidence presented how many utility lines are involved and whether a separate eight foot area can be cleared for each utility line. If several separate utility lines are involved, this provision could effectively prevent the regeneration of the area into high quality hammock habitat. Free ranging domestic pets, especially cats, are a significant threat to the endangered species. One of the conditions imposed by the Proposed Permit would prohibit free ranging pets within the subdivision pursuant to a subdivision covenant to run with the land. The specific wording of such a covenant has not been provided. The Proposed Permit does not provide for any enforcement mechanism with respect to this covenant. Some enforcement mechanism must be provided in order for this condition to provide any effective protection for the endangered species. The Proposed Permit requires the Intervenors to hold four lots from sale until the off-site mitigation requirements have been met. If the planting is not accomplished within a five year period, the Intervenors are required to include these four lots as part of the conservation easement in Tract E. The lots being withheld for sale have an average market value in excess of $120,000 per lot. Thus, this requirement places a major incentive on the Intervenors to comply with the terms of the Proposed Permit. However, it is not clear whether this enforcement mechanism can be applied to the provisions of the Proposed Permit regarding the removal of exotic species. The Proposed Permit does not allow the Intervenors to kill any member of the endangered species. The Proposed Permit does allow the "incidental taking" of the threatened species (Eastern Indigo snake). The term "incidental taking" is interpreted by the Comimssion to include the killing of a member of the threatened species which is incidental to the conduct of otherwise lawful activities. The Commission contends that it has the jurisdiction to issue such an "incidental take" permit for an endangered species under appropriate conditions and mitigation requirements. The Commission did not believe an incidental take permit was necessary with respect to the endangered species on this site because the Commission felt that the habitat quality was relatively low and the likelihood of encountering a member of the species at the site was also low. The evidence established that there is a possibility that some members of the endangered species, i.e., woodrats and cotton mice, will be killed during the development and building of the subdivision. While this possibility is speculative, the chances of such a killing can be minimized by incorporating further protections in the permit. The evidence did not indicate any likelihood that East Indigo snakes or Schaus' swallowtail butterflies will be killed incidental to land clearing and/or development of Harbor Course South. The U.S.F.W.S. requires a habitat conservation plan ("H.C.P.") before it will issue an incidental take permit. A habitat conservation plan committee was established by the Governor in 1985 to prepare an H.C.P. for the North Key Largo area. The goal of the Committee is to designate areas which would be suitable for development and areas which may be necessary for conservation. A Draft Habitat Conservation Plan has been prepared, but it has not yet been officially approved. Harbor Course South is outside the study area of the Draft Habitat Conservation Plan and therefore is not proposed as a conservation area. The framework and structure of the Proposed Permit reflects the Commission's desire to apply a comprehensive permitting approach to the Harbor Course South development rather than rely upon a lot-by-lot determination of jurisdiction with each individual lot purchaser at the time clearing or development activities are sought. The evidence established that there is insufficient indicia of woodrat or cotton mouse presence on a number of the lots in Harbor Course South. Thus, if a lot-by-lot approach was used, the Commission would not have the authority under its current rules to require a number of the individual lot owners to obtain a permit before land clearing. Without question, further fragmentation of the hammock will reduce the quality of the habitat for the endangered species. If a lot-by-lot permitting process is utilized, the owners of the lots that do not show any signs of the presence of woodrats or cotton mice would be able to clear to the maximum extent allowable under the Monroe County development ordinances. Such an approach would not halt the further fragmentation of hammock. By utilizing a comprehensive permit, the Commission can establish uniform standards for development and require stronger mitigative measures to offset the impact of development in the area on the endangered and threatened species. The approach is further justified in view of the Commission's determination that the Harbor Course South property is of only minimal importance as a habitat for the endangered and threatened species. See, Findings of Fact 80-81 below. In sum, land development and land clearing activities are likely to take place on the Harbor Course South property regardless of whether the Proposed Permit is issued. If the Commission utilizes a lot-by-lot determination of jurisdiction, a large portion of the lots on Harbor Course South would not be required to obtain a permit from the Commission because many of those lots do not have nests or any indication of the presence of the endangered species. Under these circumstances, the Commission would probably not be able to obtain comprehensive mitigation conditions and the habitat for the endangered species would be further fragmented with little or no mitigation. As noted above, the Commission has not adopted any rules setting forth its policies and procedures for issuing an overall blanket permit for the "incidental taking" of endangered species. Similarly, there are no formal guidelines adopted to establish when the Commission has jurisdiction over land- clearing activities. In determining whether to assert jurisdiction over a particular piece of property, the Commission looks for evidence of existing nests or habitat of an endangered species or the probability that a taking, killing or some other molestation will occur to a particular member of the species. In connection with the Proposed Permit, the Commission determined that it had the authority under Rule 39-27.002, Florida Administrative Code, to issue permits for clearing and development activities that molest the nests of endangered species. As discussed below, the Commission has issued only one prior permit for land clearing and development activities. That prior permit is was not timely challenged. No rules or standards have been promulgated by the Commission to set forth the mitigative requirements that can be imposed, if any, upon individual lot purchasers. An important factor in the Commission's decision to issue the Proposed Permit in this case was the Commission's determination that the overall quality of the Harbor Course South property as habitat for the endangered species was minimal. In determining that the Harbor Course South property was of minimal importance to the survival of the endangered species, the Commission took into consideration various reports on the sparse density of the population of the endangered species on the subject property. The Commission also took into account what it deemed to be inevitable future development as reflected in the Vested Rights Determination, the fact that the site was not designated for preservation in the Draft Habitat Conservation Plan, and the fact that the site was not part of the North Key Largo CARL acquisition project. Finally, the Commission considered that the site was already a highly fragmented tropical hardwood hammock as demonstrated by Landsat Thematic Mapper Classfied Satellite Imagery. The only previous instance in which the Commission has issued a permit to molest or harm the nests or habitat of endangered species pursuant to land clearing or development activities involved another residential sub-division in North Key Largo. In June of 1986, separate permits were issued by the U.S.F.W.S. and the Commission to the Nichols/Post Hendrix Corporation to destroy nests and habitat of the Key Largo woodrat and Key Largo cotton mouse. (The permit issued by the Commission in connection with this prior project will be referred to as the "Budd Post Permit.") The property covered by the Budd Post Permit is south of Harbor Course South. It lies approximately six miles south of the intersection of Old State Road 905 and Card Sound Road. That property consists of approximately ten acres of high quality hardwood hammock located within the project area of the North Key Largo Hammocks, CARL land acquisition program. Thus, the property was essentially surrounded by high quality tropical hardwood hammock. The Budd Post property is similar to the Harbor Course South property in that both areas run from County Road 905 east to the ocean and both tracts contain habitat suitable for use by endangered species. However, Harbor Course South is a lesser quality habitat than the Budd Post property because it is more highly fragmented and is bordered on the north by the highly developed Ocean Reef property. Overall, there was a significantly greater indication of the presence of the subject endangered species on the Budd Post Property than there is at Harbor Course South. The Budd Post Permit was the first of its kind issued by the Commission and was processed simultaneously and concurrently with the comparable federal permit from the U.S.F.W.S. As a condition to issuance of the Budd Post Permit, the Commission required the permittee to set aside a preservation area, build debris piles to encourage nesting of woodrats and cotton mice and plant vegetation off-site to mitigate the loss of hammock habitat. A condition of the Budd Post Permit required the permittee to trap and remove the endangered species during land clearing activities. A similar condition in the Proposed Permit would help reduce the likelihood of any killing of the endangered species. The results of the mitigation plan for the Budd Post Permit indicate that such a plan can serve to enhance the survivability of the endangered species by providing high quality habitat and accelerating the revegetation of scarified areas. A little more than two years after the mitigation plan for the Budd Post Permit was implemented, it appears that the efforts are achieving their intended results. Specifically, the plants that were planted as a result of the revegetation plan are flourishing and at least some of the debris piles have been colonized by woodrats. Thus, it appears a viable habitat has been created. There is no definitive method for determining the density of population of woodrats or cotton mice at a given site. In making its jurisdictional determination with respect to the Budd Post property, the Commission looked for the presence of stick nests, (which are widely presumed to be constructed by woodrats) as the primary jurisdictional indicator. Subsequent to the issuance of the Budd Post Permit, the Commission has recognized that stick nests are not the sole indicators of the presence of wood rats and the Commission now considers other factors as well. The U.S.F.W.S. requires a trapping study of woodrats and cotton mice as part of its permit application. The permittee for the Budd Post Permit provided the U.S.F.W.S. and the Commission with a "trapping report" prepared by Dr. Stout. The Intervenors also hired Dr. Jack Stout, who is a biologist and professor at the University of Central Florida, and a similar report was prepared for Harbor Course South. The same methodology was used to trap woodrats and cotton mice on both sites. Dr. Stout concluded that the Harbor Course South property had a low density population of woodrats and cotton mice. Dr. Earl Rich, a biologist and ecologist and a former professor at the University of Miami with extensive experience researching woodrat habitat on North Key Largo, also inspected the Harbor Course South property on behalf of the Intervenors. His inspection took place after the date of the Proposed Permit. He determined that the overall quality of the subject property as habitat for the endangered species was low because of the fragmented and uneven quality of the hammock. These qualities are largely attributed to the existing intrastructure and the golf course which winds throughout the subject property. Julie Hovis, a wild life biologist employed by the Commission, performed a site inspection report in connection with the application for the Proposed Permit. While not an expert on the endangered species, she was qualified to identify certain signs of the presence of the species. She found that there was some evidence that woodrats and cotton mice were present on the Harbor Course South property. She noted that the quality of the habitat varies greatly. Her inspection and conclusions were the basis for the Commission's assertion of jurisdiction over the subject site. Dr. Steven Humphrey and Dr. Numi Goodyear inspected the area on behalf of the Petitioners to determine the presence and/or density of the endangered species populations. While their studies find more evidence of the presence of wood rats and cotton mice on the subject property than the prior studies had indicated, they also conclude that the property is a mixed quality habitat for the endangered species. While there are some areas that appear to be high quality habitat, these experts recognize the fragmented character of the habitat and the effect of the golf course in disrupting the habitat and producing "islands of vegetation." The Goodyear and Humphrey studies confirm that the densities of the endangered species are lowest in areas where the hammock is highly fragmented. The Goodyear and Humphrey studies do not refute the Commission's conclusion that a significant number of the lots of Harbor Course South do not reflect sufficient indicia of the presence of the endangered species to allow the Commission to assert jurisdiction on all the property if a lot-by-lot permitting process was utilized. The Commission has concluded that the continuing development of Harbor Course South is inevitable. The Commission has also concluded that its authority over clearing of individual homesites is limited. In view of these conclusions, the Commission has attempted to enhance the survivability of the endangered species by imposing certain mitigation requirements on the Intervenors. The evidence has established that, assuming the development of Harbor Course South is inevitable, and the Commission lacks the authority to halt the development of Harbor Course South, the Commission's comprehensive approach to permitting will be more favorable to the survival potential of the endangered species than a lot-by-lot jurisdictional determination would be.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Florida Game and Fresh Water Fish Commission enter a Final Order setting forth the terms and conditions for an Agreement with the Intervenors for a specific period of time as set forth in Paragraph 30 of Conclusions of Law, whereby permits will be issued for the incidental destruction and/or molestation of the nests and habitat of the subject endangered species in accordance with the terms and conditions of the Proposed Permit as modified in accordance with the provisions of Paragraph 32 of the Conclusions of Law above. DONE AND ORDERED in Tallahassee, Leon County, Florida, this 17th day of October, 1990. J. STEPHEN MENTON 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 18th day of October, 1990.
