Loading...
Agenda 12/08/2020 Item #16D 3 (Conservation Collier Alligator Flag Preserve update)12/08/2020 EXECUTIVE SUMMARY Recommendation to approve the Alligator Flag Preserve Final Management Plan 10-year update under the Conservation Collier Program. OBJECTIVE: To obtain approval from the Board of County Commissioners (Board) for the Alligator Flag Preserve Final Management Plan 10-year update. CONSIDERATIONS: The Conservation Collier Ordinance, No. 2002-63, as amended, Section 14(3), requires that a Final Management Plan be prepared and updated for each property every five (5) years, with review and input by the Conservation Collier Land Acquisition Advisory Committee (CCLAAC). The Alligator Flag Preserve is comprised of eighteen (18) acres located on Immokalee Road two (2) miles east of I-75, at 7875 Immokalee Road, and has been in County ownership since July 28, 2006. The initial Final Management Plan was developed and approved by the Board on April 14, 2009, Agenda Item #16E3. The approved Plan has been operational for the Alligator Flag Preserve since that time. The first five-year update to the Plan was approved by the Board on June 23, 2015, Agenda Item #16D14. Each 10-year update requires a public meeting, which was held on September 17, 2020, to allow for public input on the updated draft plan. No public comment was received. The CCLAAC reviewed and approved the updated plan on October 12, 2020. Changes in this plan include updated maps, updated property status information, additions to the plant or animal lists, the status of exotic plant and animal infestations, and streamlining of text. Track ed changes have been made so that Board members can quickly see the proposed changes. Any formatting irregularities caused by tracked changes will be resolved in the final document. FISCAL IMPACT: Annual costs are estimated at $3,000 per year for the next five (5) years. This is primarily for invasive exotic plant treatment and trail maintenance. Funds are available within the Conservation Collier Land Management Fund (174) to accomplish these activities. GROWTH MANAGEMENT IMPACT: Management of Conservation Collier lands to support appropriate public access is consistent with and supports Policy 1.1.5 and Objective 1.3 in the Recreation and Open Space Element of the Collier County Growth Management Plan. There is no specific Growth Management impact associated with this item. LEGAL CONSIDERATIONS: The Conservation Collier Ordinance (No. 2002-63, as amended), in Section 14, provides a legal framework for the development of management plans and the use of environmentally sensitive lands. This item is approved for form and legality and requires a majority vote for Board action. -JAB RECOMMENDATION: To approve the attached proposed Final Management Plan 10-year update for the Alligator Flag Preserve and direct staff to implement the updated plan. Prepared By: Christal Segura, Senior Environmental Specialist, Parks and Recreation Division ATTACHMENT(S) 1. (linked) AlligatorFlagPreserve_10yr update_combined with Plant Survey (PDF) 16.D.3 Packet Pg. 2884 12/08/2020 COLLIER COUNTY Board of County Commissioners Item Number: 16.D.3 Doc ID: 14025 Item Summary: Recommendation to approve the Alligator Flag Preserve Final Management Plan 10-year update under the Conservation Collier Program. Meeting Date: 12/08/2020 Prepared by: Title: Operations Analyst – Parks & Recreation Name: Matthew Catoe 10/23/2020 1:32 PM Submitted by: Title: Division Director - Parks & Recreation – Parks & Recreation Name: Barry Williams 10/23/2020 1:32 PM Approved By: Review: Public Services Department Melissa Hennig Additional Reviewer Completed 10/23/2020 1:48 PM Parks & Recreation Barry Williams Additional Reviewer Completed 10/23/2020 4:40 PM Parks & Recreation Ilonka Washburn Additional Reviewer Completed 10/24/2020 8:36 AM Operations & Veteran Services Kimberley Grant Level 1 Reviewer Completed 10/26/2020 1:35 PM Public Services Department Todd Henry Level 1 Division Reviewer Completed 11/04/2020 2:06 PM County Attorney's Office Jennifer Belpedio Level 2 Attorney of Record Review Completed 11/06/2020 11:59 AM Public Services Department Steve Carnell Level 2 Division Administrator Review Completed 11/18/2020 1:55 PM Office of Management and Budget Debra Windsor Level 3 OMB Gatekeeper Review Completed 11/18/2020 1:58 PM County Attorney's Office Jeffrey A. Klatzkow Level 3 County Attorney's Office Review Completed 11/18/2020 2:27 PM Budget and Management Office Ed Finn Additional Reviewer Completed 11/25/2020 10:50 AM County Manager's Office Sean Callahan Level 4 County Manager Review Completed 11/30/2020 10:34 AM Board of County Commissioners MaryJo Brock Meeting Pending 12/08/2020 9:00 AM 16.D.3 Packet Pg. 2885 Conservation Collier Program 1 Alligator Flag Preserve Land Management Plan Managed by: Conservation Collier Program Collier County, Florida NovemberApril 20202009 – NovemberApril 20302019 (10-yr plan) Revised October 2020November 2014 105 year update Prepared by: Conservation Collier Staff; Parks and Recreation DivisionDepartment Conservation Collier Program 2 Alligator Flag Preserve Land Management Plan Executive Summary Lead Agency: Collier County Board of County Commissioners, Conservation Collier Program Property included in this Plan: “Alligator Flag Preserve” 18.46-acres. Preserve consists of two adjoining parcels of 9.23-acres each in Section 21, Township 48, and Range 26 of Collier County, Florida. Management Responsibilities: Agency: Collier County - Conservation Collier Program Designated Land Use: Conservation and natural resource based recreation Unique Features: cypress-pine-cabbage palm, cypress and pine flatwoods communities; four listed plant species recorded to date; preserve is within the Corkscrew Swamp Sanctuary Wood Stork Core Foraging Area Management Goals: Goal 1: Maintain high quality habitat with lLimited disturbance for the benefit of nNative flora and fauna Eliminate or significantly reduce human impacts to indigenous flora and fauna Goal 2: Continue plant and animalDevelop a baseline monitoring program report Goal 3: Remove or control populations of invasive, exotic or problematic flora and fauna Goal 4: Determine if prescribed fire and/or mechanical treatments are feasible to decrease woody invasion resulting from past fire exclusion; if so proceed Goal 5: Restore and maintain native habitats Goal 6: MonitorDevelop a plan for public use Goal 7: Facilitate uses of the site for educational purposes Goal 8: Provide a plan for security and disaster preparedness Public Involvement: Public meetings were held in January 2009 and September 2020 to review this Final Management Plan with residents and businesses from surrounding lands including staff from the Laurel Oak Elementary and Gulf Coast High Schools. Folio Number Legal Description 00186320002 21 48 26 W ½ OF W ½ OF SE ¼ OF SE ¼ , LESS R/W 9.23 AC 00186280003 21 48 26 E ½ OF W ½ OF SE ¼ OF SE ¼, LESS R/W 9.23 AC OR 519 PG 467 Conservation Collier Program 3 Table of Contents Land Management Plan Executive Summary ................................................................ 2 List of Tables ...................................................................................................................... 4 List of Figures .................................................................................................................... 4 List of Appendices ............................................................................................................. 5 1.0 Introduction ................................................................................................................. 6 1.1 Conservation Collier: Land Acquisition Program and Management Authority .............. 6 1.2 Purpose and Scope of Plan ..................................................................................................... 7 1.3 Location of the Alligator Flag Preserve ............................................................................... 7 1.4 Regional Significance of the Alligator Flag Preserve ......................................................... 8 1.5 Nearby Public Lands and Designated Water Resources ..................................................... 9 1.6 Public Involvement ............................................................................................................... 10 2.0 Natural Resources...................................................................................................... 11 2.1 Physiography ......................................................................................................................... 11 2.1.1 Topography and Geomorphology ..................................................................................... 11 2.1.2 Geology ............................................................................................................................ 11 2.1.3 Soils .................................................................................................................................. 12 2.1.4 Hydrology/Water Management ................................................................................ 131314 2.2 Climate ................................................................................................................................... 14 2.3 Natural Plant Communities ......................................................................................... 141415 2.3.1 Wetlands: Cypress-Pine-Cabbage Palm ........................................................................... 17 2.3.2 Wetlands: Cypress ............................................................................................................ 19 2.3.3 Uplands: Pine Flatwoods .................................................................................................. 20 2.3.4 Uplands: Australian Pine .......................................................................................... 202021 2.4 Native Plant and Animal Species ......................................................................................... 21 2.4.1 Plant Species ..................................................................................................................... 21 2.4.2 Animal Species ................................................................................................................. 21 2.5 Listed Species ........................................................................................................................ 23 2.5.1 Listed Plant Species .......................................................................................................... 24 2.5.2 Listed Animal Species ...................................................................................................... 26 2.6 Invasive, Non-native and Problem Species ......................................................................... 27 2.6.1 Invasive and Problem Plant Species ............................................................................. 2827 2.6.2 Invasive and Problem Animal Species ......................................................................... 3029 3.0 Previous and Current Use of the Preserve; Adjacent Land Uses ......................... 33 3.1 Previous Use of the Preserve and Adjoining Lands ........................................................... 33 3.2 Current Land Uses ............................................................................................................ 3534 3.3 Cultural, Historical and Archeological Resource Protection ....................................... 3635 3.4 Major Accomplishments during Previous Years ........................................................... 3635 Conservation Collier Program 4 4.0 Future Use of the Alligator Flag Preserveincluding Management Issues, Goals and Objectives .............................................................................................................. 3736 4.1 Management Plan Framework ........................................................................................ 3736 4.1.1 Preserve Manager: Contact Information .................................................................... 3736 4.2 Planned Uses and Assessment of their Impacts ............................................................. 3837 4.2.1 Identification of Public Uses Consistent with Preservation, Enhancement, Restoration, Conservation and Maintenance of the Resources ......................................................... 3837 4.3 Desired Future Conditions ............................................................................................... 3837 4.4 Goals for the 10 year period 2008-2018 .......................................................................... 3837 4.5 Establish an Operational Plan for the Alligator Flag Preserve ................................... 4847 4.5.1 Maintenance .................................................................................................................. 4847 4.5.2 Estimated Annual Costs and Funding Sources ............................................................. 4847 4.5.3 Potential for Contracting Restoration and Management Activities by Private Vendors ................................................................................................................................... 525150 5.0 Literature Cited ................................................................................................. 535251 List of Tables Table 1: Acquisition History and Status of Alligator Flag Preserve ............................................. 6 Table 2: Public Lands Located near the Alligator Flag Preserve .................................................. 9 Table 3: Extent of Florida Land Use, Land Cover Classification System Designations from 1995 and 2001 on the Alligator Flag Preserve ............................................................................... 15 Table 4: Summary of Natural Communities on the Alligator Flag Preserve ................................ 16 Table 6: Breeding Bird Species Recorded in the Corkscrew SW Quadrangle ............................. 23 Encompassing the Alligator Flag Preserve ................................................................................... 23 Table 7: Listed Plant Species Detected at the Alligator Flag Preserve......................................... 24 Table 8: Invasive Plant Species at Alligator Flag Preserve ......................................................... 28 Table 9: Major Accomplishments since the Acquisition of the Alligator Flag Preserve ........ 3736 Table 10: Invasive, Exotic Plant Species Control Plan for the Alligator Flag Preserve FLEPPC Category I species a ............................................................................................................ 4241 Table 11: Estimated Annual Land Management Budget .......................................................... 4948 Table 12: Potential Contracting for Restoration and Management Activities ...................... 525150 List of Figures Figure 1: General Location of Alligator Flag Preserve. ................................................................. 7 Figure 2: Conserved Lands in Collier County, Florida Including Lands Owned by Conservation Collier. ...................................................................................................................................... 8 Figure 3: Preserves and Protected Lands in the Vicinity of Alligator Flag Preserve ................... 10 Figure 4: Aerial View of the Alligator Flag Preserve Showing Delineation of Parcels .... 12Error! Bookmark not defined.Error! Bookmark not defined.. Figure 5: Soil Units on the Alligator Flag Preserve ..................................................................... 13 Figure 6: Distribution of Natural Communities on the Alligator Flag Preserve........................... 17 A) 1995 FLUCCS Layer B) 2014 Field Verified FLUCCS Layer ........................................... 17 Conservation Collier Program 5 Figure 8: Initial Exotic Vegetation Treatment Map for the Alligator Flag Preserve ............... 3029 Figure 9: Historical Aerial Photograph from 1973 of the Alligator Flag Preserve and Adjoining Lands .................................................................................................................................. 3433 Figure 10: Historical Aerial Photograph from 1996 of the Alligator Flag Preserve and Adjoining Lands .................................................................................................................................. 3534 Figure 11: Photo Point Locations within the Alligator Flag Preserve ..................................... 4140 Figure 12: Alligator Flag Preserve Conceptual Master Plan ................................................... 4645 List of Appendices Appendix 1: South Florida Vegetation Classification Scheme Crosswalks for Plant Communities Observed on the Alligator Flag Preserve Appendix 2: Preliminary Floristic Inventory of the Alligator Flag Preserve Appendix 3: Florida Natural Areas Inventory (FNAI) Managed Area Tracking Record and Element Occurrence Summary; FNAI ranking system explanation Conservation Collier Program 6 1.0 Introduction The Alligator Flag Preserve is an 18.46-acre natural area within the boundary of Collier County, Florida. Native plant communities within the preserve include cypress-pine-cabbage palm, cypress and pine flatwoods. A site assessment to determine compliance with Conservation Collier’s initial screening criteria was conducted in February 2005 and the Conservation Collier Program purchased the property on July 28, 2006. The County holds a fee simple title to the Alligator Flag Preserve. The Conservation Collier program manages these lands under authority granted by Conservation Collier Ordinance 2002-63 as amended (2007-65; available from www.municode.com). Initial acquisition activities are summarized in table 1. Conservation, restoration and natural resource-based recreation are the designated uses of this preserve. Management activities allowed include those necessary to preserve, restore, secure and maintain this environmentally sensitive land for the benefit of present and future generations. Public use of the site must be consistent with these management goals. Final management plans are considered living documents and can be updated at any time. All management plans must be approved by both the CCLAAC and the Collier County BCC. The original Final Management Plan was approved in 2009. This is the 10five-year update to the plan. 1.1 Conservation Collier: Land Acquisition Program and Management Authority The Conservation Collier program was originally approved by voters in November 2002 and subsequently confirmed in the November 2006 ballot referendum. Both voter-approved referendums enable the program to acquire, preserve, restore, and maintain vital and significant threatened natural lands, forest, upland and wetland communities located in Collier County, Florida (Ordinance 2002-63, as amended). Properties must support at least two of the following qualities to qualify for consideration: rare habitat, aquifer recharge, flood control, water quality protection, and listed species habitat. The BCC appointed a Land Acquisition Advisory Committee to consider any selected or nominated properties that an owner has indicated a willingness to sell. The committee recommends property purchases for final approval by the BCC. Lands acquired with Conservation Collier funds are titled to “COLLIER COUNTY, a political subdivision of the State of Florida, by and through its Conservation Collier program.” The BCC established the Conservation Collier program to implement the program and to manage acquired lands. As such, Conservation Collier holds management authority for the Alligator Flag Preserve. Table 1: Acquisition History and Status of Alligator Flag Preserve Year Benchmark 2005 Property nominated to the Conservation Collier Program 2005 Initial Criteria Screening Report accepted by the Conservation Collier Land Acquisition Advisory Committee 2006 Purchase approved by the Board of County Commissioners (BCC) and lands purchased 2006 Interim Management Plan completed and approved by BCC 2009 Final Management Plan completed 2010 Preserve Renamed the Alligator Flag Preserve 2014 Final Management Plan 5 year update 2020 Final Management Plan 10 year update Conservation Collier Program 7 1.2 Purpose and Scope of Plan The purpose of the plan is to provide management direction for Alligator Flag Preserve by identifying the goals and objectives necessary to eliminate or minimize any threats to the resources and integrity of the preserve. This text is a working document that establishes the foundation of the ten-year plan by identifying the appropriate management techniques necessary to restore and preserve the resource. This plan will balance resource restoration and protection with natural resource-based recreational and educational use while looking at restoration needs, listed species protection and maintenance of the site free of invasive, exotic plant and animal species. This plan is divided into sections that incorporate an introduction, descriptions of the natural and cultural resources, projected uses of the property, management issues, and goals and objectives. 1.3 Location of the Alligator Flag Preserve Alligator Flag Preserve is located approximately 2.10 miles east of Interstate 75 (I-75) between Preserve Lane and Preserve Circle on the north side of Immokalee Road (Figure 1). The Alligator Flag Preserve is in northwest Collier County in Section 21, Township 48 and Range 26. Figure 1: General Location of Alligator Flag Preserve. Conservation Collier Program 8 1.4 Regional Significance of the Alligator Flag Preserve Ecosystem services such as the protection of water resources, flood control, maintenance of nutrient cycles, preservation of biological diversity, carbon sequestration, and the availability of recreational lands are imperative for the well-being of the citizens of Collier County and may be achieved through the preservation of natural areas. As of March 2019February 2013, approximately 68% (over 881,070 877,000 acres) of all lands in Collier County were protected in conservation areas (Figure 2) and managed by private, local, state and federal agencies (FNAI 20193). Collier County’s Conservation Collier Program manages the 18.46-acre Alligator Flag Preserve; it contains cypress, cypress-pine-cabbage palm and pine flatwood communities. Specific information on the plant communities found on the Alligator Flag Preserve may be found in section 2.3 (Natural Plant Communities) of this document. Figure 2: Conserved Lands in Collier County, Florida Including Lands Owned by Conservation Collier. Conservation Collier Program 9 1.5 Nearby Public Lands and Designated Water Resources Currently, the closest preserved, natural areas to the Alligator Flag Preserve are the adjoining conservation easements to the north and west managed by Olde Cypress. Other preserves, in order of increasing distance, are provided in table 2. Figure 3 shows the locations of these preserves. Table 2: Public Lands Located near the Alligator Flag Preserve Name Approximate Distance (miles) Direction Type Olde Cypress Conservation Area 0.00 (adjoining) N & NW Private Corkscrew Regional Ecosystem Watershed 3.60 NE State Rivers Road Project 3.62 E/SE Conservation Collier Logan Woods Preserve 4.20 S Conservation Collier Cocohatchee Creek Preserve 4.45 W Conservation Collier Unit 53 Acquisition Boundary 4.50 NE Conservation Collier Railhead Scrub Preserve 5.15 W/NW Conservation Collier Nancy Payton Preserve 5.60 S/SE Conservation Collier Wet Woods Preserve 5.80 W/NW Conservation Collier Delnor-Wiggins Pass State Park 7.15 W State Barefoot Beach Preserve 7.40 W/NW County Conservation Collier Program 10 Figure 3: Preserves and Protected Lands in the Vicinity of Alligator Flag Preserve 1.6 Public Involvement Neighborhood involvement was sought through direct mailing notices for public meetings that were held in January 2009 and September 2020 to residents, other preserve managers and businesses within 1,500 feet of the preserve boundaries. Official public notices were posted on the County website. Staff will seek to coordinate management actions, such as exotic removal and prescribed fires with owners of adjoining lands. Staff will also work together with the adjacent Homeowners Association of the Fairway Preserve Condominiums, commercial property owners to the west and Olde Cypress to coordinate management activities (e.g., exotic plant removal/treatment) and public access efforts. Conservation Collier Program 11 2.0 Natural Resources 2.1 Physiography Alligator Flag Preserve lies within the Floridian section of the Coastal Plain. The Coastal Plain extends from New Jersey to Texas and was formed mainly from sedimentary rocks deposited in marine environments (USGS 2004). 2.1.1 Topography and Geomorphology The site is located in the Southwestern Slope region of the South Florida Water Management District. According to the Bonita Springs, Florida USGS Topographic Map, the topography of the area is relatively level with an average elevation of five feet above sea level and slopes gently westward toward the Gulf of Mexico. Surface water percolates directly into the uncovered ground or it collects in natural depressions and man-made ponds on adjacent properties. 2.1.2 Geology The geology of northern Collier County, where the Alligator Flag Preserve is located, is characterized by complex sequences of interbeded sands, clays, and limestone. Closest to the surface is the Holocene aged Pamlico Sand Formation, approximately ten feet thick and composed primarily of unconsolidated quartz sand and some silt. The Pamlico Sand unconformably overlies the Pleistocene aged Fort Thompson and Caloosahatchee Formations, which vary from a few feet to more than twenty feet in thickness and are characterized by shelly and sandy limestone with vugs and solution cavities (Miller 1986). Below the Fort Thompson and Caloosahatchee Formations are the Ochopee and Buckingham Members of the Pliocene aged Tamiami Formation, which are at least 200 feet thick in the surrounding areas (Oaks & Dunbar 1974). The Ochopee Limestone unconformably overlies the Buckingham Limestone and/or the equivalent Cape Coral Clay. This unconformity marks the bottom of the surficial aquifer separating it from the brackish underlying aquifer below. Then the Hawthorn Formation, rich in phosphate and other heavy minerals (Scott 1988), overlies the Oligocene age Suwannee Limestone and Eocene age Ocala Limestone that form the Floridan Aquifer System in Southwestern Florida. The Alligator Flag Preserve is located within the Southwestern Slope. Geologically, this is the dominant feature of Collier County (Campbell 1990). Figure 4 provides a current aerial view of the Alligator Flag Preserve including the delineation of the two parcels that make up the preserve. Conservation Collier Program 12 Figure 4: Aerial View of the Alligator Flag Preserve Showing Delineation of Parcels 2.1.3 Soils Mapped soils on this parcel were identified as Boca, riviera, limestone substratum & Copeland fine sands, Oldsmar fine sand, Holopaw fine sand and Basinger fine sand (Figure 5). Boca, riviera, limestone substratum & Copeland fine sands underlies 46% of the Alligator Flag Preserve and is a wetland soil association found in depressional areas typical of cypress swamps and marshes. Under natural conditions, these soils are ponded for 6 months of the year. Natural vegetation consists mostly of cypress, pickerelweed, rushes, alligator flag, sawgrass and willow (Liudahl et al. 1990). Oldsmar fine sand underlies 30% of the Alligator Flag Preserve and is the only non-hydric soil mapped on this Conservation Collier property. Oldsmar fine sand is a nearly level and poorly drained soil found in pine flatwoods. During extended dry periods, the water table may recede to a depth of 40+ inches, but under natural conditions, the seasonal high water table is between a depth of 6-18 inches. Flora typically associated with this soil type includes: South Florida slash pine, cabbage palm, saw palmetto and wax myrtle (Liudahl et al. 1990). Conservation Collier Program 13 Figure 5: Soil Units on the Alligator Flag Preserve The hydric Holopaw fine sand underlies 23% of the Alligator Flag Preserve. This nearly level, poorly drained soil is found in sloughs and poorly defined drainage ways. The permeability of water through this soil is moderate to moderately slow and, under natural conditions, the seasonal high water table is within a depth of 12 inches for three to six months. Water recedes to a depth of 40+ inches during extended dry periods and, during times of high rainfall, the soil may be covered with slowly moving water for approximately seven days. Flora typically associated with this soil type includes South Florida Slash Pine, cypress, cabbage palm, saw palmetto and wax myrtle (Liudahl et al. 1990). Basinger fine sand underlies 1% of the Alligator Flag Preserve and is a hydric, nearly level, poorly drained soil found in sloughs and poorly defined drainage ways. The permeability of water through this soil is rapid and, under natural conditions, the seasonal high water table is within a depth of 12 inches for three to six months. Water recedes to a depth of 40+ inches during extended dry periods and, during times of high rainfall, the soil may be covered with slowly moving water for approximately seven days. Flora typically associated with this soil type includes South Florida slash pine, cypress, cabbage palm, saw palmetto and wax myrtle (Liudahl et al. 1990). 2.1.4 Hydrology/Water Management Near the surface, the aquifer is highly permeable and the groundwater flows toward the west. However, permeability decreases downward from a porous limestone into poorly indurated Conservation Collier Program 14 sandstone cemented by micrite. The aquifer grades from freshwater downward into brackish water due to the proximity of the Gulf of Mexico to the west and the brackish water in the intermediate aquifer made primarily of Miocene aged sediments. Below that, the Hawthorne formation typically marks the upper boundary of the Floridian aquifer, which is contained within the underlying Oligocene age Suwannee Limestone (Lodge 2005). A berm runs along the southern boundary of the Alligator Flag Preserve just north of the Cocohatchee Canal. This berm prevents most water from flowing southward consequently holding water on the preserve for an artificially long period during the wet season. Some outflow does occur from the Preserve to the Immokalee Road canal via a culvert, which is placed fairly high in elevation. When surface water is high, and flows are occurring, the resulting drainage pattern in the preserve has caused some erosion. The Surficial Aquifer is an aquifer close to the surface and unconfined, typically associated with the groundwater table. This aquifer is generally limited to smaller uses such as household or small agricultural uses. The Lower Tamiami aquifer is below this aquifer and is recognized as being useful for long-term water needs. According to the South Florida Water Management District’s (SFWMD) technical publication 95-02 (Fairbank & Hohner 1995), the Surficial Aquifer recharge capacity on the Alligator Flag Preserve is moderate at 43 to 56 inches annually. The Lower Tamiami Aquifer recharge capacity on the preserve is relatively low at 7 to 14 inches annually. 2.2 Climate The Alligator Flag Preserve is located in an area of Florida where humid subtropical and tropical savanna climatic patterns overlap, with temperatures moderated by winds from the Gulf of Mexico and the Atlantic Ocean. Sharply delineated wet and dry seasons and average monthly temperatures greater than 64º Fahrenheit characterize a tropical savanna climate. Monthly rainfalls may exceed ten inches during the wet season. On the other hand, humid subtropical climates typically show less extreme rainfall fluctuations between wet and dry seasons and average monthly temperatures is less than 64º Fahrenheit in some months. The average annual temperature for the coastal portion of Collier County is approximately 75º Fahrenheit. The warmest months are usually July and August. The humidity is high during these months but frequent afternoon thunderstorms prevent excessively high temperatures. Two-thirds of the annual rainfall occurs in the wet season from May to October. Thunderstorms are frequent during the wet season, occurring every two out of three days between June and September. Rainfall records for the area indicate that there is not significant variation in the annual rainfall throughout much of the county; however, large variations often occur during a single year. The Atlantic hurricane season extends from June through November with peak activity occurring in September and October when ocean temperatures are highest. 2.3 Natural Plant Communities A plant community refers to the suite of floristic species that form the natural vegetation of any place. In addition to anthropogenic influences, the combination of factors such as geology, topography, hydrology, underlying soils and climate determine the types of plants found in an area. These plants, in turn determine the animal species that may be found there. The description or classifications of these floral communities differ by agency and are based on an agency’s goals and objectives for identifying plant communities. As some categorizations are broad (e.g., forest) while others are specific (e.g., mesic pine flatwoods), determining how each organization classifies Conservation Collier Program 15 a community may be difficult. The South Florida Vegetation Classification Scheme Crosswalks (Gilbert 2005) provides a way to decipher the classifications of plant communities across agencies. Appendix 1 provides the categorization of the plant communities observed on the Alligator Flag Preserve based on the South Florida Vegetation Classification Scheme Crosswalks; classifications from the Florida Natural Areas Inventory (FNAI) are also included in this appendix. The Florida Land Use, Land Cover Classification System (FLUCCS) created by the Southwest Florida Water Management District in 1995 classifies plant communities and provides GIS layers for users to overlay on property boundaries and aerial images to better determine the plant communities found there. The FLUCCS designates three plant communities on the preserve: Pine Flatwoods – Melaleuca Infested (FLUCCS 4119), Cypress – Melaleuca Infested (FLUCCS 6218), and Forested Mixed Wetlands (FLUCCS 630). Wilson Miller updated the FLUCCS data layer in 2001. These data also indicate that there are three plant communities on the preserve, however, the Pine Flatwood community is not identified, instead a Cypress (FLUCCS 621) community is identified in addition to the Cypress- Melaleuca Infested community. Table 3 summarizes the plant communities mapped for the Alligator Flag Preserve in 1995 and 2001; it shows the differences in the location and extent of land cover designations. Figure 6 visually represents these land cover designations from 1995 and 2001. Given that the FLUCCS layers were generated at a scale of 1:24,000 and created by different entities at different times, the change in the types and extent of plant communities between the map layers may indicate a change in hydrology within the preserve or natural discrepancy generated when different entities perform the same task. It is unlikely that these data were ground-truthed by the Water Management District or Wilson Miller specifically on the Alligator Flag Preserve, however; both layers seem to be fairly accurate in other parts of the County. During initial site visits to the Alligator Flag Preserve before acquisition, staff observed Cypress- Pine-Cabbage Palm (FLUCCS 624), Cypress and Pine Flatwoods (FLUCCS 411) communities. These communities were in varying states of exotic vegetation infestation. Additionally, a monoculture of Australian pines (Casuarina spp.; FLUCCS 4370) was observed in the southeastern portion of the property. Johnson Engineering ecologists conducting a preliminary wetlands and wildlife assessment of the site in August 2004 reported observing similar vegetative communities. They categorized the communities according to the degree of exotic infestation, described the pine flatwoods as FLUCCS 4119 (disturbed) and noted that the cypress community contained scattered pine. Given the discrepancy between the 1995 and 2001 FLUCCS digital layers (as they pertain to the Alligator Flag Preserve) and the removal of exotic vegetation since the acquisition of the property in July 2006, staff created a new digital layer showing the location and extent of the native plant Table 3: Extent of Florida Land Use, Land Cover Classification System Designations from 1995 and 2001 on the Alligator Flag Preserve FLUCCS CODE Mapped Plant Community 1995 2001 4119 Pine Flatwoods – Melaleuca Infested 45% 0% 621 Cypress 0% 12% 6218 Cypress – Melaleuca Infested 43% 84% 630 Forested Mixed Wetlands 12% 4% Conservation Collier Program 16 communities currently found on the preserve (Sept. 2008; Figure 7). Because the removal of invasive, exotic plants began in April 2008, this new layer does not reference any areas as infested with exotic plant species except for the stand of Australian pines in the southeastern portion of the preserve. Specific information on the invasive, exotic species present on the preserve is provided in section 2.6.1 of this document. The vegetation classification scheme of the Florida Natural Areas Inventory (FNAI) and the Florida Department of Natural Resources (FDNR) (1990) are presented in table 4. This table is based on the plant communities observed on the Alligator Flag Preserve. The following subsections (2.3.1, 2.3.2, 2.3.3 and 2.3.4) provide information about the plant communities observed on the preserve. Table 4: Summary of Natural Communities on the Alligator Flag Preserve FNAI Natural Community Type Global Rank State Rank Comments Strand Swamp G4 S4 Also called Flowing Water Swamps and Cypress communities Wet Flatlands G4 S4 Also called Cypress-Pine-Cabbage Palm communities and Hydric Pine Flatwoods Mesic Flatwoods G4 S4 Also called Pine Flatwoods G4: Apparently secure globally (may be rare in parts of range); S4: Apparently secure in Florida (may be rare in parts of range). Conservation Collier Program 17 Figure 6: Distribution of Natural Communities on the Alligator Flag Preserve A) 1995 FLUCCS Layer B) 2014 Field Verified FLUCCS Layer Conservation Collier Program 18 2.3.1 Wetlands: Cypress-Pine-Cabbage Palm A cypress-pine-cabbage palm community comprises approximately 57% of the Alligator Flag Preserve and is located primarily in the center portions of the preserve. This community dominates the western boundary of the preserve and occupies a little over two thirds of the eastern boundary (Figure 7). Also known as wet flatwoods, low flatwoods, hydric flatwoods (FNAI & FDNR 1990) and hydric pine flatwoods (USFWS 1999b) the cypress-pine-cabbage palm community typically includes a canopy of cypress, pine (Pinus spp.) and/or cabbage palm (Sabal palmetto) in combinations in which none of the species achieves dominance. This assemblage forms a transition between hydric sites (e.g., cypress communities) and moist upland sites (e.g., mesic pine flatwoods). This ecotonal community is unique to South Florida and functions as both a wetland and upland at different times of the year. As such, both hydrology in the wet season and fire in the dry season drive this dynamic system. As a result, this community is typically dominated by a slash pine (Pinus elliottii var. densa) overstory with a wetland plant understory. The wetland understory can be any, or a variety, of wetland plant community types ranging from wet prairie to hatrack cypress. Hydric pine flatwoods are distinct from mesic and xeric pine flatwoods in the absence of understory dominance by saw palmetto (Serenoa repens) and more xeric species such as pennyroyal (Piloblephis rigida), pawpaw (Asimina spp.), and prickly pear (Opuntia spp.). The berm that runs along the southern boundary of the Alligator Flag Preserve, just north of the Cocohatchee Canal, prevents water from flowing southward consequently holding water on the preserve for an artificially long period of time during the wet season. The cypress-pine-cabbage palm community provides important forested habitat for a number of species often found in wetlands and uplands. Wildlife species that utilize this habitat include: the Florida black bear (Ursus americanus floridanus), Florida panther, wood stork, red-cockaded woodpecker (Picoides borealis), Everglades snail kite (Rostrhamus sociabilis plumbeus), the recently de-listed bald eagle, eastern indigo snake, gopher tortoise (Gopherus polyphemus), Big Cypress fox squirrel (Sciurus niger avicennia), Bachman’s sparrow (Aimophila aestivalis), bobcat (Lynx rufus), swallow-tailed kite (Elanoides forficatus), Florida weasel (Mustela frenata peninsulae), limpkin (Aramus guarauna), northern harrier (Circus cyaneus), southeastern kestrel (Falco sparverius paulus), eastern American kestrel (F. s. sparverius) and the Florida sandhill crane (Grus canadensis pratensis). Additionally, this community provides essential habitat to the breeding life cycle of aquatic and wetland-dependent animals, and a major forest cover for cover-dependent species. Hydric pine flatwoods provide aquatic habitat for both young and adult amphibians and adult tree frog climbing areas. Hydric flatwoods serve as wading bird foraging areas, black bear foraging, denning, and travelways, and essential red-cockaded woodpecker foraging and nesting habitat (USFWS 1999b). Cypress-Pine-Cabbage Palm Community within the Alligator Flag Preserve. Photo by Annisa Karim Conservation Collier Program 19 Since the cypress-pine-cabbage palm community comprises a majority of the preserve, all soils identified on the preserve (Boca, riviera, limestone substratum & Copeland fine sands, Oldsmar fine sand, Holopaw fine sand and Basinger fine sand) are found within this community. 2.3.2 Wetlands: Cypress A Cypress community dominates approximately 24% of the northern portion of the Alligator Flag Preserve. One hundred percent of the northern boundary of the preserve contains this plant community (Figure 7). Also known as flowing water swamps (Gilbert 2005), cypress stands, stringers and strand swamps (FNAI & FDNR 1990), these forested cypress communities are shallow, seasonally inundated and commonly found along and within drainage channels (USFWS 1999a). Deeper parts of this community may be characterized as a cypress slough. The hydrology of an area drives the formation of cypress communities (Sullivan 1994). Additionally, light surface fires every 30 to 200 years are essential to the maintenance of these communities. Without these fires, invasion by hardwoods and peat accumulation would degrade this community. The canopy of the cypress community within the Alligator Flag Preserve is dominated by cypress (Taxodium sp.) and contains popash (Fraxinus caroliniana), strangler fig (Ficus aurea) and red maple (Acer rubrum). The midstory contains swamp dogwood (Cornus foemina), wax myrtle (Myrica cerifera), buttonbush (Cephalanthus occidentalis). Groundcover species include Alligator Flag PreserveFlag Preserve flag (Thalia geniculata), swamp fern (Blechnum serrulatum) and false nettle (Boehmeria cylindrica). In a landscape context, the presence of highly functioning cypress communities within a matrix of other types of wetland and upland communities is imperative for many species of wildlife, including listed species. Listed species that benefit with the presence of the cypress community on the Alligator Flag Preserveinclude the Florida panther (Puma concolor coryi), wood stork (Mycteria americana), Kirtland’s warbler (Dendroica kirtlandii), and eastern indigo snake (Drymarchon corais couperi). The recently de-listed bald eagle (Haliaeetus leucocephalus) is also a species that benefits from the presence of cypress communities (USFWS 1999a). The berm that runs along the southern boundary of the Alligator Flag Preserve, just north of the Cocohatchee Canal, prevents water from flowing southward consequently holding water on the preserve for an artificially long period of time during the wet season. This results in deeper water in the cypress area than is normally seen in other naturally functioning cypress areas. The cypress community within the preserve is underlain with depressional Boca, riviera, limestone substratum & Copeland fine sands and Basinger fine sand. Cypress Community within the Alligator Flag Preserve. Photo by Christal Segura Conservation Collier Program 20 2.3.3 Uplands: Pine Flatwoods A Pine Flatwood community dominates approximately 19% of the Alligator Flag Preserve. This plant community is located in the southeastern portion of the property and comprises over 50% of the southern boundary (Figure 7). Pine flatwoods are one of the most wide-ranging terrestrial plant communities in Florida and consequently one of the most influenced by anthropogenic activities (Abrahamson & Hartnett 1990). Fire strongly influences the community structure and composition of these communities. The term pine flatwoods is a general categorization of areas that are dominated by various species of pine (Pinus spp.) trees. Pine flatwoods may be found in mesic flatlands where the landscape is made up of flat, moderately well drained sandy substrates with a mixture of organic material, often with an underlying hard pan layer. An open canopy forest of widely spaced pine trees with little or no understory but a dense ground cover of herbs and shrubs characterize natural, mesic flatwoods that have been burned regularly (FNAI & FDNR 1990). The USDA Soil Conservation Service classification system refers to these areas as South Florida flatwoods. South Florida flatwoods are typically savannas, a type of plant community intermediate between forest and grassland. Mesic pine flatwoods are also called mesic flatwoods, pine savanna, cabbage palm savanna, and pine barrens. Oldsmar fine sand and Holopaw fine sand underlies this part of the preserve. The berm that runs along the southern boundary of the Alligator Flag Preserve, just north of the Cocohatchee Canal, prevents water from flowing southward consequently holding water on the preserve for an artificially long period during the wet season. As a result, this community holds comparably more water than other naturally functioning mesic pine flatwoods. Commo n mesic pine flatwood species such as saw palmetto, wax myrtle (Myrica cerifera), cabbage palm and saffron plum (Sideroxylon celastrinum) are found in this portion of the preserve. Additionally, species usually found in wet areas such as sawgrass (Cladium jamaicense), swamp fern (Blechnum serrulatum) and wiregrass (Aristida stricta var. beyrichiana) are found in the pine flatwood portion of the Alligator Flag Preserve. Mesic flatwoods provide essential forested habitat for a variety of wildlife species including Neotropical migratory birds, wide- ranging large carnivores, mid-sized carnivores, ground-nesting vertebrates, tree- cavity dependent species, tree-nesting species and non-aquatic plant life. “At the current rate of habitat conversion, the mesic pine flatwoods, once the most abundant upland habitat in South Florida, is in danger of becoming one of the rarest habitats in South Florida” (USFWS 1999c). 2.3.4 Uplands: Australian Pine A stand of invasive, exotic Australian pines once comprised approximately 1% of the Alligator Flag Preserve and its description is included in this section (2.3 Natural Plant Communities) to provide a comprehensive assessment of the entire Alligator Flag Preserve. Invasive, exotic species Mesic pine flatwoods within the Alligator Flag Preserve. Photo by Christal Segura Conservation Collier Program 21 are discussed in more detail in section 2.6 (Invasive, Non-native and Problem Species) of this document. The Australian pine monoculture was located in the southeastern portion of the property on the eastern edge of the pine flatwood community. The smaller Australian pines were removed in late April 2008 and the larger trees were removed in 2009. Figure 7 reflects the extent of this community after the smaller trees were removed. 2.4 Native Plant and Animal Species A cypress-pine-cabbage palm community comprises the majority (57%) of the 18.46-acre Alligator Flag Preserve. Smaller areas of the preserve are comprised of cypress (24%) and pine flatwoods (18%) communities; a small stand of Australian pines (1%) also exists on the preserve. This section discusses the flora and fauna found within these plant communities. The next section (2.5) discusses all listed species in greater detail. 2.4.1 Plant Species Initially, 63 plant species were recorded on the preserve in 2008. When Conservation Collier staff conducted a preliminary floristic inventory in August and September 2008. An updated plant survey was conducted in the Summer of 2020, in which 152 species were recorded. Another survey was conducted in March 2009, counting 80 species. There are likely more. The revised list has been added to this plan (Appendix 2). Of these 15280 species, 139 72 (9190%) are native - of which, three are listed by the State of Florida (one as endangered; two as threatened); one is listed as commercially exploited). One additional survey will be conducted in the winter of 2020-21 if additional plants are found they will be added to this plan. 2.4.2 Animal Species Due to the dearth of specific surveys for the occurrence of animal species (in contrast to plants) and the lack of on-site staffing, little is recorded for actual occurrences of animals at the Alligator Flag Preserve. Occurrences of fauna at the preserve are based on direct visual and aural observations by staff during site visits or evidence of activity such as spoor, scat, or burrows, and from the site information available in documents such as the site’s initial criteria screening report, the property’s interim management plan and anecdotal information from persons with knowledge of the site. In 2015-16, wildlife cameras were placed on the preserve. Several additional species were observed as a result. Table 5 provides a comprehensive list of animals, both native and non-native, recorded on the Alligator Flag Preserve thus far. White-tailed deer and fawn Alligator Flag Preserve 2015 Conservation Collier Program 22 The Florida Breeding Bird Atlas (FFWCC 2003) lists 49 avian species that have been recorded as confirmed, probable, or possible breeding in the vicinity of the site (Table 6). The Breeding Bird Atlas documents breeding distributions of all bird species in Florida between 1986 and 1991. Some of these species may breed at the Alligator Flag Preserve. Other wildlife species that have not yet been recorded undoubtedly occur at the Alligator Flag Preserve. During migration periods, transient bird species would be expected to utilize this area for short periods of time. The developed character of the adjacent areas may inhibit transient use by many mammal, reptile, and amphibian species, thus limiting the utilization of the preserve to resident individuals or inhibiting the dispersal of many species to and from the preserve. Table 5: Faunal Species Recorded on the Alligator Flag Preserve Common Name Scientific Name American Robin Turdus migratorius Blue-gray Gnatcatcher Polioptila caerulea Blue Jay Cyanocitta cristata Cedar Waxwing Bombycilla cedrorum Common Ground-Dove Columbina passerina Great Crested Flycatcher Myiarchus crinitus Great Egret Ardea alba Mourning Dove Zenaida macroura Northern Mockingbird Mimus polyglottos Prothonotary Warbler Protonotaria citrea Red-bellied Woodpecker Melanerpes carolinus Red-shouldered Hawk Buteo lineatus White-eyed Vireo Vireo griseus Wood stork Mycteria americana Big Cypress fox squirrel Sciurus niger Florida Black Bear Ursus americanus floridanus Coyote Canis latrans Racoon Procyon lotor Black racer Coluber constrictor priapus Brown anole a Anolis sagrei Bluestripe Ribbon snake Thamnophis sauritus nitae Water moccasin Agkistrodon piscivorus White-tailed deer Odocoileus virginianus Monarch butterfly Danaus plexippus Gulf Fritillary butterfly Agraulis vanillae Zebra Longwing butterfly Heliconius charitonius Florida Ivory millipede Chicobolus spinigerus Crab-like Spiny Orbweaver spider Gasteracantha cancriformis Red imported fire ant a Solenopsis invicta Conservation Collier Program 23 Table 6: Breeding Bird Species Recorded in the Corkscrew SW Quadrangle Encompassing the Alligator Flag Preserve Common Name Scientific Name Common Name Scientific Name Green Heron Butorides virescens Red-cockaded Woodpecker Picoides borealis Yellow-crowned Night-Heron Nyctanassa violacea Northern Flicker Colaptes auratus Wood Duck Aix sponsa Pileated Woodpecker Dryocopus pileatus Mottled Duck Anas fulvigula Great Crested Flycatcher Myiarchus crinitus Swallow-tailed Kite Elanoides forficatus Loggerhead Shrike Lanius ludovicianus Red-shouldered Hawk Buteo lineatus White-eyed Vireo Vireo griseus Northern Bobwhite Colinus virginianus Blue Jay Cyanocitta cristata King Rail Rallus elegans Fish Crow Corvus ossifragus Common Moorhen Gallinula chloropus Purple Martin Progne subis Limpkin Aramus guarauna Northern Rough-winged Swallow Stelgidopteryx serripennis Killdeer Charadrius vociferus Tufted Titmouse Baeolophis bicolor Mourning Dove Zenaida macroura Carolina Wren Thryothorus ludovicianus Common Ground-Dove Columbina passerina Blue-gray Gnatcatcher Polioptilia caerulea *Rose-ringed Parakeet Psittacula krameri Northern Mockingbird Mimus polyglottos Yellow-billed Cuckoo Coccyzus americanus Brown Thrasher Toxostoma rufum Barn Owl Tyto alba Northern Parula Parula americana Eastern Screech-Owl Megascops asio Pine Warbler Dendroica pinus Great Horned Owl Bubo virginianus Prairie Warbler Dendroica discolor Barred Owl Strix varia Common Yellowthroat Geothlypis trichas Common Nighthawk Chordeiles minor Eastern Towhee Pipilo erythrophthalmus Chuck-will's-widow Caprimulgus carolinensis Northern Cardinal Cardinalis cardinalis Red-headed Woodpecker Melanerpes erythrocephalus Red-winged Blackbird Agelaius phoeniceus Red-bellied Woodpecker Melanerpes carolinus Eastern Meadowlark Sturnella magna Wood Stork Mycteria americana Common Grackle Quiscalus quiscula Downy Woodpecker Picoides pubescens Boat-tailed Grackle Quiscalus major * = non-native species 2.5 Listed Species Official lists of rare and endangered species are produced at the federal level by the United States Fish and Wildlife Service and the National Marine Fisheries Service and at the State level by the Florida Fish and Wildlife Conservation Commission and the Florida Department of Agriculture and Consumer Services. FNAI produces a list of rare and endangered species, and maintains a database of occurrences of these species in Florida. The Institute for Regional Conservation (IRC) also ranks native plant species by conservation status in the 10-county area of South Florida. The following subsections (2.5.1 and 2.5.2) discuss the listed, rare and protected plant and animal species found within and close to the Alligator Flag Preserve in detail. Conservation Collier Program 24 2.5.1 Listed Plant Species The Florida State Statute titled “Preservation of native flora of Florida” (Statute 581.185) provides the following definitions: Endangered plants means species of plants native to the state that are in imminent danger of extinction within the state, the survival of which is unlikely if the causes of a decline in the number of plants continue, and includes all species determined to be endangered or threatened pursuant to the federal Endangered Species Act of 1973, as amended, Pub. L. No. 93-205 (87 Stat. 884). Threatened plants means species native to the state that are in rapid decline in the number of plants within the state, but which have not so decreased in such number as to cause them to be endangered. Commercially exploited plants means species native to the state, which are subject to being removed in significant numbers from native habitats in the state and sold or transported for sale. Four listed There are three (3) plant species have been found at Alligator Flag Preserve that are listed by the Florida Department of Agriculture and Consumer Services (FDACS), one (1) as endangered, one (21) as threatened., and one (1) as commercially exploited (Table 7). A brief description of these species and their status is included in the following paragraphs. Table 7: Listed Plant Species Detected at the Alligator Flag Preserve Common Name(s) Scientific Name State Stiff-leaved wild-pine, Cardinal airplant Tillandsia fasciculata E Reflexed wild-pine, Northern needleleaf Tillandsia balbisiana T West Indian mahogany Swietenia mahogoni T Royal fern Osmunda regalis var. spectabilis C T: Threatened; E: Endangered; C: Commercially Exploited Two of the three listed plant species found on the Alligator Flag Preserve are classified as bromeliads. Bromeliads are members of the pineapple family (Bromeliaceae). While some of these species may be found growing terrestrially, most native bromeliads found in Florida are found growing attached to tree trunks and branches and may therefore be referred to as epiphytes (a plant that lives upon other plants; from Greek “epi” = upon “phyte” = plant). The leaves and/or roots of these air plants (depending on the species) absorb the water and nutrients they need from the air and from the rain that falls through the canopy of the tree on which they are found. Since epiphytes use their roots only to anchor themselves to another plant, they are considered non- parasitic. Even though the three listed bromeliad species found on the Alligator Flag Preserve are fairly common in the state, they are listed due to illegal collecting and the destruction of the habitats in which they are found. Additionally, infestation by the introduced Mexican bromeliad weevil (Metamasius callizona) has been implicated in the decline of many air plant populations around the state. Currently, there are no control measures in place however, close research and monitoring is taking place. Conservation Collier Program 25 Stiff-leaved Wild Pine (Tillandsia fasciculata), is also known as cardinal air plant and common wild pine. T. fasciculata is listed as an endangered plant by the State of Florida and has been in 24 counties throughout Florida (Wunderlin & Hansen 2008). This epiphyte was frequently found in South Florida before the introduction of the Mexican bromeliad weevil. Today, it may be found in hammocks, cypress swamps and pinelands. Like most of the other bromeliads in Florida, this species is often referred to as a “tank” bromeliad because the leaf axils and central stems form a “tank” or reservoir at the base of the plant. These reservoirs capture and hold water, dead and decaying plant matter (leaves, seeds twigs, etc.), and dead and drowning non-aquatic insects; these trapped items provide nutrients for the plant (Larson et al. 2006). Reflexed wild pine (Tillandsia balbisiana) is an epiphytic, “tank” bromeliad and is listed as a threatened plant by the State of Florida. Wunderlin and Hansen reported this species in 22 counties throughout Florida as of 2008 (Wunderlin & Hansen 2008). Reflexed wild pine is an occasional species in South Florida and is usually found in scrub, pinelands, strand swamps, hammocks, mangrove swamps and on shell ridges/mounds. Royal fern (Osmunda regalis var. spectabilis) is not in danger of being extirpated in Florida because of habitat loss, habitat fragmentation or attack by an exotic, invasive pest, but because of commercial exploitation. According to Nelson (2000), the fibers from the stem of royal fern have been used as a growing medium to grow orchids as well as to make ropes and nets. Additionally, this species is believed to have medicinal benefits; other parts of the plant may have been used to treat wounds and broken bones, relieve sprains and to help alleviate coughs and diarrhea. In Florida, this species can be found in hydric areas such as wet flatwoods, cypress swamps, floodplains, stream banks and bogs. FNAI maintains a database of occurrences of rare, threatened, and endangered species in Florida. An element is any exemplary or rare component of the natural environment, such as a species, natural community, bird rookery, spring, sinkhole, cave, or other ecological feature. An element occurrence is a single, extant habitat that Tillandsia fasciculata; Photo by Annisa Karim View of T. fasciculata with water in the “tank”. Photo by Annisa Karim Osmunda regalis var. spectabilis Photo by Annisa Karim Tillandsia balbisiana Photo by Annisa Karim Conservation Collier Program 26 sustains or otherwise contributes to the survival of a population or a distinct, self-sustaining example of a particular element. This species was not found in the first 2020 botanical survey. West Indian Mahogany (Swietenia mahogoni) This species is considered to native to South Florida and into the Florida Keys. It is often planted outside of its historical range, and is now escaping from cultivation and sometimes invading conservation areas. It is a medium to large tree with an erect trunk and a broad, dense, rounded crown. Bark reddish-brown, thick, roughened by thick scales. Leaves tropical semi-deciduous, compound, 4-8 inches long, dark green above, It was heavily logged in South Florida prior to the 1900s. Poaching of logs continued in the Florida Keys well into the late 20th century. It is listed as threatened by the state of Florida (IRC 2020). These element occurrence data are built into biodiversity matrices. Each matrix encompasses one (1) square mile and includes all species and natural communities tracked by FNAI, including all federal listed species. The FNAI report for the matrix in which the Alligator Flag Preserve is located identifies three likely elements and 18 potential elements. Of the three likely elements, one has been observed on the preserve, namely mesic pine flatwoods (described in section 2.3.3 of this document). None of the 18 potential elements reported by FNAI have been detected within the preserve. Appendix 3 provides the FNAI Managed Area Tracking Record and Element Occurrence Summary as well as the Biodiversity Matrix Report. Global and state rankings are provided for each species as well as their federal and state status. 2.5.2 Listed Animal Species Big Cypress fox squirrels and woodstorks have been observed on the preserve on multiple occasions. No other listed wildlife species have been observed on the Alligator Flag Preserve. According to a 2004 Preliminary Wetlands and Wildlife Assessment prepared by Johnson Engineering, the property is within the Corkscrew Swamp Sanctuary Wood Stork Core Foraging Area (18.6 miles), a documented wood stork rookery. The report also states that research of SFWMD Permit 11-01232-S indicated that “The Woodlands” (the adjacent Olde Cypress preserve property) at one time supported a viable population of Big Cypress fox squirrels and provided some nesting and foraging habitat for listed wading birds. Three wildlife species were reported as likely to occur (rare species likely to occur on the site based on suitable habitat and/or known occurrences in the vicinity) and eleven species were reported as potential occurrences (site lies within the known or predicted range of species) within FNAI’s Biodiversity Matrix for the Alligator Flag Preserve. Appendix 3 provides the FNAI Managed Area Tracking Record and Element Occurrence Summary as well as the Biodiversity Matrix Report. Global and state rankings are provided for each species as well as their federal and state status. Swietenia mahogoni Source: Wikipedia Conservation Collier Program 27 Wood stork (Mycteria americana) The Wood Stork is listed by tThe Florida Fish and Wildlife Conservation Commission (FFWCC) and the United States Fish and Wildlife Service (USFWS) as a threatened n endangered species. Also known as the wood ibis or flint head, this species is one of the largest wading birds found in Florida and the only stork in the United States. The wood stork is a tactile feeder and may be found in fresh, brackish, and saltwater habitats. Because of its dependence on naturally functioning hydrologic systems, the National Audubon Society refers to this wading bird as the “barometer of the Everglades”. For this reason, the wood stork is an excellent environmental indicator of wetland health (Mazziotti 2002). The Big Cypress fox squirrel (Sciurus niger avicennia) Several Big Cypress fox squirrel sightings have been recorded on the preserve. Also known as the mangrove fox squirrel, the FFWCC lists this species as threatened in Florida. While the species is widespread in eastern and central North America, the subspecies is endemic to southwestern Florida – specifically in the Immokalee Rise, Big Cypress Swamp, and Devil's Garden area in Collier County. Some areas of this range have become vacated, while many other suitable areas are being altered or becoming isolated through development. The subspecies uses most types of forest occurring in its range. However, dense interiors of mixed cypress-hardwood strands seem to be avoided by Big Cypress fox squirrels due dense populations of gray squirrels (Sciurus carolinensis) occupying these areas. Big Cypress fox squirrels have been reported in cypress swamp, pine flatwood, tropical hammock, hardwood hammock, mangrove swamp, and suburban habitats including golf courses, and residential areas in native vegetation. Big Cypress fox squirrel densities appear to be quite low, and on this basis the subspecies can be considered inherently rare (Humphrey & Jodice 1992). 2.6 Invasive, Non-native and Problem Species In an ecological context, an invasive species is one that is aggressive in growth and expansion of range and tends to dominate others; its establishment and dominance can cause widespread harm to an ecological system by altering the species composition, susceptibility to fire and hydrology of an area. Non-indigenous species (i.e., non-native or exotic species) are those that have been introduced purposefully or accidentally to an area outside their normal range. The characteristics of some of these species (high rate of growth/reproduction, no natural predators, easily dispersed, able to out-compete native species) make them invasive. Some indigenous species (a species whose natural range included Florida at the time of European contact circa 1500 AD or a species that has naturally expanded or changed its range to include Florida) may also become invasive. Invasions by native and non-native species often follow an alteration to ecosystem function, disruption of the food web, large-scale fragmentation of an ecosystem and/or disturbance (e.g., clearing, fire, drought, etc) of an area. While some native species may become invasive, the establishment and dominance of non-native species is of particular concern. The exotic plant and Big Cypress Fox Squirrel Alligator Flag Preserve 2016 Wood Stork Photo Credit M. DuVall Conservation Collier Program 28 animal species documented within the preserve and those that have a potential to occur within the preserve are discussed in the following sections. 2.6.1 Invasive and Problem Plant Species The Florida Exotic Pest Plant Council (FLEPPC) maintains a list of exotic plants that have been documented to (1) have adverse effects on Florida’s biodiversity and plant communities, (2) cause habitat loss due to infestations and (3) impact endangered species via habitat loss and alteration. Fifteen ight invasive exotic non-indigenous plant species have been detected within Alligator Flag Preserve (Table 8), accounting for 913% of the plant species recorded there. AllOf the eight exotic species, six are listed by FLEPPC (eightfive Category I and sevenone Category II). FLEPPC defines Category I plants as those that alter native plant communities by displacing native species, change community structures or ecological functions, or hybridize with natives. Category II plants have increased in abundance or frequency but have not yet altered Florida plant communities to the extent shown by Category I species. These definitions do not rely on the economic severity or geographic range of the problem, but rather on the documented ecological damage caused by these plants (FLEPPC 2013). Table 8: Invasive Plant Species at Alligator Flag Preserve Scientific Name Common Names FLEPPC Category Acacia auriculiformis Earleaf acacia I Casuarina sp. Australian pine I Cupaniopsis anacardioides Carrotwood I Melaleuca quinquenervia Punk tree, Melaleuca, Paper bark I Schinus terebinthifolius Brazilian pepper I Urena lobata Caesarweed II Emilia fosbergii Florida tassleflower n/a Spermacoce verticillata Shrubby false buttonweed n/a Table 8: Invasive Plant Species at Alligator Flag Preserve Scientific Name Common Names FLEPPC Category Acacia auriculiformis Earleaf acacia I Abrus precatorius Rosary pea I *Casuarina equestifolia Australian Pine I *Cupaniopsis anacardioides Carrotwood I Leucaena leucocephala White leadtree II Melaleuca quinquenervia Punk tree, Melaleuca, Paper bark I Macroptilium lathyroides Wild bushbean II Momordica charantia Balsam pear II Panicum repens Torpedo grass I Richardia grandiflora Largeflower Mexican clover II Schinus terebinthifolia Brazilian pepper I Solanum viarum Tropical soda apple I Spermacoce verticillata Shrubby false buttonweed II Conservation Collier Program 29 Syagrus romanzoffiana Queen palm II Urena lobata Caesar’s weed I * no longer exist on the preserve As of the acquisition of the Alligator Flag Preserve by the Conservation Collier program on July 28, 2006, the most problematic exotic, invasive plant species were melaleuca (Melaleuca quinquenervia), Australian pine and earleaf acacia (Acacia auriculiformis). A Collier County approved contractor, started the initial treatment of these exotics on April 28, 2008. The following paragraphs outline the methods they used to chemically treat these exotics dependent on the species and location of treatment. For the 75-foot perimeter buffer (3.17 acres; Figure 8), all woody invasive species, primarily melaleuca and earleaf acacia, were manually cut and the stem removed from the buffer. The cut stems were stacked within the interior of the property, but outside of the perimeter buffer. The remaining stumps were treated with a dye-laced herbicide. All saplings (<3 feet tall) and herbaceous, invasive species were killed-in-place (KIP) with a dye-laced herbicide. In the interior of the property (14.21 acres; Figure 8), field crews used the frill-and-girdle (KIP) method for large trees [>4 inches DBH (diameter at breast height)] and small trees (<4 inches DBH) were cut and stacked within the interior of the property. The material was stacked in a “log cabin” formation with each “cabin” being spaced at least 50-75 feet apart. All trees frilled-and- girdled and any remaining stumps were treated with a dye-laced herbicide. All saplings (<3 feet tall) and herbaceous invasive species were killed-in-place with a dye-laced herbicide. The smaller Australian pine trees in the southeast corner (1.08 acres; Figure 8) were cut by chainsaw. All remaining stumps were treated with a dye-laced herbicide. The larger Australian pine trees remaining on site are located on the extreme eastern edge of the Australian pine area. These trees were very large (>4 inches DBH) and were successfully removed in early 2009. This species has been completely eradicated from the preserve. Conservation Collier Program 30 Figure 8: Initial Exotic Vegetation Treatment Map for the Alligator Flag Preserve 2.6.2 Invasive and Problem Animal Species Although Florida does not have an official exotic, invasive animal species list, at least 400 exotic fish and wildlife animal species have been reported in Florida, and approximately 125 species are established. Three non-indigenous, invasive animal species have been documented on the preserve: red imported fire ants (Solenopsis invicta) and brown anoles (Anolis sagrei). Coyotes have also been documented on the preserve. Based on the natural communities found within the preserve, proximity to residential areas and geographic location, several more species (native and non- native) have the potential to impact the Alligator Flag Preserve to varying degrees. Brief descriptions of documented and undocumented but potentially problematic species are provided in the following paragraphs. Red imported fire ant (Solenopsis invicta): documented within the Alligator Flag Preserve These social insects were introduced into the U.S. from Brazil into either Mobile, Alabama or Pensacola, Florida between 1933 and 1945 (Collins & Scheffrahn 2005) and have been detected in the Alligator Flag Preserve. Red imported fire ants (RIFA) have been documented to cause harm to humans and wildlife as well as economic harm (Stimac & Alves 1994; Collins & Scheffrahn 2005; Willcox & Giuliano, 2006). RIFAs are omnivorous, but they prefer insects as their primary food source (Willcox & Giuliano 2006). RIFAs have a number of impacts on wildlife; in many areas, they have eliminated native ant populations through competition and predation and have eradicated food sources utilized by some wildlife species. Ground-nesting wildlife is especially susceptible to RIFAs. Within the Alligator Flag Preserve, RIFAs have the potential to affect ground-nesting birds; small mammals; reptiles, native lizard and snake species, and native invertebrates (Willcox & Giuliano 2006). Additionally, members of the public that come into contact with RIFAs may be harmed if stung. Many people have anaphylactic reactions to the toxins released from RIFA stings. Solenopsis invicta, an invasive, non-indigenous arthropod documented within the Milano Preserve. Photo courtesy of the USDA. Conservation Collier Program 31 Brown Anole (Anolis sagrei): documented within the Alligator Flag Preserve Also known as the Cuban anole, the brown anole is native to Cuba, the Bahamas, and neighboring islands (Schwartz & Henderson 1991). Like other anoles from the islands, this species is a small, tropical, diurnal, arboreal, territorial, and insectivorous lizard (Campbell 2001). The brown anole was first documented in the Florida Keys in the late 1800s (Lee 1985) and has since spread throughout Florida, into Georgia and into two other southeastern states (Campbell 1996). The brown anole is a habitat generalist and generally prefers the fairly open areas of disturbed sites. It feeds on a wide variety of insects, amphipods, and isopods. Brown anoles also prey on other small vertebrates including the hatchlings of the native green anole (A. carolinensiis; Campbell 2000). Campbell (2000) showed that, in the absence of the exotic brown anoles, native green anoles occupy perches from ground to the canopy of vegetation. However, in the presence of the exotic anole, native anoles move higher in trees, occupying only the trunk and crown of trees. Dietary overlap is high between both species, but the overall affects of the brown anole on the green anole are still undetermined. Coyote (Canis latrans): undocumented within the Alligator Flag Preserve Coyotes were introduced in very small numbers to Florida during the 1920’s for sport hunting with domestic dogs. This introduction did not lead to the establishment of coyote populations in Florida. Concurrently, these canids expanded their range eastward across the United States and Canada as a result of nonspecific needs in habitat and food, decreased competition from other predators, large litter sizes and anthropogenic changes to the landscape. Since many species naturally expand or change their home ranges in response to climate and resource availability, the coyote may be considered native to Florida. This crepuscular (active mostly at dawn and dusk) species is elusive and may travel individually or in groups of two or three (Coates et al. 1998). Coyotes commonly enlarge burrows made by other animals such as armadillos or gopher tortoises to use as dens or use dense vegetation for cover. Coyotes may have a negative influence on indigenous wildlife as direct predators or as potential competitors with predators that may occur at the preserve such as foxes (Urocyon cinereoargenteus) or bobcats (Lynx rufus floridanus); however, this species may prove beneficial in controlling potential problem species such as feral cats. Anolis sagrei, an invasive, exotic reptile documented in the Alligator Flag Preserve. Photo courtesy of the USGS. Anolis carolinensiis, an indigenous reptile documented in the Alligator Flag Preserve. Photo courtesy of the USGS. Coyote photo from a wildlife camera- Alligator Flag Preserve 2015 Conservation Collier Program 32 Cuban tree frog (Osteopilus septentrionalis): undocumented within the Alligator Flag Preserve Like the Cuban anole, the Cuban tree frog is native to Cuba, the Bahamas, and neighboring islands. The first Cuban tree frogs probably arrived in the Florida Keys as stowaways in shipping crates originating from the Caribbean in the 1920’s. Today, they have established breeding populations as far north as Cedar Key on Florida's Gulf Coast, Jacksonville on the Atlantic Coast, and Gainesville in north-central Florida. These hylids are the largest tree frog found in Florida and because of their ability to invade natural areas and prey on native invertebrates and small vertebrates (including native tree frogs) they are considered an invasive species. Additionally, the tadpoles of this species inhibit the growth and development of the tadpoles of the native southern toad (Bufo terrestris) and green tree frog (Hyla cinerea). Cuban tree frogs thrive in residential and natural areas such as pine forests, hardwood hammocks, and swamps. In residential settings, they are most commonly found on and around homes and buildings, and in gardens and landscape plants. They are known to get into transformer boxes and electrical switches causing power outages (Johnson 2007). Due to the natural communities that are found within the Alligator Flag Preserve and its proximity to residential areas, this species has the potential of occurring in the preserve. Giant Marine Toad or Cane Toad (Bufo marinus): undocumented within the Preserve The cane toad is a tropical species native to the Amazon basin in South America, and its range extends through Central America to extreme southern Texas along the Rio Grande River. They are used as a control agent for insects that damage sugarcane and consequently, are one of the most introduced amphibian species in the world. In 1936, an attempt was made to introduce this species into Palm Beach County, FL. This attempt failed as did two subsequent efforts. Ironically, in 1955, an accidental release by an importer at the Miami International Airport in Miami-Dade County, FL proved successful. They have since been deemed an invasive species in Florida and are currently found in urban areas of south and central Florida, and are rapidly expanding northward (Brandt & Mazziotti 2005). Many of this species’ characteristics enable it to do well in south Florida. Beetles, bees, ants, winged termites, crickets and bugs are a large part of the diet of the adult marine toad. Additionally, they consume arthropods, mollusks, small vertebrates, plant matter, pet food, carrion, household scraps, marine snails, smaller toads and native frogs, small snakes, and even small mammals. Marine toads are prolific breeders and females can lay tens of thousands of eggs in a single breeding season. They prefer forested areas with semi-permanent water nearby Osteopilus septentrionalis, an invasive, exotic amphibian that has the potential to occur at the Alligator Flag Preserve. Photo courtesy of the USGS. Bufo marinus, an invasive, exotic amphibian that has the potential to occur at the Alligator Flag Preserve. Photo courtesy of the USGS. Bufo terrestris, a native toad that looks similar to the exotic, invasive cane toad. Photo courtesy of the USGS. Conservation Collier Program 33 (Churchill 2003). The cane toad looks very similar to the native, southern toad, but there are some distinct differences. The most obvious difference is adult body size (length of body not counting the legs). Adult marine toads can reach lengths of 6 -9 inches while the native southern toads only reach a length of 3.6 inches. Like other true toads, both possess poisonous, parotid glands. The parotid glands of the cane toad are angled downward behind their head to their shoulders. The southern toad has a kidney-shaped parotid gland behind each eye positioned close to the spine. The southern toad also possesses cranial crests that start between the eyes and often end in big knobs. While the parotid glands of all toads contain bufotoxins (poisonous, milky fluids exuded as a defense mechanism), the chemicals released by the exotic, cane toad are much more harmful to wildlife, pets and people (Brandt & Mazziotti 2005). Due to the natural communities that are found within the Alligator Flag Preserve and its proximity to residential areas, this species has the potential of occurring within the preserve. Adjoining residents of the preserve should be encouraged to keep pet food and water containers indoors or empty at night. Feral domestic cat (Felis catus): undocumented within the Alligator Flag Preserve Domestic cats originated from an ancestral wild species, the European and African wildcat (Felis silvestris). Humans facilitated the global distribution of cats due to their highly efficient predatory skills. Egyptians took cats with them on shipping vessels to keep rodent populations down, and they likely introduced domestic cats to Europe. Subsequently the expansion of the Roman Empire and European missionary missions facilitated the spread of domestic cats into Asia and beyond (Masterson 2007). Today, the impact of feral cats on wildlife is difficult to quantify; however, literature (FFWCC 2001; Karim 2007; Masterson 2007) strongly indicates that they are a significant factor in the mortality of small mammals, birds (including migratory birds), reptiles, and amphibians in Florida. Because free-ranging cats often receive food from humans, they may reach abnormally high numbers. An increase in the population of feral cats may lead to increased predation rates on native wildlife. While no cats have yet been observed on the Alligator Flag Preserve, there exists a high probability of their future presence on the preserve due to the proximity of Milano to human residential areas. Adjoining residents of the preserve should be encouraged to keep their cats indoors and staff should monitor the preserve for the presence of feral cats. 3.0 Previous and Current Use of the Preserve; Adjacent Land Uses 3.1 Previous Use of the Preserve and Adjoining Lands Aerial photographs taken in 1973 (Figure 9) and 1996 (Figure 10) accompanied by more recent visits to the site show that development has never occurred on the site. Digital images were downloaded from the Florida Department of Transportation’s Aerial Photo Look Up System (2008) and georeferenced in ArcMap 9.2 by Conservation Collier Staff. Conservation Collier Program 34 Figure 9: Historical Aerial Photograph from 1973 of the Alligator Flag Preserve and Adjoining Lands Conservation Collier Program 35 Figure 10: Historical Aerial Photograph from 1996 of the Alligator Flag Preserve and Adjoining Lands 3.2 Current Land Uses Conservation, restoration and natural resource-based recreation are the designated uses of this preserve. Management activities allowed include those necessary to preserve, restore, secure and maintain this environmentally sensitive land for the benefit of present and future generations. Public use of the site must be consistent with these management goals and will be discussed in section 4.4 of this document. The Olde Cypress Planned Unit Development (PUD) adjoins the Alligator Flag Preserve to the west, north and east. This PUD contains residential, commercial and conservation lands; specifically, a cypress slough under preservation is located to the northwest, north and northeast, the Fairway Preserve Condominiums are to the east and commercial lands and a drainage tract for the PUD are to the west of the Alligator Flag Preserve. Areas not contained within the PUD include a greenway trail, the Cocohatchee Canal and Immokalee Road (from north to south) to the south of the preserve and Laurel Oaks Elementary School and Gulf Coast High School on the south side of Immokalee Road (Figure 11). Conservation Collier Program 36 Figure 11: Areas Adjacent to the Alligator Flag Preserve 3.3 Cultural, Historical and Archeological Resource Protection The Alligator Flag Preserve is not within an area of historical and archaeological probability, and no historical or archaeological sites appear to be present on the property. The County will notify the Division of Historical Resources immediately if evidence is found to suggest any archaeological or historic resources are discovered. If such resources are identified on -site, staff shall cordon off the area, and a professional survey and assessment shall be instituted. The archaeologist shall prepare a report outlining results of the assessments and issue recommendations to County staff about management of any sites discovered, per provisions of the Land Development Code Section 2.2.25. This report shall be sent to the Division of Historical Resources. The County shall cooperate fully with direction from the Division of Historical Resources on the protection and management of archaeological and historical resources. The management of these resources will comply with the provisions of Chapter 267, Florida Statutes, specifically Sections 267.061 2 (a) and (b). 3.4 Major Accomplishments during Previous Years Since the acquisition of the Alligator Flag Preserve in July 2006, major accomplishments have been achieved (Table 9). Conservation Collier staff explored options of funding exotic removal through grants from the Department of Environmental Protection before contracting this service out. The invasive, exotic removal project was implemented throughout the site while staff Conservation Collier Program 37 concurrently established photo-monitoring points to better aid in the long-term management of the preserve. Subsequently, the Collier County Sheriff’s work weekenders removed large amounts of debris. Given the discrepancy between the 1995 and 2001 FLUCCS digital layers (as they pertain to the Alligator Flag Preserve) and the removal of exotic vegetation annually since the acquisition of the property in July 2006, staff created a new digital layer showing the location and extent of the native plant communities currently found on the preserve. Table 9: Major Accomplishments since the Acquisition of the Alligator Flag Preserve Accomplishment Year(s) Established photo monitoring points 2008 Removed and treated the invasive, exotic plants species on the Preserve 2008 Sherriff Dept. Weekend work crews removed large amounts of miscellaneous debris from site 2008 Created an accurate FLUCCS Map of the Preserve 2008 Updated Plant Survey 2009 Worked with Dunkin Donuts to install bear proof dumpster 2012 Updated Plant Survey 2020 4.0 Future Use of the Alligator Flag Preserve including Management Issues, Goals and Objectives This section describes the main management issues, goals, and objectives for the Alligator Flag Preserve as well as the overall management framework. Central to the management of the Preserve is the mission of the Conservation Collier Program, and the goals and objectives set forth in this management plan. 4.1 Management Plan Framework Each property purchased by Conservation Collier shall have its own management plan. At the time the Alligator Flag Preserve as purchased, the Conservation Collier Ordinance required that an “Interim” Management Plan be developed within 60 days of closing. Interim plans include basic items such as removal of invasive exotics and trash, establishing site security, developing management partnerships and planning for public access. The interim plan for this site was officially approved in October 2006. The ordinance then requires a “Final” ten-year management plan be developed within two years; the first draft of this management plan was submitted to the Lands Evaluation and Management Subcommittee in October 2008 and subsequently to the CCLAAC and Collier County BCC. Once approved, the property management plan must be reviewed every five years. This is the 10 year update to the plan. Final management plans, however, are considered living documents and can be updated at any time. All management plans must be approved by both the CCLAAC and the Collier County BCC. 4.1.1 Preserve Manager: Contact Information The site manager for Alligator Flag Preserve will be a designated Collier County Environmental Specialist who may be contacted through electronic mail: ConservationCollier@CollierCountyFL.gov.net. Conservation Collier Program 38 4.2 Planned Uses and Assessment of their Impacts Future planned use will be consistent with the primary goals of conservation, preservation, restoration and maintenance of the resource. Details of planned uses for the Alligator Flag Preserve and an assessment of their potential impacts are provided in the following sections. 4.2.1 Identification of Public Uses Consistent with Preservation, Enhancement, Restoration, Conservation and Maintenance of the Resources The Conservation Collier Ordinance 2002-63 constrains the use of this property to “primary objectives of managing and preserving natural resource values and providing appropriate natural resource-based recreational & educational opportunities.” Natural resource-based recreation shall mean all forms of uses, which are consistent with the goals of this program, and are compatible with the specific parcel. Such uses may include, but are not limited to hiking, nature photography, bird watching, kayaking, canoeing, swimming, hunting and fishing (Ord. No. 02-63, as amended§ 5, 12-3-02). Additionally, no dumping, use of unauthorized vehicles, or removal or destruction of natural or historical/archaeological resources will be permitted within the preserve. The goal is to allow limited, non-destructive public access to native plant communities and animal species. The preserve rules are those identified in Collier County Ordinance 2011-38 (available from www.municode.com), as amended. The following are consistent uses for this particular site: hiking, nature photography and bird watching. Inconsistent uses include swimming, kayaking / canoeing, fishing, hunting and off road vehicle use (ORV). In addition, there are no existing easements, concessions, or leases at the Alligator Flag Preserve. In accordance with the management goals of the preserve, no future easements, concessions, or leases are appropriate in association with this site, other than conservation related easements. 4.3 Desired Future Conditions This section includes a description of the proposed future conditions for the site’s natural areas. Management techniques to achieve these conditions are outlined in section 4.4. After managers complete recommended management actions, Alligator Flag Preserve should consist of cypress-pine-cabbage palm, cypress and pine flatwoods; these communities should have a similar structure and composition to those that existed before non-indigenous people settled the region and before the exclusion of fire. A measure of success will be that the site will be vegetated with appropriate native flora that will provide suitable cover for a variety of wildlife species. 4.4 Goals for the 10 year period 2008-2018 A set of goals and objectives for Alligator Flag Preserve were developed in conjunction with the drafting of this Management Plan. The goals and objectives in this plan are tailored specifically for Alligator Flag Preserve based on the purposes for which the lands were acquired, the condition of the resources present, and the management issues for the property. On-site managers should be familiar with this entire Management Plan. Goals and objectives from the interim management plan for the Alligator Flag Preserve were reviewed to determine whether they should be included in this plan. The goals and objectives presented here reflect programmatic goals and ideas of Conservation Collier personnel in charge of managing and protecting the area. These goals shall not be modified, but specific application of management techniques may take into consideration Conservation Collier Program 39 input by user groups and other stakeholders from outside the program, accommodating user needs and desires where practicable and where overarching management goals are not violated. Management issues are discussed below in separate sections. Within each section, approaches for dealing with these issues are described. The ability to implement the specific goals and objectives identified in this plan is dependent upon the availability of funding sources. The following goals have been identified for Alligator Flag Preserve: Goal 1: Maintain high quality habitat with limited disturbance for the benefit of native flora and fauna Eliminate or significantly reduce human impacts to indigenous flora and fauna Goal 2: Continue plant and animal Develop a baseline monitoring program report Goal 3: Remove or control populations of invasive, exotic or problematic flora and fauna to restore and maintain natural habitats Goal 4: Determine if prescribed fire and/or mechanical treatments are feasible to decrease woody invasion resulting from past fire exclusion if so proceed Goal 5: Restore native vegetation Goal 6: Monitor Facilitate appropriate public use Goal 7: Facilitate uses of the site for educational purposes Goal 8: Provide a plan for security and disaster preparedness GOAL 1: Maintain High Quality Habitat with Limited Disturbance for the Benefit of Native Flora and Fauna ELIMINATE OR SIGNIFICANTLY REDUCE HUMAN IMPACTS TO INDIGENOUS FLORA AND FAUNA Action Item 1.1 Install a fence and access gate around the perimeter of the Alligator Flag Preserve if needed. Presently, staff does not recommend a fence around the property but if trespassing, chronic dumping or other security issues arise, a field fence, four feet in height, will be installed along the boundaries of the property where these issues occur. If this fence is installed, one or more gate(s), 12 feet in width and four feet in height will be installed (if needed) along the fence-line to allow access to the Alligator Flag Preserve by authorized County staff and the fire department. Action Item 1.2 Install signs encouraging people to stay on public access trails situated on the preserve. Signs are present at the trailhead off of the bike trail in the SE corner of the preserve. Action Item 1.3 Identify locations of rare and listed native plant species. The location of these species will be generally identified to allow staff to monitor them. Public trails will be constructed to avoid areas where rare and listed species exist. Conservation Collier Program 40 Action Item 1.4 Enforce regulations prohibiting trash in or near the preserve. Staff will monitor the trails on a regular basis and if excessive dumping or littering start to occur, enforcement actions will be sought through the County Sheriff’s Department. Staff will also contact Gulf Coast High School across the street from the preserve to see if the Biology/ Environmental department might want to assist with keeping the trails clean. In March 2020, trash and debris were found in hidden areas of the preserve. Items included stacks of pallets, tires, cardboard, lawn chairs etc. A contractor was hired in April 2020 to remove these items. They might have been brought in by homeless people. The preserve will continue to be monitored and Law Enforcement will be contacted if it continues. Action Item 1.5 Identify actual and potential locations of resident animal life and take steps such as locating visitor amenities away from animal nesting sites. Action Item 1.6 Avoid non-target damage to native plants and animals, especially rare species, during invasive, exotic plant treatments. If the use of herbicides is appropriate during the removal of invasive, exotic plant species, decisions on the types of herbicides utilized will be made on the best information available at the time of exotic removal. Staff has prohibited the use of herbicides containing Imazapyr (e.g., Arsenal) due to reports that these herbicides have potentially caused a great deal of non-target damage throughout the state. Licensed County or State contractors have been (and will be) monitored closely to ensure the proper herbicide applications are being utilized while treating the site. In addition, close attention will be paid to identify listed epiphytes (Table 7) that may be attached to invasive trees being cut down or removed. Plants of these species will be relocated prior to removal. Special attention will be given to avoid damage to native species in the vicinity of exotic removal activities. Hand pulling of exotic seedlings will be done when possible. Action Item 1.7 Note and research all site development occurring adjacent to Alligator Flag Preserve to determine that the proper site development permits have been obtained and that the site development complies with the permits. Activities on adjacent lands may have an impact on the indigenous plant and animal life on the Alligator Flag Preserve. As such, all existing local, state, and federal regulations should be strictly followed and enforced during any site development adjacent to the preserve. It shall be the responsibility of the developer to establish erosion control measures and vegetation protection measures (i.e., protective fencing or barriers). If any site developer working in areas adjacent to the preserve does not take the necessary control measures, construction shall be immediately halted until control measures are put into place and mitigation and/or remediation will be the sole responsibility of the developer. GOAL 2: CONTINUE DEVELOP A BASELINE PLANT AND ANIMAL MONITORING PROGRAMREPORT Action Item 2.1 Establish a long-term biological monitoring program and conduct additional wildlife surveys. Conservation Collier Program 41 Long-term management of the preserve should be based on biological data. Changes following baseline conditions should be assessed as negative or positive, and management strategies changed appropriately. This section discusses information needs and long-term monitoring needs. Conservation Collier staff has conducted a floristic inventory of the Alligator Flag Preserve; these findings will comprise the baseline floristic data on which future actions will be based. The site should be inspected by Conservation Collier Staff at least twice a year and thoroughly inventoried at regular intervals (ca. 5-10 years) to detect new invasions (by natives or exotics) and extinctions. Areas undergoing extreme restoration should be assessed more frequently. While some wildlife data has been collected, additional baseline data should be collected, especially on invertebrates, small mammals, reptiles, and amphibians. The site manager may contract this work out or enlist the assistance of local educators to coordinate student research projects. Wildlife sampling, like plant sampling, on non-listed species only, should take place at regular intervals (ca. 5-10 years) to detect long-term trends. Figure 11: Photo Point Locations within the Alligator Flag Preserve Currently, six (6) photo points have been established throughout the preserve (Figure 11). Locations of photo points have been recorded with a GPS and all photographs taken at these locations have been taken at a standard height and angle of view. During photo documentations, one photo is taken in each of the cardinal directions (north, east, south and west) and a 360-degree panoramic photo is taken. These photos will help to monitor exotic removal and native plant recruitment over time. If necessary, more photo points will be established to aid in management decision activities. Future photo points will include photos taken with a vegetation profile board to aid in the Photo points aid in the determination of what (if any) changes occur over time. GOAL 3: REMOVE OR CONTROL POPULATIONS OF INVASIVE, EXOTIC OR PROBLEMATIC FLORA AND FAUNA TO RESTORE AND MAINTAIN NATURAL HABITATS Action Item 3.1 Acquire services of licensed and qualified contractor(s) for the removal of invasive, exotic or problematic plant species. The preserve is now in maintenance state and new or small infestations of invasive exotic plants continue to be treated once per year by contractors. The following (Table 10) describes Conservation Collier Program 42 recommended controls (Langeland & Stocker 2001) of the Category I, invasive, exotic plant species recorded to date on the Alligator Flag Preserve. These recommended control methods may be altered by site managers dependent on new information and products available on the control of these species. Table 10: Invasive, Exotic Plant Species Control Plan for the Alligator Flag Preserve FLEPPC Category I species a Scientific Name Common Name(s) Recommended Control(s)b Acacia auriculiformis earleaf acacia Hand pull seedlings or basal bark application of 10% Garlon 4 or cut- stump treatment with 50% Garlon 3A. Abrus precatorius Rosary pea Cut stem or basal bark and treat with 10% Garlon 4. Site must be revisited frequently to pull seedlings. Casuarina sp. Australian pine Basal bark treatment with 10% Garlon 4 is very effective, as is a cut- stump treatment with 50% Garlon 3A or 10% Garlon 4. When basal bark treatment is used on trees greater than 1 foot in diameter it may be necessary to slough off loose bark in the application area to prevent the bark from trapping the herbicide. Broadcut or 4-6 lb Velpar ULW may be used when appropriate. Cupaniopsis anacardioides carrotwood Hand pull seedlings or basal bark application of 100% Pathfinder II, or 10%-20% Garlon 4 diluted with oil; or cut stump application of 10% Garlon 3A, 100% Brush-B-Gon, 100% Roundup Pro, 100% Rodeo, or equivalent glyphosate containing product, or 100% Pathfinder II. Melaleuca quinquenervia melaleuca, punk tree, paper bark For seedlings and saplings: (1) hand pull, being sure not to break plant off of root system and remove or place in piles to help reduce the chance that they will re-root or; (2) Treat with foliar, low volume spot application of 5% Rodeo. For mature trees: (1) Fell large trees with chain saw leaving a level surface, or fell small trees with machete and treat with triclopyr or glyphosate products according to frill and girdle directions on SLN. Use aquatic versions where standing water is present. Monitor for resprouting and retreat as necessary. (3) Mature trees are very difficult to control with foliar applications. Schinus terebinthifolius Brazilian pepper Hand pull seedlings or cut-stump treatment with 50% Garlon 3A, 10% Garlon 4 or a basal bark application of 10% Garlon 4. Foliar application of Garlon 4, Garlon 3A, Roundup Pro, Roundup Super Concentrate, or Rodeo, according label directions may be used where appropriate. Glyphosate products are less effective when used alone in spring and early summer. Use Rodeo where plants are growing in aquatic sites. Panicum repens Torpedo grass Foliar application of 0.75%-1.5% Rodeo and surfactant solution. Re-apply as necessary when plants re-grow to within 4-6 inches in height; or foliar application of 0.5% spot treatment Solanum viarum Tropical soda apple Foliar application of 1% Garlon 4 or 3% Roundup. ACTION ITEM 3.2 Acquire services of licensed or qualified contractor(s) for the removal of invasive, exotic or problematic animal species. To date, two (2) introduced animal species have been documented on the Alligator Flag Preserve, the RIFA and the brown anole. It is doubtful that the total eradication of these species can be achieved. However, staff and/or contractors should take measures to remove RIFA populations close to or on public access trails. If feral cat colonies are found near the preserve, the elements that sustain the undesirable population(s) should be identified and efforts made to ask property owners to eliminate them (i.e., refuse bins, dumpsters, and supplementary feeding by humans). If any feral cats remain, they will be trapped and taken to Collier County Domestic Animal Services. Conservation Collier Program 43 ACTION ITEM 3.2 Coordinate the control of invasive plant and animal populations with the Olde Cypress PUD preserve management entity. Currently, the Olde Cypress preserve maintains their exotic plants. If this changes in the future, staff will contact them to coordinate management activities. GOAL 4: UTILIZE PRESCRIBED FIRE AND/OR MECHANICAL TREATMENTS TO DECREASE WOODY INVASION RESULTING FROM PAST FIRE EXCLUSION. Action Item 4.1 Develop a prescribed fire or mechanical treatment plan to mimic natural fires within the Preserve. Much of Collier County is comprised of plants that are dependent on fire to maintain species composition and diversity. These species are the same ones that are prone to lightning strike wildfires, and the controlled reduction of those fuels will prevent catastrophic wildfire damage. Prescribed fires: reduce fuel loads and consequently decrease the threat of wildfires; create open areas for wildlife to travel within; stimulate food and seed production; recycle nutrients; alter the composition and density of forested areas; and aid in the control of invasive plant species. The structure and composition of the mesic pine flatwood community is dependent on periodic fires. Fire probably occurred every 1 to 8 years during pre-Columbian times. A majority of the flora and fauna found within this community are adapted to periodic fires; several species depend on fire for their continued existence. Without relatively frequent fires, mesic pine flatwoods succeed into hardwood-dominated forests whose closed canopy can essentially eliminate herbaceous groundcover and shrubs. Additionally, the dense layer of litter that accumulates on unburned sites can eliminate the reproduction of pine trees that require a mineral soil substrate for proper germination (FFWCC 2002). Fire is the ideal ecological tool for achieving a sustainable mesic pine flatwood community. However, due to the proximity of the Alligator Flag Preserve to Immokalee Road, residential and commercial areas and the size of the parcel, alternate manual or mechanical treatments will be investigated in lieu of managing the lands through the use of fire. Action Item 4.2 If fire is deemed appropriate, delineate fire management and rescue access routes, and provide this information to the police department and emergency services. If fire is deemed an appropriate management tool on the Alligator Flag Preserve, the fire plan and access routes to and within the preserve will be provided to the police department and emergency services. GOAL 5: RESTORE NATIVE VEGETATION Action Item 5.1 Maintain a revised GIS map and description of FNAI natural communities and disturbed areas on the property. Maintaining updated maps will help to guide restoration efforts. Action Item 5.2 Plant native plant species in their appropriate habitats Conservation Collier Program 44 Periods following exotic removal and prescribed fire (or mechanical treatment) are essential to the recruitment of native plants. If native plant recruitment is not sufficient from the surrounding, intact seed source, efforts will be made to plant indigenous flora in appropriate habitats. Natural area restoration of Alligator Flag Preserve should include only site-specific native plant material that has been determined to be non-problematic at the site and whenever possible, site-specific seed sources should be utilized. In addition, hardwoods that may invade the natural areas (mesic pine flatwood area) should not be planted. GOAL 6: MONITOR DEVELOP A PLAN FOR PUBLIC USE Action Item 6.1 MaintainDevelop access and required facilities for intended public uses A parking lot will not be constructed on site due to the amount of wetlands present and the lack of vehicular access. The greenway trail just south of the property (north of the Cocohatchee Canal and Immokalee Road) will serve as the path along which the public may gain access to the southern portion of the preserve on foot or by bicycle. Conservation Collier staff has developed a conceptual site plan (Figure 12) incorporating a raised boardwalk and a seasonal trail. The planned trail system wouldill be approximately 1170 linear feet (LF) long and the materials used will be based on funding sources available. The following paragraphs describe the components of the trail system and the ideal lengths (option one) of each section. Option One ▪ A raised boardwalk may be considered if funding allows. Conceptually measuring approximately 500 feet in length, if built it shall adhere to guidelines and standards set forth by the Americans with Disabilities Act (ADA). If permitting for the boardwalk goes forward, a review of ADA compliance should be done by the County. The elevation of the boardwalk would allow for fluctuation of water levels and the movement of small animals. The entrance of the boardwalk would be located approximately 370 feet east of Preserve Lane. As depicted in the conceptual site plan, the entrance of the boardwalk would feature an interpretive sign. This sign would provide general information about Conservation Collier and the characteristics of the Alligator Flag Preserve. The southern portion of the walkway would be installed along the transition zone between the cypress-pine-cabbage palm and pine flatwoods communities; this placement along the ecotone will theoretically allow visitors the best opportunity to view the plants and animals of both communities. An interpretive sign would be placed along this portion of the boardwalk to give specific information about the plant communities and associated animals that may be seen form this portion of the boardwalk. The walkway would then continue northward through the cypress-pine-cabbage palm community and end at a platform. The route of the boardwalk was approximated from a 2008 aerial image to take advantage of areas where impacts to the community would be minimized. An engineering firm would be contracted to plan the design of the boardwalk and would be requested to do so in the least impactful way possible. The consulting, planning and permitting would be very expensive as well as the costs to build a boardwalk. This process will also be very time consuming. It is estimated that at least a year will be needed to complete the planning and permitting process. Grants will be applied for in the lag time to assist in the costs associated with this option. ▪ The optional seasonal walking trail measuring approximately 520 feet in length would be installed dependent on the costs associated with the project and the status Conservation Collier Program 45 of the budget after the construction of the boardwalk. This trail (closed to public access during times of high water) would begin at the platform and allow visitors to access the cypress area of the preserve. The route of the trail was approximated from a 2008 aerial image to take advantage of areas where impacts to the plant community would be minimized. The northern portion of this walking trail would take advantage of an existing trail running northwest to southeast on the property. As depicted in the conceptual site plan, a directional sign and trail markers will be strategically placed to help visitors stay on this trail. Additionally, if funding allows, an interpretive sign will be placed near the end of this trail. ▪ Platform and associated components: As depicted in the conceptual site plan, the platform would be located at the terminus of the boardwalk. The platform would be ADA compliant and include a bench and interpretive sign. It would be accessible from the south via the proposed boardwalk and would allow visitors access to the seasonal walking trail via a gate and stairs. The gate would be locked during times of high water. Option Two ▪ If a boardwalk proves to be cost prohibitive (no grant funding available), a seasonal walking trail only may be provided. The current path of this trail would mimic the entire trail system is illustrated in Figure 12. Plant signage can be installed as funding allows As the name suggests, this trail would only be open to the public during the dry season. Conservation Collier Program 46 Figure 12: Alligator Flag Preserve Conceptual Master Plan Conservation Collier Program 47 GOAL 7: FACILITATE USES OF THE SITE FOR EDUCATIONAL PURPOSES Actions Item 7.1 Develop interpretive signage to educate preserve visitors. Once a trail system is complete, site specific signage will be developed to educate visitors on plant identification and general ecosystem information, as funding allows. A large sign with a map of the preserve will be installed at the boardwalk or trail entrance and smaller, more site specific interpretive signs, may be placed along the boardwalk or seasonal trail. Action Item 7.2 Provide preserve brochures in rainproof box on site. A brochure outlining the native plant communities and wildlife present at the preserve wasill be created by County staff and are kept in a rainproof boxes near the preserve entrance. The preserve manager will inspect these boxes monthly and refill as necessary. GOAL 8: PROVIDE A PLAN FOR SECURITY AND DISASTER PREPAREDNESS Action Item 8.1 Discourage any visitation to the park at night. A sign designating park hours as 8:00 am to dusk has been installed at the entrance to the preserve and adjacent landowners will be given an emergency phone number if they detect human activity on the preserve after hours. If problems arise, the Collier County Sheriff’s Office will be contacted to patrol the area and site on a routine basis. Action Item 8.2 Enforce regulations prohibiting trash and landscape debris dumping in or near the preserve. Currently, there is no vehicular access. and dumping is not a problem. Monthly inspections will determine if dumping becomes a problem. Staff will work with the Collier County Sheriff’s Office to address dumping if it becomes a problem. Action Item 8.3 Survey trees along the trail and the perimeter of the property annually for damage Staff will utilize the services of a certified arborist to determine diseased, weak, or damaged trees/limbs surrounding the trails that should be removed for safety reasons and prior to hurricane season. This activity is intended to reduce the risk of visitor injury. Action Item 8.4 Visit preserve within 48 hours after a storm event to assess damage. Staff will take photos of damage and fill out appropriate Collier County Risk Management Department forms. If damage is extensive, the preserve will be closed until public safety hazards are cleared. Conservation Collier Program 48 Action Item 8.5 Promptly clear storm debris from preserve. If necessary, a Collier County emergency debris removal contractor will be contracted as soon as possible after the storm to schedule clean-up. Removal of debris and damaged or downed trees along the trail system may be needed. Downed trees and limbs that do not appear to be a public safety hazard will be cleared at the discretion of the Preserve Manager. As much hurricane debris as possible will be chipped and retained on-site – to be used as mulch for the trail. Hurricane Irma hit Collier County directly in September 10, 2017. A large amount of trees fell and others died several months after as a result. FEMA contractors came through to help remove the trees from the trail after the storm and the debris was left on site. A Collier County Contractor was also hired to remove additional hazardous dead trees months after the storm. 4.5 Establish an Operational Plan for the Alligator Flag Preserve This section provides management recommendations for operation of the Alligator Flag Preserve. It discusses maintenance and budgeting needs, the possibilities for contracting the restoration activities, coordination, and other management issues. 4.5.1 Maintenance The primary maintenance activities for the preserve will include control of dumping and littering within and around the preserve and trail. Particularly important are the security measures to keep intruders out and the signage and fencing (if installed) in good conditions. Signs that effectively convey the desired message provide an opportunity for increasing environmental education and awareness. 4.5.2 Estimated Annual Costs and Funding Sources Preliminary budget estimates for Alligator Flag Preserve include cost breakdowns associated with resource restoration and management. The funding source identified for the restoration and management activities is the Conservation Collier Program Management Trust Fund. Grants will be sought to supplement existing management funds and specifically for the costs associated with the potential construction of the boardwalk. Staff will also utilize the Collier County Sheriff’s Department weekenders program for certain labor projects and may also separately involve the County Scout programs for trail creation and enhancement. The budget in table 11 represents the actual and unmet budgetary needs for managing the lands and resources of the preserve for the next ten years. The table shows the activities planned and the initial and annual cost estimate of each activity. This budget was developed using data from Conservation Collier and other cooperating entities, and is based on actual costs for land management activities, equipment purchase and maintenance, and for development of fixed capital facilities and long range funding plans approved by the board of County Commissioners on April 8, 2014, Agenda Item 11B. The budget considers available funding and is consistent with the direction necessary to achieve the goals and objectives for Alligator Flag Preserve. 2nd DRAFT Alligator Flag Preserve Land Management Plan Conservation Collier Program 49 Table 11: Estimated Annual Land Management Budget Assumptions for Cost Estimates: The total estimated costs for the Alligator Flag Preserve from 2008 to 2018 range from $73,833 to $661,253. This range of estimated costs is based primarily on the materials used to construct the trail system. See explanations that follow. Item QTY Cost ($) 2008-09 2009-10 2010-11 2011-12 2012-13 2013-14 2014-15 2015-16 2016-17 2017-18 Total Facilities Development Boardwalk 1 0 LF - 500 LF $0 - $585,000 0$ Trails 2 520 LF - 1170 LF $650 - $4,410 $0 Entry Gates 3 1 $1,000 $0 Fence (4’ field fence) western boundary 4 1230 LF $6,273 $0 Interior interpretive signs 5 3 $500 $463 $57 $520 Plant signs 30 $10 $38 $38 Entry signage (set) 6 1 $2,250 $1,400 $1,400 Directional sign 1 $100 $0 Bench, Garbage can, Bike Rack 1 of each $1,250 $843 $843 Resource Restoration/Monitoring t.b.d. t.b.d. Establish photo points recurring n/a $0 Remove exotics 8 18.46 acres $26,000 $8,276 $1,125 $1,125 $1,350 $1,125 $1,800 $1,880 $1,962 $2,000 $46,643 Native Plant Restoration 9 t.b.d. t.b.d. Regular Maintenance Reduce Fuel Loads 10 2 $2,000 $685 $685 General Facilities Maintenance / Landscaping 11 8 $720 $900 $3,510 $2,605 $2,200 $2,200 $2,200 $2,245 $15,860 Grand Total $26,000 $8,276 $3,869 $2,025 $5,602 $3,730 $4,000 $4,080 $4,162 $4,245 $65,989 Table 11: Estimated Annual Land Management Budget (Amounts in $; see assumptions for cost estimates on next page) 2nd DRAFT Alligator Flag Preserve Land Management Plan Conservation Collier Program 50 Boardwalk will only be built if grant funding is provided. The planned trail system (Figure 12) is approximately 1170 linear feet (LF) long The ideal length of an ADA compliant, raised boardwalk would be 500 LF at $585/LF = $380,250 (rounded to $385,000). Unit price includes required materials, labor and equipment as follows. Permitting, Planning and design is estimated to cost $200,000. The actual cost of the trail system may be estimated using the following formula: [($200,000 + $585x) + $2(0.625y)] where x = the length (LF) of the raised boardwalk and y = the length (LF) of the trail. 3. Entry Gates: 1 gate at $2,000.00 each (if deemed necessary) 4. Fence: Field Fence estimated at $5.10 a foot for 1230 LF (if deemed necessary) 5. Interpretive signs: 3 interpretative signs (4'x6') at $500 each 6. Entry signage: 1 road sign indicating entrance to the preserve ($250 each) and 1 welcome sign (8'x6') estimated at $2,000 7. Bench estimated at $600; trash can estimated at $400 8. Removal of Exotics: $26,000 paid to contactor; $7,751.96 will be paid upon removal of Australian Pines; maintenance costs will be $1,850 per event- for 2009 and 2010 two events per year will take place. From 2011 on - one event will take place per year 9. Native Plant Restoration: t.b.d. 10. Reduce fuel loads: reduction of dense fuels - $2000 every 5 years if deemed necessary 11. General Maintenance: Includes mowing and landscape maintenance along the north side of the bike trail along the southern preserve boundary 2nd DRAFT Alligator Flag Preserve Land Management Plan Conservation Collier Program 51 Item QTY Cost ($)2015-16 2016-17 2017-18 2018-19 2019-20 2020-21 2021-22 2022-23 2023-24 2024-25 Total Signage and Ammenities Boardwalk*0 LF - 650 LF $0 - $585,000 0$ Interior interpretive signs 3 $57 $200 $100 $200 $100 $100 $757 Plant signs $100 $100 $100 $300 Entry signage 1 $2,250 $0 Directional signage $0 Resource Restoration/Monitoring t.b.d. Establish photo points recurring n/a $0 Exotic Treatment 18.46 acres $1,880 $1,962 $2,000 $1,350 $1,125 $1,800 $1,800 $1,800 $1,800 $1,800 $17,317 Native Plant Restoration Regular Maintenance Reduce Fuel Loads $685 $685 Trash Removal $1,220 $1,220 Landscaping $2,200 $2,200 $2,245 $3,510 $750 $1,000 $1,000 $1,000 $1,000 $1,000 $15,905 Grand Total $4,080 $4,162 $4,245 $5,602 $3,095 $3,000 $3,000 $3,000 $3,000 $3,000 $36,184 Table 11: Estimated Annual Land Management Budget 2015-2025 Alligator Flag Preserve Land Management Plan Update August 2014 Conservation Collier Program 52 4.5.3 Potential for Contracting Restoration and Management Activities by Private Vendors A significant number of Alligator Flag Preserve management operations and restoration activities can be considered for outsourcing. Restoration and management activities that can be considered for outsourcing to private entities are listed in table 12. Table 12: Potential Contracting for Restoration and Management Activities Activity Approved Conditional Rejected Prescribed fire and/ or mechanical treatment application X Minor fireline installation X Fireline, fence, and trail maintenance X Fence installation X Plant and wildlife inventory and monitoring X Listed species mapping and needs assessment X Restore/enhance encroachment and ruderal areas X Reduce exotic species X Literature development and printing X Interpretive signs development and installation X Trail and boardwalk installation X Law enforcement and patrol X Alligator Flag Preserve Land Management Plan Update August 2014 Conservation Collier Program 53 5.0 Literature Cited Abrahamson, W. G., and D. C Hartnett. 1990. Pine flatwoods and dry prairies. Pages 103-149 in R. L. Myers and J. J. Ewel editors. Ecosystems of Florida. University of Central Florida Press; Orlando, Florida. Brandt, L. A. and F. J. Mazziotti. 2005. Marine toads (Bufo marinus). University of Florida Cooperative Extension Service Document WEC11. 4pp. University of Florida, UF/IFAS Extension Digital Information Source (EDIS) Database. Available from http://edis.ifas.ufl.edu/pdffiles/UW/UW04600.pdf (accessed November 2007). Campbell K. M. 1990. Soil survey of Collier County area Florida. USDA, Natural Resources Conservation Service; Washington, D.C. Campbell, T. 2001. The brown anole. Institute for Biological Invaders: Invader of the Month. University of Tennessee, Knoxville, TN. Available from http://invasions.bio.utk.edu/invaders/sagrei.html (accessed November 2007). Campbell, T. S. 1996. Northern range expansion of the brown anole, Anolis sagrei, in Florida and Georgia. Herp. Review 27:155-157. Campbell, T. S. 2000. Analyses of the effects of an exotic lizard (Anolis sagrei) on a native lizard (Anolis carolinensis) in Florida, using islands as experimental units. Ph.D. Dissertation, University of Tennessee, Knoxville, TN. Churchill, M. 2003. Giant marine toad (Bufo marinus) - Introduced Species Summary Project. Columbia University, New York, NY. Available from http://www.columbia.edu/itc/cerc/danoff- burg/invasion_bio/inv_spp_summ/Bufo_marinus.html (accessed December 2007). Coates, S. F., M. B. Main, J. J. Mullahey, J. M. Schaefer, G. W. Tanner, M. E. Sunquist, and M. D. Fanning. 1998. The coyote (Canis latrans): Florida’s newest predator. University of Florida Cooperative Extension Service Document WEC124. 5pp. University of Florida, UF/IFAS Extension Digital Information Source (EDIS) Database. Available from http://edis.ifas.ufl.edu/pdffiles/UW/UW12700.pdf (accessed November 2007). Collins, L. and R. H. Scheffrahn. 2005. Red Imported Fire Ant, Solenopsis invicta Buren (Insecta: Hymenoptera: Formicidae: Myrmicinae). 9pp. Featured Creatures from the Entomology and Nematology Department, Florida Cooperative Extension Service Document EENY-195. Institute of Food and Agricultural Sciences, University of Florida. Available from http://edis.ifas.ufl.edu/IN352 Fairbank, P. and S. Hohner. 1995. Mapping recharge (infiltration and leakage) throughout the South Florida Water Management District. Technical publication 95-20 (DRE # 327). SFWMD, West Palm Beach, Florida. Florida Department of Transportation. 2008. Aerial Photo Look Up System Available from http://www.dot.state.fl.us/surveyingandmapping/apac.shtm (accessed October 2008). Florida Fish and Wildlife Conservation Commission (FFWCC). 2001. Impacts of feral and free-ranging domestic cats on wildlife in Florida. Tallahassee, FL. Available from http://www.floridaconservation.org/viewing/articles/cat.pdf (accessed October 2007) Florida Fish and Wildlife Conservation Commission (FFWCC). 2002. A conceptual management plan for Caravelle Ranch Wildlife Management Area: 2002 – 2007. Tallahassee, FL. 218 pp. Available from http://myfwc.com/wma- planning/CMP/Caravelle%20Ranch%20WMA/Caravelle%20Ranch%20CMP%202002-2007.pdf (accessed December 2007) Alligator Flag Preserve Land Management Plan Update August 2014 Conservation Collier Program 54 Florida Fish and Wildlife Conservation Commission (FFWCC). 2003, January 6. Florida's breeding bird atlas: A collaborative study of Florida's birdlife. http://www.myfwc.com/bba/ (accessed July 2008). Florida Natural Areas Inventory (FNAI). 2008. Acres of conservation lands by county. Florida State University, Florida Natural Areas Inventory, Tallahassee. FL. Available from http://www.fnai.org/pdf/MA_acres_counties.pdf (accessed August 2008). Florida Exotic Pest Plant Council (FLEPPC). 2019. List of Florida’s invasive plant species. Florida Exotic Pest Plant Council. Available from Internet: http://www.fleppc.org/listl1 list..htm (accessed September 2019). Florida Natural Areas Inventory Areas of Conservation Lands By County March 2019 https://www.fnai.org/pdf/MAxCounty_201903.pdf (Accessed September 2019) Florida Natural Areas Inventory (FNAI) and Florida Department of Natural Resources (FDNR) 1990. Guide to the Natural Communities of Florida. Florida Natural Areas Inventory and Florida Department of Natural Resources. Gilbert, T. 2005. South Florida Vegetation Classification Scheme Crosswalks. Florida Fish and Wildlife Conservation Commission, Office of Environmental Services. Available from http://crocdoc.ifas.ufl.edu/crosswalk/index.php?cw=ffwcclandcover (accessed June 2008). Humphrey, S.R. and P.G.R. Jodice. 1992. Big Cypress fox squirrel. Pp. 224-233. In S.R. Humphrey (ed.), Rare and Endangered Biota of Florida. Mammals. University Presses of Florida, Gainesville, FL. Institute for Regional Conservation (IRC) https://www.regionalconservation.org/beta/nfyn/plantdetail.asp?tx=Swiemaha (Accessed September 2020) Johnson, S. 2007. The Cuban treefrog (Osteopilus septentrionalis) in Florida. Department of Wildlife Ecology and Conservation Publication WEC218. 8pp. Florida Cooperative Extension Service, Institute of Food and Agricultural Sciences (IFAS), University of Florida. Available from http://edis.ifas.ufl.edu/UW259 (accessed December 2007) Karim, A. 2007. Status and use of tropical hardwood hammocks and forested residential areas as habitat for resident and Neotropical migratory birds in the Florida Keys. Master of Science Thesis. University of Florida, Gainesville, FL. 61pp. Langeland, K. A., and R. K. Stocker. 2001. Control of non-native plants in natural areas of Florida. University of Florida Cooperative Extension Service Document SP 242. 34pp. University of Florida, UF/IFAS Extension Digital Information Source (EDIS) Database. Available from http://edis.ifas.ufl.edu/pdffiles/WG/WG20900.pdf (accessed December 2007). Larson, B. C., J. H. Frank, G. M. Allen, M. B. Main. 2006. Florida’s native bromeli ads. University of Florida Cooperative Extension Service Circular 1466. 10pp. University of Florida, UF/IFAS Extension Digital Information Source (EDIS) Database. Available from http://edis.ifas.ufl.edu/UW205 (accessed November 2007). Lee, J. C. 1985. Anolis sagrei in Florida: Phenetics of a colonizing species I. Meristic characters. Copeia 1985:182-194. Lodge, T. E. 2005. The Everglades handbook - Understanding the Ecosystem. 2nd edition. CRC Press, Boca Raton, FL. Liudahl, K., D.J. Belz, L. Carey, R.W. Drew, S. Fisher, and R. Pate. 1990. Soil survey of Collier County area Florida. USDA, Natural Resources Conservation Service; Washington, D.C. Alligator Flag Preserve Land Management Plan Update August 2014 Conservation Collier Program 55 Masterson, J. 2007. Felis catus. Smithsonian Marine Station at Fort Pierce. Fort Pierce, Florida. Available from http://www.sms.si.edu/IRLspec/Felis_catus.htm (accessed November 2007). Mazziotti, F. J. 2002. Wood Storks (Mycteria americana). Wildlife Ecology and Conservation Department, Florida Cooperative Extension Service document SSWIS12. 2pp. University of Florida, UF/IFAS Extension Digital Information Source (EDIS) Database. Available from http://edis.ifas.ufl.edu/UW065 (accessed November 2007). Miller J. A. 1986. Hydrogeologic Framework of the Floridan Aquifer System in Florida and in parts of Georgia, Alabama, and South Carolina. United States Geological Survey Professional Paper 1403-B. United States Government Printing Office, Washington, D.C. Nelson, G. 2000. The ferns of Florida: a reference and field guide. Pineapple Press, Sarasota, FL. Oaks, R. Q. and J. R. Dunbar. 1974. Post Miocene Stratigraphy of the Central and Southern Atlantic Coastal Plain. Utah State University Press, Logan, Utah. Schwartz, A. and R. W. Henderson. 1991. Amphibians and reptiles of the West Indies: descriptions, distributions, and natural history. University of Florida Press, Gainesville. Scott, T. M. 1988. Lithostratigraphy of the Hawthorne Group (Miocene). Florida Geological Survey Bulletin No. 59, Tallahassee, Florida. Stimac J. L., and S. B. Alves. 1994. Pest Management in the Subtropics: Biological Control A Florida Perspective. (Rosen D, Bennett FD, Capinera JL, Ed.) pp. 353-380. Intercept Limited, Andover, Hants SP10 1 YG, UK. Sullivan, J. 1994. Cypress savanna. In: Fire Effects Information System. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available from : http://www.fs.fed.us/database/feis/ (accessed July 2008) United States Fish and Wildlife Service (USFWS). 1999. Flowing water swamps. South Florida multi- species recovery plan – a species plan…an ecosystem approach. USFWS Southeast Region, Compact Disk. United States Fish and Wildlife Service (USFWS). 1999. Hydric pine flatwoods. South Florida multi - species recovery plan – a species plan…an ecosystem approach. USFWS Southeast Region, Compact Disk. United States Fish and Wildlife Service (USFWS). 1999. Mesic pine flatwoods. South Florida multi - species recovery plan – a species plan…an ecosystem approach. USFWS Southeast Region, Compact Disk. Willcox, E. and W. M. Giuliano. 2006. Red Imported Fire Ants and Their Impacts on Wildlife. Department of Wildlife Ecology and Conservation Publication WEC 207. Florida Cooperative Extension Service, Institute of Food and Agricultural Sciences (IFAS), University of Florida . Available http://edis.ifas.ufl.edu/UW242 Wunderlin, R. P., and B. F. Hansen. 2008. Atlas of Florida vascular plants. [S.M. Landry and K.N. Campbell (application development), Floirda Center for Community Design and Research]. Institute for Systematic Botany, University of South Florida, Tampa. Available from http.//www.plantatlas.usf.edu/. 2nd DRAFT Alligator Flag Preserve Land Management Plan Conservation Collier Program 56 Appendix 1. Vegetation Scheme Crosswalks/ Florida Natural Areas Inventory Plant Community Classification FFWCC^MSRP^FNAI* ID Name Name ID Name ID Name Name Name Wet Flatwoods Freshwater Tidal Swamp FSc Cypress strands Marl Prairie FSd Cypress domes/heads Floodplain Swamp FSCpi Cypress-pines Freshwater Tidal Swamp SVC Cypress savanna Slough SVCd Dwarf cypress Strand Swamp SVCpi Cypress with pine Basin Swamp Dome Swamp F Forest 13 South Florida Slash Pine Forest Pine Rocklands Pine Rockland SV Savanna 16 Mesic-Hydric Pine Forest Compositional Group Mesic Pine Flatwoods Mesic Flatwoods SVPI Pine savanna 25 South Florida Slash Pine Woodland Dry Prairie Scrubby Flatwoods SVx Slash pine mixed with palms 29 Dry Prairie Ecological Complex Cutthroat Grass Communities Wet Flatwoods 18 Cypress Forest Compositional Group South Florida Vegetation Classification Scheme Crosswalks for Plant Communities Observed on the Alligator Flag Preserve EVSC^FLGAP^FLUCCS^ FS Swamp forest Bottomland Hardwood Forest 53 * Classification of plant communities based on the Natural Communities Guide developed by Florida Natural Areas Inventory (FNAI) ^ Crosswalks for 5 vegetation classification schemes used in south Florida: 1. Everglades Vegetation Classification System (EVSC, South Florida National Parks), 2. Florida Fish and Wildlife Conservation Commission (FFWCC), 3. Florida Gap Analysis Project (FLGAP, US Geological Survey), 4. Florida Land Use and Cover Classification System (FLUCCS, Florida Department of Transportation and Water Management Districts), 5. Multi-Species Recovery Project (MSRP, US Fish and Wildlife Service). Source: Gilbert 2005 Dwarf Cypress Prairie 621 Cypress Freshwater Marshes Flowing Water Swamps Pond Swamps Freshwater Marsh 17 Swamp Forest Ecological Complex 624 Cypress - pine - cabbage palm Pond Swamps Pineland Dry Prairie 411 Pine flatwoods Cypress Swamp DRAFT Five year update-Alligator Flag Preserve Land Management Plan Conservation Collier Program 57 Appendix 2. Preliminary Floristic Inventory of the Alligator Flag Scientific Name Common Name(s) State b FLEPPCc Acacia auriculiformis a Earleaf acacia I Acer rubrum Red maple Ambrosia artemisiifolia Common ragweed Amphicarpum muhlenbergianum Blue maidencane Andropogon glomeratus Bushy bluestem Annona glabra Pond apple Aristida stricta var. beyrichiana Wiregrass Baccharis halimifolia Saltbush, Groundsel tree, Sea-myrtle Bidens alba Beggarticks, Romerillo Blechnum serrulatum Swamp fern, Toothed midsorus fern Boehmeria cylindrica False nettle, Bog hemp Cassytha filiformis Lovevine, Devil's gut Casuarina sp.a Australian pine I Centella asiatica Spadeleaf Cephalanthus occidentalis Common buttonbush Chrysobalanus icaco Coco plum Cladium jamaicense Sawgrass, Jamaica swamp sawgrass Coreopsis leavenworthii Leavenworth's tickseed Cornus foemina Swamp dogwood, Stiff dogwood Cupaniopsis anacardioides a Carrotwood I Cyperus haspan Haspan flatsedge Cyperus ligularis Swamp flatsedge Diospyros virginiana Common persimmon Emilia fosbergii a Florida tassleflower Encyclia tampensis Butterfly orchid Eupatorium capillifolium Dog-fennel Eustachys petraea Common fingergrass, Pinewoods fingergrass Ficus aurea Strangler fig, Golden fig Fuirena scirpoidea Southern umbrella sedge Fraxinus caroliniana Carolina ash, Water ash, Pop ash Fuirena spp.Umbrella sedge Gamochaeta antillana Caribbean purple everlasting Heliotropium polyphyllum Pineland heliotrope Ilex cassine Dahoon holly, Dahoon Linaria canadensis Canadian toadflax Melaleuca quinquenervia a Punk tree, Melaleuca, Paper bark I Mikania scandens Climbing hempvine Myrica cerifera Wax myrtle, Southern bayberry Nymphoides aquatica Big floatingheart, Banana lily Osmunda regalis var. spectabilis Royal fern C Oxalis spp.Wood sorrel Panicum hemitomon Maidencane Alligator Flag Preserve: Preliminary Plant List Flora recorded by: Christal Segura, Annisa Karim, Dr. George Wilder Alligator Flag Preserve by Maureen S. Bonness, with assistance from Jean McCollom September 2, 2020 2009 2020 Scientific Name (prior name)Common Names NativeNot NativeStateFNAIFLEPPCx Abrus precatorius Rosary-pea, Crab-eyes √I x x Acacia auriculiformis Earleaf acacia √I x Acalypha arvensis Field copperleaf √ x x Acer rubrum Red maple N x Ageratum conyzoides Tropical whiteweed √ x x Ambrosia artemisiifolia Common ragweed N x x Amphicarpum muhlenbergianum Blue-maidencane N x Andropogon glomeratus Bushy bluestem N x Andropogon glomeratus var. glaucopsis Purple bluestem N x Andropogon glomeratus var. pumilus Common bushy bluestem N x Andropogon virginicus var. virginicus Broomsedge bluestem N x x Annona glabra Pond-apple N x Aristida stricta (=A. beyrichiana )Southern wiregrass N x x Asemeia violacea (=Polygala grandiflora, P. violacea) Candyweed, Showy milkwort N x x Baccharis halimifolia Saltbush, Groundsel tree, Sea-myrtle N x x Bidens alba Spanish-needles N x x Boehmeria cylindrica False nettle, Bog hemp N x Caperonia castaneifolia Chestnutleaf falsecroton N x Cassytha filiformis Lovevine, Devil's gut N x Casuarina equisetifolia Australian-pine, Horsetail casuarina √I x Cenchrus spinifex (=C. incertus)Coastal sandbur N x x Centella asiatica Coinwort, Spadeleaf N x x Cephalanthus occidentalis Buttonbush N x Chamaecrista sp.Partridge pea N x Chromolaena odorata Jack-in-the-bush N x x Chrysobalanus icaco Coco plum N x Cirsium nuttallii Nuttall's thistle N x x Cladium jamaicense Sawgrass N x Coleataenia rigidula (=Panicum rigidulum) Redtop panicum N x Conyza canadensis Canadian horseweed N x x Coreopsis leavenworthii Leavenworth's tickseed N x Cornus foemina Swamp dogwood, Stiff dogwood N x Crotalaria pallida var. obovata Smooth rattlebox √ x Croton glandulosus var. septentrionalis (=var. glandulosus) Vente conmigo N x Cupaniopsis anacardioides Carrotwood √I x x Cyperus haspan Haspan flatsedge N x x Cyperus ligularis Swamp flatsedge N x Cyperus polystachyos Manyspike flatsedge, Texas sedge N x Cyperus surinamensis Tropical flatsedge N x Desmodium incanum Beggar's-ticks √ x Dichanthelium aciculare Needleleaf witchgrass N x Dichanthelium dichotomum Cypress witchgrass N x Diodia virginiana Buttonweed, Virginia buttonweed N x Diospyros virginiana Common persimmon N x Echinochloa walteri Coast cockspur N x Eclipta prostrata False daisy N 2009 2020 Scientific Name (prior name)Common Names NativeNot NativeStateFNAIFLEPPCx x Emilia fosbergii Florida tasselflower √ x Emilia sonchifolia Lilac tassleflower √ x x Encyclia tampensis Florida butterfly orchid N x Eragrostis atrovirens Thalia lovegrass √ x Eragrostis scaligera Tender lovegrass √ x Eragrostis sp.Lovegrass x Erechtites hieraciifolius Fireweed, American burnweed N x Erigeron quercifolius Southern-fleabane, Oakleaf fleabane N x Erigeron vernus Early whitetop fleabane N x Eryngium yuccifolium Button rattlesnake master, Button eryngo N x x Eupatorium capillifolium Dogfennel N x Eupatorium leptophyllum Falsefennel N x Eupatorium mohrii Mohr's thoroughwort N x Euphorbia graminea Grassleaf spurge √ x Euphorbia hypericifolia (=Chamaesyce hypericifolia) Eyebane, Graceful sandmat N x Euphorbia hyssopifolia (=Chamaesyce hyssopifolia) Eyebane, Hyssopleaf sandmat N x x Euploca polyphylla (=Heliotropium polyphyllum) Pineland heliotrope N x Eustachys glauca Prairie fingergrass N x x Eustachys petraea Pinewoods fingergrass N x Evolvulus sericeus Silver dwarf morningglory N x x Ficus aurea Strangler fig, Golden fig N x Flaveria linearis Narrowleaf yellowtops N x x Fraxinus caroliniana Pop ash N x x Fuirena scirpoidea Umbrellasedge N x Fuirena sp.Saltmarsh umbrellasedge N x x Funastrum clausum (=Sarcostemma clausum) Whitevine, White twinevine N x x Gamochaeta antillana Caribbean purple everlasting N x Hypericum gentianoides Pineweeds, Orangegrass N x Hyptis alata Musky mint, Clustered bushmint N x x Ilex cassine Dahoon holly, Dahoon N x Ipomoea sagittata Glades morning-glory N x Juncus megacephalus Bighead rush N x Leucaena leucocephala White leadtree √II x Linaria canadensis Canadian toadflax N x Ludwigia curtissii Curtiss's primrosewillow N x Ludwigia microcarpa Smallfruit primrosewillow N x Lythrum alatum var. lanceolatum Winged loosestrife N x Macroptilium lathyroides Wild bushbean √II x Mangifera indica Mango √ x x Melaleuca quinquenervia Punktree √I x Melothria pendula Creeping-cucumber N x x Mikania scandens Climbing hempweed, Climbing hempvine N x Mitreola petiolata Miterwort, Lax hornpod N x Momordica charantia Balsampear √II x x Morella cerifera (=Myrica cerifera)Wax myrtle, Southern bayberry N x Myrsine cubana (=Rapanea punctata)Myrsine, Colicwood N x Nymphaea sp.Waterlily 2009 2020 Scientific Name (prior name)Common Names NativeNot NativeStateFNAIFLEPPCx Oldenlandia corymbosa (=Hedyotis corymbosa) Flattop mille graines √ x Osmunda regalis var. spectabilis Royal fern N x Oxalis corniculata Common yellow woodsorrel; Creeping woodsorrel N x Oxalis sp.Woodsorrel N x Panicum dichotomiflorum Fall panicgrass N x x Panicum hemitomon Maidencane N x Panicum repens Torpedo grass √I x Parietaria floridana Florida pellitory N x Parietaria praetermissa Clustered pellitory N x Parthenocissus quinquefolia Virginia-creeper, Woodbine N x x Paspalum monostachyum Gulfdune paspalum N x Paspalum setaceum Thin paspalum N x Passiflora suberosa Corkystem passionflower N x Persea borbonia Red bay N x Persea palustris Swamp bay N x x Phlebodium aureum Golden polypody N x Phoenix sp. (not reclinata)Date palm √ x x Phyla nodiflora Frogfruit, Capeweed N x Phyllanthus tenellus Mascarene Island leafflower √ x Phyllanthus urinaria Chamber bitter √ x Physalis walteri Walter's groundcherry N x x Pinus elliottii var. densa South Florida slash pine N x x Piriqueta cistoides subsp. caroliniana (=Piriqueta caroliniana) Pitted stripeseed N x x Pluchea baccharis (=Pluchea rosea)Rosy camphorweed N x Pluchea odorata Sweetscent N x Polypremum procumbens Rustweed, Juniperleaf N x Pouzolzia zeylanica Pouzolz's bush √ x Proserpinaca palustris Marsh mermaidweed N x Psilotum nudum Whisk fern N x Ptilimnium capillaceum Mock bishopsweed, Herbwilliam N x Quercus laurifolia Laurel oak, Diamond oak N x Quercus virginiana Virginia live oak N x Rhus copallinum Winged sumac N x Rhynchospora divergens Spreading beaksedge N x Rhynchospora filifolia Threadleaf beaksedge N x x Rhynchospora inundata Narrowfruit horned beaksedge N x Rhynchospora microcarpa Southern beaksedge N x Richardia grandiflora Largeflower Mexican clover √II x Rubus trivialis Southern dewberry N x x Sabal palmetto Cabbage palm N x Sabatia stellaris Rose-of-Plymouth N x Saccharum giganteum Sugarcane plumegrass N x Sagittaria graminea Grassy arrowhead N x Sagittaria latifolia Broadliaf arrowhead, Common arrowhead, duck potato N x Salix caroliniana Coastal Plain willow N x Samolus valerandi subsp. parviflorus Pineland pimpernel N x Schinus terebinthifolia Brazilian pepper √I x Schizachyrium rhizomatum Rhizomatous bluestem N x Scleria reticularis Netted nutrush N 2009 2020 Scientific Name (prior name)Common Names NativeNot NativeStateFNAIFLEPPCx Scoparia dulcis Sweetbroom, Licoriceweed N x x Serenoa repens Saw palmetto N x Setaria parviflora (=S. geniculata)Knotroot foxtail, Yellow bristlegrass N x Sideroxylon celastrinum Saffron plum, Bumelia N x Sideroxylon reclinatum Florida bully, Buckthorn N x x Smilax auriculata Earleaf greenbrier N x Solanum viarum Tropical soda apple √i x x Spermacoce verticillata Shrubby false buttonweed √II x Stenotaphrum secundatum St. Augustine grass √ x Stillingia aquatica Corkwood; water toothleaf N x Stillingia sylvatica Queensdelight N x Swietenia mahagoni West Indian mahogany N T S3 x Syagrus romanzoffiana Queen palm √II x Taxodium ascendens Pond cypress N x Taxodium sp.cypress N x x Telmatoblechnum serrulatum (=Blechnum serrulatum) Swamp fern N x x Thalia geniculata Alligatorflag; Fireflag N x Thelypteris sp.Shield fern N x x Tillandsia balbisiana Reflexed wild-pine, Northern needleleaf N T x x Tillandsia fasciculata Stiff-leaved wild-pine, Cardinal airplant N E x x Tillandsia paucifolia Potbelly airplant N x x Tillandsia recurvata Ball-moss N x x Tillandsia setacea Thin-leaved wild-pine, Southern needleleaf N x x Tillandsia usneoides Spanish-moss N x x Toxicodendron radicans Eastern poison-ivy N x Tridax procumbens Coatbuttons √ x x Urena lobata Caesarweed √II x Vicia acutifolia Sand vetch, Fourleaf vetch N x Viola lanceolata Bog white violet N x x Vitis rotundifolia Muscadine, Muscadine grape N x Woodwardia virginica Virginia chain fern N x Xyris jupicai Richard's yelloweyed grass √ 75 152 139 33 3 1 15 Sources. Scentific plant names and Native/Not-Native status is according to the Atlas of Florida Plants website as of July 2020. State status is from Florida Department of Agriculture and Consumer Services 2018 list. FNAI category is from Florida Natural Areas Inventory April 2019 list. FLEPPC category is from the Florida Exotic Pest Plant Council 2019 list. Count State Codes: E=Endangered, T=Threatened FNAI Codes: S1=critically imperiled; S2=imperiled because of rarity; S3=very rare in Florida or restricted range FLEPPC Codes: Category I = species has altered native plant communities; Category II = species with increasing abundance or frequency DRAFT Five year update-Alligator Flag Preserve Land Management Plan Conservation Collier Program 59 Appendix 3. Florida Natural Areas Inventory Report for the Alligator Flag Preserve Report for 1 Matrix Unit: 40546 Descriptions DOCUMENTED - There is a documented occurrence in the FNAI database of the species or community within this Matrix Unit. DOCUMENTED-HISTORIC - There is a documented occurrence in the FNAI database of the species or community within this Matrix Unit; however the occurrence has not been observed/reported within the last twenty years. LIKELY - The species or community is known to occur in this vicinity, and is considered likely within this Matrix Unit because: 1. documented occurrence overlaps this and adjacent Matrix Units, but the documentation isn’t precise enough to indicate which of those Units the species or community is actually located in; or 2. there is a documented occurrence in the vicinity and there is suitable habitat for that species or community within this Matrix Unit. POTENTIAL - This Matrix Unit lies within the known or predicted range of the species or community based on expert knowledge and environmental variables such as climate, soils, topography, and landcover. Matrix Unit ID: 40546 0 Documented Elements Found 0 Documented-Historic Elements Found 3 Likely Elements Found Scientific and Common Names Global Rank State Rank Federal Status State Listing Mesic flatwoods G4 S4 N N Mycteria americana Wood Stork G4 S2 LE LE Puma concolor coryi Florida Panther G5T1 S1 LE LE Matrix Unit ID: 40546 18 Potential Elements for Matrix Unit 40546 Scientific and Common Names Global Rank State Rank Federal Status State Listing Andropogon arctatus Pine-woods Bluestem G3 S3 N LT Athene cunicularia floridana Florida Burrowing Owl G4T3 S3 N LS Appendix 3 (continued). Florida Natural Areas Inventory Report for the Alligator Flag Preserve DRAFT Five year update-Alligator Flag Preserve Land Management Plan Conservation Collier Program 60 Scientific and Common Names Global Rank State Rank Federal Status State Listing Corynorhinus rafinesquii Rafinesque's Big-eared Bat G3G4 S2 N N Drymarchon couperi Eastern Indigo Snake G3 S3 LT LT Elytraria caroliniensis var. angustifolia Narrow-leaved Carolina Scalystem G4T2 S2 N N Eumops floridanus Florida bonneted bat G1 S1 N LE Gopherus polyphemus Gopher Tortoise G3 S3 N LT Lechea cernua Nodding Pinweed G3 S3 N LT Linum carteri var. smallii Small's flax G2T2 S2 N LE Mustela frenata peninsulae Florida Long-tailed Weasel G5T3 S3 N N Nemastylis floridana Celestial Lily G2 S2 N LE Picoides borealis Red-cockaded Woodpecker G3 S2 LE LS Polyrrhiza lindenii Ghost Orchid G2G4 S2 N LE Pteroglossaspis ecristata Giant Orchid G2G3 S2 N LT Rostrhamus sociabilis plumbeus Snail Kite G4G5T3Q S2 LE LE Sceloporus woodi Florida Scrub Lizard G3 S3 N N Sciurus niger avicennia Mangrove Fox Squirrel G5T2 S2 N LT Ursus americanus floridanus Florida Black Bear G5T2 S2 N LT* Disclaimer The data maintained by the Florida Natural Areas Inventory represent the single most comprehensive source of information available on the locations of rare species and other significant ecological resources statewide. However, the data are not always based on comprehensive or site-specific field surveys. Therefore, this information should not be regarded as a final statement on the biological resources of the site being considered, nor should it be substituted for on-site surveys. FNAI shall not be held liable for the accuracy and completeness of these data, or opinions or conclusions drawn from these data. FNAI is not inviting reliance on these data. Inventory data are designed for the purposes of conservation planning and scientific research and are not intended for use as the primary criteria for regulatory decisions. Unofficial Report These results are considered unofficial. FNAI offers a Standard Data Request option for those needing certifiable data.