Loading...
Agenda 01/27/2026 Item #16A14 (Resolution - Related to the Stewardship Sending Area 15 – Restoration Credits and to award Restoration II credits to Collier Land Holdings, Ltd.)1/27/2026 Item # 16.A.14 ID# 2025-5173 Executive Summary Recommendation to approve a Resolution related to the Stewardship Sending Area 15 – Restoration Credits (CLH & CDC SSA 15) in the Rural Lands Stewardship Area Zoning Overlay District (RLSA) and to award Restoration II credits to Collier Land Holdings, Ltd. in accordance with the approved restoration plan. OBJECTIVE: To approve a Resolution to the fifteenth Stewardship Sending Area (SSA) (CLH & CDC SSA 15) in the Rural Lands Stewardship Area Zoning Overlay District (RLSA) and to award Restoration Credits to Collier Land Holdings, Ltd., in accordance with the approved restoration plan. CONSIDERATIONS: The Stewardship Credit Program is the foundation of the RLSA. Collier County adopted the RLSA Overlay as the implementing regulation for the Growth Management Plan amendments, known broadly as the “Rural/Eastern Lands Amendments.” These amendments were developed in response to the Administration Commission Final Order No. AC 99-002, which required a “Rural and Agricultural assessment.” On January 28, 2020, the Board of County Commissioners (BCC) approved amendments to the fifteenth Stewardship Sending Area (SSA) known as “CLH & CDC SSA 15,” and awarded 20,653 Stewardship Credits immediately and an additional 10,714 Stewardship Credits to be available for the Owner to use, sell, transfer, all or in part, upon successful completion of the restoration improvements as set forth in the Restoration Plan within Resolution 2020-25. This SSA consists of 5,253.4 acres within the Camp Keais Strand, a significant regional flow way and wildlife corridor connecting Lake Trafford and Corkscrew Swamp at its northern extent to the Florida Panther National Wildlife Refuge to the south. In December 2025, staff conducted a site visit to SSA 15, reviewed the completed restoration activities in Restoration Area 1, as identified in the Restoration Plan approved in Resolution 2020-25. This restoration consisted of hydrologic improvements, including: • Removal of an old farm road was removed in SSA 14 to the north of SSA 15 (approved by the BCC on April 22, 2025), • Removal of an old farm road approximately 1 mile long immediately south of Oil Well Road, • Removal of approximately 500-foot long old farm road in the southern portion of the SSA that severely constricted water flow and created a “pinch point.” Staff verified the farm roads, including the fill material, were removed and restored to the natural grade of the adjacent wetlands and ditches were backfilled. The remaining 449.5 credits will be available upon successful completion of activities associated with Restoration Areas 2, 3, and 4. This item is consistent with the Collier County strategic plan objectives to preserve and enhance the character of our community and to protect our natural resources. FISCAL IMPACT: There are no fiscal impacts to the County associated with the application. The applicant is responsible for the cost of the SFWMD permits and restoration activities. GROWTH MANAGEMENT IMPACT: The Rural Lands Stewardship Area Overlay in the Future Land Use Element (FLUE) established the process and requirements for establishing SSAs, what lands qualify for SSA designation, and the process for obtaining Restoration credits. The Rural Lands Stewardship Area Overlay is implemented through the Rural Lands Stewardship Area Zoning Overlay District. The zoning overlay contains the same requirements and limitations as the FLUE Overlay. The restoration activities completed are consistent with the restoration plan submitted and approved with the SSA designation (Resolution 2020-25). Therefore, staff’s analysis indicates this resolution for restoration credits is compliant with the RLSA Zoning Overlay and is also consistent with the FLUE. Page 1003 of 5261 1/27/2026 Item # 16.A.14 ID# 2025-5173 LEGAL CONSIDERATIONS: This item is approved as to form and legality, and it requires a majority vote for Board approval (HFAC). RECOMMENDATION(S): To adopt a Resolution awarding Stewardship Sending Area 15 (CLH & CDC 15) in the Rural Lands Stewardship Area Zoning Overlay District (RLSA) 10,264.5 restoration (R-II) credits for completing restoration activities within SSA 15. PREPARED BY: Jaime Cook, Director, Development Review Division, Growth Management Community Development ATTACHMENTS: 1. Resolution 1-2-2026 2. SSA 15 Restoration Plan_Approved 3. Camp Keais Pinchpoint Removal SSA 15 4. Old Roadbed Removal Areas Page 1004 of 5261 [25-LDS-00392/1993839/1]9 Page 1 of 3 SSA 15 Restoration II credits 1-2-26 RESOLUTION 2026 - _____ A RESOLUTION OF THE COLLIER COUNTY BOARD OF COUNTY COMMISSIONERS APPROVING THE USE, TRANSFER, OR SALE OF STEWARDSHIP CREDITS BY OWNERS FOR THE COMPLETION OF RESTORATION IMPROVEMENTS IN RESTORATION AREAS 1A, 1B, AND 1C IN ACCORDANCE WITH THE RESTORATION PLAN FOR THE STEWARDSHIP SENDING AREA WITH A DESIGNATION AS “CLH & CDC SSA 15” IN THE RURAL LANDS STEWARDSHIP AREA OVERLAY, WHICH CREDITS WERE APPROVED BY RESOLUTION 2020-25 WHEREAS, on November 18, 2008, by Resolution No. 2008-329, the Board of County Commissioners (“Board”) created a Stewardship Sending Area with a designation of “CLH & CDC SSA 15” and entered into a Credit Agreement, Easement Agreement and Escrow Agreement with Collier Land Holdings, Ltd. and CDC Investments, LLC; and WHEREAS, on September 10, 2013, by Resolution No. 2013-200, the Board approved an amendment to the Credit Agreement and Easement Agreement to extend certain dates by one (1) year; and WHEREAS, on September 23, 2014, by Resolution No. 2014-187, the Board approved the Second Amendment to the Credit Agreement and Easement Agreement, which Second Amendment extended the date by which the SSA 15 Stewardship Credits must be exchanged for development of Rivergrass Village Stewardship Receiving Area to November 18, 2017; and WHERAS, on October 10, 2017, by Resolution No. 2017-185, the Board approved the Third Amendments to the Credit Agreement and Easement Agreement, which Third Amendments extended the exchange date to November 18, 2020; and WHEREAS, on January 28, 2020, by Resolution No. 2020-25, the Board of County Commissioners approved an amendment to CLH & CDC SSA 15 removing 5.6± acres from the SSA, redesignating 5,253.4± acres as CLH & CDC SSA 15, removing additional land use layers, providing restoration credits, establishing the number of Stewardship Credits generated by the Amended and Restated Credit Agreement, Amended and Restated Easement Agreement and Amended and Restated Escrow Agreement, and extending the exchange date to November 18, 2023 (the Fourth Amendment); and Page 1005 of 5261 [25-LDS-00392/1993839/1]9 Page 2 of 3 SSA 15 Restoration II credits 1-2-26 WHEREAS, on October 10, 2023, by Resolution No. 2023-197, the Board approved the Fifth Amendment to the Credit Agreement and Escrow Agreement, which extended the exchange date to November 18, 2025; and WHEREAS, on December 31, 2025, the Easement Agreement was recorded in Official Records Book 6541 Page 1484 et. seq. of the Public Records of Collier County, Florida; and WHEREAS, One of the owners, Collier Land Holdings, has completed the restoration improvements for Areas 1A, 1B and 1C as set forth in the Restoration Plan within Resolution 2020-25; and WHEREAS, County staff has verified that the restoration improvements for Areas 1A, 1B and 1C were completed in 2025 during a staff site visit in December 2025; and WHEREAS, County staff is requesting that the Board of County Commissioners approve the use of ten thousand, two hundred sixty-four and five-tenths (10,264.5) Stewardship Credits for completed restoration improvements for Areas 1A, 1B and 1C. NOW, THEREFORE, BE IT RESOLVED BY THE BOARD OF COUNTY COMMISSIONERS OF COLLIER COUNTY, FLORIDA, that: 1. The Board approves the use, transfer or sale of ten thousand two hundred sixty- four and five-tenths (10,264.5) Stewardship Credits and approves the use of the credits in exchange for the completion of restoration improvements for Area Areas 1A, 1B and 1C as set forth in the Restoration Plan within Resolution 2020-25. 2. Four hundred forty-nine and five-tenths (449.5) Stewardship Credits will be available upon completion of the restoration improvements for Areas 2, 3 and This Resolution is adopted after motion, second and majority vote, this _____ day of ________________, 2026. ATTEST: BOARD OF COUNTY COMMISSIONERS CRYSTAL K. KINZEL, CLERK COLLIER COUNTY, FLORIDA By: ___________________________ By:________________________________ Deputy Clerk Dan Kowal, Chairman Page 1006 of 5261 [25-LDS-00392/1993839/1]9 Page 3 of 3 SSA 15 Restoration II credits 1-2-26 Approved as to form and legality: ____________________________ Heidi Ashton-Cicko Managing Assistant County Attorney Page 1007 of 5261 Passarella & Associates, Inc. 1 of 10 #05CEM1481 Revised 10/18/19 STEWARDSHIP SENDING AREA 15 COLLIER COUNTY RESTORATION PLAN Revised October 2019 1.0 INTRODUCTION The following provides details of the restoration plan for Stewardship Sending Area (SSA) 15 located in Sections 25, 26, 35, and 36; Township 47 South; Range 28 East; and Sections 1, 2, 12, 13, 14, 23, 24, 25, 26, 35, and 36; Township 48 South; Range 28 East; Collier County. This restoration plan and the accompanying drawings (Sheets 1 through 7) are provided in compliance with Collier County Land Development Code (LDC) Section 4.08.06.C.5.j.(5) and contain the required elements per the LDC. SSA 15 includes the Camp Keais Strand, which is a significant regional flow-way and wildlife corridor that connects Lake Trafford and Corkscrew Swamp at its northern extent to the Florida Panther National Wildlife Refuge (FPNWR) to the south. The State of Florida targeted the lands that encompass SSA 15 as essential lands remaining in the Florida Forever Corkscrew Regional Ecosystem Watershed (CREW) project. The State noted that these lands, as a component of CREW, will conserve connections between existing conservation areas, provide protection for rare wildlife, and protect the flows of water feeding the FPNWR, Fakahatchee Strand, and other areas. SSA 15 is located adjacent to and in close proximity to other existing and proposed SSAs (Collier County SSAs 1, 2, 6, 9, and 14). SSA 15 is also located in the vicinity of existing public lands and designated acquisition areas including CREW, Corkscrew Swamp Sanctuary, Big Cypress National Preserve, FPNWR, and Fakahatchee Strand Preserve State Park. Proposed restoration within SSA 15 totals 2,678.49± acres and includes 2,566.11± acres of flow- way restoration, the restoration of native habitat in 104.23± acres of existing agricultural fields, and the restoration of 8.15± acres of habitat through exotic removal. The entity responsible for completion of this restoration plan is the Big Cypress Stewardship District. 2.0 RESTORATION GOALS The goal of the restoration plan is to return natural/historic functions to degraded and altered habitats, which will in turn provide regional benefits for surface water flow and wildlife. The Project site offers a unique opportunity for the restoration and protection of a regional wetland system, flow-way, and wildlife habitat corridor. The Camp Keais Strand is a natural, regional cypress slough system that conveys flows from the Corkscrew Swamp and Lake Trafford into the FPNWR and Fakahatchee Strand to the south. Restoration and protection of this regional network of conservation lands provides continuity of surface water flow in the region; essential habitat and foraging areas for fauna, including the endangered wood stork (Mycteria americana); and a corridor for movement by wildlife, including the endangered Florida panther (Puma concolor coryi). Exhibit F to Easement Agreement Page 1008 of 5261 Passarella & Associates, Inc. 2 of 10 #05CEM1481 Revised 10/18/19 2.1 Flow-Way Restoration The South Lee County Watershed Plan identified the restoration of hydrology in Camp Keais Strand as a means to alleviate regional flooding in Southern Lee County and Collier County. Camp Keais Strand was once a large natural slough delivering and cleansing water from Lake Trafford south to Fakahatchee Preserve State Park. The original flow-way has been constrained and bisected in numerous places by man-made alterations and impediments causing water to flow west from Lake Trafford and flooding residential development. The northernmost impediment to water flow in Camp Keais Strand, as identified by the South Lee County Watershed Plan, is an existing historic roadway which was the original connection from Immokalee to Big Corkscrew Island. This old roadway bisects the north end of SSA 14, which lies to the north of SSA 15, and is designated for removal as part of the SSA 14 restoration plan. The removal of this road will provide increased water flow throughout Camp Keais Strand, including the portions of the strand within SSA 15 north and south of Oil Well Road. Water flows south from SSA 14 through a bridge and box culvert under Immokalee Road, and continues south through SSA 15. In addition to the hydrologic improvements achieved through restoration designated as part of SSA 14, flow-way restoration activities are planned for other portions of Camp Keais Strand located within SSA 15. Further flow-way restoration will be accomplished through the removal of an elevated road grade that crosses the strand on the south side of Oil Well Road, and through the alleviation of a major pinch point in the strand south of Oil Well Road. The location of the road removal areas are shown on Sheet 4 of the attached drawings. The goal of the flow-way restoration is the enhancement of foraging habitat for wading birds, including the wood stork; the hydrologic improvement of Camp Keais Strand; and the restoration of historic sheet flow conditions within Camp Keais Strand. 2.1.1 Removal of Road Grade South of Oil Well Road The road grade to be removed is located approximately 150 feet south of, and runs parallel to, Oil Well Road in Section 24, Township 48 South, Range 28 East. Water flows south through Camp Keais Strand through a bridge and box culvert under Oil Well Road. The flow of water is then impeded by the elevated road grade. The restoration work will consist of removing the elevated road (approximately 3.8 acres). 2.1.2 Elimination of the Pinch Point in Camp Keais Strand Significant flow-way improvements will be achieved through the elimination of the pinch point in Camp Keais Strand south of Oil Well Road. Approximately 1.25 miles south of Oil Well Road, the existing footprint of Camp Keais Strand narrows to approximately 500 feet in width where agricultural fields border the east and west sides of the strand. At this location an elevated farm access road providing access between the fields, bisects the strand and further constricts the flow of water. Page 1009 of 5261 Passarella & Associates, Inc. 3 of 10 #05CEM1481 Revised 10/18/19 The farm road is approximately 20 feet wide and sits approximately 3 feet above natural grade. A narrow area has eroded in the middle of the road, only allowing the flow of water across a narrow opening of roughly 30 feet during the wet season. This pinch point creates a severe constriction of the water flow south through Camp Keais Strand. Elimination of the pinch point will be accomplished through removal of the farm road that crosses the strand and restoration of the farm field on the east side of the strand in this location (Sheet 6). 2.2 Farm Field Restoration The restoration plan for SSA 15 includes restoring habitat from a 104.2± acre farm field within SSA 15 that has been in active agriculture use for several decades. The location of the farm field is shown on Sheet 4 of the attached drawings and consists of Restoration Area 4. Area 4 totals 104.2± acres and is located on the east side of Camp Keais Strand along the eastern boundary of SSA 15. Area 10 (referred to as the “pinch point” field) stretches approximately 1.4 miles from north to south and up to 0.2 mile east to west. The goal of the restoration of this farm field is the creation of quality foraging habitat for wading birds, including the wood stork; the hydrologic improvement of Camp Keais Strand; the restoration of historic sheet flow conditions within Camp Keais Strand; and the creation of a wider corridor for passage by large mammals, including the endangered Florida panther. 2.3 Restoration through Exotic Treatment The restoration plan for SSA 15 also includes enhancing habitats that are infested with exotic and nuisance vegetation. There are two areas in SSA 15 totaling 8.15± acres with greater than 50 percent coverage by exotic vegetation. Due to the infestation by exotic and nuisance vegetation, these areas provide limited value to wildlife. The goal of exotic removal is to restore quality native wetland and upland habitats for utilization by wildlife, including the wood stork. The location of these restoration areas are shown on Sheet 4 of the attached drawings and consist of Restoration Areas 2 and 3. 3.0 RESTORATION WORK The vegetation communities to be restored will consist primarily of wetland habitats with scattered uplands. The wetlands habitats to be restored will include cypress, hydric pine, wet prairie, and freshwater marsh. The upland habitats to be restored will include pine flatwoods and palmetto prairie. The farm field restoration activities will include the creation of short and long hydroperiod wetlands for wading bird habitat. The exotic vegetation species to be treated are those species identified as Category I and Category II invasive exotic plant species, pursuant to the list established by the Florida Exotic Pest Plant Page 1010 of 5261 Passarella & Associates, Inc. 4 of 10 #05CEM1481 Revised 10/18/19 Council (EPPC). The exotic species to be treated include, but are not limited to, melaleuca (Melaleuca quinquenervia), Brazilian pepper (Schinus terebinthifolius), earleaf acacia (Acacia auriculiformis), torpedograss (Panicum repens) and Old World climbing fern (Lygodium microphyllum). 3.1 Removal of Road Grades Removal of the old road grade will consist of the (1) excavation of the fill material; (2) backfilling of adjacent ditches with material from road grade; (3) grading to wetland elevation; and (4) establishment of native wetland vegetation. Prior to removal activities, the limits of the road grade to be removed will be flagged in the field and silt fencing installed. The fill material will then be mechanically removed and used to backfill the adjacent ditches. The road footprint will then be graded to match existing ground elevations in the adjacent wetlands. An as-built survey of the graded site will be performed to ensure the desired elevations have been obtained. After surveying of the final grades, the area will be allowed to naturally recruit and/or be planted as described for the wetland habitats in Section 3.2 below. 3.2 Farm Field Restoration The farm field restoration work for Restoration Area 4 will involve the removal of the perimeter ditching and berms, and grading of the fields to wetland and upland elevations. The fields will be graded as shown on Sheet 5 of the attached drawings. The grading plan for these areas includes the establishment of wading bird foraging habitat. These areas will be graded to varying depths to allow the concentration of prey for wading birds at alternating times of the year as water levels seasonally rise and recede. The excess fill generated from the excavation and grading will be utilized within the Big Cypress Stewardship District or by Collier County and may not be sold for off-site use. An as-built survey of the graded site will be performed to ensure the desired elevations have been obtained. After surveying of the final grades, the areas will be allowed to naturally recruit with native plants common to the habitat type to be restored. Wetland plantings/seeding will be conducted in the farm field restoration areas if, after two years, natural recruitment has not occurred, and sufficient coverage of native vegetation has not been achieved. Wetland ground cover plantings/seeding will include a mix of the species listed in Table 1. The species selected for planting will depend on site conditions and market availability at the time the plantings are to occur. Table 1. Wetland Planting List Common Name Scientific Name Alligator flag Thalia geniculata Arrowhead Sagittaria lancifolia Blue maidencane Amphicarpum muhlenbergianum Page 1011 of 5261 Passarella & Associates, Inc. 5 of 10 #05CEM1481 Revised 10/18/19 Table 1. (Continued) Common Name Scientific Name Broomsedge Andropogon virginicus Cordgrass Spartina bakeri Dense flower knotweed Polygonum glabrum Golden canna Canna flaccida Gulfdune paspalum Paspalum monostachyum Little blue maidencane Amphicarpum muhlenbergianum Maidencane Panicum hemitomon Muhly grass Muhlenbergia capillaris Pickerelweed Pontederia cordata Sawgrass Cladium jamaicense Soft-stem bulrush Scirpus validus Spatterdock Nuphar luteum Spikerush Eleocharis interstincta Swamp lily Crinum americanum Waterlily Nymphaea odorata Wiregrass Aristida stricta Upland tree plantings and ground cover plantings will include a mix of the species listed in Table 2. The species selected for planting will depend on site conditions and market availability at the time the plantings are to occur. Table 2. Upland Planting List Common Name Scientific Name Broomsedge Andropogon virginicus Cabbage palm Sabal palmetto Cordgrass Spartina bakeri Dahoon holly Ilex cassine Fakahatchee grass Tripsacum dactyloides Gulfdune paspalum Paspalum monostachyum Laurel oak Quercus laurifolia Little blue maidencane Amphicarpum muhlenbergianum Live oak Quercus virginiana Muhlygrass Muhlenbergia capillaris Purple lovegrass Eragrostis spectabilis Saw palmetto Serenoa repens Slash pine Pinus elliottii Wiregrass Aristida stricta Page 1012 of 5261 Passarella & Associates, Inc. 6 of 10 #05CEM1481 Revised 10/18/19 3.3 Exotic Treatment Exotic treatment will be conducted using one or more of the following methods: (1) cut exotic trees within 12 inches of ground elevation and treat remaining stump with approved herbicide; (2) girdle standing melaleuca with diameter at breast height (DBH) greater than 4 inches and apply approved herbicide to cambium; (3) foliar application of approved herbicide to melaleuca saplings, Brazilian pepper, and earleaf acacia; (4) foliar application of approved herbicide or hand pulling of exotic seedlings; and (5) direct application of approved herbicide to exotic grasses, ground cover and vines. Exotic trees greater than four inches DBH will be (1) girdled, treated with approved herbicide, and left standing; or (2) the exotic vegetative debris will be cut and stacked in piles at approximately 100-foot intervals. If stacking of debris is utilized, smaller cuttings will be stacked butt end to the ground into a nearly vertical position (i.e., teepee method). Larger cuttings will be cut and stacked side by side into an area approximately six feet on a side. Cuttings will be stacked perpendicular to the previous layer up to a height of approximately four feet (i.e., log cabin method). 4.0 MAINTENANCE AND MANAGEMENT Following the completion of the initial road grade removal, farm field restoration and exotic treatment activities, semi-annual maintenance events and inspections will occur in the restoration areas for the first two years. An ecologist will inspect the restoration areas and identify any areas in need of treatment. Locations of exotic species will be targeted for immediate treatment with an appropriate herbicide. Any additional potential problems will also be noted, and corrective actions taken. Once exotic species levels have been reduced to acceptable limits (i.e., less than five percent cover), inspections of the restoration areas will be conducted annually. 5.0 MONITORING The proposed monitoring of the restoration areas will consist of baseline, time-zero, and annual monitoring of vegetation, wildlife, rainfall, and wetland water levels. The baseline monitoring event and report will document conditions of the restoration areas as they currently exist. The time- zero monitoring event and report will document conditions immediately following completion of restoration activities. Annual monitoring and reporting will then be conducted for a total of five years. The annual reports will document conditions of the restoration areas and the extent of success of the restoration activities. If needed, the annual reports will identify specific actions to be taken to improve the conditions within the restoration areas. 5.1 Vegetation Monitoring Vegetation will be monitored prior to and following restoration activities. Sampling will involve canopy, sub-canopy, and ground cover strata along monitoring transects established within the restoration areas. Sampling transects and methodology for the Page 1013 of 5261 Passarella & Associates, Inc. 7 of 10 #05CEM1481 Revised 10/18/19 baseline, time-zero, and annual reports will utilize identical methods of data collection from identical sampling stations. See Sheet 7 of the attached drawings for the proposed monitoring transect locations within the farm field restoration area. Additionally, two monitoring transects within the exotic treatment restoration areas and three transects within the road grade removal area will be installed and monitored. Forested habitats, canopy, and sub-canopy vegetation species will be monitored within 20 x 50-foot plots established along the monitoring transects. Species richness and visual estimate of percent cover will be calculated for canopy and sub-canopy strata. For forested and herbaceous habitats, ground cover will be monitored using the point frame method. Point frames will be sampled at approximately 25-foot intervals along each monitoring transect. Each point frame consists of a one-meter square wire grid with 25 cross points. Any plant species directly below a cross point will be recorded, including bare ground. Each cross point represents four percent of the square meter. Water depths will also be recorded at each sampling station. For each sampling station, identified species will be listed and percent cover computed and discussed. 5.2 Wildlife Monitoring Regular observations of wildlife will be made during the monitoring event by qualified ecologists. Observations will consist of recording evidence and sign of wildlife (i.e., direct sightings, vocalizations, burrows, nests, tracks, droppings, etc.). 5.3 Fish and Aquatic Macroinvertebrate Monitoring Qualitative sampling of fish and aquatic macroinvertebrates will be conducted using a standard D-frame aquatic dip net with mesh size of one millimeter. Sampling will be conducted along vegetation monitoring transects with a minimum of two centimeters of standing water. The collector will work the net vigorously within the vegetation, open water, and surficial bottom sediments. Net contents will be placed in a white pan and sorted with forceps. Hard substrate, if any, will also be examined for the presence of aquatic macroinvertebrates. Sampling will continue until no new species are encountered for ten minutes. Sample size and collection times will not exceed 200 organisms or one hour, respectively. Samples will be preserved in alcohol, returned to the laboratory, and identified to the lowest taxonomic level possible. When possible, fish will be identified in the field and released. 5.4 Photographic Documentation Permanent fixed-point photograph stations will be established along each vegetation monitoring transect to provide physical documentation of the condition and appearance of the restoration area, as well as any changes taking place within it. Monitoring photographs will accompany vegetation data in each report. Locations of photograph stations will remain the same throughout the duration of the monitoring program. Page 1014 of 5261 Passarella & Associates, Inc. 8 of 10 #05CEM1481 Revised 10/18/19 5.5 Monitoring Wells and Rainfall Data Hydrologic monitoring for the farm field restoration area will include the installation of two continuous recording monitoring wells. These monitoring wells will be set to record hydrologic data on a daily basis. Monitoring well data will be downloaded once every three months and will be summarized in the annual monitoring reports along with available rainfall data for the area. 6.0 MONITORING REPORTS Annual monitoring reports will be submitted to the County documenting the success of the restoration program and general condition of the restoration areas. The monitoring reports will include the following information: • Brief description of restoration and management activities performed since the previous report along with a discussion of any modifications to the restoration or maintenance program • Brief description of anticipated restoration and maintenance work to be conducted over the next year • Results of quantitative vegetation monitoring • A list of observed wildlife species • A list of fish and aquatic macroinvertebrates collected • Monitoring photographs taken at photograph stations • Monitoring well data for the farm field restoration areas and available local rainfall data 7.0 WORK SCHEDULE The proposed restoration activities will be completed in phases in accordance with the work schedule outlined in Table 3. Table 3. Work Schedule Phase Restoration Area Restoration Activity Estimated Time to Complete Activity¹ 1 Nos. 2 and 3 Restoration through exotic treatment 1 month 2 Road Grade South of Oil Well Road Flow-way restoration through removal of road grade 6 to 8 months² Page 1015 of 5261 Passarella & Associates, Inc. 9 of 10 #05CEM1481 Revised 10/18/19 Table 3. (Continued) Phase Restoration Area Restoration Activity Estimated Time to Complete Activity¹ 3 No. 4 (Pinch Point Field) Farm field restoration 8 to 12 months² 4 Pinch Point Farm Road Flow-way restoration through removal of road grade 1 to 2 months² ¹Estimated time is for restoration activities listed and does not include semi-annual and annual maintenance events. ²If planting required after two years, estimated time to complete planting activities is an additional 18 months. 8.0 SUCCESS CRITERIA The following section describes the success criteria for each of the proposed restoration activities. Upon achievement of the success criteria as described for each restoration activity, the corresponding restoration implementation Stewardship Credits shall be available for use by the Owner. 8.1 Flow-Way Restoration The following are the success criteria for flow-way restoration: (1) removal of the old road grade designated for removal as part of the SSA 14 restoration plan will be completed; (2) removal of road grade south of Oil Well Road will be completed; (3) removal of the pinch point farm road will be completed; (4) if two years after removal of the road grades natural recruitment of native vegetation within the footprint of the old road grades has not occurred, then planting/seeding will be completed; and (6) the restored areas will be free from exotic vegetation immediately following a maintenance activity and will consist of no more than five percent cover for exotic species. A total of 10,264.5 Stewardship Credits shall be available upon the achievement of these success criteria. 8.2 Farm Field Restoration The following are the success criteria for farm field restoration: (1) removal of farm field berms and backfilling ditches will be completed; (2) roller chopping of farm fields will be completed; (3) herbicide treatment of farm fields will be completed; (4) disking of farm fields will be completed; (5) as-built survey of graded elevations will be completed; (6) if after two years natural recruitment of native vegetation has not occurred, planting/seeding will be completed; and (7) the farm field restoration areas will be free from exotic vegetation immediately following a maintenance activity and will consist of no more than five percent cover for exotic species. A total of 416.9 Stewardship Credits shall be available upon the achievement of these success criteria. Page 1016 of 5261 Passarella & Associates, Inc. 10 of 10 #05CEM1481 Revised 10/18/19 8.3 Restoration through Exotic Treatment The following are the success criteria for restoration through exotic treatment: (1) initial eradication of exotic and nuisance vegetation will be completed in treatment areas; and (2) the treatment areas will be free from exotic vegetation immediately following a maintenance activity and will consist of no more than five percent cover for exotic species. A total of 32.6 Stewardship Credits shall be available upon the achievement of these success criteria. Page 1017 of 5261 AS1Engineering Firm Number: 31200Surveying Firm License: LB8569Collier County7400 Trail Boulevard, Suite 200Naples, FL 34108P: 239.597.3111F: 239.566.2203EMPLOYEE OWNEDCLIENT FOCUSEDTarpon Blue CE, LLCRESTORATION & GRADING PLANSPHASE 1 - EXISTING & AS-BUILT139049Pinch Point Existing Farm FieldFARM ROAD REMOVAL PLANxxxx13904ME02-ASB.dwg - AS1 ROP -12/16/25NN,Page 1018 of 5261 13620 Metropolis Avenue Suite 200 Ft. Myers, FL 33912 Phone (239) 274-0067 Fax (239) 274-0069J:\2022\22tbc3940\GIS\2026\Meetings_and_Field_Maps\Old Roadbed Maps 010625\Old Roadbed Maps 010625.aprx 1/7/2026 8:51 AM reidfDRAWING No. SHEET No. REVISIONS DRAWN BYDATE DESIGNED BY REVIEWED BY DATE DATE DATE OIL WELL RDOIL WELL RD 641E1 514 630E3 625E3 631E3 618E3 621E1 74017407401 641E3 434E2 641E1 411E2 641E2 641E1 641E1 618E4 4221 641E1 411E2 617E3 621E1 630E2 621E2 618E1 411E1 625E3 630E2 630E1 618E1 747 624E1 630E2 624E2 618E3 625E1 630E3 625E2 618E2 630E2 630E1 625E3 514 618E1 617E1 630E1 8146 8146 8146 621E2 621E1 214 LEGEND SSA 15 OLD ROADBED OLD ROADBED REMOVAL E-3 05CEM1481 OLD ROADBED REMOVAL AREAS SSA 15 12/30/15K.C.P. 12/30/15K.C.P. 12/30/15H.H. 0 250 500 Feet ¶ NOTES: AERIAL PHOTOGRAPHS WERE ACQUIRED THROUGH THE COLLIER COUNTY PROPERTY APPRAISER'S OFFICE WITH A FLIGHT DATE OF DECEMBER 2021. COUNTY INFORMATION AND ROADWAY NETWORS WERE ACQUIRED FROM THE FLORIDA GEOGRAPHIC DATA LIBRARY WEBSITE. SSA 15 03/03/22Revised FLUCFCS MAP EY ap extents Page 1019 of 5261