Community and record history

Tarpon Woods through time

The neighborhood, golf-course landscape, watershed, property records, and permit proceedings have different histories. This page keeps them distinct.

Record links last checked: .

Open the dated permit timeline
Media note: The historic federal maps shown below have a verified public-record source chain. Other museum images, brochure scans, drone photography, deed screenshots, meeting images, and property-condition photos remain out of public files while source credit, privacy, and republication rights are reviewed.

Community landscape

Tarpon Woods residents describe a long-standing golf-course and neighborhood landscape with ponds, trees, open areas, homes, and Brooker Creek watershed connections. Those community descriptions provide context, but individual historical claims still require a dated primary source.

Pinellas Lake Tarpon watershed · 2025 SWFWMD SWIM Plan

Property and permit record

Parcel, deed, land-use, zoning, title, and permit-boundary questions must be resolved through the controlling records. Historical screenshots are research leads, not substitutes for current title, planning, survey, or County records.

Pinellas County GIS applications · Applications on This Land

Michelle Hollidge’s research trail, independently checked

The 1847 survey and later federal quadrangles

Longtime resident advocate Michelle Hollidge directed SWFWMD to pages 65–67 of the official 2005 Tarpon Woods Drainage Improvements application package. We retrieved that package from SWFWMD Application 57947 / ERP 30028.000 and confirmed that those pages reproduce an 1847 General Land Office township plat and federal quadrangle sheets labeled 1944 and 1970.

Open the 2005 package at page 65
What these maps can and cannot establish: They are strong evidence of what surveyors and federal mapmakers depicted at particular times. They do not, by themselves, establish today’s wetland jurisdiction, ordinary high-water line, floodway, property boundary, soil condition, or the precise predevelopment hydroperiod. The 1847 symbols and handwritten notes require expert interpretation together with the original field notes, modern elevations, soils, aerials, and a current wetland delineation.
1847 General Land Office plat for Township 27 South, Range 16 East, reproduced in the 2005 SWFWMD Tarpon Woods drainage application
1847 GLO township plat. Section 34 is along the bottom row. The plat depicts pine symbols and separately patterned low or wet features, but it is not a modern wetland delineation. Source chain: federal survey reproduced at SWFWMD package page 67.
Federal quadrangle map labeled 1944 showing Lake Tarpon, Brooker Creek, and Section 34, reproduced in the 2005 SWFWMD record
Quadrangle labeled 1944. This regional sheet predates the golf course and neighborhood. The legend, scale, and mapmaking conventions must control any interpretation. Source: SWFWMD package page 66.
Federal quadrangle map labeled 1970 showing the Tarpon Woods golf course area, Lake Tarpon, and Brooker Creek, reproduced in the 2005 SWFWMD record
Quadrangle labeled 1970. The sheet shows the golf-course area and Brooker Creek setting near the beginning of modern development. Source: SWFWMD package page 65.

What the historic record supports

The 1847 plat is consistent with a landscape containing both pine-dominated uplands and mapped wet or low features across the township. The later quadrangles document changing roads and development around Lake Tarpon and Brooker Creek. Together they justify requiring the applicant to explain, feature by feature, which areas it calls restoration, enhancement, creation, preservation, or upland supporting habitat.

What remains unresolved

The maps do not support the absolute statement that no wetlands ever existed anywhere in the present project area. Nor do they prove that every present wetland is natural or previously unaltered. SWFWMD should require a georeferenced overlay, original GLO field-note analysis, historic-aerial interpretation, soils and elevation evidence, and a current surveyed wetland line before accepting a “restoration” baseline or awarding credits.

BLM General Land Office records · USGS topoView · Map-source notes

Official adjacent-area environmental history

FDEP's PATS_127253 archive documents a different, earlier project east of Tarpon Woods Boulevard

The names in this archive overlap with Tarpon Woods history, but the record must not be confused with the present golf-course parcels or mitigation-bank applicant. FDEP labels the facility “EAST OF TARPON WOODS BLVD.” Our review did not locate folio 34-27-16-00000-140-0000 or 34-27-16-00000-110-0400 on the reviewed sheets.

Open the official source records

1986: several names describe the same evolving east-side development record

The official plans use the names Tarpon Woods Estates I, Ridgewood, and Woodridge Lakes. They document historical development, drainage, and mitigation planning in the broader Tarpon Woods area east of the boulevard. The changing names make this file useful for tracing older references that might otherwise look unrelated.

Limits: the plans identify different historical parties and do not establish work on today's golf-course parcels, a present wetland line, current ownership, or any conduct by the current applicant.

1987–1995: a wetland-fill permit and later agency performance concerns

FDEP permit 521272533 was issued May 29, 1987 and expired May 29, 1992. The file describes 0.75 acre of wetland fill for Bridlewood at Tarpon Woods and required 1.46 acres of forested-wetland mitigation. It names First Florida International as permittee and gives 800 Tarpon Woods Boulevard as its address.

An August 3, 1995 FDEP memo reports that an inspection found less than half of the required mitigation area had been created and much of the created area was herbaceous. The file also discusses an earlier warning and permit transfers; a separate memo says Parkwood performed the development.

Limits: those observations concern that older project and the conditions seen then. They do not prove present conditions, current-property work, a current mitigation failure, or wrongdoing by today's applicant.

Why publish this limited history: it shows that wetland fill, mitigation acreage, monitoring, transfers, and ecological performance have been part of agency review in the broader Tarpon Woods area for decades. It also shows why names and locations must be matched carefully. For Application 930235, SWFWMD should rely on current parcel-specific mapping, title evidence, baseline data, performance standards, and monitoring—not assume that an adjacent historical file proves or disproves anything about the proposed bank.
Evidence review

What Michelle’s filing adds to the public record

Michelle Hollidge’s 42-page submission is now itself part of SWFWMD’s official permit file. That establishes receipt and preserves its questions for review. It does not automatically turn every statement in the packet into an agency finding, so we checked the strongest points against earlier permit documents and original government sources.

Read the official-record filing

Corroborated source trails

  • The historic-map exhibits are in SWFWMD Application 57947 / ERP 30028.000.
  • The prior applicant-retained Phase I environmental assessment identified long-term golf-course chemical use as a business environmental risk and stated that soil and groundwater analysis and a soil-mitigation plan may be required before a land-use change.
  • EPA says MSMA is an organic arsenical, can convert to inorganic arsenic in soil, and may not be used in Florida except on cotton in twelve named counties.
  • EPA mitigation-bank guidance calls for scrutiny of contamination potential, floodplain goals, adjacent land uses, significant existing habitat, technical risk, financial assurances, contingencies, and performance-linked credit release.
  • Florida Rule 62-342.700 expressly addresses financial responsibility for both construction/implementation and perpetual management.

Material questions, not settled facts

  • Whether the applicant has demonstrated the exact real-property interest required for every acre in the proposed bank and conservation easement.
  • How Pinellas County’s wetland-buffer code applies to each proposed wetland edge; the code’s 50-foot standard is not automatically a 50-foot setback around the entire bank perimeter.
  • Whether the applicant’s credit acreage, planting density, cost estimate, release schedule, and current survey reconcile line by line.
  • Whether historic drainage infrastructure and modeled flood behavior remain compatible with the current design.
  • Whether existing wetlands or already-functioning habitat are being assigned only the incremental credit permitted by the governing assessment method.

Claims requiring a final primary record

  • The existence, scope, and final outcome of the reported FDACS Target 6 Plus investigation.
  • Any conclusion that the property is contaminated; testing is needed.
  • Any conclusion that the entire project area was historically all upland or all wetland.
  • Any claim that the project will worsen or improve flooding without current signed-and-sealed modeling.
  • The presence and current legal status of each listed wildlife species; sightings, agency classifications, and survey dates must be checked species by species.
Our demand to SWFWMD: Resolve these items in writing before credit release or construction authorization. Where a prior applicant document conflicts with the current narrative, require the applicant to identify the conflict, state which version it relies on, provide the original supporting data, and explain the correction under professional certification.
The opposition’s full reading of Michelle’s filing

Why this filing strengthens the case to deny the application

Michelle Hollidge has worked beside this community from the beginning. Her August 26, 2026 submission does more than object in general terms: it connects the current application to older permit records, historic maps, environmental due-diligence material, flood concerns, property-control questions, mitigation-credit rules, financial-assurance requirements, and wildlife issues. Her filing gives SWFWMD a roadmap of questions it can no longer say were never raised.

Our position as the organized opposition is clear: when a commercial mitigation-bank application depends on uncertain boundaries, unresolved title and control, untested contamination concerns, unclear ground disturbance, inconsistent planting and cost figures, aggressive early credit release, and incomplete proof of long-term stewardship, the proper outcome is denial—not approval based on promises that essential details will arrive later.

1. The applicant must prove control of every acre

A mitigation bank is supposed to bind land and management obligations for the long term. That cannot rest on an approximate boundary, an incomplete transfer, or a promise to record documents later.

What the record raises

The current RAI response states that deed transfer and recordation remain in process. Earlier permit materials also generated questions about legal control over Parcel 3 and whether another owner or entity would need to participate. A survey can describe geometry, but it does not by itself prove present ownership, authority to encumber the land, or that every proposed bank acre will be inside the final conservation easement.

The public needs a parcel-by-parcel reconciliation showing record owner, applicant, legal interest, bank acreage, easement acreage, exclusions, access rights, existing encumbrances, and the document that authorizes each obligation.

Why this supports denial

Credits should not be issued against land the applicant has not conclusively demonstrated it can control and permanently manage. If the final deed, title evidence, joinders, access rights, and recordable easement are not complete and internally consistent, SWFWMD cannot reasonably assure that the promised work and perpetual restrictions are enforceable.

Our demand: deny the application if complete legal control is not established before approval. Do not substitute a future permit condition for a prerequisite that determines whether the applicant can lawfully deliver the bank at all.

2. Existing wetlands and functioning habitat are not newly created improvements

The central accounting question is not simply how many acres fall inside the proposed boundary. It is what ecological function already exists, what measurable additional function the applicant will produce, and which portion—if any—is eligible for credit.

What must be reconciled

  • Existing wetlands and surface waters, including their current condition and regulatory status.
  • Existing floodway and floodplain functions that already convey or store water.
  • Existing tree canopy, soils, root systems, wildlife use, and upland support that already benefit adjacent wetlands.
  • Historic alterations such as golf-course grading, ponds, ditches, drainage works, and managed turf.
  • Each proposed restoration, enhancement, creation, preservation, and upland-support polygon.
  • The assessment score before work, the predicted score after work, and the incremental functional gain assigned to each polygon.

The opposition’s conclusion

The applicant should not receive credits merely for placing an existing wetland, existing floodway, or already-functioning upland inside a bank boundary. Preservation and upland-support credit may be available under governing rules in appropriate circumstances, but it must be justified as additional value—not assumed from acreage alone.

Our demand: one signed-and-sealed, georeferenced credit map and acreage table that lets any reviewer trace every tenth of an acre from existing condition to proposed action to claimed credit. Any unexplained overlap or double counting should be resolved against credit issuance.

3. Historic maps challenge an oversimplified ecological story

Michelle identified the 1847 GLO plat and the federal quadrangles labeled 1944 and 1970 in an older SWFWMD drainage file. Those maps matter because mitigation credit depends on a defensible baseline and a defensible explanation of what is being restored.

1847

The township plat depicts pine symbols and separately patterned low or wet features across the surveyed landscape. It does not prove that the entire modern project was upland or wetland. It does show that a blanket historical description is inadequate and that the original field notes deserve professional interpretation.

1944

The federal quadrangle predates the modern neighborhood and golf-course configuration. It provides regional context for Brooker Creek, Lake Tarpon, roads, and drainage features, but its scale cannot replace a current delineation.

1970

The later quadrangle shows the area near the beginning of modern development. Comparing it with later aerials and drainage plans can help distinguish natural features, golf-course modifications, and subsequent infrastructure.

Our demand: require the applicant to georeference these maps and the original GLO field notes against modern topography, soils, historic aerials, drainage records, and the current surveyed wetland line. If the applicant cannot demonstrate what condition is historic, what is altered, and what is presently functioning, SWFWMD should not award restoration credit on an assumed narrative.

4. Former golf-course soils must be tested before they are disturbed

Michelle’s filing connects the proposal to earlier environmental due-diligence material describing long-term golf-course chemical use as a business environmental risk. It also reports an unresolved investigation involving alleged Target 6 Plus use. Neither point proves contamination at Tarpon Woods—but together they make “no testing needed” an indefensible assumption.

What is verified and what is not

EPA identifies MSMA as an organic arsenical and explains that organic arsenic can transform into inorganic arsenic in soil. EPA also states that MSMA use in Florida is restricted to cotton in specified counties. Those general facts justify investigation; they do not establish that a particular product was applied here, at what rate, or that site soil exceeds any cleanup or disposal criterion.

The reported FDACS investigation must be resolved through its final agency record. Until then, the allegation should remain labeled as pending and unproven.

What testing must cover

  • Systematic background sampling across former tees, greens, fairways, roughs, maintenance areas, chemical storage or mixing areas, drainage paths, pond margins, and proposed work zones.
  • Targeted sampling wherever staining, stressed vegetation, storage history, or prior records identify a possible release.
  • Sampling at proposed planting locations and at intervals representative of the more than 60,000 proposed plants.
  • Depth intervals matching planting holes, root balls, ditch work, equipment rutting, grading, excavation, and any utility or monitoring installation.
  • Laboratory methods, detection limits, quality assurance, chain of custody, and comparison criteria identified before sampling.
  • Waste characterization, worker protection, dust and runoff controls, transportation requirements, disposal facilities, and certified costs if impacted soil is encountered.

5. The planting numbers, disturbance, and costs must agree

The proposal is described as avoiding earthwork while also relying on extensive planting and ditch-related restoration. More than 60,000 plants cannot be treated as if they enter the ground without holes, displaced material, equipment access, soil contact, and potential effects on roots, microorganisms, fungi, insects, soil structure, and water movement.

A conservative displacement example

At only one cubic foot per plant, 60,000 plants would create 60,000 cubic feet of planting-hole volume—about 2,222 cubic yards. Spread one foot deep, that volume covers approximately 1.38 acres. This is not a prediction of the final disturbed volume: small plugs may require less, while pines and larger container plants may require substantially more. It demonstrates why plant size, container size, hole dimensions, spacing, installation method, soil reuse, and excess-material disposition must be disclosed.

If displaced soil is spread nearby, the applicant must show whether finished elevations, flood storage, runoff paths, or wetland hydroperiods change. If removed, the applicant must identify characterization, transport, and lawful disposal.

Internal consistency

The reviewed response reportedly uses different pine densities in the work plan and cost estimate—75 per acre in one place and funding for 40 per acre in another—and contains an apparent Year 15 arithmetic problem. These may be correctable errors, but they directly affect ecological feasibility and financial assurance.

Our demand: a final planting plan showing species, quantities, sizes, spacing, exact polygons, installation details, replacement assumptions, survival standards, monitoring, access, and a professionally certified cost estimate using the same quantities. If the plants physically cannot fit, survive, or be funded as represented, the credit claim must be reduced or the application denied.

6. Credit release must follow performance, and perpetual promises must be funded

Mitigation credits may be sold to offset impacts elsewhere. Once those impacts occur, failure at the bank creates a public ecological liability. That is why credit release, corrective-action money, and perpetual management cannot depend on optimism about future cash flow.

The risk residents see

The response proposes releasing a substantial majority of credits before an interim ecological success level is demonstrated. Early credits may generate revenue before the most difficult biological and hydrologic results are known. If establishment fails, contamination raises costs, ownership changes, or the operator defaults, the remaining unsold credits may not finance correction.

A conservation easement restricts land use; it does not itself place cash in an account, hire a replacement manager, correct hydrology, replace failed plants, control invasives, or safely remove contaminated material.

The enforceable protection required

  • Financial assurance covering construction, implementation, monitoring, corrective work, and perpetual management.
  • An irrevocable instrument—such as an authorized trust, escrow, bond, letter of credit with standby trust, or stronger combination—that remains available after ownership or operator changes.
  • Certified costs with inflation, contingency, mobilization, professional services, testing, disposal, replacement planting, invasive control, storm recovery, and emergency work.
  • Clear draw conditions, replenishment requirements, replacement-manager authority, default remedies, and District access.
  • Credit releases tied to verified hydrologic and ecological performance, not merely document execution or elapsed time.

Our demand: no approval and no credit release until SWFWMD demonstrates that the public will not inherit the cost of failure.

7. Wildlife and flood risk require current, project-wide evidence

Old observations, limited surveys, and general habitat descriptions cannot answer what species use the property now or how the final work could affect nesting, foraging, movement, refuge, and flood behavior.

Wildlife

Require current seasonal surveys by qualified professionals across the complete proposed bank, access routes, staging areas, and management zones. The record should distinguish direct observations, suitable habitat, agency database records, survey dates, methods, weather, coverage, and limitations. Species-specific avoidance, buffers, timing restrictions, monitoring, and stop-work procedures should be enforceable conditions—not deferred suggestions.

Flooding

The FEMA regulatory floodway follows Brooker Creek through the broader landscape, and the neighboring pool review shows that even a small encroachment can trigger watershed-scale modeling and compensatory-storage questions. The applicant must overlay the effective floodway with every credit polygon and every proposed disturbance, demonstrate no rise or adverse impact under applicable standards, and obtain County and FEMA approvals where required.

Read the full floodway case study without leaving the site.

The opposition’s conclusion

SWFWMD should deny this application unless the applicant first closes every material gap

Michelle’s filing, the applicants’ own submissions, the prior permit history, and the public-source research do not describe a project ready for approval. They describe a proposal whose essential acreage, baseline, title, hydrology, floodway interaction, soil condition, planting feasibility, cost, wildlife protections, credit-release safeguards, and perpetual funding still require proof.

Residents should not be told to trust that these matters will be solved after approval. Mitigation credits can authorize damage elsewhere, and some environmental losses cannot be easily reversed. The burden belongs to the applicant now—not to neighbors after flooding changes, plantings fail, soil is disturbed, credits are sold, or the operator defaults.

We call on residents to oppose the application and on SWFWMD to deny it unless and until the applicant supplies complete, consistent, professionally certified, independently reviewable, and enforceable answers. If those answers cannot be produced during permitting, there is no reasonable basis to assume they will appear during decades of implementation and perpetual management.

Three separate mitigation-bank applications

The three filings share a project name and permit family, but their designs and procedural statuses are not interchangeable. Dates are repeated here only as a short orientation; the application comparison is the detailed record.

Compare the files
Conceptual / withdrawn

Application 889588 / ERP 47575.000

Filed March 1, 2024. SWFWMD issued an RAI and later clarification; the record contains responses, extensions, plans, and comments. The applicant withdrew it effective December 6, 2024, and SWFWMD acknowledged the withdrawal December 11.

Open first withdrawn record
Individual / withdrawn

Application 907654 / ERP 47575.001

Filed December 6, 2024 and withdrawn November 13, 2025. All 102 documents publicly listed in its SWFWMD viewer at retrieval show an applicant design proposing major excavation, pond and ditch filling, wetland creation, material export, a 172.59-acre easement, and a stated total of 79.57 potential credits. Its displayed 13.86- and 65.72-credit components sum to 79.58, a one-hundredth difference that may reflect rounding and requires reconciliation. SWFWMD’s September clarification said the file remained incomplete.

Limit: the retrieved viewer archive is not represented as SWFWMD’s entire internal file. Proposed quantities in a withdrawn application are not approved work, released credits, or proof of the current design.

Open second withdrawn record
Current / incomplete as verified

Application 930235 / ERP 47575.002

Filed November 14, 2025. SWFWMD issued a separate RAI dated December 14, 2025. A partial response, extension filings, and the August 26, 2026 response followed. Filing a response is not a completeness determination or approval.

Open current record
Why this matters: the middle application is the missing bridge between the early conceptual plan and today’s “no earthwork” account. SWFWMD should require a signed-and-sealed change matrix showing what happened to every excavation, fill, pond, ditch, pipe, access route, disposal plan, credit polygon, and conservation-easement boundary before it treats the current design as complete.

Historical materials under review

The repository preserves historical images and locally collected documents outside the public deployment tree. Before any return to the site, the owner should document source, creator, date, permission or license, required credit, edits, depicted people, sensitive details, and intended use.

Media review status

Help improve the record

Submit a source lead with enough information to verify it. Do not submit confidential records, expose another resident’s personal information, or represent a community submission as an official filing.

Submit a historical source lead
New official environmental-history records

FDEP's files confirm prior drainage work, a historical diesel discharge, and a current tank-account record at 1100 Tarpon Woods Boulevard

These records materially strengthen the demand for a current, site-specific environmental baseline. They do not establish that the property is contaminated today. They establish that a reviewer cannot responsibly dismiss testing, mapping, and contingency planning without first reconciling the official history.

Open the source shelf

1990–1991 fuel and soil record

FDEP's historical file contains an August 1990 notification reporting a diesel discharge detected through soil analysis/OVA-FID. A closure-report package received in March 1991 describes removal of gasoline and diesel underground tanks, excavation of approximately 80 cubic yards of soil with elevated field-vapor readings at the diesel pit, laboratory soil results below detection limits, a gasoline-pit groundwater sample slightly above the then-state benzene target, and a later nondetect result from one temporary monitoring well. Later correspondence identified closure-report deficiencies.

What it does not prove: these events do not establish current contamination, the present location or condition of every affected area, an open enforcement case, or an agency no-further-action determination. They identify precise historical areas and pathways that a current professional assessment should locate and evaluate.

Current tank-account snapshot

FDEP's DOPPLER cover report, run September 1, 2026 from data refreshed August 31, identifies facility 8624510 at the exact address as a fuel-user/non-retail facility with status “OPEN.” It lists one 550-gallon vehicular-diesel aboveground tank and one 550-gallon unleaded-gasoline aboveground tank as “In Service,” plus three other tanks as removed. Its current summary also states “No Compliance Activity Data Found,” “No Open AOCs Found,” “No Open Violations Found,” “No Discharges Found,” and “No Property Owner Information Found.”

Read the current fields correctly: “OPEN” is the storage-tank facility/account status, not a finding of an open contamination or enforcement case. Conversely, the current “No Discharges Found” field does not erase or resolve the separate 1990–1991 documents; it reports what the present DOPPLER summary displays. The report lists no property-owner information and cannot establish legal title, current soil or groundwater quality, a no-further-action decision, or the location of every historical condition. Its removed-tank inventory also differs from the 1991 consultant report, so each source must remain separate until FDEP or a qualified professional reconciles them.

Drainage work tied to Brooker Creek

FDEP construction-stormwater record FLR10BW24 reports 3.73 disturbed acres at the address and identifies “Brooker Creek Channel A (tributary to Lake Tarpon)” as receiving water. Later record FLR10MM29 reports 4.1 disturbed acres and identifies “BROOKER CREEK” as receiving water. The current facility reports list both records inactive.

What that means: these are historical construction-general-permit records, not mitigation-bank approvals or current hydrologic models. They are official evidence of prior exact-address disturbance and of the receiving-water connection that must be built into any credible baseline and cumulative-impact review.

Our demand: before SWFWMD accepts more than 60,000 plant installations, ditch work, equipment access, or any soil displacement, require the applicant to map every current and former tank, excavation, known discharge area, drainage-work footprint, maintenance or chemical-handling area, and proposed disturbance. Require a current Phase I update, appropriately scoped soil and groundwater sampling, a quality-assured sampling plan, worker and water-protection controls, lawful handling and disposal procedures, replacement-planting contingencies, and certified costs. If the applicant cannot demonstrate that the proposed work will avoid mobilizing contaminants and will succeed in the actual soil conditions, SWFWMD should deny the application.
Recorded-property checkpoints

The 2019 County waiver was limited to 3.40 acres; current assessor pages do not supply the missing deed citation

Two official record sets add important—but carefully limited—context to the applicant's title, survey, utility, and conservation-easement showing. Neither source substitutes for a complete current title chain.

Open the source records

2019: the County released specified rights only on a described 3.40-acre tract

Pinellas Clerk Instrument 2019338177, Official Records Book 20738, Page 2541, concerns County rights arising from an earlier agreement for golf-course management and maintenance, treated-effluent disposal, and a right of first refusal. The recorded waiver releases the specified rights only as to the 3.40-acre tract in Exhibit A. It expressly says the waiver applies to that tract and not to the remainder of the Golf Course Property.

The instrument also says the earlier agreement remains effective on the balance, including continued acceptance of treated effluent. The metes-and-bounds courses in the 3.40-acre Exhibit A appear again in Application 930235 title material as Parcel 3 (Fee Estate).

Limits: this is not evidence that the County released the stated rights over the entire golf-course property. The matching description is a document-reconciliation fact, not a title opinion, present-ownership determination, or conclusion about whether later recorded instruments changed any right.

2022 sale indexing: both folios point to the applicant, but the deed field is a placeholder

The Property Appraiser currently indexes both folios—34-27-16-00000-140-0000 and 34-27-16-00000-110-0400—to TARPON WOODS PROPERTIES LLC. Each page lists a February 3, 2022 unqualified sale for $1,650,000. Each also displays AAAAA/AAAA in the “Last Recorded Deed / Book-Page” field rather than an identifiable Clerk instrument and official-record book/page.

Limits: assessor ownership and sale indexing can guide research, but it is not a Clerk deed citation, title opinion, surveyed legal boundary, or proof of authority to place every project acre under a conservation easement. The applicant must supply the controlling recorded deed, current title evidence, and a parcel-by-parcel crosswalk to the survey, bank, credit, security, and conservation-easement boundaries.

Why this matters to the permit: SWFWMD should require the applicant to plot the 3.40-acre Exhibit A tract against the current Parcels 1, 2, and 3; identify which recorded County rights affect each remaining area; produce every later instrument on which it relies; and explain how those rights interact with access, reclaimed-water or treated-effluent obligations, perpetual management, and the proposed conservation easement. The District should not infer a whole-property release from a tract-specific waiver or infer a complete title chain from an assessor page whose deed field does not name the controlling instrument.