CAC Agenda 09/08/2011 R
CAC
MEETING
AGENDA
SEPTEMBER 8, 2011
COASTAL ADVISORY COMMITTEE (CAC)
THURSDAY, SEPTEMBER 8,2011 -1:00 P.M.
BOARD OF COUNTY COMMISSIONERS CHAMBERS
THIRD FLOOR, COLLIER COUNTY GOVERNMENT CENTER
3299 TAMIAMI TRAIL EAST, NAPLES
· Sunshine Law on Agenda Questions
· PUBLIC NOTICE
I. Call to Order
II. Pledge of Allegiance
III. Roll Call
IV. Changes and Approval of Agenda
V. Public Comments
VI. Approval of CAC Minutes
1. May 12,2011
2. June 9, 2011
VII. Staff Reports
1. Expanded Revenue Report
2. Project Cost Report
3. Clam Bay Marker Permit Update - USACE Letter
4. Beach Easement Executive Summary
5. Report on Clam Bay Water Quality
a. Backup Material
6. Long Range Fund Requests with FDEP
7. Captiva/Collier Combination Project
a. Additional Backup
8. Critical Erosion Designation for Clam Pass
9. Lee County Renourishment - Update
10. Wiggins Pass Straightening - Update
11. Fund 195 Spending Analysis
12. FEMA Fay Update and Revision Timing
13. Sensitivity Analysis
VIII. New Business
1. Collier Bay Dredging Approval
2. Conceptual Plan Approval - Marco South Renourishment
a. Backup Material
3. Catagory "A" Ordinance Changes
4. RFP Engineering Consultants
5. CEC Proposal for Marco South Beach Renourishment Design/Permitting
6. CEC Proposal for Construction, Addministration Collier Creek - $18,650
7. CEC Proposal for Processing JCP Application for Marco South
IX. Old Business
X. Announcements
1. Mr. Pires - 10-year Service Award
XI. Committee Member Discussion
XII. Next Meeting Date/Location
October 13,2011 Government Center, 3rd Floor
XIII. Adjournment
All interested parties are invited to attend, and to register to speak and to submit
their objections, if any, in writing, to the board prior to the meeting if applicable.
For more information, please contact Gail D. Hambright at (239) 252-2966.
If you are a person with a disability who needs any accommodation in order to
participate in this proceeding, you are entitled, at no cost to you, to the provision of
certain assistance. Please contact the Collier County Facilities Management
Department at 3301 East Tamiami Trail, Naples, FL 34112, (239) 252-8380.
Public comments will be limited to 3 minutes unless the Chairman grants
permission for additional time.
GAG September 8, 2011
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EXECUTIVE SUMMARY
Recommendation to review and re-approve the May 12, 2011 CAC Minutes with
revisions.
OBJECTIVE:
revisions.
To review and re-approve the May 12, 2011 CAC Minutes with
CONSIDERATIONS: At the June 9, 2011 CAC meeting the minutes of the CAC May
12, 2011 meeting was approved 7 to 0 with the following changes:
Page 4, paragraph 7, line 3 - from "Carried unanimously 7 "yes - 1 "no." to "Motion
carried 7 "yes" - 1 "no."
The following error in the minutes have been noted and need to be reviewed and re-
approved by the CAC vote:
On Page 4 of the May 12, 2011 minutes under 1. Reaulatorv and Permit
Compliance: Grant approval for "Beach Tilling" was added twice. The first one is
correct where approval was Second by Mr. Rios.
The following vote and approval was omitted from the minutes: Under.L
Reaulatorv and Permit Compliance: Mr. Pires moved to approve a grant request
in the amount of $30,000 for the "Biological Monitoring Collier County 90033."
Second by Mr. Moity. Carried unanimously 8-0.
FISCAL IMPACT: The Source of funds is from Category "A" Tourist Development Tax.
GROWTH MANAGEMENT IMPACT: There is no impact to the Growth Management
Plan related to this action.
LEGAL CONSIDERATIONS: This item has been reviewed and approved by the
County Attorney's Office and is legally sufficient for Board action. - CMG
RECOMMENDATION: To approve the May 12, 2011 minutes with the following
changes: 1) Striking the 2nd Grant approval for Beach Tilling; 2) Add - Mr. Pires moved
to approve a grant request in the amount of $30,000 for the "Biological Monitoring
Collier County 90033." Second by Mr. Moity. Carried unanimously 8-0.
PREPARED BY: Gail Hambright, CAC Accountant
GAG September 8, 2011
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MINUTES OF THE MEETING OF THE COLLIER COUNTY
COASTAL ADVISORY COMMITTEE
Naples, Florida, May 12,2011
LET IT BE REMEMBERED, that the Collier County Coastal Advisory
Committee, in and for the County of Collier, having conducted business
Herein, met on this date at 1 :00 P.M. in REGULAR SESSION at
Administrative Building "F", 3rd Floor, Collier County Government
Complex Naples, Florida with the following members present:
CHAIRMAN: John Sorey, III
VICE CHAIRMAN: Anthony Pires
Randy Moity
Jim Burke
Murray Hendel
Robert Raymond
Joseph A. Moreland
Victor Rios
Wayne Waldack (Excused)
ALSO PRESENT: Gary McAlpin, Director, Coastal Zone Management
Colleen Greene, Assistant County Attorney
Gail Hambright, Accountant
Dr. Michael Bauer, City of Naples
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Any persons in need of the verbatim record of the meeting may request a copy of the
video recording from the Collier County Communications and Customer Relations
Department or view online.
I. Call to Order
Chairman Sorey called the meeting to order at 1 :02 PM
II. Pledge of Allegiance
The Pledge of Allegiance was recited.
III. Roll Call
Roll call was taken and a quorum was established.
IV. Changes and Approval of Agenda
Gary McAlpin, Director, Coastal Zone Management
Mr. Rios moved to approve the Agenda. Second by Mr. Moreland. Carried
unanimously 8 - O.
V. Public Comments
None
VI. Approval of CAC Minutes
1. April 14, 2011
Mr. Raymond moved to approve the minutes of the April 14, 2011 Meeting.
Second by Mr. Burke. Carried unanimously 8- O.
VII. Staff Reports
1. Expanded Revenue Report - Gary McAlpin
The Committee reviewed the "Tourist Tax Revenue Report - FY 201 0 - 2011 "
updated through April 2011.
2. Project Cost Report - Gary McAlpin
The Committee reviewed the "FY 201 0/2011 TDC Category "A n Beach
Maintenance Projects" updated through May 6, 2011.
3. Backup Tallahassee Report
Gary McAlpin provided the following documents for information purposes:
. Letter to Hershel T. Vinyard, Secretary, Florida Department of
Environmental Protection dated April 5, 2011 - Re: "Collier County FDEP
Permitting Discussion. n
. Email string between himself and Jeff Littlejohn, Florida Department of
Environmental Protection dated April 29, 2011 - Subject: "WJPJ Channel
Dimension Comparison. "
. Letter to Mike Barnett, Bureau Chief, Florida Department of
Environmental Protection dated March 18,2011 - Re: "Wiggin's Pass
long- term inlet plan and permit application. n
GAG September 8,2011
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. Letter to Mike Barnett, Bureau Chief, Florida Department of
Environmental Protection dated April 13, 2011 - Re: "Wiggin's Pass
Telephone Conference April 5,2011 and Wiggin's Pass long-term inlet
plan and permit application memo dated 3/18/2011. n
He reported on a meeting he and Chairman Sorey had with Mr. Vinyard and
Governor Rick Scott.
Speakers
Nicole Johnson, Conservancy of Southwest Florida
Kathy Worley, Conservancy of Southwest Florida
VIII. New Business
1. Conceptual Design Update CP&E
Gary McAlpin provided the document "Draft - Collier County Conceptual
Renourishment Project Analysis n prepared by Coastal Planning & Engineering,
Inc. Boca Raton, FL - May 2011 for information purposes.
The Committee recommended the title of the study be renamed to identify the
project area as "Vanderbilt, Park Shore and Naples Beaches" (or similar
wording) as opposed to "Collier County. "
It was noted the document will be reviewed in a future meeting.
2. 19510 Year Plan
Gary McAlpin provided the document "TDC Category "A" 195 Fund
Projections" for consideration.
The Committee requested staffreview the "Interest Income" row under the
Revenue Category to ensure it is accurately depicted in the document.
Mr. Moreland moved to approve the "TDC Category "A" 195 Fund Projection"
document subject to the Committee's above request. Second by Mr. Pires.
Carried unanimously 8 - O.
3. Fiscal Year 11/12 Proposed Budget
Gary McAlpin provided the document "FY1l/12 -195 Fund Budget and
Analysis - Rev. 1 " dated May 12, 2011 for consideration.
Mr. Rios moved to approve the "FY11/12 -195 Fund Budget and Analysis-
Rev. 1 " dated May 12,2011 subject to the approvals in item VIIL4 (Grant
Funding). Second by Mr. Pires. Carried unanimously 8 - O.
4. Fiscal Year 11/12 Grant Applications
a. Backup Material
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Gary McAlpin provided the Executive Summary "Share TDC Category "A:
Grant Applications from the City of Naples, the City of Marco Island and
Collier County for FY-1l/12" dated May 12, 2011 and related backup
material for consideration.
Barry Williams, Director, Parks and Recreation provided a copy of an
email from himself to John Sorey dated May 02,2011 - Subject: "Sea Turtle
Monitoring" for information purposes. He provided an overview of the
Sea Turtle Monitoring Program.
Speaker
David Addison
The Committee approved the following grant requests from the
Executive Summary as listed below:
1. Re2ulatorv and Permit Compliance
Mr. Moreland moved to approve a grant request in the amount of $163,000
for the "Sea Turtle Protection Program - Collier County." Second by Mr.
Burke. Carried unanimously 7 'yes" -1 "no." Mr. Pires voted "no."
Mr. Pires moved to approve a grant request in the amount of $17,500 for the
"Beach Tilling - Collier County 081071." Second by Mr. Rios. Carried
unanimously 8 - O.
Mr. Pires moved to approve a grant request in the amount of $260,000 for
the "Physical Beach & Pass Monitoring Collier County Beaches - 90536."
Second by Mr. Moreland. Carried unanimously 7 'yes" -1 "no." Mr.
Hendel voted "no. "
The Committee requested staff, for budgetary planning purposes, prepare a
report for Committee review on prioritization of Coastal Zone Management
projects.
Mr. Pires moved to approve a grant request in the amount of $17,500 for the
"Beach Tilling - Collier County 081071." Second by Mr. Moity. Carried
unanimously 8 - O.
2. Planned Projects
Mr. Moreland moved to approve a grant request in the amount of $50,000
for the "Wiggin's Pass Maintenance Program - Engineering - 90522. "
Second by Mr. Burke. Carried unanimously 8 - O.
Mr. Pires moved to approve a grant request in the amount of $350,000 for
the "Emergency Truck Haul- Vistas at Park Shore - 88030" subject to its'
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being renamed "Truck Haul- Vistas at Park Shore - 88030." Second by
Mr. Hendel. Carried unanimously 8 - O.
Mr. Pires moved to approve a grant request in the amount of $600,000 for
the "FY12/13 Beach Design and Permit with HS Solutions - 80096" subject
to its' be renamed "FY11/12 Beach Design and Permit with HS Solutions-
80096." Second by Mr. Hendel. Carried unanimously 8 - O.
Mr. Moity moved to approve a grant request in the amount of $300,000 for
the "MI Renourish Deign & Permit with BW Solutions - 80166." Second by
Mr. Rios. Carried unanimously 8 - O.
Mr. Moity moved to approve a grant request in the amount of $20,000 for
the "Laser Grading North Marco Beach (R133-141)." Second by Mr. Rios.
Carried unanimously 8 - O.
Mr. Rios moved to approve a grant request in the amount of $25,000 for the
"Tigertail Beach Refurbishment." Second by Mr. Burke. Carried
unanimously 8 - O.
3. Beach Maintenance
Mr. Moreland moved to approve the following grant requests ($341,950
total):
. Beach Maintenance - Collier County/Marco Island - 90533 -
$135,100
. Beach Maintenance - City of Naples - 90527 - $76,850
· Vegetation Repairs/Exotic Removal- County Wide - 90044 - $75,000
· Naples Pier Annualized Repair & Maintenance - City of Naples -
90096 - $55,000
Second by Mr. Hendel. Carried unanimously 8 - O.
4. Administration Fees
Mr. Pires moved to approve thefollowing grant requests ($727,500 total):
. Fund 195 and 183 Administration - Collier County - 90020 - $510,500
· Indirect Administration Costs - $107,700
. Tax Collector Fees (2.5%) - $109,300
Second by Mr. Moreland. Carried unanimously 8 - O.
5. Other Expenses
Mr. Rios moved to approve the following grant requests ($20,843,600):
· Renourishment and Emergency Reserves - $17,000,000
. Revenue Reserve (5%) - $218,600
. Category D Pier Reserve - $79,000
· Reservefor Contingency Totals - $146,000
. Reservefor FDEP Reimbursement- $3,400,000
Second by Mr. Raymond. Carried unanimously 8 - O.
CAC September 8, 2011
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5. Summer Schedule
Gary McAlpin provided the Executive Summary "Determine summer schedule
for CAC Meetings" dated May 12,2011 for consideration.
Mr. Rios moved to cancel the regularly scheduled July meeting of the Coastal
Advisory Committee. Second by Mr. Burke. Carried unanimously 8 - O.
6. Chair and Vice-Chair
Gary McAlpin provided the Executive Summary "Election of Chairman and
Vice-Chairman" dated May 12,2011 for consideration.
Mr. Hendel moved to appoint John Sorey, III as Chairman and Tony Pires as
Vice-Chairman of the Coastal Advisory Committee. Second by Mr. Burke.
Carried unanimously 8 - O.
IX. Old Business
None
X. Announcements
The Clam Bay Stakeholders will meet on May 17, 2011.
XI. Committee Member Discussion
Mr. Moreland reported Commissioner Coletta will be touring Wiggin's Pass on
June 6, 2011.
Mr. Hendel reported he toured Wiggin's Pass.
XII. Next Meeting Date/Location
June 9, 2011- Government Center, Administration Bldg. F, 3rd Floor
*****
There being no further business for the good of the County, the meeting was
adjourned by order of the chair at 2:44 P.M.
Collier County Coastal Advisory Committee
John Sorey, III, Chairman
These minutes approved by the Board/Committee on
as presented or as amended
CAC September 8, 2011
VI-2 Approval of CAC minutes
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MINUTES OF THE MEETING OF THE COLLIER COUNTY
COASTAL ADVISORY COMMITTEE
Naples, Florida, June 9, 2011
LET IT BE REMEMBERED, that the Collier County Coastal Advisory
Committee, in and for the County of Collier, having conducted business
Herein, met on this date at 1:00 P.M. in REGULAR SESSION at
Administrative Building "F", 3rd Floor, Collier County Government
Complex Naples, Florida with the following members present:
CHAIRMAN:
VICE CHAIRMAN:
John Sorey, III
Anthony Pires
Randy Moity
Jim Burke
Murray Hendel (Excused)
Robert Raymond
Joseph A. Moreland
Victor Rios
Wayne Waldack
ALSO PRESENT:
Gary McAlpin, Director, Coastal Zone Management
Colleen Greene, Assistant County Attorney
Gail Hambright, Accountant
CAC September 8, 2011
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Any persons in need of the verbatim record of the meeting may request a copy of the
video recording from the Collier County Communications and Customer Relations
Department or view online.
I. Call to Order
Chairman Sorey called the meeting to order at 1 :02 P.M.
II. Pledge of Allegiance
The Pledge of Allegiance was recited.
III. Roll Call
Roll call was taken and a quorum was established.
IV. Changes and Approval of Agenda
Mr. Moreland moved to approve the Agenda. Second by Mr. Rios. Carried
unanimously 7 - O.
V. Public Comments
None
VI. Approval of CAC Minutes
1. May 12, 2011
Mr. Rios moved to approve the minutes of the May 12,2011 meeting subject to
the following change:
. Page 4, paragraph 7, line 3 - from "Carried unanimously 7 "yes - 1 "no."
to "Motion carried 7 "yes" -1 "no."
Second by Mr. Pires. Carried unanimously 7 - 0."
The Committee directed staff to prepare a sensitivity analysis for the purposes of
analyzing revenue reductions (-10%, -20% and - 30%) for the department and
place it on the agenda for their review.
VII. Staff Reports
Mr. Burke arrived at 1:10 p.m.
1. Expanded Revenue Report - Gary McAlpin
The Committee reviewed the "Tourist Tax Revenue Report - FY 201 0 - 2011"
updated through May, 2011.
2. Project Cost Report - Gary McAlpin
The Committee reviewed the "FY 201 0/2011 TDC Category A: Beach
Maintenance Projects" updated through June 1,2011.
VIII. New Business
The Committee determined to hear Items in the order as 4, 5, 2, 3 and 1.
CAC September 8, 2011
VI-2 Approval of CAC minutes
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4. Clam Bay Markers
a. Backup Material
Gary McAlpin presented the Executive Summary "Recommendation to endorse the
recommendation of the Clam Bay work group and the coastal installation and
maintenance of the Clam Pass/Bay markers; and authorize staff to proceed with
Florida Wildlife Commission (FWC); United States Army Corps of Engineers
(USACE); Florida Department of Environmental Protection (FDEP); and the United
States Coast Guard (USCG) permitting" dated June 9, 2011. The Executive
Summary contained 4 options for the installation and maintenance of the
proposed markers in Clam Pass/Bay.
He noted Ernest Wu, Seagate Homeowners Association has submitted an email
dated June 9, 2011 with related attachments on the Item- "Subject.' Clam Bay
Markers at today's CAC meeting" which has been distributed to the Committee.
Speakers
Noreen Murray, Pelican Bay Resident.
Ernie Wu, Seagate Homeowners Association.
Jeff Fridkin, Attorney for Seagate, Homeowners Association.
Steve Feldhaus, Pelican Bay Foundation.
Keith Dallas, Pelican Bay Services Division Board.
Mr. Burke moved to recommend the Board of County Commissioners
implement Option #1 for the installation and marking of the system: (as
follows).
1. Develop a written agreement between the four key stakeholders of Clam
Pass/Bay. The Pelican Bay Services Division, the Pelican Bay Foundation,
the City of Naples and Collier County would be parties to this agreement
with the following key points:
. Any changes to the permitted marking plan within Clam Pass/Bay
would need to be reviewed and concurrence obtained by three of
the four parties.
. Each party would share one-fourth of the installation costs and
maintenance cost for the next 10 years. Installation costs are
expected to be less than $20,000 and yearly maintenance is
expected to be less than $500.
. This agreement would last for 10 years and could be extended with
concurrence from each agency.
. Ifa dispute arose, an affirmative action of three ofthefour parties
would be required to resolve it. Dispute resolution would be by the
Chairman or designee of each respective agency.
. Coastal Zone Management would take the lead in processing the
permit modification for all 33 markers. The permit would be
modified and issued in Collier County's name only.
CAC September 8, 2011
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. Installation and maintenance of the 12 new markers in
Outer/Lower Clam Pass/Bay would be by Coastal Zone
Management. Maintenance of the 21 markers in Middle and Upper
Clam Bay would be performed and paid for by the Pelican Bay
Services Division. Informational signage on the beach at the mouth
of Clam Pass, at Clam Pass County Park, at the park walkway to
the beach, on the bridge, in the parking lot and at the kayak launch
site will be the responsibility of Coastal Zone Management. All
other poles and markers that are not permitted would be removed
from the system.
Second by Mr. Moreland. Motion carried 6 'yes" - 2 "no." Mr. Pires and Mr.
Rios voted "no. "
Mr. Pires stated he supports the Pelican Bay Services MSTU as the permittee.
Mr. Rios opposed on "principle."
5. Wiggins Pass
a. Backup Material
Gary McAlpin presented the Executive Summary "Recommendation to award
Contract #10-5572 for Wiggins Pass Channel Straightening - Design and Permitting
to Coastal Planning and Engineering (CP&E) and authorize the Chairman to execute
the standard contract after County Attorney approval in the amount of $177,489"
dated June 9, 2011.
Mr. Moreland, Chairman ofthe Wiggins Pass Subcommittee provided an
overview on the economic impact the pass has on County properties values and
related tax revenue.
Mr. Rios moved to recommend the Board of County Commissioners award
Contract #10-5572 for Wiggins Pass Channel Straightening - Design and
Permitting to Coastal Planning and Engineering (CP&E) and authorize the
Chairman to execute the standard contract in the amount of$177,489" dated June
9, 2011. Second by Mr. Burke. Motion carried 7 'yes" -1 "no." Mr. Pires voted
"no. "
Break: 2:30p.m.
Reconvened: 2:42 p.m.
2. H&M - Inlets Annual Monitoring
Gary McAlpin presented the Executive Summary "Recommendation to approve
Humiston & Moore Engineers proposal for Collier County Beaches and Inlets
Annual Monitoringfor 2011 and 2012 under Contract #08-5124 for a not to
exceed amount of $183,367.50" dated June 9, 2011.
Colleen Greene, Assistant County Attorney requested the Coastal Advisory
Committee recommend the contract be approved subject to approval by the County
CAC September 8, 2011
VI-2 Approval of CAC minutes
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Attorney's Office and Board of County Commissioners on its conformance with any
County Purchasing Policies or other legal requirements.
Mr. Rios moved to recommend the Board of County Commissioners approve
Humiston & Moore Engineers proposal for Collier County Beaches and Inlets
Annual Monitoringfor 2011 and 2012 under Contract #08-5124 for a not to
exceed amount of$183,367.50 subject to Ms. Greene's above request. Second
by Mr. Waldack. Carried unanimously 8 - O.
3. Conceptual Design Update-Coastal Engineering-Marco South Beaches
Gary McAlpin presented the Executive Summary "Provide the CAC with a
conceptual design update for Marco South beach along with the Emergency
Dredging at Collier Creek" dated June 9, 2011 copy of the slideshows "Collier Bay
Entrance Channel Emergency Dredging Update - Coastal Advisory Committee" and
"Marco Island South Beach Update - Coastal Advisory Committee" dated June 9,
2011 and provided an update on the projects.
1. Conceptual Design Update CP&E - Vanderbilt, Park Shore and Naples
Beaches
a. Conceptual Engineering Report
Gary McAlpin presented the document "Draft Collier County Conceptual
Renourishment Project Analysis" for information purposes.
Steve Keehn, P. E., Coastal Planning and Engineering presented a
slideshow "Collier County Conceptual Engineering Report" for information
purposes.
He noted page 9 of 19 of the "Collier County Conceptual Engineering
Report" outlines 4 alternatives (Alt. 1,2, 2A and 3) formajorrenourishment
of the beaches.
The Committee determined Alternative 2A or 3 would be the most optimal
for consideration.
IX. Old Business
1. Beach Funding Update
Chairman Sorey stressed the importance of maintaining beaches to a high
quality as visitor responses to questionnaires indicate a major reason people visit
the area is due to the high quality of the beaches.
X. Announcements
None
XI. Committee Member Discussion
None
XII. Next Meeting Date/Location
August 11, 2011 - Government Center, Administration Bldg. F, 3rd Floor
CAC September 8, 2011
VI-2 Approval of CAe minutes
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There being no further business for the good of the County, the meeting was
adjourned by order of the chair at 3:50 P.M.
Collier County Coastal Advisory Committee
John Sorey, III, Chairman
These minutes approved by the Board/Committee on
as presented or as amended
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DEPARTMENT OF THE ARMY
JACKSONVillE DISTRICT CORPS OF ENGINEERS
P.O. BOX 4970
JACKSONVillE, FLORIDA 32237-0019
CAC September 8,2011
VII-3 Staff Reports
1 of 1
REPLY TO
ATTENTION OF
July 25, 2011
Regulatory Division
Special Projects and Enforcement Branch
SAJ-1996-02789
Mr. J. Gary McAlpin, Director
Collier County Public Services Division
Coastal Zone Management
W. Harmon Turner Building, Suite 103
Naples, Florida 34112
Dear Mr. McAlpin:
I am referring to previous correspondence dated March 2, 2009, and September 10, 2009,
regarding the completion of the Clam Bay Restoration Management Plan required in Special
Condition 2 of your previously issued permit for the installation of culverts and dredging in
Clam Bay and the Gulf of Mexico. This letter further clarifies your requirement to comply with
Special Condition 2 and the installation of channel markers required in the Management Plan.
Recently we discussed the Division's efforts to install the required markers and comply with
Special Condition 2. Please provide photographs of the markers once installed and a drawing
showing the location of each of the installed markers. Once the photographs and drawings have
been provided as verification of your compliance, we will consider this matter resol ved. Your
cooperation in this matter is greatly appreciated.
If you have any further questions, please contact Cynthia Ovdenk by calling 239-334-
1975 x24.
Sincerely,
~~{;.~
Chief, Enforcement Section
Copy furnished:
Mr. Ernest Wu, via e-mail
CAC September 8, 2011
VII-4 Staff Reports
1 of 7
EXECUTIVE SUMMARY
Recommendation to obtain direction from the Board of County Commissioners on how to
proceed with an Easement Agreement for use between Collier County and Beachfront
Property Owners requiring the Property Owners to provide public beach access in
exchange for publically funded major beach renourishment, vegetation planting and dune
restoration to the subject property.
OBJECTIVE: To obtain direction on how to proceed with an Easement Agreement requiring
Property Owners to provide public beach access in exchange for publically funded major beach
renourishment, vegetation planting and dune restoration.
CONSIDERATIONS: Collier County is planning major beach renourishment, vegetation
planting, and dune restoration within the next two to four years. This project will be financed
using Tourist Development Taxes and/or a combination of grant money. This project will
directly affect and benefit the upland property owners as well as the residents and visitors of
Collier County.
The Board of County Commissioners discussed requiring a public use easement from the private
property owners at the May 11,2010 BCC meeting (Agenda Item 10(C)). This easement would
require upland property owners to agree and consent to allow full access to the beach seaward of
the vegetation line to Collier County residents and visitors as a condition of using public funds to
renourish private beach property, provide plantings on private property and restore the dunes on
private property.
On April 12, 2011, the Board directed staff to obtain input from the City of Naples and the City
of Marco Island on this approach (item lOG). A detailed proposed easement agreement as well as
the responses from the City of Naples and the City of Marco Island is attached. Both cities
recommend against the use of this proposed Easement Agreement.
The City of Naples felt that this approach was not necessary because previous easement
agreements have allowed renourishment to occur without incident; no access issues have
occurred within Naples; risk exists that the proposed easement agreement will not be executed by
property owners; failure to obtain easements will result in a less successful renourishment; little
risk exists that the public will be denied access within the City of Naples and funds/energy
required can be better used to challenge any restrictions to the public's access to the dry sand
beach.
The City of Marco Island believes that the benefit of this program is not significant enough to
justify the expenditure considering that the previous restoration efforts have not required this
effort and no problems on Marco Island have occurred.
It is expected that this easement agreement will require at least two years to execute county wide.
If a property owner refuses to execute this agreement, it is expected that no renourishment,
plantings or dune restoration will occur on that property. Additionally, FDEP is concerned about
GAG September 8, 2011
VII-4 Staff Reports
2 of 7
the structural stability of the beaches if excessive locations occur where no renourishment takes
place. FDEP declined to comment on how this might affect permitting.
ADVISORY COMMITTEE RECOMMENDATIONS: On December 9,2010 the Coastal
Advisory Committee recommended conceptual approval of this Easement Agreement (4 to 2
vote) and that the easement should terminate if the funding and the routine execution of beach
renourishment, vegetation plantings and dune restoration was to terminate.
At the Tourist Development Council February 28, 2011 meeting a recommendation not to
approve this Easement Agreement passed unanimously 9 to O.
FISCAL IMPACT: The Source of funds is from Category "A" Tourist Development Taxes,
State and/or Federal Grants.
It is anticipated that the cost to execute this easement for the Vanderbilt, Park Shore, Naples and
Marco Island beaches can be as high as $150,000. This cost would include researching property
data information, preparation of the easement documents, development of property owner letters,
telephone calls, meeting with owners and recording the documents. The cost to execute 10 and
20 year temporary construction easements in 2005 for the Naples, Park Shore and Vanderbilt
beaches was approximately $68,000.
GROWTH MANAGEMENT IMPACT: There is no impact to the Growth Management Plan
related to this action.
LEGAL CONSIDERATIONS: This item has been reviewed by the County Attorney's
Office, requires majority vote, and is legally sufficient for Board action. - CMG
RECOMMENDATION: To obtain direction from the Board of County Commissioners on how
to proceed with an Easement Agreement for use between Collier County and Beachfront
Property Owners requiring the Property Owners to provide public beach access in exchange for
publically funded major beach renourishment, vegetation planting and dune restoration to the
subject property.
PREPARED BY: Gary McAlpin, CZM Director
CAC September 8, 2011
VII-4 Staff Reports
3 of 7
City o:f M<1J1JI'CO 1[s]l<1J1uJ
": . , ,~\.,';:" (
May 18, 2011
(':F n!F; ,01;,
~.iAY ~~:j 2011
Mr. Leo E. Ochs, Jr.
County Manager, Collier County
3299 Tamiami Trail East
Naples. FL 34112-5746
Re: Draft Beach Renourishment Easement Agreement for City Council review
and consideration
Dear Leo:
At the regular City Council meeting on May 16,2011, Mr. Gary McAlpin provided
a presentation and explanation of the proposal concerning mandatory easement
agreements in connection with the renourishment projects undertaken by the
County and funded, in large part, through TDC dollars. Gary stated that the
Board of County Commissioners would welcome input from the City of Marco
Island as part of the process.
City Council took no formal action on the item, but directed me to summarize the
points and concerns raised by Council in their deliberations:
1. The reference to "allow full access to Collier County residents and visitors
alike to the beach" in the 4th "whereas" clause is confusing; though the
stated intent is lateral access, it could be construed to mean access to the
beach through upland private property;
2. For a one-time beach renourishment project, the granting of a perpetual
easement to the public is not proportional as a quid pro quo. Stated in
another way, there is no sunset of the easement in the event that beach
renourishment program ends.
3. The notice of damage to be provided by grantor in paragraph 5 is limited
to 7 days after actual knowledge of any damage; this is not a sufficient
period of time to act; further, notice should go to the office of Director,
Coastal Zone Management, but not to a named individual;
4. Overall, given the projected cost of the program for it implementation, the
City of Marco Island believes that the benefit is not significant enough to
support the expenditure; previous restoration efforts have not required
such efforts and no problems on Marco Island have been documented.
50 ]BaRJ Eagle Drive, Marco IslanJ, Florida. 34145
(239) 389-5000 FAX (239) 389-4369
www.entyofm.a.rcoisland.com
,
CAC September 8, 2011
VII-4 Staff Reports
4 of?
"""lIIIIIII
On behalf of the citi,?:ens of Marco Island and City Council, we appreciate the
opportunity to comment on this proposal in advance of a hearing before the BCC.
With kind regards,
~''''
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James C. Riviere, Ph.D.
City Manager
GAG September 8, 2011
VII-4 Staff Reports
50f7
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lULL BARNETT
MAYOR
May 5, 2011
Honorable Chairman and Board of County Commissioners
Collier County Government Complex
3299 Tamiami Trail East, Suite 303
Naples, Florida 34112
Dear Chairman Coyle and Board of County Commissioners:
By letter dated April 19, 2011, County Manager Ochs conveyed a request on behalf of
the Board of County Commissioners for input from the Naples City Council regarding a
proposed easement agreement to be utilized for beach renourishment projects. The
Naples City Council reviewed the proposed easement agreement, previOUS easement
agreements, and considered state law regarding access to the beach.
While City Council applauds the desire of the Board of County Commissioners to
preserve and protect the public's right of access to use and enjoy the beach, we
recommend that .the. Board continue to rely upon the 20-year easements previously
granted by upland property owners and, where necessary, utilize the same or similar
easement language contained in those agreements. Most of the 115 existing
easements granted by property owners within the City of Naples expire in the year
2024.
Our recommendation is based on the following:
1) The 2004 easement agreements have allowed beach renourishment projects.
2) Private property owners and the public have enjoyed the Naples beach without
major conflicts as to the public's right to use and enjoy the beach.
3) There is a fair risk that Collier County will not obtain many easement agreements
from upland property owners because of the proposed easement language.
4) Failure to obtain easements may result in a substantially less successful
renourishment due to the by-passing of properties that have not provided an
easement.
735 EIGHTH STREET SOUTH' NAPLES. FLORIDA 341 O::!(i7%
<;_.......'..;,;----,,,..._,~--,;'....'"""----.''''*.__..
TELEPHONE (::!3l)j 2: J IOI)() FAX '2.19, 2111010 CELL (239) 777 7952
EMAIL: MayorNaplcs:;. ""I.,om HOME FAX (239j 417 SRR3
CAC September 8, 2011
VII-4 Staff Reports
6 of?
Honorable Chairman and Board of County Commissioners
May 5, 2011
Page Two
5) There is relatively little risk that the public will be denied access to the dry sand
beach by a private property owner.
6) Funds used to acquire and record the new easement, and the considerable
energy that will be required of City and County staff and elected officials, may be
better used to challenge any restrictions to the public's access to the dry sand
beach.
We extend our gratitude to the Board of County Commissioners for their desire to obtain
Input from the Naples City Council, and we trust the views of the Naples City Council
will be considered.
?Jtt
Bill Barnett
Mayor
cc: City Council
Leo Ochs
Gary McAlpin
CAC September 8, 2011
VII-4 Staff Reports
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~
McAlpinGary
Subject:
Djfinlay@aol.com
Friday, May 06,2011 10:23 AM
OchsLeo; CoyleFred; FialaDonna; HillerGeorgia; HenningTom; ColettaJim; KlatzkowJeff;
collengreen@colliergov.net; McAlpinGary; RamseyMarla; WilliamsBarry;
bmoss@naplesgov.com; dlykins@naplesgov.com; dfnaplescouncil@aol.com
Beach Use/Concessions
From:
Sent:
To:
Dear Leo and Commissioners.
As you know the Naples City Council unanimously rejected the revised beach renourishment easement. The Mayor has
sent you a letter offering the reasons. However, because I have been very involved in beach issues, including this
particular one, I wanted to add a few personal comments.
1. Florida statute 161.141 should adequately protect public use of a renourished beach. This issue has been litigated to
the benefit of the public up to the US Supreme Court, making the revised easement irrelevant.
2. I would be very surprised if all, or any, of the beachfront hotels would sign the revised easement. If a hotel(s) did not
sign, I can't imagine the county refusing to place sand on the hotel beach, if for any reason, the beachfront hotels
contribute substantial funding (TDC) to the beach. And, if the hotels won't sign and they still get sand, you will be unable
to keep sand from others who refuse to sign. A real administrative, if not legal nightmare.
3. If am convinced Florida Statute 718 does not allow a condominium president or board to grant public use of a common
element property-the privately owned, high, beach. For example, my board of condominium could not authorize general
public use of our building's swimming pool or party room. The use of common elements is specified in the Declaration of
Condominium and that document can only be changed by a super majority vote of all condo owners. The only reason the
current easement has not created a controversy among condominiums is because it granted temporary use of the private
beach to construction workers, equipment, and the placement of sand. The revised easement is much different. It is a far
reaching document that formally grants general public use of common element property and I am convinced many
condominiums, along with the hotels, will not sign. Some single family homes may not sign as well.
In conclusion, there is simply no need to go down this road--especially for the city of Naples which has long been a cordial
if not a welcoming host of public beach use. Personally, I strongly support public use of the beach, from the vegetation
line to the water--but not with the revised easement.
On to one more beach matter. If we exclude the city of Naples and Marco Island populations from the county we find that
Collier County must supply beach access and facilities to about 300,000 unincorporated residents, with more to come in
the future. Yet despite that sizeable population, the county (not city) has woefully inadequate beach facilities. Just as
inadequate, the county has only one beach concession area, at Clam Pass. Unfortunately the prices at Clam Pass are
high and geared towards upper income, resort visitors--not the median income resident of the county. To get reasonable,
if not cheap, concession prices, a county resident must rely on the city of Naples, at either the pier or Lowdermilk
Park. This heavy reliance on city of Naples facilities needs to be tempered by a county concession facility at Vanderbilt
Beach. The county owes such a facility to its 300,000 residents, as well as adequate and properly located bathroom
facilities.
Thanks,
Doug Finlay
cc: Jeffery Klatzkow, Colleen Green, Gary McAlpin, Marla Ramsey, Barry Williams, Bill Moss, David Lykins
This communication is my own and not a request or an action from Naples City Councilor the Naples City Manager
1
CAC September 8, 2011
VII-5 Staff Reports
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ENTRIX
Shaping the Future
Clam Bay
Dissolved Oxygen Site Specific Alternative Criteria Development
DRAFT INTERIM REPORT
Prepared for the Pelican Bay Foundation
Cardno ENTRIX has prepared this brief draft summary of
concerning the development of Site Specific Alternative
this interim report is to keep the Pelican Bay Foundation
collection and analysis activities concerning this effor
discussions with the Florida Department of EnvirQI}
regulatory efforts to manage the Clam Bay resourt
viewed as draft since dissolved oxygen data collectio
en (DO) analyses to date
for Clam Bay. The purpose of
abreast of the recent data
provide ion that may be useful in
al Protection (FDEPtegarding water quality
e results presented inthi$summary should be
. ities a going.
FDEP has embarked on a revision of th 'da freshwater a rine dissolved oxygen criteria, but
does not expect to have draft rule langu for review until th d of 2011 at the earliest. Currently,
FDEP has a draft Technical Support Document (TSD) posted on its website regarding criteria revision
methodologies and is going through a Peer Review Comm' e process to determine the most
scientifically defensible criteria development process. arine waters, the proposed methodology is
the Virginian Province method and Clam Bay disso ygen data will be evaluated against this
methodology here to determine the current status m Bay DO relative to potential revised DO
criteria.
Vir
Dissolved Ox e
ment
survival,
defined as
larval
based~pproach that defines three DO concentration levels based on
of serl$itive estuarine species. The three DO concentrations are
1. Criterion
hour period woul
draft TSD sets this lev 2.9 mg/L.
2. Criterion Continuous Concentration (CCC) - the mean daily DO concentration above which
continuous exposure is not expected to result in unacceptable chronic effects. Using 12 native
Florida species, FDEP's draft TSD sets this level at 4.8 mg/L.
3. Final Recruitment Curve (FRC) - establishes the duration of exposures at DO concentrations
between the CCC and CMC which can be tolerated without causing unacceptable effects on total
larval survival.
DO concentration below which any exposure for a 24
acute effects. Using 23 native Florida species, FDEP's
The following graph illustrates these draft criteria:
CAC September 8, 2011
VII-5 Staff Reports
Ofl!:ardno
ENTRIX
Shaping the Future
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20
30
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Duration, days
Figure 1.
Potential revised marine D
Derivation of Dissolved
Waters
Technical Support Document:
in Florida's Fresh and Marine
Clam Bay continuous
the current status of
strategies at
potential criteria to determine
potential criteria implementation
DRAFT
Collier Cou has conductedthi'ee conti~.t.I9uS recorder deployments at 3 locations (Upper, Middle, and
Outer Clam Baylpuring 2011. Each deployment lasted between 4 and 6 days. The first deployment
occurred in March,l~~ril, the secOI'l~in May, and the third in August. A fourth location in Clam Pass is
included in the monitoril1g prograr)ll~owever logistical and data issues have hampered data collection
at this location and therefore thisSl(ltion is not included in this summary. A brief summary and
discussion of the data is presellt~din the graphs below.
Figure 2.
Figure 3.
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CAC September 8, 2011
VII-5 Staff Reports
oft!:ardno
ENTRIX
Shaping the Future
E3 Upper Clam Bay
o Outliers
Extremes
iddle Clam Bay
iers
s
III Bay
and each deployment during 2011
E3 Upper Clam Bay
o Outliers
* Extremes
E3 Middle Clam Bay
o Outliers
* Extremes
E3 Outer Clam Bay
o Outliers
* Extremes
Box plots showing a summary of all dissolved oxygen data collected at each station during
2011 compared to the potential CMC and CCC criteria.
<J
CAC September 8, 2011
VII-5 Staff Reports
Oft!:ardno
ENTRIX
Shaping the Future
As figure 2 indicates, expected seasonal differences in dissolved oxygen concentrations are occurring at
all stations with Clam Bay. Figure 3 shows Outer Clam Bay tends to have somewhat higher DO than
Upper or Middle Clam Bay. All stations and deployments show measurements that fall below the
current minimum DO criteria of 4.0 mg/L and the potential CMC of 2.9 mg/L. Median DO falls below the
current minimum criterion during the August deployment at Upper and Middle Clam Bay, but does not
exceed the potential CMC at any station.
Figure 4 shows the mean daily dissolved oxygen concentration at each station over each deployment
period. This figure provides a more accurate comparison of Clam Bay to the potential revised criteria.
The CMC is defined as the concentration below which exposure fora:;a4 hour period is expected to
result in acute effects. Therefore, individual measurements m elow this level, however, acute
effects are not expected unless this criterion is exceeded f ntir~..24 hour period. Similarly, the CCC
is defined as a mean daily DO concentration, so the calculi:ltElpJor each 24 hour period during
each deployment at each station. As the figure indic; ,uter Clam Bay ceeded the potential CCC
during at least one 24 hour period during the Apri ay deployments, Middle and Upper Clam
Bay had daily mean DO concentrations that fall be CCC criterion during ay and August
deployments. Outer Clam Bay and Upper Clam Bay daily DO CMC during at
least one 24 hour period during the s well. Although t average DO
concentration for a 24 hour period fell tions, not all measurements for that
day did, so the CMC was never actually period at any station.
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. Upper Clam Bay . Middle Clam Bay A Outer Clam Bay -CMC -CCC
Figure 4.
Mean daily dissolved oxygen concentrations at each Clam Bay sampling location during each
deployment compared to the potential CMC and CCC criteria.
CAC September 8, 2011
VII-5 Staff Reports
Oft!:ardno
ENTRIX
Shaping the Future
An important consideration in evaluating dissolved oxygen data is the time of day samples are collected.
Temperature, photosynthetic activity, and seasonality can affect the DO at any given time of day.
Figures 5, 6, and 7 show a summary of DO data collected over all deployments at each station by hour of
the day.
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- Outer Clam Bay -25th Percentile -75th Percentile
the
all deployments. Also shown is
...._.._-_..~_.~.._...._.._--.~_.._ m.._.....~...~._____..m.~~.~m...______m____M..._........___~_.......___._._..___.....____
o 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23
Hour of Day
- Middle Clam Bay -25th Percentile -75th Percentile
Figure 6. Middle Clam Bay dissolved oxygen data by hour of the day for all deployments. Also shown is
the 25th and 75th percentile distribution of measurements.
CAC September 8,2011
VII-5 Staff Reports
of Card no
ENTRIX
Shaping the Future
o 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23
Hour of Day
- Upper Clam Bay -25th Percentile -75th Percentile
lam Bay eX'p~r.iences diel swings in DO likely as a result of
Hg~er CJ~~.. Bay experience larger swings in DO than
of estuari~li>throughout Florida (and actually all waterbodies),
were ac criteria Implementation during the recent FDEP DO
The Peer Review Committee discussed potential
problems in ev~tl.lClting DO meas!.lrements any criterion because of the large daily swings in DO
and the time of daY!be sampler c ted the measurement. At the heart of the problem is the
acknowledgment thatJIQt all estuanes are monitored with continuous recorders and FDEP cannot
require all potential stakehgJder urchase or rent and deploy continuous recorders to monitor
compliance with the criteri refore, the Peer Review Committee suggested conducting an analysis
to determine if a certain time of day could be identified that most represented the daily average DO
concentration. When completed, only data collected during this time frame would be used to measure
compliance against the criteria. This would allow a determination of compliance based on an
instantaneous measurement.
Figure 7.
deployments. Also shown is
To this end, figures 5, 6, and 7 also depict the 25th and 75th percentile distributions ofthe data set for
each station. Using this distribution, the assumption is made that measurements within this range are
the most representative of the mean DO value over a 24 hour period. This analysis shows that, for all
CAC September 8, 2011
VII-5 Staff Reports
Ofl!:ardno
ENTRIX
Shaping the Future
stations, measurements collected between approximately 10 am and 3 pm on any given day provide the
best representation of the mean daily DO concentration.
On~oin~ Analvses Not Included In This Summary
The following bullet list presents some of the analyses and data compilation efforts that are ongoing.
This list is not comprehensive as new analyses are continually being explored.
· Clam Bay is being compared to continuous recorder from E Bay which has been identified
as a reference system by FDEP. Preliminary analysis ay continuous recorder dissolved
oxygen data over the same time period as Clam tes a very similar dissolved
oxygen regime between the two systems.
· Biological data from Clam Bay is being com
FDEP in developing the Virginian Provinc
· Clam Bay DO data is being analyzed with te perature, pH,salinity, con and nutrient
data identify the factors most affecting DO in CI~1'll
· An evaluation of the necessity eloping a SSA in Clam Bay given ongoing effort
by FDEP and, if so, what thresho include at supporting documentation is
necessary.
CAC September 8, 2011
VII-5 Staff Reports
Collier County: Numeric Nutrient 8of40
Criteria
Clam Bay - Development of Site-
Specific Alternative Water Quality
Criteria
V1
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PI!an Design Enable
Collier County- Numeric Nutrient Criteria
Clam Bay~ Development of Site-Specific Alternative Water Quality Criteria
CAC September 8, 2011
VII-5 Staff Reports
9 of 40
Table of contents
Chapter
Pages
2
1
1
3
4
4
6
6
7
9
10
11
12
16
16
16
17
20
22
23
24
Introduction
1. Introduction
1.1. Background Information
1.2. Report Objectives
2. Data Sources
3. Naples (WBID 3278Q)
4. Is Clam Bay "impaired" using existing FDEP criteria?
4.1. Fecal coliform bacteria
4.2. Dissolved Oxygen
4.3. Chlorophyll-a (Nutrient Criteria)
4.4. Sediment Characterization
5. Review of previous TMDL development
5.1. Salinity based Nutrient Targets
6. Techniques to derive numeric water quality criteria for Clam Bay
7. Proposed water quality criteria for Clam Bay
7.1. Is Clam Bay Healthy?
7.2. Proposed NNC normalized for salinity
7.3. Conceptual Management Responses
7.4. 2010 Clam Bay Management Assessments
8. Downstream Protective Values
9. Literature Cited
Tables
Table 1. Water quality comparison between Clam and Moorings Bay (2009-2011) 5
Table 2. Fecal coliform bacteria summary statistics (2009-2011) 7
Table 3. Dissolved oxygen correlation with potential causative parameters 8
Table 4. Dissolved oxygen statistics for four WBIDs in Southwest Florida (from Atkins 2011) 8
Table 5. Quarter and annual average chlorophyll-a values for Clam Bay (2009-2011). 9
Table 6. Chlorophyll-a correlation with nutrients and secchi depth. 10
Table 7. Summary of DO Monitoring Data in the Verified Period for Hendry Creek, WBIDs 3258B and
3258B1 (Table 2.2 from Hendry Creek TMDL, FDEP 2008). 11
Table 8. Conductivity (f..IM) summary statistics for Estero Bay wetlands, Hendry Creek (Freshwater) and
Hendry Creek (Marine). 12
Table 9. Comparison of expected total nitrogen based on Estero Bay wetland relationship with average
conductivity with Hendry Creek TMDL target TN and Average TN. 16
Table 10. List of benthic organisms identified in Clam Bay (Conservancy of Southwest Florida 2010). 16
Table 11. Conductivity (f..IM) summary statistics for Clam Bay and Estero Bay wetlands 18
Table 12. Comparison of expected TN and TP based on Estero Bay wetland relationship with
average conductivity and average TN and TP. 19
Table 13. Comparison of TN and TP screening criteria, Hendry TMDL targets, Clam Bay proposed
NNC and Clam Bay average. 20
Table 14. Minimum, median and maximum proposed DPV TN and TP concentrations for Charlotte
Harbor estuary compared to proposed Clam Bay DPV values. 23
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Figures
Figure 1. Upper, Inner, and Outer Clam Bay are all part of the Clam Bay system. 1
Figure 2. Proposed revision dividing Clam and Moorings Bays into separate WBIDs. 5
Figure 3.Relationship between color and dissolved oxygen in the Fakahatchee Strand (WBID 3278G;
p<0.05)(from Atkins 2011) 9
Figure 4. Location of sediment cores collected in Clam Bay. 10
Figure 5. Location map of Estero Bay Wetlands (WBID 3258A), Hendry Creek (Freshwater) (WIBD
3258B), and Hendry Creek (Marine) (WBID 3258B1). 12
Figure 6. Kruskal-Wallis comparison of medians for conductivity values in Estero Bay wetlands (EBW),
Hendry Creek (Freshwater) (HCF) and Hendry Creek (Marine) (HCM). 13
Figure 7. Diagram of salinity distribution patterns along an estuary from the riverine (freshwater) input to
the Gulf (Ocean). 13
Figure 8.Significant correlations between salinity and total nitrogen (mg/L) were found for the
Hillsborough River, Sarasota Bay, Charlotte Harbor and Estero Bay Wetlands. Graphs shown with
best-fit line and 95% prediction limits. 14
Figure 9. Expected, upper, and lower (95 percent prediction limits) total nitrogen concentration for Estero
Bay Wetlands based on the average conductivity. 15
Figure 10. Expected total nitrogen concentration for Hendry Creek (Marine) based on the average
conductivity using the Estero Bay Wetland best-fit equation with 95 percent prediction limits. 15
Figure 11. Mann-Whitney comparison of medians for conductivity values in Clam Bay and Estero Bay
wetlands (EBW). 18
Figure 12. Clam Bay potential TN target based on Estero Bay Wetlands regression and Clam Bay
salinity with 90 percent prediction limits. 19
Figure 13. Clam Bay potential TP target based on Estero Bay Wetlands regression and Clam Bay
salinity with 90 percent prediction limits. 20
Figure 14. Clam Bay conceptual water quality flowchart 21
Figure 15. Management response matrix using outcomes from both TN and TP evaluation. 22
Figure 16. Management response actions in response to various outcomes. 22
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1. Introduction
1,1. Background Information
1.1.1. Clam Bay
Clam Bay is an important natural feature in Collier County. The Clam Bay system consists of three tidally
influenced lagoons: Upper, Inner and Outer Clam Bays (Figure 1). Associated with the increased
development of Collier County, there has been concern among the public that Clam Bay might have been
adversely impacted by environmental pressures that typically accompany population growth. In its historical
configuration, Clam Bay would have received fresh water discharges mostly via small tidal creeks and
groundwater inflow. Watershed development most likely increased both the amount of freshwater discharged
into Clam Bay due to an increase in stormwater runoff, as well as loads of total suspended solids, nitrogen,
and phosphorus (PBS&J, 2008).
Figure 1.
Upper, Inner, and Outer Clam Bay are all part of the Clam Bay system.
Inner Clam Bay
Upper Clam Bay
Outer Clam Bay
The Clam Bay system was impacted in the 1950s by the construction of two roads; Vanderbilt Beach Road
to the north and Seagate Drive to the south. Historically, Clam Bay was connected to the Gulf of Mexico
indirectly via Wiggins Pass to the north and Doctor's Pass to the south, as well as its direct connection via
Clam Pass. Outer Clam Bay temporarily lost its historic connection to Moorings Bay (located to the south) in
the 1950's when Seagate Drive was constructed. As it was originally configured, Seagate Drive cut off tidal
connections to the south, and Clam Pass was left as the only connection to the Gulf of Mexico. In response
to water quality concerns, culverts were placed under Seagate Drive in 1976 to allow for tidal exchange
between Clam and Moorings Bays. Originally, the culverts were intended to allow flows only from Moorings
Bay into Clam Bay, but their construction was such that flows occurred in both directions (Collier County,
1997). In the 1980s, the tidal connection between Upper Clam Bay and Vanderbilt Lagoon (to the north) was
severed due to development activities (Collier County, 1997). Although Clam Bay's watershed had been
extensively developed, the shoreline of Clam Bay has remained in an almost entirely natural condition, with
mangroves, rather than seawalls, as the dominant feature.
Though watershed development has not directly impacted the shoreline features of most of Clam Bay,
secondary impacts associated with the alteration of freshwater and nutrient delivery could have produced a
negative impact to the overall ecology. Excessive nutrient (Le., nitrogen and phosphorus) concentrations in
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surface waters can lead to eutrophication, which can be indicated by algal blooms, decreased water clarity,
depressed dissolved oxygen levels, declines in seagrass coverage, fish kills, and reduced benthic
productivity. However, in estuaries such as Clam Bay, nutrient concentrations are only one factor
determining the degree of eutrophication. For Clam Bay, other critical factors could include residence time
and the interaction of other chemical constituents (i.e., tannin concentrations).
While it would not be unreasonable to expect that water quality within Clam Bay cou:d have experienced
negative impacts associated with the rapid population growth that has occurred in Southwest Florida, it has
also been concluded (Conservancy of Southwest Florida, 2010) that, "... the spatial distribution of seagrasses
in Clam Bay has remained relatively consistent over the last 30 years." In addition, the organic content of
sediments in the Clam Bay system does not appear to be indicative of substantial over-enrichment by
nutrients (PBS&J 2010). Instead, it has been suggested that the fine-grained sediments that characterize
much of Clam Bay are likely due to reduced flushing rates and low tidal velocities within Clam Bay (PBS&J
2010) a conclusion similar to those reached by the United States Environmental Protection Agency (EPA) in
the 1970s (EPA, 1977) and by Collier County in the 1980s (Collier County, 1987). The lack of evidence for
excessive nutrient enrichment in Clam Bay may be due to the substantial stormwater treatment system that
occurs on the western boundary of the Pelican Bay development, as noted in PBS&J (2008).
Levels of metals in Clam Bay sediments did not exceed threshold levels except for a site within one of the
canals within the Seagate neighborhood; this elevated level of arsenic was postulated as perhaps being due
to the use of pressure-treated wood for docks in that canal (PBS&J 2010).
1.1.2. State and Federal Water Quality Guidance
The State of Florida, through the Florida Department of Environmental Protection (FDEP) has historically
used a narrative standard for nutrient concentrations in surface waters, which states that nutrient
concentrations must not cause ".. .an imbalance of flora and fauna." This approach has generally served
Florida well, as it allows for the recognition that there can be locations where water quality impairment from a
regulatory viewpoint can actually reflect natural conditions.
In the 1990s, the State of Florida passed the Florida Watershed Restoration Act (FWRA; Chapter 99-223,
Laws of Florida) wherein FDEP committed to a specific course of action to meet the requirements of the
Federal Government's Clean Water Act (CWA). Within the CWA, Section 303(d) requires states to submit
lists of surface waters that do not meet applicable water quality standards and to establish Total Maximum
Daily Loads (TMDLs) for these waters. Under Florida Law (Chapter 99-223, Laws of Florida), a TMDL is
defined as "... the maximum amount of a pollutant that a water body or water segment can assimilate from all
sources without exceeding water quality standards..."
The FWRA directed FDEP to develop a method that would clearly define those waters that should be
included in the state's 303(d) list of water bodies that did not meet their appropriate water quality standards
(i.e., "impaired waters"). Waterbodies on this list would then require a TMDL to be developed. To prepare
the 303(d) list, FDEP relied upon advice received from various Technical Advisory Committees (TACs) made
up of individuals with expertise in matters of water quality and ecological assessments. TAC's were formed
for developing impairment criteria for lakes, streams, and estuaries, as it was determined early on that
separate criteria would have to be developed for these very different types of waterbodies. Based on input
from these TACs, the State of Florida's Environmental Regulation Commission adopted (in 2001) a FDEP-
approved method for identifying impaired surface waters in Florida (Chapter 62-303, Florida Administrative
Code; Identification of Impaired Surface Waters) also known as the "Impaired Waters Rule" or IWR.
After the development of the IWR, FDEP implemented a plan for the development of numeric nutrient
concentration criteria (NNC) which was reviewed and approved by EPA. FDEP's plan to establish NNC was
designed to establish NNC for lakes and streams as a first effort. The plan called for adoption of criteria by
the end of 2010, but the schedule was accelerated in response to EPA's January 2009 determination that
NNC are necessary under the CWA.
In January of 2009, the Assistant Administrator of EPA concluded that the State of Florida's narrative
standard for nutrients was inadequate, and that EPA would then "... propose numeric nutrient criteria (NNC)
for lakes and flowing waters within 12 months, and for estuaries and coastal waters, within 24 months." The
push by EPA to develop NNC (rather than allow FDEP's EPA-approved process to continue) originated from
legal action brought against EPA in 2008 by Earthjustice, a public interest law firm. Earthjustice filed a
lawsuit to require EPA to create NNC for Florida waters, in a lawsuit filed on behalf of the Florida Wildlife
Federation, the Sierra Club, the Conservancy of Southwest Florida, the Environmental Confederation of
Southwest Florida, and the St. Johns Riverkeeper. In August 2009, EPA entered into a Consent Decree with
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Earthjustice to settle the 2008 lawsuit by committing to the development of NNC for lakes and flowing waters
by January 2010, and for estuaries and coastal waters by January 2011. Final standards were to be
established for lakes and flowing waters by October 2010 and for estuaries and coastal waters by October
2011 More recently the parties involved in the original Consent Decree agreed to extend the timeline for
proposed estuarine and coastal waters nutrient criteria to November 14, 2011, with a deadline for finalized
criteria for NNC for estuarine and coastal waters of August 15, 2012
As relates to coastal systems such as Clam Bay, an earlier (2010) EPA report on numeric nutrient standards
for estuaries and their watersheds seems to have been withdrawn from further consideration. The
withdrawal of this earlier report appears to be based at least in part on strong and negative feedback from
the various resource management entities and the FDEP. In their latest timeline, EPA has stated that it will
release revised numeric nutrient criteria for estuaries, their watersheds, and coastal waters by November
2011, with final nutrient criteria developed by August 2012. The schedule for estuarine and coastal water
criteria requires EPA to propose estuarine and coastal waters nutrient criteria and downstream protective
values for Florida by November 14, 2011 to allow for peer review by the Science Advisory Board (SAB) and
to allow for public comment, followed by potential revisions to the proposed NNC by EPA.
For Clam Bay, prior assessments have indicated that existing water quality standards described in FDEP's
IWR are often times not met, particularly in Upper Clam Bay (i.e., PBS&J 2009). In that report, PBS&J
(2009) noted that "Data from these five locations, while not properly located for ambient monitoring
purposes, clearly indicate that Clam Bay would be classified as a "Verified Impaired" for water quality. Levels
of dissolved oxygen (DO) are frequently below standards set in the IWR (FAC 62-302.530). Additionally, the
data indicate that portions of Clam Bay exceed threshold values of chlorophyll-a established in the IWR
(FAC 62-302.530)." In response to concerns raised by Collier County, PBS&J (2009) designed a water
quality monitoring program for Clam Bay, which is currently being implemented by Collier County staff.
Water quality data are now collected using FDEP-trained staff, sampling procedures are consistent with a
Quality Assurance / Quality Control Plan, station locations are appropriate for an ambient monitoring
program, and the data are uploaded into the currently used database for the storage of biological, chemical,
and physical data for ground and surface waters, the STORage and RETrieval database, or STORET (which
was not done for earlier data collected in Clam Bay).
However, it was also concluded (PBS&J 2009) that both the DO and the chlorophyll-a standards outlined in
FDEP's IWR can be inappropriate in Southwest Florida water bodies, and that Collier County should work
with staff from FDEP to develop site-specific alternative criteria (SSAC) for parameters such as chlorophyll-a,
total nitrogen (TN), total phosphorus (TP), and DO.
This report is meant to propose SSAC for Clam Bay, based on guidance provided by EPA (2010) in "Water
Quality Standards for the State of Florida's Lakes and Flowing Waters" published in the Federal Register on
December 6, 2010 (75 Federal Register 75762). This report uses a combination of relevant background
information, a summary of existing studies on Clam Bay, and well-developed and scientifically appropriate
empirical methods to develop NNC for Clam Bay. The methods employed are consistent with prior studies
conducted for the Tampa Bay, Sarasota Bay, and Charlotte Harbor National Estuary Programs (Le., Janicki
Environmental, Inc., 2010) as well as guidance outlined in EPA (2010).
1.2, Report Objectives
The report addresses six topics which are outlined below:
Section 2: Data sources
Section 3: Should Naples (WBID 3278Q) which combines both Clam Bay and Moorings Bay, be split
into two separate WBIDs
Section 4: Is Clam Bay "impaired" using existing FDEP criteria and is impairment likely due to nutrient-
related impacts to water quality?
Section 5: Review of previous TMDL development
Section 6: Techniques to derive numeric water quality criteria for Clam Bay
Section 7: Proposed water quality criteria for Clam Bay
Section 8: Downstream protective values
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2. Data Sources
The data used for the analyses included data provided by Collier County, the City of Naples and IWR Run 42
data (supplied by FDEP) to create a comprehensive dataset. All available water quality data were subject to
a quality assurance I quality control plan. All stations identified with an organization code of 21 FLKWA T
(Lakewatch) were removed from the dataset prior to analysis. At this time, Lakewatch data are not included
as part of the data sets used for the determination of impairment status by FDEP. Data from the following
eight waterbodies were retrieved and reviewed: Clam Bay, Moorings Bay, Estero Bay Wetlands, Hendry
Creek, Charlotte Harbour, Sarasota Bay, and the Hillsborough River.
3. Naples (WBID 3278Q)
The Naples WBID (3278Q) was comprised of both Clam and Moorings Bay (Figure 2). In response to water
quality concerns, culverts were placed under Seagate Drive in 1976 to allow for the restoration of historical
tidal exchange between Clam and Moorings Bays. Originally, the culverts were intended to allow flows only
from Moorings Bay into Clam Bay, but their construction was such that flows could occur in both directions
(Collier County, 1997).
While a re-established hydrologic connection exists between Clam and Moorings Bay, comparisons of nine
water quality parameters between the two Bays indicate statistically significantly differences in water quality
(Table 1). A Mann-Whitney comparison of medians test was performed using data provided by Collier
County and the City of Naples, which included data from 2009 to 2011. Eight of the nine parameters were
statistically significantly different (p<0.05) when comparing median values in Clam to Moorings Bays (Table
1). Overall, Clam Bay has higher TN, TP, chlorophyll-a, and color values compared to Moorings Bay.
Biological Oxygen Demand (BOD) was the only parameter with similar values between Bays. Salinity,
temperature, Secchi disk depth and DO for Clam Bay were below the values calculated for Moorings Bay.
The substantially different water chemistry between Clam and Moorings Bay, in addition to the land use and
hydrologic modifications which have occurred in both systems, suggests that separation of the two
waterbodies is required for water quality purposes. Although Clam Bay's watershed had been developed
rather extensively, the shoreline features of Clam Bay have not been altered nearly as much as the shoreline
features of Moorings Bay, which had undergone significant modifications due to dredge and fill activities as
early as the 1970s.
Through coordination between FDEP, Collier County, and the City of Naples, FDEP agreed to divide WBID
3278Q (Naples) into two separate waterbodies (pers. Communication Jennifer Nelson, FDEP). The
proposed name for the northern WBID is Clam Bay which will be defined using the Clam Bay drainage basin.
The southern WBID will encompass Moorings Bay. The new WBID designation best reflects the water
quality and hydrologic variability shown between the Clam and Mooring Bay systems (Figure 2).
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Figure 2.
Proposed revision dividing Clam and Moorings Bays into separate WBIDs.
Clam Bay
Moorings Bay
Table 1. Water quality comparison between Clam and Moorings Bay (2009-2011)
Salinity (ppt) 32.2 34.8 Y
Temperature (oC) 23.9 27.0 Y
Secchi Depth (m) 0.7 1.3 Y
Color (PCU) 30 15 Y
Chlorophyll-a (fJg/L) 6.2 3.2 Y
Total Nitrogen (mg/L) 0.62 0.43 Y
Total Phosphorus (mg/L) 0.046 0.032 Y
Dissolved Oxygen (mg/L) 4.9 6.2 Y
BOD (mg/L) 2.1 2.1 N
Data from Collier County and City of Naples (2009-2011)
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4. Is Clam Bay "impaired" using
existing FDEP criteria?
The FDEP IWR contains approved methods for evaluating water quality of lake, stream, and marine
waterbodies. Clam Bay is designated as a Class II, marine waterbody. Class II status indicates that the
designated use of the waterbody is for shellfish propagation and harvesting. Clam Bay data provided by
Collier County for the period of 2009 to 2011 were compared against the appropriate standard for fecal
coliform bacteria, DO, and chlorophyll-a. If Clam Bay water quality fell above or below "impairment" for DO
or chlorophyll-a, data were then compared against FDEP (2010) and EPA (2007) threshold concentrations
for nutrients:
1.0 mg TN I liter screening level used by FDEP (2010) and EPA (2007)
o 19 mg TP I liter screening level used by FDEP (2010) and EPA (2007)
Additionally, assessments were performed to evaluate potential nutrient impacts on DO directly or indirectly
on water clarity (Secchi disk depth). Finally, toxins levels in sediments were quantified and 210 Pb and 137CS
testing were utilized to evaluate the sediment accumulation rate in Clam Bay.
4.1. Fecal coliform bacteria
Fecal coliform bacteria standards are more stringent for Class II waterbodies compared to Class III
(recreational use). The appropriate standard to evaluate fecal coliform bacteria impairment status in Clam
Bay, based on the FAC. 62-303.470 is stated as follows:
Glass 1/ waters shall be included on the verified list for coliform impairment if, following review of the available
data as described in subsection 62-303.460(2), F.A.G.
(a) The number of samples above 43 counts per 100 mL meet the requirement in subsection 62-303.420(6),
FAG., with the exception that paragraph 62-303.320(4)(a), F.A.G., does not apply and samples collected on
different days within any four day period will be assessed as daily samples, or
(b) The water segment includes a sampling location that has a median fecal coliform MPN value that
exceeds 14 counts per 100 ml for the verified period. To calculate a median value for a sampling location,
there shall be at least 20 samples collected during the verified period.
Fecal coliform bacteria data from Clam Bay were compared to two criteria. The first criteria evaluated was to
test if sufficient samples exceeded 43 CFU/100 mL based on the sample size (N=132). A minimum of 19
samples are required to not meet the fecal coliform bacteria criteria in order for Clam Bay to be placed on the
verified list. Sixty-eight of the 132 data points (52%) exceeded Class II standard of 43 CFU/100mL. Based
on this comparison alone, Clam Bay is impaired for fecal coliform bacteria. The second criteria compared
the median fecal coliform value for each station to 14 CFU/100 mL (Table 2). Sufficient data points are not
currently available to complete a station by station comparison with the 14 CFU/1 OOmL criteria required for
the verified list. However, only ten samples are required by station for inclusion on the planning period list.
All nine water quality stations had median fecal coliform bacteria values above 14 CFU/100mL.
Though values exceed the regulatory standard, it should be considered that fecal coliform bacteria may not
be an appropriate indicator of pathogenic diseases in sub-tropical environments such as Florida. The
specificity of the fecal coliform test is compromised by the more constant and warmer ambient water
temperatures in Southwest Florida. The inability to specifically identify humans as a source of bacteria using
traditional indicator testing protocols has been noted by Fujioka (2001) and Fujioka et al. (1999) for various
tropical locations. Source identification studies are recommended to determine whether anthropogenic
factors cause of the elevated bacteria concentrations prior to developing recommendations for remediation
(Bernhard and Field 2000).
Elevated fecal coliform bacteria concentrations have been attributed to wildlife, livestock, domesticated
animals and birds (Levesque et al. 1993, Minnesota Pollution Control Agency 2002). In prior TMDLs, birds
were estimated to produce 200 to 400 million fecal coliform bacteria per bird per day (humans about 2 billion
per day; Minnesota Pollution Control Agency 2002). Using a low end estimate of 200 milion fecal coliform
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bacteria per bird per day, one bird could cause 124,000 gallons of water to exceed 43 CFU / 100 mL. The
total volume of Clam Bay is approximately 105 million gallons. Therefore, it is feasible to expect that 850
birds could produce enough bacteria - every day - to cause 105 million gallons of water to exceed 43
CFU/100 mL. Fecal coliform bacteria are susceptible to both die-off due to the saline environment and in-
situ production. Regardless, it is within the realm of possibilities that birds are an important source of the
bacteria in Clam Bay.
In an effort to quantifiably identify the potential fecal coliform bacteria sources to Clam Bay, Collier County is
pursuing a microbial source tracking effort for Clam Bay. Samples will be collected in Clam Bay and
analyzed for bacterial genes or viruses specific to humans. Positive results would indicate an anthropogenic
source but negative results do not prove that human sources are not present.
Table 2. Fecal coliform bacteria summary statistics (2009-2011)
Average M
Clam 132 55 44 35 310 43
Bay
Station statistics
CB1 11 109 94 89 28 310 14
CB2 14 95 70 80 32 230 14
CB3 14 58 60 49 17 111 14
CB4 14 56 47 43 6 114 14
CB5 16 52 48 37 1 115 14
CB6 16 28 16.5 18 3 88 14
CB7 16 24 22 16 3 54 14
CB8 16 54 27 32 4 290 14
CB9 15 42 28 23 1 153 14
Data from Collier County (2009-2011)
4,2, Dissolved Oxygen
Dissolved oxygen standards are differentiated based on the salinity designation of the waterbody. Clam Bay
is designated a marine waterbody, therefore the appropriate standard to evaluate DO impairment status in
Clam Bay based on FAC. 62-303.470 is as follows:
Dissolved oxygen concentrations shall not average less than 5.0 in a 24-hour period and shall never be less
than 4. O. Normal daily and seasonal fluctuations above these levels shall be maintained.
Dissolved oxygen concentrations in ambient waters can be influenced by many factors, including
temperature and salinity;
4.2.1. Is Clam Bay impaired for Dissolved oxygen?
Dissolved oxygen data from Clam Bay were compared to the minimum 4.0 mg/L criteria. Based on the
sample size (N=144), a minimum of 18 and 20 samples are required to not meet the DO criteria in order for
Clam Bay to be placed on the planning or verified list, respectively. DO values were below the minimum
criteria of 4.0 mg/L in 30 of the 144 samples. In accordance with the IWR standard for DO, Clam Bay is
impaired for DO. Sufficient daily DO data are not available to calculate a daily average for comparison with
the 5.0 mg/L daily average criteria. To calculate the daily DO average, a minimum of four temporally
independent samples (at least 4 hours apart) is required. Additionally, a minimum of 20 samples are
required in to be eligible for placement on the verified list. As of June 2011, only 17 sampling events have
been completed in Clam Bay.
4.2.2. Is dissolved oxygen impairment linked to nutrients?
A correlation analysis between DO and multiple parameters (Le. nutrients, color, salinity, temperature and
chlorophyll-a) was performed to identify the potential cause for suppressed DO concentrations in Clam Bay
(Table 3). A significant regression was not observed between DO and TN. Dissolved oxygen was indirectly
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related to TP (p=0.0157) but TP only explained 4% of the variability in DO values. The best explanation in
variability of DO concentrations in Clam Bay is predicted by a multiple regression model including color and
temperature (~=0.38).
Table 3. Dissolved oxygen correlation with potential causative parameters
Potential causative
para,rneter
Total phosphorus Dissolved oxygen exponential 0.0157 0.04 inverse
Color Dissolved oxygen exponential 0.0000 0.14 inverse
Salinity Dissolved oxygen exponential 0.0188 0.04 direct
Temperature Dissolved oxygen exponential 0.0000 0.33 inverse
Chlorophyll-a Dissolved oxygen exponential 0.0003 0.10 inverse
Total nitrogen Dissolved oxygen NA NS NA NA
Data from Collier County (2009-2011)
While the FDEP IWR requires a minimum DO of 4.0 mg/L in all Florida estuaries, DO values below 4.0 mg/L
are expected in Southwest Florida (Atkins 2011). The Fakahatchee watershed (WBID 3278G) has been
identified as a reference watershed that has undergone minimal disturbance. Despite this, the median DO in
the Fakahatchee Strand (3278G) was significantly lower than the Faka-Union North and South Segments
and the Rookery Bay (Inland East Segment) watersheds (Kruskal-Wallis; p<0.05, Table 4). Additionally, the
median DO concentration in the Fakahatchee Strand was lower than the Florida freshwater and marine DO
standard (5.0 mg/L).
Table 4. Dissolved oxygen statistics for four WBIDs in Southwest Florida (from Atkins 2011)
WBID (mg/L
3278G Fakahatchee Strand 4.1 3.7 0.2
3278H Faka-Union (North Segment) 5.3 5.2 1.6 12.8
32781 Faka-Union (South Segment) 6.2 6.4 1.2 12.9
3278V Rookery Bay (Inland East 6.2 6.4 2.1 11.4
Segment)
Similar to Clam Bay, no significant relationships between TN and DO or TP and DO were observed at the
water quality sites reviewed in the mostly pristine watershed of the Fakahatchee Strand. Therefore, there is
little evidence to suggest that TN or TP load reductions would have an impact on DO in the Fakahatchee
Strand. However, a significant correlation between color and DO was evident in the Fakahatchee Strand
(p<0.05; Figure 3). Tannins (color) are predominantly produced from leaves, wood, bark and other detritus
from trees. An increase in tannins (color) usually coincides with an increase in organic material resulting in a
decrease in DO. Due to the heavily forested landscape within the Fakahatchee Strand (85% natural land
cover), increased levels of tannins or color would be expected, especially during wetter time periods.
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Figure 3. Relationship between color and dissolved oxygen in the Fakahatchee Strand (WBID
3278G; p<0.05)(from Atkins 2011)
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Fakahatchee Strand
2000-2008
14
..
:J 12 R2 = 0 1377
Ch
S 10 ..
c ..
<l> 8 .m.
01
:>.
x ..
0 6 .
"0 5.0 mq/L standard
<l> . .
~
0 4 ..
!/J
!/J
is 2 . m..
I. ..
: .. .
0 ..
0 50 100 150 200 250 300 350 400 450
Color (PCU)
4.3. Chlorophyll-a (Nutrient Criteria)
Chlorophyll-a is evaluated as a proxy for nutrient impairment. The IWR provides a narrative interpretation of
nutrient criteria (FAC. 62-303.450) which allows for the development of a site specific alternative threshold
with the presence of sufficient data that reflect "imbalance in flora or fauna". In the absence of sufficient
data, estuaries and open coastal waters are subject to a standard of annual chlorophyll-a average of 11 J..I9/L
(FAC.62-303-353). Based upon the data available for Clam Bay, the default standard of 11 J..I9/L was used
to assess nutrient impairment.
4.3.1. Is Clam Bay impaired for chlorophyll-a (nutrients)?
The technique for calculating the annual average chlorophyll-a values is provided in FAC. 62-303-350. In
summary, the chlorophyll-a average for each three month season (Quarter 1, Quarter 2, Quarter 3, and
Quarter 4) is calculated. The chlorophyll-a average of four consecutive seasons is calculated to assess
impairment. For Clam Bay, sufficient data were only available in 2010 to calculate an annual average (9.0
J..I9/L) which was below the 11 J..Ig/L standard required for estuaries (Table 5). However, a separate
evaluation of the annual chlorophyll-a average for Upper Clam Bay (14.6 J..Ig/L) alone indicates elevated
phytoplankton production. While Clam Bay is not impaired for chlorophyll-a or nutrients based on
chlorophyll-a values below the 11 J..Ig/L threshold, further investigation of the elevated values in Upper Clam
Bay might be warranted.
Table 5. Quarter and annual average chlorophyll-a values for Clam Bay (2009-2011).
Year Quarter 1 Quarter ..... .....6.n"..""
..................
2009 8.3
2010 6.8 8.2 15.1 5.9 9.0
2011 7.7
Data from Collier County (2009-2011)
4.3.2. Is chlorophyll-a linked to nutrients?
A correlation analysis between chlorophyll-a and TN and TP was performed to identify the potential cause for
elevated chlorophyll-a concentrations in Clam Bay (Table 6). A significant regression was observed
between chlorophyll-a and both TP and TN, which explained 22 and 25% of the variability in data,
respectively. However, despite the link between nutrients and chlorophyll-a, a resulting impact on water
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Criteria
clarity (Secchi disk depth) was not observed. Connections between nutrients and chlorophyll-a, chlorophyll-
a and water clarity, and water clarity and seagrass is thus not evident in Clam Bay.
Table 6. Chlorophyll-a correlation with nutrients and secchi depth.
Potential causative
par<lrn~ter
Total phosphorus Chlorophyll-a
Total nitrogen Chlorophyll-a
Chlorophyll-a Secchi Depth
Data from Collier County (2009-2011)
lationship
exponential
exponential
0.0000
0.0000
21.54
24.83
NA
direct
direct
NA
NS
NA
4.4. Sediment Characterization
As part of a study performed by Atkins (formerly PBS&J) for Collier County in Clam Bay (PBS&J 2010), a
sediment characterization was completed to address the the predominance of fine-grained sediments in
Clam Bay and the potential for such sediments to be influenced by flushing rates within Clam Bay. The
sediment characterization study included an assessment of the physical and chemical characteristics of
sediments throughout the Clam Bay system (including organic content, carbonate content), an assessment
of levels of toxins throughout the bay, and an assessment of the relative rate of accumulation of sediments
throughout the bay.
4.4.1. Toxins
In 2010, cores were collected from 13 sites in Clam Bay for sediment physical (organic and carbonate
contents) and chemical characterization (toxin levels) (Figure 4). Low levels of organic enrichment suggest
a lack of impact from excessive algal blooms. Only one site (station 2) had toxin values above established
thresholds. Elevated arsenic was observed at this site within the Seagate canals, which could have been
due to the pressure-treated wood used for docks in this canal.
A review of the sediments indicated that Outer Clam Bay's sediments are mostly a mixture of fine-grained
sediments, rather than sand. The sediment composition are likely due to reduced current velocities within
Clam Bay (US EPA 1977, Collier County 1987). Past studies of Clam Bay have shown that areas with fine-
grained sediments have lowered diversity of benthic invertebrates (Collier County 1987)
Figure 4.
Location of sediment cores collected in Clam Bay.
4.4.2. Sediment Accumulation
Sediment cores were collected from five locations in Clam Bay (two from canals and three from open bay
systems) (Fi~ure 4). The cores were frozen and transported to Louisiana State University (LSU) to be
analyzed for 10Pb and 137CS. 210Pb provides relative sediment accretion rate estimates while 137CS provides
a reference point for dating using residual of nuclear bomb fallout (which peaked in 1963/64). At the open
bay sites, 0.32 to 0.35 cm/yr sediment accretion rates were measured. These values are within range from
Sarasota Bay (0.32 cm/yr; Tomasko and Keenan 2010) as well as within the range of expected rates with
and without accelerated sea level rise (0.24 to 0.52 cm/yr; Clark 1992).
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5. Review of previous TMDL
development
While Clam Bay appears to be impaired for DO, nutrients cannot be linked to these low values. Additionally,
elevated chlorophyll-a concentrations are found in Upper Clam Bay, but a resulting impact on water clarity is
not evident. While a local interpretation of the TMDL development process is logical in nature it is not
accurate as to the application of Florida statutes: The Conservancy of Southwest Florida expressed the
following sentiments in 2009, ".. .in order to trigger a TMDL, dissolved oxygen levels have to be below
standards in concert with causative pollutants. Biological Oxygen Demand, Total Nitrogen and Total
Phosphorus also have to exceed State standards. Dissolved oxygen levels recorded in Clam Bay have been
below the State standard, typical of a lot of estuarine waterways in the County including Rookery Bay...
these levels are not surprising and can be defended (K. Worley 2009)." Presently, screening levels exist for
TN and TP but there are no nutrient standards for the state of Florida.
However, TMDLs have been developed in waterbodies with DO impairments even when TN and TP
concentrations were below screening criteria (i.e. Hendry Creek TMDL, FDEP 2008). Hendry Creek,
freshwater (3258B) and marine (3258B1), located in Lee County, have both been declared impaired for DO
(Figure 5), and in 2008, FDEP developed a TMDL requiring a 32% load reduction for TN, even though
nutrient concentrations were below (TN) or well below (TP) screening criteria (Table 7).
Table 7. Summary of DO Monitoring Data in the Verified Period for Hendry Creek, WBJDs 3258B
and 3258B1 (Table 2.2 from Hendry Creek TMDL, FDEP 2008).
Total number of sarnp!les
IWR required number of violations for the Verified list
Number of observed violations
Number of observed! nonviolations
Number of seasons during which. sampJeswere collected
Highest observation (mg!l)
Lowest observatIon (mgfL)
Medi.an observation (mg/L)
Mean observation (mglL)
Screening value for BOD (mg/L)
Screening value for TN (mg!L)
Screening value for TP (mglL)
Median value for BOD observatlons(mglL)
Median value for TN observations (mgfL)
Median value for TP observations (mg/q
Possible causative pollutant by rWR
59
10
31
28
4
13.0
1.1
4,9
5.0
2.0
1.6
0.22
1.5
'0.775
0.'03
TN
39
7
34
5
4
6.9
0.5
2.6
2.7
2.1
1.0
0.19
1.3
0.8815
0.054
TN
Impaired
FI!NAL ASSESSMENT Impaired
MgJl. - MiWgrams per !:iter; BOD - Biological o~en demand; TP - Tolal phosphorus.
For the development of the Hendry Creek TMDL, a reference wetland (the Estero Bay Wetlands -WBID
3258A) was selected to establish target nutrient concentrations (Figure 5). FDEP stated that, "Estero Bay
Wetland has similar hydrologic features to Hendry Creek and the anthropogenic influence is minimal, making
it a good reference waterbody for developing a target concentration representing "natural conditions (FDEP
2008)". The target TN and TP concentrations for Hendry Creek(Marine) were calculated using the median
values from the Estero Bay Wetlands, 0.6 and 0.05 mg/L, respectively..
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Figure 5. Location map of Estero Bay Wetlands (WBIO 3258A), Hendry Creek (Freshwater)
(WIBO 3258B), and Hendry Creek (Marine) (WBIO 3258B1).
5.1. Salinity based Nutrient Targets
Using the period of record data from IWR Run 42, the conductivity (a proxy for salinity) values for each
waterbody from the Hendry Creek TMDL were compared to evaluate the hydrologic similarities between
water bodies (Figure 6, Table 8). A Kruskal-Wallis comparison of medians indicated that the Estero Bay
Wetlands (EBW) is statistically more saline than Hendry Creek (Freshwater; HCF) or Hendry Creek (Marine;
HCM; Figure 6). The importance of evaluating the conductivity characteristics of the reference location
compared with the selected waterbody is because Hendry Creek is part of an estuary (Figure 7), and by
definition, an estuary is "a body of water formed where freshwater from rivers and streams flows into the
ocean, mixing with the seawater" (www.epa.gov). Due to the changes in hydrologic inputs and weather
impacts, the salinity (conductivity) at any given point in an estuary vary in a given day. A variation in
hydrologic inputs (freshwater flows) results in a change in salinity in the estuary. Nutrient concentrations
have been shown to be inversely related to salinity in various locations in Southwest Florida (i.e.
Hillsborough River, Sarasota Bay, Charlotte Harbor, Estero Bay Wetlands; Figure 8).
Table 8. Conductivity (I.lM) summary statistics for Estero Bay wetlands, Hendry Creek (Freshwater)
and Hendry Creek (Marine).
Estero Bay Wetlands 46,488
Hendry Creek (Freshwater) 3,638
Hendry Creek (Marine) 11,679
Period of record data from IWR Run 42
48,475
755
4,975
2,500
250
96
61 ,400
40,400
52,500
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Figure 6. Kruskal-Wallis comparison of medians for conductivity values in Estero Bay wetlands
(EBW), Hendry Creek (Freshwater) (HCF) and Hendry Creek (Marine) (HCM).
80000
i' 60000
2-
B
~ 40000
0.
::l
"0
c:
0
() 20000
0
EBW HCF HCM
Figure 7. Diagram of salinity distribution patterns along an estuary from the riverine (freshwater)
input to the Gulf (Ocean).
River
0.5 :psu }-
" : Ongoha,llne
5 PSU},
MesohaHne
(Frnh Willer)
Estuary
(Bral;:kish WIIl.r)
Polyhaline
- 30 psu
Ocean
Euhaline
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Figure 8. Significant correlations between salinity and total nitrogen (mg/L) were found for the
Hillsborough River, Sarasota Bay, Charlotte Harbor and Estero Bay Wetlands. Graphs shown
with best-fit line and 95% prediction limits.
2
Ol
g
C
W
g
Z
ro
'0
f-
HiIIsborough River
A.Total Nitrogen = exp(0.08356 - 0.0306509'A.Salinity)
3 ,.-
"'Q .
~,
4
Charlotte Harbor
ATN = 1.37947 - 0.0237786*A.SALlN
a
a
:J'
0, 3
g
C
tV
g 2
Z
ro
'0
f-
10
20
30
40
2
a
o
o 10 20 30
Salinity (ppt)
Sarasota Bay
A.TN = exp(-O.0436092 - O.0253919'A.SALlN)
40
00
Salinity (ppt)
4
Estero Bay Wetlands
tlvitynutrientanalysis.TN = 1.24451 - 0.0191291'conductlvitynu1
3
"'- aa
::J' "~" 2
0, 3 0>
g E. 2
c c
W tV
g 2 0>
a 0
.j:;
z Z
ro ro
'0 '0
f- f-
0
10 20 30 40 50 0
Salinity (ppt)
o 0 0
10
20 30
Salinity (ppt)
40
50
Revised nutrient targets for the Estero Bay Wetlands can thus be calculated after normalizing for
conductivity. The best-fit equation for Estero Bay Wetlands between conductivity and TN is linear (Equation
1)
Equation 1: Total nitrogen (mg/L) = 1.30908 - 0.0000166414' (Conductivity (J..IM))
Using the average conductivity for Estero Bay Wetlands (46,488 J..IM), the corresponding TN value is 0.54
mg/L (Figure 9). The upper and lower limit at the average conductivity value are 1.08 and 0.0 mg/L,
respectively, when using the 95% prediction limits (Figure 9). In comparison, the conductivity-normalized
TN concentration for Hendry Creek (Marine) based on the average conductivity is 1.11 mg/L using the
Estero Bay Wetlands best-fit equation (Figure 10). As a result, the average TN for Hendry Creek (Marine)
(1.09 mg/L) is less than the conductivity-normalized TN target (1.11 mg/L; Table 9) derived from the
reference WBID of Estero Bay Wetlands. Based upon the conductivity-normalized TN target, Hendry Creek
(Marine) does not have elevated TN.
This approach to developing conductivity-normalized TN and TP targets serves as the foundation for
developing NNC for Clam Bay.
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Criteria
Figure 9. Expected, upper, and lower (95 percent prediction limits) total nitrogen concentration
for Estero Bay Wetlands based on the average conductivity.
2
-
...J 1 .5
-
C)
E
--
c:
(])
C) 1
0
"-
~
Z
CO 0.5
15
.....
0
0
o
o
o
o
o
1.08 mg/L- Upper Limit
:~ ~
0.54 mg/L- expected TN
j
0.0 mg/L- Lower Limit
20000 40000 60000
Conductivity (uS)
80000
Figure 10. Expected total nitrogen concentration for Hendry Creek (Marine) based on the average
conductivity using the Estero Bay Wetland best-fit equation with 95 percent prediction limits.
2
.-
...J
0. 1.5
E
-
o
o
o
o
o
m
g>> 1
"-
.;t::
z
ro
(5 0.5
.....
o
o
20000 40000 60000
Conductivity (uS)
80000
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Criteria
Table 9. Comparison of expected total nitrogen based on Estero Bay wetland relationship with
average conductivity with Hendry Creek TMDL target TN and Average TN.
TMDL (EBW)
Target TN
based
nship*
Average TN
Estero Bay
Wetlands
Hendry Creek
(Marine)
46,488
NA
0.54
0.60
11,679
0.60
1.11
1.09
6. Techniques to derive numeric water
quality criteria for Clam Bay
Three approaches have been developed to derive numeric nutrient criteria by FDEP (Taken from FDEP 2nd
draft overview of marine NNC approaches (11/2010)
Maintain healthy existing conditions
provides for maintaining the current nutrient regime in a system determined to be biologically healthy
(from the standpoint of nutrient enrichment).
2. Historical conditions
3. Total Maximum Daily Load (TMDL) modeling or response-based approach
7. Proposed water quality criteria for
Clam Bay
7.1. Is Clam Bay Healthy?
Multiple studies including water quality collection and analysis, pollutant loading model development, benthic
invertebrate evaluation, toxin quantification and sediment accumulation rate assessments have been
completed to evaluate the "health" of Clam Bay. After reviewing these studies, the weight of evidence
suggests that Clam Bay is a healthy system. The Conservancy of Southwest Florida recently completed a
benthic habitat assessment in Clam Bay (2010), with forty-five different types of organisms identified,
including polychaetes. crabs, shrimp, seagrass and clams (Table 10).
However, water quality in a "healthy" system can still fail existing criteria. In order to supplement the
conclusion that Clam Bay is a "healthy" system which experiences natural fluctuations in water quality, a
comparison of Clam Bay to an FDEP-established reference waterbody was completed. The Estero Bay
Wetlands has been previously identified as a reference waterbody by FDEP and is located in close proximity
to Clam Bay. Evaluating Clam Bay water quality based on a comparison with Estero Bay Wetlands could be
a valuable supplement for the conclusion of Clam Bay's overall ecological health.
Table 10. List of benthic organisms identified in Clam Bay (Conservancy of Southwest Florida
2010).
Species or lowest taxon listed Common Name Kingdom Phylum
Class Polychaeta polychaete Animal Annelida
Pectin aria gouldi trumpet worm Animal Annelida
Panopeus herbstii common mud crab Animal Arthropoda
Eurypanopeus depress us depressed mud crab Animal Arthropoda
Rhithropanopeus harrisii white fingered mud crab Animal Arthropoda
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Criteria
Species or lowest taxon listed Common Name Kingdom Phylum
Family Ocypodidae mangrove mud crab Animal Arthropoda
Family Grapsidae mangrove mud crab Animal Arthropoda
Family Coenobitidae mangrove mud crab Animal Arthropoda
Uca spp. fiddler crab Animal Arthropoda
Callinectes sapidus blue crab Animal Arthropoda
barnacle Animal Arthropoda
Family Penaeidae penaeid shrimp Animal Arthropoda
Order Amphipoda amphipod Animal Arthropoda
Order Decapoda decapod Animal Arthropoda
Family Portunidae portunid crab Animal Arthropoda
Anguilla rostrata American eel Animal Chordata (order Anguilliformes)
Class Ascidiacia sea squirt Animal Chordata (subphylum Tunicata)
Moira atropos heart urchin Animal Ech inodermata
Ophiophragmus fi/ograneus brittle star Animal Echinodermata
Crassostrea virginica American oyster Animal MolluscCi
Family Mytilidae mussels Animal Mollusca
Tage/us plebeius razor clam Animal Mollusca
Anomalocardia amberiana pointed Venus clam Animal Mollusca
Argopecten irradians Atlantic bay scallop Animal Mollusca
Mercenaria mercenaria quahog Animal Mollusca
Bittiolum varium grass cerith Animal Mollusca
Melongena corona Florida crown conch Animal Mollusca
Strombus alatus Florida fighting conch Animal Mollusca
Pleurop/oca gigantea horse conch Animal Mollusca
Chicoreua florifer dilectus lace murex Animal Mollusca
Family Melongenidae whelk Animal Mollusca
Vermicu/aria fargoi West Indian worm snail Animal Mollusca
Urosalpinx cinera Atlantic oyster drill Animal Mollusca
Littoraria angulifera mangrove periwinkle Animal Mollusca
Family Cerithiidae cerith Animal Mollusca
sponge Animal Porifera
blue-green algae Bacteria Cyanobacteria
Caulerpa sertu/aroides green algae Plant Chlorophyta
Acetabularia crenulata green algae Plant Chlorophyta
Ha/odu/e wrightii shoal grass Plant Tracheophyta
Ha/ophila decipiens paddle grass Plant Tracheophyta
Thalassia testudinum turtle grass Plant Tracheophyta
Subfamily Lemnaoideae duckweed Plant
red drift algae Plant Rhodophyta
Acanthophora spicifera spiny seaweed Plant Rhodophyta
7.2. Proposed NNC normalized for salinity
The data used for the comparison between Clam Bay and Estero Bay Wetlands were from the IWR Run 42
and Collier County for the period of record. The median conductivity values were compared using a Mann-
Whitney comparison of medians (Figure 11). While the medians were found to be significantly different with
Estero Bay Wetlands slightly more saline, the overall range was fairly similar (Table 11).
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Figure 11. Mann-Whitney comparison of medians for conductivity values in Clam Bay and Estero
Bay wetlands (EBW).
80000
(i) 60000
~
z.
~ 40000
:::I
"0
C
o
<.)
20000
o
Clam Bay
Estero Bay Wetlands
Table 11. Conductivity (IJM) summary statistics for Clam Bay and Estero Bay wetlands
WBID Average Median Minimum Maximum
Clam Bay 42,453 45,093 150 64,465
Estero Bay Wetlands 46,488 48,475 2,500 61 ,400
Period of record data from IWR Run 42 and Collier County
Both Clam Bay and the Estero Bay Wetlands are classified as estuaries; therefore, salinity values can vary
over a single day, week or season. As previously discussed, nutrients vary as a function of salinity. As such,
target nutrient concentrations should be normalized to a salinity regime. The variability in TN as a function of
conductivity is similar in both Clam Bay and the Estero Bay Wetlands (Figure 12). Similar to the calculations
previously completed for Hendry Creek (Marine), the linear regression line between conductivity and TN for
the Estero Bay Wetlands was used to calculate a potential TN target for Clam Bay (Equation 1). Using the
average conductivity value 42,453 J..IS (25.4 ppt) for Clam Bay, the corresponding TN is 0.60 mg/L providing
a potential TN target (Figure 12, Table 12). A potential target TP was also calculated using the exponential
relationship found between TP and conductivity in the Estero Bay Wetlands (Equation 2). Based on the
average salinity for Clam Bay (42,453 J..IS), a potential target for TP is 0.057 mg/L (Figure 13, Table 12).
Equation 2: Total Phosphorus (mg/L)= exp(-2.3091 - 0.0000129727*conductivity(J..IS))
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Criteria
Figure 12. Clam Bay potential TN target based on Estero Bay Wetlands regression and Clam Bay
salinity with 90 percent prediction limits.
2
-
....J
""-
0>
E
-
..
41-
o ..
41- Clam Bay
D 0 Estero Bay Wetlands
1.5
o
41-
'"
'" ,. 0
$$
c:
Q)
8> 1
'-
:t:
z
(ij
<5 0.5
t-
o
o
20000 40000 60000
Conductivity (uS)
80000
Table 12. Comparison of expected TN and TP based on Estero Bay wetland relationship with
average conductivity and average TN and TP.
WBID Average TMDL (EBW) Expected TN based Average
Conductivity (",S) Target TN on EBW relationship TN
Estero Bay Wetlands 46,488 0.6 NA 0.60
Clam Bay 42,453 ------ 0.60 0.71
TMDL (EBW) Expected TP based Average
Target TP on EBW relationship TP
Estero Bay Wetlands 46,488 0.050 NA 0.068
Clam Bay 42,453 ------ 0.057 0.055
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Figure 13. Clam Bay potential TP target based on Estero Bay Wetlands regression and Clam Bay
salinity with 90 percent prediction limits.
0.4
.-
...J
-
0>
E 0.3
--
~ Clam Bay
Cl Estero Bay Wetlands
o
0.2
o
f/)
::J
....
a
..c:
0-
f/)
a
..c:
0..
ro
'0
J-
o
o
.. 0 nU1
0.1
00
o
o
o
20000 40000 60000
Conductivity (uS)
80000
The proposed ClaITI Bay numeric nutrient criteria for TN and TP at the current average salinity are similar to
the targets established for the Hendry Creek TMDL but lower than the screening criteria accepted by both
FDEP and EPA (Table 13). Presently, the average Clam Bay TP (0.055 mg/L) is below both the FDEP and
EPA screening criteria (0.19 mg/L) and the proposed target TP of 0.057 mg/L (Table 13). In contrast, the
average Clam Bay TN (0.71 mg/L) is below the screening criteria (1.00 mg/L) but above the proposed target
TN NNC (0.60 mg/L; Table 13). Based upon this comparison, should Clam Bay be considered impaired
since the average TN concentration is above the proposed target? That issue is considered in the next
section (Section 7.3) of this report.
Table 13. Comparison of TN and TP screening criteria, Hendry TMDL targets, Clam Bay proposed
NNC and Clam Bay average.
Total Nitrogen (mg/L) Total Phosphorus (mg/L)
FDEP and EPA 1.00 0.190
screening criteria
Hendry Creek TMDL 0.60 0.050
ClaITI Bay proposed NNC* 0.60 0.057
Clam Bay average 0.71 0.055
* calculated using nutrient vs. salinity relationship from EBW
7.3. Conceptual Management Responses
The proposed Clam Bay NNC provides a protective approach to water quality evaluation and management
for the waterbody. The proposed NNC are lower (more stringent) than the FDEP and EPA screening criteria,
and they were derived based upon a nutrientsalinity relationship from the Estero Bay Wetlands, an
established reference WBID. However, the NNC have to be considered in the context of salinity due to the
variability in nutrient concentrations found within a given salinity range. Therefore, management responses
due to deviations from the proposed NNC should be a function of rnagnitude and duration of any
exceedances, similar to the management approach used by the Tampa Bay Estuary Program.
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As part of the development of the Numeric Nutrient Criteria, FDEP is considering revisions to the existing DO
standards for freshwater streams, lakes and estuaries in Florida (Frydenborg et aI., presentation from
6/14/2011). A revised technique for streams and lakes evaluated the DO values for all sites with a Land
Development Index (LDI) less than 2, a stream condition index (SCI) greater than 40, nitrate concentration
less than 0.35 mg/L and conductivity values less than 250 umhos/cm. Sites were selected based on these
four parameters in order to minimize the effect of confounding variables. The sites which satisfied these four
criteria were identified as reference locations for DO evaluation. Using available data, the 10th percentile DO
value was calculated to produce both state-wide and regional minimum DO standards. DO values below the
10th percentile value more would result in violation.
A modification of the reference site approach FDEP is considering to modify the DO criteria was used to
identify salinity-normalized TN and TP criteria for Clam Bay. Because Clam Bay appears to be co-limited by
both TN and TP were selected to evaluate water quality. The 90th percent prediction limit for the Estero Bay
Wetlands regression between TN or TP and conductivity was produced. The 90th percent prediction limit
was selected because 10 percent of the TN and TP values at the corresponding conductivity would be
expected to exceed the prediction limit. This approach is consistent with the calculation of the 10lh percentile
of reference waterbody DO values. Similar to the color grading system implemented in Tampa Bay, Clam
Bay would be assigned a green, yellow, or red designation annually based on the magnitude and duration of
exceedances of the 90th percent prediction limit. The color designation would then be used to identify if
management actions are required.
Within a calendar year, each individual TN and TP value collected within the waterbody would be compared
to the nutrientconductivity 90th percent prediction limit (Figure 14). An annual percent exceedance would be
calculated to determine the magnitude of exceedance. The minimum number of samples required to not
meet an applicable water quality criterion by FDEP to be included on the Planning or Verified list equates to
approximately 13 and 15 percent exceedance rates, respectively. To be consistent with the method
currently implemented by FDEP to identify impaired water bodies, if greater than or equal to 13 percent of
the TN or TP values in a calendar year exceed the 90th percent prediction limit, the duration of exceedance
would then be determined. Based on the duration of exceedance (one year or greater than one year), the
outcome designation is assigned. If less than 13 percent of the values exceed the 90th percent prediction
limit, then the outcome is "0". If the magnitude (i.e., 13 percent) and duration (i.e., >1 year) of the
exceedances are small, the outcome is "1". If the magnitude or duration of the exceedances is large, then
the outcome is "2". If both the magnitude and duration of the exceedances are large, then the outcome is "3".
The management response for Clam Bay would be determined based on the outcomes assigned to both the
TN and TP evaluations for the magnitude and duration of exceedance (Figure 15).
Figure 14.
Clam Bay conceptual water quality flowchart
Do :!e13% of all TN aJorTP
~ values from a calendar year .
exceed the 90% prediction limit
from thereferem:eW8ID?
. ,
No
Yes
;:::13%
Magnitudeof
exceedance
;:::15%
1 year
1 year
Atkins Doc Name I Doc Version I Doc Date I JobNumber
Collier County- Numeric Nutrient Criteria
Clam Bay- Development of Site-Specific Alternative Water Quality Criteria
CAC September 8, 2011
VII-5 Staff Reports
32 of 40
Figure 15.
Management response matrix using outcomes from both TN and TP evaluation.
Total Phosphorus
Total Nitrogen Outcome 0 Outcome 1 Outcome 2 Outcome 3
Outcome 0
Outcome 1
Outcome 2
Outcome 3
Annual management response actions would be identified based on the response to nutrient concentrations
of phytoplankton and DO, as well as impacts on water clarity (Figure 16). If the outcome of the TN and TP
evaluation was green, then no management actions are required. However, if the outcomes are yellow or
red then further evaluation of the effect of elevated nutrient concentrations on both phytoplankton biomass
and DO concentrations need to be reviewed. If there is no relationship between nutrients and chlorophyll-a
or DO, then no management actions are required. If there is a signification relationship, then the impact of
chlorophyll-a on the water clarity (Secchi disk depth) needs to be evaluated. If there is no relationship
between chlorophyll-a and water clarity, then no management actions are required. If there is a significant
relationship between chlorophyll-a concentrations and water clarity, an outcome designation of "yellow"
(indicative of small magnitude or duration of exceedances) identifies that management actions should be
taken to identify the potential causes and responses for the elevated nutrient levels. It the outcome
designation is "red" (indicative of a large magnitude or duration of exceedances), management actions
should be taken to implement recommended response tactics to reduce nutrient concentrations. The
"health" of Clam Bay would be assessed annually.
Figure 16.
Management response actions in response to various outcomes.
6r",en
; Response
evaluation
Yellow or Red
Not significant
(p>0,05)
Not significant
(p>0.05)
Evaluate water clarity
response to chlorophyil*a
IdentifY potential ca uses
and implement
recommended respol1se
Small difference or
short duration
large difference or
long duration
7.4. 2010 Clam Bay Management Assessments
Using the technique outlined in the previous section (7.3), Clam Bay was evaluated using water quality data
from 2010. A total of 97 TN or TP samples were collected in Clam Bay in the 2010 calendar year. For TN,
Atkins Doc Name I Doc Version I Doc Date I JobNumber
22
Collier County- Numeric Nutrient Criteria
Clam Bay- Development of Site-Specific Alternative Water
CAC September 8, 2011
VII-5 Staff Reports
33 of 40
Criteria
23 of the 97 (24%) samples exceeded the 90 percent prediction limit. Greater than 13 percent of the TN
values were in exceedance in 2010 and only one year of data is available for analysis. The outcome for TN
is "1". For TP, 3 of the 97 (3%) samples exceeded the 90 percent prediction limit, resulting in an outcome of
"0". In 2010, Clam Bay would be designated as "yellow". While there is a relationship between nutrients and
phytoplankton biomass, no relationship exists between nutrients and DO, or between chlorophyll-a and water
clarity. Therefore, no management actions are required and a "hold the line" approach is recommended.
Su Downstream Protective Values
In addition to the development of NNC for Clam Bay, proposed downstream protective values (DPVs) can be
estimated using the salinity:nutrient relationship. DPVs are generally assigned to the portion of a watershed
classified as freshwater in order to protect the downstream waterbodies. As such, it should be reasonable to
solve the salinity:nutrient relationships established for TN and TP in the Estero Bay Wetlands assuming a
salinity of 0, indicating inflows of stormwater runoff. Since the Estero Bay Wetlands has been identified as a
reference waterbody, establishing DPVs for Clam Bay based on a more "pristine" waterbody should result in
more adequate protection. For TN, the median DPV equates to 1.31 mg/L but could range to as high as 1.8
mg/L using the 90th percent prediction limit (Figure 12). For TP, the median DPV equates to 0.1 mg/L but
could range to as high as 0.25 mg/L using the 90th percent prediction limit (Figure 13). The proposed DPVs
calculated for various segments of the Charlotte Harbor estuary range from 1.43 to 2.61 mg/L for TN and
0.14 to 0.81 mg/L for TP (Janicki Environmental Inc., 2011). Thus, the proposed DPVs for Clam Bay are
within the range identified for Charlotte Harbor (Table 14).
Table 14. Minimum, median and maximum proposed DPV TN and TP concentrations for Charlotte
Harbor estuary compared to proposed Clam Bay DPV values.
Total Nitrogen Total Phosphorus
Charlotte Harbor Clam Bay Charlotte Harbor Clam Bay
Minimum 1.43 NA 0.14 NA
Median 1.64 1.31 0.29 0.10
Maximum 2.61 1.80 0.81 0.25
NA=not applicable
Atkins Doc Name I Doc Version I Doc Date I JobNumber
Collier County- Numeric Nutrient Criteria
Clam Bay- Development of Site-Specific Alternative Water Quality Criteria
CAC September 8, 2011
VII-5 Staff Reports
34 of 40
9. Literature Cited
Atkins 2011. Collier County Watershed Management Plan. Submitted to Collier County. Draft May 2011.
Appendix C EPA. 1986. Ambient Water Quality Criteria for DO. EPA 440/5-86-003.
Clark, P. 1992. Implications of a sea-level rise on the Sarasota Bay region. Pp. 7.1-7.24 in: Sarasota Bay
National Estuary Program. Sarasota Bay Framework for Action.
Collier County. 1987. Preliminary Analyses of Seagrass and Benthic Infauna in Johnson and Clam Bays,
Collier County, Florida. Department of Natural Resources Management, Collier County, Florida. 29
pp.
Collier County, 1997. Clam Bay Natural Resources Protection Area. Report. 85 pp.
Conservancy of Southwest Florida. 2010. Clam Bay Natural Resource Protection Area (NRPA) Benthic
Habitat Assessment. Submitted to Pelican Bay Owners Association, Pelican Bay Foundation, Inc.,
and the Mangrove Action Group. 116 pp.
EPA 1977. Field Studies - Parkshore and Clam Bay Systems Naples, Florida. Report from US EPA Region
IV, Surveillance and Analysis Division. Atlanta, GA. 57 pp.
EPA. 2010. Environmental Protection Agency 40 CFR Part 131 [EPA-HQ-OW-2009-0596; FRL-XXXX-X]
[RIN 2040-AF11] Water Quality Standards for the State of Florida's Lakes and Flowing Waters.
EPA. 2007. Total Maximum Daily Loads for the Northern and Central Indian River Lagoon and Banana River
Lagoon, Florida: Nutrients and Dissolved Oxygen. USEPA Region 4.
FDEP. 2008. TMDL Report: Dissolved Oxygen TMDLs for Hendry Creek (WBIDs 3258B and 3258B1). 39
pp.
FDEP. 2010. TMDL Report: Dissolved Oxygen TMDLs for Brushy Creek (WBID 1498) and Sweetwater
Creek (WBID 1516), and for DO and Nutrients in Lower Rocky Creek (WBID 1563). FDEP
Southwest District.
Fujioka, R.S. 2001. Monitoring coastal marine waters for spore-forming bacteria of faecal and soil origin to
determine point from non-point source pollution. Water Science and Technology. 44: 181-188.
Fujioka, R.S., Stan-Denton, C., Borja, M., Castro, J., and K. Morphew. 1999. Soil, the environmental source
of Escherichia coli and enterococci in Guam's streams. Journal of Applied Microbiology. (Symposium
supplement) 85: 83S-89S.
Janicki Environmental, Inc. 2010. Empirical Approaches to Establishing Numeric Nutrient Criteria for
Southwest Florida Estuaries. Prepared for Tampa Bay Estuary Program, Sarasota Bay Estuary
Program and Charlotte Harbor Estuary Program. 56 pp.
Janicki Environmental, Inc. 2011. Charlotte Harbor: Numeric Nutrient Criteria: Task 9- Downstream
Protection Values. Draft Letter Memorandum submitted to Charlotte Harbor National Estuary
Program.
Levesque, B., P. Brousseau, P. Simard, E. Dewailly, M. Monica, D. Ramsay, and J. Joly. 1993. Impact of
Ring-Billed (Larus delawarensis) on the Microbiological Quality of Recreational Water. Applied and
Environmental Microbiology 59 (4): 1228-1230.
Minnesota Pollution Control Agency. 2002. Regional Total Maximum Daily Load Evaluation of Fecal Coliform
Bacteria Impairments in the Lower Mississippi River Basin in Minnesota. Submitted to the U.S.
Environmental Protection Agency. October 2002.
PBS&J. 2008. Clam Bay Seagrass Assessment. Submitted to Collier County Coastal Zone Management
Department.
Atkins Doc Name I Doc Version I Doc Date I JobNumber
24
Collier County- Numeric Nutrient Criteria
Clam Bay- Development of Site-Specific Alternative Water Quality Criteria
CAC September 8, 2011
VII-5 Staff Reports
35 of 40
PBS&J, 2009. Clam Bay System: Data Collection and Analysis. . Submitted to Collier County Coastal Zone
Management Department.
PBS&J.2010. Technical Memorandum: Summary of Preliminary Findings on Sediment Studies. Submitted
to Collier County.
Tomasko, DA, and E. H. Keenan. 2010. Potential Impacts of Sea Level Rise on Sarasota Bay
Seagrasses. In "Proceedings, Tampa Bay Area Scientific Information Symposium, BASIS 5: 20-23
October 2009. St. Petersburg, Fl." S.T. Cooper (ed.) p. 463-477.
Atkins Doc Name I Doc Version I Doc Date I JobNumber
25
CAC September 8, 2011
VII-5 Staff Reports
36 of 40
David A. Tomasko
Integrated Water Resources, Atkins North America
4030 West Boy Scout Boulevard, Tampa, Florida 33607
Email: David.tomasko@atkinsglobal.com
Telephone: 1.813.282.7275
Direct Telephone: 1.813.281.8346
Fax: 1.813.636.8583
@ Atkins Ltd except where stated otherwise.
The Atkins logo, 'Carbon Critical Design' and the strapline
'Plan Design Enable' are trademarks of Atkins Ltd.
CAC September 8, 2011
Vll-5 Staff Reports
37 of 40
Standards and Assessment Section Comments on
Collier County: Numeric Nutrient Criteria
Clam Bay-Development of Site-Specific Alternative Water Quality Criteria
(Atkins July 2011 Draft)
The Atkins proposal represents an innovative approach that potentially would account for a greater level
of natural variability than a simple distributional reference approach. However, I cannot recommend
that DEP support the current proposal or adopt it as a water quality standard because the proposed
nutrients limits are overly stringent and perhaps unrealistic for Clam Bay. The document makes a
convincing argument that Clam Bay is a healthy system. Thus, it could be concluded that the existing TP
and TN concentrations are protective. The problem with the proposal is that it could lead to the
conclusion that Clam Bay requires nutrient reductions both in terms of within-bay concentrations as well
as within upstream waters (i.e., exceeding DPVs).
The problem originates from the fact that the conductivity to TP or TN relationships differ between Clam
Bay and Estero Bay Wetlands (Figures 1 and 2). The proposal sets nutrient targets based on the
regression line between conductivity and TN or TP for the Estero Bay Wetlands (EBW). Limits are then
set at the average conductivity (42A53 115) of Clam Bay. The corresponding limits are 0.60 mg/L and
0.057 mg/L for TN and TP, respectively. I would interpret these levels to represent long-term limits.
Inspection ofthe conductivity and TP regression relationship from Clam Bay (Figure 1) suggests that
0.057 mg/L might be a reasonable long-term TP limit for the Bay. However, inspection of the TN
regression lines suggests that 0.60 mg/L TN would be overly stringent (by 0.21 mg/L) for Clam Bay,
where a TN of 0.81 mg/L corresponds with 42A53 IlS.
0.4
- - ~ (lam Ba'f 9ft%Upper PrtQ:, limit
-E6WRfjression
J_55
v_3
0.25
0.2
Cil",&'V<
0_15
111
c.os
.u,45:lJ.6
1[lOOD
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~'::xlC(l
""'''''
5_
60000
8i',MiiJtl~ Fit d TP By (ON08"v",!.:"tf.'rt} Say Wdkplh
Trardorrnetirit L(;'K
~lif,np) -~ -1.3G91C4 - 1,2913~-S'CON)
BiVclti.HI.' fit d P B'i CONDBi.'y:'Cl<\tt1 8,,1'
Ttdll~Iornllfd Fit lag
!.ugnPJ '" -1.4;'634/- 3.3G31e.j'COND
T frllli--'-E-stim,lteSt(ru---t Rmij} .....Pi:ob>Tii
CAC September 8. 2011
VII-5 Staff Reports
38 of 40
Figure 1. Summary of regression analyses between conductivity and total phosphorus concentrations
for Clam Bay and Estero Bay Wetlands.
~
~ 1.5
~
05
""""
3t:oC;QC'
8i'.'<lrl.ate Fit ofm 8'{COND Bdv=[stero B.a'! \Vetl,mds
lilleMfIt:
TN =1.;(J~811.1.6641e-5~(f)tV
Si\'.~fL,tt' tit tlf fN ~'i (C'ND .by,(hlrl O;~1{
LineClIf'it
IN" 1.).:j'.)631 .1.u83l!'-.',.;C:OND
Figure 2. Summary of regression analyses between conductivity and total nitrogen concentrations for
Clam Bay and Estero Bay Wetlands.
The document proposes an interesting approach for assessing annual achievement of the long-term
limits. There are elements of the approach that DEP may want to consider, with some modification, for
reference or existing condition based nutrient thresholds. Monitoring data are initially assessed against
upper 90% prediction limits calculated from conductivity regression relationships to TN and TP for EBW.
The assessment is conducted by evaluating the percentage of measurements above the 90% prediction
limits as well as duration of exceedances on an annual basis (Figure 3A). The waterbody would be
assigned to a management outcome (status) if the nutrient data exceeded the frequency and duration
requirements. A green status indicates that Clam Bay meets both the TP and TN limits. Yellow or red
status indicates that the bay is not meeting either or both of the limits. An evaluation of chlorophyll and
DO responses to nutrient concentrations would be conducted if the bay were to be placed into either
yellow or red status (Figure 3B). If there is not a significant relationship, then no management action is
required; that is, the water is not impaired. However, if there is a significant relationship between
nutrient levels and chi-a, then the impact of chl-a on water clarity would be evaluated. Management
action would only be taken if there is a demonstrated significant response between chl-a and clarity or
between nutrient levels and DO.
GAG September 8, 2011
VII-5 Staff Reports
39 of 40
A.
No
IWtl3%"h1l1tl!\l...n
V.il'llJ~ft(l@i1l uf~tftM
Wlt~ttmglJ%'~timif
fr-omlher~-oort:WUHll
B.
Ev.lu3Ie1l!1V!<1pIookI0<1
d,ssolvMl_
""P""$<'to n~trI.nl
com:enttatkm:s
Siiflifj(>lnl
,.jr.'"to
-
'1'('"
lji\.';ll
l#alu.t....terclallty
f!llI>On",tothlolll1l!1j!1N
-
-
;,rn.;dl(IiiHi>("j"fI.""l
<,k'rldllliiij,Ul
i..;,rgt-lIlftHwlf',,(''-
lWi'"hlt.ll!;m
Figure 3. Flowchart describing the proposed a) conceptual assessment of 90th percent prediction limit
exceedances based on duration and frequency; and b) management responses to the variolJs
outcomes of the assessment. Outcome 0 equates to "Green" status in the second flowchart (8), while
Outcomes I, 2, or 3 equate to "Yellow" or "Red" status depending on duration of exceedance and
whether just one of the nutrient parameters exceeds the limit or both exceed.
This assessment approach is highly prone to trigger unnecessary assessments given the differences in
the conductivity to nutrient relationships between EBW and Clam Bay. DEP staff calculated 90%
prediction limits for both the EBW and Clam Bay (Figures 1 and 2). The Clam Bay prediction limit for TN
is well above the prediction limit for EBW indicating that Clam Bay would exceed the EBW derived limits
with a frequency significantly greater than the assumed 10 percent. For TP, the Clam Bay and EBW
prediction limits intersect at 27,500 IlS, meaning that below 27,500 IlS the EBW based limit would be
overly stringent (I.e., >10% exceedance), while above this conductivity level the EBW limit would not be
sufficiently protective (<10% exceedance). In other words, the TN limits are prone to high type I errors,
while the TP limits would be prone to both high type I and" errors depending on the conductivity.
Ultimately, application of the EBW derived limits to Clam Bay would require response evaluations more
frequently than is truly necessary.
The proposal suggests that DPVs can be derived by assuming a conductivity of zero based on either the
regression lines or 90% prediction limits. However, inspection of the data and regression analyses
suggest that the EBW DPVs would be overly stringent for Clam Bay. Both the TP and TN concentrations
associated with 0 115 are significantly greater than the values predicted for EBW (Figures 1 and 2). The
proposed DPVs would most likely necessitate substantial upstream nutrient reductions.
An alternative approach would be to develop existing condition nutrient thresholds using the
conductivity to TP and TN relationship from Clam Bay. The document already argues that Clam Bay is
not impaired at existing nutrient levels.
Specific Comments
1. Pages 9-10: What is the p value for the regression analysis between chlorophyll a and secchi
depth? Are there any transparency measurements for Clam Bay or is Secchi the best available
measure of water clarity?
2. Page 18: The 90% prediction limits referenced in Figures 12 and 13 appear to be two-sided
prediction intervals. Ifthat is the case, then the upper limit represents a level that would be
CAC September 8, 2011
VII-5 Staff Reports
40 of 40
expected to be exceeded only 5% of the time, not the assumed 10%. Note: 90% of the data are
expected to fall between a 90% prediction interval, with 5% above and 5% below. The
prediction limits shown in Figures 1 and 2 were calculated as 80% prediction intervals.
3. Page 19: The r-squared value for the TN-conductivity regression from EBW was 0.21. Although
conductivity only explains a small portion for the TN variability, it does explain substantially
more of the variance than a simple percentile of the reference distribution meaning that a
salinity normalized TN criteria would be less prone to statistical errors. Normalizing the nutrient
data to salinity (or conductivity) is a defensible approach.
4. Page 20: The r-squared for the EBW TP-conductivity regression is only 0.04. I do not believe
that this is a sufficiently robust relationship to derive criteria. The prediction interval is
extremely wide as a result of the uncertainty in the relationship. As stated in our general
comments, the relationship between TP and conductivity is much stronger for Clam Bay. A
"maintain the existing condition" SSAC could be developed using this relationship.
5. Page 21: The minimum number of samples exceeding applicable criteria required to place a
water on the verified or planning lists under the IWR were established to provide a statistical
test with a known and consistent confidence level. Reducing these numbers to set percentages
(I.e., 13 and 15%) will eliminate that consistency. The conceptual flowchart (Figure 14) should
reference the IWR planning and verified list binomial thresholds in order to maintain full
consistency with the statistical assumptions of the statistical test.
6. Figure 21, Figure 14: There will be a higher than a 10% probability of Clam Bay being placed in
Outcomes 2 or 3 for TN if the thresholds are developed based on EBW. Likewise, there will be a
greater than 10% chance of Clam Bay TP being list in Outcomes 2 or 3 during low salinity years.
7. Page 22, Figure 16: Overall, I believe that the assessment approach has a lot of merit and is
analogous to the biological verification process proposed by DEP for freshwaters. I would
recommend that a hard chlorophyll a threshold (e.g., 11Ilg/L) be added to the response
assessment; that is, Clam Bay would be considered impaired for nutrients ifthe chlorophyll a
concentration exceeded the threshold and there is a statistically significant relationship
between either nutrient and chlorophyll.
CAC September 8, 2011
VII-5-a Staff Reports
1 of 11
From:
To:
Subject:
Date:
Importance:
McAIDinGarv
HambriahtGail
FW: Technical memorandum on NNC for Clam Bay
Wednesday, September 07, 2011 3:20:46 PM
High
Please add this to the CAC agenda - Staff reports item 5 and post it.
From: Frydenborg, Russel [mailto:RusseI.Frydenborg@dep.state.f1.us]
Sent: Wednesday, September 07, 2011 1:52 PM
To: 'Tomasko, David A'; Weaver, Kenneth
Cc: Joyner, Daryll; Mandrup-Poulsen, Jan; McAlpinGary; KeyesPamela; Keenan, Emily C.G.H.; Bartlett,
Drew
Subject: RE: Technical memorandum on NNC for Clam Bay
Dave,
Ken Weaver and I have reviewed your August 31, 2011 Technical Memorandum that outlines
proposed numeric nutrient criteria for the protection of Clam Bay. We are pleased that you
thoroughly incorporated Ken's previous technical recommendations, and as such, we both find
that your proposed numeric nutrient approach is a scientifically defensible method to protect the
designated use of Clam Bay, while minimizing Type I errors.
This is good work.
Thanks, Russ
Please take a few minutes to share your comments on the service you received from the department
by clicking on this link D.E.E!. Customer Survev.
From: Tomasko, David A [mailto:David.Tomasko@atkinsglobal.com]
Sent: Wednesday, August 31, 2011 7:30 PM
To: Bartlett, Drew
Cc: Joyner, Daryll; Mandrup-Poulsen, Jan; Weaver, Kenneth; Frydenborg, Russel; McAlpinGary;
KeyesPamela; Keenan, Emily C.G.H.
Subject: Technical memorandum on NNC for Clam Bay
Drew:
Attached is a technical memorandum produced for Collier County's Clam Bay estuary. This memo
is a shortened version of the earlier report FDEP reviewed, with a focus on the derivation of the
salinity-normalized TN and TP targets. As per guidance from FDEP, the targets are based on data
from Clam Bay alone. However, the longer back-up report will include a comparison of Clam Bay's
nutrient vs. salinity relationship with that from FDEP's reference WBID of Estero Bay Wetlands.
We've also used the upper 10th percentile limit for determining what is an appropriate TN or TP
concentrations (based on the salinity) and the percent of results that can "exceed" this guidance is
based on the percent of exceedances required to place a water body into either the Planning or
Verified Impaired lists compiled by FDEP.
CAe September 8, 2011
VII-5-a Staff Reports
2 of 11
The larger report will also include results from our just-completed first round of source ID efforts
for bacteria, using DNA sequence tests with Bacteroidetes (which are obligate anaerobes) and the
human polyoma virus. Both results were negative. We also ran a test where we collected
droppings from birds (Ibis) in the mangrove canopy of Clam Bay and found that a single bird
defecation amount produced approximately 290,000 fecal coliform bacteria. This latter test not
only shows that birds can be a source of a laboratory's finding of "fecal coliform bacteria" but it
showed that a single bird's individual defecation event can produce enough bacteria to cause 180
gallons of water to exceed the 43 cfu / 100 ml standard for Class II waters. We are excited by
these findings, and will consider them in combination with a sanitary features survey to discuss the
likely sources of bacteria in Clam Bay.
Gary and others wanted me to express our gratitude to you and your staff for giving us the
guidance needed to develop these NNC for this important natural resource.
Thanks,
Dave
David A. Tomasko, Ph.D.
Senior Group Manager
Integrated Water Resources
ATKINS North America
Cell: +1 (813) 597 3897 Direct: +1 (813) 281-8346
4030 West Boy Scout Boulevard, Tampa, Florida 33607
Email: David.Tomasko@atkinsglobal.com I Web: www.atkinsalobal com/northamerica www.atkinsalobal.com
This electronic mail communication may contain privileged, confidential, and/or proprietary information which is the property of The
Atkins North America Corporation, WS Atkins pic or one of its affiliates. If you are not the intended recipient or an authorized agent of
the intended recipient please delete this communication and notify the sender that you have received it in error. A list of wholly owned
Atkins Group companies can be found at http://www.atkinsglobal.com/site-services/disclaimer
Consider the environment. Please don't print this email unless you really need to,
Under Flonda Law. e-mail addresses are public records If you do not want your e-mail address released In response to a public
records request. do nof send electronic mail to this entity, Instead, contact this office by telephone or in writing,
CAC September 8. 2011
VII.5-a Staff Reports
3 of 11
From:
To:
Subject:
Date:
Attachments:
McAloinGarv
HambriahtGail
FW: Technical memorandum on NNC for Clam Bay
Thursday, September 08, 2011 9:27:06 AM
revised NNC Quidance to FDEP 8-31-2011.docx
From: Tomasko, David A [mailto:David.Tomasko@atkinsglobal.com]
Sent: Wednesday, August 31, 2011 7:30 PM
To: Bartlett, Drew
Cc: Joyner, Daryll; Mandrup-Poulsen, Jan; Weaver, Kenneth; Frydenborg, Russel; McAlpinGary;
KeyesPamela; Keenan, Emily C.G.H.
Subject: Technical memorandum on NNC for Clam Bay
Drew:
Attached is a technical memorandum produced for Collier County's Clam Bay estuary. This memo
is a shortened version of the earlier report FDEP reviewed, with a focus on the derivation of the
salinity-normalized TN and TP targets. As per guidance from FDEP, the targets are based on data
from Clam Bay alone. However, the longer back-up report will include a comparison of Clam Bay's
nutrient vs. salinity relationship with that from FDEP's reference WBID of Estero Bay Wetlands.
We've also used the upper 10th percentile limit for determining what is an appropriate TN or TP
concentrations (based on the salinity) and the percent of results that can "exceed" this guidance is
based on the percent of exceedances required to place a water body into either the Planning or
Verified Impaired lists compiled by FDEP.
The larger report will also include results from our just-completed first round of source ID efforts
for bacteria, using DNA sequence tests with Bacteroidetes (which are obligate anaerobes) and the
human polyoma virus. Both results were negative. We also ran a test where we collected
droppings from birds (Ibis) in the mangrove canopy of Clam Bay and found that a single bird
defecation amount produced approximately 290,000 fecal coliform bacteria. This latter test not
only shows that birds can be a source of a laboratory's finding of "fecal coliform bacteria" but it
showed that a single bird's individual defecation event can produce enough bacteria to cause 180
gallons of water to exceed the 43 cfu /100 ml standard for Class II waters. We are excited by
these findings, and will consider them in combination with a sanitary features survey to discuss the
likely sources of bacteria in Clam Bay.
Gary and others wanted me to express our gratitude to you and your staff for giving us the
guidance needed to develop these NNC for this important natural resource.
Thanks,
Dave
David A. Tomasko, Ph.D.
CAe September 8, 2011
VII-5-a Staff Reports
4 of 11
Senior Group Manager
Integrated Water Resources
ATKINS North America
Cell: +1 (813) 597 3897 Direct: +1 (813) 281-8346
4030 West Boy Scout Boulevard, Tampa, Florida 33607
Email: David.Tomasko@atkinsglobal.com I Web: www.atkinsglobal.com/northamerica www.atkinsalobal.com
This electronic mail communication may contain privileged, confidential, and/or proprietary information which is the property of The
Atkins North America Corporation, WS Atkins pic or one of its affiliates. If you are not the intended recipient or an authorized agent of
the intended recipient please delete this communication and notify the sender that you have received it in error. A list of wholly owned
Atkins Group companies can be found at htlp:l/www.atkinsglobal.com/site-services/disclaimer
Consider the environment. Please don't print this email unless you really need to.
Under Fiorida law, e.mail addresses are public records If you do not want your e-mail address released in response to a public
records request, do not send electronic mail to this entity, Instead, contact this office by telephone or in writing.
CAC September 8, 2011
VIl-5-a Staff Reports
5 of 11
Project: Clam Bay Numeric To: Gary McAlpin, Collier County
Nutrient Criteria
Subject: Proposed Guidance From: David A. Tomasko, PhD
Emily Keenan, MS
Date: Aug 31 2011 cc:
The proposed Clam Bay Numeric Nutrient Criteria (NNC) provides a protective approach
to water quality evaluation and management for the waterbody of Clam Bay, in Collier
County. The proposed NNC are lower (more stringent) than the Florida Department of
Environmental Protection (FDEP) and Environmental Protection Agency (EPA) estuarine
screening criteria. The NNC for Clam Bay are based upon a nutrient: salinity relationship
that was developed for Clam Bay, after first comparing that relationship to a similarly
derived nutrient: salinity regression from a site previously used by FDEP to develop
nutrient targets for estuaries in Southwest Florida (Estero Bay Wetlands). These NNC
have to be considered in the context of salinity due to the relationship between nutrient
concentrations and salinity that is found in most estuaries. Since there is substantial
variability in the relationship between nutrient concentrations and salinity, management
responses due to deviations from the proposed NNC should be a function of magnitude
and duration of any exceedances from salinity-normalized NNC values, similar to the
resource management approach used by the Tampa Bay Estuary Program.
Clam Bay appears to be co-limited by both TN and TP (PBS&J 2008). Consequently,
salinity-normalized targets were developed for both TN and TP tar~ets were. To be
consistent with existing methodology used by FDEP, the upper 10t percentile prediction
limit for the regression between TN or TP and conductivity (from Clam Bay) was used for
target setting (Figures 1 and 2). The upper 10th percentil prediction limit was selected in
order to identify the number of TN and TP values at the corresponding conductivity that
exceed the upper boundaries of the relationship. This approach is consistent with the
calculation of the 10th percentile of DO values from reference waterbodies, as is used by
FDEP in ongoing target setting efforts. Clam Bay would be assigned differential
designation categories based on the magnitude and duration of exceedances of the upper
10th percentile prediction limit for salinity-normalized nutrient concentrations. The bay's
designation would then be used to identify the level of resource management actions
appropriate for any period of time examined (i.e., a single year or numerous years
combined).
Individual TN and TP values from the waterbody would be compared to the upper nutrient:
conductivity 10th percentile prediction limit (Figure 3). The minimum number of samples
required to not meet an applicable water quality criterion would be based on the approach
used by FDEP for determining if the percent of "impaired" water quality values are
supportive of a site being included on the Planning or Verified list. The number of
"violations" (i.e., number of TN or TP values higher than the upper 10th percentile of the
nutrient vs. salinity regression) would be compared to guidance shown in Tables 1 and 2.
CAC September 8, 2011
VII-5-a Staff Reports
6 of 11
If the number of exceedances is greater than or equal to the minimum number of
exceedance required for a waterbody to be classified as impaired, the duration of
exceedance would then be determined. Based on the duration of exceedance (one year
or greater than one year), an outcome designation is assigned. If the number of
exceedances is less than the minimum number of samples required based on sample size,
then the outcome would be a category of "0". If the number of exceedances and the
duration (i.e., >1 year) of the exceedances are small, the outcome would be a category of
"1 ". If the magnitude or duration of the exceedances is large, then the outcome would be
a category "2". If both the magnitude and duration of the exceedances are large, then the
outcome would be a category of "3". The management response for Clam Bay would be
determined based on the outcomes assigned to both the TN and TP evaluations for the
magnitude and duration of exceedance (Figure 4).
Management response actions would be identified based on presence or absence of co-
occuring phenomena that could be attributed to nutrient availability, in particular the
responses of phytoplankton and DO, as well as potential impacts to water clarity (Figure
5). If the outcome of the TN and TP evaluation was classified as "green", then no
management actions are required. However, if the outcomes are classified as "yellow" or
"red" then further evaluation of the effect of elevated nutrient concentrations needs to be
conducted. If there is no relationship between nutrients and chlorophyll-a or DO, then no
management actions are required. If there is a signification relationship between nutrients
and chlorophyll-a or nutrients and DO, then the impact of chlorophyll-a on the water clarity
(Secchi disk depth) would be evaluated as well as an evaluation of the annual chlorophyll-
a value to the 11 jJg/L standard found in F.A.C. 62-303-353. If there is no relationship
between chlorophyll-a and water clarity or annual chlorophyll-a concentrations are below
11 /Jg/L, then no management actions are required. If there is a significant relationship
between chlorophyll-a concentrations and water clarity, or annual chlorophyll-a
concentrations are above 11 jJg/L, an outcome designation of "yellow" (indicative of small
magnitude or duration of exceedances) signified that management actions should be
taken to identify the potential causes of the elevated nutrient levels. It the outcome
designation is "red" (indicative of a large magnitude or duration of exceedances),
management actions should be taken to implement recommended actions to reduce
nutrient concentrations. Using this approach, the health of Clam Bay would be assessed
on a regular basis, and appropriate resource management options, from no action needed
to implementation of corrective actions, would be determined.
CAe September 8, 2011
VII-5-a Staff Reports
7 of 11
Figure 1. Clam Bay proposed TN NNC based on Clam Bay linear regression with 80 percent
prediction limits.
2
..-.
-I
0, 1.5
E
---
c:
())
0) 1
E
."!:
Z
,<<1
~ 0..5
'"
""'-,
'"
'''>''-
o 0"", 0
'~ 0 Upper 1 Qth
"''QJ . percentile
D'~ ~ prediction
o "', OJ
o~ D limit
."-.,., om
"
o DO
o
42,4531JS
o
20000 40000 60000
Conductivity (uS)
80000
Figure 2. Clam Bay proposed TP NNC based on Clam Bay linear regression with 80 percent
prediction limits.
0.2
o
3
-
C)
E 0.15
---
fI)
::J
"-
o
-a 0.1
en
o
.s::.
n.
<<1 0.05
-
o
I-
o
o
o
o
42,4531JS
2.0000 40000 60000
Conductivity (uS)
80000
o
CAC September 8, 2011
VII-5-a Staff Reports
8 of 11
Figure 3.
Clam Bay conceptual water quality flowchart
No
Outcome 0
Yes
30'% confidence
(Planning list)
Magnitude of
exceedance
based on IWll
binomial
, distributions
90% confidence
(Verified list)
;> 1 year
>1 year
1 year
1 year
,
OuttOmel
Outcomel
Outcome 2
Outcome3
Table 1. Minimum number of samples not meeting an applicable water quality criterion needed to
put a water on the planning list with at least 80% confidence (Table 1 from F.A.C. 62-303)
Sample sizes Are lis ted if they Sample Are listed if they have
have at least this # of SIze s at least this # of
samples that do not samples that do not
From To me eta criterion From To meet a criterion
10 15 3 256 264 31
16 23 4 265 273 32
24 31 5 274 282 33
32 39 6 283 292 34
40 47 7 293 301 35
48 56 8 302 310 36
57 65 9 311 320 37
66 73 10 321 329 38
74 82 11 330 338 39
83 91 12 339 348 40
92 100 13 349 357 41
101 109 14 358 367 42
110 118 15 368 376 43
119 126 16 377 385 44
127 136 17 386 395 45
137 145 18 396 404 46
CAe September 8, 2011
VII-5-a St3ff Reports
9 of 11
Sample sizes Are lis ted if the y Sample Are listed if they have
have at least this # of SIze s at least this # of
samples that do not samples that do not
From To meet a criterion From To me eta criterion
146 154 19 405 414 47
155 163 20 415 423 48
164 172 21 424 432 49
173 181 22 433 442 50
182 190 23 443 451 51
191 199 24 452 461 52
200 208 25 462 470 53
209 218 26 471 480 54
219 227 27 481 489 55
228 236 28 490 499 56
237 245 29 500 500 57
246 255 30
Table 2. Minimum number of samples not meeting an applicable water quality criterion needed to
put a waterbody on the Verified list with at least 90% confidence (Table 3 from F.A.C. 62-
303).
Sample sizes Are listed if they Samp Ie Are listed if they have
have at least this # of SIze s at least this # of
samples that do not samples that do not
From To meet a criterion From To meet a criterion
20 25 5 254 262 33
26 32 6 263 270 34
33 40 7 271 279 35
41 47 8 280 288 36
48 55 9 289 297 37
56 63 10 298 306 38
64 71 11 307 315 39
72 79 12 316 324 40
80 88 13 325 333 41
89 96 14 334 343 42
97 104 15 344 352 43
105 113 16 353 361 44
114 121 17 362 370 45
122 130 18 371 379 46
131 138 19 380 388 47
139 147 20 389 397 48
148 156 21 398 406 49
Figure 4.
CAe September 8, 2011
VII-5-a Staff Reports
10 of 11
Sample sizes Are listed if they Sample Are listed if they have
have at least this # of SIze s at least this # of
samples that do not samples that do not
From To me eta criterion From To meet a criterion
157 164 22 407 415 50
165 173 23 416 424 51
174 182 24 425 434 52
183 19'1 25 435 443 53
192 199 26 444 452 54
200 208 27 453 461 55
209 217 28 462 470 56
218 226 29 471 479 57
227 235 30 480 489 58
236 244 31 490 498 59
245 253 32 499 500 60
Management response matrix using outcomes from both TN and TP evaluation.
Total Phosphorus
Total Nitrogen Outcome 0 Outcome 1 Outcome 2 Outcome 3
Outcome 0
Outcome 1
Outcome 2
Outcome 3
Figure 5.
Management response actions in response to various outcomes.
Green
.
Response
evaluation
Not significant
(p>O.OS)
___._,___ Not significant
(p>O.OS)
, ICfentif'{potential CaUses
and implement
recommended response
Yellow or Red
Large difference or
long duration
CAe September 8, 2011
VII-5-a Staff Reports
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Small difference Ot
short duration
n::sponsf.1S
CAC September 8, 2011
VII-6 Staff Reports
1 of 39
FY 2012-13 Local Government Funding Request
Project Name: Collier County Beach Nourishment Proiect
Project Description: This project includes the yearly physical beach monitoring, biological
monitoring for the nearshore hardbottom, permitting, and design leading to renourishment in
2013/14. The project's goal is to optimize both cost and design.
The proposed nourishment project for 2013/14 is described in a recent engineering report (CPE
2011). The purpose of the study was to evaluate the effectiveness of existing structures and
beach fill design templates, and changes needed to resolve hot spots and improve project
performance and durability. The proposed design addresses the renourishment needs of the three
segments constructed as part of the 2006 renourishment project with an increased beach width
and heightalong with the consideration of including two additional small reaches adjacent to
Clam and Wiggins Passes. Structural changes (removal, modification or addition) or other
methods needed to meet the project objectives are also being considered for the upcoming
project in a modeling study.
The same borrow area (BA-Tl) is proposed as the primary sand source for use in the upcoming
renourishment project. The main objective of this study is to develop a design that will enhance
project performance and increase the project life to maintain a healthy beach for 10 years without
significant impacts to the natural resources within the project area. The design volume for the
expanded design is based on the quantity of sand needed to widen the construction profile to
provide 10 years of advanced nourishment. The design beach width remains the same as 2006
proj ect.
This design volume will be 874,000 cy and includes raising the berm 1 foot to accommodate the
natural rise in the beach elevation caused by recent storms. The berm will be raised from 4 ft-
NA VD to 5 ft-NA VD, with proper transition between the natural beach and berm system.
Additional areas for extra fill have been identified from an analysis of hot spots within the
County. These areas are either outside of the current project limits, or warrant special attention.
The two new areas that are proposed for the expanded project are located directly north of
Wiggins Pass and directly south of Clam Pass.
The Barefoot Beach project area, which is located between R14 and RI6.3, will be restored using
sand from an offshore borrow area, Tl. The level of restoration will be determined during final
design and compliment sand bypassed from the Wiggins Pass dredging project. The restoration
project will used approximately 100,000 cubic yards to restore the shoreline and the adjacent ebb
shoal. Based on modeling, beach placement closer to the inlet will have the greatest impact
toward restoring Barefoot Beach. Past disposal practices placed dredged material where it
creates a sediment deficit within a ~ mile north of the inlet's vicinity.
CAC September 8, 2011
VII-6 Staff Reports
2 of 39
Collier County
Long Range Budget Plan
FY 12/13 - Collier County Beach Renourishment
aj
~
BAREfOOT BEACH
(j)-
WiGGINS PASS
DEl~R'WIOOI~
STATE PARK
t
TALlAHASSEE
JACKSONVIU.E
VANDERBILT
~
"""--
--"-~ EXISTIN:;
r PIPElIN::
/; CORRIDOR
/i
I I
/ l
/ /
/
UJ
a
C5
SR800
\
I
,
\
\
t>4 660W)
/'
/
/
I
/
/
,
I
/ PARK SHORE
N eaoo::o
SR 856
N S5O()))
NAPLES
N 600{Xl0
SRM
LEGEND:
EXISTING PIPELINE CORRIDOR
Pf~OPOSED PIPELINE CORRfDOH
EXPANDED TEMPLATE
c::::=::::J
~
EZZ~:;z'J
t-;-:-;-;-;-;-;J
GULF
OF
MEXICO
",,1
Z\
~ \\",
I \...~
o 4000 8000"
1.;.....;1 I'
GHAPHIC SCALE IN FT "-"
FEMA TEMPLATE
EXISTING TEMPlATE
NEW SEGMENTS
L R70 FDEP MONUMENTS
NOTES:
L COORDINATES ARE IN FEET
BASED ON FLORIDA STATE
PLANE COORDINATE SYSTEM,
EAST lONE. NORTH .AAr'tERICA.\l
DATUM OF 1963 (N!\D63),
2, FILL WIDTHS ARE NOT TO SCALE
\
\" > ~I
~, ,'~:.f ~
\... \"
FIGURE 1. Project Location Map
"'I
~.'.
'"
oJ
The area south of Clam Pass from R-42 to R-44 is the second proposed expansion area to the
Collier County Renourishment Project. Pill to the north of Park Shore will stabilize the area,
acting as a feeder beach. Approximately 36,400 cubic yards is proposed within this area. The fill
will supplement sand bypassing at Clam Pass, which alone is insufficient. The design template
will be the same proposed for the Clam Pass dredging project.
CAC September 8, 2011
VII-6 Staff Reports
3 of 39
Collier County
Long Range Budget Plan
FY 12/13 - Collier County Beach Renourishment
The 2005/06 re-nourishment project consisted of the restoration, using approximately 665,000
cubic yards of hydraulic fill, and maintenance of up to eight miles of Gulf of Mexico shoreline
along unincorporated Collier County and the City of Naples. This project was completed in May
2006 with the main goal to avoid environmental impacts such as hard-bottom coverage and a
design project life of six to eight years. The borrow area (Tl) was located just over 33 miles
north-northwest of Vanderbilt Beach and was chosen due to the coarser sand availability which
will avoid near-shore hard-bottom coverage. A one acre artificial reef was constructed to satisfy
mitigation permit requirements. The performance of the beach in avoiding hardbottom coverage
has exceeded permit expectations, and the results of 4 years of physical monitoring indicate that
the beach can be widened without a significant increased risk of hardbottom impacts. The design
alternatives will incorporate the recently approved FEMA authorization.
In 1995/1996 much of the same project area was hydraulically nourished with approximately 1.2
million cubic yards.
Project Location: The City of Naples/Collier County Beach Renourishment Project is located
on the southwest Florida coastline in Collier County between Florida Department of
Environmental Protection monuments R-14 to R-16 (newly proposed) and R-22 to R-79. The
project consists of approximately 8 miles of critically eroded Gulf shoreline shown on Figure 1.
Use of Requested Program Funds: Funds requested for FYI2/13 will be used for annual
physical monitoring, biological monitoring, and turtle monitoring activities associated with the
2006 construction and design and permitting tasks in preparation of the upcoming renourishment
in FY 13/14.
Local Government Support
Does this sponsor have dedicated support staff whose sole priority is to manage beach erosion
control activities? Yes
Name Title Email Percent
Commitment
Gary McAlpin Director, Coastal Zone Gary McAlpin@colliergov. 100%
Mana2:ement net
Address 1: 3301 East Tamiami Trail Phone: 239-252-2966
W. Harmon Turner Bldg., Suite
103
Address 2: Naoles, Florida 34112 Fax: 239-252-2950
Quarterly Report Compliance:
Com liant
N
N
N
N
CAC September 8, 2011
VII-6 Staff Reports
4 of 39
Collier County
Long Range Budget Plan
FY 12/13 - Collier County Beach Renourishment
How will revenue for the local funding cost share be established?
Local funding for the project will be obtained by Collier County through a Tourist Development
Tax. This provides a dedicated long term funding source through a 'bed tax'. Collier County
levies a four (4%) percent Tourist Development Tax on all rental income received from
accommodations rented for six months or less.
The four-percent (4%) Tourist Development Tax revenue is allocated by the Tourist
Development Plan approved by the Board of County Commissioners as follows:
50% for beach park facilities or beach improvement, maintenance, renourishment, restoration
and erosion control, including pass and inlet maintenance shoreline protection, enhancement,
cleanup or restoration of inland lakes and rivers to which there is public access as these uses
relate to the physical preservation of the beach, shoreline or inland lake or river.
13.4% for County owned or operated museums, to acquire, construct, extend, enlarge, remodel,
repair, improve, maintain, operate or promote one or more county owned museums and for non-
County owned museums that are owned and operated by not-for- profit organizations and open
to the public.
36.6% for Advertising/Promoting and Special Events to bring tourism to Collier County.
Is the funding from a dedicated long term source for this project? Yes
Collier County has dedicated the majority of the Tourist Taxes to beach maintenance, including
funding projects within the City of Naples.
In order to acquire funding, a resolution from the local governmental entity must be
provided by the application deadline which declares:
· Support from the Sponsor for the Proposed Project
· Willingness to serve as the Local Sponsor
· Ability to provide the full Local Cost Share
· Funding Source
Has the local sponsor resolution been attached to the application fulfilling all of these
requirements? Yes, it will be provided after approval at a July 2011 board meeting.
This project is detailed in Collier County's 10-year Capital Plan for Beach Projects which has
been approved by Collier County Board of County Commissioners.
Has the State cost-shared in a feasibility or design phase of this project?
Yes
Previous State Cost Share percentage
36.2%
10-Year Proiect Schedule and 5-Year Estimated Bud2et
Does this project have Congressional Authorization?
Yes
CAC September 8, 2011
VII-6 Staff Reports
5 of 39
Collier County
Long Range Budget Plan
FY 12/13 - Collier County Beach Renourishment
Does this project have a Federal Project Cooperative Agreement?
No
What is the end date of the Federal Authorization?
n/a
Federal cost share available for this erosion control project: 75%
Vanderbilt, Park Shore, and Naples have FEMA Category G funds due to damage as a result of
Tropical Storm Fay. This has been included within the 5-year estimated budget under the
Federal Cost Share column at 75% of FEMA eligible cost. It is essential that construction be
funded by the State in a timely manner, since Federal (FEMA) funds are time limited with
restricted extension rules.
Schedule and Budget (Include estimated phases for 10 years and estimated project costs for
5 years.):
Year
Proposed
Method
Description
Total Federal Cost
Estimated Cost Share
State Cost
Share
Local Cost
Share
2012/2013
Renourishment
Phys, Biological
Phys, Biological
Renourishment
Renourishment
$91,975
243,872
$246,384
$67,463
18,422,088
2013/2014
2014/2015
2015/2016
2016/2017
2017/2018
2018/2019
2019/2020
2020/2021
2021/ 2022
Length of Project Boundary in Feet:
39,912 ft
Length of commercial or recreational property fronting the project shoreline:
10,760 ft
Percentage of project shoreline designated as commercial or recreational property
23.96%
Eligibility:
Access Points and Public Lodging Establishments:
See Attachments 1 to 4 for detailed listing and maps.
CAC September 8, 2011
VII-6 Stafi' Reports
6 of 39
Collier County
Long Range Budget Plan
FY 12/13 - Collier County Beach Renourishment
Comercial &
Reach Length (ft) Eligible Length (ft) Recreation
-------------------------------------- ---------------- ----------------------------- --------------------------
Barefoot Beach* 2,360 2,360 2,360
Vanc4:rbilt Beach 6,777 6,318 2,469
Park Shore/Clam Pass Park 11,400 2,206 2,844
~~P..!~~_~~~~~_____________________ _.__!2~~2~____ ---------_!~-'-~?_~---------- __________~19_~2_________
Total 39,912 29,277 10,760
Eligible Shoreline % 73.35% 26.96%
State Cost Share % * 41.94%
Cost Sharing Summary
Includes 2,260 feet of State Lands
The Collier County occupational licenses and the Florida Department of Businesses and
Professional Regulation licenses for the hotels listed on Attachment 1 are on file and can be
provided if required.
Additional Rankin!! Criteria
Will this project enhance or increase the longevity of a previously- constructed project?
Yes
The engineering report will fine tune the beach, structures, and sand bypassing to reduce project
cost and increase durability. The project life will be 10 years.
Will this project nourish a previously restored shoreline?
Yes
Rate of Erosion as determined by the Bureau based on long term data (ft/yr)
4.5 ft/yr
Severity of Erosion:
A majority of the project area has been designated by FDEP as critically eroded. The Naples
Beach area is currently experiencing severe erosion in the project area, losing an average of 6.4
ft/yr since June 2006. The Vanderbilt Beach and Pelican Bay project areas have been eroding at
a rate of 5.0 feet per year since construction of the 2006 project. The Park Shore project area has
eroded 5.4 feet since June 2006. Erosion within the total project area has averaged 4.5 ft/yr since
1996.
The newly proposed Barefoot Beach Segment is currently experiencing the greatest amount of
erosion within the project area. Barefoot Beach has eroded approximately -8.6 feet per year
since March 2001 with the largest amount of erosion occurring at R-16. The erosion at each R-
monument adjusted for fill placed is shown below:
CAC September 8, 2011
VII-6 Staff Reports
7 of 39
Collier County
Long Range Budget Plan
FY 12/13 - Collier County Beach Renourishment
Collier County Average Erosion Rates from 1996-2010
-1996-2004
-2006-2010
-Composile (199610 2010)
-2003-2009
-18.00
Barefoot Beach
Hot Spot
-16.00
-14.00
Doctors Pass
Hot Spot
-12.00 -;::
~
~
- 10.00 ~
...
;I
.c
U
-8.00 y
"
e
=
-6.00 <;
;;.
-4.00
-2.00
0.00
C~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~c~~~~~~~~~~~~~n~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
~t~~~~~~j~~~~~~~$~~~~~t~~~~~~~~~~~~~0~~~~k~t66~t~~~~~~~88~~~~~~~~~8~~~~~'~~~~~=
>0 * * * * * * * * * * * * * * * ..:!
Note: iil ef [;;;
t~)2:~~:::::donlY available from June 2000 to May 2004 for 1!6 FDEP R-Monumen; ~
2.) Accretional values are not shown. Represented by zero on the plot
FIGU
FIGURE 2. Erosion Trends throughout Collier County
Threat to Upland Structures:
The recession associated with a 25 year storm is approximately 167 feet using the curve shown
below developed for Captiva Island in 2010, which is in the county immediately to the north.
Based upon the Captiva modeling study within the region, 41 structures are threatened due to
recession from the 25-year storm.
Storm R..anion, S.p, 2009 CondlUons
AVlirage o1RB4,ft10~, CapUva,FL
350
300
i,250
~
! 200
S
:., 150
E
a
;.; 100
Jf _,I',.' ,
, '1--1
. -,l---J i
rJ:
{~
so
10
toO
1000
Return Period lyesfS)
FIGURE 3. Storm Recession, Captiva, FL
(error bars:l:: 1 standard deviation).
CAC September 8, 2011
VII-6 Staf1 Reports
8 of 39
Collier County
Long Range Budget Plan
FY 12/13 - Collier County Beach Renourishment
Project Benefits:
Shoreline development within the project area consists of over 29,000 linear feet of publicly
accessible beach. 6,318 linear feet (93%) of the Vanderbilt Beach property is commercial or
recreational. This includes four hotels, Delnor- Wiggins State Park and Collier County's
Vanderbilt Beach Road Park. 2,206 linear feet (19.4%) of the Park Shore property is zoned
commercial or recreational and eligible. Another 2,300 feet is Clam Pass Park, but although this
area is erosional, it is not designated as critically eroded. This includes three public access streets
(City of Naples). 18,393 linear feet (95%) of the Naples Beach property is zoned commercial or
recreational. This includes the City of Naples' Lowdermilk Park, two hotels and numerous
public access streets and walkways. The attached maps identify public beach access points,
hotels, and other commercial facilities within the project area. Threatened and endangered
marine turtles utilize the entire project area for nesting purposes although none of the areas
within the project area have been designated as a sea turtle refuge.
Periodic dredging and bypassing has taken place at Wiggins Pass, Clam Pass, Doctors Pass and
Gordon Pass in recent decades. The total volume of sand bypassed to adjacent beaches from the
four inlets since completion of the 1996 project is estimated at approximately 600,000 cubic
yards.
Miti2:ation of inlet effects:
Since December 2005, Doctors Pass has been dredge twice, for a total volume of 86,000 cy. All
of the material was by-passed south of the inlet to Lowdermilk Park. The State Strategic
Management Plan calls for bypassing 10,000 cy per year, which recent effort have exceeded.
Sediment bypassing has exceeded 100% of the goal. Bypassing has occurred at both Wiggins
Pass and Clam Pass to meet state and local non-numerical objectives.
Use ofInnovative Applications of Existing Technologies:
Current technologies in practice will be used for the upcoming renourishment project and
subsequent monitoring. In addition, an investigation to improve hot spot performance and tune
structures using modeling is planned. Sand performance has met expectations, and beach
widening is feasible without significant threat to nearshore hardbottom. Major outfall and groin
combinations will be redesigned to reduce their impact on the adjacent beaches and reduce hot
spot sizes.
Nourishment Interval (vears):
10 (2013/2014 proiect design)
Project Performance:
The next full nourishment is scheduled for FY 2013/2014 at the planned 7.5-year renourishment
interval. The 1996 project lasted 10 years between nourishment, which is the goal for the next
nourishment (CPE 2011).
The project was built between January 23, 2006 to May 23, 2006, with dredging starting on
February 21, 2006. Collier County's 8.5 miles of renourished shorelines include Vanderbilt
Beach, Pelican Bay, North Park Shore, Park Shore, and Naples Beach. These beaches were
renourished with an as-built sand volume of approximately 667,562 cubic yards of sand during
Collier County
Long Range Budget Plan
FY 12/13 - Collier County Beach Renourishment
CAC September 8,2011
VII-6 Staff Reports
9 of 39
construction. The project was constructed by Great Lakes Dredge & Dock Company (GLDD)
with two hopper dredges, the Sugar Island and the Manhattan Island. Dredge and fill operations
lasted a total of 92 days. All of the project areas were renourished with sand from the Borrow
Area T-l, which is located approximately 33 miles northwest of Delnor-Wiggins State Park.
Volumetric changes measured from the pre-construction November 2005 survey to the four year
post-construction in October 2010 measured 483,233 cubic yards remaining in the project area or
72% of the design volume. It appears that the shorelines are still recovering from the active
2004-5 and 2008 storm season where Tropical Storm Fay affected the project area.
Is this project being planned or constructed in cooperation with another local government?
Explain? Yes
Collier County and the City of Naples are jointly sponsoring this project, and monitoring for all
of Collier County projects is combined for economy.
Collier County
Long Range Budget Plan
FY 12/13 - Collier County Beach Renourishment
CAC September 8, 2011
VII-6 Staff Reports
10 of 39
ATTACHMENT 1
FUNDING ELIGIBILITY
COLLIER COUNTY BEACH RENOURISHMENT PROJECT
Vanderbilt Beach Se2:ment
Project Boundary: 350' south ofR22 to 500' south ofR30
Approximate Shoreline Length: 8,480'
Public Access
Delnor Wiggins State Recreation Area*
Vanderbilt Beach Road*
On-site
Spaces
355
155
Adjacent
Spaces
o
21
Total
Spaces
355
176
Oualifyin2: Hotels
La Playa
Ritz Carltont
Oualifyin2: Shoreline
360'
750'
Area determined to be publicly accessible
300' south ofR22 to 110' north ofT25
30' south ofR26 to R30.5t
Total Len2:th
2,640'
4,137'
Area determined to be critically eroded
R22.3 to R30.5
Total eligible shoreline length: 6,318'
Total project shoreline length: 6,777'
Percent eligible for State funding: 93.23%
State eligibility incorporates the total project length (critical and non-critical) and eligibility only recognizes publicly
accessible critically eroded shoreline.
*Primary beach access contains a minimum of 100 parking spaces and public restrooms.
tOverlap
706000
704000
702000
700000
.
1 inch = 700 feel
350
CAC September 8, 2011
VII-6 Staff Reports
11of39
t
Project Boundaries
D Public Beach Access & Parking
Zoning:
J:Jcommercial (2,077 Linear Feet f 25%)
Recreational (238 Linear Feet I 3%)
I'V Critical Erosion Area
... FDEP Monuments
Notes:
"f"'COO'rdinates are in feet based on the Florida
State Plane Coordinate System, East Zone,
North American Datum of 1983. (NAD83).
2. Date of Aerial Photography: 2009.
Gulf
Mexi
MflIlWIOC...II.ATIlII'llUU!yAltD
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~O..:1II1-3fl..I.Z
'AX:Stl-3II...1.
....ucJaI.....'I..............
700
Collier County
Long Range Budget Plan
FY 12/13 - Collier County Beach Renourishment
CAC September 8, 2011
VII-6 Staff Reports
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FUNDING ELIGIBILITY
COLLIER COUNTY BEACH RENOURISHMENT PROJECT
Park Shore & Clam Bay Park Seement
Public Access
Horizon Way
Vedado Way
Seagate Drive
Clam Pass Park
Project Boundary: R42 to 390' south ofR54 with a gap in the vicinity ofR-49 and R-50
Approximate Shoreline Length: 11,400'
On-site Parking Spaces
Metered Permit*
21 17
25 14
o 0
o 172
Adjacent
Spaces
o
o
38
o
Total
Spaces
38
39
38
172
Area determined to be publicly accessible
R42 to 494' south ofR44
1087' south ofR50 to 60' north ofR54
Total Leneth
2,206'
Area determined to be critically eroded
R50.5 to 390' south ofR54
Total eligible shoreline length: 2,206'
Total project shoreline length: 11,400'
Percent eligible for State funding: 19.35%
State eligibility incorporates the total project length (critical and non-critical) and eligibility only recognizes publicly
accessible critically eroded shoreline.
*Permit spaces are available to residents and the general public for the same price.
CAC September 8, 2011
VII-6 Staff Reports
130f39
Project Boundaries
DPublic Beach Access & Parking
Zoning:
LJCommercial (100 Linear Feet / 0.8%)
WRecreational (2,329 Linear Feet /18%)
/V'Critical Erosion Area
... FDEP Monuments
674000
t
)IInIlWMCAII.ATOII.Olll..aVAIlO
~CAII.ATOJtA.0II1OJ,JU31
~O":Hl-3""IOZ
'J,)(,Sthlfl...lI
...llCt<o..I1II,I"'~In..n.'
625
1,250
Feet
o
o
o
~
~
M
1 inch = 1,250 feef
CAC September 8, 2011
VII-6 Staff Reports
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Collier County
Long Range Budget Plan
FY 12/13 - Collier County Beach Renourishment
FUNDING ELIGIBILITY
COLLIER COUNTY BEACH RENOURISHMENT PROJECT
Naples Se2ment
Project Boundary: 1,050' north ofR58 to R79
Approximate Shoreline Length: 19,375'
On-site Spaces Adjacent Spaces Total
Public Access Public Permit** Public Permit** Spaces
Lowdermilk Park* 46 164 0 0 210
8th Avenue North 20 1 0 0 21
ih Avenue North 10 4 0 0 14
North Lake Avenue 19 20 0 0 39
6th Avenue North 5 5 0 0 10
5th Avenue North 0 0 0 0 0
4th Avenue North 11 4 0 0 15
3rd Avenue North 10 4 0 0 14
2nd Avenue North 12 4 0 0 16
15t Avenue North 11 6 0 0 17
Central Drive 8 4 0 0 12
15t A venue South 5 12 0 0 17
2nd A venue South 7 4 0 0 11
3rd Avenue South 8 6 0 0 14
4th Avenue South 8 7 0 0 15
5th A venue South 34 0 20 0 54
6th A venue South 4 8 0 0 12
ih A venue South 7 9 0 0 16
8th Avenue South 6 5 0 0 11
9th A venue South 11 4 0 0 15
10th A venue South 9 35 0 0 44
11 th A venue South 8 5 0 0 13
Broad Avenue 49 22 0 0 71
12th Avenue South 25 8 0 0 33
Pier Parking Lot 81 0 0 0 81
13 th A venue South 31 13 0 0 44
14th Avenue South 16 14 0 0 30
15th A venue South 10 7 0 0 17
16th A venue South 16 14 0 0 30
1 ih A venue South 7 3 0 0 10
18th Avenue South 12 13 0 0 25
19th A venue South 0 0 0 0 0
215t A venue South 0 0 0 21 21
*Primary beach access contains a minimum of 100 parking spaces and public restrooms
Collier County
Long Range Budget Plan
FY 12/13 - Collier County Beach Renourishment
CAC September 8, 2011
VII-6 Staff Reports
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**Permit spaces are available to residents and the general public for the same price
Oualifyine Hotels
Edgewater Hotel
Oualifyine Shoreline
265'
Area determined to be publicly accessible
85' north ofR58 to R79
Total Leneth
18,410'
Area determined to be critically eroded
R57.8 to R79
Total eligible shoreline length: 18,393'
Total project shoreline length: 19,375'
Percent eligible for State funding: 94.93%
State eligibility incorporates the total project length (critical and non-critical) and eligibility only recognizes publicly
accessible critically eroded shoreline.
*Primary beach access contains a minimum of 100 parking spaces and public restrooms.
670000
668000
666000
664000
662000
660000
658000
656000
654000
. Feet
1 inch = 1,500 feet
.. ..
.. ..
.. ..
o 0
g g
Doctors Pass
Gulf of
Mexico
t
750
1,500
CAC September 8,2011
VII-6 Staff Reports
160f39
Project Boundaries
CJPublic Beach Access & Parking
Zoning:
t::'J,Commercial (1,241 Linear Feet/6%)
mRecreational (939 Linear Feet /5%)
/'V Critical Erosion Area
.A. FDEP Monuments
Notes:
1, Coordinates are in feet based on the Florida
State Plane Coordinate System, East Zone,
North American Datum of 1983. (NAD83).
2. Date of Aerial Photography: 2009.
... N..... MC...Il...TON.OUU:V......O
ItOCAIlATllN,lILO/I.IllA:DQl
""0.''''-'311'''01
....1...OU...~...."'......1
CAC September 8, 2011
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Collier County
Long Range Budget Plan
FY 12/13 - Collier County Beach Renourishment
FUNDING ELIGIBILITY
COLLIER COUNTY BEACH RENOURISHMENT PROJECT
Barefoot Beach Seement
Project Boundary: R14 to 300' south ofR16
Approximate Shoreline Length: 2,360'
Public Access
Barefoot Beach Preserve*
On-site
Spaces
100+
Adjacent
Spaces
100+
Total
Spaces
200+
Area determined to be publicly accessible
R14 to 300' south ofR16
Total Leneth
2,360'
Area determined to be critically eroded
R14 to R16.3
Total eligible shoreline length: 2,360'
Total project shoreline length: 2,360'
State owned shoreline length:
County owned shoreline length:
2,260'
100'
Percent eligible for State funding: 100.0%
Cost Sharing with State Lands: 97.88 %
State eligibility incorporates the total project length (critical and non-critical) and eligibility only recognizes publicly
accessible critically eroded shoreline.
*Primary beach access contains a minimum of 100 parking spaces and public restrooms.
CAC September 8,2011
VII-6 Staff Reports
180f39
!&lwllt
Project Boundaries
~C:":,::::]1PublicIY-Owned Property (Beach Access)
c::JState Land
~ Critical Erosion Area
... FDEP Monuments
Notes:
1. Coordinates are in feet based on the Florida
State Plane Coordinate System, East Zone,
North American Datum of 1983. (NAD83).
2. Date of Aerial Photography: 2009.
3. Publicly-Owned Property and Beach Hotels
and Resort Condos provided by the
Collier County GIS Department.
t
KI1IIWMCAIIATOlllOULaYAltD
IOCAIIAlOlI.1'l.0ItDA.!W1
",ONl!:1I14~""Z
'All:5I14~"""
-1Ocoa....I.........II.'
250
500
1 inch ::= 500 feel
CAC September 8,2011
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FY 2012-13 Local Government Funding Request
Proiect Name: Wiggins Pass Inlet Management Plan Implementation
Proiect Description: The project's goal is to improve inlet conditions without the use of
structures and reduce erosion on adjacent beaches at Wiggins Pass, Collier County, FL. One
primary component of the new Wiggins Pass Inlet Management Plan Implementation is to
reduce the erosion of Barefoot Beach, which was been designated as critically eroded by the
state. The erosion caused by the current inlet position will be mitigated by distributing beach
quality dredged material with a modified balance to adjacent eroded shorelines and realignment
of the channel to reduce erosion. The proposed inlet management plan meets state criteria for
inlet management projects, which are described within the inlet ranking criteria below.
The updated inlet management plan will be implemented by straightening the inlet channel
layout and modifying bypassing, which in return will minimize erosion at the downdrift
shoreline. The designated dredge disposal locations and quantities will be modified and
relocated to increase management flexibility, reduce sediment loss to the system and impacts to
Barefoot Beach shoreline. A dynamic design will be incorporated into the maintenance plan for
the inlet so that long-term dredging can be reduced, thus increasing project life compared to
current methods and making the update inlet plan more cost effective than the previous inlet
management plan. Impacts to natural resources will be avoided or minimized. The project not
only addresses navigation, but also addresses improved sand bypassing, modifications to channel
dredging, improved locations for sand disposal and an update of the 1995 inlet management plan.
The goals for the Wiggins Pass improvement study as developed by Collier County and the
Wiggins Pass Modeling Evaluation Work Group are:
1. To provide a safe channel for boating
2. To address erosion at Barefoot Beach
3. To lengthen the dredge cycle and accomplish it with the least effect on the
environment
4. To provide a solution that is economically effective.
The Wiggins Pass Modeling Evaluation Work Group represented a broad group of local stake
holders appointed by the County government, including representatives of the Florida Park
Service.
There have been five new findings since the current plan for Wiggins Pass was formulated in the
1990's that will be addressed by the new plan:
I. The flood channel is migrating north significantly - Causes are both natural and man
induced
2. Net alongshore transport is to the north, but with periodic strong reversals detriment
3. Unbalanced bypassing has occurred to the north
4. The inlet and flood shoal are infilling from the north and south by a reoccurring sand
wave
Collier County
Long Range Budget Plan
FY 12/13 - Wiggins Pass Inlet Management Plan Implementation
CAC September 8, 2011
VII-6 Staff Reports
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5. The rock ledge/ hard substrate extends to both sides of the channel
These facts are the basis for the new design proposed in Wiggins Pass Engineering Reports (CPE
February 2010); http://bcs.deo.state.fl.us/env-prmt/collier/oending/O 142538 Wiggins Pass/008-
JC/ Aoolication/JCP-PDF%20Wiggins%20Pass%2002- 2010/ Attachment%20No. %2033%20-
%20Analvsis%200flIo20the%20 Effect%200n%20Coastal %20Svstem/ A ttachment%20N o. %203 3
a%20-%20Engineering%20Report:.pdf), submitted as Attachment No. 33a of the JCP permit.
An inlet management plan with modeling and permit application is currently in progress. The
modeling report (CPE 2009) for Wiggins Pass can be found at the following path:
http://bcs.deo.state.fl. us/env-onnt/collier/oending/O 142538 Wiggins Pass/008-
J C/ Aool i cation/J CP - PDF%20 Wiggins%20Pass%2002-
201 0/Wiggins%20Pass%20Modeling%20Report%200 12009%20Full%20Report.pdf
The project will be implemented in four phases. The phases include initial construction (Figure
I), major maintenance dredging, intermediate ebb channel dredging, monitoring, mitigation and
contingency plans. A Barefoot Beach nourishment will supplement the bypassing proposed in
this project to address past short falls and background erosion. The details for each phase are
summarized below. Almost every task listed below contributes to both navigation and inlet
management as defined by section 161.143 of Florida Statute.
1) Initial construction of straighten channel
i) Dredge compatible Sand from Ebb Channel - 45 kcy
ii) Dredge Flood Channel-28 kcy
iii) Dredge Incompatible sand and disposal of upland - 7 kcy
iv) Build Gulf beach and scour repair with compatible sand 35 kcy
v) Fill Meander with compatible sand -repairing shoreline vicinity of and at the
mangroves (45 kcy)
vi) Upland Disposal for 7.5 kcy of unsuitable sand
2) Major Maintenance Dredge - 50 kcy each 4 yr with disposal balanced to favor adjacent Gulf
shoreline with greatest need.
i) Place beach compatible sand in nearshore or ebb disposal areas to rebuild adjacent
shorelines and ebb shoal.
3) Intermediate Ebb Channel Dredging as needed
i) Excavate and clear ebb channel and laterally place about 8-10 kcy in the north ebb
shoal to promotes rebuilding it.
4) Create contingency, monitoring and inlet management plans
i) No direct mitigation expected
5) Nourish critical erosion area on Barefoot Beach & re-build Ebb Shoal every 10 years with
100,000 cy to supplement by-passing until the shoreline and shoal recovers.
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Collier County
Long Range Budget Plan
FY 12/13 - Wiggins Pass Inlet Management Plan Implementation
Figure 1. Project Illustration
The modeling studies (CPE 2009) indicate that improved inlet conditions and mitigation of
erosion on adjacent beaches can be achieved by redesigning the main channel and modifying the
placement location and quantity of the dredged material. The total initial cut volume estimate is
80,000 CY (Figure 1) and it will provide a prolonged maintenance interval. The maintenance
will include major maintenance dredging of approximately 50,000 CY each 4 years along with
intermediate ebb (surgical) channel dredging of approximately 8,000 CY as needed. This
restoration will provide additional sand for bypassing to Barefoot Beach, mitigating the historic
erosion problem in this area. Periodic bypassing to Delnor Wiggins State Park will be part of the
plan. Bypassing will be rebalanced to place approximately 70% of dredged sand north and 30%
south based on an analysis of coastal processes since the 1990's (CPE 2010). A straightened
inlet improves human engineering of the inlet, making it easier for boats to find the channel.
A nourishment of Barefoot Beach is being considered as a separate project to restore the
shoreline and adjacent ebb shoal with periodic nourishment of 100,000 CY, supplementing this
plan. This project will help restore the sediment deficit to the north.
In order to implement the inlet management study, four phases of the plan have been identified:
1. Prepare IMP Study and resubmit permit application and response to RAI #1, based on the
FDEP May 13, 2011 letter.
2. Prepare Plans & Specifications.
3. Implement Project
4. Implement next beach nourishment
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Collier County
Long Range Budget Plan
FY 12/13 - Wiggins Pass Inlet Management Plan Implementation
Project Location: The Wiggins Pass Project is located on the southwest Florida coastline in
Collier County between Florida Department of Environmental Protection monuments R-16 and
R-17 and the project is adjacent to approximately 2,300 feet of critically eroded Gulf shoreline.
Use of Requested Pro2:ram Funds: Funds requested for FYI2/13 will be used for final design
and initial construction of the project.
Local Government Support
Does this sponsor have dedicated support staff whose sole priority is to manage beach erosion
control activities? Yes
Name Title Email Percent
Commitment
Gary McAlpin Director, Coastal Zone GaryMcAlpin@colliergov. 100%
Management net
Address 1: 3301 East Tamiami Trail Phone: 239-252-2966
W. Harmon Turner Bldg., Suite
103
Address 2: Naples, Florida 34112 Fax: 239-252-2950
Quarterly Report Compliance:
None, this is an initial request.
Revenue for the local cost share will be provided by: Local funding for the project will be
obtained by Collier County through a Tourist Development Tax. This provides a dedicated long
term funding source through a 'bed tax'. Collier County levies a four (4%) percent Tourist
Development Tax on all rental income received from accommodations rented for six months or
less.
The four-percent (4%) Tourist Development Tax revenue is allocated by the Tourist
Development Plan approved by the Board of County Commissioners as follows:
50% for beach park facilities or beach improvement, maintenance, renourishment, restoration
and erosion control, including pass and inlet maintenance shoreline protection, enhancement,
cleanup or restoration of inland lakes and rivers to which there is public access as these uses
relate to the physical preservation of the beach, shoreline or inland lake or river.
13.4% for County owned or operated museums, to acquire, construct, extend, enlarge, remodel,
repair, improve, maintain, operate or promote one or more county owned museums and for non-
County owned museums that are owned and operated by not-for- profit organizations and open
to the public.
36.6% for Advertising/Promoting and Special Events to bring tourism to Collier County.
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Collier County
Long Range Budget Plan
FY 12/13 - Wiggins Pass Inlet Management Plan Implementation
Is the funding from a dedicated long term source for this project? Yes
Collier County has dedicated the majority of the Tourist Taxes to beach maintenance, including
funding projects for inlet dredging that benefits adjacent shorelines. Collier County has a
dedicated staff.
In order to acquire funding, a resolution from the local governmental entity must be
provided by the application deadline which declares:
. Support from the Sponsor for the Proposed Project
. Willingness to serve as the Local Sponsor
· Ability to provide the full Local Cost Share
. Funding Source
Has the local sponsor resolution been attached to the application fulfilling all of these
requirements? Yes, it will be provided
Previous State cost-share for a feasibility or desien/permittine phase of this proiect:
The 1995 Inlet Management Plan was cost shared 50%. 50%
10-Year Proiect Schedule and 5-Year Estimated Budeet
Does this project have Congressional Authorization?
No
Does this project have a Federal Project Cooperative Agreement?
No
What is the end date of the Federal Authorization?
NA
Federal cost share available for this maintenance dredging project:
NA
Schedule and Budget (Include estimated phases for 10 years and estimated project costs for
5 years.):
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Collier County
Long Range Budget Plan
FY 12/13 - Wiggins Pass Inlet Management Plan Implementation
Proposed Total Federal Cost State Cost Local Cost
Year Method Description Estimated Cost Share Share Share
2012/2013 Design $250,000 $62,500
Construction 1,726,450 431,613
2013/2014 Design $100,000 $25,000
Monitoring 40,000 10,000
2014/2015 Construction $300,000 $100,000
Monitoring $41,616 $10,404
2015/2016 Design $100,000 $25,000
Monitoring 42,448 10,612
2016/2017 Construction $850,000 $212,500
MonitOrIng $43,297 10,824
2017/2018 omtormg
2018/2019 omtormg
2019/2020 eSlgn
2020/2021 onstructlOn
2021/ 2022 omtormg
Mappin!!- Maps are provided as attachments alon!! with ownership.
Length of Project Boundary in Feet: This is an Inlet Management Project, but public parks
stretch over a mile in either direction.
Length of commercial or recreational property fronting the project shoreline:
All adjacent shoreline is Public Park, which is recreational property.
Percentage of project shoreline designated as commercial or recreational property
100%
Eligibility: Access Points and Public Lodging Establishments:
Adjacent beaches are Parks with ample parking
Inlet Additional Rankin!! Criteria
Mitigation of Inlet Impacts
The Strategic Beach Management Plan for Wiggins Pass states the strategy for the inlet as
follows:
"Place beach quality maintenance dredged material on adjacent beaches north and south
of Wiggins Pass within areas of greatest need; monitoring and analysis of inlet effects."
The dredging that has occurred at the Pass has placed approximately 70% of the material in areas
with the greatest need. Recent findings have indicated that the beaches to the north of the pass
need 2.65 times the bypass material as the south in order to place the fill within areas of greatest
need. The updated inlet management plan currently proposes to rebalance the sediment
CAC September 8, 2011
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Collier County
Long Range Budget Plan
FY 12/13 - Wiggins Pass Inlet Management Plan Implementation
distribution based on the recent analysis (CPE 2010) which will increase targeted bypassing to
100%.
The Pass will have an annual bypassing goal of 14,500 cubic yards per year. During the past two
maintenance dredging in 2009 and 2011 for the pass have removed approximately 50,000 cubic
yards for each event, placing the majority of the material north of the pass to mitigate for past
imbalances.
An estimate of the annual quantity of beach quality material reaching the up drift
boundary of the inlet channel
An estimated 20,000 cubic yards per year are reaching the boundary of Wiggins Pass where sand
from both sides contributes to bypassing (CPE 2010).
Severity of Erosion
The north shoreline (R-14 to R-16) of Wiggins Pass was evaluated in order to analyze shoreline
changes to present. During the time span from 1988 to present, the northern shoreline area has
lost approximately -5.0 feet per year. The largest erosion has occurred at R-16. This monument
alone has lost approximately -12 feet per year since 1988.
The high losses that have occurred to the north of the inlet can be attributed to the northern
migration of the channel meander and inlet management practices, which allowed for an
approximate even disposal of dredged material on the north and south shorelines. From analysis,
it appears that in order to alleviate the erosion to the north, approximately 2.65 times more
dredged material needs to be placed on the shorelines to the north than the south. This material
needs to be targeted south of the nodal area at R-14.
The erosion has impacted the vegetation at Barefoot Beach, which is being pushed by the
northward migration of the flood channel, which has moved approximately 100 feet since the
1970's. This migration has both a natural and man induced component. The mangroves have
retreated a total of 52 feet since 1973 and 13 feet since 2002, which is a loss of about 0.3 acres.
The loss of the mangrove habitat is critical because of it being snook habitat. The proposed inlet
management strategy's goal is to prevent the erosion to the mangroves, which will restore the
snook habitat that is currently being lost. On the Gulf, the vegetation has retreated 194 feet in
some areas since 1973, and 123 feet in the last 8 years. Overall, the increased erosion north of
the inlet on the Gulfbeaches has caused 3.2 acres of vegetation to be lost since 2002.
This loss of habitat may affect important native species such as the gopher tortoise (Gopherus
polyphemus), a state-listed Species of Special Concern. Barefoot Beach is one of the remaining
few natural barrier islands along the southwest coast of Florida and is important habitat for the
gopher tortoise: a total of 712 burrows were recorded from June 13 through September 7 of
2009; 186 were recorded as Very Active; 277 were recorded as Active; 76 were recorded as
Inactive; 173 were abandoned. Considering the substantial loss of vegetation at the southern end
of the island, it is likely that gopher tortoise burrows have been lost to erosion in the past, and
their habitat at the south end of Barefoot Beach will continue to disappear without measures to
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Collier County
Long Range Budget Plan
FY 12/13 - Wiggins Pass Inlet Management Plan Implementation
mitigate for the erosion. The burrows along the edge of vegetation between approximately
R15+500 and R16 are threatened with imminent loss to erosion.
The proposed inlet management strategy will mitigate for the current erosive effects of the inlet.
By realigning the channel, stress upon the northern interior shoreline will be reduced, thus
reducing the mangrove loss that has historically occurred within this area. The inlet management
study also plans on rebuilding the north Gulf shoreline and ebb shoal that has been lost, which
will reduce wave energy, which in return will reduce erosion upon the neighboring shorelines.
The overall significance and anticipated success of the proposed project in balancing the
sediment budget of the inlet and adjacent beaches and addressing the sand deficit along the
inlet affected shoreline
Overtime, bypassing at Wiggins pass has moved towards an even split compared to an emphasis
to the south when dredging first began. Based on what has been learned during recent studies, a
ratio of 2.65: 1 favoring the north will rebalance dredge spoil distribution. This action in
combination with rebuilding the ebb shoal and a spoil area closer to inlet bodes well for success.
It is anticipated that the project will be successful in balancing the sediment deficit currently at
Barefoot Beach through findings brought to light from the updated inlet management study.
Approximately 2.65 times more dredged material will be placed on the shorelines to the north
than the south along with being placed within the areas of greatest need, which are closer to the
inlet than current practices. This will aid in alleviating erosional stresses on the northern
shoreline in conjunction to the channel realignment.
Details of the sediment budget and transport patterns can be found in the engineering report
(CPE 2010) (link provided within project description section) and modeling report (CPE 2009).
The extent to which existing bypassing activities at an inlet would benefit from modest,
cost-effective improvements when considering the volumetric increases from the proposed
project, the availability of beach quality sand currently not being bypassed to adjacent
eroding beaches, and the ease with which such beach quality sand may be obtained.
The inlet management study is cost effective due to the fact it proposes better management
practices, which will cause less erosion within the project area. A rebalance of the dredge
material in conjunction with new disposal locations will make best use of available sands. The
project will also improve navigation by the channel realignment while reducing erosion.
The interest and commitment of local governments as demonstrated by their willingness to
coordinate the planning, design, construction, and maintenance of an inlet management
project and their financial plan for funding the local cost-share for initial construction,
ongoing sand bypassing, channel dredging, and maintenance.
Collier County has been committed to maintaining Wiggins Pass since the mid 1990s, when the
first inlet management study was implemented. Since then, the inlet has been dredged on a
biannual basis. The County has been studying the inlet actively since 2006 through engineering
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Collier County
Long Range Budget Plan
FY 12/13 - Wiggins Pass Inlet Management Plan Implementation
and modeling studies in order to develop the most effective strategy to maintain the inlet and the
adjacent shorelines.
The previous completion or approval of a state-sponsored inlet management plan or local-
government-sponsored inlet management study concerning the inlet addressed by the
proposed project, the ease of updating and revising such plan or study, and the adequacy
and specificity of the plan's or study's recommendations concerning the mitigation of an
inlet's erosive effects on adjacent beaches.
An inlet management plan was previously done for Wiggins Pass in 1995, and is currently in the
process of being updated now. The engineering report (CPE 2010) has most of the elements of
an inlet management study. It will update the 1995 plans with better management methods by
quantifying amounts of material to dispose to the northern and southern shorelines and
identifying the best location for the disposal sites.
The degree to which the proposed project will enhance the performance and longevity of
proximate beach nourishment projects, thereby reducing frequency of such periodic
nourishment projects.
The project will aid in extending the design width at the newly proposed nourishment segment at
Barefoot Beach with the placement of beach quality dredged material, and the channel
realignment will reduce stresses upon the northern shoreline, which will reduce the erosion
within the area. The project will also enhance the nourishment project by recreating the ebb
shoal directly offshore of Barefoot Beach, which will help to alleviate erosion within the area.
Additional Rankin!! Criteria
Will this project enhance or increase the longevity of a previously- constructed project?
Yes, the proposed inlet management strategy will reduce erosion partially caused by the current
inlet management practices and help lengthen dredging intervals from 2 to 4 years within the
project area once complete, which will reduce impacts to the natural community. The human
engineering aspects of a straighter channel will go a long ways toward reducing the frequency of
major dredging.
Project Benefits:
The project will attempt to reestablish the historic shoreline and the ebb shoal size. Also, Gopher
tortoises utilize Barefoot Beach for nesting purposes.
Periodic dredging and bypassing has taken place at Wiggins Pass in recent decades. The total
volume of sand bypassed to adjacent beaches from maintenance dredging has been 498,650
cubic yards since 1984. Approximately 260,937 cubic yards of that fill has been placed to the
north, with the remaining 237,713 cubic yards being placed to the south of the inlet. The ratio
needs to be shifted to approximately 2.6: 1 in favor of the north, but monitored during each
dredging.
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Collier County
Long Range Budget Plan
FY 12/13 - Wiggins Pass Inlet Management Plan Implementation
Use of Innovative Applications of existing technologies:
Allow for natural inlet migration after implementation and use of intermediate (surgical) dredge
events to delay major dredge events and reduce cumulative quantities dredged. Utilization of
advanced computer modeling to refine the disposal location, channel dimensions, and trends in
equilibration.
Dredging Interval (years):
1
Project Performance:
Wiggins Pass was designed to be dredged at regular intervals of approximately 2 to 4 years but is
currently dredged at regular intervals of approximately 2 years or less to maintain navigable
depths for recreational boaters. The dredge channel extends from the inlet throat to about 1,200
feet offshore. Periodic dredging has occurred at the intersection of the interior channels. The
inlet has been dredged since 1984 under two previous permits, secured by the County.
Since maintenance dredging began in 1984, the overall erosion has increased along with the
magnitude of erosion experienced at beaches to the north. Initially, the beaches to the south were
erosional prior to the 1990s. Since 1992, the shoreline north of the inlet at Barefoot Beach has
retreated on average approximately 87 feet. The worst area of erosion is occurring at R16,
where, since 1992, it has lost approximately 437 feet of shoreline.
Overall, it appears that the current maintenance dredging practices are not adequately addressing
the northern losses at Barefoot Beach nor the stability of the dredged channel. Historic reports
indicated that sediment transport was from north to south, and erosion was higher south of the
inlet between 1957 and 1979. However, the recent volumetric data contrasts with that belief.
From 1979 to 2009, the area north of Wiggins Pass (R11 to R 16) eroded 252,926 cubic yards,
while the area south of the inlet has accreted 49,603 cubic yards. Prior to 1979, before
maintenance dredging, the erosion accretion pattern was reversed, with the north accretional.
Using these values along with the historic shoreline changes, it appears that more sand needs to
be disposed of at the north during maintenance dredging to reduce erosion on Barefoot Beach.
The amount of dredge disposal north and south of the inlet has been nearly equal since dredging
began in 1984. Lately, the trend is towards north disposal since 2001. An analysis was made to
calculate the disposal balance needed to make each area have an equal erosion rate. As an
example, the areas south of the inlet (R17 to R21) showed a gain of almost 50,000 CY since
1979, while the area north of the inlet (Rll to R16) lost 253,000 CY. To equalize the rate of
volumetric change in these areas since 1979, disposal volumes should have been 2.7 times
greater to the north (Barefoot Beach Park) than the south (Delnor Wiggins Park). This is a major
shift over past practices. Ultimately, this bypassing ratio should equalize stability of the
shoreline north and south of the inlet.
Navigation will be improved by straightening the channel through the flood and ebb shoal,
reducing both the need for dredging. Boaters have difficulty finding the channel in the S-shape
natural alignment. The S-shape is caused by a long term natural process where growth in the
flood shoals pushes the flood channel north with a corresponding rotation of the ebb shoal to the
south. Human engineering factors are needed for improved channel design.
CAC September 8, 2011
VII-6 Staff Reports
29 of 39
Collier County
Long Range Budget Plan
FY 12/13 - Wiggins Pass Inlet Management Plan Implementation
Is this project being planned or constructed in cooperation with another local government?
Explain? No
ATTACHMENT A
FUNDING ELIGIBILITY
Wil!1!ins Pass Inlet Mana2ement Plan Implementation
2009 Project Boundaries:
Project Boundary: R16 south to north R17
Public Access
DelnOf Wiggins State Recreation Area*
Barefoot Beach
On-site
Spaces
355
362
Adjacent
Spaces
o
Total
Spaces
355
362
Area determined to be publicly accessible
Both adjacent shorelines
Area determined to be critically eroded
R14 to R16.3
Fundin2 Rate:
75% for IMP
CAC September 8, 2011
Vll~6 Staff Reports
30 of 39
~
Project Boundaries
:""']Publicly~Owned Property (Beach Access)
c::JState Land
IT:}] Beach Disposal Area
c::J Dredge Area
~ Critical Erosion Area
.... FDEP Monuments
Notes:
1. Coordinates are in feet based on the Florida
State Plane Coordinate System, East Zone,
North American Datum of 1983. (NAD83).
2. Date of Aerial Photography: 2009.
3. Publicly-Owned Property and Beach Hotels
and Resort Condos provided by the
Collier County GIS Department.
t
M.tIlW.,CAJtArOIl.OUUIIYMD
"CAJtATON."'-ClJtlDADoI:I1
1It40..'5114....'.1
'....'5114"4111
_~...tol,t.....Io..lI.'
350 700
Collier County Beach
Long Range Beach Plan
Wiggins Pass
Inlet Management Plan Implentation
Feel
1 inch = 1,000 feet
o
o
o
...
..
..,
CAC September 8, 2011
VII-6 Staff Reports
31 of 39
FEMA Correspondence
Collier County Beach Projects
From: Mcleod, Chad (Martinez) rmailto:Chad McLeod@)martinez.senate.qovl
Sent: Tuesday, February 24,20092:30 PM
To: mudd-.i
Cc: Sheffield Michael; wight_d
Subject: DHs/FEMA Funding for Collier County, Florida
Mr. Mudd,
I just wanted to let you know (in case you haven't already heard) that FEMA has announced two federal
grants for Collier County associated with Tropical Storm Fay. The information is below.
I hope all is well in Naples.
Chad McLeod
Southwest Florida Regional Director
U.S. Senator Mel Martinez
2120 Main Street, Suite 200
Fort Myers, FL 33901
239.332.3898
239.332.3447 fax
COllIER County
Total Project Cost - This Version $7,982,133.96 - FEMA Share
$5,986,600.47 (JCCC02 = PW01146)
This project involves the re-nourishing of Vanderbilt Beach/ Park Shore
Beach and Naples Beach as a direct result of Tropical Storm Fay. These
three beaches are to be restored to pre-storm conditions, as defined by the
previous beach re-nourishment project in 2006/07 completed under Collier
County Beach Renourishment Bid No. 05-3584. Work will consist of
mobilizing offshore dredge equipment and pumping, placing and shaping
fV174/576 CY of beach-quality sand that meets approved geotechnical
specifications. The offshore borrow area for the approved sand is located
approximately 33.1 miles northwest of Delnor-Wiggins State Park. Sand is to
be placed and shaped per engineering specifications to restore these
beaches to pre-storm design elevations.
Total Project Cost -This Version $2,822,578.00 - FEMA Share -
$2,116,933.50 (JCCCOl = PW00561)
CAC September 8, 2011
VII-6 Staff Reports
32 of 39
An estimated 76,728 CY of sand along 4,383 linear feet of beach was eroded
form the southwestern tip of Marco Island by wave action during Tropical
Storm Fay. The purpose of this project is to restore sand to this improved
section of beach. Most recently, in 2007, the applicant completed the South
Marco Island Beach Nourishment Program over this same project area in the
wake of Hurricane Wilma.
FEMA obligates funding for these projects directly to the State. It is the
State's responsibility to ensure that eligible sub-grantees receive these
awards. Following the State's review process and upon receipt of
appropriate documentation, they will provide funds to the sub-grantees on a
reimbursable basis.
From: Seibert, Robert rmailto:Robert.5eibert(6lem.mvflorida.com)
Sent: Friday, August 13, 2010 4: 17 PM
To: McAlpinGary
Subject: PW Numbers for TS Faye Beaches
Gary,
Here is the PW numbers for the two Beach Projects.
JCCCOl = PW00561 =$2,822.578.00 in eligible funding.
JCCC02 = PW01146 = $7,982,133.96 in eligible funding.
These are available in FLPA where you can download or print the PWs and note the Federal amount,
Admin Costs, State Share, which will give you the $ total available to Collier County. If you have any
questions on what you see, please give me a call.
Have a good weekend,
Bob
Robert M. (Bob) Seibert
Lead Deputy Public Assistance Officer
Florida Division of Emergency Management
Phone: 407-268-8609
Blackberry: 850-528-5096
email: robert.seibert(a)em.mvflorida.com
CAC September 8, 2011
VII-6 Staff Reports
33 of 39
FY 2012-13 Local Government Funding Request
Project Name: South Marco Island Beach Renourishment
Project Description: This project includes the yearly physical beach monitoring, beach tilling,
and turtle/shorebird monitoring leading to beach nourishment and improved structures in
2012/2013. All the monitoring activities are required by the FDEP permit.
Marco Beach was restored in early winter 2007 using approximately 180,000 cubic yards of
hydraulic fill along 4,500 feet of Gulf of Mexico shoreline at City of Marco Island. The project
area was previously renourished in 1997. The same borrow area from the 1997 project was used
for the 2007 project which was the maintenance dredging of Caxambas Pass. It was completed
in March 2007. The design project life for the recent nourishment is between six to eight years.
Collier County plans to place approximately 104,000 cubic yards of beach compatible material to
restore approximately 4,400 feet along South Marco Island. The beach fill will be within the
2005 permitted project limits. The main goals of the upcoming renourishment project are for
restoring storm protection, natural resource habitats, and recreational beach areas to offset the
storm damage caused by Tropical Storm Fay in 2008. The project being designed for the next
nourishment is currently undergoing a modeling study considering structural alternatives to hold
sand within the project area.
Project Location: The South Marco Island Beach Renourishment Project is located on the
southwest Florida coastline of Collier County between Florida Department of Environmental
Protection monuments R-143 and beyond R-148 to the terminal groin. The project's borrow area
is the 1997/2007 Caxambas Pass Borrow Area. A supplemental borrow area is the Cape
Romano Shoal, but is not anticipated on being needed.
Use of Requested Program Funds: Funds requested for FYI2/13 will be used for annual
physical monitoring and turtle monitoring activities associated with the 2007 construction
required by permits. Funds wills also be used to complete the modeling study, preliminary
design, final design, permitting, and construction of the next renourishment project.
Local Government Support
Does this sponsor have dedicated support staff whose sole priority is to manage beach erosion
control activities? Yes
-
Name Title Email Percent
Commitment
Gary McAlpin Director, Coastal Zone GaryMcAlpin@colliergov. 100%
Management net
Address 1: 3301 East Tamiami Trail Phone: 239-252-2966
W. Harmon Turner Bldg., Suite
103
Address 2: Naples, Florida 34112 Fax: 239-252-2950
CAC September 8, 2011
VII-6 Staff Reports
34 of 39
Collier County
Long Range Budget Plan
FY 12/13 - South Marco Island Beach Renourishment
Quarterly Report Compliance:
Com liant
N
N
N
N
How will revenue for the local funding cost share be established?
Local funding for the project will be obtained by Collier County through a Tourist Development
Tax. This provides a dedicated long term funding source through a 'bed tax'. Collier County
levies a four (4%) percent Tourist Development Tax on all rental income received from
accommodations rented for six months or less.
The four-percent (4%) Tourist Development Tax revenue is allocated by the Tourist
Development Plan approved by the Board of County Commissioners as follows:
50% for beach park facilities or beach improvement, maintenance, renourishment, restoration
and erosion control, including pass and inlet maintenance shoreline protection, enhancement,
cleanup or restoration of inland lakes and rivers to which there is public access as these uses
relate to the physical preservation of the beach, shoreline or inland lake or river.
13.4% for County owned or operated museums, to acquire, construct, extend, enlarge, remodel,
repair, improve, maintain, operate or promote one or more county owned museums and for non-
County owned museums that are owned and operated by not-for- profit organizations and open
to the public.
36.6% for Advertising/Promoting and Special Events to bring tourism to Collier County.
Is the funding from a dedicated long term source for this project? Yes
Collier County has dedicated the majority of the Tourist Taxes to beach maintenance, including
funding projects within Marco Island. Collier County has a dedicated staff.
In order to acquire funding, a resolution from the local governmental entity must be
provided by the application deadline which declares:
· Support from the Sponsor for the Proposed Project
· Willingness to serve as the Local Sponsor
· Ability to provide the full Local Cost Share
· Funding Source
Has the local sponsor resolution been attached to the application fulfilling all of these
requirements? Yes, it will be provided.
This project is detailed in Collier County's lO-year Capital Plan for Beach Projects which has
been approved by Collier County Board of County Commissioners.
CAC September 8, 2011
VII-6 Staff Reports
35 of 39
CoIlier County
Long Range Budget Plan
FY 12/13 - South Marco Island Beach Renourishment
A County Commission resolution specifically in support of this individual project is on file at
DEP offices.
Has the State cost-shared in a feasibility or design phase of this project?
Yes
Previous State Cost Share percentage
20.88%
10-Year Proiect Schedule and 5-Year Estimated Budf!et
Does this project have Congressional Authorization?
No
Does this project have a Federal Project Cooperative Agreement?
No
What is the end date of the Federal Authorization?
n/a
Federal cost share available for this erosion control project: 75%
Marco Island Beach has FEMA Category G funds due to damage as a result of Tropical Storm
Fay. This has been included within the 5-year estimated budget under the Federal Cost Share
column at 75% of eligible cost.
Schedule and Budget (Include estimated phases for 10 years and estimated project costs for
5 years.):
Year
2012/2013
2013/2014
2014/2015
2015/2016
2016/ 2017
2017/2018
2018/2019
2019/2020
2020/ 2021
2021/ 2022
Proposed
Method
Total Federal Cost
Estimated Cost Share
State Cost
Share
Local Cost
Share
Description
Monitoring
Construction
$58,040
$2,025,000
$0
Momtonng
Monitoring
Monitoring
Momtonng
Momtonng
Momtonng
Momtonng
Momtonng
omtonng
Length of Project Boundary in Feet:
4,700 ft
Length of commercial or recreational property fronting the project shoreline:
2,011ft
Percentage of project shoreline designated as commercial or recreational property
42.78%
CAC September 8, 2011
VII-6 Staff Reports
36 of 39
Collier County
Long Range Budget Plan
FY 12/13 - South Marco Island Beach Renourishment
Eligibility:
Access Points and Public Lodging Establishments:
Project Boundary: 690' south ofR143 to 600' south ofR148
Approximate Shoreline Length: 4,700'
Public Access
Swallow A venue
Parkin!:! Spaces
70 (on site)
Oualifyin!:! Hotels
Hilton Hotel
Radisson Hotel
Oualifyin!:! Shoreline
510'
350'
The Collier County occupational licenses and the Florida Department of Businesses and
Professional Regulation licenses for the following hotels are on file and can be provided if
required.
Area determined to be publicly accessible
330' north ofR144 to 500' north ofR145
20' north ofR146 to R148+600
Total Len!:!th
860'
1,880'
Area determined to be critically eroded
R143 to R148
Total eligible shoreline length: 2,740'
Total project shoreline length: 4,700'
Percent eligible for State funding: 58.30%
State eligibility incorporates the total project length (critical and non-critical) and eligibility only recognizes publicly
accessible critically eroded shoreline.
See attached map of eligible shorelines.
Additional Rankin!:! Criteria
Will this project enhance or increase the longevity of a previously- constructed project?
Engineering is find tuning structures to increase durability and sand retention on the island,
which will increase project life Yes
Will this project nourish a previously restored shoreline?
Yes
Rate of Erosion as determined by the Bureau based on long term data (ft/yr)
7.2 ft/yr
CAC September 8, 2011
VII-6 Staff Reports
37 of 39
Collier County
Long Range Budget Plan
FY 12/13 - South Marco Island Beach Renourishment
Severity of Erosion:
The project area's shoreline has been designated by PDEP as critically eroded. Using the
January 2007 and February 2011 monitoring surveys, the MHW shoreline change was found to
be eroding at an average rate of -7.2 feet per year.
Project Benefits:
2,011 linear feet (42.78%) of the Marco Island Beach property is zoned commercial or
recreational. This includes two hotels/resort condos and a public access point with parking
across the street.
Periodic dredging has taken place at Caxambas Pass. The total volume of sand dredged and
hydraulically pumped to the adjacent beach from Caxambas Pass since 1990 is estimated at
800,000 cubic yards.
Though Collier County has no federally designated sea turtle refuges, loggerhead sea turtles nest
throughout the county, and this project will enhance those opportunities. Beach tilling will
directly support turtle nesting by decreasing beach sand compaction.
Use of Innovative Applications of Existing Technologies:
Improvements to the combined breakwater and groin system at the south end of the project area
are being investigated for improvements to control sand being lost off the south end of the island.
This investigation is being completed through a computer modeling study. It will increase the
project life.
Nourishment Interval (years):
6-8 years
Project Performance:
Beach fill material was dredged from Caxambas Pass and placed between FDEP R-monuments
R-145 to R-148. Overall, approximately 176,000 cubic yards of sand were placed onto the
beaches of South Marco Island.
North of R-146, approximately 87% of the fill volume remains in the template, while only 51 %
of the volume remains within the template south ofR-146 to the groin. With respect to beach fill
width, north of R-146, 100% of the beach fill width remains in place, while on average, only
33% of the beach fill width remains in place south ofR-146 to the groin. Overall, approximately
64% of the 2007 project volume remains within the permitted fill template, and on average,
approximately 67% of the beach fill width remains within the project area as measured in
February 2011.
Is this project being planned or constructed in cooperation with another local government?
Explain ? Yes
Collier County and the City of Marco Island are jointly sponsoring this project. The project
combines beach nourishment with inlet dredging. All county monitoring, including the two
cities, is combined for economy.
Collier County
Long Range Budget Plan
FY 12/13 - South Marco Island Beach Renourishment
CAC September 8, 2011
VII-6 Staff Reports
38 of 39
The Marco Island project is nourished in synergy with maintaining Caxambas Pass for
navigation. The type of project is widely practiced in North Carolina and New Jersey, and it is
economical and reduces cumulative environmental impacts.
576000
574000
CAG September 8. 2011
VII-6 Staff Reports
39 of 39
Notes:
1. Coordinates are in feet based on the Florida
State Plane Coordinate System. East Zone,
North American Datum of 1983. (NAD83).
2. Date of Aerial Photography: 2009.
I
.~NWeoCAll."'TON.OUl.EVAIIID
aoc.o.IIATOIl,l'I.CIlIIIOA3).Q1
.....!O<OKlOIlII_........1
275
550
,
1 inch = 550 feel
CAC September 8, 2011
VII-7 Staff Reports
1 of 2
From:
To:
Subject:
Date:
McAloinGarv
HambriahtGail
CAe meeting 9-8-2011 5taff reports - Item 7
Monday, August 29, 2011 11:05:27 AM
CAC meeting 9-8-2011 Staff reports - Item 7
8/4/2011
Collier County Beach Renourishment
Attendees:
J. Gary McAlpin, PE
Director - Coastal Zone Management
3299 Tamiami Trail East, Suite 103
Naples, Florida 34112
GaryM cAI p in CWcolliergov. net
(239) 252-5342
John Sorey
Vice Mayor - The City of Naples
Chairman - Coastal Advisory Committee for Collier County
Discussion Points
1. Eight miles of beach renourishment for Collier County's Barefoot, Vanderbilt, Park
Shore and Naples beaches.
2. Approximatly 800K Cy's of sand; +/- $25M in cost; renourished from 11/1/13 to
5/1/14 (if outside of turtle nesting season).
3. Sand source 14 miles SW of Sanibel (T -1) with renourishment using hoper
dredges.
4. Critical grain size requirements.
5. Major permit modification of existing permit required. Currently modeling
beaches to optimize locations and amount of sand required.
6. Last renourishment in 2005 with GLDD for a 6 year design life. FDEP permitting
prevented anything else due to concerns over impacts to hardbottom. Cost of $18M.
7. Seeking to achieve a true 10-year renourishment with higher and wider beaches
CAC September 8,2011
VII- 7 Staff Reports
2of2
including erosion control structures to reduce the impact of hot spots.
8. Request permit to allow year round renourishment as allowed by recent
biological opinion from FWS.
9. We will require sand screening at the borrow site. Previous renourishment
incoraporated three-quarter inch stationary vessel screens with rejects over the side.
10. CP&E is developing our conceptual design. RFP required for detailed design and
permiting.
11. Program funded with TDC funds that have been allocated. Funding
supplemented with FEMA and FDEP monies.
12. Advantages:
. Share fixed cost savings
. $40-$50M project will create leverage and excitement.
. FDEP Cost Share points
. Equal partners with a structured bid and contract
. Possibility of saving between $2M - $4M overall on a combined project.
Saving could be expected from sharing fixed costs; splitting mob/demobsavings;
Leverage in unit pricing; and year round timing (avilibity / demand/weather).
J. Gary McAlpin, Director
Coastal Zone Management
3299 Tamiami Trail East, Suite 103
Naples, Florida 34112
Ga ryMcAlpi n{ii)colliergov. net
(239) 252-5342
Fax: (239) 353-4061
Under Florida Law, e-mail addresses are putllic records, If you do not want your e-mail address released in response to a public
records request, do not send electronic mail to this entity. Instead, contact this office by telephone or in writing.
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CEPD, Naples join forces for
beach renourishment
August 12, 2011
By SHANNEN HAYES, shayes@breezenewspapers.com , Island Reporter, Captiva
Current, Sanibel-Captiva Islander
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The City of Naples is looking to team up with Captiva Erosion
Prevention District on the next beach renourishment project. The
partnership would have several advantages, including hefty cost
savings on multi-million-dollar projects.
"It makes sense," said J. Gary McAlpin, director of Coastal Zone
Management in Naples.
McAlpin, along with Naples Vice Mayor John Sorey, discussed the
idea of joining forces with Captiva during the CEPD's Wednesday
meeting. In 2013-14, Collier County will be renourishing eight miles
of its beaches Barefoot, Vanderbilt, Park Shore and Naples at a cost
of approximately $25 million.
Its sand source will be 14 miles southwest of Sanibel using hoper
dredges. While Collier's beach renourishment project in 2005 was
designed for a six-year life span, the next project will seek to achieve
a true 10-year renourishment with higher and wider beaches
including erosion control structures to reduce the impact for hot
spots.
The CEPD will be looking at a minimum of six miles of beaches,
including the first mile of Sanibel, for its next project.
If the two were to team up there would be a shared fixed cost
savings and potential leverage on a $40 to $50 million project. In
addition, there would be cost share points with the Florida
Department of Environmental Protection and the possibility of saving
between $2 and $4 million overall on the combined project.
CEPD, Naples join forces for beach renourishment - CaptivaSanibe1.com I Island Reporte... Page 2 of 2
"It behooves us to do this," stated CEPD Chairman Mike Mullins. "We
are happy to be talking with Naples (about this joint effort)."
Savings can also be expected by splitting mobilization and
demobilization costs, and becoming equal partners with a structured
bid and contract. McAlpin told CEPD the details could be worked out
if a partnership evolves.
"We are very flexible," said McAlpin. "There could be millions in
savings to both parties involved."
In other business:
CEPD unanimously voted to transfer $50,000 out of its legal and
professional fees budget and into its general operating reserves fund.
At the end of the fiscal year in September, the money will then be
moved to the capitol projects fund.
The next regular meeting will be at 3 p.m. Sept. 8 in the Wakefield
Room at 'Tween Waters Inn. It will be immediately followed by an
initial budget hearing at 5:01 p.m. The final budget hearing will be
held Sept. 22.
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CAC September 8, 2011
VII-8 Staff Reports
1 of 39
Critical Erosion Area Evaluation
for Clam Pass Park and North Park Shore, Collier County
August 18, 2011
INTRODUCTION
There is beach erosion and threats to habitat, structures, and recreational areas at Clam Pass Park
and North Park Shore, which will justify a critical erosion area designation. This report provides
the information for making this designation. Clam Pass Park (vicinity R-42 to R-45) is a Collier
County park located south of Clam Pass (Figure 1). Park Shore is a neighborhood in the City of
Naples and extends from Seagate Drive (between R-45 and R-46) south to Doctors Pass. There
is a small segment of unincorporated county located between the two areas.
FIGURE 1. Project location map.
In 1986, pursuant to Sections 161.10 1 and 161.161, Florida Statutes, the Department of
Environmental Protection, Bureau of Beaches and Coastal Systems, is charged with the
responsibility to identify those beaches of the state which are "critically eroding" and to develop
and maintain a comprehensive long-term management plan for their restoration. In order for a
1
COASTAL PLANNING & ENGINEERING, INC.
CAC September 8, 2011
VII-8 Staff Reports
2 of 39
segment of eroded coastline to be eligible for State of Florida funding for beach management, it
must be designated as "critically eroded" by the State.
The following definition has been adopted by the Bureau to identify critically eroded areas:
Critically eroded area is a segment of the shoreline where natural processes or
human activity have caused or contributed to erosion and recession of the beach or
dune system to such a degree that upland development, recreational interests,
wildlife habitat, or important cultural resources are threatened or lost. Critically
eroded areas may also include peripheral segments or gaps between identified
critically eroded areas which, although they may be stable or slightly erosional now,
their inclusion is necessary for continuity of management of the coastal system or for
the design integrity of adjacent beach management projects.
In order for an erosion problem to be critical, there must exist a threat to or loss of one of four
specific interests: upland development, recreation, wildlife habitat, or important cultural
resources. This evaluation will provide information on three of the four for a request for Critical
Erosion Area (CEA) designation for the area south of Clam Pass in Collier County, Florida.
SHORELINES
PA
+ U:C~TJDN IT .ONR' JO<<JHOO
19]s-8C) kOS.. MKV
-~ f972".M.*""
__,___,________.. t565-1 U,$.C .. &,$" )t.i'-'
i'o
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....
m
._____________ I'l5HI U~.. _
+
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FIGURE 2. FDEP Historic Shoreline Map.
Inlet History
Clam Pass is a very small pass located in northern Collier County. The pass is approximately
100 feet wide and its mouth is very shallow due to the presence of bars. The location of the
channel varies seasonally, turning southward during the winter and northward during the
summer. The pass has a very small tidal prism and has migrated in the past. Between 1954 and
1970, Clam Pass migrated approximately 600 feet north (USF, 1980). From the FDEP's historic
2
COASTAL PLANNING & ENGINEERING, INC.
CAC September 8, 2011
VII-8 Staff Reports
3 of 39
shoreline map, it is illustrated that in 1885, the pass was located between R-42 and R-43
compared to its location between R-41 and R-42 currently. This illustrates the natural variability
of the inlet's position, which greatly impacts the downdrift shoreline. The topography and
bathymetry south of Clam Pass is illustrated in the 2004 Lidar map in Appendix C. This map
show the location of the nearshore hardbottom mapped in 2003 and 2005.
Dredge & Fill History
In 1999, the Clam Pass Restoration and Management Plan was undertaken to improve tidal flow
throughout the Clam Bay System and surrounding 500-acre mangrove preserve. During the
initial restoration, the flood shoal and select interior waterways were dredged in order to achieve
the goal of improved tidal flow and also to increase tidal prism within the system (Figure B-5).
With an increased tidal prism, greater amounts of water can enter and exit Clam Pass during each
tidal cycle. This, in return, allows for stronger currents which aids in keeping inlets open and
improving flushing in support of habitat within Clam Bay system.
Clam Pass has been dredged three times since 1999 in order to improve water quality and
flushing and smaller undocumented dredgings occurred prior to 1999. The most recent dredging
event at Clam Pass occurred in April 2007. Approximately 22,000 cubic yards was removed
from the mouth of the channel and within the flood shoal from Stations 0+00 to 18+00. No
interior dredging of the pass occurred in 2007. The material that was dredged from the inlet was
placed to the south of the pass near R-43. Periodic inlet monitoring has occurred since the start
of the project in 1999.
The southern Clam Pass area has also received fill from the 2006 Collier County Beach
Renourishment Project south of R-46. Nourishment also occurred north of R-46 with the 2006
project. The profiles that were nourished during this project were R-46 to R-49. Table 1
illustrates fill volumes for the project area from inlet bypassing and the 2006 nourishment
project.
TABLE 1
FILL VOLUMES FOR CLAM PASS AREA
Profile Dist. (ft) Fill Placed (C.Y.)
1999 2002 2005/6 2007
R-42 1,057 6,400 2,345 4,400
R-43 1,015 22,400 8,208 15,400
R-44 1,016 3,200 1,173 2,200
R-45 1,073
R-46 1,040 13,104
R-47 954 8,002
R-48 1,000 10,150
R-49 1,076 10,193
Total 8,231 32,000 11,725 41,449 22,000
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PHYSICAL RECESSION AND EROSION
The conditions causing the critical erosion condition and its magnitude are described below.
Shoreline Change
The Mean High Water (MHW) elevation measured at each profile is used to represent the typical
shoreline location. In Collier County, the MHW elevation is +0.33 ft NA VD 88. The MHW
shoreline is approximated by the high-tide mark on the beach. The MHW shoreline changes
were calculated using historic beach profiles and historic shoreline data from the Florida
Department of Environmental Protection (FDEP) and Collier County's monitoring of the inlet
and adjacent beaches.
The northern shoreline (R-34 to R-41) and the south shoreline (R-42 to R-49) of Clam Pass were
evaluated in order to analyze shoreline changes to present. Table 2 presents shoreline changes
from 1988 through 2010, as well as selected periods which coincide with major dredging events
at Clam Pass. Table 3 illustrates shoreline changes south of the pass with the fill factored out.
Beneficial fill from inlet dredging has occurred in 1999, 2002, and 2007 and was accounted for
within this table.
From Table 2, it can be seen that south of Clam Pass, the erosional arc extends to R-48 for the
1988-2010 period. Since maintenance dredging began in 1999 in order to improve flushing of
the pass, the erosional trend has increased south of the pass and decreased to the north of the
pass. Since 1998, the northern shoreline has been accretional, while the southern shoreline has
eroded approximately 16 feet. The arc of erosion south of the pass increased by 2,000 feet
between 2005 and 2010. Even with the existing bypassing program in place at Clam Pass, the
downdrift shoreline is showing an increased impact compared to the pre-1998 period.
When fill placed south of the pass is considered, erosion rates are substantially greater (Table 3).
The fill accounted for within this table is from sand bypassing at the inlet and beach
renourishment (Table 1). When fill is discounted, the area with the greatest erosion is located at
R-43, which has experienced over 100 feet of shoreline loss since dredging began in 1999. The
increased erosion south of the pass is associated with the dredging implemented within the area
in order to restore flushing to the Clam Bay system. The increased flushing has improved
mangroves and other aquatic habitat within Clam Bay based on annual monitoring conducted by
Terrel Hall and Associates through 2010 for the Pelican Bay Services Division. The gap in the
hardbottom (Appendix C) south of the pass and the groins at the Seagate Drive public access are
contributing to the erosion in this area. Two groins are located between R-45 and R-46, and the
hardbottom gap is north of this region. In addition, an examination of the comparative profiles
show the 2005 hurricane season was a catalyst to increase erosion. Notice the offshore shift in
profile volume measured with the November 2005 profiles, and the disappearance of the volume
in the 2010 profiles.
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Pro file Shoreline Changes (ft)
Number 1988 to 1998 to 2005 to 1988 to 1998 to
1998 2005 2010 2010 2010
R-34 -18.7 -21.3 30.0 -10.0 8.7
0-
R-35 -19.6 -14.5 18.4 -15.7 3.9
R-36 -18.0 -7.5 10.9 -14.6 3.4
..
R-37 -38.1 -0.1 -4.0 -42.2 -4.1
'"
R-38 -0.1 -0.9 -3.9 -4.9 -4.8
...
R-39 -9.3 2.8 13.5 7.0 16.3
R-40 -1.6 -25.4 39.7 12.7 14.3
R-41 -70.7 39.3 -5.6 -37.0 33.7
Clam Pas s
R-42 -7.8 -2.1 -17.7 -27.6 -19.8
R-43 -22.2 -17.4 -7.6 -47.2 -25.0
R-44 -38.0 -11.1 -10.6 -59.7 -21.7
R-45 1.3 -27.2 -12.6 -38.5 -39.8
R-46 -6.3 7.4 -21.3 -20.2 -13.9
R-47 -22.4 5.8 -14.7 -31.3 -8.9
0-
R-48 -8.3 -6.6 6.6 -8.3 0.0
R-49 45.9 -1.5 4.9 49.3 3.4
N.Avg. -22.0 -3.5 12.4 -13.1 8.9
S.Avg. -7.2 -6.6 -9.1 -22.9 -15.7
TABLE 2
MHW SHORELINE CHANGES
TABLE 3
MHW SHORELINE CHANGES WITH FILL FACTORED OUT
Prof11e Shoreline Changes (ft) with Fill Factored Out
Number 1988 to 1998 to 2005 to 1988 to 1998 to
1998 2005 2010 2010 2010
R-42 -7.8 -16.7 -25.1 -49.6 -41.8
R-43 -22.2 -70.6 -34.4 -127.2 -105.0
R-44 -38.0 -18.7 -14.4 -71.1 -33.1
R-45 1.3 -27.2 -12.6 -38.5 -39.8
R-46 -6.3 7.4 -43.5 -42.4 -36.1
R-47 -22.4 5.8 -29.5 -46.1 -23.7
R-48 -8.3 -6.6 -11.3 -26.2 -17.9
R-49 45.9 -1.5 -11.8 32.6 -13.3
Avg. -7.2 -16.0 -22.8 -46.1 -38.8
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Figure 3 illustrates the shoreline changes centered around the inlet. The figure illustrates the
erosional and accretional patterns within the study area. It can be seen that during the time
period from 1998 to 2005, the erosional arc from the inlet extended to R-46. In the past five
years, the erosional arc has expanded and now goes to R-48. The figure illustrates that the
erosional area south of the pass is growing, which is threatening the shoreline farther south and
could cause further loss of vegetation and habitat.
SHORELINE POSITION COMPARED TO 1998 SHORLlNE
VICINITY OF CLAM PASS 1988 TO 2010
80.0
60.0
40.0
f='
w
w
!:. 20.0
w
z
::;
w 0.0
cr:
0 III
J: !II
en
.. -20.0 '''!II
'"
~
1998
III 1998 to 2005
_1998 t02010
_1998 to 201 0 (VVithout Fill)
I
~ -40.0
cr:
LL
~ -60.0
z
~
!!l -80.0
o
-100.0
-120.0
R34 R35 R36 R37 R38 R39 R40 R41 Clam R42 R43 R44 R45 R46 R47 R48 R49
Pass
R.MONUMENT LOCATION
FIGURE 3. Shoreline Changes near Clam Pass (1998 to Present)
The erosion and loss of shoreline has impacted vegetation (Table 8). Along the Gulf shoreline,
the vegetation has retreated on average 35 feet from its 1994 position. Overall, this increased
erosion south of the inlet on the Gulf beaches has caused approximately 2.25 acres of vegetation
to be lost.
Volumetric Changes
The volumetric changes in this report represent the difference in the quantity of sand measured
along the beach between surveys. All volumetric changes are given in cubic yards. Volumetric
changes were calculated between the dunes (upland) and the approximate depth of closure of
-11.3 feet NA VD.
The volumetric changes for two different periods are shown in Tables 4 and 5, along with the
impact from bypassing and nourishment. Table 4 illustrates volumetric changes from 1998 to
2010 and Table 5 depicts the recent volumetric changes at the pass from 2005 to 2010.
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Volumetric Change (C.Y.) Fill Placed (C.Y.) Net Vol. Net Ann.
Pro file Dist. (ft)
June 1998 to Oct. 2010 1999 2002 2005/6 2007 Change Change
R-42 1,057 -13,691 6,400 2,345 4,400 -26,836 -2,176
R-43 1,015 -10,213 22,400 8,208 15,400 -56,221 -4,558
R-44 1,016 -4,088 3,200 1,173 2,200 -10,661 -864
R-45 1,073 -6,636 -6,636 -538
R-46 1,040 332 13,104 -12,772 -1,036
R-47 954 -1,749 8,002 -9,751 -791
R-48 1,000 4,824 10,150 -5,326 -432
R-49 1,076 2,194 10, 193 -7,999 -649
Total 8,231 -29,027 32,000 11,725 41,449 22,000 -136,201 -11,043
TABLE 4
VOLUMETRIC CHANGES
JUNE 1998 to OCT. 2010
Volumetric Change (C.Y.) Fill Placed (C.Y.) Net Vol. Net Ann.
Profile Dist. (ft)
Nov. 2005 to Oct. 2010 2005/6 2007 Change Change
R-42 1,057 -26,462 4,400 -30,862 -7,716
R-43 1,015 1,617 15,400 -13,783 -3,446
R-44 1,016 -6,543 2,200 -8,743 -2,186
R-45 1,073 -5,102 -5,102 -1,276
R-46 1,040 -7,992 13,104 -21,096 -5,274
R-47 954 -7,612 8,002 -15,614 -3,904
R-48 1,000 996 10,150 -9,154 -2,289
R-49 1,076 4,339 10,193 -5,854 -1,464
TOTAL 8,231 -46,759 41,449 22,000 -11 0,208 -27,552
TABLE 5
VOLUMETRIC CHANGES
NOV. 2005 to OCT. 2010
During the time period from 1998 to 2010, the Clam Pass area from R-42 to R-49 eroded
approximately 29,000 cubic yards. Also during that time period, 107,174 cubic yards were
placed within the same area. Accounting for fill placed, the Clam Pass area eroded
approximately 136,000 cubic yards or -11,000 cubic yards per year.
Recently, from 2005 to 2010, erosion within the study area has increased. The annual erosion
rate has more than doubled and was measured to be approximately -27,500 cubic yards per year
when fill within the study limits was accounted for. This increase in erosion may have been
triggered by the 2005 hurricane season.
For the period since dredging began, there is a 29,000 cubic yard deficit south of Clam Pass
through R-49.
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The Clam Pass Park Pavilion is located between R-42 and R-43 south of the inlet. These two
profiles have some of the highest erosion rates within the study area. Since 2005, these two
profiles have lost almost 45,000 cubic yards of material. If these profiles continue to erode at the
current rate, portions of the pavilion could become undermined.
Summary of Changes
The Clam Pass Park Area is not designated critical, but Collier County believes it qualifies as
critically eroded as described below. The shorelines near Clam Pass have been eroding at an
accelerated rate since 1998, which directly affects the amount of recreational area available to
the public. During the period from 1988 to 2010, the largest shoreline retreat was observed at R-
43 when fill placed at the profile was factored out. The shoreline recession at Clam Pass Park
has caused beach vegetation to be lost, which is habitat for gopher tortoises. The beach
narrowing will impact nesting sea turtles soon. In Figures 5a and 5b, it was found that over 2
acres of vegetation has been lost since 1994 along the Gulf shoreline. This affect's the public's
accessibility to the Park and enjoyment of nature along this recreational area.
STORM RECESSION, OVERWASH, AND BREACHING THREAT
In order to evaluate the potential of storm recession, overwash, and breaching, previous storm
erosion studies were reviewed. In March 1994, the USACE published the Collier County,
Florida Shore Protection Study, which contained various storm recession curves and storm surge
levels for Collier County's beaches. Considering both recession and storm surge calculated from
the studies, multiple profile locations in the Clam Pass area are threatened by recession and
breaching from storms with a return interval of 10 to 25 years.
Figure 4 illustrates the results from the storm recession study for the Clam Pass Park profiles.
The study found that the 5-year return period storm would cause approximately 70 feet of
shoreline recession within the Clam Pass area. Shoreline recession is the distance from the
normal shoreline landward to the point where land elevation is reduced by 0.5 foot. The lO-year
storm is expected to cause 105 feet of recession. The 20-year storm was found to produce 155
feet of shoreline recession, and the 25-year storm reaches 170 feet. These values of recession
were compared with available beach width along with expected storm surge within the project
area to determine breaching potential. Table 7 shows that a lO-year storm can erode through the
dune crest, and approaches the distance to Outer Clam Bay shoreline from the Gulf. This poses a
breach threat.
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COLLIER COUNTY. FLORIDA
RETURN PERIOD VS. RECESSION DISTANCE
STORM INDUCED RECESSION
PARK SHORER-42 TO R-57
275
75
250
225
~
200 ~
----1
;.;
Q
elS0
w
V
z 125
:;S
(/J
i5 100
50
25
0-;
10
'RETURN PERIOD (yeors)
. .
100
FIGURE 4. Frequency curve of storm-induced recession (USACE, 1994).
A breach on a barrier island will occur if a strong flow develops a channel over and through the
island. Breaches can either form along the Gulf side or along the Clam Bay side in the Clam
Pass Park area. Once the breach forms, the dimensions of the breach (width and depth) have
been found to increase exponentially until equilibrium is reached (Kraus, 2003). The breach is
driven by three components: difference in bay and Gulf water levels, wave run-up, and
overwash. A barrier island breach can increase erosion, expose the back bay or estuarine
environment to Gulf waves and stronger currents, increase salinity and water levels in the back
bay or estuarine environment, and reduce or impede navigability in adjacent inlets sharing the
same water bodies as the breach. A breach may close naturally, but if the tidal exchange is
strong and longshore sediment transport is weak, the breach can increase in size and become a
new inlet. If a breach were to occur within the study area, the mangroves located along Clam
Bay System could be adversely affected by a change of flushing due to the formation of a new
channel (i.e. the volume of flushing at Clam Pass would be lessened by the diversion to the new
breach). Also, once a breach occurs, an overwash fan would be anticipated to occur which could
cover seagrasses, mangroves, and other potential habitat within the affected area (Refer to
Appendix B for map of seagrasses and mangroves within study area).
Table 6 illustrates the surge levels determined from the study. Dune crest characteristics were
also examined within the study area to determine which areas were susceptible to overwash and
breaching (Table 7). The peak dune elevation from R-42 to R-45 is between 6.1 and 7.3 feet
NA VD and the dune crest is located between 76 and 102 feet back from the shoreline. When
comparing dune height to the storm surge found in the USACE study, it was found that the 20-
year storm exceeds the dune crest at R-42 and R-43. At profiles R-44 and R-45, the storm surge
from a 25-year storm will overtop the dune, given that the storm recession would erode the
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heights. The breaching potential is likely at the 20-year return surge and recession rate at the
profiles described above. Breaching and overwash of the narrow beach at R-44 can impact the
habitat in Outer Clam Bay by creating overwash fans that could impact mangrove and seagrass
habitats (refer to Appendix B for seagrass and approximate mangrove locations). In addition,
the infusion of Gulf waters could change the salinity of the bay, further affecting seagrass and
other species growing there. Breaches can also eliminate gopher tortoise habitat by filling in or
washing away burrows and sea turtle nests (see Threats to Vegetation and Wildlife Habitat
below). On the other hand, overwash fans are good habitat for wading birds such as the
threatened piping plover, while they remain unvegetated. However, no piping plover
observations have been recorded in the study area, and no known shorebird nesting has been
observed.
TABLE 6
STORM SURGE ELEVATIONS
(FEMA, 1986 and CHIU, 1989)
SURCE LEVEL
(feet, NOVD)
2 2.52
5 4.02
10 5,8
20 8,4
50 11.2
100 13.1
200 14.7
1 Hiih lid. ,.pproxl....l.ly I fOOl) wu d.duct.d from IOIllI JIOnn lid. lovel ,iven in Chlu.
: E'xtnlpolaled value
TABLE 7
DUNE CREST CHARACTERISTICS
Location Height ( ft-NA VD) Distance from Shoreline (0' NA VD)
R-42 6.1 102
R-43 6.5 76
R-44 7.2 92
R-45 7.3 87
R-46 11.9 151
Note: Based upon the 2010 survey for R-42 to R-45 and 2009 survey for R-46
NA VD is 1.3 feet higher than NGVD
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THREATS TO VEGETATION AND WILDLIFE HABITAT
The erosion that has been measured along the Clam Pass study area has caused a significant loss
of vegetation over the past 17 years. Table 8 shows the measured losses at Clam Pass Park and
Figures 5a and 5b illustrate those changes. Since 1994, approximately 2.25 acres of vegetation
has been lost to erosion. The southern portion of the study area, from approximately R-44.5
south, supports a narrow dune system fronting beach-front development. Vegetation in this
portion includes planted native dune species such as sea oats (Uniola paniculata) and rail-road
vine (Ipomoea pes-caprae) as well as non-native landscaping such as inkberry (Scaevola
taccada). The northern portion of the study, from approximately R-44.5 north to Clam Pass,
transitions into more natural habitat, with similar dune species backed by coastal shrub/scrub and
mangroves (dune heights provided in Table 7 above). During a site visit conducted August 9,
2011, beach and dune vegetation was observed encroaching upon the active wave zone due to
erosion in many places (Photograph 1).
PHOTOGRAPH 1. Planted sea oats at risk from scarping observed around R-44.
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Notes:
1. Coordinates are in feet based on the
Florida State Plane Coordinate System,
East Zone, North American Datum of
1983 (NAD 83).
2.2010 NAIP Natural Color Imagery for
Florida acquired between April 24, 2010
and October 21,2010.
Leaend:
""""-- 2010 Vegetation Line
-- 1994 Vegetation Line
A FDEP
Monuments
FIGURE Sa. Change in vegetation line from 1994 to 2010 from just north ofR-42 to just
south of R-43.
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Notes:
1. Coordinates are in feet based on the
Florida State Plane Coordinate System,
East Zone, North American Datum of
1983 (NAD 83).
2.2010 NAIP Natural Color Imagery for
Florida acquired between April 24.2010
and October 21, 2010.
FIGURE 5b. Change in vegetation line from 1994 to 2010 from just south ofR-43 to just
south of R-45.
"'^"""" 2010 Vegetation Line
"'^-' 1994 Vegetation Line
... FDEP
Monuments
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TABLE 8
VEGETATION LOSS FROM 1994 TO 2010
Profile Vegetation Loss (ft)
R-42 -35
R-43 -31
R-44 -39
Avg. -35
The beach, dune, scrub and mangroves within the study area provide important habitat for
wildlife including threatened and endangered species. Impacts to these species and their habitats
are described below.
Gopher Tortoises
The gopher tortoise (Gopherus polyphemus) is State-listed threatened species. These reptiles
live in well-drained sandy areas with abundant low-growing vegetation. They are commonly
found in beach and dune environments along the southwest Florida coast. They are active earth-
movers and their burrows average 15 feet long and 6 to 7 feet deep. Gopher tortoises have been
observed in in the study from Clam Pass south to Doctors Pass (Maura Kraus, Collier County,
pers. comm. 2011). Much of this area has high vegetative dunes isolated from pedestrian traffic.
The dunes between Seagate Drive and R-49 are especially well developed and protected as
illustrated in topography in Appendix C. Informal surveys have also been conducted within the
Clam Pass Park area (Figure 7). During the August 9 site survey, several gopher tortoise
burrows were observed in the study area (Figure 6).
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Notes:
1. Coordinates are in feet based on the
Florida State Plane Coordinate System,
East Zone, North American Datum of
1983 (NAD 83).
2.2010 NAIP Natural Color Imagery for
Florida acquired between April 24, 2010
and October 21,2010.
Leaend:
2011 Gopher Tortoise Burrow Survey
Active
Inactive
. Abandoned
... FDEP
Monuments
FIGURE 6. Gopher tortoise burrows observed during August 9, 2011 site visit.
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2011 AERIAL SOURCE, COLUER
COUIITT PROPERTY APPRAISER
I, I
o SO 100 200
SCALE: 1" = 1 00'
LEGEND
Lmmm; 1989 CCCL
E~ 1979 CCCL
@'> COPHER TORTOISE BURROW
mt'......
Figure 7. Gopher Tortoise Survey (CEC, 2009)
...., -
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Sea Turtles
Erosion and loss of habitat within the study area has a negative impact upon nesting sea turtles.
A high number of nests were inundated or washed away in 2008, attributable to the passing of
Tropical Storm Fay that year near Cape Romano, Florida (Table 9). Aside from this occurrence,
no trend in number of nests inundated or washed away is apparent over the past five-year period;
however, there is a decreasing trend in the distance of nests laid from MHW (Table 10). If this
trend continues, sea turtle nests are at an increased risk of inundation and erosion. For 2010, the
closest nest to the MHW line was approximately 36 feet away, while the maximum distance for a
nest was 68 feet. From the findings from the USACE storm recession study, all sea turtle nests
within the study area in 2010 will be threatened by a 5-year storm which causes 70' of recession.
Nests closer to the water, such as the nest at R-48, will be threatened by storms with a smaller
return interval of 5 years, which puts this nesting habitat at risk.
During the site visit, sea turtle nests were observed perilously close to breaking waves and some
looked as though they had already been inundated (Photograph 2); others appeared at risk ofloss
from scarp formation (Photograph 3). The growth of the arc of erosion through R-48 is
increasing the threat to nesting sea turtles, and will lead to continued erosion of nesting habitat.
TABLE 9
NUMBER OF SEA TURTLE NESTS INUNDATED OR WASHED A WAY
-
Year Nests Inundated Nests Washed Away
2010 3 4
2009 I 4 I 4
2008 I 9 I 11
2007 I 10 I 0
2006 4 0
TABLE 10
AVERAGE DISTANCE OF SEA TURTLE NESTS FROM MHW
R-42 R-43 R-44 R-45 R-46 R-47 R-48 A veral!:e
2010 68.0 45.8 41.1 56.3 40.3 35.6 47.2
,
2009 66.0 47.5 31.7 53.2 64.0 40.0 51.6 50.6
mm
2008 64.0 51.0 47.6 46.8 58.7 48.3 51.1 52.5
2007 80.0 64.7 68.0 70.0 56.4 47.4 51.3 62.5
2006 52.0 56.0 64.5 78.7 64.5 91.0 68.0 67.8
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PHOTOGRAPH 2. Sea turtle nest at risk of inundation near southern end of study area
(vicinity ofR-44).
PHOTOGRAPH 3. Sea turtle nest and dune vegtetation at risk from scarp formation
within the study area (vicinity of R-49).
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Birds
Each winter the Audubon Society organizes a Christmas Bird Count, using volunteers to identify
and count bird species all over the country. Data from this count were tabulated for the Naples
area for the years 2000 through 2010. No piping plovers (Charadrius melodus) were observed in
the Naples area during this time period, although another study conducted between Doctor's Pass
and Gordon Pass to the south reported piping plovers as common (Below, 2004). Red knots
(Calidris canutus rufa), a candidate species for listing under the Endangered Species Act, have
occasionally been sighted in the Naples area during the Audubon Christmas Bird Count, with the
largest number observed during the tabulated time period in the winter of 2005-2006 (Table 11).
Least terns are known to nest in Collier County and Below (2004) noted them as common in the
Naples Beach study area. Although suitable nesting habitat for shorebirds is present in the study
area, primarily at the north end adjacent to Clam Pass, no local bird surveys are conducted there
because there is currently no known nesting in the area (Ricardo Zambrano, FWC, pel's. comm.),
likely due to the high pedestrian traffic at Clam Pass Park.
TABLE 11
NUMBER OF RED KNOTS OBSERVED IN THE NAPLES SURVEY AREA DURING
AUDUBON CHRISTMAS BIRD COUNTS BETWEEN 2000 AND 2010
Year Number
2000-01 0
2001-02 I 0
2002-03 I 6
2003-04 I 0
2004-05 I 22
2005-06 I 33
2006-07 I 0
2007 -08 I 5
2008-09 I 2
2009-10 i 5
THREATS TO UPLAND STRUCTURES
In order to evaluate the threat to upland structures, the recession and storm surge from the 1994
USACE study were used. Considering both recession and storm surge calculated from the
studies, threat to structures within the Class Pass area can be expected from moderate storms.
The study shows that the 25-year storm will cause approximately 170' of erosion. This
magnitude of erosion puts the structure at Clam Pass Park between R-42 and R-43 at risk. The
boardwalks connecting the building to the beach, the pavilion, the deck, and the front of the two
main building are at risk and within the 170' erosional area if the 25-year storm were to impact
the area. Also, photographs 4a and 4b illustrated the close proximity of the structure at Clam
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Pass Park to the MHW waterline. The structure was fronted by a substantial dune width and
vegetation in 1994 which provided a protective buffer from storms, but current conditions
indicate a much smaller width between the structure and the water's edge, which puts the
structure at risk. Photograph 4 below illustrates the location of the structures in comparison to
the water.
PHOTOGRAPH 4. Proximity of boardwalk at Clam Pass Park to tide line.
THREATS TO RECREATION
Clam Pass Park, located within the study area, is a beach access point in the North Naples area of
Collier County, Florida, which is one of the most populated sections of the County. This area is
one of the most popular beach access points. Clam Pass boasts 35 acres of coastal habitat and
preserves that habitat by providing beach access from a three-quarter-mile boardwalk to the
sandy beach. The board walk is a destination itself for those adventurists who love a quiet nature
walk. The boardwalk runs through a mangrove forest of salt-tolerant red (Rhizophora mangle),
white (Laguncularia racemosa) and black (Avicennia germinans) mangroves. It also has a tidal
bay area that acts as a breeding ground and nursery for marine life, wildlife, specifically many
species of birds. Erosion threatens all of the uses and activities that beach goers do within Clam
Pass Park. If erosion continues, the sandy beach in front of the park will be reduced, which in
return will deter beach goers due to lack of beach. The Clam Pass Park area is in threat by
overwash and breaching from storms, which can dramatically reduce the recreational area.
20
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Along with the Clam Pass Park access, the County has also created a public access point at
Seagate Drive between R-45 and R-46, which is popular with County residents as well. This
beach access is adjacent to a large beach parking lot, which the County is considering to provide
bathrooms for due to its high use. If this portion of the beach were to be cut off from the
northern section due to a breach, the public would not be able to enjoy Clam Pass Park from the
access. There would also be less recreational width for users of this beach to enjoy with
increased erosion. The Seagate Drive access point underwent an emergency nourishment project
during the last year in order to create a wider beach for beach users due to the high erosion rates
that have occurred.
CONCLUSIONS
The area south of Clam Pass (R-42 to R.48) is presently not identified as critically eroded, but
from the analysis performed, it can be seen that erosion is a threat and has created a loss of
recreational and habitat area. The Clam Pass Park north of Seagate Drive area warrants
designation as critically eroded beach and should be designated as such based on existing losses
and threats. The area south of Seagate Drive is being threatened by increased erosion, and
contains dune habitats frequented by gopher tortoises. This area qualifies under the State's
Definition of Critical Erosion due to threats to recreation, upland structure, and wildlife habitat.
The County's upcoming nourishment project is considering including this reach within the
project area to stabilize and mitigate the long term erosional trend, to protect beach habitat for
gopher tortoises and sea turtles, and to increase recreational shoreline.
P:\Collier\8500.82 CEA Clam Pass Park\Engineering Files\Critical Erosion Area Evaluation Report 08-17-11
21
COASTAL PLANNING & ENGINEERING, INC.
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REFERENCES
Brown, Ted R, and Hilburn O. Hillestad, Clam Bay Restoration and Management Plan, 1998.
Below, T.H., (2004 & 2009). Coastal waterbird beach utilization, Naples, Florida). Report
prepared for City of Naples, Florida.
Coastal Planning & Engineering, Inc., (June 2004). Critical Erosion Area Evaluation Collier
County Nourishment Project.
Coastal Planning & Engineering, Inc. ( September 2006). Analysis of Clam Pass Inlet Impacts 7
Years After Implementation of the Clam Bay Restoration and Management Plan.
Dean, RG., Chiu, T.Y and Wang, S.Y., Combined Total Storm Tide Frequency Analysis for
Collier County. Florida, Florida Department of Natural Resources, 1989.
Federal Emergency Management Agency, Flood Insurance Study. Collier County. Florida, June
1986.
Kraus, N.C. and Wamsley, T.V. (2003). Coastal Barrier Breaching. Part 1: Overview of
Breaching Processes. Coastal and Hydraulics Laboratory Technical Note ERDC/CHL CHETN
IV-56.
PBS&J, (October 2007). Clam Bay Seagrass Assessment, Draft Final Report. Collier County,
FL.
PBS&J, (October 2009). Clam Bay System: Data Collection & Analysis, Final Report. Collier
County, FL.
Terrell, Hall, and Associates, Inc., (September 2010). Mangrove Monitoring Report.
University of South Florida. (1980). Impact of Florida's Gulf Coast Inlet on the Coastal Sand
Budget.
U.S. Army Corps of Engineers, (March 1994). Collier County, Florida Storm Protection Study:
Reconnaissance Report.
Worley, Kathy and Jeffrey R Schmid, (December 2010). Clam Bay Natural Resource
Protection Area (NRP A) Benthic Habitat Assessment. Environmental Science Division,
Conservancy of Southwest Florida.
Agnoli, Barber, and Brundage, Inc. Beach Profile Monitoring Data at the Department of
Environmental Protection Reference Monuments R-38 through R-44, 1999 to 2004.
Coastal Engineering Consultants, Inc., Collier County Beach Restoration Project, Post-
Construction Monitoring Report, 2000.
22
COASTAL PLANNING & ENGINEERING, INC.
CAC September 8, 2011
VII-8 Staff Reports
23 of 39
Coastal Planning & Engineering, Inc, Collier County Beach Restoration Project. September
2005 Pre-Construction Survey.
Humiston & Moore Engineers, Clam Pass Restoration and Management Plan Bathymetric
Monitoring Report No.5, 2004.
23
COASTAL PLANNING & ENGINEERING, INC.
APPENDIX A
COMPARATIVE PROFILES (1988 to 2010)
R-42 to R-49
COASTAL PLANNING & ENGINEERING, INC.
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CAC September 8, 2011
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APPENDIX B
NATURAL RESOURCES
COASTAL PLANNING & ENGINEERING, INC.
CAC September 8, 2011
VII-8 Staff Reports
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_ Shoal grass THA 1999
_ $eagrass Collier County Seagrass Inventory 1994
_ Seagrass Colliet County Seagrass Protection Plan1992
Figure B-1. Clam Pass Seagrass Mapping - 1992 to 1999 (Worley, 2010).
COASTAL PLANNING & ENGINEERING, INC.
CAC September 8, 2011
VII-8 Staff Reports
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CSWF 2010 Shoal grass
Bl Shoal grass Observed
.. Shoal grass Isolated
.. Shoal grass Sparse
.. Shoal grass Present
.. Shoal Grass Dense
CSWF 2010
Paddle grass
Figure B-2. Clam Pass Seagrass Mapping - 2007 to 2010 (Worley, 2010).
PBSJ 2009
Paddle grass
PBSJ 2007
. Paddle grass
Turtle grass
COASTAL PLANNING & ENGINEERING, INC.
CAC September 8, 2011
VII-8 Staff Reports
36 of 39
Mangrove Prop Roots
Crustaceans
_ Unidentified bamaele$l sh~l)
_ Unidentified bamaeles(IVingl
_ Mangrove crab
Figure B-3. Mangrove Location is indicated based upon Mangrove Crab Habitat
Locations (Worley, 2010).
COASTAL PLANNING & ENGINEERING, INC.
CAC September 8, 2011
VII-8 Staff Reports
37 of 39
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COASTAL PLANNING & ENGINEERING, INC.
APPENDIX C
2004 LIDAR SURVEY
TOPOGRAPHIC AND BATHYMETRIC MAP
CLAM PASS PARK AND NORTHERN PARK SHORE
COASTAL PLANNING & ENGINEERING, INC.
CAC September 8, 2011
VII-8 Staff Reports
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CAC September 8, 2011
VII-9 Staff Reports
1 of 1
From:
To:
Subject:
Date:
McAlDinGarv
HambriahtGilll
CAC meeting 9-8-2011 Staff reports - Item 9 Florida Dock and Dredge - Ft. Myers Beach
Monday, August 29, 20111:37:35 PM
CAC meeting 9-8-2011 Staff reports - Item 9 Florida Dock and Dredge - Ft. Myers Beach
In January 2011 the Wiggins Pass Maintenance Dredging Project was awarded to
Southwind Dredging to dredge 50,000 CY of material out of Wiggins Pass in Tidal Gulf
waters. Southwind proposed a 14 inch cutter head dredge as was specified. The project
needed to be complete by the beginning of Turtle nesting season which began on 5/1.
Southwind began mobilizing on 2/15 and Completed the work by 4/1/2011.
At the time of award, considerable pressure was exerted to use Florida Dock and Dredge to
dredge Wiggins Pass. They had just been awarded a project to renourish Ft. Myers beach
and proposed to dredge Wiggins Pass before beginning the Ft. Myers project. Florida Dock
and Dredge indicated that they could do the project but staff was concerned that their
equipment was too small. There was considerable discussion as to whether they met our
specification for a 14 inch dredge.
Lee County staff awarded the Ft. Myers beach project to Florida Dock and Dredge with the
clear understanding that their equipment was marginal to perform dredging/renourishment
in tidal waters off Lee County. Recent television and newspaper reports have criticized
project delays. This is an example of undersized equipment trying to perform in an
environment that it was not designed for. The project began on May 1st and is currently 6
weeks behind schedule. It is scheduled to be completed January 1, 2012 pending no more
issues.
This projects validated our decision to stand fast on the larger equipment as specified to
perform the dredging of Wiggins Pass.
J. Gary McAlpin, Director
Coastal Zone Management
3299 Tamiami Trail East, Suite 103
Naples, Florida 34112
Ga ryMcAI pi n(@colliereov.net
(239) 252-5342
Fax: (239) 353-4061
Under Florida Law, e-mail addresses are records_ If you do not want your e-mail address released in response to a public
records request, do not send electronic to this entity. Instead, contact this office by telephone or in writing_
SCOPE OF WORK for PREPARATION OF INLET MANAGEMENT PLAN,
COUNTY ENVIRONMENTAL IMPACT STATEMENT AND GEOTECHNICAL
INVESTIGA TION FOR DESIGN AND PERMITTING OF WIGGINS PASS
IMPROVEMENTS FOR CONTRCT 10-5572
May 2011 (Revise August 31, 20 11)
The enclosed scope of work describes additional tasks necessary to complete the
permitting process for a new 10 year permit for Wiggins Pass. These tasks were not
included in the initial Engineering and Permitting scope of work for Wiggins Pass, since
they were identified following its approval.
This work will be based on the 1995 Inlet Management Plan prepared for Collier County
(County), the recently completed Joint Coastal Permit Application (February 2010), and
the Wiggins Pass Modeling Report (January 2009) for Navigation Improvements and
Erosion Reduction Project for Wiggins Pass, Florida. These tasks will be incorporated
into the new report and EIS, and will be the basis for responding to March 2010 RAI
from the Corps and FDEP. This is a revised scope of work and fee proposal to support
additional work on Wiggins Pass based on the letter dated May 13, 20 II and the May 20,
2011 telephone conference from FDEP.
The tasks include:
Task 1. Preparation for and Attendance at Meetings
Task 2. Prepare Inlet Management Study
Task 3. Prepare County Environmental Impact Statement
Task 4. Modeling of Additional Alternatives
Task 5. Additional Geotechnical Field Investigation
Contingency
$ 9,227
$55,374
$25,065
$0
$77 ,823
$10,000
TOTAL T &M NTE
$177,489
.IYlodification to this SOW ret1ects the result of a meeting with FDEP OIl August 26. 2011,
~vhich changed.rIJ_", intent of some orthe earlier E-mail comment.
I. PREPARATION FORAND ATTENDANCE AT MEETINGS
There is a need to attend meetings with FDEP and meet with agency representatives
including NMFS to kick off the next phase of the project and for periodic in progress
review. The number of meeting will be 1 in Tallahassee, 2 in Collier County with the
agencies, and/or one at an agency office. Meeting includes some preparation time.
CAC September 8, 2011
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II. PREPARE INLET MANAGEMENT STUDY
The Florida Department of Environmental Protection (FDEP) is requiring the preparation
of a new inlet management study as part of the permitting process as described below
from Chapter 62B-41 Rules and Procedures for Application of Coastal Permits:
(m) Demonstration of consistency with adopted statewide strategic management plan, an
inlet management plan or a proposed draft inlet management plan in accordance with
Rule 62B-41.005(J6). If not included in the inlet management plan the applicant will
provide the following:
1. A description of the physical characteristics of the inlet;
2. A sediment budget for the inlet;
3. An analysis of the stability and hydraulic characteristics of the inlet including current
velocities, tidal prism and current patterns of the flood and ebb tides;
4. A description of the wind and wave climate in the area of inlet influence;
5. A description of the sediment characteristics of the inlet and its related shoals;
6. The influence of existing manmade structures;
7. The current and historic shoreline erosion and accretion trends;
8. A statement of performance objectives and an analysis of the expected effect of
proposed coastal construction on the coastal system and marine turtles within the inlet
area of influence;
9. An analysis of available alternatives to the proposed coastal construction, including
the no action alternative, on meeting the stated performance objective and any related
effects on the coastal system or marine turtles; and
10. A demonstration of the anticipated public benefits of the coastal construction.
The inlet management plan will consider the intent in the new legislation that modifies
how sediments are managed at navigation inlets, which may be directive in nature as it
pertains to Wiggins Pass. Specific guidance from FDEP will be provided during the
review of the draft inlet manaQement studv and attendance at periodic meetin\!s as it
pertains to treport prepllralJ(JD-~::'. "I'he new legislation changes made to Section
161.142 and 161.143 F.S.
The completed inlet modeling report, Joint Coastal Permit (JCP) application and field
data collection for Wiggins Pass improvements will provide the basis for addressing the
10 requirements listed above, and will be incorporated in the final plan. The plan will
also address comments received from FDEP during their site visit on March 10, 2010,
their initial request for additional information (RA!) and the May 13, 2011 letter. A
committee appointed by the County will review progress of the plan preparation and their
decisions will be incorporated into the plan.
renresentatives. The initial draft plan will be submitted to the County and FDEP for their
comments. The FDEP's adopted plan may differ from the County's based on the State's
procedures and ioeal desires in areas of their separate responsible.
The goals for the Wiggins Pass navigation improvement study as developed by Collier
County and the Wiggins Pass Modeling Evaluation Work Group are:
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1. To provide a safe channel for boating;
2. To address erosion at Barefoot Beach;
3. To lengthen the dredge cycle and accomplish it with the least effect on the
environment; and
4. To provide a solution that is economically effective.
The tasks incorporating the above are A-E below:
TASK II-A. COASTAL ENGINEERING ANALYSIS
I. Data Collection & Review. This task was largely completed with the initial permit and
modeling work, but a comprehensive search will be conducted to locate recent literature
and data to supplement the previously developed history of recent natural and manmade
modifications to the inlet and adjacent areas. Recent topographic and bathymetric data of
the navigation channel and ebb and flood shoals will also be compiled. Potential data
sources include FDEP and County beach and inlet profile surveys, high density LiDAR
data, or other local entities including previous data collection and compilation by other
local consultants. Available aerial photography may be utilized to provide supplemental
shoreline position information.
2. Shoreline Position MaDDing & Change Analvsis. The analysis of shoreline positions
will provide the basis for assessing short-term and long-term shoreline change. The
consultant will consider episodic sediment transport trends resulting from hurricanes,
inlet modifications and beach nourishment. We will analyze and document inlet activities
that have occurred since dredging began in 1984. since dredging was changed in 2000
and evaluate if those activities may have had impacts to the inlet shoreline or adjacent
areas.
The consultant will use a geographic information system (GIS) approach to compile and
analyze the temporal shoreline position change analyses. The GIS analysis will enable
temporal and spatial comparison of FDEP historical shorelines and historical aerial
For time periods where survey data are not available, shoreline changes will be estimated
from the interpretation of aerial photographs. An effort will be made to collect photos in
digital format. If only hard copies are available, they will be scanned and geo-rectified
using GIS so that shorelines can be mapped. Special considerations will be given to
short-term changes so natural and man-made responses are not minimized by averaging
data.
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Inlet ebb and flood shoal configurations, channel orientation and dimensions will be
illustrated with available aerial photography sets. The inlet change data will be compared
to beach shoreline changes to identify correlations and shoal configurations.
3. Volumetric Changes and Sediment Budget Update. A post-dredge sediment budget
analysis will be used to describe the sediment transport pathways in the vicinity of
Wiggins Pass and adjacent beaches. It will be compared to the sediment budget from the
1995 study. The sediment budget will be expanded beyond the I-mi monitoring area
north and south of the inlet.
Available wind, wave, and tidal data will be reviewed. The wave climate will be assessed
in the vicinity of the project to determine the representative range of incident wave
angles, wave heights, and wave periods. The intent is simply to help confirm the
influences of storms and of changes in inlet and nearshore morphology on the sediment
transport patterns.
The inlet area of influence will be defined and inlet impacts and solutions will be
determined based on these zones.
~-----------~-----------~---------------------"'--':-.
Formatted: Indent: Left: 0"
.._-_.._~_.__.~.._~
An odd-even analysis will be based on this defined region.
4. Development of Inlet Management Alternatives. The consultant will identify and
describe various non-structural alternatives to improve sediment management within
Wiggins Pass. No structural alternative will be considered. The alternatives will address
methods to control inlet channel migration, channel modifications, dredge management
options for the navigation channel entrance, and sand distribution and bypassing to re-
establish near-historic levels of sediment transport. Quantity and costs will be developed
for hlJLthe selected alternatives that mQts shown to be viable. The performance of viable
management options will be evaluated in Task B.
Alternatives will consist of various channel dimensions, orientations, and on-and-
offshore disposal plans compared to the existing conditions.
TASK II-B. INCORPORATE WAVE & CURRENT MEASUREMENTS, MODELING
AND STABILTY CURVE
The consultant has previously deployed two acoustic Doppler current profiIers (ADCPs)
in the study area for a period of one month. The tide height, current and wave information
collected from this deployment was used to calibrate the Delft-3D model determining
effects such as wave damping and wave transformation as waves approach the nearshore.
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The results of field data collection and modeling will be described and illustrated in the
plan per items I and 4 above. The measured wave, current and water level data will also
be delivered in raw and processed (time series) formats on a CD-ROM. Survey data was
collected during the wave measurement programs, and will be used to develop an updated
stability curve for the inlet which will be compared to the historic curve developed in the
1995 plan. The results of the modeling will be summarized and illustrated in the
modeling section.
.----rFor',-;;tted: No bullets-~r numbe~;;;;;-----!
, .. . ...._....m..m_ . ...... .....m~mmJ
+-----j For;;'a~;:': Indent: ~~ft-~_.c>::.____m_:::=]
measurements (New contract ta.'ikL
----{ Formatted: Indent: Left: 0"
TASK II-C. IMP COORDINATION AND MEETING
1. Proiect Administration. The consultant will attend meetings with FDEP, the Coastal
Advisory Committee (CAC) and its Sub-committee on Wiggins Pass, and assist with
formulating a plan acceptable to a broad range of local and state interests. Coordination
with FDEP Bureau of Beaches and Coastal Systems (BBCS) will be maintained
throughout the process in order to solicit their comments if they do not attend the
meetings.
It is assumed that the consultant will attend up to three (3) Committee and Sub-committee
meetings of the CAC, to be held in Naples. The consultant will prepare meeting exhibits
and other project documentation. The consultant will attend the meetings and assist the
County with communications with key stakeholders and development of the County's
plan.
TASK I-D. ENVIRONMENTAL EFFECTS OF PROPOSED CONSTRUCTION
I. Environmental Section. Previously obtained information will be incorporated into an
environmental section describing the effects of the proposed construction on the coastal
system and sea turtles.
2. Natural Resources Map. A map of natural resources in the project area compared to
the project layout will be updated for inclusion in the report.
TASK II-E. PREPARATION OF UPDATED INLET MANAGEMENT DOCUMENT
5
1. Preparation of Draft Report. The consultant will prepare a draft IMP based on the
coastal engineering analysis, updated sediment budget and numerical modeling results of
management alternatives. The report will summarize the construction quantities and
estimated costs as well as the impact on adjacent beaches, channel shoaling and
maintenance requirements. The consultant will also summarize potential environmental
issues that may affect the permitting of inlet modifications. Based on the results of the
investigations, the consultant will recommend a modified inlet and beach sediment
management approach. Drawings will be prepared for the selected alternative. The draft
of the IMP will be submitted to the County and the FDEP for review and comment.
2. Preparation of Final Report. Based on County, State, Federal and public comments, a
final updated Inlet Management Plan will be prepared. Five (5) printed copies and digital
CD-ROM copies of the final report will be provided to the County and FDEP. Pertinent
comments provided during the permit process will be integrated into the plan.
III. PREPARE COUNTY ENVIRONMENTAL IMPACT STATEMENT
According to Collier County Land Development Code (LDC) lO.02.02A, an
Environmental Impact Statement (EIS) must be prepared in support of a Special
Treatment Permit approval. Special Treatment (ST) Overlays (LDC 02.03.07) are areas
within the County which, "because of their unique assemblages of flora and/or fauna,
their aesthetic appeal, historic or archeological significance, rarity in the County, or their
contribution to their own and adjacent ecosystems, make them worthy of special
regulations." Such areas include mangrove and freshwater swamps, barrier islands,
hardwood hammocks, and coastal beaches, all of which fall within the Wiggins Pass
project vicinity. The purpose of the ST is to assure the preservation and maintenance of
these resources. An EIS provides a method to objectively evaluate the impact of a
proposed project UpOI! these resources and environmental quality of the project area. An
EIS will be prepared for this project according to the requirements listed in LDC
10.02.02A. The EIS will require the preparation of special maps, ecological analysis and
engineering calculations to supplement information already prepared for the JCP permit
application. The EIS will incorporate the new and existing information into the County
EIS format the consultant will attend up to two (2) meetings to discuss and present the
result of the EIS.
As part of the EIS process, CPE's marine biologist and project manager will research and
incorporate facts and concerns discovered since submittal of the State and Federal permit
application in Feb 2010 into the EIS and permit process, specifically FDEP decisions
described in the May 13, 2011 letter. These will be incorporated into the RAI process the
County's EIS, and will be fully coordinatcd with the Fcderal agcncies. Including the
meetings in I above.
IV. MODELING OF ADDITIONAL ALTERANTIVES
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Based on FDEP's letter data May 13, 2011 and a telephone conference on May 20, 2011,
no additional modeling will be required \.In\i~r thi~_J;>h;~Qf thes::onJI'lfL'i.upject tQ_i.\
;?lIcccsfull geotechnical field investagion and channel pain. If the County'; ;tmightcncd
channel de.;lgn if the County's proposed mam,gement of dredged :;edimentc and
a';okb.nec of .;tablllzlng geological felttllre:- is acceptable. No modeling will be
conducted under thi:; phase of the contract.
leaves in place most of the marine peat, rock and clay substrate that stabilizes the inlet
location. The inlet management study will present a plan to restore the ebb shoal and
beach, the major purpose of the new modeling.
There is a statement in this task that "no additional modeling will be required if the
County's straightened channel design leaves in place most of the marine peat, rock and
clay substrate that stabilizes the inlet location." The statement implies that the
geotechnical investigation and the horizontal and vertical interpretation of this material
(in Task V) must be successful in order to avoid the marine peat, rock, and clay
substrate.
V. ADDITIONAL GEOTECHNICAL FIELD INVESTIGATION
The purpose of this investigation is to collect data within the Wiggins Pass flood and ebb
shoals as a basis for addressing substrate concerns raised by the Bureau of Beaches and
Coastal Systems, Department of Environmental Protection (BBCS) in the March 2010
Request for Additional Information (RAI) and their May 13 2011 letter. The
investigation plan discussed in this scope of work and shown on Figure I was developed
in coordination with Coastal Planning and Engineering, FDEP BBCS and Collier County
during May 2011. The investigations will include geophysical and geotechnical surveys,
data processing and interpretation, and production of a Field Geotechnical Report needed
to respond to the March 20 I 0 RAI and provide a basis for updating the channel alignment
and design. Investigation results incorporated into the RAI will include a series of fence
post diagrams and a plan view map depicting elevation contours of key seismic reflectors.
Within flood shoal and the inlet throat the contours of the known rock and clay layers
previously identified within the investigation area will be mapped from the sub-bottom
survey. Probes and cores across this area will be used to ground truth these features,
Although the seismic will be limited by depth within the interior channel, any sub-bottom
data collected along with the historic cores and those collect during this investigation will
be utilized to develop the contour elevations of the interior organic surface
A one (I) day seismic reflection profiling survey will be conducted over the investigation
area. Following the geophysical survey, sixteen (16) vibracores will be collected. It will
take 3 days to obtain the 16 vibracores due to the shallow nature of the work area and the
dangerous conditions working in the strong currents within the inlet and hazardous wave
conditions on the shoals and inlet throat. Both investigation need to be conducted during
period of higher tide levels.
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TASK V-A: Proiect Manae:ement
This task includes the management of the project.
TASK V-B: GEOPHYSICAL SURVEY
The geophysical investigation will be comprised of a one (1) day joint seismic and
bathymetric survey. The geophysical survey includes subbottom profiling using the
EdgeTech X-Star SB-5l2i/2l6s "chirp sonar system". The minimum area to be surveyed
is provide in Figure 1, and will be limited by depth. Time permitting; the survey will
extend outside this region to define the extent of the substrate. Tides will be considered in
selecting the time of the survey to maximize coverage. The shallowest region will be
scheduled for high tide.
The survey control and accuracy standards will be consistent with FDEP specifications, a
report from the surveyor will be submitted certifying that the survey meets Bureau of
Beaches and Coastal Systems (BBCS) Technical Standards established in Part II.A of
section 01200 in the BBCS Monitoring Standards for Beach Erosion Control Projects,
March 2004 and minimum technical standards of Chapter 61 G 17-6, Florida
Administrative Code.
Geophysical Survey Equipment
Navigation System
A Trimble Real Time Kinematic Global Positioning (RTK GPS) system with dual
frequency receivers will be used on board the survey vessel to provide high-
precision navigation and instantaneous tide corrections. In order to maintain the
vessel navigation along the profile lines the Hypack Inc.'s hydrographic system
Hypack 201O@ will be used. This software merges RTK GPS vertical and
horizontal positioning with the sounding data, allowing real time review of the
profile data in plan view or cross section format. It also provides navigation to
the helm to control the deviation from the online azimuth.
Seismic Reflection Profile Surveys
An EdgeTech X-STAR 512i or 216s seismic sub-bottom system will be used to
conduct the seismic reflection profile surveys. The X -STAR SB-512i/216s Full
Spectrum Sonar is a versatile wideband FM sub-bottom profiler that collects
digital normal incidence reflection data over many frequency ranges. This
instrumentation generates cross-sectional images of the seabed (to a depth of up to
50 ft). The X-STAR SB-512i/2l6s transmits an FM pulse that is linearly swept
over a full spectrum frequency range (also called a "chirp pulse"). The tapered
waveform spectrum results in images that have virtually constant resolution with
depth.
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Throughout the offshore seismic reflection survey, selection of the chirp pulse
will be modified in real time to obtain the best possible resolution of geological
features and the sequence stratigraphy (i.e. vertical sequence and lateral
distribution of sediment bodies comprised by different grain sizes and sediment
composition) that in turn optimizes data quality and enhances subsequent
interpretation. High frequency and/or short duration pulses are, for example, used
to obtain highest resolution (clearest reflector image) in near surface situations;
low frequency or longer duration pulses are used where deeper penetration is
required.
Bathymetric Survey
Bathymetric data will be obtained along the seismic track lines and at each
vibracore site. This investigation will not be sufficient to develop a complete
bathymetric map of the interior channels. The 2009 bathymetric survey will be
utilized for permit and preliminary design in the flood shoal, and the latest annual
survey will be used for the ebb shoal where appropriate. The Odom Hydrographic
Systems, Inc.'s Hydrotrac, a single frequency portable hydrographic echo
sounder, will be used to perform the bathymetric survey. The Hydrotrac operates
a frequency of 210 kHz and is a digital, survey-grade sounder. The sounder will
be calibrated using an Odom Hydrographic Systems, Inc.'s Digital Pro@ speed-
of-sound velocity meter. Speed of sound through water and other selected
parameters will be adjusted to accurately reflect physical water conditions in the
survey area.
Geophysical Data Analysis
The EdgeTech Discover data acquisition system collects and stores geophysical survey
data in a digital format. EdgeTech's Discover is a modular acquisition and processing
software package that is compatible with all of EdgeTech's systems. It serves as the
digital image processing, display, storage, and surface control station for the EdgeTech
512i/216s sub-bottom profiler (chirp sonar system). This data acquisition system
digitizes, stores, and processes seismic signals and combines the seismic imagery with
navigational inputs to georeference data in real-time. Hardcopy records will be produced
during data acquisition.
All seismic reflection data will be processed using the SonarWiz.MAP software package
developed by Chesapeake Technologies Inc. This software package allows for advanced
processing, interpretation, and digital mosaic output and can produce georeferenced
HTML's viewable in generic web-browser software programs. SonarWiz.MAP also
produces digital geographic information for the sub-bottom data that are exportable for
incorporation into a GIS database. All sub-bottom profile data will be processed and
interpreted by CPE personnel.
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TASK V-C: GEOTECHNICAL SURVEY
A geotechnical survey plan (Figure I) was developed in coordination with the Florida
Department of Environmental Protections Bureau of Beaches and Coastal Systems
(BBCS). Sixteen (16) vibracores will be collected during this investigation. The coring
depths will extend at least 2 feet below the proposed channel depth plus overdredge or
refusal at the hard substrate.
Geotechnical Survey Equipment
A Rossfelder P3 Vibracore, or equivalent, configured to collect undisturbed sediment
cores up to 20 feet in length, will be used for this project. This self-contained,
freestanding electronic vibracore unit contains a vibratory hammer assembly, an
aluminum beam which acts as the vertical beam upright on the seafloor, an aluminum
coring pipe, and a cutting edge.
Geotechnical Data Analysis
Sediment Sample Analysis
Upon completion of field operations, all vibracores will be transported to CPE's
office in Boca Raton, FL. There, the vibracores will be logged by describing
sedimentary properties by layer in terms of layer thickness, color, texture (grain
size), composition and presence of clay, silt, gravel, or any other identifying
features. The vibracores will be photographed in 2.0 ft intervals. Sediment
samples will be extracted from the vibracores at irregular intervals based on
distinct stratigraphic layers in the sediment sequence. The vibracores will then be
wrapped and archived. Cores will be stored for a period of up to one (I) year.
After this time, cores will either be relinquished to the client or stored for an
additional annual cost of $25 per core.
Mechanical Sieve Analysis
The sediment samples will be analyzed to determine color and grain size
distribution. During sieve analysis, any obvious uncharacteristically large
fragments will be removed and the description (weight and size) of the material
will be noted. The wet, dry and washed Munsell colors will be noted. Sieve
analysis of the sediment samples will be performed in accordance with the
American Society for Testing and Materials (ASTM) Standard Methods
Designation D 422-63 for particle size analysis of soils. This method covers the
quantitative determination of the distribution of sand size particles. For sediment
finer than the No. 230 sieve (4.0 phi) the ASTM Standard Test Method,
Designation D 1140-00 will be followed. The sieve stack used for mechanical
analysis will conform to the BBCS guidelines provided in Table I.
Weights retained on each sieve will be recorded cumulatively. Grain size results
will be entered into the gfNT@ software program, which computes the mean and
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median grain size, sorting, silt/clay percentages for each sample using the moment
method.
Table I. Mesh sizes to be used for granularmetric analysis.
Sieve No.
3/4
5/8
7/16
5/16
312
4
5
7
10
14
18
25
35
45
60
80
120
170
200
230
Size (phi)
-4.25
-4.0
-3.5
-3.0
-2.5
-2.25
-2.0
-1.5
-1.0
-0.5
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
3.75
4.0
Size (mm)
19.00
16.00
11.20
8.00
5.60
4.75
4.00
2.80
2.00
1.40
1.00
0.71
0.50
0.36
0.25
0.18
0.13
0.09
0.08
006
TASK V-D: FIELD REPORT DEVELOPMENT AND RAI RESPONSE
A final Field Report summarizing the results of the geotechnical investigation will be
prepared and submitted to Collier County and the FDEP as a response to the March 2010
RAI and as an appendix to the inlet management study. This report will include project
results, sub-bottom (seismic) survey profiles, vibracores logs, vibracores photographs,
granularmetric reports and grain size distribution curves.
From the vibracores, as discussed above we will be described for sedimentary properties
by layer in terms of layer thickness, color, texture (grain size), composition and presence
of clay, silt, gravel, or any other identifying features. We will use this information to
develop a dredge cut protocol similar to the 2007 Lee county "Sediment Quality
Assurance/ Quality Control Plan" for Blind Pass. The protocol will be in accordance with
FAC 62B-41.007Ch.k and olher guidance for FDEP) which calb for "l\laterial with up to
I 0"';, fine.: by <,,-,cight, u:: defined by pas.;ing the "230 ::ieve, .:hull be pla:;cd directly on the
beut.-4t-rvlaterHtl--witl-1--fH\)rethun-I+l%-hui-lesS-HtfltJ-2!l!!;,-fifles.lvy-.wetght-w-i+l-~)e-ptUBmj.-i-n
the nearshore -region of tbe~tffii-itf-ea. iVlutcrial v.-itb clay or c::ccs::ive fine content
sftttl-l--b\H.~e4.+n-an up1uncl~ Table .2 ::]]0\\.; the specil1catiolls for the pbccment
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Tuble2. PI,!cemen: Spec(:!"<\!:iOlI
D -' 10% by \Veight Pa,;smg &t11-Ge+JtBtH
~ :&~ve
D 5l~ ~, by W ci sJ-H-I~elBffied ---Fifl~
on 1 Eic.,c
24%-<-I)-.<~1~-WBigltl &tll-GelHetl1:
NCllr:;hore Pa.;sm2; 230 Sieve
D 51)6 by Weight Retamed Fine CiLlyel
on--4-&i-eve
-,::;:- ~'.." ;-;-, Silt Content
'.J 'CO' 'CO
2Jq-S.i~
O-->--S%-lTy--\l.ieiglti-R-etaitted FiHe--Gruvel
on I Siele
I ~ Wood. Roclc, D;:;bri~ or
-l-:i*uHO G{.Jte~~t-MtlteTffit
I Materi II 1 resultin; r,_ "., ,-,
m <OJ
Cernentutioll on the bcach Wood, Rock, Debri:; or
Other Forei;n IVI uteri ul
ePE will provide all geotechnical information to the FDEP ffi
rcoort suitablc f()r permittinQ and inclusion in the inlct mana(':emcnt study. r:. electronic
format5-l;titahlef(lftllfJUtl{)tRv---ffiEPRe€BHfrab&LH1i."e-()fit51J{we-SalliJ~H:::h--fRGSS-)
Jataha~Jilre-fl.attt,-will~tl:m-litted in ,\G~T files. l'He--&t!l:lmiscion will
fnf,lttdc :hapefile: (with the (l,;soeiaied FGDG-ee.mj3-ltnni metadata) of \'ibrueere-H.'1€ffi'iefffi
UH4-si.c'bt-"Hit--I+a,,*1-if~Seismic data will be provided in HTML format. Seismic
timestamps and shot points are not recorded as HTML formatting embeds all navigation
data, making timestamps and shot points obsolete.
ePE will use the data collected from these investigations to respond to the Request for
Additional information issued by BBeS on March 24th 2010 and develop the new
channel alignment in Task I above.
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CAVEATS
CPE proposes to perform the Wiggins Pass Improvements Investigation to the industry
standard of care and will coordinate the investigations with governmental agencies as
required. CPE will attempt to avoid potential problems and restrictions, but there may be
adverse circumstances that cannot be avoided or mitigated. Investigation outcomes are
beyond the control of CPE and may result in the need for additional services. The client
herein recognizes the above referenced risks and agrees to work with CPE to complete
the work. CPE is working exclusively on your behalf and will attempt to limit the risks
as described above to the greatest extent practicable. No new field investigations other
than those described above are anticipated or included in this scope of work.
A small amount has been set aside for contingencies or future RAIs, to be used by
approval of the County.
VI. CONSTRUCTION SERVICES:
To be determined: Plans, specification, construction observations, surveys, post-
construction report and certification.
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From: George, Vincent [mailto:Vincent.George@dep.stateJl.us]
Sent: Wednesday, August 24,2011 3:33 PM
To: McAlpinGary
Cc: Steve Keehn
Subject: Wiggins Pass IMP Update, etc.
Gentlemen,
Please see the comments below for the May 25,2011 SOW. Please address these inquiries
ASAP to begin a shorter 14 day review of a revised SOW. These are the comments referred to in
yesterday's teleconference from the initial 21 day review.
Regards,
Vince
SW FL Project Manager
Beach Erosion Control Program
DEP Bureau of Beaches and Coastal Systems
850-413-7783
The CES engineering staff review of the scope of work for Wiggins Pass, which includes the
preparation of the inlet management plan report, has been completed.
The following comments are provided:
1) II. PREPARE INLET MANAGEMENT STUDY
a) Please clarify what specific guidance is expected in "Specific guidance from FDEP will be
provided during the report preparation process. The new legislation changes Section
161.142 and 161.143 F.S."
b) A committee appointed by the County will review progress of the plan preparation and
their
decisions will be incorporated into the plan. The initial draft plan will be submitted to the
County and FDEP for their comments. The FDEP's adopted plan may differ from the
County's based on the State's procedures.
Are Florida Parks Services (FPS) and Bureau of Beaches and Coastal Systems (BBCS)
represented in the committee?
2) TASK II-A. COASTAL ENGINEERING ANALYSIS
2. Shoreline Position Mapping & Change Analysis.
a) The consultant will use a geographic information system (GIS) approach to compile and
analyze the temporal shoreline position change analyses. The GIS analysis will enable
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temporal and spatial comparison of FDEP historical shorelines and historical aerial
photography.
Is the GIS data a deliverable item?
b) Special considerations will be given to short-term changes so natural and man-made
responses are not minimized by averaging data.
Special consideration should be given to the period since 1999 since the inlet channel was
modified and maintenance dredged.
3. Volumetric Changes and Sediment Budget Update.
A post-dredge sediment budget analysis will be used to describe the sediment transport
pathways in the vicinity of Wiggins Pass and adjacent beaches. It will be compared to the
sediment budget from the
1995 study. The sediment budget will be expanded beyond the sediment budget will he
expanded beyond the 1-mi monitoring area north and south of the inlet.
The monitoring area north and south of the inlet should include the zone of influence of
the inlet. Is the odd-even analysis method valid for this location? Other methods, such as,
the examination of historical MHW shoreline and volume changes, alongshore variations
in beach morphology (steepness), wave refraction analysis and/or net sink effects should
be considered. How will the coastal cells be defined?
4. Development of Inlet Management Alternatives.
a) The consultant will identify and describe various non-structural alternatives to improve
sediment management within Wiggins Pass. No structural alternative will be considered.
The alternatives will address methods to control inlet channel migration, channel
modifications, dredge management options for the navigation channel entrance, and sand
distribution and bypassing to reestablish
near-historic levels of sediment transport. Quantity and costs will be developed for the
selected alternative that is shown to be viable. The performance of viable management
options will be evaluated in Task B.
Quantity and costs should be developed for all the alternatives shown to be viable.
b) The scope of work should include the following task. The study of the effect of the north
and south tributaries at the confluence of the interior Wiggins Pass channel should be
included in the preparation of Wiggins Pass Inlet Management Study.
The objectives of the study should be to analyze the flow velocities at the confluence of
the channel and the tributaries to determine the minimum ebb flow velocity necessary to
prevent/reduce shoaling. Also, the study should include determining the orientations of
the north and south tributaries at the confluence that will maintain the Wiggins Pass
channel design and optimize the flow conditions in the channel that will minimize
shoaling.
(The measurement of flow velocities of the north, south and Wiggins Pass channels at the
confluence should be included in the monitoring program. Also, bathymetric surveys of
the area to determine changes in flood shoal should be included in the monitoring
program.)
15
CAC September 8, 2011
VII-10 Staff Reports
15 of 17
3) IV MODELING OF ADDITIONAL ALTERNATIVES
Based on FDEP's letter data May 13, 2011 and a telephone conference on May 20,2011,
no additional modeling will be required if the County's straightened channel design
leaves in place most of the marine peat, rock and clay substrate that stabilizes the inlet
location. The inlet management study will present a plan to restore the ebb shoal and
beach, the major purpose of the new modeling.
Please note that the May 13,2011 FDEP letter does not state or imply".. . leaves in place
most of the marine peat, rock and clay substrate... " rather it states in part "The County
shall revise the width and depth of a straightened navigation channel to avoid dredging
and excavation of the consolidated materials (marine peat, clay and rock) that are beneath
the sandy bottom of the Pass. This material acts to stabilize the mouth of Wiggins Pass at
its historic location, and as has been clearly articulated, Bureau staff is concerned that
removal of this material could lead to lateral migration of the inlet channel and beach-
dune erosion of the adjacent Parks."
ec: CE Review
GEOTECH COMMENTS:
These comments are organized according to the scope of work submitted for review.
Task IV:
There is a statement in this task that "no additional modeling will be required if the
County's straightened channel design leaves in place most of the marine peat, rock and
clay substrate that stabilizes the inlet location." The statement implies that the
geotechnical investigation and the horizontal and vertical interpretation of this material
(in Task V) must be successful in order to avoid the marine peat, rock, and clay
substrate.
Task V:
This study should include the quantification of the material to be dredged/removed by
type. (In order to know if a sufficient quantity of beach compatible sand exists to fill the
meander, one must know how much there is available, and what the capacity of the
meander is/will be.)
Task V-D: This is not a maintenance dredge project. This project includes channel
improvements and new work. Therefore, Chp 62B-41.007(2)(k) does not apply. Because
this is construction, Chp 62B-41.007(2)(j) applies.
Task V-D: Please adjust Table 2 based on the comment above AND include information
in this table regarding the meander fill.
16
CAC September 8, 2011
VII-10 Staff Reports
16 of 17
Task V-D: Please note that this information is not needed for inclusion in the ROSS-
OSS! database because this project is channel and shoal related, not an offshore project.
The Department of Environmental Protection values its customers' opinions and feedback.
Please take a few minutes to share comments on the service you received from the
on this
17
CAC September 8, 2011
VII-10 Staff Reports
17 of 17
CAC September 8, 2011
VII-11 Staff Reports
1 of2
Attachment 2
Fund 195 Spending/Budget Analysis for Fiscal Year 2008/2009 through 2011/2012
County Sea Turtle Protecion Program $ 63,733.33 $ 54,319.67 $ 54,866.67 $ 54,333.33
County Beach Tilling $ 13,333.33 $ 13,333.33 $ 5,833.33 $ 5,833.33
County Physical Beach & Pass Monitoring $ 50,000.00 $ 76,000.00 $ 65,666.67 $ 86,666.67
County Wiggins Pass Intermediate Program-
Engineering & Dredge $ 750,000.00
Cou nty Wiggins Pass Master Plan Engineering
and Permitting $ 160,717.00 $ 177,489.00
County Wiggins Pass Engineering/Dredging $ 783,210.00
County Wiggins Pass Inlet Monitoring $ 30,000.00 $ 22,500.00
County Wiggins Pass Maintenance Program $ 50,000.00
Cou nty Clam Pass Ebb Shoal Modeling $ 125,000.00
County Clam Pass Inlet Monitoring $ 20,000.00
Cou nty FY 12/13 Beach Analysis/Model With Hot
Spot Solutions $ 150,000.00
County Beach Maintenance - County $ 55,000.00 $ 67,500.00 $ 67,500.00 $ 67,550.00
County Vegetation Repair/Exotic Removal-
County $ 25,000.00 $ 25,000.00 $ 25,000.00 $ 25,000.00
County Fund 19S Administration $ 177,400.00 $ 166,666.67 $ 170,366.67 $ 170,166.67
County Indirect Administration Costs $ 39,233.33 $ 35,900.00
County Biological Hardbottom and Artificial Reef
Monitoring $ 116,666.67 $ 91,666.67 $ 15,000.00
County
Collier Beaches Design/Permitting-Fay $ 150,000.00
TOTAL $ 1,334,343.33 $ 952,703.33 $ 1,328,466.67 $ 687,939.00
COLLIER COUNTY
2008/2009
2009/2010
2010/2011
2011/2012
$ 4,303,452.33
City of Naples Sea Turtle Protection Program $ 63,733.33 $ 54,319.67 $ 54,866.67 $ 54,333.33
City of Naples Beach Tilling $ 13,333.33 $ 13,333.33 $ 5,833.33 $ 5,833.33
City of Naples Physical Beach & Pass Monitoring $ 50,000.00 $ 76,000.00 $ 65,666.67 $ 86,666.67
City of Naples Beach Maintenance - City of Naples $ 134,760.00 $ 73,460.00 $ 75,850.00 $ 76,850.00
City of Naples Vegetation Repair/Exotic Removal -
Naples $ 25,000.00 $ 25,000.00 $ 25,000.00 $ 25,000.00
City of Naples Naples Pier Annualized Repair &
Maintenance $ 55,000.00 $ 55,000.00 $ 55,000.00
City of Naples Naples Conceptual Drainage Design $ 50,000.00
FY 12/13 Beach Analysis/Model With Hot
City of Naples Spot Solutions $ 150,000.00
City of Naples Fund 195 Administration $ 177,400.00 $ 166,666.67 $ 170,366.67 $ 170,166.67
City of Naples Indirect Administration Costs $ 39,233.33 $ 35,900.00
City of Naples Doctors Pass Inlet Monitoring $ 20,000.00 $ 22,700.00
City of Naples Doctors Pass Dredging $ 783,210.00
Biological Hardbottom and Artificial Reef
City of Naples Monitoring $ 116,666.67 $ 91,666.67 $ 15,000.00
City of Naples Emergency Truckhaul Project $ 1,500,000.00
City of Naples Truck Haul- Vista's at Park Shore $ 350,000.00
City of Naples Doctor's Pass Jetty Rebuilds $ 653,200.00
TOTAL $ 1,384,103.34 $ 2,105,446.34 $ 1,317,716.67 $ 874,750.00
CITY OF NAPLES
2008/2009
2009/2010
2010/2011
2011/2012
$ 5,682,016.35
City of Marco Island Sea Turtle Protection Program $ 63,733.33 $ 54,319.67 $ 54,866.67 $ 54,333.33
City of Marco Island Beach Tilling $ 13,333.33 $ 13,333.33 $ 5,833.33 $ 5,833.33
City Of Marco Island
Physical Beach & Pass Monitoring $ 50,000.00 $ 76,000.00 $ 65,666.67 $ 86,666.67
CITY OF MARCO ISLAND
2008/2009
2009/2010
2010/2011
2011/2012
CAC September 8, 2011
VII-11 Staff Reports
20f2
City Of Marco Island FY 12/13 Marco Island Analysis/Model
with BW Engineering $ 150,000.00
City Of Marco Island Beach Maintenance - Marco $ 55,000.00 $ 67,500.00 $ 67,500.00 $ 67,550.00
City Of Marco Island Vegetation Repair/Exotic Removal -
County Wide $ 25,000.00 $ 25,000.00 $ 25,000.00 $ 25,000.00
City Of Marco Island Caxambas Pass Inlet & Marco South
Beach Monitoring $ 45,000.00 $ 25,000.00
City of Marco Island Breakwaters & Jetties of South Beach -
Marco $ 100,000.00
City of Marco Island MI Renourish Design & Permit with BW
Solutions $ 300,000.00
City Of Marco Island Hideaway Beach trosion Control
Structu res $ 1,600,000.00
City Of Marco Island
Fund 195 Administration $ 177,400.00 $ 166,666.67 $ 170,366.67 $ 170,166.67
City Of Marco Island
Indirect Administration Costs $ 39,233.33 $ 35,900.00
City Of Marco Island Hideaway Beach GrOin/Physical
Monitoring $ 25,000.00 $ 30,000.00
City Of Marco Island
Tigertail Beach Refurbishment $ 25,000.00
City of Marco Island Laser Grading North Marco Beach $ 20,000.00
City Of Marco Island
Collier Creek Emergency Dredging $ 280,000.00
TOTAL $ 454,466.67 $ 2,057,819.67 $ 678,466.67 $ 1,070,450.00
$ 4,261,203.01
G:TDC Information FiJes!TDC Info by Year/TOe 2011 Agenda Items{B-ll TDC Meeting Budet for 3 years
CAC September 8, 2011
VII-12 Staff Reports
1 of 1
From:
To:
Subject:
Date:
McAloinGarv
HambriahtGail
CAe meeting 9-8-2011 Staff reports - Item 12 Fema Fay Update/timing
Monday, August 29, 201111:13:33 AM
CAC meeting 9-8-2011 Staff reports - Item 12 FEMA Fay Update
The Council requested Staff provide quarterly reports on the status (including)
collections/receivables) of the FEMA reimbursements.
· The FEMA second appeal for Tropical Storm Gabrielle is still under review
with FEMA Washington. Over the last month, Connie Mack office, The Ferguson
Group (Collier County's federallWashington, DC lobbyists) and our consultant James
Lee Witt have all contacted FEMA Washington at our request to determine status of
our appeal/claim. Each reply is that the Appeal is under review with the FEMA staff
in Washington.
· TS Faye existing work authorizations to Collier County will expire in August
2012. Staff will revise the justification and seek an extension to
these authorizations once the conceptual design for the main beach
renourishment and the Marco South renourishment is completed.
J. Gary McAlpin, Director
Coastal Zone Management
3299 Tamiami Trail East, Suite 103
Naples, Florida 34112
Ga ryMcAI pi n(a)coll iergov. net
(239) 252-5342
Fax: (239) 353-4061
Under Forida Law. e-n1ail addresses are records If yOU do not want e-mail address released in response to a public
records request, do not send electronic to this entity. Instead, contact office by telephone or in wriling,
TOC Funds Sensititivy Analysis
CAC September 8, 2011
VII-13 Staff Reports
1 of 8
Revenue Sensitivitv Analvsis
Category
"A" 195 Fund 183 Fund
TDC Revenue Revenue Revenue Revenue
Projected TOC Revenue $13,000,000 $6,500,000 $4,355,000 $2,145,000
Reduction in TOC Revenue by 10% $11,700,000 $5,850,000 $3,919,500 $1,930,500
Reduction in TOC Revenue by 20% $10,400,000 $5,200,000 $3,484,000 $1,716,000
Reduction in TOC Revenue by 30% $9,100,000 $4,550,000 $3,048,500 $1,501,500
Priorities
Priority #1- Regulatory Compliance $470,500
Priority #2 - Beach Maintenance $341,950
Priority #3 - Fee's (Admin; Indirect; Tax Collector) $727,075
Priority #4 - Reserves (Revenue; Pier maintence Contingency) $442,750
Priority #5 - Renourishment and Emergency Reserve $2,500,000
Subtotal $4,482,275
Fundin~ Priorities at 10% Revenue Reduction $3,919,500
10% reduction in TDC Beach Funds $435,500
Eliminate truck Haul at Vista at Park Shore $350,000
Eliminate Marco laser Grading $20,000
Eliminate Tigertail Beach Refurbishment $25,000
Reduce Beach renourishment costs by $40,000 $40,000
Subtotal $435,000 $0
Fundin~ Priorities at 20% Revenue Reduction $3,484,000
20% reduction in TDC Beach Funds $871,000
Eliminate truck Haul at Vista at Park Shore $350,000
Eliminate Marco laser Grading $20,000
Eliminate Tigertail Beach Refurbishment $25,000
Reduce Beach Design renourishment costs by $100,000 $100,000
Reduce WPass maintenance dredge engr. by $25,000 $25,000
Reduce Administrative Fee's by $50,000 $50,000
Use $301,000 from Reserve Surplus $301,000
Subtotal $871,000 $0
Gary McAlpin 8/30/2011
TOC Funds Sensititivy Analysis
CAC September 8, 2011
VII-13 St2ff Reports
2 of 8
Fundin~ Priorities at 30% Revenue Reduction
30% reduction in TDC Beach Funds
Eliminate truck Haul at Vista at Park Shore
Eliminate Marco laser Grading
Eliminate Tigertail Beach Refurbishment
Reduce Beach Design renourishment costs by $100,000
Reduce WPass maintenance dredge engr. by $25,000
Reduce Administrative Fee's by $50,000
Use $736,500 from Reserve Surplus
$3,048,000
$1,306,500
$350,000
$20,000
$25,000
$100,000
$25,000
$50,000
$736,500
Subtotal $1,306,500 $0
Gary McAlpin 8/30/2011
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FY11/12 -195 Fund Budget and Analysis - Rev.1
FY 10/11 Carry Forward
Carry Forward Total
Projected FY11/12 Revenue
Tourist Tax Revenue for Beachesllnlets
Revenue Reimbursement FDEP
Revenue - FDEP Cost Share Contract
Tilling and Cleaning Revenue
Revenue Reserve (5%)
Projected Expenses
1. Regulatory and Pennit Compliance - FY 10/11
Sea Turtle Protection Program
Beach Tilling
Physical Beach Monitoring - Entire County
Biological Monitoring
2. Planned Projects/Future Projects - FY 10/11
Wiggins Pass Intermediate Dredging - Engineer
Emergency Truck Haul - Vista @ Park Shore
FY12/13 County Beach Design and Permitting
FY12/13 Marco Beach/B'water Design/Permitting
Laser Grade North Marco Beach (R133-R141)
Tigertail Beach Refurbishment
3. Beach Maintenance - FY 10/11
Collier County/Marco Island
City of Naples
Vegetation Repairs/Exotic Removal
Naples Pier and Dock Maintenance
4. Administration Fee's - FY 10/11
Fund 195 Administration
Indirect Administrative Costs
Tax Collector Fee's (2.5%)
6. Other Expenses - FYi 0/11
Renourishment and Emergency Reserves
Contingency Reserve
Category D Pier Reserve
Revenue Total
Sub-Total
Sub-Total
Sub-Total
Sub-Total
Total Expenses
Sub-Total
Fund Balance Total
$4,371,800
-$3,400,000
$50,000
$1,500
-$218,600
$22,332,900
CAC September 8, 2011
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FY11/12 Totals
$22,332,900
$804,700
CAC September 8, 2011
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Evaluation/Approval Guidelines for TDC Category A Yearly Grant Requests by the Coastal
Advisory Committee
Yearly grant requests to the Coastal Advisory Committee will be evaluated, prioritized and funded
based on the following criteria.
1. Grants associated with the completion of a previously approved project that are required to
complete that project.
2. Grants required to meet Permit Regulatory Compliance. Examples of these grants would be
Physical and Biological monitoring, turtle monitoring, shorebird monitoring and tilling.
3. Safety related activities and projects, which are the responsibility of the CAC.
4. Commitments covered by inter-local agreement and lor projects previously
approved/identified in the 10 year plan. Examples would be the dredging of Clam, Wiggins,
Doctors, Caxambas and Capri Passes and the IO-year cycle of beach re-nourishment.
5. Projects or studies that improve or have a high probability of improving our beach efficiency,
the preservation of CAC capital or save us money. These projects would have to have a
undisputed payout. Items that would fall into this category would be engineering or studies
that could lengthen times between dredge events or re-nourishments.
6. Grants associated with the maintenance and upkeep of our beaches. Examples of these
activities that preserve the quality of the beach experience are beach cleaning, raking and
grading.
7. Projects that outside funding or third party funding can be obtained on that offset the capital
cost. Examples would be FDEP funding, FEMA funding or third party grants.
8. Necessary or required projects would be next. Examples of this type of projects would be
Doctors Pass Rip-Rap replacement.
9. New projects not required by law or consent decree would follow.
CAC September 8, 2011
VII~~C'~!f~%)~ 1
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Share TDC Category "A" Grant Applications from the City of Naples, The City
of Marco Island and Collier County for FY-l1/12.
OBJECTIVE: To share Category "A" grant applications and requests.
CONSIDERATIONS: Received TDC Category "A" Grant Applications as follows:
2010/11
PROJECT/DESCRIPTION: AMOUNT REOUESTED GRANTED
1. Re!!ulatorv and Permit ComDliance .Jj. /'
Sea Turtle Protection Program - Collier County $.168-,ruu'. fA)~ r $164,600
Beach Tilling - Collier County - 80171 $ 17,500 r~._ $ 17,500
Physical Beach & Pass Monitoring Collier County Beaches - $~1,6ol'- $260,000
90536
Biological Monitoring - 90033 $ 30,000 " ,.,<- ~
SUB-TOTAL $483,400 $442,100
2. Planned Proiects
Wiggins Pass Maintenance Program - Engineering - 90522 $ 50,000 ~k: $750,000
.. -"Truck Haul Vista's at Park Shore 88030 $350,000 OK.. 0
Q 'h1;.w ~Beach Design and Permit with HS Solutions - 80096 $600,000 tYk $300,000
~v11 Renourish Design & Permit with BW Solutions - 80166 . $300,000 tJk., $150,000
Laser Grading North Marco Beach (R133-RI41) $ 20,000 d1< 0
Tigertail Beach Refurbishment $ 25,000 tJt,- 0
SUB-TOTAL $1,345,000 $1,200,000
3. Beach Maintenance
Beach Maintenance - Collier County/Marco Island - 90533 $135,100 ) $ ] 35,000
Beach Maintenance - City of Naples- 90527 $ 76,850 (9t\. $ 75,850
Vegetation Repairs/Exotic Removal - County Wide - 90044 $ 75,000 . $ 75,000
Naples Pier Annualized Repair & Maintenance - City of $ 55,000 ) $ 55,000
Naples - 90096
SUB-TOTAL $341,950 $340,850
4. Administration Fee's
Fund 195 and 183 Administration - Collier County- 90020 $510,500 $511,100
Indirect Administration Costs $107,700 $117,700
Tax Collector Fee's (2.5%) $109,300 $104,863
SUB-TOT AL $727,500 $733,633
5. Other EXDenses
Renourishment and Emergency Reserves $17 ,000,000 $14,500,000
Revenue Reserve (5%) $ $218,608 $ 217,800
Category D Pier Reserve $ 79,000 $ 79,000
CAC September 8, 2011
VII-~~~2P~a~1
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Reserve for Contingency Totals $ 146,000
Reserve for FDEP Reimbursement $ 3,400,000
SUB-TOTAL $20,843,600 $14,796,800
TOTAL $23,741,450 $17,563,413
COUNTY ATTORNEY FINDING: A finding by the County Attorney is not required for this
item.
STAFF RECOMMENDATIONS:
Reeulatorv and Permit Compliance:
All these items are required by FDEP permit and required by law. Approval is recommended.
Planned Proiects:
~ Wiggins Maintenance Program - En?:ineering for - Intennediate Dredging of Wiggins Pass
for FY 2012/13. Approval is recommended.
~ Emergency Truck Haul- Vista's at Park Shore - The Vista's condominium is located directly
south of the Seagate emergency renourishment recently completed. This location was
previously approved for re-nourishment by the CAe but analysis and design could not be
accomplished by Sea Turtle nesting season. Approval is recommended.
~ FY 12/13 Beach Design and Permit with HS Solutions - This item will fund beach design
and pennitting to detennine a renourish plan (including Hot Spot permanent solution) for the
main Collier County beaches. The conceptual design basis should be completed and these
funds are a preliminary estimate to begin the design. Approval is recommended.
~ Marco Island Renourish Design & Penn it with BW Solutions - This item will fund beach
design and permitting to determine a renourish plan (including Hot Spot pennanent solution)
for the Marco "Island South beach. The conceptual design basis should be completed and
these funds are a preliminary estimate to begin the design. Approval is recommended.
~ Laser Grading North Marco Beach (R 133-R 141) - Laser grade the northern portion of Marco
Island Beach just south of Sand Dollar Island. This has had limited effectiveness in the past
but is requested by the Marco Island Beach committee.
~ Tigertail Beach Refurbishment - Tigertail will be tilled prior to turtle nesting season.
Investigate what options exist to enhance the beach at Tigertail to be more attractive to
tourists. Approval is recommended.
Beach Maintenance:
Exceptional beach experience for our residents and visitors has been at the heart of our success in the
past. These items are required to maintain that experience. Approval is recommended.
Administration Fee's:
This item funds County staff to manage the projects, maintain the beaches, administer the program.
It includes the Director; an Office Manager/Accountant; a Field Supervisor/Project Manager; and
two equipment operators to clean and maintain the County and Marco Beaches. It also includes
Administrative Indirect Fees required for administrative functions like purchasing, infonnation
CAC September 8, 2011
VIIC~C'~~~1
8 OV~I-4 New Business
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technology, motor pool and human resources. Tax collector fees are also included in this item.
Approval is recommended.
Other Expenses:
This item provides for board mandated renourishment reserves, emergency reserves and revenue
reserves. Approval is recommended.
FISCAL IMPACT: The total amount of grant applications for FY 11/12 in the amount of
$24,198,190 is in the proposed budget for Category "A" Tourist Development Taxes.
GROWTH MANAGEMENT IMPACT: There is no impact to the Growth Management Plan
related to this action.
RECOMMENDATION: That the CAC recommend approval of the attached Tourist Development
Category "A" grant applications and request in the amount of $23,741 ,450 and approve all necessary
grant agreements per County Attorney's approval.
PREPARED BY: Gail Hambright, CZM Accountant
CAC September 8,2011
VIII-1 New Business
1 of 5
EXECUTIVE SUMMARY
Recommendation to award Bid No.11-5763 to Energy Resources, Inc in the amount of
$262,000 for the emergency dredging of Collier Bay entrance channel and authorize the
Chairman to execute the standard contract after County Attorney approval.
OBJECTIVE: To award Bid No. 11-5763 to Energy Resources, Inc. for the emergency
dredging of Collier Bay entrance channel in the amount of $262,000.
CONSIDERATION: Collier Bay on Marco Island is experiencing hazardous boating
conditions with the accretion of approximately 10,000 CY's of beach compatible sand in the
mouth of its entrance channel. Approximately one third of the Marco Island boating community
routinely access Collier Bay using this channel. This project will restore safe navigation by
removing the shoal that is creating a hazardous boating condition. Beach compatible sand
dredged from this location will be discharged in the near shore tidal zone on the down drift
Hideaway Beach beaches.
This entrance channel was dredged in 2001 using TDC funds and the dredged sand was placed
on Hideaway Beach. The Rock Jetty was built in 2005 using TDC funds. County Ordinance
2001-03 authorizes this activity as per section 2, item D. Additionally the County Attorney's
Office has issued an opinion in 2003 and 2005 that TDC funds can be used for the dredging of
Collier Creek if a finding is made that it promotes tourism. These opinions are attached.
An Emergency Resolution form the City of Marco Island is attached supporting this dredging
activity.
On 8/12/2011, bids were posted in the lobby of the Purchasing Department with 200 vendors
being notified and 78 bidders electronically downloaded plans. On September 2, 2011, 9 bids
were received. Staff evaluated the bid received and determined that Alternative #1 allowing a 75
day construction be accepted. Additionally, staff determined that Energy Resources, Inc. was the
lowest, qualified and responsive bidder for both the 60 day and 75 day construction schedules.
Energy Resources, Inc is also a local vendor. The bid tabulation is attached.
Therefore, in consideration of the lowest, qualified and responsive bidder staff recommends that
Alternative #1 allowing for a 75 day construction schedule for Bid No. 11-5763 be awarded to
Energy Resources, Inc. in the amount of $262,000.
FISCAL IMPACT: In partnership with Collier County, the Hideaway Beach Improvement
District through the City of Marco Island is funding the engineering and permitting of this
project. Funds requested for this project are for permitting fees and on site dredging. All
permits will be jointly issued to both the City of Marco Island and Collier County.
The Source of funds is from Category A Tourist Development Tax fund 195
GROWTH MANAGEMENT IMPACT: There is no impact to the Growth Management Plan
related to this action.
CAC September 8, 2011
VIII-1 New Business
2 of 5
ADVISORY COMMITTEE RECOMMENDATION: Conceptual approval of this project
was granted by the CAC on 4/14/2011 by unanimous vote. Unanimous conceptual approval was
also granted by the TDC on 5/27/2011.
Staffis recommending approval of this request.
LEGAL CONSIDERATIONS: The TDC and the BCC should make a finding that this project
and expenditure will promote tourism in Collier County. This item requires majority vote and is
legally sufficient for Board action. - CMG
RECOMMENDATION: Recommendation to award Bid No.1 1-5763 to Energy Resources, lnc
in the amount of $262,000 for the emergency dredging of Collier Bay entrance channel and
authorize the Chairman to execute the standard contract after County Attorney approval.
PREPARED BY: Gary McAlpin, PE - Coastal Zone Management
CAC September 8, 2011
VIII-1New Business
30f5
RESOLUTION NO. 11-05
A RESOLUTION OF THE CITY OF MARCO ISLAND, FLORIDA DECLARING
AN EMERGENCY FOR THE DREDGING OF THE ENTRANCE TO COLLIER
BAY, ALSO KNOWN AS COLLIER CREEK, TO RESTORE SAFE
NA VIGA TION WITHIN THE CHANNEL, IN THE CITY OF MARCO ISLAND,
FLORIDA; AND PROVIDING AN EFFECTIVE DATE.
WHEREAS, the entrance to Collier Bay, also known as .Collier Creek, within the City of
Marco Island, is located in Sections 5, 6 and 7, Township 52 South, Range 26 East, Collier
County, Florida; and
WHEREAS, the City of Marco Island Waterways Advisory Committee, at its meeting of
March 24, 2011, reviewed the current status of the channel entrance and determined that an
emergency situation exists due to the excessive deposition of sand into the previously dredged
area; and
WHEREAS, pursuant to the recommendation of the Waterways Advisory Committee the
Marco Island City Council fmds that the area has experienced severe limitations to safe
navigation and increased scouring velocities along the adjacent waterfront infrastructure, and
agrees that emergency dredging of the channel is necessary; and
WHEREAS, the area of the City's entrance to Collier Bay, also known as Collier Creek,
has experienced severe limitation to safe boating navigation and increased scouring velocities
along the adjacent waterfront infrastructure as a result of significant deposits of sand within the
channel; and
WHEREAS, the City is working jointly with the Collier County Coastal Zone
Management (CZM) department to seek Florida Department of Environmental Protection/Corp
of Engineers (FDEP/COE) permits for emergency dredging of the entrance to Collier Bay.
NOW, THEREFORE, BE IT RESOLVED by the City Council of the City of Marco
Island, Florida, that:
SECTION 1. The emergency dredging of the entrance to Collier Bay is a viable
temporary solution to the erosion; and the City, with support from the CZM, is making an
application to FDEP/COE for an emergency permit approval to dredge the channel as described
above.
SECTION 2. FDEP/COE is requested to expedite pemlitting and approval for the
emergency dredging, as FDEP/COE did for a rock revetment abutting the roadway Royal Marco
Way, and for the CZM to support a request for Tourist Development funds from the Collier
County Board of Commissioners to finance the emergency dredging project.
SECTION 3. The City Council of the City of Marco Island declares an emergency
and directs and authorizes the City Manager or his designee to support and assist the CZM in
1
CAC September 8, 2011
VIII-1 New &JsiAess.
40f5 .
obtaining governmental approvals for the emergency dredging of the entrance to Collier Bay,
also known as Collier Creek.
SECTION 5. EFFECTIVE DATE. This Resolution shall take effect immediately
upon its adoption.
DULY PASSED AND ADOPTED in open and regular session by the City of Marco
Island, Florida, this 4th day of April 2011.
ATTEST
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CAC September 8, 2011
VIII-2 New Business
1 of 2
EXECUTIVE SUMMARY
Recommend Approval of the conceptual design and program approach to the
Marco South Beach Renourishment project.
OBJECTIVE: Recommend approval of the conceptual design and program approach to the
Marco South Beach Renourishment Project.
CONSIDERATIONS: The Southernmost 4,400 LF of Marco Island beach is designated as
Critically Eroded by FDEP. The South Marco Island Beach between RI44 and G-2 has been
renourished in 1990, 1997 and 2006. The worst erosion in this segment is the last 2,000 feet
between RI47 and G2. Unfortunately, this is also the area that has the only public beach access
with adequate parking in south Marco Island.
Tropical Storm Fay severely eroded this beach when it made landfall in August, 2008. Collier
County was successful in obtaining federal disaster assistance to renourish this beach. 77,000
CY's of beach fill was authorized for an estimated total project cost of $2,822,578. FEMA's
portion with a 75% reimbursement will max out at $2,116.933 if additional scope amendments
are not authorized. At Collier County's request, FEMA has extended the expiration date for this
authorization twice. The current expiration date is August 2012.
Coastal Engineering has been awarded a Work Order to develop the conceptual design for this
renourishment program. The program consisted of three components.
I. Beach Renourishment including system modeling to determine the optimum sand
placement quantities to maximize the renourishment cycle. Modeling determined that
104,000 CY's will optimize the fill template to resist future erosion. 77,000 CY's is
authorized under FEMA's disaster order. A new FDEP permit will be required and is
expected to take 5 months to obtain. The existing USACE permit is good till 2021.
However, the existing Biological Opinion does not authorize renourishment during turtle
nesting season. This component of the project is expected to cost $1,800,000.
2. Refurbishment of existing erosion control structures is required. There are three
breakwaters and two groins at the end of Marco Island to control erosion. Little to no
maintenance has occurred over the years and these structures need to be rebuilt to the
original design to perform as intended. This will require authorizations from the FDEP
and USACE to restore the structures to their original design and function. Permitting is
expected to take 6 to 8 months and this work is expected to cost $1,200,000.
3. The addition of an additional Erosion Control Structure is anticipated. When modeled,
an additional Rock Groin located between RI47 and RI48 out performed both a feeder
beach alternative and an additional segmented breakwater alternative in reducing beach
erosion. The model predicts beach width and volume are sustained by 20%-25% over
other options at this critical location. It is anticipated that beach width and volume will
continue to be sustained as the Rock Groin area fills with sand, These findings and
assumptions will be confirmed through additional simulations run over a longer term
"multiple year" cycle, Permitting for this option is expected to approach a year and this
option is expected to cost up to $700,000.
CAC September 8, 2011
VIII-2 New Business
20f2
Recent FEMA funding discussions have made us reconsider our approach to this program. Staff
believes that in the current national political environment, there will be no will to extend the
project authorization any farther or fund mitigation strategies that will reduce emergency
renourishments in the future.
With that said, Staff is recommending the following course of action:
1. Proceed immediately to issue a Work Order to Coastal Engineering Consultants to
proceed with the design and permitting of the beach renourishment portion of this
program. To be successful, the permits must be issued, the construction completed and
the invoicing completed to FEMA by 8/2012. This effort represents a $750,000-
$1,000,000 reimbursement to the County.
2. Continue the conceptual design for the additional erosion control structure between Rl47
and Rl48 to confirm erosion abatement performance over longer term cycle. Confirm
the costs to benefits of this solution. Expected completion is within 6 to 8 weeks. This
will complete the conceptual design phase of this program.
3. Issue an RFP for engineering consultants to perform the design and permitting for
rebuilding the existing structures and possibly the new erosion control structure. Select a
consultant and proceed with the work. A consultant should be selected within the next
60 days.
4. Work with the USACE to determine if the Regional Biological Opinion that was just
issued within the past 90 days supersedes the permit Biological Opinion. This will be
required to perform beach renourishment during next year's turtle nesting season.
5. Obtain approval from the CAC/BCC to perform renourishment during turtle nesting
season.
6. Separately bid and execute the erosion control structure project(s) as permits are
obtained.
7. Obtain concurrence for this plan from the City of Marco Island.
COUNTY ATTORNEY FINDING: This item has been reviewed and approved by the
County Attorney's Office. This item is not quasi-judicial, and as such ex parte disclosure is not
required. This item requires majority vote only. This item is legally sufficient for Board action.
-CMG
ADVISORY COMMITTEE RECOMMENDATIONS: Staffis recommending approval of
this approach.
FISCAL IMPACT: The Source of funds is from Category "A" Tourist Development Tax fund
195.
GROWTH MANAGEMENT IMP ACT: There is no impact to the Growth Management Plan
related to this action.
RECOMMENDATION: Recommend approval of the conceptual design and program
approach to the Marco South Beach Renourishment Program.
PREPARED BY: Gary McAlpin, PE
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CAC September 8, 2011
VIII-3 New Business
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EXECUTIVE SUMMARY
Recommendation to approve and authorize Staff to advertise proposed amendments to the
Tourist Development Tax Ordinance No. 92-60, as amended. Amendments include (1)
delineating the allocation of administrative costs in support of Fund 194 Tourism
Promotion, Fund 195 Beaches, and Fund 183 Beach Park Facilities, (2) incorporating into
the ordinance the Category "A" Funding Policy approved by the Board of County
Commissioners, and directing that the Funding Policy be included in the Collier County
Administrative Code, (3) incorporating provisions of Section 125.0104(5)(A)1, Fla. Stat.,
relating to the use of Category "C" funds for museul)ls, and (4) removing expired
provisions pertaining to the use of certain revenues for tourism destination marketing.
OBJECTIVE: To amend the Tourist Development'faxOrdinanceiiNo. 92-60, as amended.
CONSIDERATIONS: The Coastal Adv'ry Committee (CAC) directed Coastal Zone
Management (CZM) Staff to propose an ame ent to the Tourist Development Tax Ordinance
regarding CZM personnel and administrative costs. Follow' a review of the ordinance, the
County Attorney believes there are additional items Ordinance which the Board may
wish to amend.
The following four amendments are proposed:
(1) The Coastal Advisory Committee dire9ted roPoselliamendments to the Tourist
Development Tax Ordinance to specifically iI1~lude adml strative costs for Fund 195 and Fund
183 and to allocate tH dministrative costs b~tween the two funds based on a pro rata share.
Administrative costs udemaI1.ag~ment. indirect overhead, and program
administration.
There is presently a provision
as follows:
promotion administrative cost. That provision states
"Tourism promotion administrative costs shall not exceed 32% of the total amount collected
each fiscal year for Category B uses and shall be financed solely from the 23.236% of the two
percent tax." The ordinance is silent as to where the remaining 8.764% comes from, which staff
has historically taken from the fourth percent tax, To both clean this up and to simplify the issue,
the County Attorney recommends that the existing language on tourism promotion
administrative costs be deleted, and that the following new subsection to Section Three-Uses of
Tax Revenue, be added to the Ordinance dealing solely with administrative costs:
4. Administrative costs.
a. Tourism promotion administrative costs shall not exceed 32% of the total amount
collected each fiscal year for Category "B" revenue.
CAC September 8, 2011
VIII-3 New Business
2of9
b. Proiect Management, Indirect Overhead, and Program Administration in support
of Fund 195 (Beaches) and Fund 183 (Beach Park Facilities) shall not exceed 15% of
Category "A" revenues. These charges to be split 75% to Fund 195 (Beaches) and 25%
to Fund 183 (Beach Park Facilities).
(2) The second proposed amendment to the ordinance is as follows. Tourist development tax
revenues are utilized in four separate categories. One of these categories, Category "A" (beach
and beach park facilities), has a Board approved Funding Policy. Tourist Development Tax
Ordinance No. 92-60 makes no reference to any such Policy. order to put both the public and
future staff on notice of the existence of such a policy, t nty Attorney recommends the
Board adopt the following reference to the Policy in the or ce:
8.
(3) The third proposed amendment is af~clean-up" item.il(i0ollier County's Tourist Development
Tax Ordinance No. 92-60, as amende~l, autlJ.g~zes the<use of tourist development taxes for
"County owned or operated museums"a.nd "Mllpicipal owne(:lmuseums and museums owned
and operated by not for profit organizatigns operi to the publ The language differs slightly
from the Tourist D~~elOPrnem Tax statute,..~~ctionilt5.0 4(5)(a)l, which authorizes
expenditures for "museums that are publicly own~~.iand oper~t<1d or owned and operated by not-
for-profit organizations a d open tolthe public." The County Attorney and the Clerk of Courts'
Office have had several ssio to whether tHe statute preempts the County Ordinance and
if so whetherthisimpacts arty> e 'ents ofTnC funding. The County Attorney sees no
benefit to the County arising from this r change to the statute, and recommends simply
adoptin e language of the statute into to ordinance, which fully alleviates the concerns that
have be raised. Accordingly, thec;ounty Attorney recommends amending the definition of
Category "(C" to adopt the statutory language and proposes to amend Section Three - Uses of
Tax Revenue - Category C, as follows:
CATEGORY C -
To acquil'~,Construct, extend, enlarge, remodel, repair, improve, maintain,
op\eJ,'ategJ,'promote one or more County owned eF and operated museums
er-anciimunicipal owned museums or museums that are publicly owned
and operated or owned and operated by not-for-profit organizations and
open to the public, within the boundaries of the county or subcounty
special taxing district in which the tax is levied. Tax revenues received
pursuant to this Section may also be used for promotion of zoological
parks that are publicly owned and operated or owned and operated by not-
for-profit organizations and open to the public. However, these purposes
may be implemented through service contracts and leases with lessees
with sufficient expertise or financial capability to operate such facilities.
CAC September 8, 2011
VIII-3 New Business
3of9
The definition for C-l would be amended as follows:
County owned eF and operated museums, or museums owned by not-for-profit
organizations and open to the public operated by the County through Board approved service
contracts and leases: 22%
The definition for C-2 would be amended as follows:
MURieipal owned lffilseums and Mblseums owned ood operated by not f-or profit
organizations open to the Pblblio All other qualified museums: 4;764%
This change to the ordinance will not affect any currenlTunding.
(4) Lastly, Sections 7 and 8, regarding additionali'lfurtds for destinatiop advertising have expired
and as such, the County Attorney's Office recommends removin ese sections from the
Ordinance. Each section was valid for one year following date of a ion on November 10,
2009.
FISCAL IMP ACT: The cost to advertise th
approximately $500 which funds are ayaila1:>l~:from Fun
posed Ordinance Amendment IS
95 and 194,
GROWTH MANAGEMENT IMPACT: There is no impactOI1ithe Growth Management Plan
from this action.
ADVISORY BOARDliIRECOMNIENDATIONS: Staff is recommending approval of these
changes to both the CoasfalAdvis Committee and the Tourist Development Council (TDC),
LEGAL e(!i)NSIDERATIONS:. .... iterrrhas been.ireviewed by the County Attorney, requires
super majority vote, andisJegallysufficient for Board action. - JAK
RECOMMENDATION: T(rapproveane authorize Staff to advertise proposed amendments to
the Tourist Development Tax. Ordinance No. 92-60, as amended, amendments include (1)
delineating the allocation of adrninistrative costs in support of Fund 194 Tourism Promotion,
Fund 195 Beaches, and Fund l$ipiBeach Park Facilities, (2) incorporating into the ordinance the
Category "A" Funding Policy approved by the Board of County Commissioners, and directing
that the Funding Policy beiinclUded in the Collier County Administrative Code, (3) incorporating
provisions of Section 125.0104(5)(A)I, Fla. Stat., relating to the use of Category "C" funds for
museums, and (4) removing expired provisions pertaining to the use of certain revenues for
tourism destination marketing.
SUBMITTED BY: Gary McAlpin, Coastal Zone Management Director
Jack Wert, Tourism Director
Jeffrey A. Klatzkow, County Attorney
Colleen Greene, Assistant County Attorney
CAC September 8, 2011
VIII-3 New Business
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ORDINANCE NO. 2011 -
AN ORDINANCE OF THE BOARD OF COUNTY COMMISSIONERS OF
COLLIER COUNTY, FLORIDA, AMENDING ORDINANCE NO. 92-60, AS
AMENDED, RELATING TO THE LEVY OF A 2% TOURIST
DEVELOPMENT TAX, AN ADDITIONAL 1 % TAX (3RD PERCENT), AND
AN ADDITIONAL 1% TAX (4TH PERCENT) THROUGHOUT COLLIER
COUNTY PURSUANT TO THE LOCAL OPTION TOURIST
DEVELOPMENT ACT, SECTION 125.0104, FLORIDA STATUTES, AS
AMENDED; SPECIFICALLY AMENDING SECTION THREE, USES OF
TAXES, CODIFIED IN SECTION 126-83 OF THE CODE OF LAWS AND
ORDINANCES, BY 1) INCORPORATING PROVISIONS OF SECTION
125.0104 (5)(A)1, FLORIDA STATUTES, RELATING TO THE USE OF
CATEGORY "C" FUNDS FOR MUSEUMS; 2) DELINEATING THE
ALLOCATION OF ADMINISTRATIVE COSTS FOR TOURISM
PROMOTION AND BEACH PARK FACILITIES AND BEACH
IMPROVEMENTS; 3) REMOVING EXPIRED PROVISIONS
PERTAINING THE USE OF CERTAIN REVENUES FOR TOURISM
DESTINATION MARKETING; AND 4) INCORPORATING BY
REFERENCE THE CATEGORY "A" FUNDING POLICY APPROVED BY
THE BOARD OF COUNTY COMMISSIONERS; PROVIDING FOR
CONFLICT AND SEVERABILITY; PROVIDING FOR INCLUSION IN
THE CODE OF LAWS AND ORDINANCES; AND PROVIDING FOR AN
EFFECTIVE DATE.
WHEREAS, Section 125.0104, Florida Statutes, provides for the levy of a local option
tourist development tax by any county; and
WHEREAS, on August 18, 1992, the Board of County Commissioners (Board) adopted
Ordinance No. 92-60, which levied and imposed a 2% tourist development tax throughout Collier
County for the purposes permitted in Section 125.0104, Florida Statutes, as amended; and
WHEREAS, through adoption of Ordinance No. 95-56 and Ordinance No. 2005-43, the
Board leyied an additional 3rd and 4th percent tourist deyelopment tax; and
WHEREAS, on November 10, 2009, the Board adopted Ordinance No. 2009-58 which for
a period of one year, or until November 10, 2010, reallocated certain tourist development tax
revenues for use in tourism destination marketing; and
WHEREAS, the Board, by an extraordinary vote, desires to amend Section Three of
Ordinance No. 92-60, as amended, in order to: 1) incorporate provisions of Section 125,0104
(5)(a)l, Florida Statutes, relating to the use of Category "C" funds for museums; 2) delineate the
allocation of administrative costs for tourism promotion and beach park facilities and beach
improvements; 3) remove expired provisions pertaining to the use of revenues for tourism
Words Underlined are added; Words Struek ThrElugh are deleted.
Page I of6
CAC September 8, 2011
VIII-3 New Business
5of9
destination marketing; and 4) incorporate by reference the Category "A" Funding Policy as
approved by the Board of County Commissioners ; and
WHEREAS, the proposed amendments were presented to and approved by the Collier
County Tourist Development Council.
NOW, THEREFORE, BE IT ORDAINED BY THE BOARD OF COUNTY
COMMISSIONERS OF COLLIER COUNTY, FLORIDA, that:
SECTION ONE: AMENDMENT TO SECTION THREE OF ORDINANCE NO. 92-60, AS
AMENDED.
Section Three - Uses of Tax Revenues.
a) The tax revenues received pursuant to this division shall be used to fund the County Tourist
Development Plan, which is hereby amended as follows:
**************
(1) The categories of use of the two percent and one percent (3rd percent) and additional
one percent (4th percent) tax revenues by specific project or special use are hereby listed in
the order of priority:
CATEGORY A
To finance beach park facilities or beach improvement, maintenance,
renourishment, restoration and erosion control, including pass and inlet
maintenance, shoreline protection, enhancement, cleanup or restoration of
inland lakes and rivers to which there is public access as these uses relate to
the physical preservation of the beach, shoreline or inland lake or river.
Percentage of
Net revenue
50% of the 2% tax and 100% of the 1% tax (3rd
percent), reduced by the amount required for
Category D.
CATEGORY B
To promote and advertise county tourism within the State of Florida,
nationally and internationally, which encourages tourism with an emphasis
on off-season visitors to Collier County and to fund convention bureaus,
tourist bureaus, tourist information centers and news bureaus as county
agencies. If tax revenues are expended for an activity, service, venue or
event, the activity, service, venue or event shall have as one of its main
purposes the attraction of tourists as evidenced by the promotion of the
activity, service, venue or event to tourists.
Words Underlined are added; Words Struelc Through are deleted.
Page 2 of6
CATEGORYC-
CATEGORY D -
CAC September 8, 2011
VIII-3 New Business
6of9
Percentage of
Net revenue
23.236% of the 2% tax and 100% of the additional
1 % tax (4th percent).
To acquire, construct, extend, enlarge, remodel, repair, improve, maintain,
operate or promote one or more County owned eF and operated museums eF
and munioipal owned museums or museums that are publicly owned and
operated or owned and operated by not-for-profit organizations and open to
the public, within the boundaries of the county or subcounty special taxing
district in which the tax is levied. Tax revenues received pursuant to this
Section may also be used for promotion of zoological parks that are publicly
owned and operated or owned and operated by not-for-profit organizations
and open to the public. However, these purposes may be implemented
through service contracts and leases with lessees with sufficient expertise or
financial capability to operate such facilities.
Percentage of
Net revenue
26.764% of the 2% tax. This amount may be
amended upwardly or downwardly prospectively
from the date of the budget amendment approval,
provided that the amount of the aggregate allocation
per fiscal year budget amendment does not exceed
26.764% of the 2% tax,
Sub-categories:
C(I):
County owned eF and operated Museums, or
museums owned by not-for-profit organizations and
open to the public operated by the County through
Board approved service contracts and leases: 22%
C(2):
Muni0ipal owned museums and Mblseums oVflled and
operated by not for profit organizations open to the
f*lblie All other qualified museums: 4.764%
To acquire, construct, extend, enlarge, remodel, repair, improve, maintain,
operate or promote one or more fishing piers which are publicly owned and
operated.
Words Underlined are added; Words Struck Through are deleted.
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Percentage of
Net revenue
Amount budgeted for this Category by the Board of
County Commissioners each fiscal year, but not to
exceed $200,000. This amount may be amended
upwardly or downwardly prospectively from the date
of the budget amendment approval, provided that the
amount of the aggregate allocation per fiscal year
does not exceed $200,000.
It is the intent of this division that the above uses shall be funded separately, but simultaneously in
the above percentages regardless of the actual amount of net revenues collected.
**************
(3) The additional one percent tax (4th percent) collected pursuant to section TWO (G)
shall be used entirely to finance tourism promotion including advertising, public relations,
promotion, research and fulfillment. Tourism promotion administrative costs shall not
eJweed 32 % of the total amount oolleoted eaoh fisoal yea:r for Category B uses and shall be
finanoed solely from the 23.236%, portion of the 2~( tax. The Disaster Recover Advertising
Fund will continue to be financed from the 23.236% of the 2% tax to maintain a maximum
level of $1 million, At the end of each fiscal year, any remaining funds in the 23.236% of
the 2% tax after fulfillment of the above uses in the 23,236% of the 2% tax will be
distributed to Category "B" (Marketing and Promotion). It is the intent of the Board of
County Commissioners to maintain this new level of tourism promotion dollars in the
future.
4. Administrative costs.
a, Tourism promotion administrative costs shall not exceed 32% of the total amount
collected each fiscal year for Category "B" revenue,
b. Proiect Management Indirect Overhead, and Program Administration in support of
Fund 195 (Beaches) and Fund 183 (Beach Park Facilities) shall not exceed 15% of
Category "A" revenues. These charges to be split 75% to Fund 195 (Beaches) and 25% to
Fund 183 (Beach Park Facilities).
4,. .i. The revenues to be derived from the tourist development tax may be pledged to
secure and liquidate revenue bonds in accordance with the provisions of Section 125,0104,
Florida Statutes. Such revenue bonds and revenue refunding bonds may be authorized and
issued in such principal amounts, with such interest rates and maturity dates, and subject to
such other terms, conditions and covenants as the governing board of Collier County shall
provide. This paragraph shall be full and complete authority for accomplishing such
purposes, but such authority shall be supplemental and additional to, and not in derogation
of, any powers now existing or later conferred under law.
Words Underlined are added; Words Struolc Through are deleted.
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~ 6. The event bonds are issued by Collier County for any of the purposes enumerated
by the Tourist Development Plan, the amount of tourist development tax receipts used to
pay debt service on such bonds may exceed the percentages provided for the purpose for
which such bonds were issued; provided, however, the maximum annual debt service on
such bonds, together with any other obligations of Collier County which were issued to
finance improvements for the same purpose and which are secured by the tourist
development tax, must not exceed the stated percentage of tourist development tax receipts
provided in the Tourist Development Plan for such purposes, as calculated as of the date of
sale of such bonds. For purposes of performing the calculations described in this
paragraph, the amount of tourist development tax receipts shall be assumed to be the
amount provided as such in Collier County's immediately preceding annual audit, plus, if
the levy of such tax was imposed or increased subsequent to the beginning of the period
which was audited, an amount equal to the estimate by the County Manager of the moneys
the County would have received if the tax imposition or increase had been in effect during
the entire audit period. At or prior to the issuance of bonds the County Manager shall
provide a certificate as to the findings required in this paragraph, which certificate shall be
conclusive as to all matters provided herein.
&.- L The sum of $1 ,000,000 annually allocated for Category "A" - Beach Park Facilities
Fund 183 shall be reallocated to Fund 184 to be used for destination marketing for a period
of one year from enactment of this amendment, at which time this provision will expire and
be of no further force or effect unless further extended by the Board of County
Commissioners,
7. The sum of $500,000 annually allooated for Catastrophe Reserves from County
Fund 195 shall be reallocated to Fund 181 to be used for destination marketing for a period
of one year from enactment of this amendment, at vihioh time this provision 'Nill expire and
be of no further force or effeot unless further extended by the Board.
8. Five hundred thousand dollars ($500,000) of the Two million dollars ($2,000,000)
that is annually allooated for Major Beaeh Renourishment Reserves from County Fbll'l.d 195
shall be reallooated to Fund 1 g 1 to be blsed for destination marketing for a period of one
year from enactment of this amendment, at whioh time this provision '.",ill expire and be of
no further foroe or effect unless further extended by the Board.
8. The currently existing Category "A" Funding Policv, as approved by the Board of
County Commissioners, is incorporated and referenced herein. This Category "A" Funding
Policy shall be included within the Collier County Administrative Code, and may only be
amended by the Board of County Commissioners.
9. The above and foregoing Tourist Development Plan may not be substantially
amended except by ordinance enacted by an affirmative vote of a majority plus one
additional member of the Board of County Commissioners.
Words Underlined are added; Words Struek Through are deleted.
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SECTION TWO: CONFLICT AND SEVERABILITY.
In the event this Ordinance conflicts with any other ordinance of Collier County or other
applicable law, the more restrictive shall apply. If any phrase or portion of the Ordinance is held
invalid or unconstitutional by any court of competent jurisdiction, such portion shall be deemed a
separate, distinct and independent provision and such holding shall not affect the validity of the
remaining portion.
SECTION THREE: INCLUSION IN THE CODE OF LAWS AND ORDINANCES.
The provisions of this Ordinance shall become and be made a part of the Code of Laws and
Ordinances of Collier County, Florida, The sections of the Ordinances may be renumbered or
relettered to accomplish such, and the word "ordinance" may be changed to "section," "article," or
any other appropriate word.
SECTION FOUR: EFFECTIVE DATE.
This Ordinance shall be effective upon filing with the Department of State.
PASSED AND DULY ADOPTED by a vote of a majority plus one of the Board of County
Commissioners of Collier County, Florida, this _day of
, 2011.
ATTEST:
DWIGHT E. BROCK, CLERK
BOARD OF COUNTY COMMISSIONERS
COLLIER COUNTY, FLORIDA
By:
, Deputy Clerk
By:
FRED W. COYLE, CHAIRMAN
Approved as to form
and legal sufficiency:
Colleen M. Greene
Assistant County Attorney
Words Underlined are added; Words Struck ThrougH are deleted.
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EXECUTIVE SUMMARY
Obtain a recommendation of approval from the Coastal Advisory Committee to
solicit an RFP for Engineering Consultants as required to provide:
1. Design Engineering and Permitting for the renourishment of the Barefoot,
Vanderbilt, Clam Pass, Park Shore and Naples beaches, and
2. Design Engineering and Permitting for the Marco Island South beach.
OBJECTIVE: Obtain a recommendation of approval from the Coastal Advisory
Committee to Solicit an RFP for two coastal projects for Collier County. The two
projects are:
1. Design Engineering and Permitting for the renourishment of the Barefoot,
Vanderbilt, Clam Pass, Park Shore and Naples beaches.
2. Design Engineering and Permitting for the Marco Island South beach.
CONSIDERATIONS: An RFP solicitation for engineering services is now required for
any capital project that will result in a construction contract of $2M or greater.
Both the Marco South Renourishment and the Renourishment project for the Barefoot,
Vanderbilt, Clam Pass, Park Shore and Naples beaches will result in large construction
contracts and an RFP solicitation is required.
The basis for this solicitation is attached but generally covers detailed Design
Engineering and permitting.
Conceptual scope definition is currently being performed by Coastal Engineering for the
Marco South project and Coastal Planning and Engineering for the main Collier County
beach renourishment project.
It is anticipated that two separate engineering firms will be awarded contracts from this
one RFP solicitation.
ADVISORY COMMITTEE RECOMMENDATIONS: Staff is recommending approval of
this item.
FISCAL IMPACT: The Source of funds is from Category "A" Tourist Development Tax
fund 195.
GROWTH MANAGEMENT IMPACT: There is no impact to the Growth Management
Plan related to this action.
LEGAL CONSIDERATIONS: This item has been reviewed and approved by the
County Attorney's Office. This item is not quasi-judicial, and as such ex parte disclosure
is not required. This item requires majority vote only. This item is legally sufficient for
Board action. - CMG
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RECOMMENDATION: Obtain a recommendation of approval from the Coastal
Advisory Committee to solicit an RFP for Engineering Consultants as required to
provide Design Engineering and Permitting for the renourishment of the Barefoot,
Vanderbilt, Clam Pass, Park Shore and Naples beaches, and Design Engineering and
Permitting for the Marco Island South beach.
PREPARED BY: Gary McAlpin, PE
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8/15/2011
Solicitation is an RFP for two coastal projects for Collier County. The two projects are:
1. Design Engineering and Permitting for the renourishment of the Barefoot, Vanderbilt, Clam Pass,
Park Shore and Naples beaches.
2. Design Engineering and Permitting for the Marco Island South beach.
Specifics of these projects are as follows:
Renourishment of the Barefoot. Vanderbilt. Clam Pass. Park Shore and Naples beaches
Coastal Planning and Engineering has completed the conceptual design for the Barefoot, Vanderbilt,
Clam Pass, Park Shore and Naples beaches. A draft ofthe conceptual design report is attached.
Construction of this project is expected to begin 11/1/2013 and be completed by 5/1/2014. This project
is expected to be coordinated and bid with the Captiva Erosion Control District project that is being
developed in conjunction with this project.
A construction budget of $25M has been established for this project. However scope adjustments will
be most likely be required as state and federal funding sources are resolved.
This RFP will select a consultant that will complete the execution of this project consistent with the
conceptual design to include but not limited to:
1. Pre-application meeting with FDEP
2. Pre-construction survey to include beach, side scan and environmental aerials
3, Pre-construction biological reef and hardbottom monitoring and report
4, Hardbottom mapping and ground truthing
5, Pipeline corridor mapping
. Three new routes (environmental clearing)
· Operational Areas for Booster Pumps - possibility ofthree new locations
. New Hardbottom Clearing for Barefoot Beach
6. Special design Survey for structures, Eel and 3D design
. Design survey R8 to R85
. Survey and process ECl (Barefoot and Clam Pass Park)
. Survey new structural foundation areas for erosion control structures
. Survey intermediate lines for 3D design around hardbottom
. Borrow area survey
7. 3D Design/Plans Update (area around hardbottom) and new reaches
. Clam Pass Park and Barefoot Beach
. Address Hot Spots and hardbottom avoidance with intermediate lines
. Permit sketches
8. Engineer and design structural modifications or additions
9. Specifications
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10. Prepare MMS Environmental assessment
11. Prepare and submit permit modifications to 2005 permit and permit sketches
. Environmental Sections changes as a result of learning's since 2005
. Geological sections (with OA/QC Plan) learning's since 2005
. Engineering sections justifications for varying width and height requirements
. Year-round renourishment condition inclusion into the permit
. Agency visits
. Others
12, RAI cycle and meetings
13. Update Biological and physical monitoring plans
14. UMAM assessment of hardbottom coverage
15, Essential Fish Habitat report
16, Biological assessment
17. Bid documents and bidding support
18. Permit modification to the Doctors Pass dredging permit to change the disposal site for beach
sand placement to R57 to R59.
19. Coordination with Captiva Erosion Control District.
20, Construction contract inspection and monitoring (1 day per week)
21. Construction contract volume adjustment by segment and reach.
22, Attendance at weekly coordination meetings
23. Pipeline corridor monitoring during construction
24, Post-construction surveys
25, Record drawings and certification report
26. Agency coordination to include but not limited to National Marine Fisheries, FWS and FWC.
27. County and contractor coordination
28. USACE permit modification and coordination in conjunction with the FDEP permit modification,
A detailed design schedule based on activities outlined above is expected as part of the submittal
package.
Collier County has expended considerable resources in the development of a conceptual design that
balances needs for more robust and longer lasting renourishments with available resources. Consultant
will need to document success in the completion of engineering and permitting activities from a third
party conceptual design.
Examples of successful project implementation along with key project personnel proposed will be critical
to the selection of this consultant.
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Renourishment of the Marco Island South beach.
Coastal Engineering Consultants has completed the conceptual design for the Marco Island South Beach
project. A preliminary copy of the conceptual design report is attached. Renourishment of the beach is
expected to begin 11/1/2012 and be completed by 5/1/2013. Rebuilding ofthe three existing
breakwaters along with the two existing T-Groins can follow the renourishment if permits for this
activity are not obtained in time for concurrent construction. If additional structures are recommended,
a schedule for permitting and construction will need to be established independently.
Renourishment of approximately 104,000 Cy's of beach compatible sand to restore approximately 4,400
feet of beach is anticipated. Rebuilding the five erosion control structures is also included in the scope of
this project. Scope adjustments will be most likely be required as state and federal funding sources are
resolved.
This RFP will select a consultant that will complete the execution of this project consistent with the
conceptual design to include but not limited to:
1. Pre-application meeting with FDEP
2, Pre-construction beach and structure survey including site aerials
3. Special design Survey for structures, ECl and 3D design
. Design survey R144 to G2
. Survey and process ECl if required
· Survey new structural foundation areas for erosion control structures if recommended
in the project scope.
. Borrow area survey
4. Engineer and design structural modifications or additions
5, Specifications
6. Prepare and submit permit application and permit sketches
. Year-round renourishment condition inclusion into the permit
. Agency visits, if required
. RAI cycle and meetings
7. Update to biological monitoring; sediment OA/QC plan and the physical monitoring plan
8. Essential Fish Habitat report
9. Biological assessment
10. Bid documents and bidding support
11. Construction contract inspection and monitoring (1 day per week)
12, Attendance at weekly coordination meetings
13. Post-construction surveys
14. Record drawings and certification report
15. Agency coordination to include but not limited to National Marine Fisheries, FWS and FWC.
16. Coordination with City of Marco Island and Marco Island Beach Committee
17. County and contractor coordination
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18. USACE permit modification and coordination in conjunction with new FDEP permit.
A detailed design schedule based on activities outlined above is expected as part of the submittal
package.
Collier County has expended considerable resources in the development of a conceptual design that
balances needs for more robust and longer lasting renourishments with available resources. Consultant
will need to document success in the completion of engineering and permitting activities from a third
party conceptual design,
Examples of successful project implementation along with key project personnel proposed will be critical
to the selection of this consultant.
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EXECUTIVE SUMMARY
Recommendation to award a $126,000 Work Order to Coastal Engineering Consultants for
the design and permitting required to obtaining a FDEP permit for the 2012 Marco South
Beach renourishment project along with modifications to the existing USACE permit.
OBJECTIVE: To award a $126,000 Work Order to Coastal Engineering Consultants for the
design and permitting required to obtaining a FDEP permit for the 2012 Marco South Beach
renourishment project along with modifications to the existing USACE permit.
CONSIDERATION: Collier County will renourish the Marco South Beach by placing 104,000
CY's of beach compatible sand dredged out ofCaxambas Pass on the southernmost 4,400 LF of
beach, The Southernmost 4,400 LF of Marco Island beach is designated as Critically Eroded by
FDEP. The South Marco beach between R144 and G-2 has been renourished in 1990, 1997 and
2006. The worst erosion in this segment is the last 2,000 feet between R147 and G2.
Tropical Storm Fay severely eroded this beach when it made landfall in August 2008. Collier
County was successful in obtaining federal disaster assistance to renourish this beach. 77,000
CY's of beach fill was authorized for an estimated total project cost of $2,822,578. FEMA's
portion with a 75% reimbursement will max out at $2,116.933 if additional scope amendments
are not authorized.
At Collier County's request, FEMA has extended the expiration date for this authorization twice.
The current expiration date is August 2012. Staff believes that in the current national political
environment, there will be no will to extend the project authorization any farther or fund
mitigation strategies that will reduce emergency renourishments in the future,
With that said Staff is recommending that we proceed immediately to issue a Work Order to
Coastal Engineering Consultants for the project design and permitting to FDEP and provide
modifications to the existing USACE permit as necessary to support an August 2012 completion
date.
Time is of the essence and the permit application is the critical path to completing this project by
August 2012. To be successful, the permits must be issued, the construction completed and the
invoicing completed to FEMA by August 2012. This effort represents a $750,000-$1,000,000
reimbursement to the County.
A copy of their proposal is attached,
FISCAL IMPACT: $126,000 is estimated to perform these activities, The Source of funds is
from Category A Tourist Development Tax fund 195,
GROWTH MANAGEMENT IMPACT: There is no impact to the Growth Management Plan
related to this action.
ADVISORY COMMITTEE RECOMMENDATION: Staff is recommending approval of this
request.
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LEGAL CONSIDERATIONS: The TDC and the BCC should make a finding that this project
and expenditure will promote tourism in Collier County. This item requires majority vote and is
legally sufficient for Board action. - CMG
RECOMMENDATION: Recommendation to award a $126,000 Work Order to Coastal
Engineering Consultants for the design and permitting required to obtaining a FDEP permit for
the 2012 Marco South Beach renourishment project along with modifications to the existing
USACE permit.
PREPARED BY: Gary McAlpin, PE - Coastal Zone Management
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Collier County
South Marco Beach Renourishment
CEC Contract No. 09-5262
Design and Permit Processing Scope of Work
SCHEDULE "A"
WORK ORDER NO.2
Collier County proposes to place approximately 104,000 cubic yards of beach compatible
sediment excavated from the Caxambas Pass borrow area to restore approximately 4,400 feet
along South Marco Island. The proposed beach fill falls within the 2006 project limits, as
previously permitted by JCP0235209-001-JC (FDEP) and SAJ-2005-2726 (IP-MN) (USACE),
The FDEP Permit expired in 2010, thus new state approvals are necessary for the Project. The
USACE Permit expires in 2021; however a modification is necessary to authorize construction
during sea turtle nesting season,
The County proposes the Project for the primary purposes of restoring storm protection, natural
resource habitats, and recreational beach areas to offset the storm damage caused by Tropical
Storm Fay in 2008. Post-storm surveys and analyses documented approximately 77,000 cubic
yards eroded within the permitted fill template. The County is seeking federal reimbursement as
defined in FEMA Project Worksheet, Declaration No. 1785DRFL.
This scope of services defines Final Design and Permit Processing related services associated
with the beach fill placement only. No design or permitting of structural repairs or new structures
is included in the services at this time.
TASK 2: USACE PERMIT MODIFICATION LETTER
Based upon the Statewide Programmatic Biological Opinion for Beach Placement in Florida
(SPBO), CEC will prepare for County review and approval, a letter report rendering a
professional opinion specific to how the Project qualifies for the SPBO. CEC shall incorporate
County review comments and submit the letter report to the USACE along with a complete copy
of the JCP Application (prepared under a prior work order). Within the submittal, CEC shall
request the USACE expedite both coordination with the USFWS to deem the Project eligible for
construction during sea turtle nesting season and issuance of a permit modification to adopt the
SPBO into the federal authorization.
TASK 3: PERMIT PROCESSING
Subsequent to submittal of the permit application, CEC will serve as the County's agent for the
permit process. CEC will pro actively engage FDEP and USACE staff to informally monitor the
process, address staff questions, and facilitate agency consideration of the application. CEC will
compile, clarify, and provide existing information as may be requested by FDEP and USACE
staff. CEC will seek to negotiate permit conditions for the project that are acceptable to the
County.
For the purposes of this scope, it is expected that FDEP and USACE will make one (1) request
for additional information (RAI) each, and that one (1) meeting will be required with FDEP staff
in Tallahassee to favorably conclude the permit application. It is assumed that existing
information (including design details/analysis) will be sufficient to meet permit application
requirements with minor adjustments, clarifications, or analysis. If FDEP mandates additional
surveys, geotechnical data, modeling analyses, or studies beyond those identified herein, CEC
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Collier County
South Marco Beach Renourishment
CEC Contract No. 09-5262
Design and Permit Processing Scope of Work
will undertake these additional tasks under separate authorization as may subsequently be
approved by the County.
TASK 4: FINAL DESIGN
Based on the permit processing results including comments received from the agencies, accepted
preliminary design documents, and the 2011-12 annual monitoring surveys (beach profiles, inlet,
shoals, etc. to be performed by the County's other consultants), CEC will prepare for review and
approval by the County, construction plans and technical specifications to show the general
scope, character and extent of the work to be furnished and performed by the contractor. CEC
shall design the final beach fill and borrow area including horizontal and vertical control, survey
baseline, construction access and staging area, beach fill limits, design fill templates, pipeline
corridors, borrow area limits, dredge templates, mixing zones, and construction quantities.
TASK 5: BID AND CONTRACT PROCUREMENT PROCESS
CEC shall prepare a Final Opinion of Probable Construction Cost. CEC shall prepare
supplemental conditions and bid schedule forms for inclusion in the Bid Documents. CEC shall
assist the County in coordinating a one-time bid process. These services will include attending
one meeting as requested by the County, e.g., pre-bid meeting; assisting the County issue
addenda as appropriate to interpret, clarify or expand the Bid Documents; assisting the County in
obtaining bids from dredging contractors; assisting the County in evaluating the bids; and
making a recommendation for award to the lowest responsive bidder. CEC provide technical
support to the County during the construction contract procurement process, request and obtain
permit required items from the contractor, and coordinate the Notice to Proceed from the FDEP.
TASK 6: PROJECT ADMINISTRATION & CLIENT COORDINATION
This task includes coordination with the County including routine meetings (5 budgeted);
stakeholder meetings (2 budgeted); routine email updates to the County; and written or phone
correspondence in reference to the Project beyond the scope of tasks described above.
TASK 7: CONTINGENCIES
Due to the complex nature of the work involving marine environments, it is anticipated that
additional work may be necessary such as field work, stakeholders meetings, or agency
coordination. A contingency budget is recommended for these circumstances.
ASSUMPTIONS
The scope and budget estimates for the Project are based on the following assumptions.
I. Annual Monitoring Surveys
The County shall provide the following survey/monitoring deliverables for use by CEC in the
Project design by March 1, 2012 in order to provide sufficient time for preparation of the
construction plans required by FDEP as a condition of Notice to Proceed:
· controlled (scale rectified) digital photography,
· current beach profile, borrow area, inlet, and shoal survey data as xyz files in Excel or similar
file format, and
· survey certification and monitoring report.
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Collier County
South Marco Beach Renourishment
CEC Contract No. 09-5262
Design and Permit Processing Scope of Work
No beach, inlet and shoal, or borrow area bathymetric survey data collection is included in the
scope.
II. Borrow Area
The borrow area shall be the previously permitted Caxambas Pass Borrow Area. In recognition
of the three prior successful projects (1990-91, 1997 and 2006), and due to the time constraints,
it is assumed that no geotechnical testing, i.e. vibracoring, will be required, thus none is proposed
in this scope. The borrow area design shall include the magnetic anomaly buffer area previously
identified and incorporated into the 2006 project, thus no magnetometer survey is proposed in
the design phase. If deemed necessary during the design phase, in recognition of the time
constraint, this survey could be conducted as a pre-construction requirement. Because the County
has previously permitted this borrow area and utilized it successfully for a sand source, it is
assumed that wave refraction analyses to verify that no adverse impacts to adjacent shorelines
will occur from borrow area excavation will not be required thus none are proposed in this scope.
III. Beach Fill
Because this is the next maintenance cycle of the existing permitted Project, CEC bases this
scope on the following assumptions:
· The Project has an established Erosion Control Line for the entire shoreline to be
renourished, and
· The County has its own property or has obtained construction easements from private upland
property owners for construction access and staging and to allow for placement and
maintenance of beach fill and coastal structures upland of the ECL.
IV. Statewide Programmatic Biological Opinion
The federal authorization permit modification process scope and budget are based on the
assumption that the Project qualifies under the SPBO and that Project will be eligible for
construction during sea turtle nesting season.
v. Miscellaneous
A. The County shall provide the following:
· Funding related tasks (FEMA coordination, public access requirements, etc.),
· Agency related permit processing fees,
· Construction Access / Staging area agreements if required,
· Local approval by the Board of County Commissioners and Marco Island City Council
for construction during sea turtle nesting season, and
· Public Noticing requirements for permit issuance.
B. Construction Services shall be provided under subsequent work order(s).
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Collier County
South Marco Beach Renourishment
CEC Contract No. 09-5262
Design and Permit Processing Scope of Work
BUDGET
TASK DESCRIPTION TIME AND MATERIALS
2 USACE Permit Modification Letter $ 7,000
3 Permit Processing $ 62,000
4 Final Design $ 19,000
5 Bid and Contract Procurement Process $ 8,000
6 Proiect Administration $ 10,000
7 Contingencies $ 20,000
Total $126,000
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EXECUTIVE SUMMARY
Recommendation to award an $18,650 Work Order to Coastal Engineering Consultants for
construction support and project certification for the Collier Bay dredging project.
OBJECTIVE: To award an $18,650 Work Order to Coastal Engineering Consultants for
construction support and project certification for the Collier Bay dredging project.
CONSIDERATION: Construction administration, observation and monitoring on this project
will be performed by Collier County's Coastal Zone Management staff.
However, certain activities are required by FDEP permit to be performed by the Engineer of
Record. Substantial completion verification, final inspection verification, final certification to
FDEP and the monitoring report will need to be performed by Coastal Engineering Consultants
A copy of their proposal is attached.
FISCAL IMPACT: $18,650 is estimated to perform these activities. The Source of funds is
from Category A Tourist Development Tax fund 195.
GROWTH MANAGEMENT IMPACT: There is no impact to the Growth Management Plan
related to this action.
ADVISORY COMMITTEE RECOMMENDATION: Conceptual approval of this project
was granted by the CAC on 4/14/2011 by unanimous vote. Unanimous conceptual approval was
also granted by the TDC on 5/27/2011.
Staff is recommending approval of this request.
LEGAL CONSIDERATIONS: The TDC and the BCC should make a finding that this project
and expenditure will promote tourism in Collier County. This item requires majority vote and is
legally sufficient for Board action. - CMG
RECOMMENDATION: Recommendation to award an $18,650 Work Order to Coastal
Engineering Consultants for construction support and project certification for the Collier Bay
dredging project.
PREPARED BY: Gary McAlpin, PE - Coastal Zone Management
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Collier County
Collier Bay Dredging Construction Administration
CEC Contract No. 09-5262
Scope of Work
SCHEDULE "A"
WORK ORDER NO.1
Collier County is proceeding with an emergency dredge project of the entrance channel to
Collier Bay. The project includes excavating approximately 10,000 cubic yards of beach
compatible sand from tHe previously permitted borrow area and placing the sand along the
previously permitted beach fill on Hideaway Beach. The primary purpose of the project is to
restore safe navigation by removing the shoal that has created hazardous conditions for the
boating community. CEC proposes the following scope of work to assist the Coastal Zone
Management Department (CZM) administer the Contractor's construction contract.
TASK 1
CONSTRUCTION ADMINISTRATION
A. Contractor Pre-Construction Conference
Attend one pre-construction conference with the County and Contractor covering contract
obligations, construction plans, general and special conditions, and technical specifications.
Record and distribute the minutes of the meeting.
B. Agency Pre-Construction Meeting
Arrange, prepare for, and attend one agency required pre-construction meeting with the County,
Contractor, DEP, FWC and permitted sea turtle monitor to review construction schedule and
methods and explain or clarify the sea turtle protection measures.
C. Work Plan and Submittal Forms
Review the Contractor's work plan and submittal forms (e.g. turbidity, daily qa-qc) to determine
compliance with the plans and specifications. Upon completion of the review, submit to the
County in writing recommended changes or a written approval of the Contractor's work plan,
and submittal forms. Review one round of work plan revisions from the Contractor.
D. Construction Progress Meetings
Attend construction progress meetings with the County and Contractor on average once every
two weeks covering work progress and schedule, conformance to plans and specifications, and
other relevant issues that need to be addressed. Record and distribute the minutes of each
meeting. The budget includes senior engineer representation at up to five (5) on-site construction
progress meetings and site observations.
E. Pay Applications
Review invoices for payment submitted by the Contractor along with daily records of the
County, Contractor and Engineer and surveys provided by the Contractor, and determine the
amounts of progress payments due based on completion of work as requested by the County.
Upon completion of review, submit recommendations to County for payment of invoices to the
Contractor. The budget includes up to three (3) reviews. Alternately, the County may request the
Engineer perform other records reviews such as daily reports or turbidity monitoring reports.
Page 1 of 3
September 1, 2011
CAC September 8, 2011
VIII-6 New Business
3 of 5
Collier County
Collier Bay Dredging Construction Administration
CEC Contract No. 09-5262
Scope of Work
F. Change Orders and Contract Modifications
Assist the County prepare required field changes, change orders, or contract modifications
requested by the Contractor and submit to the County for approval.
G. Interpretation of Contract Documents
Provide to the Contractor instructions issued by the County in addition to providing any
necessary interpretations or clarifications of the contract documents requested by the Contractor.
Make determinations on non-conforming and unauthorized work as authorized in the contract
documents.
H. Substantial Completion
Upon receiving written notice from the County that the Project is substantially complete, conduct
a one-time comprehensive review of the Project, prepare a punch list of items needing
completion or correction, forward said list to the County and Contractor, and provide written
recommendations to the County concerning the acceptability of work done and the use of the
Project.
I. Final Inspection
Upon receiving written notice from the County that the Project is finally complete, perform final
site observations in conjunction with the County to verify the punch list has been completed and
the Project is ready for its intended use, and assist the County in closing out the construction
contract.
J. Final Certification
Prepare and submit the agency required Final Certifications.
The Construction Administration budget is based on a 75 day construction window.
TASK 2
PHYSICAL MONITORING REPORT
Utilizing the survey data and certifications provided by the Contractor's surveyor, prepare and
submit to CZM a draft Physical Monitoring Report in accordance with the DEP Permit. Upon
receipt of written comments from CZM, finalize and submit the Report to DEP.
COUNTY / CONTRACTOR RESPONSIBILITIES
The scope of services and budget are based on the County providing the following:
.
Sediment QA-QC Monitoring as required by the DEP Permit (County)
Turbidity Monitoring as required by the DEP Permit (Contractor)
Sea Turtle Monitoring as required by the DEP and USFWS Biological Opinion (County)
Shorebird Monitoring as required by the DEP and USFWS Biological Opinion (County)
DEP Reporting (e.g. Turbidity, Tilling, Sediment QA-QC) (County and Contractor)
.
.
.
.
Page 2 of 3
September 1, 2011
CAC September 8, 2011
VIII-6 New Business
4of5
Collier County
Collier Bay Dredging Construction Administration
CEC Contract No. 09-5262
Scope of Work
· Physical Monitoring Surveys and Surveyor's Report/Certification as required by the DEP
Permit (Contractor)
· Survey Data for the channel and beach fill shall be provided in e-format such as x,y,z file
format (Contractor)
BUDGET
TASK DESCRIPTION FEE
1 Construction Administration $ 13,660
3 Physical Monitoring Report $ 4,990
Total $ 18,650
Page 3 of3
September 1, 2011
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CAC September 8, 2011
VIII-7 New Business
1 of4
EXECUTIVE SUMMARY
Recommendation to award an $20,000 Work Order to Coastal Engineering Consultants
develop and submit the JCP permit application to FDEP for the 2012 Marco South Beach
renourishment project.
OBJECTIVE: To award a $20,000 Work Order to Coastal Engineering Consultants to
develop and submit a JCP permit application to FDEP for the 2012 Marco South beach
renourishment project.
CONSIDERATION: Collier County will renourish the Marco South Beach by placing 104,000
CY's of beach compatible sand dredged out of Caxambas Pass on the southernmost 4,400 LF of
beach. The Southernmost 4,400 LF of Marco Island beach is designated as Critically Eroded by
FDEP. The South Marco Island Beach between R144 and G-2 has been renourished in 1990,
1997 and 2006. The worst erosion in this segment is the last 2,000 feet between R147 and G2.
Tropical Storm Fay severely eroded this beach when it made landfall in August, 2008. Collier
County was successful in obtaining federal disaster assistance to renourish this beach, 77,000
CY's of beach fill was authorized for an estimated total project cost of $2,822,578. FEMA's
portion with a 75% reimbursement will max out at $2,116.933 if additional scope amendments
are not authorized.
At Collier County's request, FEMA has extended the expiration date for this authorization twice.
The current expiration date is August 2012. Staff believes that in the current national political
environment, there will be no will to extend the project authorization any farther or fund
mitigation strategies that will reduce emergency renourishments in the future.
With that said, Staff is recommending that we proceed immediately to issue a Work Order to
Coastal Engineering Consultants to develop and submit the JCP permit application for this
project. Time is of the essence and the permit application is the critical path to completing this
project by August 2012. To be successful, the permits must be issued, the construction
completed and the invoicing completed to FEMA by August 2012. This effort represents a
$750,000-$1,000,000 reimbursement to the County.
This approach will allow Collier County to issue a work order and Notice-to-Proceed
immediately to Coastal Engineering Consultants for this work.
A copy of their proposal is attached.
FISCAL IMPACT: $20,000 is estimated to perform these activities. The Source of funds is
from Category A Tourist Development Tax fund 195.
GROWTH MANAGEMENT IMPACT: There is no impact to the Growth Management Plan
related to this action.
CAC September 8, 2011
VIII-7 New Business
2of4
ADVISORY COMMITTEE RECOMMENDATION: Staff is recommending approval of this
request.
LEGAL CONSIDERATIONS: The TDC and the BCC should make a finding that this project
and expenditure will promote tourism in Collier County. This item requires majority vote and is
legally sufficient for Board action. - CMG
RECOMMENDATION: Recommendation to award a $20,000 Work Order to Coastal
Engineering Consultants to develop and submit a JCP permit application to FDEP for the 2012
Marco South beach renourishment project.
PREPARED BY: Gary McAlpin, PE - Coastal Zone Management
CAC September 8, 2011
VIII-7 New Business
3of4
Collier County
South Marco Beach Renourishment
CEC Contract No. 09-5262
JCP Application Scope of Work
SCHEDULE" A"
WORK ORDER NO.1
Collier County proposes to place approximately 104,000 cubic yards of beach compatible
sediment excavated from the Caxambas Pass borrow area to restore approximately 4,400 feet
along South Marco Island. The proposed beach fill falls within the 2006 project limits, as
previously permitted by JCP0235209-001-JC (FDEP) and SAJ-2005-2726 (IP-MN) (USACE).
The FDEP Permit expired in 2010, thus new state approvals are necessary for the Project. The
USACE Permit expires in 2021; however a modification is necessary to authorize construction
during sea turtle nesting season.
The County proposes the Project for the primary purposes of restoring storm protection, natural
resource habitats, and recreational beach areas to offset the storm damage caused by Tropical
Storm Fay in 2008. Post-storm surveys and analyses documented approximately 77,000 cubic
yards eroded within the permitted fill template. The County is seeking federal reimbursement as
defined in FEMA Project Worksheet, Declaration No. 1785DRFL.
This scope of services defines the Joint Coastal Permit (JCP) Application preparation related
services associated with the beach fill placement only.
TASK 1: JCP PERMIT APPLICATION (FDEP)
CEC shall arrange, prepare for, and attend via teleconference or webinar a pre-application
meeting with the Florida Department of Environmental Protection (FDEP),
Based upon the 2006 project permits from the FDEP and USACE and USFWS Biological
Opinion and results of the pre-application meeting, CEC shall prepare for County review and
approval updates of the following Supporting Documents:
· physical monitoring plan,
· sediment QAlQC plan,
· shorebird management plan, and
· turbidity monitoring plan,
CEC shall prepare for County review and approval, a draft JCP application for the FDEP
authorizations required for the Project including an "Application for Joint Coastal Permitting,
Authorization to Use Sovereign Submerged Lands, and Federal Dredge and Fill Permit" and a
Public Easement or Consent of Use for the previously utilized pipeline corridor if necessary. The
application shall include the following:
· County provided documents (e.g, agent authorization letter, permit fees),
· City of Marco Island consistency letter with comprehensive plan,
· permit drawings,
· sketch and legal description for previously utilized pipeline corridor,
· analysis of potential Project related impacts to spawning marine fisheries for construction
between May I st and October 31 s\
· coastal systems assessment (prepared under a prior work order),
· alternatives analysis and modeling results (prepared under a prior work order), and
Page I of2
September 7,2011
CAC September 8, 2011
VIII-7 New Business
4of4
Collier County
South Marco Beach Renourishment
CEC Contract No. 09-5262
JCP Application Scope of Work
· existing historical geotechnical data for the native beach and borrow area from the prior
projects,
CEC will verify the JCP Application processing fee amount and notify the County when
payment by the County is due to FDEP. In the application, CEC will request:
· construction plans with updated survey data (within 6 months) be a condition for issuance of
a "Notice to Proceed" following agency review and acceptance of the final design,
· mixing zone within the fill area, and
· waiver of dredge fees for use of borrow material obtained from sovereign lands.
CEC shall incorporate County review comments and submit the JCP Application and Supporting
Documents to the FDEP.
ASSUMPTIONS
The scope and budget estimates for the Project are based on the following assumptions.
A. The County shall provide the following:
· Permit Fees,
. Public Noticing, and
. Agent Authorization Letter.
B. Final Design, Permit Processing, and Construction Services shall be provided under
subsequent work order(s).
BUDGET
DESCRIPTION
JCP Permit A lication (FDEP
TIME & MATERIALS
$ 20,000
Page 2 of2
September 7,2011
Board of Collier County Commissioners
Donna Fiala
District 1
Georgia A. Hiller, Esq.
District 2
Tom Henning
District 3
Fred W. Coyle
District 4
Jim Coletta
District 5
June 30, 2011
Mr. Anthony P. Pires, Jr,
209 Madison Drive
Naples, Florida 34110
Reference: Collier County Coastal Advisory Committee
Dear Mr. Pires:
On September 21, 2004, the Board of County Commissioners adopted Resolution No. 2004-280
to recognize volunteers serving on Advisory Committees. The Board would like to recognize
your dedicated service and commitment as a volunteer member on the Collier County Coastal
Advisory Committee.
We have scheduled your IO-year service award ceremony for the Board of County
Commissioners meeting on Tuesday, July 26, 2011 at 9:00 a,m. in the Board Chambers, 3rd
Floor, W, lIarmon Turner Building, 3299 Tamiami Trail East, Suite 303, Naples, Florida.
Congratulations and please e-mail me at ianmitchell0)colliergov.net or give me a call at
(239) 252-8097 to confirm your attendance on July 26, 2011.
Very truly yours,
Ian Mitchell, Executive Manager to BCC
Board of County Commissioners
1M
Cc: Gary McAlpin
3299 Tamiami Trail East. Suite 303 . Naples, Florida 34112-5746 . 239-252-8097 . FAX 239-252-3602