Clam Bay Committee Agenda 09/05/2013 PELICAN BAY SERVICES DIVISION
Municipal Service Taxing and Benefit Unit
NOTICE OF PUBLIC MEETING THURSDAY, SEPTEMBER 5, 2013
THE CLAM BAY COMMITTEE OF THE PELICAN BAY SERVICES
DIVISION BOARD WILL MEET THURSDAY, SEPTEMBER 5 AT 1:00 PM
AT THE COMMUNITY CENTER AT PELICAN BAY, 8960 HAMMOCK
OAK DRIVE, NAPLES, FL 34108.
AGENDA
The agenda includes, but is not limited:
1 . Roll Call
2. Approval of June 26 and July 16 Clam Bay Committee Meetings
Minutes
3. Discuss Draft Clam Bay Management Plan
4. Discuss scientific services for PBSD
5. Watercraft violating County ordinance
6. Audience comments
7. Adjourn
ANY PERSON WISHING TO SPEAK ON AN AGENDA ITEM WILL RECEIVE UP TO
THREE (3) MINUTES PER ITEM TO ADDRESS THE BOARD. THE BOARD WILL
SOLICIT PUBLIC COMMENTS ON SUBJECTS NOT ON THIS AGENDA AND ANY
PERSON WISHING TO SPEAK WILL RECEIVE UP TO THREE (3) MINUTES. THE
BOARD ENCOURAGES YOU TO SUBMIT YOUR COMMENTS IN WRITING IN
ADVANCE OF THE MEETING. ANY PERSON WHO DECIDES TO APPEAL A
DECISION OF THIS BOARD WILL NEED A RECORD OF THE PROCEEDING
PERTAINING THERETO, AND THEREFORE MAY NEED TO ENSURE THAT A
VERBATIM RECORD IS MADE, WHICH INCLUDES THE TESTIMONY AND
EVIDENCE UPON WHICH THE APPEAL IS TO BE BASED. IF YOU ARE A PERSON
WITH A DISABILITY WHO NEEDS AN ACCOMMODATION IN ORDER TO
PARTICIPATE IN THIS MEETING YOU ARE ENTITLED TO THE PROVISION OF
CERTAIN ASSISTANCE. PLEASE CONTACT THE PELICAN BAY SERVICES
DIVISION AT (239) 597-1749. VISIT US AT
HTTP://PELICANBAYSERVICESDIVISION.NET.
8/23/2013 2:20:52 PM
CLAM BAY COMMITTEE MEETING MINUTES
WEDNESDAY,JUNE 26,2013
LET IT BE REMEMBERED that the Clam Bay Committee of the Pelican Bay Services Division
Board met on Wednesday,June 26,2013 at 3:00 PM at the Community Center at Pelican Bay, 8960
Hammock Oak Drive,Naples,Florida. The following members were present:
Clam Bay Subcommittee
Susan O'Brien, Chairman John Domenie
Joe Chicurel Mike Levy
Tom Cravens
Pelican Bay Services Division Staff
W.Neil Dorrill,Administrator Mary McCaughtry, Operations Analyst
Kyle Lukasz, Operations Manager Lisa Resnick,Recording Secretary
Moderator Tim Hall, Senior Ecologist&Principal,Turrell, Hall &Associates, Inc.
Also Present
Lauren Gibson,Biologist&Project Manager,Turrell, Hall &Associates, Inc.
Jim Hoppensteadt, President and Chief Operating Officer, Pelican Bay Foundation
Linda Roth, Mangrove Action Group
Kathy Worley, Conservancy of Southwest Florida
AGENDA
1. Roll Call
2. Approval of May 14 and May 23 meeting minutes
3. Development of Clam Bay Management Plan
a. Draft of Outline of Plan
b. Proposal for Monitoring and Investigative Backup Needed
c. Estimate of Costs
d. Point person for writing draft of plan
e. Timeline for first draft of plan
4. Water Quality 1 ,
a. Compiling available data from County and PBSD
b. Ongoing monitoring program
c. Resolving copper impairment in Clam Bay
5. Audience comments
6. Adjourn
ROLL CALL
All Committee members were present.
APPROVAL OF MAY 14 AND MAY 23 MEETING MINUTES
Mr. Cravens motioned,Dr. Chicurel seconded to approve t ,a and ", t4 23 meeting
minutes as presented. The Committee voted unanimous!_ + 1 ., Ilion passed.
r
23
Clam Bay Committee Meeting Minutes
June 26,2013
DEVELOPMENT OF CLAM BAY MANAGEMENT PLAN
Mr. Hall described the purpose of the management plan as a document to provide guidance to the
community by identifying and outlining goals, objectives, scope of activities, and form the basis for
future permitting that would provide agency authorization to do the activities outlined in the Plan. For
example,the Plan would identify dredging"triggers",parameters, and scope of work. When the Plan
indicates it is time to dredge, authorization to dredge would be sought.
ESTIMATE OF COSTS
Mr. Hall estimated it would cost approximately$200,000 in total to develop the management
plan. Approximately$100,000 includes annual monitoring and reporting contract services the firm
already provides. Surveys, engineering services, document compilation, surveys, meetings, and permitting
services would cost an estimated$100,000 in total.
TIMELINE FOR FIRST DRAFT OF PLAN
Mr. Hall estimated the timeline was approximately six months to prepare the management plan
and an additional six months for permitting, or longer depending upon whether the County Purchasing
Department requires the project to go through the Request for Proposals(RFP)process.
To clarify the timeline, Mr. Dorrill and Ms. O'Brien would schedule a meeting with the County
Purchasing director and Clerk's Finance director to find out whether an RFP will be required and provide
a report at the July Board meeting.
WATER QUALITY
COMPILING AVAILABLE DATA FROM COUNTY AND PBSD
Ms. O'Brien reviewed water quality data from STORET and explained the Services Division may
want to consider having water quality data from other sources compiled and analyzed.
MISCELLANEOUS
Mr. Hall reported that permitting for the Osprey nest box can be done under the Foundation's
existing permit located near the South Beach facility.
Mr. Dorrill reported two issues of importance: 1) a child nearly drowned last week at C . 'ass
and reports blamed the recent dredging was too narrow as the cause. For liability purposes e
that the proper signage was in place at the Pass to warn swimmers; and 2)May 5, several hu
high school students congregated at Clam Pass. Underage drinking and other unla vity d
and reported to the Sheriff and County Parks and Recreation staff to not allow this tire.
Mr. Cravens reported sighting several North Atlantic Right Whale. 60 fe Weans an
endangered species in the Gulf of Mexico nearby the North Beach fac'
24 ry
Clam Bay Committee Meeting Minutes
June 26,2013
AUDIENCE COMMENTS
None
ADJOURN
Mr. Cravens motioned,Dr. Chicurel seconded to adjourn. The Committee voted unanimously
in favor,the motion passed, and the meeting adjourned at 4:21 p.m.
Susan O'Brien, Chairman Minutes by Lisa Resnick 7/30/2013 9:23:47 AM
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CLAM BAY COMMITTEE MEETING MINUTES
TUESDAY,JULY 16,2013
LET IT BE REMEMBERED that the Clam Bay Committee of the Pelican Bay Services Division
Board met Tuesday,July 16,2013 at 1:00 PM at the Community Center at Pelican Bay, 8960
Hammock Oak Drive,Naples, Florida. The following members were present:
Clam Bay Committee
Susan O'Brien, Chairman John Domenie
Joe Chicurel Mike Levy
Tom Cravens
Pelican Bay Services Division Staff
W.Neil Dorrill,Administrator Mary McCaughtry, Operations Analyst
Kyle Lukasz, Operations Manager Lisa Resnick,Recording Secretary
Moderator Tim Hall, Senior Ecologist&Principal, Turrell, Hall &Associates, Inc.
Also Present
Dave Cook, Pelican Bay Foundation Board of Directors
Keith Dallas, Pelican Bay Services Division Board former Member
Lauren Gibson, Biologist& Project Manager, Turrell, Hall&Associates, Inc.
Jim Hoppensteadt, President and Chief Operating Officer,Pelican Bay Foundation
Gerald Moffatt, Pelican Bay Foundation Board of Directors
Mollie Moffatt, Pelican Bay Resident
Linda Roth, Mangrove Action Group
Kathy Worley, Co-Director Environmental Science, Conservancy of Southwest Florida
REVISED FINAL AGENDA
1. Roll Call
2. Board of County Commissioners documents pertaining to approval of work order to update the
Clam Bay Management Plan
3. Available resources for update of Clam Bay Management Plan, including,but not limited to:
a. 1998 Clam Bay Restoration and Management Plan
b. 2008 Draft of Clam Bay Mangrove Management Plan
c. 2010 Florida Department of Environmental Protection documents submitted wi.
Joint Environmental Resource permit application to continue Clam Bay cha " ?„!„
maintenance activities
d. 2013 U.S. Army Corps of Engineers Nationwide Permit documents sue °d
permit application for Dredging Clam Pass
e. 2013 Priority Topics of Stakeholders and Suggested Table of Contents
4. Timeline for updated Clam Bay Management Plan
5. Scientific Services for Pelican Bay Services Division (Susan O'Brien) o t
6. Audience comments ° ;
7. Adjourn
-ItiV -
f•26
Clam Bay Committee Meeting Minutes
July 16,2013
ROLL CALL
All Committee members were present.
BOARD OF COUNTY COMMISSIONERS DOCUMENTS PERTAINING TO APPROVAL OF
WORK ORDER TO UPDATE THE CLAM BAY MANAGEMENT PLAN
Chairman O'Brien reviewed the backup material of the chronology of Board of County
Commissioners action regarding approval of the work order to update the Clam Bay Management Plan.
The material was originally prepared for the discussion with the Clerk of Courts and Purchasing staff
regarding how to proceed in terms of the procurement process to update the Clam Bay Management Plan.
AVAILABLE RESOURCES FOR UPDATE OF CLAM BAY MANAGEMENT PLAN
Ms. Kathy Worley observed that the available resources listed to update the management plan
were primarily for mangrove or hydrologic restoration and suggested looking at other plans that were
more pertinent to managing an estuary system.
The Committee discussed topics to include in the draft plan. Some agreed that it was imperative
to include dredging"triggers"and parameters; others agreed information about dredging could be added
later after the draft was complete.
Mr. Dorrill stressed that it was imperative to include dredging designs, parameters, and dredging
"triggers" in the Plan.
Mr. Hall agreed and was concerned about how to proceed with the Stakeholders input received.
The Committee agreed that the applicable parts of the 2008 Draft Clam Bay Mangrove
Management Plan,the 1998 Restoration and Management Plan and the stakeholder input would serve as
the basis for updating the Clam Bay Management Plan.
Dr. Chicurel suggested"Clam Bay Natural Resource Protection Area NRPA Management Plan"
as the title of the plan.
TIMELINE FOR UPDATED CLAM BAY MANAGEMENT PLAN
Mr. Hall would prepare a draft plan for the Committee's review by September 1 and determ.,1
estimated expenses-to-date and additional costs.
SCIENTIFIC SERVICES FOR PELICAN BAY SERVICES DIVISION(ADD-ON)
Chairman O'Brien suggested that Committee members think about whether the PB s
consider hiring a staff scientist. The Committee was concerned about locating canw ith t
required education and experience,and the cost an additional full-time employee. , VIY 'on
deferred to the next Committee meeting.
AUDIENCE COMMENTS
None
{
27
Clam Bay Committee Meeting Minutes
July 16,2013
NEXT CLAM BAY COMMITTEE MEETING
Staff would schedule a Clam Bay Committee meeting for Thursday, September 5 at 1 p.m.
ADJOURN
Chairman O'Brien adjourned the meeting at 2:03 p.m.
Susan O'Brien, Chairman Minutes by Lisa Resnick 7/30/2013 9:21:42 AM
frAp
28
September 5,2013 Clam Bay Committee of the Pelican Bay Services Division Board
3. Discuss Draft Clam Bay Management Plan(Comments by Joe Chicurel)
Page 1 of 11
t
THE CLAM BAY NATURAL RESOURCE PROTECTION
AREA MANAGEMENT PLAN (First DRAFT)
Tim,
I'd like to give you some suggestions to include in your drafting of the
2013 Clam Bay(NRPA) Management Plan. Your clarification to us that a management
plan is for our stewardship of Clam Bay helped us better focus on the task at hand.
I think, however, that it is also a historical document that catalogs the
chronologic history of the geography(boundaries),development,science(flora and
fauna-mangroves of course),engineering data, uses,governence, and the
environmental concerns and issues of the Clam Bay system.
After reading the 1998 CBRMP and the 2006/2008 drafts plans, it
seems that all had similar ingredients. Our new 2013 plan should incorporate and build
on the other plans. I believe the new 10 year plan should not only help our stewardship
but also lay out to all stakeholders an unambiguous history of the science and
engineering data of the Clam Bay NRPA.All stakeholders will then have a core
knowledge base that can hopefully help eliminate or lessen differences of opinion
as issues arise concerning Clam Bay NRPA usage,dredging, permitting,etc.
I'll use your 2013 Table of Contents as a blueprint for my suggestions.
The body of the 2008 draft looks like a good template and I followed it with my
suggestions.
Thank you for your good work and expertise.
Sincerely,
Joe Chicurel,
PBSD Board Member
September 5,2013 Clam Bay Committee of the Pelican Bay Services Division Board
3. Discuss Draft Clam Bay Management Plan(Comments by Joe Chicurel)
Page 2 of 11
July 16,2013 Clam Bay Subcommittee of the Pelican Bay Services Division Board
3e. 2013 Priority Topics of Stakeholders and Suggested Table of Contents(submitted materiel dates as indicated)
Page 11 of 12
Management Plan Discussion Items
06/26/2013
Table of Contents(DRAFT)
INTRODUCTION
PURPOSE AND SCOPE OF MANAGEMENT PLAN
MANAGEMENT PROGRAM OVERVIEW
Management Authority and Responsibilities
Management Coordination
Location and Regional Significance
Public Involvement
RESOURCE DESCRIPTION AND ASSESSMENT
Natural Resources
- Physiography
- Climate
- Plant Communities
- Plant Species
- Animal Species
- Listed Species
- Exotics
Cultural Resources
HISTORICAL OVERVIEW
NRPA GOALS AND OBJECTIVES
Provide sufficient tidal exchange to maximize benefits to the estuary
Maintain and protect native floral and faunal communities
Improve water quality
Address recreational uses with emphasis on passive recreation
LITERATURE CITED
APPENDICES(+others as needed)
Maps and Figures
Plant Species List(s)
Animal Species List(s)
Managing Documents
Permits
MAPS(+others as needed)
Location Map
Vicinity Map
Topographic Map
Soils Map
Natural Communities(FLUCFCS)Map
Page 357 of 358
September 5,2013 Clam Bay Committee of the Pelican Bay Services Division Board
3. Discuss Draft Clam Bay Management Plan(Comments by Joe Chicurel)
Page 3 of 11
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September 5,2013 Clam Bay Committee of the Pelican Bay Services Division Board
3. Discuss Draft Clam Bay Management Plan(Comments by Joe Chicurel)
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Page 5 of 11
July 18,2013 Clam Bay Subcommittee of the Pelican Bay Services Division Board
3e. 2013 Priority Topics of Stakeholders and Suggested Table of Contents(submitted material dates as indicated)
Page 7 01 12
May 23,2013 Clam Bay Subcommittee of the Pelican Bay Services Division Board
Purpose of the Clam Pass Inlet and Estuary Management Plan&Recommended Priorities
(Submitted by Tim Hall,Turrell,Hall&Associates,Inc.)
Purpose of the Management Plan
The purpose of the management plan will be to provide : dance and direction for the
management o i Clam Pass and its associated estuary s it '.y identifying the goals and
o•jecttves necessary o avoid or minimize impacts to ire natural resources and biological
integrity of the system. This plan will form the basis by which future management
decisions can be made by identifying the appropriate management techniques n
to preserve, enhance, restore, maintain and monitor the uses and resources within&ip
trystem,
The plan will attempt to balance - ■urce protection 'th passive recreational use. It Ntll
sheer consider Clam Pass mo+' • 'i r g an maul : ice,restoration needs,water quality,
listed species protection ..• ation and other issues as identified in the Plan's formulation
process.
The m: :r l ement plan shall be submitted to the Collier County Board of County
C• • 'ssioners(BCC)for its approval.When approved,this plan will form the basis for
ture permitting and other management activities within the system.
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P edn Area(N ))
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Page 1 of 3
Page 353 of 358
September 5,2013 Clam Bay Committee of the Pelican Bay Services Division Board
3. Discuss Draft Clam Bay Management Plan(Comments by Joe Chicurel)
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3. Discuss Draft Clam Bay Management Plan(Comments by Joe Chicurel)
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3. Discuss Draft Clam Bay Management Plan(Comments by Joe Chicurel)
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Dear 'lam Bay Committee:
On behalf of Chairman O'Brien,see below/attached. To avoid Sunshine issues,please do not
reply/comment. siesLia:fccryt 4 I
4 IN Thanks, ∎ ' il IS4Afs If
Lisa
Lisa Resnick 40,194 � r fAS K 1
Pelican Bay Servi C�ivi e�r1'
y
801 Laurel Oak Drive,Suite 405
Naples,FL 34108
la
Tel.239.597.1749
Fax 239.597.4502 l
i li ov.net l 5V()
http://pelicanbayservicesdivision.net 414 A
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- i From:Susan O'Brien[mail0o:na nett
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Sent:Monday,July 22,2013 9:43 AM
To:Resnida
Suter Fwd:Mangrove Action Group Meeting April 24 ),/ea
FE Lisa, 7 -1),"P' 1.Y0)(42
_____
Wo • • - : • - to distribute the bell , link to Dr.Dabees' ; • t*on that be u• about 38
.+ asites 1 • • 14,.1 b, Clam Bay Comma 7' - • ••: s presentation was men.o • : .>;
.«i. • •mmittee meeting.
Thanks very much.
Susan O'Brien
3. Visit www.Coiliergov.net. From home page hit video archive then hit work
shop video from the following line. You can advance it to around 38 minutes
when this item begins.
1 BCC Workshop1364886000Apr 2 2013 1 04h 24m It 1
ISN or go to link:
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A � arncus.com/MediaPlayerphp?yiew id-414clip id---1485
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September 5,2013 Clam Bay Committee of the Pelican Bay Services Division Board
3. Discuss Draft Clam Bay Management Plan(Comments by Joe Chicurel)
Page 9of11
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September 5,2013 Clam Bay Committee of the Pelican Bay Services Division Board
3. Discuss Draft Clam Bay Management Plan(Comments by Joe Chicurel)
Page 10 of 11
10
F..*. s: Ted Raia dedraiaegmail.c orn>
Sub4ect: Re:Response on Monday-Clam Bay Report
—ate: April 1,2013 931 S5 PM EDT
To: Jeanne Findlater.<tindlaterecomcast.neb
Cc: Linda Roth<lor3lor3 @aol.cor%Len Rothman<judytenr22 @aol.corn>,Estelle Fishbein<e#ishbeinejhu.ed
Todd Bolan<toddboleneaot c o n>,Johan Domanie<hobodory comcast.net>,Kay Potter
<akpotter01@comcast.net>,Shed Arnold<eheriarnold28 @comcast.net>,Liliisa Brace<0:auceemsn.cant>,
Robert Schutheis<rschult @elue.edu>,Mary Vance Duggan<MaryvanceDegmaitcom>,Michael Seet
<m @aol com>,Cravens Marcia agoidandroee @mac.com ,chstlltspringsassociates.corn,
eiaine;=checkemet.com,Morgan Rees ra @ewthlink.net>,Steve Gregerson
nehotmaIl.cor%Kathy"Worety drat yweconservancy.org>.Art Riles<ARitas540 @aol.com>
annice gregereon<nannlceecornc ast.neb,ron diorio<cllorioroneyahoo.cam>,saknsw @aol.com,bob
naegele donJr naegelenet.com>.Arthur Chase<ar hur @checkemet.corn>,lave tracker
<itrecker @yatwa.com>,Torn cravens<ntn167990naplee.net>,hunter hansen<ttunb r.harsenehilton.cc
OM laluo daizzo @comcast.net>,paronewatersideshaps.com,mike levy levy<mgrelonollletnbernmalicom>
John Chandler< nchandler219 @gmafi corn>,Susan O&ten @c omcast..net>,Joesph ChM
morel r'grnatLoom>,Scott Strecke nbein yahoo.com>,Somme rata<filra a5gmail.c c
pat bush<pibushwork @conKast.nab,David Cook<mednc dcrillgrnaLcom>,swan boland
<johnsusanboiand @aol.cocn>
Folks. I appreciate your last edits but they arrived a little too late to enter. Fortunately I do not believe they
would have materially altered the report. This is what was stbmitt•d:
The Mangrove Action Group is submitting the following written
statement as requested by Tim Hall of Turret!, Hall &
Associates to be included in the preparation of a new ten year
management plan for the Clam Bay mangrove estuary. We
have been identified as one of the players but our comments
must be in writing. However at our public meeting that was
held on March 27, 2013 these comments were made and
•iscussed.
z be to Wilted C PEESSICIEffil
Bay as a NEdural Resources es Protection Area (NRPA) to ifitlietaillk
preseiveand protect the entire mangrove estuary system
including the mangroves, seagrass, benthic quality, water and
wildlife. The process must follow the Federal Guideline to do
E: dam: •ins •racticabW alternative
to . laving a d - - - �...
rom t e expenence o e • • ; Clam :ay 'estoration and
,
eta avrbein 7 2S, $44/ PBsb v-fie/c'
September 5,2013 Clam Bay Committee of the Pelican Bay Services Division Board
3. Discuss Draft Clam Bay Management Plan(Comments by Joe Chicurel)
Page 11 of 11
fJ
SECONDARY USE; Pji/'gi'1t 461 CiffkLS gig,� 54 PC
„ it er.`t+abort that's We with elite�des use. •
i' Passive recreation has been consistent and concurrent with the history of primary
•`� / designated land uses which includes submerged lands,swamps, and waters. Thousands of
�i residents in Pelican Bay,Seagate,and Naples Cay enjoy their unique access to the back bay
lagoons and thousands of other city/county residents and tourist visitors to Clam Pass Park
benefit from passive recreation opportunities at Clam Pass Park that is highly compatible
with its Primary Designated Functional Uses. Residents and visitors from near and far
benefit from Clam Pass Park beach and waterway access with opportunities to walk/hike on
the boardwalk,nature trail or open beach;lounge at the concession or on the beach;
observe and photograph wildlife; safely wade,swim,snorkel,float,and fish at Clam Pass;
and many visitors enjoy paddling the popular Clam Pass Park Canoe Trail with access from t
several sites.
i
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' t ! ings w€ 't wdd I � wa ; r; °a:-to viiduabie
benthic commundes and the publics safe*,, ,e ' - : II'
travel inthe nutrked
ng tree in Idle sperm" as cum : = preserve's
des'.an"idle Speed/No INftdoi" zmety Count/
. 9646 by
......... , COWAtir 04
Ted Raia, M.D., President
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CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
September 3, 2013
TABLE OF CONTENTS
1.0 Introduction
Purpose and Scope of the Management Plan.
Overview of the Clam Bay NRPA
Personnel/Consultants Responsible
Role of Pelican Bay Services Division
2.0 Clam Bay Location and Setting
Maps, description of Pelican Bay and the estuary system
Natural history of the system and pass
3.0 Historical Overview
Historical time line
Original mangrove die-off causes
Restored characteristics of Clam Bay
4.0 Resource Descriptions
Soils
Climate
Natural Communities
Species
Hydrology
Water Quality
Inlet Dynamics
5.0 Authorized Construction Activities
List of permits and work undertaken to date
6.0 Management Goals and Objectives
Management action/work required, performance criteria and monitoring, responsible
entities, timeframe
6.1 Provide sufficient tidal exchange to maximize benefits to the estuary while
minimizing environmental impacts.
6.2 Maintain and protect the native floral and faunal communities
6.3 Manage and improve water quality
6.4 Address recreational uses with emphasis on passive recreation
6.5 Improve community awareness and involvement
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
September 3, 2013
1.0 Introduction
Purpose of the Management Plan
The purpose of this management plan will be to provide guidance and direction for the
management of Clam Pass and the Clam Bay estuary system by identifying the goals and
objectives necessary to avoid or minimize impacts to the natural resources and biological
integrity of the system. This plan will form the basis by which future management decisions can
be made by identifying the appropriate management techniques necessary to preserve, enhance,
restore, maintain and monitor the uses and resources within the Natural Resource Protection
Area.
The plan will attempt to balance resource protection with passive recreational use. It will
consider Clam Pass monitoring and maintenance, restoration needs, water quality, listed species
protection, education and other issues as identified in the Plan's formulation process.
The final management plan and any subsequent revisions shall be submitted to the Collier
County Board of County Commissioners (BOCC) for its approval. When approved, this plan will
form the basis for future permitting and other management activities within the system.
Overview of the Clam Bay System
The Clam Bay estuarine system is a 570-acre area of sandy beaches, shallow bays, seagrass beds
and mangrove forests on the coast of Collier County in southwest Florida. The community of
Pelican Bay abuts the northern and eastern edges of the system, while the Seagate and Naples
Cay communities abut the southern portion of the system. This system is an important natural
and recreational resource for local residents and visitors. It was designated a Natural Resource
Protection Area(NRPA) by Collier County in 1994.
This plan, in addition to providing a brief history of activities undertaken within this system,
outlines management goals, objectives and methods to achieve optimal functioning of the
delicate mangrove system. Drawing on an earlier plan (The Clam Bay Restoration and
Management Plan prepared by the firm of Wilson Miller Barton& Peek, CBRMP 1998), and the
findings of 14 years of monitoring activities within the system, this plan outlines the goals for
future enhancements to, and maintenance of, the ecosystems throughout Clam Bay.
The Clam Bay Restoration and Management Plan, 1998
In 1992 a small area of dead black mangroves was first observed in the northern part of the
system. In 1995 a significant area (approximately 50 acres) of dead and dying mangroves was
reported (Turrell, 1996). Following the die-off, restorative dredging was proposed to increase
tidal flushing by opening up the pass and widening several tidal creeks within the system. The
CBRMP was prepared in conjunction with State and Federal environmental permits to carry out
the work, and consequently focused on management objectives which were proposed at that
time, namely;
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
September 3, 2013
• Deepening and maintaining Clam Pass
• Dredging portions of the interior tidal creeks to improve flushing capacity
• Studying the potential for improvements in upland stormwater/freshwater management
• Installation of flushing culverts under Seagate Drive
The Clam Pass Natural Resource Protection Area Management Plan, 2013
This Clam Pass Natural Resource Protection Area Management Plan (CPMP, 2013) combines
the comprehensive outline and background provided in the original 1998 plan with lessons
learned during and subsequent to its implementation. The goals of this Plan will be to direct the
management activities undertaken to enhance the estuarine and associated habitats in a manner
that maintains and contributes to the overall integrity of the Clam Bay ecosystem. Namely, the
activities undertaken under the Plan will:
• Provide sufficient tidal exchange to maximize benefits to the estuary
• Maintain and protect native floral and faunal communities
• Improve water quality while maintaining the stormwater discharge and surface water
management necessary to support the adjacent communities
• Address recreational uses within the system with emphasis on passive recreation
• Continue to educate and inform residents and visitors about the importance of the
ecosystem
Personnel/Consultants Responsible
This CPMP has been prepared by the firm of Tunell, Hall & Associates, Inc., who, as project
managers for the restorative dredging and associated monitoring work has a long history with the
project and ecosystem. Input and monitoring data has been incorporated from coastal engineers,
Humiston & Moore, Inc., as well as other interested stakeholders such as the Pelican Bay
Foundation, the Mangrove Action group, the Conservancy of Southwest Florida, adjacent
community associations, and the City of Naples. The ongoing support and assistance of the
PBSD and Collier County is gratefully acknowledged.
Pelican Bay Services Division Turrell, Hall &Associates
Tom Cravens—Chairman Tim Hall—Project Manager
801 Laurel Oak Drive, Suite 605 3584 Exchange Ave
Naples, FL 34108 Naples, Fl 34104
(239) 597-1749 (239) 643-0166
Humiston& Moore Engineers
Brett Moore—Project Manager
5679 Strand Court
Naples, FL 34110
(239) 594-2021
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT) .
Pelican Bay Services Division
September 3, 2013
Pelican Bay Services Division
In order for the management and enhancement of the Clam Pass NRPA to be successful,
coordination between a myriad of local, state, and federal agencies and concerned citizen's
groups is required. The Pelican Bay Services Division (PBSD) has undertaken that role for most
of the past fifteen years.
The PBSD is a dependent special district known as the Pelican Bay Municipal Services Taxing
and Benefit Unit. It was formed pursuant to Chapter 125 of the Florida Statutes and was
formally enabled by the Collier County Commission pursuant to Ordinance numbers 90-111 and
91-22. These ordinances were replaced in 2002 by Ordinance 2002-27 which further clarified
the basis and role of the MSTBU and PBSD Board. This MSTBU was created to, among other
things, provide for the maintenance of conservation and preserve areas within Pelican Bay. This
responsibility was undertaken diligently from 1998 to 2009 and resulted in the implementation of
the previous Management Plan and the recovery of the mangrove die-off area. The Collier
County Coastal Zone Management Department assumed responsibility of the Pass monitoring
and maintenance for a short while from 2009 to 2012 while the PBSD continued to monitor and
maintain the mangrove communities within the system. At the beginning of 2013, the Collier
County BOCC returned responsibility of the Pass to PBSD via Ordinance 2013-19 and it is under
their direction that this current management plan is being written.
As a dependent special district, the PBSD is an arm of local county government and as such does
not enjoy the ability to make decisions concerning the implementation of the Management Plan
independent of the desires of the Collier County BOCC. The PBSD budget, and therefore its
ability to undertake work projects, is controlled by the Collier County BOCC. In practical
application, this has not proved problematic, as the BOCC has routinely approved the mangrove
management undertakings of the PBSD and the BOCC has authorized the development of this
Management Plan. The PBSD implements County policy within the confined geography of the
Pelican Bay community and the defined responsibilities of the PBSD. The PBSD sets it own
budget and agenda and routinely submits same to the Collier County BOCC for approval. The
actual workings of the relationship suggest therefore, that the PBSD has experienced a
significant degree of practical autonomy and that this is expected to continue in regards to the
implementation of this Management Plan. The result is that the PBSD will be the official
manager of this Management Plan with delegated authority to be implemented consistent with
Ordinances 2002-27, and 2013-19 of Collier County.
The PBSD will direct this Management Plan and have the responsibility for its implementation
and operation over time. As such, the PBSD will plan and implement defined management
activities (with BOCC approval) whose purpose will be to protect, enhance and maintain the
natural communities and ecological integrity of the Clam Bay NRPA.
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
September 3, 2013
The PBSD has several attributes which already make it a logical guiding force in the
management of Clam Bay. The PBSD:
• Is located within the Clam Bay drainage basin;
• Has an advisory board(appointed by the County Commission)made up of residential,
and business members within Pelican Bay;
• Garners fiscal support collected from local benefit assessments;
• Is accessible by the public due to its local governing board and advertised public monthly
meetings; and
• Has demonstrated a long-term commitment to the resource and its preservation and
enhancement over the past fifteen years.
These attributes give PBSD the knowledge and expertise in matters of local concern and, in
particular, the problems, opportunities and interests of local residents as they relate to the Clam
Bay ecosystem. Its relationship to the BOCC give it an additional level of access to technical
expertise and oversight that will be necessary to assure that the Management Plan, as
contemplated in this document, is fully implemented in the field.
As part of its responsibilities, the PBSD will assemble and distribute various technical reports
and assessments as required under the Management Plan, as well as coordinate with the other
public and private groups interested in Clam Bay. The PBSD is organized for and designed to
maintain both its knowledge of the Clam Bay resources and to generate public support for the
same. PBSD will insure that the general public, residents in Pelican Bay, PBSD consultants, and
representatives from government agencies with jurisdiction over Clam Bay each have on-going
involvement and input into the Management Plan as appropriate.
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
September 3, 2013
2.0 Clam Bay Location and Setting
Maps, description of Pelican Bay and the estuary system
Clam Bay was designated a Natural Resource Protection Area by the Board of County
Commissioners of Collier County in 1994 (Collier County, 1994) and consists of approximately
420 acres of mangroves and some 115 acres of shallow, open water bays, as well as a 35 acre
beachfront parcel (Clam Pass Beach Park). The system consists of three primary bays; Outer
Clam Bay (southernmost), Inner Clam Bay (central), and Upper Clam Bay (northernmost),
connected by a series of tidal creeks.
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The entire system receives runoff from adjacent upland and wetland areas. Upper Clam Bay is
connected to Inner Clam Bay by a winding narrow creek. Inner Clam Bay is connected to Clam
Pass through another narrow creek. Outer Clam Bay is connected to the Gulf of Mexico by a
wider creek through Clam Pass. Some water also flows south to Doctor's pass through the
culverts under Seagate Drive.
Clam Bay Vital Statistics
Total acres: Approx. 570 acres
Beaches: Approx. 3 miles
Mangrove: Approx. 420 acres
Open Water: Approx. 115 acres
i Latitude and Longitude of Pass: N 26° 13' 11", W 81° 49' 01"
Section, Township, Range: Sec. 32 & 33, Twp 48S, Rng 25E, &
Sec. 4, 5, 8, & 9, Twp 49S, Rng 25E
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
September 3, 2013
Clam Pass is a small, marginally stable inlet that has migrated north and south along the shore
over the years. Prior to dredging, average water depths were -2.5' to -1.0' with a width of 30-50'
(Collier County, 1994). The Pass remains the primary source of tidal exchange for the Clam Bay
system, but it is restricted by sediment deposits just inside the pass and in the long meandering
tidal creeks surrounded by mangrove forests. The smaller embayments located primarily to the
north of the pass are not subject to normal tidal exchange except during exceptionally high tides.
Tidal range is restricted throughout the Clam Bay system (Turrell 1995; Collier County Report
1996; Tackney 1996).
Tide gauges are installed and monitored on the County boardwalk at the north end of Outer Clam
Bay, the north and south Pelican Bay boardwalks, and in Upper Clam Bay. These gauges
indicate that the dredging done at the pass and in the interior creeks has drastically improved the
tidal exchange throughout the system. Tidal ranges vary from 2 feet out in the Gulf to 1.5 feet in
the southern portion of the system down to about 0.5 feet at the northern end of the system.
South of Clam Pass, a channel oriented north-south with water depths varying between -1.0' to -
4.0' leads to Outer Clam Bay (approx. 72 acres), itself connecting to the Venetian lagoon system
via a couple of concrete culverts under Seagate Drive. There are also three dead end canals off
the south end of Outer Clam Bay that are associated with the Seagate community.
North of Clam Pass, a long narrow (approximately 6,600') tributary leads to Inner Clam Bay
(approx. 32 acres). Evidence in the literature suggests that oyster bars were once present in this
channel (Humm and Rehm, 1972). A further,narrow creek(5,400') leads north from Inner Clam
Bay to the smallest and most isolated; Upper Clam Bay(approx. 20 acres).
Historical aerials and anecdotal recollections from long-time County residents note a connection
of the system at Upper Clam Bay to Vanderbilt Lagoon and Wiggins Pass to the north via a small
creek (Collier County, 1994, Tropical Biolndustries, 1978). This connection was eventually
severed with the development of Vanderbilt Beach Road in the 1950s.
The system is bounded on the north by Vanderbilt Beach Road, to the south by Seagate Drive,to
the east by the Pelican Bay development and to the west by the Gulf of Mexico.
Pelican Bay is predominately a residential community of private single-family homes, as well as
both high and low-rise condominium units. The community also includes a 27-hole golf course,
common areas with meeting rooms, tennis courts, beach park facilities, emergency services
facilities, and commercial areas with shopping and hotels. The 2,104-acre Planned Unit
Development (PUD) was approved in 1977 as a partnership between Collier Enterprises and
Westinghouse Communities. It was one of the first developments in Florida required to save
fragile coastal wetlands and associated ecosystems (Urban Land Institute, 1981). The
development of Pelican Bay had a limited impact on the wetlands themselves (approximately 94
acres in total with about 78 of those acres located in the northwestern corner of the property)
leaving the mangrove forest intact and preserved around the bays. As mitigation for these
wetland impacts, the 35 acre beach park was donated to Collier County.
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT) -
Pelican Bay Services Division
September 3, 2013
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Approximate extent of Clam Bay Estuary system.
Development landward of the mangroves required a stormwater management system designed to
spread runoff along the eastern edge of the Clam Bay estuary (Collier County Report 1996). A
four to six foot high and 2 1/2 mile long berm separates the developed portion of Pelican Bay
from the estuary lying to the west of the development, but numerous culverts through the berm
discharge water to a swale system along the eastern perimeter of Clam Bay. The eastern edge of
Pelican Bay is about 12-14 feet above sea level at US 41, sloping in an east-west direction to
about 2 feet near the berm. Six drainage basins operate on a gravity system to slowly move
surface water into the receiving area of Clam Bay.
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
September 3, 2013
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Approximate locations of Drainage Basins within the Pelican Bay Development(photo is oriented with east up and
north to the left).
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT) -
Pelican Bay Services Division
September 3,2013
Natural History
Prior to development, the entire coastline of south Florida would have resembled the Clam Bay
system with meandering mangrove lined waterways buffering sandy barrier islands and
terrestrial communities. Unique within the moderately developed coastal community of Collier
County, Clam Bay is a valuable resource for wildlife (particularly juvenile marine species and
birds) as well as residents and visitors to the area who enjoy the recreational opportunities the
system offers such as kayaking, fishing, walking, swimming, bird watching, beach going, and
others.
The system is a mixture of mangrove-lined tidal creeks,mangrove forests, shallow bays and tidal
passes, seagrass beds, tidal flats, sandy beaches and brackish interior wetlands. A man-made
water management berm now divides natural and developed portions where historically
mangrove forest would have transitioned gradually into the mesic coastal hammocks and upland
pine scrubs that made up the now developed portions of the Pelican Bay community.
A brief overview of these important habitat types, their key characteristics and value is provided
in the Resource Description Section of this Plan.
Pass History -
Historically, Clam Pass was a small part of a large system of waterways extending from Lee
County to Doctors Pass. A limited amount of small boating activities took place within this area.
The construction of Vanderbilt Beach Road in the early 1950's cut off any navigation from the
north from what is presently called Vanderbilt Lagoon. Tidal connection with Vanderbilt Lagoon
was eventually severed as well. Later, the construction of Seagate Drive limited the amount of
tidal flow from the south,the waterway presently called Venetian Bay which connects to Doctors
Pass
Prior to the surrounding development, the natural stormwater (rain run-off) flow in this area was
by sheet flow in a southwesterly direction towards the Inlet. The stormwater flow pattern has
since been modified in direction, volume, and timing by the use of retention/detention basins,
primarily in the Pelican Bay development area.
The Clam Pass opening has moved over its lifetime up and down the shoreline, influenced by
major storm events and by man's alteration of the tidal prism and drainage basin that feeds the
Pass. A detailed discussion of the Pass is provided in the Coastal Processes Element of this Plan.
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
September 3, 2013
3.0 Historical Overview
Original land use, development history, die-off and restoration work.
To properly understand and successfully implement proposed management objectives, actions
and events which have lead to the current situation in Clam Bay should be described. This
chapter starts off with a time-line to most clearly portray the system in its historical context. It is
intended as background information and as a factual recount based on personal experiences and
comments, press reports, published and unpublished reports. The chapter finishes with an
overview of the mangrove die-off including causes, and the work that was undertaken as part of
the 1998 Clam Bay Restoration and Management Plan to restore the system.
Time Line
1920
A dirt road is built by Forest Walker running from the north-east to south portion of Pelican Bay,
a forerunner of US 41.
1950
With 6,000 residents of Naples, Clam Bay is part of a connected system of barrier islands,
mangrove passes and waterways. The orientation of the beaches and passes would have changed
seasonally and with storms
Late 1950's
Vanderbilt Road is constructed severing connection with the Wiggins Pass system to the north.
1958
Seagate Drive is constructed as the Parkshore community is developed. Flow is blocked into
Venetian Bay to the south.
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Circa 1960 Aerial Photograph Circa 1958 Aerial Photograph
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT) -
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September 3, 2013
1972
Tri-County Engineering produces reports:
• An Ecological Study of the Clam Pass Complex is published by Humm&Rehm
• Hydrographic Investigation of the Clam Bay System
Coral Ridge-Collier Properties, Inc. (a partnership between Westinghouse and Collier Properties)
acquired the property and initiated development of Pelican Bay.
1974
Pelican Bay Improvement District is formed to manage common property in Pelican Bay and
provide for long term sustainable infrastructure.
1976
Three, bi-directional 24-inch culverts are placed under Seagate Drive to provide hydrologic
connection to Venetian Bay.
Report`Environmental Assessment for Development Approval" is prepared for Pelican Bay.
Clam Pass closed in and then was re-opened by dragline.
1977
Pelican Bay Planned Unit Development is approved and construction commences.
1977-1979
Gee & Jensen Hydrographic Engineers conduct a series of tidal studies within the system and
distribute"A hydrographic study of Clam Bay system" in 1978.
1978
Tropical Bio-Industries produce a report: Carbon Flows in portions of the Clam Pass estuarine
system.
Ecological assessment work by Tropical Bio-Industries for permitting of the north-west fill area,
notes a small area of stressed and dead mangroves close to Upper Clam Bay.
1979
Environmental Assessment of the northwest fill area is distributed.
Tropical Bio-Industries produce biological reports:
• A comparative study of the water and carbon flows of Upper Clam Bay
• Invertebrate Population Studies in the vicinity of Upper Clam Bay
1981
Clam Pass closed in was re-opened by dragline.
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
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1982
Clam Pass preserve is dedicated to Collier County.
1983
Tropical Bio-Industries produce biological reports:
• Fish populations of tidal ponds west of Upper Clam Bay
1986
Collier County constructs a 2,900' boardwalk to provide access across Outer Clam Bay to the
county park, south of Clam Pass.
1988
Clam Pass closes twice, first in the spring and again in the late fall after Tropical Storm Keith
(November 23, 1988).
1989
Small areas of stressed and dying mangroves are noted by residents in the basin west of Upper
Clam Bay and east of The Strand in Bay Colony. A DNR interdepartmental memo highlights
cause of the stress as "the lack of adequate water circulation resulting from the closure of Clam
Pass".
First emergency dredging permit received from DNR to re-open clogged Clam Pass, following
memo by David Crewz to the DNR highlighting problems and danger if the pass was not re-
opened.
1990
Pelican Bay Improvement District comes under Collier County as the Pelican Bay Services
Division.
1992
The area of dead mangroves is reported at 7 acres.
1994
20 acres of mangroves are reported dead.
1994
Clam Bay is approved by the Board of County Commissioners as Collier County's first Natural
Resource Protection Area(NRPA).
1995
Emergency dredging permit issued allowing opening of the pass, but no work farther back than
600 feet.
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1996
Permits to open Clam Pass received from DEP and USACE and work completed in April. In
summer and fall blasting and hand excavation was permitted and completed in 1997.
1996
Mangrove die-off area estimated at 50 acres.
1997
Clam Pass dredged again under modification to 1996 Permits.
1998
Ten year permits received from DEP and USACE for dredging Clam Pass and the interior
channels and Seagate culverts with associated monitoring work and storm and freshwater
studies.
1999
Dredging work associated with the CBRMP is completed in the spring by Ludlum Construction
Company.
Ellicott Series 370HP Pumping Sand out of Clam Pass (1999)
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1999
Staff at The Conservancy of Southwest Florida commences a 3-5 year study of mangroves,
surface water level and elevation within the mangrove die-off area.
2002
Maintenance dredging of Clam Pass flood shoals completed to improve tidal circulation.
2004
Hurricane Charley comes ashore about 50 miles north of Clam Pass. A lot of sand was
redistributed but the pass did not close. Extensive limb and leaf loss was documented within the
mangrove forest.
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
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2005
Hurricane Wilma comes ashore about 30 miles south of Clam Pass. More limb and leaf loss is
noted. Pass does not close.
Hurricane damaged mangroves along bay 2005 Same mangroves along bay 2007
2007
Maintenance dredging of Pass and entrance channel completed to 1999 specifications.
2008
Tropical Storm Fay comes ashore about 30 miles south of Clam Pass. The area received over 10
inches of rainfall. Pass not affected.
2009
1998 DEP and ACOE permits for maintenance of the pass expire after 1-year extensions.
2010
Permits issued to continue maintenance of hand-dug flushing channels throughout the system.
2011
White mangrove die-off was observed in central portion of the system and found to be caused by
a bark beetle infestation of trees that had suffered cold temperature stress.
2012
New interior makers are installed. Markers include canoe trail identifiers and informational
signage.
The mouth of the pass moves to the north and threatens the Pelican Bay Beach Facility. The
northern shoreline of the pass is temporarily reinforced with the installation of concrete barriers.
The pass closes in December
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
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September 3, 2013
2013
A single event permit is issued to dredge Clam Pass. In March dredge work is completed and the
pass is open.
Development of a new Management Plan is initiated through stakeholder input and multiple
public meetings.
1995 Die-off and Related Causes
The majority of the original die-off occurred within the northernmost black mangrove areas of
the system. Three defined processes of the black mangrove forest are applicable to the Clam
Bay ecosystem. These three processes are briefly reviewed here are:
Salt balance: Salt is available to the black mangrove forest from a variety of sources,but
normal tidal exchange is the most important. Black mangroves can tolerate slightly higher
sediment salinity than the other two mangrove species but can be affected adversely by an excess
accumulation of salt. In a natural setting,toxic accumulation of salt is usually prevented by
dilution and leaching due to rainfall and washout on outgoing tides. Accordingly, the transport
of dissolved and diluted salt back to the Gulf is critical to the health of the black mangrove.
Organic matter budget: Like the salt balance,the organic matter budget is intimately related to
the flushing component of the tidal cycle. It is generally recognized that even in the best of
circumstances only 60-86% of the decomposing matter generated by a mangrove forest is
consumed on site. The balance has to be exported. This export is in the form of highly
fragmented or dissolved organic matter fractions and as such is also dependent upon tidal
flushing.
Water budget: Water enters the Clam Bay system through rainfall, freshwater run-off and
through the influx of seawater. It leaves via evaporation from water surfaces, transpiration from
leaves and tidal out-flow to the Gulf. Since evapotranspiration rates within mangrove forests are
relatively low it follows that the forest must freely drain or else water logging occurs that quickly
leads to stress and mortality.
Rainfall in South Florida contributes about 53 plus inches of water per year and most of that
occurs in the wet season. Additional freshwater inputs to this system occur from groundwater
flow and from irrigation in the developed portions of Pelican Bay. The irrigation amounts to
about 26 to 28 inches (on average) of rainfall every year but can vary widely due to weather
conditions. In a perfect world this irrigation component would be entirely taken up by the soil
and plants but in these non-perfect conditions, it is expected that some run-off is also generated
due to the irrigation. When this amount is added to normal rainfall, the export capacity of the
system to the Gulf becomes critical, especially when considered in the context of the need to
transport the organic matter and salt described above.
• CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
September 3, 2013
The combination of these mangrove species and other intertidal vegetation makes mangrove
forests extremely productive natural resources,but their productivity depends on the right
combination of tidal "flushing" (movement of water and suspended material in and out of the
estuarine wetland) and freshwater run-off to maintain their ability to function. The freshwater
input dilutes the high salinity of marine waters, thereby reducing the effort needed by the
mangrove to exclude or excrete salt. This allows more of the trees' energy to be directed to
normal growth and maintenance.
Tidal flushing also allows nutrients to be distributed within the forest and provides for the
transportation of dead leaves, twigs, etc. As these materials decay,they become food for marine
life. It is this mangrove detritus which is consumed by the many organisms at the base of the
food chain and which in turn create the next level of the food chain necessary to support the fish
populations that characterize the mangrove community. It is the combined interaction of fresh
and salt water through tidal flushing that is critical to the ability of the mangrove forest to sustain
itself. It follows therefore, that anything that materially disrupts the maintenance of the flushing
component threatens the long term viability of the mangrove forest itself
According to detailed field surveys performed in the early 1970's (Tropical BioIndustries
Company and Gee and Jenson 1978)tree densities ranged from 726 to 7,580 per acre and
maximum canopy height was 39 feet. Within the black mangrove dominated basin forests,
16% of the trees or 8.8 acres of dead black mangroves were reported in the 1978 document.
Dead and stressed mangroves were again reported for Clam Bay in 1989 when David W.
Crewz, a biologist with the Florida Marine Research Institute,was asked to inspect Clam
Pass Park by Mary Ellen Hawkins,then a Collier County representative to the legislature
(letter to Don Duden dated April 3, 1989). Mr. Crewz concluded that the"dead and stressed
mangroves were caused by lack of adequate water circulation resulting from the closure of
Clam Pass.... allowing toxin and salt buildup."
Westinghouse Consultants, Inc., employees in February 1992 noted additional mangrove
die-offs, north of Clam Pass Park on the west side of Upper Clam Bay. This area was
inspected by Dr. Eric Heald, a consultant to WCI, and reported to WCI in April 1992, as
probably due to hypersalinity, although 1991 was an above average rainfall year. The same
conclusion was reached by Robin Lewis of Lewis Environmental Services, Inc., after an
inspection in May 1994. At this time the die-off area was approximately 6 acres. A
widespread mortality of mangroves in Florida Bay was also reported in the summer of 1991
(Yarbro et al. 1994) and it was attributed, in part,to natural drought conditions and unusual
tidal inundation patterns.
After above average rainfall in the summer of 1995, The Conservancy, Inc.'s staff and
residents in Pelican Bay reported additional mangrove deaths which continued through 1995
and 1996. The total area of the die-off through July 1999 was around 50 acres.
The death of trees occurred around hyper saline ponds and is consistent with conditions caused
by periods of excessive inundation of freshwater followed by periods of continuous dry down,
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
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September 3, 2013
particularly where the mechanism for flushing is impaired. (Lugo 1976). During the period
immediately preceding the observed die off, and during the periods following, Clam Bay
received record amounts of rainfall. This rainfall, when coupled with an admittedly impaired
circulation system and intermittent pass closure, resulted in water levels that were high enough
for a long enough period of time to adversely impact the mangroves.
It should be noted, however,that the death of trees around hyper saline ponds is a process that is
now occurring for a variety of reasons elsewhere in Florida and the Caribbean and is not
necessarily evidence that the forest is in a state of irretrievable decline. The presence of new
seedlings confirms that these conditions may well be able to return. (Lugo 1976;). Presently the
die-off areas appear to be recovering as a result of the restoration work done to date.
The remedial efforts described later in this Plan, in particular the dredging of Clam Pass and the
opening of several of the impacted tidal creeks,have had the desired effect of improving the
circulation of tidal waters within the system. (Humiston, pers. comm. 2007).
Restored Characteristics of Clam Bay
In assessing a variety of alternatives to the restoration of Clam Bay,the original need was not so
much to restore the system to a mangrove forest(although that remained the primary goal) as it
was to stabilize and restore the system as a thriving natural resource. It was recognized that with
changes to naturally induced flushing rates and hydrological regimes the mangroves would likely
adjust by altering zonation patterns, species compositions, rates of growth and mortality, etc.
(CBRMP 1998).
Clam Pass
The single most important thing that has been done to restore the health of the Clam Bay system
is to improve the total tidal flushing capacity of the system. (Humiston& Moore 2003; Lewis
2007; Turrell 2007). As has been discussed earlier, the tides in the upper reaches of Clam Bay
were weak and variable. Runoff from rainfall further reduced the interior tidal range and during
Tackney's field study,total rainfall of approximately 4 inches in three days was sufficient to
flood Upper Clam Bay to such an extent that tidal fluctuation was completely eliminated.
During Hurricane Charlie, storm surge and rainfall far exceeded this 4 inch level and yet Upper
Clam Bay was experiencing tidal fluctuations the following day. The restoration efforts of
dredging the pass, dredging the interior channels, and construction of the network of flushing
cuts throughout the original die-off area proved very effective in maintaining the tidal exchange
and drainage capability of the system.
In Outer Clam Bay, where the channel leading to Clam Pass is relatively short, the tidal range
was only 50% of its potential value. This diminished exchange capacity was a direct result of the
constricted nature of the inlet and its adjacent interior channels.
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During flood tides, sand is carried into the pass by tidal currents and settles out of the water
column where the current drops below the magnitude necessary to maintain the sediment in
suspension. At Clam Pass this has resulted in the gradual accumulation of sediment in the
channels interior to the inlet. This sedimentation process reduces the hydraulic efficiency of the
channels and results in diminished tidal ranges for the interior bays.
In 1998, when the restoration activities commenced, the channels immediately interior to the
pass were so constricted that even when the pass was excavated, the interior tides remained
muted. Efforts to maintain the pass in an open condition were dramatically improved by
enlarging the dredge area to include not only Clam Pass,but also the critical areas of the adjacent
interior channels. This action not only augmented the volume of tidal flow through Clam Pass,
but also reduced the likelihood of inlet closure during adverse weather conditions. Currently,
Outer Clam Bay's tidal range has been improved by 4 to 6 inches as a result of the dredging
activities and the increased self-maintenance capability of the inlet.
The single most critical causative factor of the Upper Clam Bay mangrove die off and lack of
natural regeneration of mangroves was the relative absence of adequate tidal flushing, or tidal
pumping, typically measured in terms of tidal amplitude and its frequency of occurrence
(CBRMP 1998, Roessler pers. comm. 2004). Tidal pumping refers to the hydraulic change in
water pressure in mangrove sediment that is controlled largely by tidal activity. When rising
tides force a rise in the water table in the sediment beneath mangroves, gasses(e.g., carbon
dioxide, hydrogen sulfide, methane, ammonia) and various fluid wastes (including refractory and
labile dissolved organic matter) are expelled from the sediment. Since some of these compounds
are toxic,particularly hydrogen sulfide, their frequent(daily to twice daily) removal is critical to
the health of the mangroves. Conversely, on falling ties and a drop in the sediment water table,
gases (e.g., oxygen) and nutrients present in the over-lying water are drawn into sediment. The
frequent renewal of sediment oxygen is particularly important because it is required in normal
root respiration which, if stopped, causes mortality. Thus in the absence of tidal pumping,
metabolic wastes accumulate in the sediment and it eventually turns toxic and anoxic, meaning
no oxygen. It is important to note that this critical process has nothing to do with the salinity, or
absence thereof, or with the presence of absence of surface and subsurface water.
Because the tidal amplitude was wholly inadequate mainly due to the restricted tidal circulation
and tidal pumping within the Clam Bay system, and between the Clam Bay system and the Gulf
of Mexico, the correction provided by the restoration activities has been critical to the creation
and management of conditions required to foster mangrove growth in addition to maintaining
water quality within Clam Bay.
Interior Tidal Creeks
It is also important to recognize the interrelationship between the maintenance of Clam Pass and
the maintenance of the interior connecting tidal creeks. The tides in the upper reaches of Clam
Bay were weak and variable. In the absence of rainfall, the tidal ranges of the Upper and Inner
Clam Bay's were on the order of 15%to 19% of the Gulf tidal range. Run-off from rainfall
quickly flooded the upper bays and further reduced the interior tidal range. The reduced tidal
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
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September 3, 2013
range in the interior bays were due to the restrictive condition of the interior connecting tidal
creeks. (Tackney 1996; CBRMP 1998). These restrictions not only super-elevated the average
water surface elevation within the bays but also retarded drainage. The problem was exacerbated
by the addition of pulsed water from the stormwater management system, which by design stores
water in its detention/retention areas and then allows it to discharge into the bays. The
constricted condition of the interior tidal creeks coupled with the additional water being
continuously discharged into the bay elevated the water surface elevation in the upper bays and
contributed to extending the periods of flooding beyond tolerance levels that mangroves can
accommodate,particularly the black mangrove. (Turrell 1995; Tackney 1996; Lewis 2007).
The second restorative action of the plan required that three sections of interior tidal creek be
dredged open and in some cases enlarged in order to augment the transfer of water. Removing
the constrictions present in these waterways allowed the increased inflow of water as well as
enhancing the outflow of water. These adjustments enhanced the flood tide ingress and allowed
for increased volume to exit on the ebb tide. The results of this work showed an almost doubling
of the tidal amplitude in the upper reaches of the system. While the amplitude is still far below
the levels seen in the Gulf, it is still much improved from the pre-restoration levels.
Interior Flushing Channels
The third restorative action of the original plan was the creation of a network of flushing cuts
within the mangrove forest and die-off areas. These cuts were dug by hand throughout the
system the purpose of which was to connect depressional zones and areas subject to ponding to
the main waterways of the system. This allowed for tidal water to flow into and out of the forest
areas much easier and further enhanced the tidal exchange that could occur.
Biological monitoring work over the past ten years has conclusively shown that the improved
drainage, which has been achieved through excavation of these small flushing cuts within the
forest basin, has greatly alleviated ponding and contributed to the observed improvements in the
Clam Bay mangrove community.
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
•
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4.0 Resource Description and Assessment
SOILS
Based on the National Resource Conservation Service (NRCS) "Soil Survey of Collier County
Area, Florida" (NRCS, 1998) there are 8 different soil types (soil map units) present on the
project lands. Two of the units are associated with the NRPA while the remaining units are
associated with the upland developments. The following sub-sections provide a brief description
of each soil map unit identified within the Clam Bay and Pelican Bay areas. Information is
provided about the soil's landscape position(i.e. its typical location in the landscape on a county-
wide basis), the soil's profile (i.e. textural composition and thickness or depth range of the layers
or horizons commonly present in the soil), and the soil's drainage and hydrologic characteristics.
In addition, the hydrologic soil group is also identified for each soil. There are 4 groups that are
used to estimate runoff from precipitation. Soils are grouped according to the rate of infiltration
of water when the soils are thoroughly wet and are subject to precipitation from long-duration
storms. The four groups range from A (soils with a high infiltration rate, low runoff potential,
and a high rate of water transmission) to D (soils having a slow infiltration rate and very slow
rate of water transmission).
It is important to understand that where the soil survey shows mapping units named for soil
series, they represent the dominant undisturbed soils in that landscape that existed
predevelopment. They do not recognize or appropriately interpret the drastically disturbed
nature of urban landscapes created after the Soil Survey was completed.
The soils occurring within the development areas are as follows:
Immokalee fine sand(Map Unit#7)
Landscape position—Pine Flatwoods.
This is a nearly level, poorly drained soil. Individual areas are elongated and irregular in shape,
and range from 10 to 500 acres. The slope is 0 to 2 percent. Typically, the surface layer is black
fine sand about 6 inches. The subsurface layer is light gray fine sand to a depth of about 35
inches. The subsoil is fine sand to a depth of about 58 inches; the upper part is black, the middle
part is dark reddish brown, and the lower part is dark brown. The substratum is pale brown fine
sand to depth of about 80 inches. The permeability of this soil is moderate. The available water
capacity is low. In most years, under natural conditions,the seasonal high water table is between
6 to 18 inches of the surface for 1 to 6 months. In other months, the water table is below 18
inches and recedes to depth of more than 40 inches during extended dry periods. Rarely is it
above the surface. Hydrologic group is B/D.
Natural vegetation consists of South Florida slash pine, saw palmetto, wax myrtle, chalky
bluestem, creeping bluestem and pineland threeawn.
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Urban land(Map Unit#32)
Landscape position—Urban Areas
Urban land consists of areas that are 75 percent or more covered with streets, buildings, parking
lots, shopping-centers, highways, industrial areas, airports and other urban structures. Small
areas of undisturbed soils are mostly lawns, vacant lots, playgrounds and green areas. The
original soils in some areas have been altered by filling, grading and shaping. Urban land is
nearly level except for some parking areas that are sloped to drain off water. Individual areas are
usually rectangular in shape and range from 10 to 1200 acres. The slope is 0 to 2 percent. The
depth of the water table varies with the amount of fill material and the extent of artificial
drainage within any mapped area. Hydrologic group is not applicable.
Urban Land-Immokalee-Oldsmar limestone substratum Complex (Map Unit#34)
Landscape position—Urban Areas
These nearly level poorly drained soils are on urban areas of the county. Individual areas are
blocky to irregular in shape and range from 20 to 500 acres. The slope is 0 to 2 percent.
Typically, urban land consists of commercial buildings, houses, parking lots, streets, sidewalks,
recreational areas, shopping centers and other urban structures where the soil cannot be
observed. In 90 percent of the area mapped in this unit; urban land makes up about 45 percent,
Immokalee soils makes up about 35 percent and Oldsmar soil makes up about 20 percent of the
map unit. The soils occur as areas so intricately mixed or so small that mapping them separately
is not practical. The Immokalee and Oldsmar soils may or may not have been filled or reworked
to accommodate Urban land uses. The permeability of the Immokalee is moderate and the
available water capacity is low. The permeability of the Oldsmar soil is moderately slow and the
available water capacity is low. In most years, under natural conditions, the seasonal high water
table is between 6 to 18 inches of the surface for 1 to 6 months. In other months, the water table
is below 18 inches and recedes to a depth of more than 40 inches during extended dry periods.
Most areas have had drainage systems installed to help control the seasonally high water table
and runoff. Hydrologic group is B/D.
Urban Land Aquents Complex, organic substratum (Map Unit#35)
Landscape position—Urban Areas.
This unit consists of soil materials that have been dug from different areas in the county and have
been spread over the muck soils for coastal urban development. Individual areas are blocky to
irregular in shape and range from 20 to 300 acres in size. The slope is 0 to 2 percent. Typically,
Urban land consists of commercial buildings, houses, parking lots, streets, sidewalks,
recreational areas, shopping centers and other urban structures where the soil cannot be
observed. The depth of this fill material varies from 30 to more than 80 inches. Muck of various
thickness underlies the fill material, with mineral material under the muck. The depth to the
water table varies with the amount of fill material and the extent of artificial drainage within any
mapped area. Hydrologic group is not applicable.
Udorthents shaped(Map Unit#36)
Landscape position—Golf courses and athletic fields.
These nearly level to undulating, somewhat poorly to moderately well drained soils are on golf
courses and adjacent areas where soil material has been mechanically altered and shaped.
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Individual areas are elongated and irregular in shape and range from 40 to 640 acres in size. The
slope is 1 to 6 percent. A common profile has mixed grayish brown and pale brown fine sandy
loam to a depth of 18 inches. The next layer is gray gravelly fine sand to a depth of about 37
inches. The subsoil is light brownish gray fine sandy loam to a depth of about 47 inches.
Limestone bedrock is at a depth of about 47 inches. This map unit is comprised of many altered
soils with widely differing chemical and physical characteristics. Some areas maybe comprised
entirely of fine sands to a depth of 80 inches. The depth to the water table varies with the
amount of fill material and the extent of irrigation and artificial drainage within any mapped
area. Hydrologic group is D.
Satellite fine sand(Map Unit#39)
Landscape position—Coastal ridges.
This nearly level, somewhat poorly drained soil is on low-lying coastal ridges. Individual areas
are elongated and irregular in shape and range from 10 to 400 acres. The slope is 0 to 2 percent.
Typically, the surface layer is gray sand about 3 inches thick. The substratum is light gray to
white fine sand to a depth of about 80 inches. Permeability is very rapid. The available water
capacity is very low. In most years, under natural conditions, the seasonal high water table is at
a depth of between 18 to 10 inches for 1 to 4 months. In other months, the water table is below
40 inches. Rarely is it above the surface. Hydrologic group is C.
Natural vegetation consists of Florida rosemary, sand live oak, south Florida slash pine,
sawpalmetto,prickly pear, pineland threeawn and creeping bluestem.
The soils occurring within the NRPA are as follows:
Durbin and Wulfert mucks, frequently flooded(Map Unit#40)
Landscape position—Mangrove swamps.
These level, very poorly drained soils are in tidal mangrove swamps. Individual areas are
elongated and irregular in shape and range from 50 to 1000 acres. The slope is 0 to 1 percent.
Typically,the Durbin soil has a surface soil of dark reddish brown to black muck about 63 inches
thick. The substratum is dark gray fine sand to a depth of about 80 inches. Typically, the
Wulfert soil has a surface soil of dark reddish brown to black muck about 40 inches thick. The
substratum is dark gray fine sand to a depth of 80 inches. The permeability of the Durbin soil is
rapid and the available water capacity is high. The permeability of the Wulfert soil is rapid and
the available water capacity is moderate. The water table fluctuates with the tide and is within
12 inches of the surface most of the year. The soil is subject to tidal flooding. Hydrologic
group is D.
Natural vegetation consists of red, white and black mangroves.
Canaveral-Beaches Complex (Map Unit#42)
Landscape position—Beaches and low coastal ridges
This map unit consists of the nearly level, moderately well drained Canaveral soil on low ridges
and of beaches. Individual areas are elongated and irregular in shape and range from 20 to 300
acres. The slope is 0 to 2 percent. Typically, the Canaveral soil has a surface layer of dark
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brown fine sand about 4 inches thick. The substratum is brown to light gray fine sand mixed
with shell fragments to a depth of about 80 inches. Typically, beaches consist of sand mixed
with shell fragments and shells. Beaches are subject to frequent wave action. The permeability
of the Canaveral soil is rapid to very rapid. The available water capacity is very low. In most
years, the seasonal high water table is at a depth of between 18 to 40 inches for 1 to 4 months. In
other months, the water table is below 40 inches. This soil is subject to tidal flooding under
severe weather conditions. Hydrologic group is C.
Natural vegetation consists of Australian pines, sea oats, sea grape, cabbage palm, Brazilian
pepper and salt grasses.
Insert Soils Map when Available
CLIMATE
Clam Bay's climate falls within tropical classification, more precisely the tropical wet and dry or
savanna type, Aw under the Koppen system. As a consequence,there are essentially two seasons
are experienced. The wet season occurs in the summer and the dry season occurs in the winter.
Typical rainfall and temperature data is provided in Tables 4.1 and 4.2.
In the summer the center of the trade winds shift north and moisture-laden breezes blow from the
east or south-east. In winter, the trade winds shift southward and the winds are less constant.
Weather, is then more influenced by fronts advancing from the northwest. This brings cooler
conditions, although temperatures never reach freezing, due to the fact that they are being
moderated by the surrounding waters. Cold fronts are typically preceded by winds from the
southwest, which clock to the west then northwest as the front passes, with strong winds of 20-25
knots and cooler air. In general terms, winds are predominantly southeast during the summer
and northeast during the winter.
Historical meteorology for Clam Bay is based on data collected for 30 years (from 1981 to 2010)
from the Naples Municipal Airport by the Florida Climate Center (NOAA & FSU). The
following charts present meteorological statistics for temperature and precipitation.
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
September 3, 2013
1981-2010 TEMPERATURE AND PRECIPITATION NORMALS GRAPH
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O Precip(in) 0 Min Imp(CF) 0 Avg Tmp(°F) 0 Max Imp(`F)
Temperature
The monthly average temperatures range from 64.5°F to 83.2°F. The lowest monthly minimum
temperature is 54.2°F while the highest monthly maximum temperature is 91.2°F. The data
reflects a temperate climate with a narrow fluctuation in air temperature.
Precipitation
Annual rainfall for the Naples Municipal Airport NOAA station is documented at 51.89 inches.
The data in the table indicates the highest rainfall occurs during the summer, the months of June,
July, August, and September.
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1981-2010 TEMPERATURE AND PRECIPITATION NORMALS CHART
0 Precip (in) 0 Min Imp (CF) 0 Aug Imp (CF) 0 Max Imp (`F)
January 1.85 54.2 64.5 74.7
February 2.10 56.8 66.9 76.9
March 2.38 60.0 70.0 79.9
April 2.36 63A 73.3 83.2
May 3.16 68.5 78.2 87.8
June 8.82 73.9 81.9 89.9
July 7.27 74.9 83.1 91.2
August 8.58 75.3 83.2 91.0
September 7.69 74.8 82.4 89.9
October 4.19 70.0 78.5 86.9
November 2.04 62.9 72.1 81.2
December 1.45 57.0 66.8 76.6
Winds
Winds are predominantly easterly throughout the year, but with a tendency to become
northeasterly from October to April and southeasterly from May to September. Wind speeds, not
including storm events are, on average, below 10 knots. During the winter months when fronts
move through, for a day or two at a time, winds out of the northwest to northeast may increase to
about 25 knots.
Sea breeze
As the land surface around Naples and Clam Bay heats it in turn heats the air above it. The
warm air is less dense and tends to rise creating a lower air pressure over the land than the water.
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
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September 3, 2013
The cooler air over the water then flows inland creating a sea breeze. In the evening the reverse
occurs and the cooler air over the land will flow back toward the water creating a land breeze.
The incoming sea breeze acts as a lifting mechanism, resulting in the warmer air rising up to
higher altitudes. This creates cumulus clouds that begin to build which leads to the development
of afternoon showers and thunderstorms in the area.
Storms
Naples and Clam Bay specifically are within the Atlantic Tropical Cyclone basin. This basin
includes much of the North Atlantic, Caribbean Sea, and the Gulf of Mexico. On average, six
(6) to eight (8) tropical storms form within this basin each year. The hurricane season lasts from
June 1st to December 1St. The formation of these storms and possible intensification into mature
— — -- hurricanes takes place over warm tropical and subtropical
{ Safflr-Simpson Hurricane Scale
Category Wind speed Storm surge waters. Eventual dissipation or modification, averaging seven
mph ft (7) to eight (8) days later, typically occurs over the colder
(km1h) (m) waters of the North Atlantic or when the storms move over
land and away from the sustaining marine environment.
7 ;y TAW ,
Due to the destructive nature of these storms, landfall can
Three 111-130 9-12
(178-209) (2.7-33) result in significant damage to upland development and
96-110 6-8 facilities from storm surge, waves, and wind. A good example
Two
(154-177) (1•e-2.4) ' of this would be Hurricane Wilma which formed in 2005.
One 74-95 4-5
(119-153) (1.2-1.5)
Additional classifications
Tropical 39-73 OA A tropical storm is defined by maximum sustained winds from
storm (63-117) (o ` 35-64 knots (40-74 mph). A hurricane has maximum
Tropical 0-3e sustained winds that exceed 64 knots (74 mph). Hurricanes are
depression ({)) �
i classified into different categories according to the Saffir-
Simpson scale. Hurricanes can also spawn severe weather such as tornadoes as they move
inland.
The table below lists the number of tropical storms and hurricanes that passed through or near
Naples over the past 20 seasons including 1992 through 2012 as reported by the National
Oceanic and Atmospheric Administration (NOAA) Coastal Services Center and Hurricane City
(www.hurricanecity.com). Analysis of the available information indicates that Naples, on
average, is brushed or hit by a tropical storm or hurricane once every 2.71 years and is directly
hit once every 7.05 years.
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Table Number of Named Storms Passing through or near Naples
Year #of Storms Names
1992 1 Andrew
1993 0
1994 1 Gordon
1995 1 Jerry
1996 0
1997 0
1998 1 Mitch
1999 1 Harvey
2000 0
2001 0
2002 0
2003 0
2004 1 Charley
2005 1 Wilma
2006 0
2007 0
2008 1 Fay
2009 0
2010 0
2011 0
2012 0
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September 3, 2013
NATURAL COMMUNITIES
Mangroves
Mangroves are salt tolerant trees that grow in tidal areas of the tropics and are legally protected
for their ecological value, with such functions as;
• Providing habitat for marine and terrestrial wildlife.
• Protecting coastal areas from storm surges and coastal erosion.
• Acting as a natural filter for land based freshwater run-off.
• Forming the basis of an incredibly productive estuarine food chain which includes many
commercially valuable species.
Three species are common in Florida as far north as Cedar Key and St. Augustine, where cold
winter temperatures limit their range. All have special biological adaptations to cope with salt
and unstable, mucky, low oxygen soils that result in a tidal, hence continually waterlogged
environment. The dominance of mangroves in tidal areas is a function of these adaptations and
hence their ability to out-compete other wetland plants.
Red mangroves (Rhizophora mangle) are recognized by their tangle of reddish looking prop
roots, long cigar shaped seedlings (the propagules which can be seen in the summer months) and
their large, pointed evergreen leaves. They are typically the most seaward of the three species
with the prop roots and vertical drop roots providing support, small pores on the trunks called
lenticels allow oxygen exchange via air as the waterlogged soils become rapidly oxygen
depleted. Salt is excluded from the plants cells through a process called ultra-filtration in the
roots. The characteristic propagules germinate on the parent tree and drop and float for up to a
year, finally becoming heavier at one end so that when encountering a suitable substrate they are
ready to root upright. Good tidal flushing is essential for healthy development of red mangroves,
to prevent the build up of toxic metabolic waste products in the mangrove soils. The mass of
prop and drop roots forms extensive surface area under water for attachment of sessile, filter
feeding marine species (such as sponges, tunicates and mollusks) as well as hiding places for
juvenile fish. Birds, butterflies, insects and mammals find home and food within the canopy.
Fall and breakdown of Red mangrove leaves is the start of productive estuarine food webs.
Black mangroves (Avicennia germinans) are typically found slightly further inland and key
identification features include the snorkel like pneumaptophores which radiate upwards out of
the soil from the base of the trunk, a grey-black rough bark and slightly pointed, oval leaves
which are silvery with salt deposits on the undersides. The pneumatophores play an important
role in oxygen exchange and unlike the Red mangroves, which keep salt, out of body cells, the
Black mangrove excretes salt onto the backside of the leaves. They are also reliant on adequate
tidal exchange but lack the supporting prop roots that typify the Red mangrove. Small white
flowers and small lima bean shaped propagules are apparent during the summer months and, on
falling from the parent tree, float for a short period and establish in the mucky soil.
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
September 3, 2013
invertebrates that scavenge detritus or, in the case of many bivalve mollusks, extend siphons at
high tide and filter vast quantities of water. Birds such as a variety of herons, ibis, egrets and
spoonbills pick through the sediment for the invertebrate food sources.
Sandy Beach
In addition to the 35-acre Clam Pass Beach Park, south of the pass, sandy beach also extends
north all the way to Wiggins Pass. Shorebirds feed on marine invertebrates such as coquina
clams and mole crabs at the water's edge and beaches are crucially important habitat for nesting
sea turtles. Coastal plants colonizing the dunes are key players in trapping windblown sand and
preventing coastal erosion as the first defense against heavy winds and surge of tropical storms.
Species common on the beaches of the Clam Bay system include; Sea oats (Uniola paniculata),
Seagrape (Coccoloba uvifera), Cabbage palm (Sabal palmetto), Buttonwood (Conocarpus
erectus) and Railroad vine (Ipomoea pes-caprae).
Brackish Marsh
At the interface between forested mangrove areas and the water management berm are
depressional areas that have become colonized by aquatic freshwater plants such as cattails
(Typha latifolia), Carolina willow (Salix caroliniana), Bulrush (Scirpus californicus),
Needlerush (Juncus romerianus) and Leather fern (Acrostichum danaeifolium). Wildlife such as
otters (Lutra canadiensis), alligators (Alligator mississippiensis), various turtles, and wading
birds can be commonly observed. These areas require regular maintenance to prevent the spread
of nuisance and exotic plant species and ensure optimal functioning of the water management
system.
Add FLUCFCS Exhibit when available
Tidal Passes
The Clam Bay system was originally part of a larger tidal system connected to the Gulf of
Mexico by three tidal inlets; Wiggins Pass, Clam Pass and Doctors Pass. During the 1950's and
60's this system was isolated from adjacent bays by the construction of Seagate Drive to the
south and the construction of Vanderbilt Beach Road to the north. The practical effect was to
leave Clam Pass as Clam Bay's only connection to the Gulf. The exchange of seawater between
Clam Bay and the Gulf is critical to the ability of the mangrove forest to export organic matter,
as well as excess salt and freshwater. It also supplies oxygen rich water and nutrients from the
Gulf. The greater the tidal amplitude (or tidal prism) the greater the benefit to the mangroves —
more needed resources are delivered and more wastes are removed. Conversely, in the absence
of surface water circulation or tidal activity, mangroves slowly die due to deleterious changes in
the sediment: 1) in the absence of oxygenated water, the sediments become anaerobic or anoxic,
and 2) metabolic wastes and hydrogen sulfide accumulate in the anoxic sediment (CBRMP,
1998).
• CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
September 3, 2013
Tides in the Gulf of Mexico are mixed, with the norm being two high tides and two low tides
experienced per day and normal amplitude (range) of approximately 2 feet. The highest tides
(springs) are experienced twice per lunar month at full and new moons when the gravitational
pull on the earth's surface waters is greatest. Neap tides also occur twice per lunar month when
the planetary (gravitational) influences of earth,moon and sun are perpendicular.
Add Tidal Exhibit from Clam Bay Monitoring Report
It can be seen that the health of mangrove forests is directly related to the efficiency of the tidal
passes. These are dynamic creeks whose location vary annually and, as illustrated by Clam Pass,
can periodically close such as has happened at least four times in the last 25 years (Turrell 1995;
Tackney 1996).
Tidal creeks are passageways for fish and marine invertebrates between the open waters of the
Gulf and the protected embayments of Clam Bay. Manatees and turtles may also use the passes.
Scouring action of the fast flowing tide generally prevents colonization by seagrasses and other
benthic plants and the substrate is typically sand and shell with the finer sediments carried in
suspension and deposited just outside the mouth of the pass (the ebb shoal delta) or to the interior
of the system on the incoming(flood)tide.
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
PelicanBay Services Division
September 3, 2013
,f� ,11 UPPER CLAM BAY
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Tide Gauge Locations
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
September 3, 2013
Hardbottom Communities
Another important marine habitat marginally associated with the estuarine system is the hard
bottom reef community found just seaward of Clam Pass. In about 10-15 feet of water a variety
of sponges, stony corals, gorgonians, fish and associated invertebrates can be found within a
system of rocks and ledges. Outcroppings of similar habitat type occur along the length of
Collier County and are a little known resource of regional significance.
PLANT SPECIES -List to be added based on FLUCFCS Mapping
LISTED SPECIES
Smalltooth Sawfish (Pristis pectinata)
A juvenile smalltooth sawfish was observed in 2008 in the connector creek between Inner and
Outer Clam Bays. Smalltooth sawfish are found in the tropical and subtropical Atlantic Ocean.
In the western Atlantic they have historically ranged from New York to Brazil, including the
Gulf of Mexico and Caribbean Sea. Habitat destruction and overfishing have succeeded in
eradicating the smalltooth sawfish from the majority of its former range. Consequently, it
survives in small pockets throughout its current range. The last remaining population in U.S.
waters is off south Florida, a small remnant of a population that once ranged from New York to
Texas.
This sawfish primarily occurs in estuarine and coastal habitats such as bays, lagoons, and rivers.
It does at times occur in deeper waters, however, and may make crossings to offshore islands. It
can tolerate freshwater. This fish is easily recognized by its flattened body and wing-like
pectoral fins. The mouth is located ventrally, the eyes are positioned dorsally. The "saw" is
approximately 25% of the body's total length. It is widest at the base, with teeth more broad than
long, and spaced apart. The tips of the teeth are sharp, becoming blunt over time. Dorsally, it is
brownish or bluish gray body with a white underside. The maximum length recorded is 24.7 feet
(7.6 m); however, a length of 18 feet (5.5 m) is considered average. The average lifespan for the
smalltooth sawfish is unknown.
On April 1, 2003 the U.S. National Marine Fisheries Service placed the smalltooth sawfish on
the Endangered Species List, making it the first marine fish species to receive protection under
the Endangered Species Act. Florida has also designated critical habitat areas to further protect
its habitat.
Mangrove Rivulus (Rivulus marmoratus)
This small fish has not been identified within the Clam Bay system in previous surveys or field
work but the mangrove habitat is appropriate and they could be present in the upper reaches of
the mangrove forest. The mangrove rivulus is primarily a saltwater or brackish water species,
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
September 3, 2013
with limited occurrence in freshwater. Within the Everglades and along Florida's west coast, this
fish occurs in stagnant, seasonal ponds and sloughs as well as in mosquito ditches within
mangrove habitats.The mangrove rivulus is able to survive in moist detritus without water for up
to 60 days during periods of drought, anaerobic, or high sulfide conditions.
This fish can reach a maximum size of 2 inches (5 cm) in length, however it is more commonly
observed at lengths between 0.4-1.5 inches (1.0-3.8 cm). The head and body are maroon to dark
brown or tan, with small dark spots and speckling on the body, particularly the sides. The dorsal
surface is always darker than the creamy ventral surface. The color of the body is reflective of
the habitat, with light coloration in areas of light colored sediments and darker coloration in
environments with dark leaf litter substrates. A large dark spot surrounded by a band of yellow is
located at the upper base of the caudal fin in hermaphroditic individuals. Males lack this dark
spot and have a red-orange cast to their flanks and fins.
The mangrove rivulus was once listed as a threatened species in the Gulf of Mexico. However,
recently additional surveys have revealed the existence of numerous populations. In Florida it
has been downlisted to a species of special concern. In 1999, it was submitted by the National
Marine Fisheries Service as a candidate for protection under the Endangered Species Act. As of
yet, it has not been officially listed as endangered or threatened.
The main threat to the survival of the mangrove rivulus is habitat degradation and destruction as
well as exposure to pollutants. Disturbances that alter salinity and temperature as well as
vegetation cover may also reduce naturally occurring populations.
Loggerhead Sea Turtle (Caretta caretta)
Loggerhead sea turtles have been documented nesting on beaches within the Clam Bay NRPA.
Loggerheads are circumglobal, occurring throughout the temperate and tropical regions of the
Atlantic, Pacific, and Indian Oceans. They are the most abundant species of sea turtle found in
U.S. coastal waters. In the Atlantic, the loggerhead turtle's range extends from Newfoundland to
as far south as Argentina.
During the summer, nesting occurs primarily in the subtropics. Although the major nesting
concentrations in the U.S. are found from North Carolina through southwest Florida, minimal
nesting occurs outside of this range westward to Texas and northward to Virginia. Adult
loggerheads are known to make extensive migrations between foraging areas and nesting
beaches. During non-nesting years, adult females from U.S. beaches are distributed in waters off
the eastern U.S. and throughout the Gulf of Mexico, Bahamas, Greater Antilles, and Yucatan.
Loggerheads were named for their relatively large heads, which support powerful jaws and
enable them to feed on hard-shelled prey, such as whelks and conch. The top shell (carapace) is
slightly heart-shaped and reddish-brown in adults and sub-adults, while the bottom shell
(plastron) is generally a pale yellowish color. The neck and flippers are usually dull brown to
reddish brown on top and medium to pale yellow on the sides and bottom.
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September 3, 2013
In the southeastern U.S., mating occurs in late March to early June and females lay eggs between
late April and early September. Females lay three to five nests, and sometimes more, during a
single nesting season. The eggs incubate approximately two months before hatching sometime
between late June and mid-November.
Loggerheads occupy three different ecosystems during their lives: beaches (terrestrial zone),
water (oceanic zone), and nearshore coastal areas ("neritic" zone). Because of this, NOAA
Fisheries and the U.S. Fish and Wildlife Service (USFWS) have joint jurisdiction for marine
turtles, with NOAA having the lead in the marine environment and USFWS having the lead on
the nesting beaches.
The loggerhead turtle was first listed under the Endangered Species Act as threatened throughout
its range on July 28, 1978. In September 2011, NMFS and U.S. Fish and Wildlife Service listed
9 Distinct Population Segments of loggerhead sea turtles under the ESA. The population in our
Northeast Atlantic Ocean Segment is listed as endangered. The agencies are currently proposing
Critical Habitat designations on several areas which contain a combination of nearshore
reproductive habitat, winter area, breeding areas, and migratory corridors. The Clam Pass NRPA
is contained within the LOGG-N-27 segment of this proposed critical habitat area.
Gopher Tortoise (Gopherus polyphemus)
Gopher tortoises and their burrows are found along the coastal strand portions of the Clam Pass
NRPA. The range of the tortoise includes southern portions or Alabama, South Carolina,
Louisiana, Mississippi, and Georgia as well as most of Florida.
Gopher tortoises are one of the few species of tortoise that dig burrows. These burrows can be up
to ten feet deep and 40 feet long, and are as wide as the length of the tortoise that made it. In
addition to providing the tortoise a home, it has been documented that as many as 350 other
species also use the burrows including the indigo snake, Florida mouse, gopher frog and
burrowing owl.
Gopher tortoises can live 40 to 60 years in the wild and average 9 to 11 inches in length. These
tortoises are superb earth-movers, living in long burrows from 5 to 45 feet long and up to 10 feet
deep that offer refuge from cold, heat, drought, forest fires and predators. The burrows maintain
a fairly constant temperature and humidity throughout the year and protect the gopher tortoise
and other species from temperature extremes, drying out, and predators. The mating season
generally runs from April through June and gestation for the eggs is between 80 and 100 days.
The shell or "carapace" of the gopher tortoise is mostly brownish gray and the underside of the
shell, or "plastron," is yellowish tan. Their front legs are shovel-like which helps them when
digging their burrows.
The gopher tortoise has been regulated in Florida since 1972 and has been fully protected since
1988. Despite the afforded protection, gopher tortoise populations throughout the state have
declined. As a response to the continuing decline of the species, a new management plan was
drafted and approved in September 2007 as a precursor to reclassifying the gopher tortoise from
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Pelican Bay Services Division
September 3, 2013
a "species of special concern" to a "threatened species." The threatened status was approved and
went into effect on November 8,2007.
West Indian Manatee
Manatees have been sighted on numerous occasions within the Clam Pass NRPA boundaries.
Manatees can be found in shallow, slow-moving rivers, estuaries, saltwater bays, canals, and
coastal areas—particularly where seagrass beds or freshwater vegetation flourish. Manatees are
a migratory species. Within the United States, they are concentrated in Florida in the winter. In
summer months, they can be found as far west as Texas and as far north as Massachusetts, but
summer sightings in Alabama, Georgia and South Carolina are more common.
Manatees are large, gray aquatic mammals with bodies that taper to a flat, paddle-shaped tail.
They have two forelimbs, called flippers, with three to four nails on each flipper. The average
adult manatee is about 10 feet long and weighs between 800 and 1,200 pounds. They eat a large
variety of submerged, emergent, and floating plants and can consume 10-15% of their body
weight in vegetation daily. Because they are mammals, they must surface to breathe air. They
rest just below the surface of the water, coming up to breathe on an average of every three to five
minutes. It is believed that one calf is born every two to five years, and twins are rare. The
gestation period is about a year. Mothers nurse their young for one to two years, during which
time a calf remains dependent on its mother.
Protections for Florida manatees were first enacted in 1893. Today, they are protected by the
Florida Manatee Sanctuary Act and are federally protected by both the Marine Mammal
Protection Act and the Endangered Species Act
OTHER LISTED SPECIES THAT MAY NEED TO BE ADDRESSED (American Crocodile
(Crocodylus acutus), Florida Black Bear (Ursus americanus floridanus))
ANIMAL SPECIES
The following lists of species have been observed within the Clam Pass NRPA and adjacent
Pelican Bay development areas.
Aquatic Invertebrates–Add from Conservancy Report
Fish
Common Name Scientific Name
Atlantic needlefish Strongylura marina
Barracuda Sphyraena barracuda
Bay anchovy Anchoa mitchilli
Blacktip Shark Carcharhinus limbatus
• CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
September 3, 2013
Blue crab Callinectis sapidus
Cowfish Acanthostracion quadricomis
Flounder Paratichthys alb!gutta
Gray snapper Lutjanus griseus
Great barracuda Sphyraena barracuda
Gulf killifish Fundulus grandis
Inshore Iizardfish Synodus foetens
Killifish spp. Fundulus spp.
Leatherjacket Oligoplites saurus
Longnose killifish Fundulus simitis
Mangrove snapper Lutjanus griseus
Mullet Mugil cephalus
Mutton snapper Lutjanus anatis
Needlefish Strongylura marina
Permit Trachinotus falcatus
Pigfish Orthopristus chrysoptera
Pinfish Lagodon rhomboides
Pipefish Syngnathus spp.
Puffer Sphoeroides parvus
Sailfin molly Poecilia latipinna
Sand perch Diplectrum bivittatum
Scaled sardine Harengula pensacolae
Sea robin Prionotus scitulus
Sheepshead Archosargus probatocephal
Sheepshead minnow Cyprinodon variegatus
Silver jenny Eucinostomus gula
Smalltooth Sawfish Pristis pectinata
Snook Centropomus undecimalis
Spot Leiostomus xanthurus
Spotfin mojara Eucinostomus argenteus
Spotted seatrout Cynoscion nebulosus
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
September 3, 2013
Tidewater silverside Menidia peninsulae
Triggerfish Batistes capriscus
White grunt Haemulon plumierii
Whiting Menticirrhus tittoratis
Reptiles and Amphibians
Common Name Scientific Name
Banded water snake Nerodia faciata faciata
Black racer Coluber constrictor
Common garter snake Thamnophis sirtalis
Eastern coachwhip Masticophis flagellum
Mangrove salt marsh water snake Nerodia clarkii
Mud snake Farancia abacura
Red rat snake Elaphe guttata guttata
Ring-necked snake Diadophis punctatus
Yellow rat snake Elaphe obsoleta
American Alligator Alligator mississippiensis
Brown anole Anolis sagrei
Eastern glass lizard Ophisaurus ventralis
Green anole Anolis carolinensis
Southeastern five-lined skink Eumeces inexpectatus
Cuban treefrog Osteopilus septentrionalis
Eastern narrow-mouthed toad Gastrophryne carolinensis
Eastern spadefoot toad Scaphiopus holbrookii
Giant marine toad Bufo marinus
Green treefrog Hyla cinerea
Oak toad Anaxyrus quercicus
Southern leopard frog Lithobates sphenocephalus
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
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September 3, 2013
Southern toad Bufo terrestris
Squirrel treefrog Hyla squirella
Chicken turtle Deirochelys reticularia
Florida box turtle Terrapene carolina bauri
Florida softshell turtle Apalone ferox
Gopher tortoise Gopherus polyphemus
Green sea turtle Chelonia mydas
Loggerhead sea turtle Caretta caretta
Pond slider Trachemys scripta
Striped mud turtle Kinosternon baurii
Birds
COMMON NAME SCIENTIFIC NAME
American avocet Recurvirostra americana
American coot Fulica americana
American kestrel Falco sparverius
American oystercatcher Haematopus palliatus
Anhinga Anhinga anhinga
Bald eagle Haliaeetus leucocephalus
Barred owl Strix varia
Belted kingfisher Megaceryle alcyon
Black skimmer Rynchops niger
Black vulture Rynchops niger
Black-and-white warbler Mniotilta varia
Black-bellied plover Pluvialis squatarola
Black-crowned night heron Nycticorax nycticorax
Black-necked stilt Himantopus mexicanus
Blue jay Cyanocitta cristata
Blue-gray gnatcatcher Polioptila caerulea
Boat-tailed grackle Quiscalus major
Brown pelican Pelecanus occidentalis
Brown thrasher Toxostoma rufum
Budgerigar Melopsittacus undulatus
Caspian tern Hydroprogne caspia
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
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September 3, 2013
Cattle egret Bubulcus ibis
Chuck-will's-widow Caprimulgus carolinensis
Common grackle Quiscalus quiscula
Common ground-dove Columbina passerina
Common moorhen Gallinula chloropus
Common nighthawk Chordeiles minor
Common snipe Gallinago gallinago
Common tern Sterna hirundo
Common yellowthroat Geothlypis trichas
Double-crested cormorant Phalacrocorax auritus
Dowitcher long-billed Limnodromus scolopaceus
Dowitcher short-billed Limnodromus griseus
Downy woodpecker Picoides pubescens
Dunlin Calidris alpina
Eastern screech owl Megascops asio
Eurasian collared dove Streptopelia decaocto
European starling Sturnus vulgaris
Fish crow Corvus ossifragus
Forster's tern Sterna forsteri
Glossy ibis Plegadis falcinellus
Gray catbird Dumetella carolinensis
Great blue heron Ardea herodias
Great crested flycatcher Myiarchus crinitus
Great egret Ardea alba
Great horned owl Bubo virginianus
Greater yellowlegs Tringa melanoleuca
Green heron Butorides virescens
Green-winged teal Anas crecca
Herring gull Larus argentatus
Hooded merganser Lophodytes cucullatus
House sparrow Passer domesticus
Killdeer Charadrius vociferus
Laughing gull Leucophaeus atricilla
Least sandpiper Calidris minutilla
Limpkin Aramus guarauna
Little blue heron Egretta caerulea
Loggerhead shrike Lanius ludovicianus
Magnificent frigate bird Fregata magnificens
Mangrove cuckoo Coccyzus minor
Merlin Falco columbarius
Mocking bird Mimus polyglottos
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
September 3, 2013
Mottled duck Anas fulvigula
Mourning dove Zenaida macroura
Muscovy duck Cairina moschata
Northern cardinal Cardinalis cardinalis
Northern gannet Morus bassanus
Northern parula Parula americana
Northern waterthrush Seiurus noveboracensis
Osprey Pandion haliaetus
Painted bunting Passerina ciris
Palm warbler Dendroica palmarum
Peregrine falcon Falco peregrinus
Pied-billed grebe Podilymbus podiceps
Pilleated woodpecker Dryocopus pileatus
Piping plover Charadrius melodus
Prairie warbler Dendroica discolor
Purple gallinule Porphyrula martinica
Red knot Calidris canutus
Red-bellied woodpecker Melanerpes carolinus
Red-breasted merganser Mergus serrator
Reddish egret Egretta rufescens
Red-shouldered hawk Buteo lineatus
Red-tailed hawk Buteo jamaicensis
Red-winged blackbird Agelaius phoeniceus
Ring-billed gull Larus delawarensis
Robin Turdus migratorius
Roseate spoonbill Platalea ajaja
Royal tern Sterna maxima
Ruby-throated
hummingbird Archilochus colubris
Ruddy turnstone Arenaria interpres
Sanderling Calidris alba
Sandwich tern Sterna sandvicensis
Semipalmated plover Charadrius semipalmatus
Snowy egret Egretta thula
Spotted sandpiper Actitis macularia
Swallow-tailed kite Elanoides forficatus
Tri-colored heron Egretta tricolor
Turkey vulture Cathartes aura
Western sandpiper Calidris mauri
White ibis Eudocimus albus
White pelican Pelecanus erythrorhynchos
Willet Catoptrophorus
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
September 3, 2013
semipalmatus
Wood stork Scolopax minor
Yellow-bellied sapsucker Sphyrapicus varius
Yellow-crowned night
heron Nyctanassa violacea
Yellow-rumped warbler Dendroica coronata
Yellow-throated warbler Dendroica dominica
Mammals
COMMON NAME SCIENTIFIC NAME
Virginia opossum Didelphis Virginia
Eastern mole Scalopus aquaticus
Brazilian free-tailed bat Tadarida braziliensis
Big brown bat Eptesicus fuscus
Nine-banded armadillo Dasypus novemcinctus
Marsh rabbit Sylvilagus palustris
Eastern gray squirrel Sciurus carolinensis
House mouse Mus musculus
Roof rat Rattus rattus
Gray fox Urocyon cinereoargenteus
Black bear Ursus americanus
Raccoon Procyon lotor
River otter Lutra canadensis
Feral domestic cat Felis catus
Bobcat Lynx rufus
West Indian manatee Trichechus manatus
Bottle-nosed dolphin Turciops truncatus
HYDROLOGY
The most critical factor for mangrove maintenance is the hydrological regime, sometimes
referred to as the surface water or surficial hydrology. This is because the surficial hydrology
has both horizontal and vertical components and provides key ecological functions to the
mangrove forest.
With respect to the horizontal component, incoming water(both tidal and surface water run-off)
into a mangrove wetland brings with it nutrients, dissolved oxygen, and marginally lower salt
concentrations. Conversely,the outgoing water leaving a mangrove wetland (through tidal
exchange)removes metabolic waste products (e.g., carbon dioxide and toxic sulfides) and excess
salt. The vertical component refers to incoming water that percolates down into the sediment
CLAM PASS NRPA MANAGEMENT PLAN(DRAFT)
•
Pelican Bay Services Division
September 3, 2013
and root zone, and the sediment drainage, on a falling tide, which removes metabolic wastes and
excess salt.
It is the inflow and outflow of sea water that is critical to the ability of the mangrove forest to
manage these two ecological functions and as such dissipate salts, organic matter and freshwater.
It follows that anything that affects the system and alters the ability of the system to perform
these functions,will, in most instances, cause stress to the system and, at some point in time,
result in the death of the system, or portions of it.
The Clam Bay system was originally part of a larger tidal system connected to the Gulf of
Mexico by three tidal inlets; Wiggins Pass, Clam Pass and Doctors Pass. (Turrell 1996). During
the early 1950's this system was isolated form adjacent bays by the construction of Seagate
Drive to the south and the construction of Vanderbilt Beach Road to the north. The practical
effect was to leave Clam Pass as Clam Bay's only connection to the Gulf.
In 1976 culverts were placed under Seagate Drive to provide some exchange from Venetian Bay
(a residential sea wall bay system) and improve water quality in the Doctors Pass area. One-way
valves were placed on the pipes in 1999 but there was not enough head differential to operate the
valves and they ended up acting as plugs instead. In October, 2002 these valves were removed
to promote more flushing and water exchange in this southern portion of the system.
Hydrologic studies indicate that the tidal flushing capacity of Clam Bay prior to the restoration
dredging was limited and almost insignificant in Upper Clam Bay. The preliminary
hydrographic assessment of the Clam Bay system prepared by Tackney &Associates, Inc.
(August 1996) demonstrated rather dramatically that there was a significant reduction in tidal
range between the middle boardwalk and Inner Clam Bay. Tackney described the flow in that
area as "measurably reduced" and"very inefficient". This connecting tidal creek is the key
conduit for tidal input and outflow to the northern reaches of the Clam Bay system. And its
constriction and the ancillary constriction of tributaries connection to it, impact the quantity and
quality of the flushing that can occur in Inner and Upper Clam Bay.
As noted earlier, it is the daily rise and fall of the tide and the exchange of seawater between
Clam Bay and the Gulf that are critical to the ability of the mangrove forest to export both
organic matter, and excess salt and freshwater as well as receive oxygen rich water and nutrients.
The greater the tidal amplitude (or tidal prism)the greater the benefit to the mangroves—more
needed resources are delivered and more wastes are removed. Conversely, in the absence of
surface water circulation or tidal activity, mangroves can become stressed and, in certain
instances,rapidly die due to deleterious changes in the sediment or water levels. The
consequence is that the root systems wither and eventually the whole tree dies. Note that the
tidal exchange mechanism that is critical to the health of the mangrove forest was, within this
ecosystem, seriously constrained. (Turrell 1995). Another key aspect of the surficial hydrology
is the vertical location of the water level elevation relative to the mangrove sediment elevation.
Specifically, the mean low water (tide) elevation has to be sufficiently lower than the mangrove
sediment elevation in order for mangrove sediments to drain during low tide. A persistent high
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surface water elevation stops sediment drainage and results in anoxic sediment and the
accumulation of toxic waste products.
It should be observed that the black mangrove forest does not require the kind of intense flushing
that is more typical of the red mangrove systems in order to maximize its productivity.
However,the total absence of meaningful exchange was certainly a contributor to the significant
degradation of the mangrove system within Clam Bay. (Tackney 1996; Lewis pers. comm.
2008).
In this context Tackney observed that even in the absence of rainfall,the average water surface
elevations for the inner and upper bays were higher than the average surface elevation for the
Gulf. Analysis of the tidal data indicated that average water surface elevations in the Inner and
Upper Clam Bays were both elevated above the average Gulf water surface elevation by
approximately 0.2 feet. This indicated that the tidal range in Inner and Upper Clam Bays was
muted and that the system was receiving significant additional water through runoff and
restricted capacity to drain additional inflow. In fact, during portions of the Tackney study no
tidal fluctuation was noted in the Upper Clam Bay and only marginal tidal effects were observed
in Inner Clam Bay.
The reduced tidal ranges were also accompanied by relatively large phase lags. The phase lag is
the average time delay measured in hours and minutes between the occurrence of slack(high or
low) water in the Gulf of Mexico and the measurement stations. It is affected by both the
distance between measurement stations and the amount and quality of hydraulic resistance of the
connecting channel. The longer the distance and the higher the resistance,the more pronounced
one would expect the phase lag to be. In the upper bays, high and low waters generally occurred
over three hours later than the Gulf tides.
These conditions indicate that the tidal creeks connecting the interior bays are hydraulically very
inefficient. As a result,the upper bays are prone towards extended periods of flooding as a result
of freshwater runoff and the inability of the system to drain efficiently. During Tackney's field
studies of May 1996, rainfall of approximately 4 inches in three days was adequate to flood the
Upper Clam Bay above high tide levels and sustain this flooded condition for over two days.
Accordingly,he concluded that the creeks and bays that serve to connect the Inner and Upper
Bays were significantly less efficient in the ebb tide stage than they were in the flood stage.
Studies undertaken by both Lewis Environmental Services, Inc. and Turrell &Associates, Inc.
would support this conclusion. (Turrell 1995).
Finally, an additional attribute of the system that is directly related to tidal prism and the quantity
of inflow and outflow is the question of inlet stability. Inlet stability refers to a tidal inlet's
capacity to adequately scour out deposited sediments and prevent inlet closure. For a given wave
environment, inlet stability is governed primarily by the volume of water(tidal prism)carried by
the inlet. To remain stable, an inlet must have the characteristic that a temporary constriction in
cross sectional area produces an increase in current velocities adequate to scour out the
constriction. To function without mechanical intervention, the system must generate sufficient
volume off water on the ebb tide to scour out the inlet naturally, otherwise the inlet will, over
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time, continue to close. This is particularly true during periods of high wave activity and low
tidal ranges. (Turrell 1995; Tackney 1996). The five closures of Clam Pass that have occurred
in the past twenty-five years indicate that stability of Clam Pass is marginal. (Turrell 1995;
Tackney 1996).
Freshwater Component
Under predevelopment conditions, much of the area's rainfall was held on the surface of the land
in sloughs and other low areas. This water would either slowly filter through the soil to recharge
the shallow aquifer or move through the mangrove community to the bay. Less than ten inches
of the approximately 53 inch average rainfall is estimated to have been lost from the uplands east
of Clam Bay as surface runoff. The storage capabilities of the land thus moderated surface
flows,preventing extremely high flow rates during the rainy season and serving to maintain
surface flow and groundwater flow during the dry season. (FDER 1981).
In 1977 the Pelican Bay Planned Unit Development was established by Westinghouse
Communities, Inc. The development contains a mixture of residential, retail, commercial and
recreational facilities and lies east of Clam Bay. As a condition of development, Clam Bay,the
area that lies west of the Pelican Bay and consists of approximately 530 acres of mixed
mangrove forest and wetlands was designated as the Pelican Bay Conservation Area. As such, it
was designated for conservation but with limited recreational access. This area was eventually
given to Collier County and is currently classified as a Natural Resource Protection Area
(NRPA).
The development of Pelican Bay had limited fill impact to the Clam Bay system,but it did
modify the pattern of freshwater entering the Clam Bay system. (Wilson, Miller et.al. 1996).
The stormwater management system as designed, permitted and implemented at Pelican Bay
employs a series of detention ponds, swales and culverts to regulate the discharge of run-off into
Clam Bay. Discharge occurs almost continuously along the eastern perimeter of the
conservation area. Run-off from the northern end of Pelican Bay is collected and discharged into
Upper Clam Bay. Irrigation water for 27 holes of golf and landscaping in Pelican Bay is
approximately 3.0 MGD which approximates 26 inches per year of additional rainfall
equivalent, (Wilson, Miller et.al., 1996). When added to the average rainfall for South Florida of
approximately 53 inches per year, the local area has an effective rainfall of approximately 80
inches plus annually. This is significant, particularly when viewed in the context of predictable
storm events that have the potential for altering the amount of average rainfall entering the Clam
Bay system.
The "Pelican Bay Water Management System—Stormwater Detention Volume and Water
Budget Analysis" (Wilson, Miller, Barton&Peek, Inc. April, 1996) describes the water
management system as being divided into six watersheds or drainage systems. Rainfall,
including irrigation, reaches the ground and either seeps into the ground or runs off to a
stormwater detention area within each system. The stormwater detention plan for Pelican Bay
has a standard,permitted design capacity to hold the first inch of stormwater during a 25-year
storm event. The stormwater is detained for flood protection and water quality treatment.
Stormwater discharge is controlled by a series of weirs designed such that the post-development
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stormwater run-off rate does not exceed pre-development rates. Stated differently, the system is
designed to discharge stormwater in the development portion of Pelican Bay in the same manner
that it discharged stormwater prior to development. The stormwater discharge exits the weir
system for a final release into Clam Bay.
Stormwater runoff from an additional 130 acres of watersheds, outside of Pelican Bay,
contributes an additional and significant volume of discharge to Clam Bay. This water
represents 7.9% of the total stormwater discharge to Clam Bay.
As the area of Pelican Bay to the east has undergone development, it has increased the
impervious surface area, with a concomitant increase in surface runoff,which is eventually
discharged to Clam Bay. The daily irrigation water volume enhances the saturation of the
uplands which reduces their ability to accommodate rainfall volume, thus effectively increasing
surface and groundwater discharge. Groundwater discharge can be commonly observed
throughout-the eastern side of Clam Bay and is discernable as a very slight sheet flow. Where
this water encounters a discharge system, even one that is not operating at peak efficiency, such
as Outer Clam Bay, excess water is effectively removed from the system. However, in the
northern section, sheet flow was not efficiently removed due to lack of flow through the forest.
Thus, it accumulated, increasing soil saturation and raising the mean water table elevation, and
apparently overwhelming the black mangrove's anaerobic soil/gas exchange mechanisms.
Mangroves in these areas became stressed and died.
WATER QUALITY—More detail to be added from annual report
During the initial environmental permitting of Pelican Bay, the agencies required water quality
testing within the Pelican Bay subdivision and the Clam Bay estuary to help evaluate the impact
of development on Clam Bay. The water quality-testing program was first implemented by
Pelican Bay Improvement District (PBID) starting in the early 1980's. In 1991, PBID became
the Pelican Bay Services Division (PBSD), a dependent Division of Collier County. PBSD
continued the testing program after 1991. PBSD is currently the responsible entity for the testing
program.
The water quality testing is performed at several sample points within Pelican Bay and Clam
Bay. The sample point locations are shown on Figure 1. There are currently ten sampling
locations within Pelican Bay and Clam Bay. Sample points W-7, W-6, W-1, North Seagate, and
Upper Clam Bay (UCB) are within Clam Bay, which are categorized as Class II waters by the
Florida Department of Environmental Protection (FDEP). The remaining five sampling points
are PB-13, E PB-13, PB-11, Glenview, and St. Lucia, are located in the stormwater treatment
portion of the property(Class III waters) within Pelican Bay.
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Water quality sampling is conducted within the Clam Bay system on a monthly basis. The
samples are collected by PBSD staff and transported to the Collier County Pollution Control
laboratory for processing. Parameters sampled and collected, include;
• Field pH
• Field Temperature
• Field Salinity
• Field D.O.
• Ammonia
• Carbon- Total Organic
• Chlorophyll a
• Copper* (added to the parameter suite in 2013)
• Nitrate-Nitrite (N)
• Nitrite (N)
• Nitrogen-Total Kjeldahl
• Orthophosphate (P)
• Pheophytin
• Phosphorus- Total
• Residues- Filterable (TDS)
• Silica(SiO2)
Add Sampling Station exhibit
INLET DYNAMICS— To be added from Engineer's report(s)
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5.0 Authorized Construction Activities
List of permits for work undertaken to date and relevant legal framework
Eighteen years ago, Collier County processed a permit to dredge limited areas of Clam Pass to
facilitate the movement of tidal water in and out of Clam Bay. The FDEP permit for this activity
was issued on March 28, 1996 with the companion USACOE permit being issued on April 2,
1996. The FDEP permit was modified on April 10, 1996 with the authorized work being
undertaken and completed on April 17th, 1996. The practical effect of implementing this Permit
was to reopen the Pass, but it was clear that without a more comprehensive strategy, this effort,
standing alone, would not revitalize the Clam Bay ecosystem.
A permit to improve the channel flow within defined areas of the Clam Bay system by a
combination of blasting and hand excavation was issued on June 26, 1996. The work was
undertaken and completed in two segments. The first channels were opened in August 1996 and
the second channels were opened in November 1996. The results of these two initiatives were
positive in that measurable improvements in tidal flow were discernible and with that have come
improved conditions for natural revegetation.
A permit was issued on January 5, 1997 to construct a portable pump and pipe system as an
interim measure to divert freshwater within the Clam Bay system to the Gulf while a more
permanent solution contemplated by the construction of an outfall structure was reviewed.
Although this plan was never implemented and is no longer considered, it envisioned two pumps
that would be operational when the water surface elevation within Clam Bay exceeded a
specified threshold. The plan anticipated the direct discharge of excess water into the Gulf with
the expectation that this system would augment the natural discharge through the tidal
mechanism after severe storm events.
Subsequently, Collier County authorized the pursuit of a ten-year permit to allow the County, or
its designee (whichin this case was the Pelican Bay Services Division), to maintain Clam Pass in
an open condition. The application, as filed, did not address any other issues affecting the
operational characteristics of Clam Bay and essentially mirrored the 1996 Permit described in the
first paragraph above. This permit was issued in 1998 and has been the guiding document for the
maintenance activities undertaken in the Clam Pass system since then.
It is anticipated that new DEP and ACOE permits will be applied for and implemented in
conjunction with this new Management Plan. The permit duration will be coordinated with both
DEP and the Corps of Engineers but is anticipated to be for a minimum period of five (5) years
but hopefully for a longer duration such as the previous 10-year permits. The permits will allow
for ongoing maintenance and enhancement activities to continue along with occasional, modest
removal of material by dredging within a discreet area of Clam Pass in order to maintain the
existing tidal regime within the system. Any changes to the submitted dredging scope or other
new management initiatives will be reviewed and permitted (as necessary) under separate
applications. Additional investigations which may be undertaken at a later date to look at, for
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example, additional faunal investigations, more in-depth water quality concerns, dredging
outside of previously approved templates, or other issues that may arise as a result of stakeholder
discussions could also necessitate additional permitting. This Management Plan is specifically
tasked to maintain the improvements and benefits already realized and to insure that the
restoration success observed to date is continued.
The following list contains more details related to existing and historical permits issued for the
Clam Pass system.
Permit Details
Department of Environmental Regulation Construction Permit/Certification No.: 11-50-3769
Date of Issue: May 23, 1979
Expiration Date: May 15, 1984
Project Description: To provide construction sites for residential development in a planned
community by: placing approximately 700,000 cy of clean upland fill material onto
approximately 94 plus acres of submerged lands of waters of the state landward of the line of
mean high water.
Department of the Army Corps of Engineers Permit No.: 00754929
Date of Issue: November 18, 1981
Expiration Date: November 18, 1984
Project Description: This permitted the filling of 75± acres of mangrove wetlands north, east and
west of Upper Clam Bay and south of Vanderbilt Beach Road.
Department of Environmental Regulation Modification Permit No.: 11-50-3769
Date of Issue: December 23, 1981
Expiration Date: November 18, 1986
Project Description: This modification extended the expiration date of the permit to November
18, 1986.
Department of the Army Corps of Engineers Permit No.: 79K-0282
Date of Issue: August 2, 1983
Expiration Date: November 18, 1986
Project Description: This was an extension of the permit authorizing the filling of 75± acres of
mangrove wetlands north, east and west of Upper Clam Bay and south of Vanderbilt Beach
Road, plus approximately 2 acres of mangroves at the existing Collier County beach access at
Vanderbilt Beach Road. The request was reviewed and no objections were raised to the
proposed work schedule; therefore, the completion date of the permit was extended for 2 years
until November 18, 1986.
Department of Environmental Regulation Modification of Surface Water Management Permit
No.: 11-00065-5
Date of Issue: December 15, 1983
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Date of Expiration:
Project Description: Approved modifications to 1) Revise system V, drainage area 3. 2)
Construction and operation of water management system number VI.
Department of Environmental Regulation Permit/Certification No: 110974055
Date of Issue: September 12, 1985
Expiration Date: September 11, 1987
Project Description: To construct approximately 2900 linear feet of 10' wide public access
elevated boardwalk and pier with a 6' wide navigation access lift gate in Outer Clam Bay.
Department of Environmental Regulation Permit No.: 86IPT-20328
Date of Issue: December 18, 1986
Expiration Date: December 18, 1991
Project Description: Discharge±2.3 acres of clean fill to construct an access road.
Department of Environmental Regulation Modification Permit No.: 11-50-3769
Date of Issue: January 7, 1987
Expiration Date: December 18, 1991
Project Description: This permit modification extended the expiration date and reduced the
amount of fill in the area extending south along the coastal edge from approximately 13 acres, as
permitted,to 2.43 acres in order to construct a linear access road (for The Strand in Bay Colony).
Department of Environmental Protection Permit/Certification No: 112659015
Date of Issue: March 14, 1995
Expiration Date: March 14, 2000
Project Description: Re-establish the connection between the Gulf of Mexico to the Clam Bay
system, by dredging from the mouth of Clam Pass and spoiling the sand over an upland beach
site.
Collier County Ordinance No: 96-16
Date of Issue: April 9, 1996
Expiration Date: n/a
Project Description: To impose idle speed zones in the Clam Bay system.
Department of Environmental Protection Permit/Authorization No.:0128463-001-JC
Date of Issue: July 06, 1998
Expiration Date: July 06, 2008
Project Description: This Permit authorized activities to improve the hydrodynamics of, and thus
restore and manage, the Clam Bay ecosystem.
Department of the Army Corps of Engineers Permit No.:199602789 (IP-CC)
Date of Issue: April 1, 1998
Expiration Date: July 08, 2008
Project Description: This Permit authorized the following works: 1) Replacement of Seagate
Drive Culverts (pages 44 —49 of the CBRMP). 2) Clam Pass main channel dredging for Cuts 1,
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2, 3 and 4 (pages 49 — 65 of the CBRMP). 3) Excavation and maintenance of Interior Tidal
Creeks (pages 65 —71 of the CBRMP).
Department of Environmental Protection Permit Modification DEP Permit No.:0128463-001-JC
Date of Issue: December 15, 1998
Expiration Date: July 06, 2008
Project Description: This permit modification authorized: 1) an alternative to upland spoil
disposal area for Cut #1; 2) an increase in the width of the channel Cut #4 through Clam Pass;
and 3) alternative pipeline corridors between the dredge cuts and the disposal areas.
Department of Environmental Protection Permit Modification for Permit No: 0128463-001-JC
Date of Issue: February 16, 1999
Expiration Date: July 6, 2008
Project Description: Authorize minor revisions to the mangrove trimming procedures pursuant
to site verification.
Department of the Army Corps of Engineers Modification#1 for Permit No.:199602789 (IP-CC)
Date of Issue: February 26, 1999
Expiration Date: July 08, 2008
Project Description: This application requested a modification to: 1) discharge the dredge
material from Cut #1 to new disposal area identified as an upland parking area; 2) increase the
width of channel Cut #4; 3) remove native vegetation and excavate a portion of upland Disposal
Site #2; 4) remove native vegetation and excavate a portion of upland Disposal Site#3. Issues 1
&2 were found to be insignificant and the permit was modified. The requests regarding issues 3
&4 were not approved at this time.
Department of the Army Corps of Engineers Modification#2 for Permit No.:199602789 (IP-CC)
Date of Issue: March 08, 1999
Expiration Date: July 08, 2008
Project Description: This application requested a modification to: 1) discharge the dredge
material from Cut #1 to new disposal area identified as an upland parking area; 2) increase the
width of channel Cut #4; 3) remove native vegetation and excavate a portion of upland Disposal
Site #2; 4) remove native vegetation and excavate a portion of upland Disposal Site #3. The
proposed modification to widen channel Cut #4 is to be done without any additional seagrass
impacts. Based on the review and coordination with FWS, the permit was modified in
accordance with these requests.
Department of Environmental Protection Permit Modification for Permit No: 0128463-001-JC
Date of Issue: May 19, 1999
Expiration Date: May 28, 1999
Project Description: Re-grade beach fill material during the marine turtle nesting season to
remove pockets of fine silty material and to remove an escarpment which may interfere with
nesting marine turtles.
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Florida Fish and Wildlife Conservation Commission File No: 2003-0511-016BS for Permit No:
CO-016
Date of Issue: March 24, 2000
Expiration Date: n/a
Project Description: This Permit granted approval for placement of canoe markers in Clam Bay.
Department of the Army Corps of Engineers for Permit No: 200001076 (NW-EF)
Date of Issue: April 13, 2000
Expiration Date: February 11,2002
Project Description: Approved the installation of 32 waterway markers for a canoe trail in the
Clam Bay system.
Department of the Army Corps of Engineers Modification#3 for Permit No.:199602789 (IP-CC)
Date of Issue: May 05, 2000
Expiration Date: July 08, 2008
Project Description: This application requested modifications to the monitoring and reporting
schedule referenced on page 93 (Biological Monitoring) of DA Permit (CBRMP). The request
was to submit annual reports instead of semi-annual reports. The permit was modified as
requested.
Department of Environmental Protection Permit for Permit No: CO-732
Date of Issue: October 25, 2002
Expiration Date: October 25, 2003
Project Description: Perform dune and beach restoration, and plant salt-tolerant native dune
vegetation in association with interim maintenance dredging event.
Department of the Army Corps of Engineers Permit No.:199602789 (IP-CC) Extension
Date of Issue: May 8, 2008
Expiration Date: July 08, 2009
Project Description: This Permit authorized the extension of the expiration date for a period of
one year.
Department of Environmental Protection Permit/Extension No. 0128463-001-JC
Date of Issue: June 5, 2008
Expiration Date: July 06, 2009
Project Description: This modification extends the expiration date for a period of one year.
Department of Environmental Protection Permit No: 11-0128463-005
Date of Issue: December 17, 2010
Expiration Date: December 17, 2015
Project Description: Continue maintenance activities to the hand-dug channels in the Clam Bay
system originally permitted under Permit No. 0128463-001-JC.
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Department of Environmental Protection Permit No: 11-0295193-004
Date of Issue: November 2, 2011
Expiration Date: November 2, 2016
Project Description: Install 32 canoe trail markers and informational signage.
Department of Environmental Protection Permit No: 0296087-001-JC
Date of Issue: August 14, 2013
Expiration Date: August 14, 2022
Project Description: Restore the alignment of Clam Pass to the previously approved location and
conducting periodic maintenance dredging of a portion of the Clam Pass Channel in order to
maintain tidal exchange between Clam Bay and the Gulf of Mexico.
Department of the Army Corps of Engineers Permit No: SAJ-1996-02789 (NWP-WDD)
Date of Issue: February 28, 2013
Expiration Date: March 18, 2017
Project Description: Dredging from Clam Pass and tidal creek to restore tidal exchange into
Clam Bay.
Department of Environmental Protection Permit Modification to Permit No: 0296087-002-JN
Date of Issue: March 1, 2013
Expiration Date: August 14, 2022
Project Description: Modification to re-open Clam Pass
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Clam Bay Management Plan Amendments
Studies within the Clam Bay Estuary as well as in other similar local ecosystems are either ongoing or
expected to occur within the asked for time frame of this document. The Management Plan is not
expected to be a static document and ongoing research and data collection related to water quality,
hydrographic changes in the various areas of the system, benthic community health, mangrove
community health, exotic and nuisance vegetation control and public education will be conducted
and/or collected. Conclusions, recommendations, or alternative management activities that come about
as a result of studies conducted outside of the scope of this management plan will be examined and
considered by the Pelican Bay Services Division and its consultants. Those modification that are
found to be viable, pertinent, and economically feasible alternatives or additions allowed under the
scope of this plan will be added to the plan. Those changes in management activities or new work
items that are outside of the scope of the Plan but are considered important or practicable by the
Pelican Bay Services Division and its consultants will be submitted to DEP and the ACOE for
consideration and inclusion into this management plan.
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Clam Pass NRPA Management Plan Bibliography
1. Gee &Jensen Engineers, Architects and Planners, Inc., 1978, Hydrographic Study Clam Bay
System Collier County, Florida for Coral Ridge- Collier Properties Inc.,report.
2. Tri-County Engineering, Inc., 1971, Tidal Datum Plane Determination for the Collier
Company.
3. Davis, R.A. Jr., Gibeaut, James C., 1990, Historical Morphodynamics of Inlets in Florida:
Models for Coastal Zone Planning, Technical Paper.
4. Department of Coastal and Oceanographic Engineering, Florida Engineering and Industrial
Experiment Station,University of Florida, 1970, Proposed Navigation Entrance to Clam Bay
on Marco Island, Collier County, Marco Island Development Corporation,technical paper.
5. February 1979, Environmental Assessment Northwest Fill Area for Pelican Bay, Turrell &
Associates, Inc.,technical paper.
6. Devlin,Donna J., Gore, Robert H., Proffitt, C. Edward, 1987, Preliminary Analyses of Seagrass
and Benthic Infauna in Johnson and Clam Bays, Collier County, Florida,Natural Resources of
Collier County Florida, technical paper.
7. Devlin, Donna J., Collier County Beach Renourishment Project: A Survey of the Marine
Benthos,technical paper.
8. Heald, Eric J., Tabb, Durbin C., Roessler, Martin A., Beardsley, Gary L., Ward, Gerlad M.,
Durrance, Dallas H., Yeend, John S., 1978, Carbon Flows in Portions of the Clam Pass
Estuarine System, Collier County, Florida, Tropical Biolndustries Company and Gee and
Jenson,Engineers-Architects-Planners, Inc.,technical paper.
9. 1994, Clam Bay Natural Resources Protection Area Management Plan Draft, Collier County
Natural Resources Department,technical paper.
10. Worley, Kathy, Hennig, Markus, July 2000, Clam Bay Mangrove Projects: Interim Summary
of Statistical Results, The Conservancy of Southwest Florida, technical paper.
11. Benedict, Mark A., Harvey, Judson W., Curran,Maura E., 1983, Part 1 Beach Management
Planning and Implementation Strategies at the Local Level,Natural Resources of Collier
County Florida,technical paper.
12. Benedict, Mark A., Harvey, Judson W., Curran,Maura E., 1983, Part II The Beach in Collier
County: A Model in Southwest Florida,Natural Resources of Collier County Florida,technical
paper.
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13. Benedict,Mark A., Harvey, Judson W., Curran,Maura E., 1983, Part 3 A Resource
Management Program for the Coastal Barriers of Collier County Florida,Natural Resources of
Collier County Florida,technical paper.
14. October 1990, Collier County Sand Source and Environmental Report Phase II Hard Bottom
Characterization, Continental Shelf Associates, Inc.,technical paper.
15. Hartwell,Richard W., Hatcher, James M., Grabe, Stephen, August 1994, Clam Bay Natural
Resources Protection Area(NRPA), Collier County Environmental Services Division,
Publication Series NR-SP-94-01,technical paper.
16. Dean,R.G., O'Brien, M.P., December 1987,Florida's West Coast Inlets Shoreline Effects and
Recommended Action, Coastal and Oceanographic Engineering Department and Division of
Beaches and Shores Department of Natural Resources, technical paper.
17. Heald, E.J., Roessler M.A., Beardsley, G.L., 1979, Litter production in a Southwest Florida
Black Mangrove Community, Reprint from Proceedings of the Florida Anti-Mosquito
Association 50th Meeting, Abstract.
18. May 1970, Coastal Engineering Study of the Proposed Clam Pass Improvement, The Collier
Company,Department of Coastal and Oceanographic Engineering, technical paper.
19. Sarkar, Chiranjib K., October 1972, Hydrographic Investigation of the Clam Bay System, Tri-
County Engineering, Inc., Technical paper.
20. June 1979,A Comparative Study of the Water and Carbon Flows of Upper Clam Bay, Tropical
Biolndustries and Missimer and Associates, Inc.,technical paper.
21. Heald,Eric J., Roessler, Martin A.,December 1979, Invertebrate Population Studies in the
Vicinity of Upper Clam Bay, Collier County, Florida, Tropical Biolndustries,technical paper.
22. Heald, Eric J., July 1983, Populations of Melampus coffeus and Cerithidea scalariformis West
of Upper Clam Bay, Collier County, Florida, Tropical BioIndustries, Inc.,technical paper.
23. Heald,Eric J., July 1983, Fish Populations of Tidal Ponds West of Upper Clam Bay Collier
County, Florida, Tropical BioIndustries,technical report.
24. Crewz, David W., 1989, Clam Pass Park mangrove damage, Department of Natural Resources
Interoffice Memorandum.
25. Wanless, Harold R., Risi, J. Andrew, July 1996, Observations on Barrier Beach Stratigraphy
and Groundwater Flow in the Vicinity of the Mangrove Die Off Adjacent to the Strand, Pelican
Bay, Collier County, Florida, Collier County Natural Resources Department,technical report.
26. Wanless, Harold R., February 1975, Report on the Beaches of Naples, Florida,technical report.
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27. Hawkins, Mary Ellen, Obley, Ross P., "Pelican Bay-Visit and Revisit."Urban Land Vol. 40,
No 11., (December 1981) 21-27.
28. Lorenz, William, D. Jr., January 1996, Clam Bay NRPA Nutrient Reduction Program Draft,
technical report.
29. Scott, Will, December 1993, "Water, Water...Everywhere what you may not know about
Pelican Bay's innovative water management system." Draft-memorandum, ABB.
30. Heald, Eric J., January 1972, Investigation of Fluctuations in the Clam Bay System, Tri-County
Engineering, Inc and Tropical Biolndustries, technical report.
31. Acquaviva, Daniel J., October 1993, Responses to Development of Regional Impact Questions
Number 14 and 17 Pelican Marsh Community,North Naples, Florida,ViroGroup
Inc./Missimer Division,technical paper.
32. Davis, Richard A Jr., Gibeaut, James, January 1990, Historical Morphodynamics of Inlets in
Florida: Models for Coastal Zone Planning. Department of Geology, University of South
Florida,technical report.
33. Knapp, Michael S., Burns, Wm. Scott, Sharp, Timothy S. Preliminary Assessment of the
Groundwater Resources of Western Collier County, Florida. Technical publication#86-1.
February 1986.
34. "Modification of Permit No. 11-00065-S Pelican Bay." Pelican Bay Improvement District Staff
Report. March 1983.
35. Preliminary Hydrographic Assessment Clam Bay Systems. Tackney&Associates, Inc., August
1996.
36. Hole,Montes& Associates, Inc., Post, Buckley, Schuh& Jernigan, Inc. Water Management
Plan Construction Permit Application for Systems 4 and 5. Pelican Bay Improvement District,
September 1982.
37. Goodrick,Robert L. "Pelican Bay—Environmental Considerations,permit No. 11-00065-S."
Memorandum to file, January 15, 1982.
38. Hermanson, George H. "Proposed Modifications to Drainage Area 3, System No. V."Hole,
Montes &Associates, Inc., January 28, 1988.
39. "Modification of Permit No. 11-00065-S Pelican Bay."Pelican Bay Improvement District Staff
Report, 1983.
CLAM BAY MANGROVE MANAGEMENT PLAN
Pelican Bay Services Division
May 15, 2008
40. Florida. South Florida Water Management District. In Reply to Request for Modification of
Surface Water Management Permit No. 11-00065-S." October 19, 1978.
41. Stanley W. Hole and Associates, Inc., Post, Buckley, Schuh&Jernigan, Inc. Water
Management Plan Permit Application. Pelican bay Improvement District,April 1978.
42. Florida. Collier County Environmental Services Division Inlet Management Resources.
Bibliography.
43. Florida. South Florida Water Management District. Application No. 04718-C for Surface Water
Management Permit Staff Report. August 1978.
44. Post, Buckley, Schuh& Jernigan, Inc. Consulting Engineers and Planners. Engineering Report
Water Management System VI for the Pelican Bay Improvement District. February 1984.
45. Wilson, Miller, Barton& Peek, Inc. Pelican Bay/Clam Bay Water Management System
Contributing Areas. CAD drawings. October 1998.
46. Coral Ridge-Collier Properties, Inc. Pelican Bay A Planned Residential Community.
47. Florida. Natural Resources of Collier County Florida. Part 5 Coastal Zone Management Units:
Atlas. 1984.
48. Suboceanic Consultants Inc.Naples Beach Study Report. University of Florida Coastal
Engineering Archives. August 1980.
49. Wilson, Miller, Barton& Peek, Inc. Pelican Bay Mangrove Investigation, Pelican Bay Water
Management System-Stormwater Detention Volume and Water Budget Analyses. April 1996.
50. Continental Shelf Associates, Inc. Collier County Sand Source and Environmental Report
Phase I Hard Bottom Mapping. Coastal Engineering Consultants, Inc, October 1990.
51. Collier County Pelican Bay Services Division. Clam Bay Restoration and Management Plan.
Florida Environmental Resource and Joint Coastal Permit Application, Federal Dredge and Fill
permit Application. April 1997.
52. Missimer and Associates, Inc. Subsurface Water and Carbon Floes to Portions of the Clam Pass
Estuarine System, Collier County, Florida. Technical report, March 1979.
53. The Collier Company. Coastal Engineering Study of the Proposed Clam Pass Improvement.
Engineering and Industrial Experiment Station, College of Engineering, University of Florida.
May 1970.
54. Crewz, David W. Florida. Department of Natural Resources. Clam Pass Mangrove Damage.
Interoffice Memo, May 1989.
CLAM BAY MANGROVE MANAGEMENT PLAN
Pelican Bay Services Division
May 15, 2008
55. Wilson,Miller,Barton&peek, Inc. Figure 1 Existing Stormwater Flows on an Outgoing Tide
(Diagrammatic). Map of Clam Bay.
56. Wilson,Miller, Barton&Peek, Inc. Figure 2 Proposed Expedited Conveyance Plan of
Stormwater Flows on an Outgoing Tide (Diagrammatic). Map of Clam Bay.
57. Acquaviva,Daniel J. Site Specific Investigations to Obtain Hydrologic Information for the
Design of Horizontal Well Systems at Pelican Bay,Naples,Florida. Water Resource Solutions,
Inc., September 1999.
58. Hole, Montes &Associates, Inc. "Evaluation of an Onsite Irrigation Water Source." The
Pelican Bay Improvement District,April 1984.
59. Post, Buckley, Schuh&Jernigan, Inc. Hydrology and Geology of a Proposed New Well Field
Site in North Collier,Florida. For the Pelican Bay Improvement District, March 1978.
60. Obley,Ross P., letter to Jim Ward. July 1999.
61. Gee &Jenson Engineers, Architects &Planners,Inc. "Pelican bay System VI Drainage." April
1983.
62. Wilson, Miller, Barton&Peek, Inc. "Pelican Bay."Memo to file. May 1987.
63. Florida. "Aquatic Plant Management Annual Operations Report."Florida Department of
Environmental Protection Bureau of Aquatic Plant Management. January 1999.
64. Florida. "Agreement for Delivery and use of Treated Wastewater Effluent for Spray Irrigation."
Official record of Collier County, Florida. Interoffice Memo. August 1996.
65. Florida. Department of Environmental Protection. "Aquatic Plant Management Permit."
January 1999.
66. Davis, Richard A., Hine, Albert C., Bland, Michael J. "Midnight Pass, Florida: Inlet Instability
Due to Man-Related Activities in Little Sarasota Bay." Coastal Sediments `87, May 1987.
67. Metz, Charles. "More than Mangroves at Stake." April 1997.
68. Florida. South Florida Water Management District. "Request for Modification of Surface
Water Management Permit No. 11-00065-S." Staff Report. October 1978.
69. Florida. South Florida Water Management District. "Water Use Permit." June 1998.
CLAM BAY MANGROVE MANAGEMENT PLAN
Pelican Bay Services Division
May 15, 2008
70. Hartman,P.K. "Excavation Permit No. 59.156." Collier County Water Management
Department letter, March 1983.
71. Fox, Lloyd II. "Collier County- DW Spray Irrigation-Unrestricted Public Access (Residential)
Groundwater Monitoring."Department of Environmental Regulation, State of Florida, letter.
May 1987.
72. Florida. South Florida Water Management District. "Water Use Permit Staff Report." June
1978.
73. Florida. South Florida Water Management District. "Surface Water Management Staff Review
Summary."April 1992.
September 5,2013 Clam Bay Committee of the Pelican Bay Services Division Board
3. Discuss Draft Clam Bay Management Plan-Chapter 6(Received 9/3/2013)
Page 1 of 3
6.0 Management Plan Goals and Objectives
The following goals and objectives for the management of the Clam Pass Natural
Resource Protection Area were developed in accordance with the directives of the Collier
County BOCC and the Pelican Bay Services District. The goals and objectives were
formed in conjunction with stakeholder input and are based on the management issues
present in the preserve as well as the purposes for which the land is help in public trust.
The document goals set forth in this plan should not appreciable change over time but the
management techniques and activities proposed may be modified based on ongoing
coordination with stakeholder and user groups or when management objectives are not
being met.
Management concerns are addressed in the following sections along with the
management techniques or activities proposed for addressing those concerns. The ability
to implement specific goals or objectives presented in this plan will be based on funding
and staffing availability. The following goals were identified during the stakeholder and
PBSD committee meetings.
Goal 1 - Provide sufficient tidal exchange to maximize benefits to the estuary
while minimizing environmental impacts.
Goal 2 -Maintain and protect the native floral and faunal communities
Goal 3 -Manage and improve water quality
Goal 4 -Address recreational uses with emphasis on passive recreation
Goal 5 - Improve community awareness and involvement
GOAL 1 - Provide sufficient tidal exchange to maximize benefits to the estuary while
minimizing environmental impacts.
A. Establish appropriate metrics to determine when dredging is necessary.
Monitoring of the Pass and internal waterways will provide information to
determine when and how much dredging is necessary. Bathymetric surveys of
cross-sectional areas of the Pass, Tide gauge data, and biological indicators can all
be used to trigger dredging events as needed. Dredge for tidal exchange benefit
only, not for navigation or beach renourishment.
B. Minimize dredge footprint(s) to the least damaging practicable
alternative.
Dredging should be conducted only in those areas necessary to achieve the
desired flow improvements. Current survey data and cross sectional areas will be
examined before establishing the dredge footprint for each dredging event.
September 5,2013 Clam Bay Committee of the Pelican Bay Services Division Board
3. Discuss Draft Clam Bay Management Plan-Chapter 6(Received 9/3/2013)
N. Page 2 of 3
C. Maximize the dredge interval as much as possible while maintaining
environmental standards.
While dredging smaller amounts may be less damaging in the short term, the
potential need to dredge more often may offset that benefit. Develop a scope
which balances the tidal exchange benefits while minimizing the number of times
dredging is needed.
GOAL 2 -Maintain and protect the native floral and faunal communities
A. Establish baseline floral and faunal resource populations
Conduct floral and faunal surveys as needed to document baseline conditions and
establish parameters upon which future survey efforts can be compared.
B. Protect Listed Species
Identify listed species utilization of the NRPA. Provide buffers around nesting
activities to prevent adverse anthropogenic impacts during nesting seasons.
Increase public awareness as necessary through signage or other efforts to
minimize adverse impacts.
C. Protect and maintain vegetative communities
Regularly inspect habitats for exotic vegetation. Remove exotics when observed
without damaging integrity of native communities. Conduct periodic monitoring
of habitats to track changes over time.
D. Protect and where possible enhance wildlife utilization of the NRPA
Conduct periodic monitoring of wildlife populations within the NRPA
boundaries. Identify utilization priorities and enhance protection as needed to
insure that continues use is viable.
GOAL 3 -Manage and improve water quality
A. Insure adequate freshwater inputs
Freshwater inputs are an important factor in maintaining a healthy mangrove
system. Mangroves typically thrive in estuaries, where salt and freshwater mix.
The reduced salinities lessen the energetic burden involved in excreting or
excluding salt while the presence of some salt prohibits different aquatic
vegetation from establishing and out-competing mangrove species.
September 5,2013 Clam Bay Committee of the Pelican Bay Services Division Board
3. Discuss Draft Clam Bay Management Plan-Chapter 6(Received 9/3/2013)
Page3of3
Freshwater flows into this system provide valuable flushing activities in the
northern reaches where tidal exchange is decreased. Freshwater flows also
contribute to the Pass stability by adding outgoing flow which helps to keep the
pass open. Activities within the development area will be examined to insure that
adequate flows into the estuary are maintained.
B. Coordinate with adjacent developments to improve upstream inputs.
Adjacent developments will be made aware of the ongoing water quality
conditions of the NRPA and provided information on how they can help maintain
or improve their stormwater contributions into the system.
C. Develop a monitoring program to build on past data and provide basis by
which to make future water quality related decisions.
Develop a long term monitoring program to track water quality conditions within
the system. Include the means to track inputs into the system.
GOAL 4 -Address recreational uses with emphasis on passive recreation
A. Maintain access and required facilities for intended uses
Conduct periodic inspections of access points and visitors facilities. Conduct
trimming of vegetation as needed to maintain boardwalk access and open
waterways for canoe and kayak passage.
B. Maintain existing signage or develop new signage to educate visitors
Site specific signage can developed, or maintained where already present, to
educate visitors on plant identification and general habitat information. Also
included should be information on how to help preserve habitats and prevent
unwanted impacts to the plants and animals sharing the area.
GOAL 5 -Improve community awareness and involvement
Continue to foster stakeholder involvement through public meetings, information
dispersal, and periodic management and monitoring plan reviews.
° September 5,2013 Clam Bay Committee of the Pelican Bay Services Division Board
5. Watercraft violating County Ordinance 96-16
Page 1 of 5
fi
ORDINANCE NO.96- 16
rS. 9
AN ORDINANCE RELATING TO VESSEL CONTROL AND WATEIE-'. -,
• SAFETY IN TIIE CLAM BAY SYSTEM; PROVIDING FOR INTENT�= "
X9202122 a ND PURPOSE; PROVIDING TITLE AND CITATION;SETTING if/J. N
•
���$ e 'TII APPLICABILITY; PROVIDING FOR VESSEL SPEED
R . 111.ATlON; PROVIDING DEFINITIONS; PROVIDING )
�1 C0° PErfALTIES;PROVIDING FOR ENFORCEMENT;PROVIDING
• • Y co FOli ONFLICTAND SEVERABILITY;AND PROVIDING -';;
S``, 100.<NAN EFFECTIVE DATE. 1,
• WHEREAS, Collier County, pursuant to Section 327.60, Florida Statutes, has the legal
authority to adopt this Ordinance to impose idle speed zones on waterways in the unincorporated
areas of the County;and
WHEREAS,the Collier County Manatee Protection Plan, adopted by the Collier County
•
Board of County Commissioners on May 23, 1995,has identified the Clam Bay System as an idle
speed zone;and
WHEREAS, it is necessary that the speed and operation of vessels located in the Clam
Bay System as specified herein be controlled m order to protect manatees and their habitat;and
WHEREAS,the Clam Bay System has been designated as a Natural Resource Protection
Area in Collier County;and
WHEREAS, it is in the interest for the safety and welfare of the canoeing public,
• kayakers,and small boat operators,that certain controls and regulations be enacted to reduce risk •
and injury to the canoeing public,kayakers,and small boat operators and ensure the enjoyablity of
these natural resources by the general public.
NOW, THEREFORE, BE IT ORDAINED BY THE BOARD OF COUNTY
COMMISSIONERS OF COLLIER COUNTY,FLORIDA,that:
SECTION ONE: INTENT AND PURPOSE
It is the intent and purpose of this Ordinance to protect and promote the health,safety and
welfare of the public, including residents and visitors to Collier County and in particular to the
• Clam Bay area by providing reasonable regulation to the operation of vessels as defined it is
•
further intended that this ordii ance shall be liberally construed to effect such intent and purpose.
SECTION TWO: TITLE AND CITATION ;
This Ordinance shall be known and be cited as the "Clam Bay System Water Safety and
Vessel Control Ordinance."
.SECTION THREE: APPLICABILITY
•
This Ordinance shall apply to and be enforced on all the waters of the following described
• Restricted Areas: •
•
1. The Clam Bay System including Upper Clam Bay, Inner Clam Bay, Outer Clam
Bay,and Clam Pass. The restricted areas are as specified on the map attached hereto as"Exhibit
A."
•
2. Reserved,
• •i-
September 5,2013 Clam Bay Committee of the Pelican Bay Services Division Board
5. Watercraft violating County Ordinance 96-16
Page 2 of 5
SECTION FOUR: VESSEL SPEED REGULATION
ATION
Except during an emergency or operation by an official of the government while engaged
in official business,the operation of any vessel in excess of idle speed,as defined herein,in or on
any waters of the Clam Bay System is hereby prohibited and is a violation of this Ordinance. Said
prohibition is effective and enforceable provided the"no wake" area is designated by regulatory
marker,signage,buoy,or any other notice of the"no wake"status. The locations of such notices
shall be placed at the discretion of the County Staff. All such notices posted by the County are
official notices of the County. It is no defense to a violation of this Ordinance to allege that the
Defendant did not observe notice of the"no wake"status of the waters of the Clam Bay System.
SECTION FIVE: DEFINITIONS
For the purposes of this Ordinance,the following words are defined as follows:
A. IDLE SPEED means the minimum speed through or over the surface of the water
that will allow the vessel operator to maintain steerage of the vessel.
B. OPERATE means to be in control of the speed of a vessel traveling over or in
water.
C. VESSEL means a motor propelled and/or artificially propelled boat, sailboat,
barge, airboat or other watercraft used or capable of being used as a means of transportation of
one(I) or more persons over or in the water, whether propelled by wind, propeller, or forcing
flow of water by propeller or impeller, or otherwise. Vessel does not include a canoe, kayak, or
similar small minimum wake type vessels provided the vessel is then being propelled only by
paddle and not by motor,pump,or sail. "Vessel"does not include seaplane.
SECTION SIX: PENALTIES
f I Each violation of this Ordinance is a civil infraction. If a Citation of Violation is not
contested and is paid in full and on time, the fine shall be Fifty dollars ($50.00) for the first
violation within any six (6) month period, and one hundred dollars ($100.00) for a second
violation by the same person within any one(I)year period. If the fine is not paid in full and on
time, the Court may impose a fine of up to five hundred dollars ($500.00) plus court costs and
•
any other costs and/or fees authorized to be imposed by the Court by Florida Statutes. As an
alternative means of enforcement, violations of this Ordinance may be referred to the Collier
• County Code Enforcement Board.
•
SECTION SEVEN: ENFORCEMENT
The provisions of this Ordinance shall be enforced by any member of any duly authorized
law enforcement agency or officers having enforcement jurisdiction in Collier County, Florida.
•
Civil Citations may be used to notify the defendant of allegations of violations of this Ordinance.
• SECTION EIGHT: 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.
September 5,2013 Clam Bay Committee of the Pelican Bay Services Division Board
5. Watercraft violating County Ordinance 96-16
Page 3 of 5
1 .
i
SECTION NINE: INCLUSION USION 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 Ordinance may be renumbered or
relettered to accomplish such,and the word"ordinance"may be changed to"section,""article,"
or any other appropriate word.
SECTION TEN: EFFECTIVE DATE ,
• This Ordinance shall take effect upon filing with the Secretary of State. I o
PASSED AND DULY ADOPTED by the Board of County Commissioners of Collier
County,Florida,this .91/-" day of e/ , 1996.
•
ATTEST: ,
. BOARD OF COUNTY COMMISSIONERS •
DWIGHT•E.•DROCK,Clerk OF COLLIER COUNTY,FLORIDA
. 8 • ..,‘,........„...... ..!-_.;... .._ _ Ale/i '.--
•r C.NORRIS
• airman '
Approved as to form and This ordinorca filed with the
pp Secretory of State's Office the
• legal sufficiency: �!oy of 6- , 199C .
knry.. ement of that
Iand a doY
.M %. of. '' 'l. cyC.. ""'
Thomas C.Palmer '' e""
Assistant County Attorney
I
TCP/rtvb '.;I I',
r ordinancalwatenafeiy-cb
. \ i .
September 5,2013 Clam Bay Committee of the Pelican Bay Services Division Board
5. Watercraft violating County Ordinance 96-16
Page 4 of 5
o i
OPOSED SPEEMv1ARKER LOCATI®6 •
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September 5,2013 Clam Bay Committee of the Pelican Bay Services Division Board
5. Watercraft violating County Ordinance 96-16
Page 5 of 5
STATE OF FLORIDA)
COUNTY OF COLLIER)
I, DWIGHT E. BROCK, Clerk of Courts in and for the Twentieth
Judicial Circuit, Collier County, Florida, do hereby certify that the
foregoing is a true copy of:
ORDINANCE NO. 96-16
Which was adopted by the Board of County Commissioners on the 9th day
of April, 1996, during Regular Session.
WITNESS my hand and the official seal of the Board of County
Commissioners of Collier County, Florida, this 10th day of April, 1996.
DWIGHT E. BROCK
Clerk of Courts and Cle2'k** i
Ex-officio to Board of . •
County Commissioners. . •
By: /s/Maureen KMndn,
Deputy Clerk'
"'•