Agenda 02/18/2014 PELICAN BAY SERVICES DIVISION
Municipal Service Taxing and Benefit Unit
TUESDAY, FEBRUARY 18, 2014
THE OF THE PELICAN BAY SERVICES
DIVISION WILL MEET TUESDAY, FEBRUARY 18 AT 1:00 PM AT THE
COMMUN'TY CENTER AT PELICAN BAY, 8960 HAMMOCK OAK DR.,
NAPLES, FL.
AGENDA
The agenda includes, but is not limited:
1 . Roll call
2. Agenda Approval
3. Audience comments
4. Approval of January 21 meeting minutes
5. Discussion of latest draft of management plan
6. Review of Clam Bay related expenses
7. Discussion of Turrell-Hall and Associates contract renewal
8. Other
9. Adjourn
ANY PERSON WISHING TO SPEAK ON AN AGENDA ITEM WILL
RECEIVE UP TO ONE (1) MINUTE 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.
2/14/2014 9:25:59 PM
CLAM BAY COMMITTEE MEETING MINUTES
TUESDAY,JANUARY 21,2014
The Clam Bay Committee of the Pelican Bay Services Division met on January 21 at 1 p.m., at
the Community Center at Pelican Bay located at 8960 Hammock Oak Drive,Naples, Fl.
The following Committee members attended:
Clam Bay Committee
Susan O'Brien, Chairman John Domenie
Joe Chicurel Mike Levy
Tom Cravens
Pelican Bay Services Division Board
Frank C. Dickson, II Scott Streckenbein
Dave Trecker
Pelican Bay Services Division Staff
Neil Dorrill,Administrator Mary McCaughtry, Operations Analyst
Kyle Lukasz, Operations Manager Lisa Resnick,Recording Secretary
Also Present
Tim Hall, Turrell-Hall and Associates
Clam Bay Stakeholders
Marcia Cravens Linda Roth
Ted Raia Kathy Worley
AGENDA
1 . Roll Call
2. Agenda Approval
3. Audience comments
4. Discussion of latest draft of chapter 6 on goals and objectives
5. Discussion of studies/costs recommended for Fiscal Year 2015,
Fiscal Year 2016, etc.
6. Discussion of ways to expand water quality section on pages
61-63 of Jan. 3 draft
7. Topics for February 4 and 18 meetings
8. Other
8.1 Update on conceptual design
9. Adjourn
ROLL CALL
All Committee members were present.
50
Clam Bay Committee of the Pelican Bay Services Division
January 21, 2014
AGENDA APPROVAL
Mr. Cravens motioned,Dr. Chicurel seconded, to approve the agenda as amended.
The motion carried unanimously.
CHAPTER 6 ON GOALS AND OBJECTIVES,SURVEYS & COST ESTIMATES
The Committee reviewed goals and objectives of the management plan and the estimated
costs of activities. Costs would vary depending upon circumstances. Some surveys were to be
done on an as-needed basis; other surveys were optional and dependent upon available funds.
Mr. Hall estimated it would cost$25,000—50,000 to do an initial bathymetric survey.
Mr. Dorrill would discuss funding these activities with the County's budget office.
Mr. Cravens motioned,Mr.Domenie seconded, that the Clam Bay Committee
recommend to the full Board that the Services Division spend$25,000-50,000 to do an
initial bathymetric survey and additional surveys. The motion carried unanimously.
The Committee discussed coordinating maintenance activities in Clam Pass Park with the
County in lieu of a formal agreement, revising the Canoe Trail map, and agreed to reorder the
goals and add a vision statement.
Mr. Dorrill explained that throughout this process public participation has been poor;
therefore,to avoid any appearance of impropriety, it was necessary to clarify the Stakeholders
commenting process. Stakeholders should submit their comments directly to Mr. Hall because he
is the professional in charge of this project. To complete the record, comments should be
provided to the office as well.
WAYS TO EXPAND WATER QUALITY SECTION PP.61-63 OF JAN 3 DRAFT
Mr. Hall planned to revise this section to address areas of concern, dissolved oxygen and
copper issues, and historical records as exhibits.
TOPICS FOR FEBRUARY 4 & 18 MEETINGS
The Committee planned to discuss the management plan engineering aspects and
conceptual plans on February 4 and latest draft of the plan on February 18.
ADJOURN
The meeting was adjourned at 3 p.m.
Susan O'Brien, Chairman 2/13/2014 3:35:29 PM
51
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
From: Lauren Gibson
To: ResnickLisa
Subject: RE:dam Bay Mgmt Plan
Date: Friday,February 14,2014 1:20:35 PM
Just a quick FYI to go along with that latest version...Tim wanted to let the committee know that he
didn't make changes to the goals and objects. He was waiting for feedback on Kathy's comments.
Thanks!
Lauren Gibson
Turrell, Hall &Associates, Inc.
Marine&Environmental Consulting
3584 Exchange Ave.
Naples, FL. 34104
Phone: (239) 643-0166
Fax: (239) 643-6632
Web: www.turrell-associates.com
THE INFORMATION CONTAINED IN THIS TRANSMISSION IS INTENDED ONLY FOR THE USE OF THE
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PLEASE NOTIFY US BY TELEPHONING US (COLLECT)AND RETURN THE ORIGINAL MESSAGE TO US AT
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Save a tree. Consider the environment before printing this email.
Original Message
From: ResnickLisa [mailto:LResnickacolliergov.net]
Sent: Friday, February 14, 2014 1:07 PM
To: Lauren Gibson
Subject: RE: Clam Bay Mgmt Plan
Thanks a lot
Original Message
From: Lauren Gibson (mailto:LaurenCa)turrell-associates.com]
Sent: Friday, February 14, 2014 11:55 AM
To: ResnickLisa
Subject: FW: Clam Bay Mgmt Plan
Lisa,
The latest version of the Management Plan is attached for distribution. Thanks.
Lauren Gibson
Turrell, Hall &Associates, Inc.
Marine&Environmental Consulting
3584 Exchange Ave.
Naples, FL. 34104
Phone: (239) 643-0166
Fax: (239) 643-6632
Web: www.turrell-associates.com <http://www.turrell-associates.com/>
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
CLAM BAY NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
February 14,2014
Ver.4.0
TABLE OF CONTENTS
1.0 Introduction
Purpose of the Clam Bay NRPA Management Plan.
Development of the Clam Bay NRPA Management Plan
Role of Pelican Bay Services Division
2.0 Clam Bay Location,Setting,And Historical Overview
Maps, description of Pelican Bay and the estuary system
Natural history of the system and pass
Historical time line of system
Time line of Clam Bay NRPA establishment
1995 mangrove die-off and related causes
Restored characteristics of Clam Bay
3.0 Resource Descriptions
Soils
Topography
Climate
Natural Communities
Exotic Species
Listed Species
Other Wildlife Species
Hydrology
Water Quality
Archaeological Resources
Inlet Dynamics
Recreational Use
4.0 Authorized Construction Activities
List of permits and work undertaken to date
5.0 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 Clam Bay NRPA
while minimizing negative environmental impacts.
6.2 Maintain and protect the native floral and faunal communities
6.3 Manage and improve water quality
6.4 Protect the integrity of known archaeological sites within the Clam Bay NRPA
6.5 Address recreational uses with emphasis on passive recreation
6.6 Improve public awareness and involvement
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
CLAM BAY NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
February 14,2014
Ver.4.0
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 the Clam Bay Natural Resource Protection Area (NRPA). This plan will form
the basis by which future management decisions can be made by identifying the appropriate
management techniques necessary to protect, preserve, maintain and monitor the natural
resources and their uses within the Clam Bay NRPA.
This plan, in addition to providing a brief historical perspective of activities undertaken within
this system, will identify management goals and objectives; develop methods to achieve these
goals and objectives; and develop implementation, assessment, and evaluation strategies that
strive to balance resource protection with recreational use. The Plan will draw from the 1998
Clam Bay Restoration and Management Plan, input from multiple interested stakeholders, and
the findings of 15 years of biological and hydrographic monitoring activities within the system,
to outline goals for future enhancements to, and maintenance of, the ecosystems throughout
Clam Bay.
The Clam Bay NRPA Management Plan and any subsequent revisions shall be submitted to the
Collier County Board of County Commissioners(BOCC) for approval. When approved,this plan
will serve as a tool for future permitting and other management activities necessary to protect,
preserve, maintain, and monitor resources within the system.
Development of the Management Plan
Turrell, Hall& Associates served as the principal consultant for the management plan. This
consultant firm has a long history of work in the Clam Bay NRPA and was responsible for the
implementation the Clam Bay Restoration and Management Plan(1998)that resulted in the
successful restoration of Clam Bay's mangrove forest. The coastal engineering firm of
Humiston& Moore, Inc. provided input and monitoring data for the 2014 Management Plan
relative to the Pass and the dredging activities and templates.
The Clam Bay Committee, which consists of five members of the Pelican Bay Services Division
Board, an advisory Board to Collier County's Board of Commissioners, met regularly in 2013
and 2014 and provided input and direction to the consultants. Additional regular input was
provided by representatives of the Conservancy of Southwest Florida;the Mangrove Action
Group; and the local Calusa branch of the Sierra Club. All Committee and Board meetings were
properly noticed, open to the public, and allowed audience participation.
Input was also solicited via notices to about 35 area businesses, government officials and
employees, condominium associations, and individuals who regularly use Clam Bay. These
representatives were invited to participate in two meetings held in the spring of 2013. They were
also notified in , 2014 that a draft of the management plan was available on the PBSD's
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February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
CLAM BAY NRPA MANAGEMENT PLAN(DRAFT)
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February 14,2014
Ver.4.0
website and they were invited to send their comments to the PBSD's office. (A list of these area
people/organizations is on p. .)
Pelican Bay Services Division Turrell. Hall& Associates
Tom Cravens—Chairman Tim Hall—Project Manager
801 Laurel Oak Drive, Suite 302 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
2
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
CLAM BAY NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
February 14,2014
Ver.4.0
Role of the Pelican Bay Services Division
In order for the management and enhancement of the Clam Bay 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.
Per action by the Collier County commissioners, the responsibility for the monitoring and
maintenance of Class Pass was given to the Collier County's Coastal Zone Management
Department from 2009 to 2012. . In 2013, the Collier County BOCC returned responsibility of
the Pass to PBSD via Ordinances 2013-19 and 2013-61. It is under the PBSD's direction that
this current management plan has been written.
As a dependent special district,the PBSD is an arm of Collier County government and makes
recommendations to the Collier County Board of County Commissioners(BOCC). The PBSD
implements its defined responsibilities within the Pelican Bay community; sets its own budget
and agenda; and regularly submits them to the BCC for approval. The BCC has regularly
approved the Clam Bay management activities related to mangrove restoration and authorized
the development of the 2014 Clam Bay NRPA Management Plan. (2014). The PBSD's
effective working relationship with the BOCC is expected to continue as the PBSD serves as the
official manager of the 2014 Management Plan which is consistent with Ordinances 90-111,
2002-27, 2013-19, and 2013-61 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.
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 made up of residential, and business members within Pelican Bay;
• Garners fiscal support collected from local special assessments(non ad valorem taxes);
• Is accessible by the public due to its local governing board and advertised public monthly
meetings; and
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February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
CLAM BAY NRPA MANAGEMENT PLAN(DRAFT)
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February 14,2014
Ver.4.0
• Has demonstrated a long-term commitment to the Clam Bay NRPA and a successful
track record regarding its preservation,restoration and maintenance 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 gives 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.
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February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
CLAM BAY NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
February 14,2014
Ver.4.0
2.0 Overview of the Clam Bay NRPA
The Clam Bay NRPA is a 570-acre estuarine system consisting of sandy beaches, shallow bays,
seagrass beds, mangrove forests, and Clam Pass on the west coast of Collier County in southwest
Florida. The Clam Bay system is part of the Cocohatchee-Gordon River Transition, referred to
by Collier County Department of Natural Resources as Coastal Zone II. It is one of the few
remaining estuarine systems in the Cocohatchee-Gordon River Drainage System. Historically,
Clam Bay was tidally connected to the Gulf of Mexico via Wiggins pass to the north, Doctor's
Pass to the south, and centrally located Clam Pass(Collier County, 1994, Tropical Biolndustries,
1978). These connections were eventually severed with the development of Vanderbilt Beach
Road and Seagate Drive in the 1950s.
Today,the system includes three primary bays; Outer Clam Bay(southernmost), Inner Clam Bay
(central), and Upper Clam Bay (northernmost), connected by a series of tidal creeks and
connected to the Gulf of Mexico by Clam Pass. 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. The operation of motorized watercraft is limited to idle
speed/no wake per Collier County Ordinance 96-16.
The Clam Bay system is bounded on the north by Vanderbilt Beach Road and the Bay Colony
portion of the Pelican Bay development, to the south by Seagate Drive, and the Seagate and
Naples Cay developments, to the east by the Pelican Bay development and to the west by the
Gulf of Mexico and the Strand enclave of the Pelican Bay development.
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 570 acre preserve area, including the 35 acre beach park, was donated to
Collier County and eventually became the NRPA which is in place today.
Development of Pelican Bay 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
5
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
CLAM BAY NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
February 14,2014
Ver.4.0
near the berm. Six drainage basins operate on a gravity system to slowly move surface water
into the receiving area of Clam Bay.
Naples Cay is a high rise development consisting of 8 multi-story condominium buildings. The
community also includes pools, tennis courts, approximately 33 acres of park and preserve areas,
and two canoe and kayak launching piers. The first building started in Naples Cay in the late
1970's and the last was completed in 2002. Stormwater management is accomplished through
several internal detention areas before water flows into Outer Clam Bay.
The Seagate community is composed of single family residences. The community was first laid
out in the 1950's and still has a few undeveloped lots. Because development of this community
occurred so early, there is no community-wide stormwater management system in place.
Seagate is the only community adjacent to the Clam Bay NRPA that is allowed under the County
Manateee Protection Plan to have motorized vessels and the associated boat docks.
Clam Bay was designated a Natural Resource Protection Area (NRPA) by Collier County in
1995 (See below for more details on the NRPA history). The purpose of the NRPA designation
is to protect endangered or potentially endangered species and to identify large connected intact
and relatively unfragmented habitats, which may be important for these listed species (Collier
County Growth Management Plan, Future Land Use Element).
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6
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
CLAM BAY NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
February 14,2014
Ver.4.0
Clam Bay NRPA Vital Statistics
Total acres: Approx. 570 acres
Beaches: Approx. 1.5 miles
Mangrove: Approx. 420 acres
Open Water: Approx. 115 acres
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
Water Body Identification(WBID) 3278Q1
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 of Clam Pass were -2.5' to -1.0', and its
width ranged from 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.
7
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
CLAM18,
MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
February 14,2014
Ver.4.0
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Approximate extent of Clam Bay NRPA boundary.
8
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
CLAM BAY NRPA MANAGEMENT PLAN(DRAFT)
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February 14,2014
Ver.4.0
Natural History
Prior to development, the entire coastline of south Florida would have resembled the Clam Bay
ecosystem with meandering mangrove lined waterways buffering sandy barrier islands and
terrestrial communities. Unique within the heavily 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, and beach going.
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. It 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) and approximately 1.5 miles of sandy
beach.
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(Section 3.0) of this Plan.
Historical Overview
Historically, Clam Pass was a small part of a large system of waterways and interconnecting
wetland communities extending from Lee County to Doctor's Pass. Anecdotal evidence suggests
that small boating activities took place within many of these interconnected areas.
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 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, as well as aerial photographs of the Pass over time, is
provided in Section 3.0 of this Plan.
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. The
following time lines are intended as background information and as a factual recount based on
anecdotal evidence,press reports,published and unpublished reports.
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February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
CLAM BAY NRPA MANAGEMENT PLAN(DRAFT)
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February 14,2014
Ver.4.0
Time Line of important moments within the Clam Bay System
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
Clam Bay is part of a connected system of barrier islands, mangrove forest, passes and
waterways. The orientation of the beaches and passes would have changed seasonally and with
storms.
1952
Vanderbilt Road is constructed, eventually severing connection with the Wiggins Pass system to
the north.
1958
Seagate Drive is constructed as the Parkshore community is developed. Flow from north to south
Venetian Bay is severed.
! -•'r' ; DSM-11-9
Vanderbilt Lagoon
Y ,
Outer Clam Bay
�a Upper Clam Bay
. any , ,
ILE:=1
444 I
Circa 1960 Aerial Photograph Circa 1952 Aerial Photograph
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.
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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 and was mechanically dredged by dragline to re-open the entrance; no records
of quantities or dredge limits are available.
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 and was mechanically dredged by dragline to re-open the entrance; no records
of quantities or dredge limits are available.
WCI, the developers of Pelican Bay, transferred title to Clam Bay to Collier County with the
stipulation that Clam Bay shall remain a conservation/preservation area in perpetuity.
1982
WCI deeded Clam Pass Park and Clam Bay to Collier County and in accordance with the Pelican
Bay PUD, required the County to seek approval of WCI or its successors for any modifications
to Clam Bay.
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1983
Tropical Bio-Industries produce biological reports:
• Fish populations of tidal ponds west of Upper Clam Bay
• Populations of Melampus co9eus (Coffee bean snail) and Cerithidea scalariformis (Ladder
hornsnail)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 Department of Natural Resources
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.
Clam Pass was mechanically dredged to re-open. Approximately 700 cubic yards of material
were removed from the mouth of the inlet and the south bend of the channel. Material was
placed south of the pass. Multiple closures of the inlet occurred during the construction process.
1990
Pelican Bay Improvement District becomes a dependent district of Collier County called the
Pelican Bay Services Division.
1992
The area of dead mangroves is reported at 7 acres.
1994
20 acres of mangroves are reported dead.
1995
Clam Bay is approved by the Board of County Commissioners as Collier County's first Natural
Resource Protection Area(NRPA).
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Ellicott Series 370HP Pum•ing Sand out of Clam Pass(1999)
..;.I , 4. s
111
,—
,I, ' 141061110k—
Iiik7`-' '*".--! ., -,, .-: al _
MI.
2000
Hurricane Gordon impacts the area with no inlet closure.
2002
Hydraulic maintenance dredging of Clam Pass flood shoals between stations 3+10 and 18+00
(Mgmt by PBSD) completed to improve tidal circulation. The entrance of the pass was not
dredged during this event.
Flap valves on Seagate culverts removed due to insufficient head differential causing them to act
as plugs instead of valves.
Canoe trail markers permitted and installed throughout Clam Bay system.
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.
2005
Hurricane Wilma comes ashore about 30 miles south of Clam Pass. More limb and leaf loss is
noted. Pass does not close.
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ksix : f Ilm'
r> i tt,c+E �d{sj#z �.�� i s ki 1
q
E
Hurricane damaged mangroves along bay 2005 Same mangroves along bay 2007
2007
Hydraulic maintenance dredging of pass and entrance channel was conducted between Stations 0+00
and 18+00. The entrance of the pass was dredged at 80" width. (Mgmt by Collier County Coastal
Zone Management Dept.).
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.
Benthic Habitat Assessment study completed within the Clam Bay NRPA by the Conservancy of
Southwest Florida. Study provides comprehensive mapping of benthic habitat compositions and
distribution throughout the Clam Bay NRPA.
2012
Canoe trail markers and informational signage installed throughout Clam Bay.
The mouth of Clam Pass moves to the north near the Pelican Bay Beach Store. The northern shoreline
of the pass is temporarily reinforced with the installation of concrete barriers.
Impacts from tropical storms Debby and Iassic, along with numerous winter storm fronts caused the
closure of the pass.
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2013
A single event mechanical dredge is carried out in March under DEP and ACOE permits with an
entrance cut of 45 feet. Beach compatible material is placed north and south of the pass above the
mean high water line.
Development of a new Management Plan is initiated through stakeholder input and multiple public
meetings.
Time Line specific to the establishment of the Clam Bay NRPA
1976
Collier County Ord. 76-30 zoned coastal areas environmentally sensitive lands as ST(Sensitive
Treatment)
1977
Approval of the Pelican Bay PUD (Ord. 77-18)by Collier County. The PUD identified 98 acres of
coastal mangrove wetlands to be filled in for development while preserving 570 acres of ST lands as
the Pelican Bay Conservation Area. (35 acres in the south and 5 acres in the north would become parks
providing public beach access).
1981-82
Department of Army Permit(79K-0282) authorized the fill of the 78 acres of coastal wetlands (76
acres for residential development and 2 acres for public parking area). It required 570 acres including
Upper, Inner, and Outer Clam Bays, and their adjacent wetlands to be conveyed to Collier County and
to remain a conservation/preservation area for the use of the public in perpetuity. It also prohibited
dredging Clam Pass except to keep it open to the Gulf of Mexico.
1988
The Pelican Bay Conservation Area(570 acres) was approved and recorded as FL-64P by Congress
and became part of the Federal Coastal Barrier Resources System(CBRS).
1995
The Collier County Board of County Commissioners approved the County Natural Resources
Department's recommendation to establish the County's first Natural Resource Protection Area
(NRPA); stipulating that that it would have the same boundaries as the Pelican Bay Conservation Area
within the Pelican Bay PUD.
The Collier County Manatee Protection Plan is approved. It contains the recommendation to establish
an"Idle Speed/No Wake"zone throughout the Clam Bay/Clam Pass System.
1996
Collier County Ordinance 96-16: "The Clam Bay System Water Safety and
Vessel Control Ordinance" is approved. It establishes that the Clam Bay System is an"Idle Speed/
No Wake"zone.
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Ver.4.0
2013
A single event mechanical dredge is carried out in March under DEP and ACOE permits with an
entrance cut of 45 feet. Beach compatible material is placed north and south of the pass above the
mean high water line.
Development of a new Management Plan is initiated through stakeholder input and multiple public
meetings.
Time Line specific to the establishment of the Clam Bay NRPA
1976
Collier County Ord. 76-30 zoned coastal areas environmentally sensitive lands as ST(Sensitive
Treatment)
1977
Approval of the Pelican Bay PUD (Ord. 77-18)by Collier County. The PUD identified 98 acres of
coastal mangrove wetlands to be filled in for development while preserving 570 acres of ST lands as
the Pelican Bay Conservation Area. (35 acres in the south and 5 acres in the north would become parks
providing public beach access).
1981-82
Department of Army Permit(79K-0282) authorized the fill of the 78 acres of coastal wetlands (76
acres for residential development and 2 acres for public parking area). It required 570 acres including
Upper, Inner, and Outer Clam Bays, and their adjacent wetlands to be conveyed to Collier County and
to remain a conservation/preservation area for the use of the public in perpetuity. It also prohibited
dredging Clam Pass except to keep it open to the Gulf of Mexico.
1988
The Pelican Bay Conservation Area(570 acres) was approved and recorded as FL-64P by Congress
and became part of the Federal Coastal Barrier Resources System(CBRS).
1995
The Collier County Board of County Commissioners approved the County Natural Resources
Department's recommendation to establish the County's first Natural Resource Protection Area
(NRPA); stipulating that that it would have the same boundaries as the Pelican Bay Conservation Area
within the Pelican Bay PUD.
The Collier County Manatee Protection Plan is approved. It contains the recommendation to establish
an"Idle Speed/No Wake"zone throughout the Clam Bay/Clam Pass System.
1996
Collier County Ordinance 96-16: "The Clam Bay System Water Safety and
Vessel Control Ordinance" is approved. It establishes that the Clam Bay System is an"Idle Speed/
No Wake"zone.
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Ver.4.0
1998
The Clam Bay Restoration and Management Plan(CBRMP) is developed, implemented, and managed
by the PBSD and their consultants.
FL Admin. Court Case No. 98-0324GM provided an interpretation that certain elements of the Collier
County Growth Management Plan (Conservation and Coastal Management Element)require
unequivocal protection of habitats within NRPAs which support existing and potential uses by wildlife.
2008
Public Law 110-419 was adopted identifying the Coastal Barrier Resource System, Clam Pass Unit,
FL-64P to be entirely located within the existing boundaries of the Clam Bay NRPA.
2013
Work begins on new Clam Bay NRPA Management Plan under PBSD direction.
1995 Mangrove 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
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(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.
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 1978, 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 (Yarboro et al. 1994) and it was attributed, in part, to natural
drought conditions and unusual tidal inundation patterns.
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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,particularly
where the mechanism for flushing is impaired. (Lugo, et. al. 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, the opening
of several of the impacted tidal creeks, and the construction of approximately 13 miles of hand-dug
flushing channels, 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
in 1996, 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 Charley in 2004,
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
creeks, and construction of the network of hand-dug flushing cuts throughout the original die-off area
proved very effective in maintaining the tidal exchange and drainage capability of the system.
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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.
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.
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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 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. Approximately 13 miles of these channels were
installed between 1999 and 2005.
Biological monitoring work over the past fifteen 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.
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3.0 Resource Description and Assessment
SOILS
Based on the National Resource Conservation Service (NRCS) "Soil Survey of Collier County Area,
Florida" (NRCS, 1998) there are 2 different soil types (soil map units) present within the NRPA
boundary.
It is important to understand that where the soil survey shows mapping units named for soil series, the
units represent the dominant undisturbed soils in that landscape that existed predevelopment. The unit
descriptions do not recognize or appropriately interpret the drastically disturbed nature of urban
landscapes created after the soil survey was completed.
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Durbin and Wulfert mucks, frequently flooded (Map Unit #40), covers approximately 66% of the
NRPA. These level, very poorly drained soils are most often found in association with tidal mangrove
swamps. Mapped areas can consist entirely of either Durbin or Wulfert or any combination of the two
soils. Individual areas are elongated and irregular in shape and range from 50 to 1000 acres. The
slope is 0 to 1 percent. 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. The natural vegetation within these areas consists of red, white and black
mangroves.
Canaveral-Beaches Complex (Map Unit #42) covers approximately 9 %of the NRPA.
This map unit consists of the nearly level, moderately well drained Canaveral soil on low ridges and
beaches. Individual areas are elongated and irregular in shape and range from 20 to 300 acres. The
slope is 0 to 2 percent. Typically, beaches consist of sand mixed with shell fragments and shells and
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. This soil is subject to tidal flooding under severe weather
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conditions. Natural vegetation consists of sea oats, sea grape, cabbage palm, and salt grasses. They are
commonly invaded by exotics such as Australian pine and Brazilian pepper.
TOPOGRAPHY
Topography is shown below using a Light Detecting and Ranging map (LIDAR) obtained from Collier
County. The elevations within the NRPA boundary range from +7.0 to -9.0 NAVD88. The
surrounding lands are generally higher than the NRPA and generate the freshwater flows into the
preserve.
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S r, 1 1 (
23
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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
experienced. The wet season occurs in the summer, and the dry season occurs in the winter. Typical
rainfall and temperature data are 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 rarely 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.
1981-2010 TEMPERATURE AND PRECIPITATION NORMALS GRAPH
110. 0
100 0
70.0
•
40.x1
30.0
20. 1
0 0 OMROPM01 tl..0100 0110000 *011440100. --°°.
Jar Jul Sep j V
0 Precip (in) 0 Min Tmp("F) i 0 Avg Tmp ( I 0 Max Tmp (`F)
Table 4.1
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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 reflect a
humid subtropical climate with a narrow fluctuation in air temperature.
Precipitation
Average 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 months of June,
July, August, and September.
1981-2010 TEMPERATURE AND PRECIPITATION NORMALS CHART
1 0 Precip fin) 0 Min Tmp(°F) 0 Avg Imp(CF) i 0 Max Tmp(`F)
January 1 85 54.2 64 5 74.7
February 2.10 56.8 66.9 76.9
March 2 3 60.0 70.0 79.9
April 2 3 63.4 73.3 83.2
May 3 1 68.5 78.2 87.8
June 8.82 73.9 81.9 89.9
July 7.27 74.9 83.1 9t2
August 8.58 75.3 83 2 91 0
September 7 6 74.8 82.4 89.9
October 4 1 70.0 78.5 86.9
November 2.04 62 9 72.1 81 2
December 1.45 57.0 66.8 76,6
Table 4.2
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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 warms, the air above is heated. The warm air is less
dense and tends to rise creating a lower air pressure over the land than the water. 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 waters. Eventual dissipation or
Saftir—Simpson Hurricane Scale modification, averaging seven (7) to eight (8) days later, typically
Category wind speed Storm surge occurs over the colder waters of the North Atlantic or when the
mph storms move over land and away from the sustaining marine
(kms) (��)
environment.
13"54 "X3-111 Due to the destructive nature of these storms, landfall can result in
01t significant damage to upland development and facilities from storm
Three 111- 30 -312 sure waves, and wind. A exam le of this would be
7e-20s> (2.7- .r> surge, goodexample
,
ss- 10 s-s Hurricane Wilma which formed in 2005.
(154-177) (1.8-2.4)
One
74-95 4-5 A tropical storm is defined by maximum sustained winds from 35-
(119-153) (1.2-1.5) 64 knots (40-74 mph). A hurricane has maximum sustained winds
Additional classifications that exceed 64 knots (74 mph). Hurricanes are classified into
different categories according to the Saffir-Simpson scale.
; Hurricanes can also spawn severe weather such as tornadoes as they
� a � ' 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
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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.
Table 4.4 Number of Named Storms Passing through or near Naples
Year #of Storms Names Strength closest to Naples
1992 1 Andrew Hurricane Cat. 3
1993 0
1994 1 Gordon Tropical Storm
1995 1 Jerry Tropical Storm
1996 0
1997 0
1998 1 Mitch Tropical Storm
1999 1 Harvey Tropical Storm
2000 1 Gordon Tropical Storm
2001 0
2002 0
2003 0
2004 1 Charley Hurricane Cat.3
2005 1 Wilma Hurricane Cat.2
2006 0
2007 0
2008 1 Fay Tropical Storm
2009 0
2010 0
2011 0
2012 0
2013 0
Hurricane Wilma image
*1 4L WILMA
10/19/'5 14 2 0088.12
3' aa i 1
t
ovor
111111111111116.
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NATURAL COMMUNITIES
In this Section, a natural community refers to the mix of plant and animal species that form the natural
basis of the Clam Bay NRPA. A combination of factors including geology, climate, hydrology, soils,
and anthropogenic influences determines the specific types of plants found in any given area. These
plants are a major factor in what type of animal species that may be present. The Florida Department
of Transportation's Land Use, Cover, and Forms Classification System(FLUCFCS 1999)has been
used to identify the plant communities found within the Clam Bay NRPA.
FLUCFCS Community Description Upland or % of Clam Bay
Code Wetland NRPA
181 Swimming Beach Upland 5.95
186 Community Recreation Facilities Upland 0.40
322 Coastal Scrub Upland 3.98
428 Cabbage Palm Hammock Upland 0.45
540 Bays (with and without direct Wetland 23.16
connection to Gulf or Ocean)
612 Mangrove Swamp Wetland 64.60
642 Saltwater Marsh Wetland 0.04
651 Tidal Flat Wetland 1.44
911 Seagrasses** Wetland 0.84**
** included in the Bays (541) category
Several other components of the Clam Bay NRPA ecosystem are also addressed below. These
components include offshore hardbottom, oyster and other benthic faunal communities that are not
specifically addressed in the FLUCFCS classification system. Additional historical information on the
Clam Bay mangrove and seagrass habitats is included as appendices to the Plan.
FLUCFCS Code 181 -Swimming Beach
Beaches form when offshore sand deposits are moved landward by wave action usually during the
spring and summer. Sand, which is stirred up as the wave breaks on the shore, drops out of suspension
as the water moves up the beach face. Thus, the beach becomes gradually higher, wider, and steeper.
In the wintertime, larger, higher energy waves associated with winter storms overflow the beach area
and stir up the sand deposited earlier in the year. The sand is pulled off the beach as the wave recedes
and is deposited in an offshore sand bar. If these two forces are in equilibrium, the beach area will be
stable from year to year. However, naturally occurring factors such as storm events, littoral drift
(lateral movement of sand because waves approach the beach at an angle), and offshore winds, upset
this equilibrium and result in the ever shifting nature of the beach environment.
Dunes form because of onshore wind action on beach sand. When wind speeds are sufficient,
individual grains of sand start to roll and bounce along the surface. This windborne sand is transported
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landward until the wind speed drops below that needed to move the sand. Coastal vegetation is critical
for slowing wind speeds and causing sand to be deposited.
Landward of the highest tides, pioneer or frontal zone sites are stabilized by sand trapping action of
various rhizomatous grasses and low growing shrubs that are tolerant of salt spray. Only a few plant
species can tolerate the stresses of a dune environment, particularly frontal dune sites. Foredune plants
must be able to survive being buried by blowing sand, sand blasting, salt spray, salt water flooding,
drought, heat, and low nutrient supply. 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.
Many plant species that occur on dune areas have developed specific attributes to help them survive these harsh
environments. These include high growth rates, dense root systems, low profiles, and high flower and seed
production rates. Species common on the beaches of the Clam Bay system include; Sea oats (Uniola
paniculata), Seagrape(Coccoloba uvifera), and Railroad vine(Ipomoea pes-caprae).
In addition to the 35-acre Clam Pass Beach Park, south of the pass,beach habitat also extends north all
the way to Wiggins Pass. There is approximately 6.,250 linear feet of shoreline north of Clam Pass to
the south end of the Strand community and approximately 3,250 feet of shoreline south of the Pass to
the north edge of the Naples Cay community. 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.
This particular habitat has been monitored periodically in terms of width as part of the Collier County
Beach renourishment program though no conclusive statements can be made about the floral or faunal
details of the ecotone over the years. Large scale generalizations based on the annual aerial
photographs can be made that the overall size, composition, and health of the habitat have remained
relatively stable and, with the exception of the areas immediately adjacent to the Pass, are mostly
unaffected by the status of the pass.
'' "v . ,� � s N ` p ,1 7it
x
rp
t a ✓r 'raj i +. �Ws-✓k F we n`» ' { NA- +t
t.
- - t �" Y1 3 � '..�. $*x cra glr4-1,-,;,,-,.„,!-1,', 7, / . l i..
�<; .- kF ` s� q a *
Beach habitat within NRPA Boundary
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FLUCFCS Code 322 - Coastal Scrub
Landward of the frontal (Beach) zone area is the back dune zone (also often called the shrub or scrub
zone), a portion of the dune that is more stable, has greater organic matter, and supports less salt
tolerant grasses and shrubs as well as some trees.
Many of the woody species found in coastal scrub are low growing and shrubby due to low nutrient
and droughty conditions of sandy soils. High winds and salt spray often prune the terminal buds of the
trees and shrubs growing on the dunes and result in salt-pruned,windswept canopies.
Coastal scrub is represented by a conglomeration of coastal species generally found in a narrow band
between the Mangrove forest and the beach areas. Species common on the beaches of the Clam Bay
system include; Seagrape (Coccoloba uvifera), Cabbage palm (Sabal palmetto), Buttonwood
(Conocarpus erectus) and Spanish bayonet (Yucca aloifolia). This is an important habitat as it helps
anchor the back dune sands and provides habitat for several listed plant and animal species including
the gopher tortoise (Gopherus polyphemus).
The primary management issues of concern in the coastal scrub are gopher tortoise habitat
management and exotic vegetation control.
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'47 ,i' l'',01 .''1",`f -4,0'1, •••,•••,'. I4..... .'''s$4,....„‘'"'ili, • ..-:, 'ZIFriv ' 1,, _ ,
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L � . * a i < * r-' - v ; 41F 5p� , # } # %
, th # i 4+A" St! t1 y ,...,-1,.....144 4� `yjP't j
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*I' )' ''''"ifittptiorom :
t-,-,i.?"---, --v...'w'ti":.-..t. ,k-A.' .
sz° .+"� w ..- ., gyp.'
+ *.- -" fi',-°'•'S'r'i q r „,..s,:-,..,--.
, t - .,h:
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+ -as �E ....E �n t � +� }
'-F:fiFor,',-_-,,,!4„,,,---4:'•'-'-'-:;;•,'''',7-'''''_''• :, --' - ,,,--.- .,,,,.-•,-----'--''''''' 3•4•‘-- - ''''''',ter-Tri,” ':-.-.4;--:i 4--f:-,4-:,,:,,',-.:.'-.,_s,-k4.„.t„...--a.'-.,-,-r-,'2-,,-,7,•.
Scrub habitat within NRPA Boundary
FLUCFCS Code 428-Cabbage Palm Hammock
This forested zone is composed of the more protected dune vegetation farthest from the ocean. The
,i.,,.::4•'i-'...:.i,,,,'u.,,:-.,:04i._'..,,.,,'.,-,.-.,,„,;l'.—,,*.1,,-
Cabbage Palm Hammock habitat is identified by the preponderance of cabbage palms (Sabal
e„,A*l--o,•,-pr'.•'-(•.i,.-?.,.„'4.l,,r,.....,k,.r!'„0;*
,4;,f-*•-'-.t,;:--,,'',?--„-:,„-:':„,k`'d„•1--i
l,,,':-'
palmetto). It is generally found in pockets located between the mangrove forest and the coastal scrub
or beach areas. Aside from the cabbage palms, sea grapes (Coccoloba uvifera), buttonwood, and
several other hammock species such as wax myrtle and myrsine are common. A hammock is a habitat
that is densely shaded by a canopy of trees. Hammocks usually have a sparse groundcover that leaves
the forest floor mostly open for animals to travel through. Hammocks also provide a reprieve from the
sun for animals and humans alike. In Clam Bay, this habitat is also susceptible to infestation by exotic
vegetation such as Australian pine and Brazilian pepper which are addressed further on in this Section.
The primary management issues for this habitat are exotic control and preventing destructive visitor
access.
ss.. 'is-•":kv; *'s" ,a .. ,w -, <.�, wpa�s-” fid" wr �,i�"
L , 1 4R a: e
, •, °j i, a. Er: -'a' m .t - fie! ,' ", -.•,, .4w
'7,;.0 '- ,c, ,7
,.t0 ' ' , z eay'sa.. , q, -t S
,q.
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,ng,,+
'.!:. 44l"l s t Y a�1': " tea$ \\
. ... r u,.,+.,,..adS,.w32 \ Lam, ..'?Y"Ya°<EYN, .- " , 1 ., a „ .,..' F1
Palm habitat within NRPA Boundary
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FLUCFCS Code 540—Bays (with and without connection to the Gulf)
The Clam Bay NRPA contains the three larger bays associated with Clam Pass (Outer, Inner, and
Upper) as well as the interconnecting waterways and small open water areas. Second in extent of
aerial coverage within the NRPA boundary, it is the bays and interconnections which serve as the life
blood of the estuary.
This open water habitat serves as the basis for many other communities. Seagrass beds, oyster bars,
clam beds, and other benthic communities can all be supported to varying degrees with the open waters
of the bays and interconnecting creeks. As outlined below, several of these communities are present
within the Clam Bay NRPA and will be considered when deciding on management activities outlined
within this Plan
Multiple studies have indicated that the single most important thing that can be done to restore the
health of the Clam Bay system is to improve the total tidal flushing capacity of the system (Tackney
1996; Lewis 1996; Wilson Miller, et al 1996; Turrell 1996.). The dredging conducted within the Pass
and the interconnecting creeks, as well as the hand-dug flushing cuts, have been seen as the major
contributing factors to the restoration of the mangrove forest community within the system (Turrell
2008; Humiston& Moore 2003).
Tidal Pass
Clam Pass is the only open water connection to the Gulf of Mexico for the Clam Bay NRPA. The
exchange of seawater between Clam Bay and the Gulf is critical to the ability of the estuary to export
organic matter, as well as to help regulate excess salt and freshwater. It also supplies oxygen rich
water from the Gulf. In the absence of surface water circulation or tidal activity, estuarine habitats
such as mangroves can 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).
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.
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CLAM BAY TIDAL RANGES
2.50
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Gage Location
It can be seen that the health of mangrove forests is directly related to the efficiency of the tidal pass.
Clam Pass and its associated waterway is a very dynamic creek whose location has varied over time
(Turrell 1995; Tackney 1996). Because of this, it is susceptible to outside events and can periodically
close, such as has happened at least six times in the last 25 years.
The following aerial photographs show how the Pass and its waterway have changed over the past 60
years.
3eR� ** F
i
,,,,,I; , ';‘.;4!' ,‘; ' :‘„ '';';'!'';''''''';':;:,[!;;:';';:!!:: '''''::::;::;t;Z.;‘;;;;:1;' ;:;:;-'i.';'.;-; ;'''' ''' ';;;' '; ;;'-' -4!!;i'll'.11;;;I:
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s
''' ' ,
'-''',-','.' -- -le ,.:1'''''"r‘.,..* .11'
A' af
°
'^„_ mom,
p
7
r x
y
C LAM y ”
PASS .
2012 . ` '�
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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 pass. 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.
Management concerns related to the bays and associated creeks include maintaining sufficient flow
through them to accomplish flushing needs of the system, stabilization of the pass without harming
other components of the NRPA, and educating recreational users of the NRPA of the need to protect
the shallow water habitats and the communities located therein.
awn�°! "� y7
yy is
� z
Open Water habitat within NRPA Boundary
FLUCFCS Code 612—Mangrove Swamps
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,terrestrial and avian wildlife.
• Protecting coastal areas from storm surges and coastal erosion.
• Improving water quality by 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.
• Enhancing the atmosphere by absorbing Carbon Dioxide and reducing greenhouse gasses.
Approximately 65%of the Clam Bay NRPA is composed of the three most common mangrove species
in Florida. Namely, red mangroves (Rhizophora mangle), black mangroves (Avicennia germinans),
and white mangroves (Laguncularia racemosa) make up the mangrove forests within the Clam Bay
NRPA. All three species have special biological adaptations to cope with salt and unstable, mucky,
low oxygen soils that result from the tidal, hence continually waterlogged, environment. The
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dominance of mangroves in tidal areas is a function of these adaptations and their ability to out-
compete other wetland plants. Tidal flushing allows nutrients to be distributed within the forest and
provides for the transportation of dead leaves, twigs, etc. As this material decays, it becomes 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.
Special attention has been given to the mangrove community in the past because of the die-off which
occurred between 1991 and 1997 (though stress in the community was documented as far back as the
late 1970's). The die-off affected black and red mangroves initially but eventually ended up
encompassing some white mangroves as well. More details on the recent history of the mangrove
management are provided in Appendix 1 included with this plan.
Red Mangroves
Red mangroves (Rhizophora mangle) are recognized by their tangle of reddish looking prop roots, long
cigar shaped seedlings and their large, pointed evergreen leaves. Red mangroves flower all year but
reach maximum propagule production during the late spring and early summer months. 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. 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.
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'.,I
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Black Mangroves
Black mangroves (Avicennia germinans) are typically found a little further inland and key
identification features include the snorkel like pneumatophores 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 keeps salt out of body cells through filtration in the roots; the
black mangrove excretes salt out of 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
lima bean shaped propagules are typically apparent during the late spring and early summer months.
Black mangroves are cryptoviviparous as the embryo develops within the fruit while on the parent
plant. When these propagules fall from the parent tree, they are able to float for a short period before
rooting in the mucky soil.
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February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
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White Mangroves
White mangroves (Laguncularia racemosa) are the third mangrove species and are often found further
inland than the other two species (although zonations described are typical they can frequently vary).
Since they often occur in drier areas, white mangroves do not exhibit the adaptations to soft, anaerobic
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soil of the other species. The bark is characteristically grooved and furrowed and leaves are oval, mid-
green and leathery with two small glands on the petiole at the base of each leaf. White mangroves also
flower in the spring and early summer and the small seedlings have the shortest floating dispersal stage
of the three species. White mangroves are semi-viviparous and germinate inside the fruit during the
approximately five day dispersal,but not while attached to the parent plant
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February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
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Buttonwood
Buttonwood (Conocarpus erectus) is considered a mangrove associate, usually occurring even further
inland than the white mangrove. Small, round, brown seeds give rise to the name. This is a hardy
species, able to withstand the full sun, high temperatures and salty conditions of coastal Florida. These
characteristics also make it an excellent and attractive landscaping plant. Buttonwoods are present
along the interface between the mangrove and palm hammock communities in Clam Bay.
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February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
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The mangrove communities are composed of both riverine (along the creeks) and basin forest
components. The species composition of mangroves within these two community components is very
distinctive. Riverine mangrove areas are almost exclusively composed of red mangroves within the
Clam Bay NRPA while all three species, along with buttonwood are found in the forest component.
Riverine (Creeks)Mangroves
On the waterward edges of small islands and the tidal creeks, passes and estuarine waterways that
make up the Clam Bay system, a fringe of red mangroves will be found growing up to 25 feet in
height. This zone can be just one or two trees in depth or extend landward for some distance,
depending on topography. The habitat provided by the prop roots of these red mangroves is of great
importance to many fish and other aquatic organisms.
Forests
The majority of the Clam Bay mangrove habitat is low-lying basin forest where the dominant
mangrove species varies between red, white, and black throughout the forest habitat. This forest
community was the habitat affected by the mangrove die-off. The hand Aug flushing channels were
constructed throughout this community to increase the flushing capacity through tidal inundation.
Associated plants within the mangrove habitat include the succulent groundcovers Saltwort (Batis
maritime), Glasswort (Salicornia cervicornis), (especially where a fallen tree provides a break in the
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5. DiFebruaryscussion 18,2014oflatest Clamdraft BayofmCommittanagementee of theplan Pelican Bay Services Division
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canopy and light penetration to the forest floor) and, further inland and closer to freshwater sources,
the Leather fern(Acrostrichum danaefolia).
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FLUCFCS Code 642 -Salt 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 (Juncos 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 and interface between the natural mangrove forest and the development water
management system. t 6
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Marsh habitat within NRPA Boundary
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FLUCFCS Code 651 -Tidal Flats
Tidal flats are flat bottomed, sub- or intertidal habitats that lack an oyster or seagrass community and
are located inside the outer coastal margin. The two most significant environmental characteristics that
control a flat's infauna (benthic organisms that live within the substrate) and epifauna (benthic animals
that live on the surface of a substrate) are: the height of the substrate relative to mean sea level and the
sedimentary consistency of the substrate. The position relative to mean sea level dictates whether the
habitat is emergent (in air) for part of a tidal cycle or how deep below the water it is. This latter
characteristic controls other physical water quality measures, such as dissolved oxygen, the frequency
and duration of hypoxic events, and light penetration. Firmness of the substrate affects the capacity to
support an epifauna by both supporting the organism on the substrate and permitting the burrowing of
the infauna.
The sand and mudflats of Clam Bay are rich feeding grounds for many species of fish and wading
birds. These organically rich sediments support a variety of mollusks, worms and 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.
The dredging of the pass associated with the 1998 Restoration and Management Plan resulted in an
increase of exposed tidal flats within the southern portion of the system. Increased tidal range
resulting from the dredging allowed more area to be periodically exposed during the tidal cycle. Some
of the area that had supported seagrasses prior to the dredging work were converted into the tidal flats
by the increased range and reduced phase lag. Management concerns related to the tidal flats include
the templates established for the dredging, the resultant currents that could be expected as a result of
dredging, and the frequency of disturbance.
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FLUCFCS Code 911 -Seagrass Beds
Seagrasses are flowering marine plants of shallow, tropical regions. With a creeping growth form
connected by horizontal rhizomes they serve to trap and anchor sediment. Both the grass blades
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themselves and the surface area they represent provide food and attachment for marine species and
seagrass beds are renowned for their value as nursery habitats.
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Several areas within the Clam Bay system host seagrass beds, specifically Outer Clam Bay and
waterways just inside Clam Pass. Three species are commonly found in these Clam Bay waters; the
largest Turtle grass (Thalassia testudinum) with flat strap shaped leaves, the smaller shoal grass
(Halodule beaudettei aka wrightii)) with narrow, flat blades and Paddle grass (Halphila decepiens)
with the smallest,paddle shaped leaves. Shoal grass is by far the most common though a small area of
turtle grass has persisted since the original 1998 dredging. Paddle grass is much more ephemeral in
nature and diligence is required to be able to locate it during the time frames when it is present.
Seagrasses rely on good light penetration to enable photosynthesis and are sensitive to reduced tidal
water quality. Growing in shallow regions they are also vulnerable to physical damage by boats. A
variety of marine algae can be associated with grass species, differing in the lack of a true rooting and
vascular system. Several species of both brown and green alga have been observed.
seagrass coverage in Clam Bay has varied over time but has always been found predominately in
Outer Clam Bay and the waterway between this bay and Clam Pass. A 1994 Collier County report
estimated seagrass coverage at approximately 10 acres. Pre-dredge surveys conducted in 1999
estimated coverage at about 5.13 acres. Annual monitoring of seagrass beds along the monitoring
transects have estimated coverage from a low of approximately 1.2 acres in 2003 to the current
estimate of 2.85 acres from the 2013 survey. It should be noted that the coverage estimates are taken
from along the suryey transects only and do not account for other scattered grasses that may be located
elsewhere in the system.
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February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
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Management concerns related to seagrasses include direct impacts due to recreational use and potential
dredging templates, turbidity and water quality concerns related to flushing(too much or too little) and
stormwater inputs, and algal infestations due to nutrient increases.
A history of the seagrass monitoring efforts in Clam Bay is included in the Appendix 2 attached to this
report.
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Other Benthic Habitats
Oyster Bars
Oysters (Croassostrea americana) are filter-feeding bivalves, which were once common within the
tidal creeks of Clam Bay (Humm and Rehm 1972). Oysters play a significant role in shaping the
environment in which they live by forming a hard structure upon which an intricate biological
community is built. Similar to coral reefs, oyster reefs are `biogenic' (formed by the accumulation of
colonial animals) and provide structure and surface area for numerous other temporary and permanent
species.
Providing complex habitat structure is the most fundamental of ecosystem services that oysters
provide. The structure provides a place for algae and non-mobile invertebrates to attach, as well as a
place for mobile invertebrates and fishes to be protected from predators. Although the relationships
between sportfish and oyster habitats are not as well studied as in other estuarine habitats such as
seagrass beds,they are considered essential fish habitat.
The numerous ecosystem services provided by oysters can be summarized into three general
categories: habitat provision, water quality improvement, and shoreline stabilization. Oyster reefs
provide habitat to a diverse array of flora and fauna. The role of oyster habitat to the estuarine food
chain is highly significant, as discussed in the previous paragraph. Through their feeding process
oysters filter large quantities of water which transfers energy and material from the water column to
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the benthic community, subsequently reducing turbidity and water column nutrients. Through bio-
deposition, nutrients are made available to the flora and fauna which comprise the complex oyster bar
food web. Additionally, oyster reefs stabilize sediments, shorelines and adjacent habitats by buffering
wave energy, further aiding water quality.
Deteriorating conditions related to closure of Clam Pass is thought to have resulted in the
disappearance of oyster bars in the system (REFERENCE); though some re-occurrence has been
observed to the south of the pass in the last few years during seagrass transect monitoring. Oysters
have been documented around the perimeter of Outer Clam Bay in past years monitoring efforts.
A 2011 benthic habitat assessment conducted by the Conservancy of Southwest Florida found living
oyster clusters in the upper reaches of Upper Clam Bay (a single cluster), in the tributarybetween
Outer and Inner Clam Bays(a single cluster), and throughout the shoreline of Outer Clam Bay.
Management concerns related to oyster growth are similar to the seagrass concerns, namely protection
from recreation users,water quality, and flushing.
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Other bivalve mollusks
In addition to oysters,the 2011 benthic habitat assessment conducted by the Conservancy of Southwest
Florida also found two other bivalves within the Clam Bay system. The pointed Venus clam
(Anomalocardia auberiana) and the stout razor clam (Tagelus plebeius) were both observed. Turrell,
Hall and Associates benthic surveys found several beds of southern hard clams (Mercenaria
campechiensis) also present within the system.
These mollusks are generally found within the shoal and tidal flat areas of the system and could ble
susceptible to impact during dredging or other disturbance operations. Management concerns would
be protection from recreational users, water quality, flushing, and dredging.
Polychaete Worms per KW
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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.
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Hardbottom outcrop off of Clam Pass
Collier County has mapped this resource through side scan sonar surveys in 2005 and 2009 as part of
its beach renourishment project. The information received from the County shows that the landward
edge of this habitat is located approximately 250 to 300 feet offshore from the Pass.
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Management concerns related to this habitat include recreation use and potential turbidity impacts
resulting from dredging or other management activities within the Clam Bay NRPA.
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Invasive,Non-native and Problem Species
In an ecological context, an invasive species is one that is aggressive in growth and expansion of range
and tends to dominate other appropriate native species. Its establishment and dominance can cause
widespread harm to an ecological system by altering the species composition, susceptibility to fire and
hydrology of an area. Non-indigenous species (i.e.,non-native or exotic species) are those that have
been introduced purposefully or accidentally to an area outside their normal range. The characteristics
of some of these species (high rate of growth/reproduction,no natural predators, easily dispersed, able
to out-compete native species)make them invasive. Some indigenous species (a species whose natural
range included Florida at the time of European contact circa 1500 AD or a species that has naturally
expanded or changed its range to include Florida) may also become invasive. Invasions by native and
non-native species often follow an alteration to ecosystem function, disruption of the food web, large-
scale fragmentation of an ecosystem and/or disturbance (e.g., clearing, fire, drought, etc.) of an area.
While some native species may become invasive, the establishment and dominance of non-native
species is of particular concern. The exotic species documented within the NRPA and those that have
a potential to occur within the NRPA are discussed in the following section.
Invasive and Problem Plant Species
The Florida Exotic Pest Plan Council (FLEPPC) maintains a list of exotic plans that have been
documented to (1) have adverse effects on Florida's biodiversity and plant communities, (2) cause
habitat loss due to infestations, and(3) impact endangered species via habitat loss and alteration. To
date, 9 non-indigenous plant species have been detected within the Clam Bay NRPA which are listed
by FLEPPC as Category I exotics. FLEPPC defines Category I plants as those that alter native plant
communities by displacing native species, change community structures or ecological functions, or
hybridize with natives. Category II plants have increase in abundance or frequency but have not yet
altered Florida plant communities to the extent shown by Category I species. These definitions do not
rely on the economic severity or geographic range of the problem,but rather on the documented
ecological damage caused by these plants (FLEPPC 2007).
FLEPPC Category I plants observed within the Clam Bay NRPA boundary:
- Brazilian Pepper(Schinus terrebinthifolius)
- Melaleuca (Melaleuca quinquenervia)
- Australian Pine(Casuarina equisetifolia)
- Beach Naupaka(Scaevola taccada)
- Earleaf Acacia(Acacia auriculiformis)
- Shoebutton Ardisia(Ardisia elliptica)
- Air Potato (Dioscorea bulbifera)
- Lantana(Lantana camara)
- Old World Climbing Fern(Lygodium microphyllum)
Methodology outlining the management activities that will be used to treat exotics is found in Chapter
6 of this Plan.
LISTED SPECIES
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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, 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
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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.
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 Bay NRPA is contained within the LOGG-N-
27 segment of this proposed critical habitat area.
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Gopher Tortoise (Gopherus polyphemus)
Gopher tortoises and their burrows are found along the coastal strand portions of the Clam Bay 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 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 Bay 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.
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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
PLANT SPECIES -List to be added based on FL UCFCS Mapping
ANIMAL SPECIES
The following lists of species have been observed within the Clam Bay NRPA and the adjacent Pelican
Bay development areas. These lists are not all inclusive but represent a wide array of the species found
within and adjacent to the Clam Bay NRPA habitats.
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
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
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Pigfish. Orthopristus chiysoptera
Pinfish Lagodon rhomboides
Pipefish Syngnathus spp.
Puffer Sphoeroides parvus
Sailfin molly Poecilia latipinna
Sand perch Diplectrum bivittatum
Scaled sardine Harengula pensacolae
Sea robin Phonon's 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
Tidewater silverside Menidia pen insulae
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
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American Alligator Alligator mississippiensis
Brown anole Anolis sagrei
Eastern glass lizard Ophisaurus ventralis
Green anole Anolis carolinensis
Southeastern five-lined skink Eumeces inexpectatus
Brown basilisk lizard** Basiliscus vittatus
Cuban knight anole** Anolis equestris
Cuban treefrog Osteopilus septentrionalis
Eastern narrow-mouthed toad Gastrophryne carolinensis
Eastern spadefoot toad Scaphiopus holbrookii
Giant marine toad** Rhinella marina (fka Bufo marinus)
Green treefrog Hyla cinerea
Oak toad Anaxyrus quercicus
Southern leopard frog Lithobates sphenocephalus
Southern toad Bufo terrestris
Squirrel treefrog Hyla squirella
Chicken turtle Deirochelys reticularia
Pond(yellowbelly) slider Trachemys scripta scripta
Florida redbelly cooter Pseudemys nelsoni
Penninsula cooter Pseudemys peninsularis
Striped mud turtle Kinosternon baurii
Florida box turtle Terrapene carolina bauri
Florida softshell turtle Apalone ferox
Florida snapping turtle Chelydra serpentina osceola
Gopher tortoise Gopherus polyphemus
Green sea turtle Chelonia mydas
Loggerhead sea turtle Caretta caretta
Birds
COMMON NAME SCIENTIFIC NAME
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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
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
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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
Mottled duck Anas fulvigula
Mourning dove Zenaida macroura
Muscovy duck Cairina moschata
Northern cardinal Cardinalis cardinalis
Northern gannet Mortis bassanus
Northern parula Parula americana
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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
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Willet Catoptrophorus 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 brariliensis
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 Fells catus
Bobcat Lynx rufus
West Indian manatee Trichechus manatus
Bottle-nosed dolphin Turciops truncatus
HYDROLOGY
Hydrological regime, sometimes referred to as the surface water or surficial hydrology, in simple terms
describes the long term spatial variation in the water depths and period of inundation within a wetland
system. This is because the surficial hydrology has both horizontal and vertical components and
provides key ecological functions to the mangrove forest. (Lewis,pers. comm. 2008)
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With respect to the horizontal component, incoming water (both tidal and surface water run-off) into
an estuary 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 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 estuary 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.
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.
Another key aspect of the surficial hydrology is the vertical location of the water level elevation
relative to the sediment elevation. Specifically, the mean low water (tide) elevation has to be
sufficiently lower than the sediment elevation in order for sediments to drain during low tide. A
persistent high surface water elevation stops sediment drainage and results in anoxic sediment and the
accumulation of toxic waste products. The 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.
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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 a sufficient volume of water on the ebb tide to scour
out the inlet naturally, otherwise the inlet will, over time, continue to close. This is particularly true
during periods of high wave activity and low tidal ranges. (Turrell 1995; Tackney 1996). The six
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, Hummiston 2010).
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).
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
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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 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.
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Approximate locations of Drainage Basins within the Pelican Bay Development (photo is oriented with north up and west
to the left).
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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(from an engineering,not historical, standpoint), 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
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 the exhibit below. There are currently nine 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.
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)
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• Nitrate-Nitrite (N)
• Nitrite (N)
• Nitrogen-Total Kjeldahl
• Orthophosphate(0PO4)
• Pheophytin
• Phosphorus-Total
• Residues-Filterable(TDS)
• Silica(SiO2)
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' �" Kr'
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q r^r � � �4 1.- )?1tili4 t,9 & fi t-'16" i` g... '&41'401
� ." .;
40;',4.; ,.4:14#' •yy"` -,t ;� -'« m '' 3: . 0:!'i 4:4';'-.. ..,,, -141:1'-:-.11..;,
*4. ,,,,; '�:, _ ,,,�e'` ate
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rs,;'f1Yfixr--` dam`-;: y .�' ». ++�1C�p€,, "e.,=. 4. Fi 3 isrt.� �t
!. ,,.. , _.% '*-44-.-;A,...:;;,ilit ligki.iiti..0,1; .' ,';',.',"4",,,T•
°'''17.,I.t4C1111 jo.% 1 i„,/,„ ),-,„;4WIte,...-- — --- .--- , i , --
i��! tS�/ - ..KK f magyy'f'`Jw,
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. ' yam d
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«a-,.... ori.,s,.,. d�. <
Sampling Locations
Water quality sampling results of nutrient loading seem to indicate that the development stormwater
management system is doing its job. No evidence of nutrient loading has been observed within the
Class II waters though several spikes and elevated nutrient(N and P) levels have been observed from
the testing locations along the berm. It is believed that the spikes observed are correlated with
fertilizer application within the community.
The Florida Department of Environmental Protection(FDEP)conducted water quality sampling within
the Clam Bay NRPA in 2012. Based on their sample results, FDEP had made an initial determination
that Clam Bay could be impaired for both Dissolved Oxygen and Copper. Subsequent coordination
between FDEP, PBSD, the Pelican Bay Foundation, and involved consultants, FDEP made a
determination that the oxygen levels in Clam Bay were natural and the system was not listed as
impaired for DO.
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FDEP did determine that the system was impaired for copper and was placing the system on the
Everglades West Coast verified list for copper with a medium TMDL priority(5 to 10 years for TMDL
development). Subsequent copper testing undertaken by PBSD has also shown periodic elevated
levels of copper within the Clam Bay Class II waters.
FDEP acknowledged that the Pelican Bay community was working on an upland stormwater and
nutrient management program that was designed to reduce nutrient and copper inputs into the
stormwater system. Once completed, this program can be given to FDEP for review and if satisfied
with the anticipated reduction of copper resulting from the implementation of the plan,the system
could be removed from the impaired list. While the upland nutrient management plan is not part of
this NRPA Management Plan, PBSD will work closely with the Pelican Bay Foundation to coordinate
and share information, and to integrate management decisions and activities into this Plan where
appropriate.
ARCHAEOLOGICAL RESOURCES
The Florida Division of Historical Resources Master Site File lists three known archaeological sites
within the Clam Bay NRPA boundary. All three are located within the mangrove forest habitat. Two
of the sites (CR476 and CR547) are located north of the Pass and south of Inner Clam Bay. The third
site(CR576) is located south of the Pass and north of the Clam Pass Park boardwalk.
Site CR476 is identified as a prehistoric campsite and shell midden possibly supporting the use of
several cultures dating from 8500 B.C. to A.D. 1700.
Sites CR547 and CR576 are identified as shell middens which were in use between 1000 B.C. and
A.D. 1700.
All three of the sites are within the mangrove forest and outside of the footprint of any previous or
future anticipated dredging activities.
INLET DYNAMICS— To be added from Engineer's report(s)
RECREATIONAL USE
Clam Bay's dense forest of mangroves significantly limits walking in the preserve. Most walkers
seeking to enjoy the rich natural environment of Clam Bay use the three boardwalks that cross the
preserve and provide access to the beach. Residents and guests of Pelican Bay residents use the
northern and middle boardwalks. The southern most boardwalk is open to the public and accessed
from the parking lot at the south end of the system. Trams are used on all three boardwalks to transport
those choosing not to walk on the boardwalk to the beach.
Kayaks and canoes are used by those wanting to enjoy the natural setting and serenity of Clam Bay's
waterways. There is a public launching area adjacent to the parking lot at the south end of the bay, and
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there is also a private launch for Pelican Bay residents on the northern boardwalk. The canoe/kayak
trail is clearly designated by canoe trail markers from Outer Clam Bay to Upper Clam Bay.
Fishing and swimming are also popular pastimes. Fishing can be done from the boardwalks and canoes
or by wading into the water. Swimming is usually confined to the beach areas, but some swimmers and
waders, if conditions permit,venture into Clam Pass.
The operation of motorized watercraft in Clam Bay is restricted by Collier County Ordinance 96-16
that requires vessels with motors to travel at idle speed with no wake throughout the Clam Bay system.
The relatively shallow waterways of the system, in conjunction with the boardwalk heights, limit the
size and drafts of motorized watercraft. The residents of the Seagate neighborhood immediately south
of Outer Clam Bay have historically utilized motorized watercraft in Clam Bay but this use is still
subject to the County ordinance. Violation of the ordinance is a civil infraction for which a fine may be
levied. Occasionally motorized vessels, including jet-skis or other personal watercraft, have been
reported to be in violation of the ordinance. Efforts to identify and report violators will continue to
insure that Clam Bay is not only a safe place for all its users,but that its unique environment is
protected. In the future should any adverse effects on Clam Bay's natural resources or water quality be
found to be related to motorized watercraft, additional management options will be explored to
ameliorate these adverse effects.
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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 17, 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
re-vegetation.
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 (which in 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. Agency comments and concerns which arose as part of the permit review led to the creation of
the 1998 Clam Bay Restoration and Management Plan. The Plan addressed agency concerns at the
time and included provisions for adding one-way flap gates to the Seagate culverts, dredging within
three sections of the creek north of Clam Pass, a network of hand dug channels throughout the forest
area, in addition to the dredging of the Pass. This permit was issued in 1998 and the Management Plan
created in support of the permit has been the guiding document for the maintenance activities
undertaken in the Clam Bay system since then.
It is anticipated that DEP and USACOE 10-year permits will be sought in conjunction with this new
Management Plan. The permits will allow for ongoing maintenance and/or 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 by the PBSD Board and Collier
County Commissioners before seeking any additional permit(s) which may be necessary for the
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modified activities. Additional investigations which may be undertaken at a later date to look at, for
example, faunal investigations, more in-depth water quality concerns, or other issues that may arise as
a result of stakeholder discussions could also necessitate permitting which will have to be reviewed by
the PBSD and BOCC prior to any such permit applications being submitted. 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
Bay 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.
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Department of Environmental Regulation Modification of Surface Water Management Permit No.:
11-00065-5
Date of Issue: December 15, 1983
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/no wake zones in the Clam Bay system.
Depaitment 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.
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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 and installation of one-way check valves on the culverts (pages 45 — 50 of the CBRMP). 2)
Clam Pass main channel dredging for Cuts 1, 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 #1; 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.
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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.
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.
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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.
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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6.0 Management Plan Goals and Objectives
The following goals and objectives for the management of the Clam Bay Natural Resource Protection
Area were developed in accordance with the directives of the Collier County Board of County
Commissioners (BOCC) and the Pelican Bay Services Division, which serves as an advisory board to
the BOCC. 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 held 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 Clam Bay NRPA while
minimizing negative environmental impacts.
Goal 2 -Maintain and protect the native floral and faunal communities.
Goal 3 - Manage and improve water quality.
Goal 4—Protect the integrity of known archaeological sites within the system.
Goal 5 -Address recreational uses with emphasis on passive recreation.
Goal 6 -Improve public awareness and involvement.
GOAL 1 - Provide sufficient tidal exchange to maximize benefits to the Clam Bay NRPA while
minimizing negative environmental impacts.
A.Establish guidelines to help determine when dredging is necessary.
Monitoring of the Pass and internal waterways will provide information to determine if
dredging is necessary. Bathymetric surveys of cross-sectional areas of the Pass, tide gauge
data, and biological indicators can all be used to indicate when dredging is needed. Dredging
for the tidal exchange benefits necessary to maintain or improve environmental aspects of the
system will be done. Dredging for navigation or beach renourishment will not be done.
a.) Conduct, at a minimum, annual surveys of the Pass.
b.) Maintain tidal gauges in good working order. Collect information periodically to
insure gauges are in good working order and data loss due to malfunctioning
equipment is minimized.
c.) Maintain backup gauges to minimize data loss due to malfunctioning equipment.
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d.) Collect annual biological information as outlined under Goal 2 for use in
determining when dredging activities might be warranted, and what impacts could
be associated with the dredging.
B. Minimize dredge footprint(s) to the least environmentally damaging practicable
alternative.
Dredging should be conducted only in those areas necessary to achieve the desired flow
improvements.
a.) Collect current survey data and cross sectional areas before establishing the dredge
footprint for each dredging event.
b.) Conduct floral and faunal monitoring within and adjacent to proposed dredge
footprint area(s). If unacceptable impacts will occur to floral or faunal
communities, explore options to modify footprint to achieve necessary flow
characteristics while protecting to the greatest extent possible the other floral or
faunal components.
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.
D. Provide for appropriate drainage of fresh water by maintaining internal creeks and
hand dug channels and modifying or augmenting hand dug channels as needed.
The original 1995 die-off of mangroves was due in large part to drainage problems in the upper
portions of the system. Maintaining the network of hand dug channels and the ability of the
upper reaches of the forest to continue to drain is important to protecting the restoration
improvements which have been realized to date.
a.) Conduct annual monitoring of the hand dug channels. Prioritize maintenance needs
and undertake maintenance clean outs of as many areas as budget allows.
b.) Conduct annual visual monitoring of the creeks connecting the three bays. Survey
sections as needed if visual inspections or tidal indicators document shoaling or
blockage sufficient to adversely impact flushing capacity.
c.) Coordinate with appropriate agencies as needed if conditions dictate maintenance
dredging is needed in interior creeks.
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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.
a.) Establish permanent vegetation monitoring plots or transects in all habitats.
b.) Establish reference photo points in all habitats.
c.) Create species lists to document floral components in each habitat.
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.
a.) Identify actual and potential locations of listed species.
b.) Conduct species specific monitoring prior to any destructive management activity
(i.e dredging, exotic removal, etc.)to insure no protected species are present.
c.) Develop educational information to make public aware of the presence of listed
species and what they can do to avoid adversely impacting them.
d.) Explore partnership opportunities with outside sources such as the Conservancy of
Southwest Florida and Florida Gulf Coast University to further investigate floral
and faunal components of the system.
C. Protect and maintain vegetative communities
Regularly inspect habitats for invasive exotic and nuisance vegetation. Remove invasive
exotics and nuisance vegetation when observed without damaging integrity of native
communities. Conduct periodic monitoring of habitats to track changes over time. Restore
native plants as appropriate throughout the system.
a.) Periodically inspect habitats utilizing transects, monitoring plots, and photo points
established under Goal 2.A. for consistency.
b.) Remove invasive exotic and nuisance vegetation from all habitats as budget allows.
Utilize contractors familiar with local species and accomplished at conducting
exotic removal from the varied habitats. Conduct pre-work surveys to identify any
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protected species in work area. Protect other native vegetation to the maximum
extent practicable during exotic removal activities.
c.) Develop educational information to make public aware of exotic vegetation and
what they can do to help eliminate them.
D. Protect and where possible enhance wildlife utilization of the NRPA
Conduct periodic monitoring of wildlife populations including nuisance wildlife within the
NRPA boundaries. Identify utilization priorities and enhance protection as needed to insure
that continued use is viable.
a.) Conduct periodic species or habitat specific surveys and monitoring to document
wildlife use of habitats within the Clam Bay NRPA.
b.) Develop strategies to minimize impacts of nuisance wildlife on habitats and native
wildlife within the NRPA boundary.
c.) When possible, explore habitat enhancements to promote wildlife utilization within
the Clam Bay NRPA. (e.g. bat houses, nesting boxes or platforms, limited or no
entry areas, etc.)
d.) Explore partnership opportunities with outside sources such as the Conservancy of
Southwest Florida and Florida Gulf Coast University to enhance habitats for
wildlife utilization within the NRPA.
GOAL 3 -Manage and improve water quality
A. Insure appropriate freshwater inputs and drainage
Freshwater inputs and drainage 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.
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. Proposed activities within the
development area which could affect flows into the system (i.e changes to stormwater
management system, changes to the berm, etc.) will be examined to insure that adequate flows
into the estuary are maintained.
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B. Coordinate with adjacent upland 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.
a.) Continue monthly water quality data collection.
b.) Examine and review data on a quarterly basis. Attempt to identify any water quality
concerns in a timely manner rather than waiting for annual reviews.
c.) Explore partnership opportunities with outside sources such as the FGCU or other
Universities to explore water quality concerns and opportunities within the Clam
Bay NRPA.
GOAL 4 -Protect archaeological sites within the system
A. Identify archaeological sites and protect them from impacts.
Insure that archaeological sites identified by the Florida Master Site file are not impacted by
management or recreational activities. Periodically monitor sites for invasive exotics and
maintain the native vegetative community. Protect sites from vandals or looting as possible.
GOAL 5 -Address recreational uses with emphasis on passive recreation
A. Maintain access to facilities for intended uses
Conduct periodic inspections of access points and visitors facilities. Trim vegetation as
needed, and as allowed by the permitting agencies, to maintain boardwalk access and open
waterways for canoe and kayak passage.
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B. Maintain existing canoe trail
Conduct periodic inspections of canoe trail signage and markers. Replace or repair permitted
signage and support posts as needed. Develop and provide map of canoe trail for paddlers.
C. Maintain existing signage relative to boater and swimmer use of the system
Conduct periodic inspections of informational and regulatory signage. Replace or repair
permitted signage and support posts as needed. Coordinate with outside regulatory agencies
(FWC or Sherriff's Dept.) to enforce regulatory"Idle Speed/No Wake"restrictions.
D. Maintain existing signage or develop new signage to educate visitors
Maintain and develop site specific signage or handouts to educate visitors on plant
identification and general habitat information, included should be information on how to help
preserve habitats and prevent unwanted impacts to the plants and animals sharing the area.
E. Define responsibilities for vegetation and litter control in Clam Pass Park
Coordinate with Collier County Parks and Recreation to define individual and shared
responsibilities within the NRPA boundary.
GOAL 6 -Improve public awareness and involvement
Continue to foster stakeholder involvement through public meetings.
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Clam Bay NRPA 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 Bay 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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February 14,2014
Ver.4.0
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 BioIndustries,technical paper.
22. Heald, Eric J., July 1983, Populations of Melampus coffeus and Cerithidea scalariformis West
of Upper Clam Bay, Collier County, Florida, Tropical Biolndustries, 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 BioIndustries, 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.
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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.
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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.
83
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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.
84
ResnickLisa
From: Susan O'Brien [naplessusan@comcast.net]
Sent: Monday, February 17, 2014 9:58 AM
To: Tim Hall; ResnickLisa
Subject: Fwd: Clam Bay NRPA Management Plan 4.0
Attachments: Clam_Bay_Mgmt_Plan_4.0_photos_deleted.rtf
FYI.
We'll discuss Linda's suggested revisions as well as others' suggestions at tomorrow's meeting.
Thanks,
Susan O'Brien
Begin forwarded message:
From: "lor3lor3@aol.com" <lor3lor3@aol.com>
Date: February 17, 2014 3:53:01 AM EST
To: naplessusan(cr�,comcast.net, nfn16799@naples.net, mikelevy@embargmail.com
<mailto:mikelevy@embargmail.com> ,jchicurel@gmail.com, hobodory@comcast.net
Cc: lor3lor3@aol.com
Subject: Clam Bay NRPA Management Plan 4.0
Dear PBSD Clam Bay Committee Member,
I am writing because I will be out of town for the next three days, and will not be able to attend the Clam
Bay Committee meeting on Tuesday.
Please see attachment. I would appreciate it very much if you would read the revisions I made on the
Clam Bay NRPA Management Plan 4.0, and consider incorporating them in the Plan as I think they are
important and would help PB. The attachment has only the pages with my revisions on them. As for the
acronyms, it is not important if they are BCC or BOCC, DEP or FDEP, so on and so forth. However, they
should be consistent throughout the document. There are a few questions regarding the permits, could you
please ask Tim Hall for the answers?
In my opinion,there is nothing more important than making this Management Plan clear, factual,
precise, and concise; leaving no room for misinterpretation. Inconsistency and ambiguity in language allows for
misinterpretation, and gives rise to costly disputes later on. A case in point is the ambiguous statement in the
1998 Management Plan regarding installation of markers in Clam Bay. This problem has cost PB a great deal of
time, effort, and attorney fees.
Silence or absence of language also allows for misinterpretation and disputes. An example of this is the
original County ordinance providing PBSD the authority to manage the conservation/preserve areas in Pelican
Bay. It seems to me the conservation/preserves areas include the mangrove forest, Clam Pass, beaches, etc., in
other words, everything within the NRPA boundary. Apparently, this language was not as clear as it appears,
requiring subsequent ordinances to amend and clarify it. Oftentimes, County Attorney Klatzkow, when asked
by the Commissioners what a contract said about certain subject in question, would answer that the document
was silent on the subject, meaning it could be open to interpretations.
Therefore, I strongly feel that appropriately worded statements (possibly supported by reasons) about no
Lateral (Red& Green)navigational markers will be installed in the Clam Bay NRPA; no dredging for flushing
of Venetian/Moorings Bay; and there is no historical connection to Venetian/Moorings should be clearly
expressed in the new Management Plan. These three issues surface repeatedly because no documents exist
stating that they are not allowed, or not true.
Additionally, the issue about the FDEP and USACE permits authorizing a dredge cut of 80 ft. wide at
the entrance of Clam Pass is false. I have the official permit applications and authorizations from the regulatory
agencies to substantiate this. It is time to stop perpetuating this unfortunate mistake made by H&M in 2006-
2007 at the request of the Coastal Zone Manager. There is no reason now to include this erroneous information
in the new Management Plan or the new 10-year dredge permit . It can be misleading.
Thank you for your kind attention and consideration.
Sincerely,
Linda Roth
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
CLAM BAY NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
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Ver.4.0
TABLE OF CONTENTS
1.0 Introduction
Purpose of the Clam Bay NRPA Management Plan.
Development of the Clam Bay NRPA Management Plan
Role of Pelican Bay Services Division
2.0 Clam Bay Location, Setting,And Historical Overview
Maps, description of Pelican Bay and the estuary system
Natural history of the system and pass
Historical time line of the system
Time line of Clam Bay NRPA establishment
1995 mangrove die-off and related causes
Restored characteristics of Clam Bay
3.0 Resource Descriptions
Soils
Topography
Climate
Natural Communities
Exotic Species
Listed Species
Other Wildlife Species
Hydrology
Water Quality
Archaeological Resources
Inlet Dynamics
Recreational Use
4.0 Authorized Construction Activities
List of permits and work undertaken to date
5.0 Management Goals and Objectives
Management action/work required,performance criteria and monitoring,responsible
entities, timeframe
Shouldn't the numbers below begin with 5.1, 5.2, etc. or Goal I, Goal 2, etc.?
6.1 Provide sufficient tidal exchange to maximize benefits to the Clam Bay NRPA
while minimizing negative environmental impacts.
6.2 Maintain and protect the native floral and faunal communities
6.3 Manage and improve water quality
6.4 Protect the integrity of known archaeological sites within the Clam Bay NRPA
6.5 Address recreational uses with emphasis on passive recreation
6.6 Improve public awareness and involvement
(Submitted by Linda Roth received 2/18/2014)
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
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Ver.4.0
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 the Clam Bay Natural Resource Protection Area (NRPA). This plan will form
the basis by which future management decisions can be made by identifying the appropriate
management techniques necessary to protect, preserve, restore, maintain and monitor the
natural resources and their uses within the Clam Bay NRPA.
This plan, in addition to providing a brief historical perspective of activities undertaken within
this system, will identify management goals and objectives; develop methods to achieve these
goals and objectives; and develop implementation, assessment, and evaluation strategies that
strive to balance resource protection with passive recreational use. The Plan will draw from
the 1998 Clam Bay Restoration and Management Plan, input from multiple interested
stakeholders, and the findings of 15 years of biological and hydrographic monitoring activities
within the system, to outline goals for future enhanc h.cnt„ to management and maintenance
of the ecosystems throughout Clam Bay.
The Clam Bay NRPA Management Plan and any subsequent revisions shall be submitted to the
Collier County Board of County Commissioners (BOCC) for approval. When approved, this plan
will serve as a tool for future permitting and other management activities necessary to protect,
preserve,restore,maintain, and monitor resources within the system.
Development of the Management Plan
Turrell, Hall &Associates served as the principal consultant for the management plan. This
consultant firm has a long history of work in the Clam Bay NRPA and was responsible for the
implementation the Clam Bay Restoration and Management Plan(1998)that resulted in the
successful restoration of Clam Bay's mangrove forest. The coastal engineering firm of
Humiston& Moore, Inc.provided input and monitoring data for the 2014 Management Plan
relative to the Clam Pass and the dredging activities and templates.
The PBSD Clam Bay Committee,(delete comma)which consists of five members of the Pelican
Bay Services Division Board, an advisory board to Collier County's Board of Commissioners,
met regularly in 2013 and 2014 and provided input and direction to the consultants. Additional
regular input was provided by representatives of the Conservancy of Southwest Florida; the
Mangrove Action Group; and the local Calusa litreuell Group of the Sierra Club. All Committee
and Board meetings were properly noticed,open to the public, and allowed audience
participation.
Input was also solicited via notices to about 35 area businesses, government officials and
employees, condominium associations, and individuals who regularly use Clam Bay. These
representatives were invited to participate in two meetings held in the spring of 2013. They were
also notified in , 2014 that a draft of the management plan was available on the PBSD's
1 1
(Submitted by Linda Roth received 2/18/2014)
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
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Ver.4.0
website and they were invited to send their comments to the PBSD's office. (A list of these area
people/organizations is on p. .)
Another Board member will be Chairman after 3/31/14.
Pelican Bay Services Division Turrell, Hall &Associates
Tom Cravens ? —Chairman Tim Hall—Project Manager
801 Laurel Oak Drive, Suite 302 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
2
2
(Submitted by Linda Roth received 2/18/2014)
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5. Discussion of latest draft of management plan
CLAM BAY NRPA MANAGEMENT PLAN(DRAFT)
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Ver.4.0
Role of the Pelican Bay Services Division
In order for the management and enhancement maintenance of the Clam Bay 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 Pelican Bay is a dependent special district known as the Pelican Bay Municipal
Services Taxing and Benefit Unit with PBSD as its governing body. 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/PBSD 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 (1998). and the recovery of the mangrove die-off areas.
P e r action by the Collier County commissioners, the responsibility for the monitoring and
maintenance of Cess Clans Pass was given to the Collier County's Coastal Zone Management
Department from 2009 to 2012. In 2013, the Collier County BOCC returned responsibility of
the Pass to PBSD via Ordinances 2013-19 and 2013-61. It is under the PBSD's direction that
this current i\ianagement Plan has been written.
As a dependent special taxing and benefit district, the Pelican Bay MSTBU/PBSD is an arm of
Collier County government and makes recommendations to the Collier County Board of
County Commissioners(BBCC). The PBSD implements its defined responsibilities within the
Pelican Bay community; sets its own budget and agenda; and regularly submits them to the
BCC for approval. The BCC has regularly approved the Clam Bay management activities
- . - - . •_ . - . . and authorized the development of the 204-4 Clam Bay NRPA
Management Plan. (2014). The PBSD's effective working relationship with the BOCC is
expected to continue as the PBSD serves as the official manager of the 2014 Management Plan
which is consistent with Ordinances 90-111, 2002-27, 2013-19, and 2013-61 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, el:that:tee preserve,
restore, monitor, and maintain the natural communities and ecological integrity of the
Clam Bay NRPA.
The PBSD has several attributes which already make it a logical guiding force in the
management and maintenance of Clam Bay. The PBSD:
• Is located within the Clam Bay drainage basin;
• Has an advisory board made up of residential, and business members within Pelican Bay;
• Garners fiscal support collected from local special assessments (non ad valorem taxes);
• Is accessible by the public due to its local governing board and advertised public monthly
meetings;find 3
(Submitted by Linda Roth received 2/18/2014)
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
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Ver.4.0
3
4
(Submitted by Linda Roth received 2/18/2014)
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• Has demonstrated a long-term commitment to the Clam Bay NRPA and a successful
track record regarding its preservation,restoration and maintenance 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 gives 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.
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2.0 Overview of the Clam Bay NRPA
The Clam Bay NRPA is a 570-acre estuarine system consisting of sandy beaches, shallow bays
and creeks, seagrass beds, mangrove forests, and Clam Pass on the west coast of Collier County
in southwest Florida. The Clam Bay system is part of the Cocohatchee-Gordon River
Transition, referred to by Collier County Department of Natural Resources as Coastal Zone
II. It is one of the few remaining estuarine systems in the Cocohatchee-Gordon River
Drainage System. Historically, Clam Bay was tidally connected to the Gulf of Mexico via
Wiggins pass to the north, Doctor's Pass to the south, and centrally located Clam Pass (Collier
County, 1994, Tropical Biolndustries, 1978). These connections were eventually severed with
the development of Vanderbilt Beach Road and Seagate Drive in the 1950s.
Today, the system includes three primary bays; Outer Clam Bay(southernmost), Inner Clam Bay
(central), and Upper Clam Bay (northernmost), connected by a series of tidal creeks and
connected to the Gulf of Mexico by Clam Pass. 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 passive
recreational resource for local residents and visitors. The operation of small motorized
watercraft is limited to Idle Speed/No Wake per Collier County Ordinance 96-16.
The Clam Bay system is bounded on the north by Vanderbilt Beach Road and the Bay Colony
portion of the Pelican Bay development, to the south by Seagate Drive, and the Seagate and
Naples Cay developments, to the east by the Pelican Bay development and to the west by the
Gulf of Mexico and the Strand enclave of the Pelican Bay development.
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 forests intact and preserved around the bays. As mitigation for these
wetland impacts, the 570 acre preserve area, including the 35 acre beach park, was donated to
Collier County and eventually became the NRPA which is in place today.
Development of Pelican Bay 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 '/z 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
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near the berm. Six drainage basins operate on a gravity system to slowly move surface water
into the receiving area of Clam Bay.
Naples Cay is a high rise development consisting of 8 multi-story condominium buildings. The
community also includes pools, tennis courts, approximately 33 acres of park and preserve areas,
and two canoe and kayak launching piers. The first building started in Naples Cay in the late
1970's and the last was completed in 2002. Stormwater management is accomplished through
several internal detention areas before water flows into Outer Clam Bay.
The Seagate community is composed of single family residences. The community was first laid
out in the 1950's and still has a few undeveloped lots. Because development of this community
occurred so early, there is no community-wide stormwater management system in place.
Seagate is the only community adjacent to the Clam Bay NRPA that is allowed under the County
Manateee Protection Plan to have small motorized vessels and the associated boat docks along
three seawall canals.
Clam Bay was designated a Natural Resource Protection Area (NRPA) by Collier County in
1995 (See below for more details on the NRPA history). The purpose of the NRPA designation
is to protect endangered or potentially endangered species and to identify large connected intact
and relatively unfragmented habitats, which may be important for these listed species (Collier
County Growth Management Plan, Future Land Use Element).
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Clam Bay NRPA Vital Statistics
Total acres: Approx. 570 acres
Beaches: Approx. 1.5 miles
Mangrove: Approx. 420 acres
Open Water: Approx. 115 acres
Beach Park: Approx. 35 acres
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
Water Body Identification(WBID) 3278Q1
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 of Clam Pass were -2.5' to -1.0', and its
width ranged from 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.
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5. Discussion of latest draft of management plan
Natural History
Prior to development, the entire coastline of south Florida would have resembled the Clam Bay
ecosystem with meandering mangrove lined shallow waterways buffering sandy barrier islands
and natural terrestrial communities. Unique within the heavily developed coastal
community of Collier County, Clam Bay estuarine ecosystem is a valuable resource for
wildlife (particularly juvenile marine species and birds) as well as residents and visitors to the
area who enjoy the passive recreational opportunities the system offers such as photography,
kayaking, fishing, walking, swimming,bird watching, and beach going.
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. It 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) and approximately 1.5 miles of sandy
beach.
A man-made water management berm now divides natural and developed portions where
historically mangrove forests 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(Section 3.0)of this Plan.
Historical Overview
Historically, Clam Pass was a small part of a large system of shallow waterways and
interconnecting wetland communities extending from Lee County to Doctor's Pass. Anecdotal
evidence suggests that small boating activities took place within many of these interconnected
areas.
During the 1950's anis1-601s this system was isolated from adjacent natural mangrove lined
shallow creeks and 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 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, as well as aerial photographs of the Pass over time, is
provided in Section 3.0 of this Plan.
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. The
following time lines are intended as background information and as a factual recount based on
anecdotal evidence,press reports,published and unpublished reports.
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Time Line of important moments within the Clam Bay System
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
Clam Bay ecosystem is part of a connected system of barrier islands, mangrove forests,
passes and shallow waterways. The orientation of the beaches and passes would have
changed seasonally and with storms.
1952
Vanderbilt Beach Road is constructed as the Vanderbilt community is developed, eventually
severing connection with the Wiggins Pass system to the north.
1958
Seagate Drive is constructed as the mere Seagate community is developed; flow from north to
south is severed prior to excavation and construction of the deep man-made
Venetian Bay/Moorings Bay seawall system.
•
Vanderbilt Lagoon
..... _ . Outer Clam Bay
Upper Clam Bay
Venetian Bay
Circa 1960 Aerial Photograph Circa 1952 Aerial Photograph
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.
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1983
Tropical Bio-Industries produce biological reports:
• Fish populations of tidal ponds west of Upper Clam Bay
• Populations of Melampus coffees (Coffee bean snail) and Cerithidea scalariformis (Ladder
hornsnail)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 Department of Natural Resources (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.
Clam Pass was mechanically dredged to re-open. Approximately 700 cubic yards of material
were removed from the mouth of the inlet and the south bend of the channel. Material was
placed south of the Pass. Multiple closures of the inlet occurred during the construction process.
1990
Pelican Bay Improvement District becomes a dependent district of Collier County called the
Pelican Bay MSTBU/PBSD. Services Division.
1992
The area of dead mangroves is reported at 7 acres.
1994
20 acres of mangroves are reported dead.
1995
Clam Bay is approved by the Board of County Commissioners as Collier County's first Natural
Resource Protection Area(NRPA).
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Clam Pass closes following a winter storm event. Emergency dredging permit issued allowing
opening of the Pass, but no work farther back than 600 feet. Mechanical dredging is undertaken
removing approximately 5,000 cubic yards of material from the entrance of the Pass.
1996
Clam Pass closes following a winter storm event. Permits to open Clam Pass received from
FDEP and USACE. Mechanical dredging event carried out at the entrance of the Pass.
In summer and fall blasting and hand excavation were permitted and completed in 1997.
Mangrove die-off area estimated at 50 acres.
1997
Clam Pass, on the verge of closing following a winter storm event is mechanically dredged again
under modification to 1996 Permits. Interior portions of the flood shoal were dredged to station
6+10.
1998
Clam Pass was on the verge of closing again following a winter storm event. A mechanical
maintenance dredging event was carried out under modification to 1996 Permits. Interior
portions of the flood shoal were dredged to station 6+10.
Ten year permits received from F DEP and USACE for dredging Clam Pass and the
interior channels. Included adjustments to the Seagate culverts and installation of hand-dug
channels throughout the system. Associated monitoring work and storm and freshwater
studies were required.
1999
Dredging work associated with the CBRMP was implemented(Mgmt by PBSD) in the spring by
Ludlum Construction Company. Hydraulic dredging of Cuts 1, 2, 3, and 4 were carried out. A
30 foot entrance cut was dredged.
One-way northerly flow flap valves installed on Seagate culverts.
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.
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Pelican Bay Services Division
February 14,2014
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Ellicott Series 370HP Pumping Sand out of Clam Pass(1999)
2000
Hurricane Gordon impacts the area with no inlet closure.
2002
Hydraulic maintenance dredging of Clam Pass flood shoals between stations 3+10 and 18+00
(Mgmt by PBSD) completed to improve tidal circulation. The entrance of the Pass was not
dredged during this event.
Flap valves on Seagate culverts removed due to insufficient head differential causing them to act
as plugs instead of valves.
Canoe trail markers permitted and installed throughout Clam Bay system.
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.
2005
Hurricane Wilma comes ashore about 30 miles south of Clam Pass. More limb and leaf loss is
noted. Pass dee did not close.
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Pelican Bay Services Division
February 14,2014
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Hurricane damaged mangroves along bay 2005 Same mangroves along bay 2007
2007
Hydraulic maintenance dredging of Pass and entrance channel was conducted between Stations 0+00
and 18+00. The entrance of the Pass was dredged at 8022 (ft., not inches) width. (Mgmt by
Collier County Coastal Zone Management Dept.).
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 FDEP and USACOE permits for maintenance of the Pass expired 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.
Benthic Habitat Assessment study completed within the Clam Bay NRPA by the Conservancy of
Southwest Florida. Study provides comprehensive mapping of benthic habitat compositions and
distribution throughout the Clam Bay NRPA.
2012
Canoe trail markers and informational signage installed throughout Clam Bay.
The mouth of Clam Pass moves to the north near the Pelican Bay Beach Store. The northern shoreline
of the Pass is temporarily reinforced with the installation of concrete barriers.
Impacts from tropical storms Debby and lassic Isaac, along with numerous winter storm fronts
caused the closure of the Pass.
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Pelican Bay Services Division
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2013
A single event mechanical dredge is carried out in March under F DEP and U S ACOE permits
with an entrance cut of 45 feet. Beach compatible material is placed north and south of the Pass
above the mean high water line.
Development of a new Management Plan is initiated through stakeholder input and multiple public
meetings.
Time Line specific to the establishment of the Clam Bay NRPA
1976
Collier County Ord. 76-30 zoned coastal areas environmentally sensitive lands as ST(Sensitive
Treatment)
1977
Approval of the Pelican Bay PUD(Ord. 77-18)by Collier County. The PUD identified 98 acres of
coastal mangrove wetlands to be filled in for development while preserving 570 acres of ST lands as
the Pelican Bay Conservation Area. (35 acres in the south and 5 acres in the north would become parks
providing public beach access).
1981-82
Department of Army Permit(79K-0282) authorized the fill of the 78 acres of coastal wetlands (76
acres for residential development and 2 acres for public parking area). It required 570 acres including
Upper, Inner, and Outer Clam Bays, and their adjacent wetlands to be conveyed to Collier County and
to remain a conservation/preservation area in perpetuity for the use of the public in-pefpetttity. It also
prohibited dredging Clam Pass except to keep it open to the Gulf of Mexico.
1988
The Pelican Bay Conservation Area (570 acres)was approved and recorded as FL-64P by Congress
and became part of the Federal Coastal Barrier Resources System(CBRS).
1995
The Collier County Board of County Commissioners approved the County Natural Resources
Department's recommendation to establish the County's first Natural Resource Protection Area
(NRPA); stipulating that that it would have the same boundaries as the Pelican Bay Conservation Area
within the Pelican Bay PUD.
The Collier County Manatee Protection Plan is approved. It contains the recommendation to establish
an "Idle Speed/No Wake"zone throughout the Clam Bay/Clam Pass System.
1996
Collier County Ordinance 96-16: "The Clam Bay System Water Safety and
Vessel Control Ordinance"is approved. It establishes that the Clam Bay System is an"Idle Speed/
No Wake"zone.
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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.
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 P ass was excavated, the interior tides remained muted. Efforts to
maintain the P ass 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 mPingreve 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.
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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 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. Approximately 13 miles of these channels were
installed between 4440 late 2001 and 2005.
Biological monitoring work over the past fifteen 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.
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conditions. Natural vegetation consists of sea oats, sea grape, cabbage palm, and salt grasses. They are
commonly invaded by exotics such as Australian pine and Brazilian pepper.
TOPOGRAPHY
Topography is shown below using a Light Detecting and Ranging map (LIDAR)obtained from Collier
County. The elevations within the NRPA boundary range from +7.0 to -9.0 (???) NAVD88. The
surrounding lands are generally higher than the NRPA and generate the freshwater flows into the
preserve.
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landward until the wind speed drops below that needed to move the sand. Coastal vegetation is critical
for slowing wind speeds and causing sand to be deposited.
Landward of the highest tides, pioneer or frontal zone sites are stabilized by sand trapping action of
various rhizomatous grasses and low growing shrubs that are tolerant of salt spray. Only a few plant
species can tolerate the stresses of a dune environment, particularly frontal dune sites. Foredune plants
must be able to survive being buried by blowing sand, sand blasting, salt spray, salt water flooding,
drought, heat, and low nutrient supply. 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.
Many plant species that occur on dune areas have developed specific attributes to help them survive these harsh
environments. These include high growth rates, dense root systems, low profiles, and high flower and seed
production rates. Species common on the beaches of the Clam Bay system include; Sea oats (Uniola
paniculata), Seagrape(Coccoloba uvifera), and Railroad vine(Ipomoea pes-caprae).
In addition to the 35-acre Clam Pass Beach Park, south of the Pass, beach habitat also extends north.
all the way to Wiggins Pass. There is approximately 6,250 4.934 linear feet of shoreline north of
Clam Pass to the south end of the Strand community and approximately 3,250 feet of shoreline south
of the Pass to the north edge of the Naples Cay community. 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.
This particular habitat has been monitored periodically in terms of width as part of the Collier County
Beach renourishment program though no conclusive statements can be made about the floral or faunal
details of the ecotone over the years. Large scale generalizations based on the annual aerial
photographs can be made that the overall size, composition, and health of the habitat have remained
relatively stable and, with the exception of the areas immediately adjacent to the Pass, are mostly
unaffected by the status of the Pass.
Beach habitat within NRPA Boundary
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FLUCFCS Code 540—Bays(with and without connection to the Gulf)
The Clam Bay NRPA contains the three larger bays associated with Clam Pass (Outer, Inner, and
Upper) as well as the interconnecting waters shallow creeks and small open water areas.
Second in extent of aerial coverage within the NRPA boundary, it is the bays and interconnections
which serve as the life blood of the estuary.
This open water habitat serves as the basis for many other communities. Seagrass beds, oyster bars,
clam beds, and other benthic communities can all be supported to varying degrees with the open waters
of the bays and interconnecting creeks. As outlined below, several of these communities are present
within the Clam Bay NRPA and will be considered when deciding on management activities outlined
within this Plan
Multiple studies have indicated that the single most important thing that can be done to restore the
health of the Clam Bay system is to improve the total tidal flushing capacity of the system (Tackney
1996; Lewis 1996; Wilson Miller, et al 1996; Turrell 1996.). The dredging conducted within the Pass
and the interconnecting creeks, as well as the hand-dug flushing cuts, have been seen as the major
contributing factors to the restoration of the mangrove forest community within the system (Turrell
2008; Humiston&Moore 2003).
Tidal Pass
Clam Pass is the only open water connection to the Gulf of Mexico for the Clam Bay NRPA. The
exchange of seawater between Clam Bay and the Gulf is critical to the ability of the estuary to export
organic matter, as well as to help regulate excess salt and freshwater. It also supplies oxygen rich
water from the Gulf. In the absence of surface water circulation or tidal activity, estuarine habitats
such as mangroves can 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).
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.
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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 Pass. 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.
Management concerns related to the bays and associated creeks include maintaining sufficient flow
through them to accomplish flushing needs of the system, stabilization of the Pass without harming
other components of the NRPA, and educating recreational users of the NRPA of the need to protect
the shallow water habitats and the communities located therein.
Open Water habitat within NRPA Boundary
FLUCFCS Code 612—Mangrove Swamps
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,terrestrial and avian wildlife.
• Protecting coastal areas from storm surges and coastal erosion.
• Improving water quality by 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.
• Enhancing the atmosphere by absorbing carbon dioxide and reducing greenhouse gasses.
Approximately 65%of the Clam Bay NRPA is composed of the three most common mangrove species
in Florida. Namely, red mangroves (Rhizophora mangle), black mangroves (Avicennia germinans),
and white mangroves (Laguncularia racemosa) make up the mangrove forests within the Clam Bay
NRPA. All three species have special biological adaptations to cope with salt and unstable, mucky,
low oxygen soils that result from the tidal, hence continually waterlogged, environment. The
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FLUCFCS Code 911 -Seagrass Beds
Seagrasses are flowering marine plants of shallow, tropical regions. With a creeping growth form
connected by horizontal rhizomes they serve to trap and anchor sediment. Both the grass blades
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themselves and the surface area they represent provide food and attachment for marine species.
acid Seagrass beds are renowned for their value as nursery habitats, and are legally protected.
Shoal grass (Halodule beaudettei) along interior channel south of Clam Pass
Several areas within the Clam Bay system host seagrass beds, specifically Outer Clam Bay and
waterways just inside Clam Pass. Three species are commonly found in these Clam Bay waters; the
largest Turtle grass (Thalassia testudinum) with flat strap shaped leaves, the smaller shoal grass
(Halodule beaudettei (fra wrightii)) with narrow, flat blades and Paddle grass (Halphila decepiens)
with the smallest, paddle shaped leaves. Shoal grass is by far the most common though a small area of
turtle grass has persisted since the original 1998 dredging. Paddle grass is much more ephemeral in
nature and diligence is required to be able to locate it during the time frames when it is present.
Insert photos of Turtle grass and Paddle grass
Seagrasses rely on good light penetration to enable photosynthesis and are sensitive to reduced tidal
water quality. Growing in shallow regions they are also vulnerable to physical damage by boats. A
variety of marine algae can be associated with grass species, differing in the lack of a true rooting and
vascular system. Several species of both brown and green alga have been observed.
Seagrass coverage in Clam Bay has varied over time but has always been found predominately in
Outer Clam Bay and the waterway between this bay and Clam Pass. A 1994 Collier County report
estimated seagrass coverage at approximately 10 acres. Pre-dredge surveys conducted in 1999
estimated coverage at about 5.13 acres. Annual monitoring of seagrass beds along the monitoring
transects have estimated coverage from a low of approximately 1.2 acres in 2003 to the current
estimate of 2.85 acres from the 2013 survey. It should be noted that the coverage estimates are taken
from along the survey transects only and do not account for other scattered grasses that may be located
elsewhere in the system.
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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 a sufficient volume of water on the ebb tide to scour
out the inlet naturally, otherwise the inlet will, over time, continue to close. This is particularly true
during periods of high wave activity and low tidal ranges. (Turrell 1995; Tackney 1996). The six
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, Hummiston 2010).
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).
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 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
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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(from an engineering,not historical, standpoint), 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
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 1990, PBID became the Pelican Bay
Services Division (PBSD), a dependent Division of Collier County. PBSD continued the testing
program after 1990. 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 the exhibit below. There are currently nine 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.
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)
4323
(Submitted by Linda Roth received 2/18/2014)
5.FebruaryDiscussion 18,2014oflatest ClamdraftBayofmanagemeCommitteent ofplan the Pelican Bay Services Division
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• Nitrate-Nitrite(N)
• Nitrite(N)
• Nitrogen- Total Kjeldahl
• Orthophosphate(0PO4)
• Pheophytin
• Phosphorus- Total
• Residues-Filterable(TDS)
• Silica(SiO2)
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.•„:„t.1-,' ,R,Ait.t.,-',.4 4 1'''''X',,..il#1:4..rt4litt.. ;,,,.,,,, :iih 00:1; "',..)#,,,id,a1••••#$#",f.;•!:#;. ##--4 ;#. t ''' -::'*1 #4;.•: ?."------4.i.3 1, f, ''- '! •-*-
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4.
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B. _ + „ • mage a determination that the oxygen levels in Clam
B -'3? ys em was not listed as impaired for DO.
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February 14,2014
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there is also a private launch for Pelican Bay residents on the northern boardwalk. The canoe/kayak
trail is clearly designated by canoe trail markers from Outer Clam Bay to Upper Clam Bay.
Fishing and swimming are also popular pastimes. Fishing can be done from the boardwalks and canoes
or by wading into the water. Swimming is usually confined to the beach areas,but some swimmers and
waders, if conditions permit,venture into Clam Pass.
The operation of motorized watercraft in Clam Bay is restricted by Collier County Ordinance 96-16
that requires vessels with motors to travel at idle speed with no wake throughout the Clam Bay system.
The relatively shallow waterways of the system, in conjunction with the boardwalk heights, limit the
size and drafts of motorized watercraft. The residents of the Seagate neighborhood immediately south
of Outer Clam Bay have historically utilized motorized watercraft in Clam Bay but this use is still
subject to the County Ordinance. Violation of the Ordinance is a civil infraction for which a fine may
be levied. Occasionally motorized vessels, including jet-skis or other personal watercraft,have been
reported to be in violation of the Ordinance. Efforts to identify and report violators will continue to
insure that Clam Bay is not only a safe place for all its users,but that its unique environment is
protected. In the future should any adverse effects on Clam Bay's natural resources or water quality be
found to be related to motorized watercraft, additional management options will be explored to
ameliorate these adverse effects.
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4.0 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 17, 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
re-vegetation.
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 (which in 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. Agency comments and concerns which arose as part of the permit review led to the creation of
the 1998 Clam Bay Restoration and Management Plan. The Plan addressed agency concerns at the
time and included provisions for adding one-way flap gates to the Seagate culverts, dredging within
three sections of the creek north of Clam Pass, a network of hand-dug channels throughout the forest
area, in addition to the dredging of the Pass. This permit was issued in 1998 and the Management Plan
created in support of the permit has been the guiding document for the maintenance activities
undertaken in the Clam Bay system since then.
It is anticipated that FDEP and USACOE 10-year permits will be sought in conjunction with this
new Management Plan. The permits will allow for ongoing maintenance and/or 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 by the PBSD
Board and Collier County Commissioners before seeking any additional permit(s) which may be
necessary for the
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modified activities. Additional investigations which may be undertaken at a later date to look at, for
example, faunal investigations, more in-depth water quality concerns, or other issues that may arise as
a result of stakeholder discussions could also necessitate permitting which will have to be reviewed by
the PBSD and BCC prior to any such permit applications being submitted. 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. Dredging for navigation, beach renourishment, or
flushing of the bays to the south of the NRPA will not be done.
The following list contains more details related to existing and historical permits issued for the Clam
Bay 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.
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Department of Environmental Regulation Modification of Surface Water Management Permit No.
11-00065-5
Date of Issue: December 15, 1983
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. Is this the
drawbridge?
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.
Dept tnient 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:No Wake 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.
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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 and installation of one-way check valves on the culverts (pages 45 — 50 of the CBRMP). 2)
Clam Pass main channel dredging for Cuts 1, 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 741 FDEP 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 (Sections B&C) through Clam Pass;
and 3) alternative pipeline corridors between the dredge cuts and the disposal areas.
Department of Environmental Protection Permit Modification#2 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 (Sections B&C); 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#1 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 (Sections B&C); 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 (Sections B&C) 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.
69 71
(Submitted by Linda Roth received 2/18/2014)
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
CLAM BA YNRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
February 14,2014
Ver.4.0
72
(Submitted by Linda Roth received 2/18/2014)
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
CLAM BAY NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
February 14,2014
Ver.4.0
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.
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 trail 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 443 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 Modification#3 for 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.
Depaitulent of Environmental Protection Permit Modification#3 for Permit
Emeilsieft 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.
70 73
(Submitted by Linda Roth received 2/18/2014)
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
CLAM BAY NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
February 14,2014
Ver.4.0
Department of Environmental Protection Permit No. 11-0128463-005
Date of Issue: December 17,2010
Expiration Date: December 17, 2015 (5 yrs)
Project Description: Continue maintenance activities to the hand-dug channels in the Clam Bay
system originally permitted under Permit No. 0128463-001-JC.
Department of Environmental Protection Permit No. 11-0295193-004
Date of Issue: November 2, 2011
Expiration Date: November 2, 2016 (5 yrs)
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 (9 yrs)
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. Is the width of Section A 80'?
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 Is this the one time permit?
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 (9yrs)
Project Description: Modification to re-open Clam Pass Is the width of Section A 45'?
71
74
(Submitted by Linda Roth received 2/18/2014)
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
CLAM BAY NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
February 14,2014
Ver.4.0
5.0 Management Plan Goals and Objectives
The following goals and objectives for the management of the Clam Bay Natural Resource Protection
Area were developed in accordance with the directives of the Collier County Board of County
Commissioners (BOCC) and the Pelican Bay Services Division, which serves as an advisory board to
the BOCC. 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 held 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 Clam Bay NRPA while
minimizing negative environmental impacts.
Goal 2 -Maintain and protect the native floral and faunal communities.
Goal 3 -Manage and improve water quality.
Goal 4—Protect the integrity of known archaeological sites within the system.
Goal 5 -Address recreational uses with emphasis on passive recreation.
Goal 6-Improve public awareness and involvement.
GOAL 1 - Provide sufficient tidal exchange to maximize benefits to the Clam Bay NRPA while
minimizing negative environmental impacts.
A. Establish guidelines to help determine when dredging is necessary.
Monitoring of the Pass and internal waterways will provide information to determine if
dredging is necessary. Bathymetric surveys of cross-sectional areas of the Pass, tide gauge
data, and biological indicators can all be used to indicate when dredging is needed. Dredging
for the tidal exchange benefits necessary to maintain or improve environmental aspects of the
system will be done. Dredging for navigation, of beach renourishment or flushing of the bays
south of the NRPA will not be done.
a.)Conduct, at a minimum, annual surveys of the Pass.
b.) Maintain tidal gauges in good working order. Collect information periodically to
insure gauges are in good working order and data loss due to malfunctioning
equipment is minimized.
c.)Maintain backup gauges to minimize data loss due to malfunctioning equipment.
72 75 (Submitted by Linda Roth received 2/18/2014)
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
(Submitted by Linda Roth received 2/18/2014)
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
CLAM BA YNRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
February 14,2014
Ver.4.0
74
(Submitted by Linda Roth received 2/18/2014)
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
CLAM BA YNRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
February 14,2014
Ver.4.0
75
(Submitted by Linda Roth received 2/18/2014)
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
5. Discussion of latest draft of management plan
CLAM BAY NRPA MANAGEMENT PLAN(DRAFT)
Pelican Bay Services Division
February 14,2014
Ver.4.0
Clam Bay NRPA Management Plan Amendments
Studies within the Clam Bay Estuary its well as in othcr 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 FDEP and the USACOE for
consideration and inclusion into this Management Plan.
78
76
(Submitted by Linda Roth received 2/18/2014)
(Submitted by Linda Roth received 2/18/2014)
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February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
7.Discussion of Turrell-Hall&Associates contract renewal
Page 1 of 2
TUZRELL, HALL & ASSOCIATES, INC.
MARINE&ENVIRONMENTAL CONSULTING
3584 Exchange Avenue,Suite B•Naples,Florida 34104-3732•(239)643-0166•Fax 643-6632•thall@turrell-associates.com
June 2,2011 RECEIVED
JUN 07 2011
Pelican Bay Services Division PELICAN BAY SERVICES DIVISION
Mr.Kyle Lukasz
801 Laurel Oak Drive,Suite 605
Naples,FL 34108
Re: Proposal for Professional Environmental Services
Clam Bay Biological Studies(Contract 10-5571)-Fiscal Year 2010-2011
Dear Mr. Lukasz:
Turrell,Hall&Associates,Inc.is pleased to provide jou with this proposal for environmental services. Based
on the Request for Proposal and the newly issued County contract(10-5571),we propose to continue annual
biological monitoring of Clam Bay with the following scope of services.
Task I-Annual Biological Monitoring to include sampling and photographs Lump Sum$22,250.00
Task II-Seagrass Monitoring of outer Clam Bay and nearby channels Lump Sum$4,680.00
Task III-Tidal Data Collection,Analysis and Hydrographic Reporting Lump Sum$28,750.00
Task IV-Water Quality Data Analysis to include coordination of data from PBSD,data input and annual
analyses to compare past and present trends Lump Sum$5,520.00
Task V-Water Level Data Collection to include installation and downloading Lump Sum$9,770.00
Task VI- Annual Report Preparation and Submittal Lump Sum$11,215.00
Task VII- Annual Report Presentation Lump Sum$3,600.00
Task VIII-Hand Dug Channel Inspection and Maintenance to include both verifying channel stability and
oversight of maintenance events if the channels are filling-in Lump Sum$10,400.00
Task IX-Additional consulting services,meeting attendance,site investigation and research field observation
and reports Time and Materials(Not to Exceed)$15,000.00
Reimbursable Expenses $1,000.00
Lump Sum Total I $96,185.00
Time and Materials Total $16,000.00
February 18,2014 Clam Bay Committee of the Pelican Bay Services Division
7.Discussion of Turrell-Hall&Associates contract renewal
Page 2 of 2
June 2,201 I
Turrell,Hall&Associates, Inc.
Page 2
TURRELL,HALL&ASSOCIATES,INC
FEE SCHEDULE
Principal!Professional Engineer $185.00!hr.
Senior Ecologist $175.00 I hr.
Senior Engineer $145.00/hr.
Engineer III $105.00!hr.
Staff Engineer(II) $ 95.00/hr.
Project Manager $125.00/hr.
Senior Biologist $105.00/hr.
Senior Marine Biologist $105.00/hr.
Staff Biologist $ 90.00/hr.
Marine Biologist $ 90.00/hr.
AutoCAD Technician $ 85.00/hr.
Field Technician $ 75.00/hr.
Project Coordinator $ 70.00/hr.
Administrative Assistant $ 50.00/hr.
Boat $45.00/hr.
Expert Witness/Engineer $275.00!hr.
Expert Witness/Biologist $250.00/hr.
Aircraft $250.00/hr.
Boat $45.00/hr.
Gheenoe $20.00!hr.
4-Wheeler $20.00/hr.
Mileage $0.45/mile
Hypack $45.00/hr.
Description Unit Price
81/2 X 11 Color Copies <10=$0.80; z 10=$0.60; ?100=$0.50
81/2 X 14 Color Copies 40=$1.25; >10=$1.00; >_100=$0.90
11 x 17 Color Copies <10=$1.60; >_10=$1.40; >_100=$1.20
24 X 36 Plot <10=$5.00; >_10=$4.00
24 X 36 Aerial Plot $15.00 ea.
24 X 36 Photo Paper Plot $20.00 ea.
Other Items as billed by our Vendors:
Conference Calling
Postage
Courier Service
Overnight Deliveries
Rev.12/6110
•
50.44 etli y 5 0 &se.
1. MAINTAN AND PROTECT THE NATIVE FLORAL AND FAUNAL M
COMMUNITIES(TH) //NY
a. Establish baseline floral and faunal resource populations and monitor for changes
over time.
b. Protect listed species
c. Protect and maintain vegetative communities
d. Protect wildlife utilization of the NRPA
1. MAINTAIN,RESTORE,AND PROTECT THE NATIVE FLORAL AND FAUNAL
COMMUNITIES WITH THE CLAM BAY NRPA (KW)
a. Maintain healthy native floral and faunal populations
b. Protect listed species
c. Remove exotic and nuisance flora and faunal
d. Develop an integrated resource management strategy to interpret research
results and configure modeling tools fro implementing a conservation
strategy.
1
2.PROTECT ARCHAEOLOGICAL SITES WITH THE SYSTEM (TH)
a. Identify archaeological sites and protect them from impacts.
2. PROTECT ARCHAEOLOGICAL SITES WITHIN THE CLAM BAY NRPA(KW)
a. Develop an effective management approach to maintain and conserve
known archaeological sites and their associated artifact assemblage from
vandalism,exotic vegetation,erosion and other forms of degradation.
2
3. ADDRESS RECREATIONAL USES WITH EMPHASIS ON PASSIVE RECREATION
(TH)
a. Maintain access to facilities for intended uses
b. Maintain existing canoe trail
c. Maintain existing signage relative to boater and swimmer use of the system
d. Maintain existing signage or develop new signage to educate visitors
e. Define responsibilities for vegetation and litter control in Clam Pass Park.
3. ENSURE RECREATIONAL ACTIVITES ARE ENVIRONMENTALLY COMPATIBLE
WITHIN THE CLAM BAY NRPA(KW)
a. Enable the public to make informed decisions when recreating by
increasing their ability to act responsibly when enjoying this coastal
community ecosystem
b. Increase active stewardship by promoting the value of coastal
resources.
c. Maintain opportunites for low impact public use.
3
4. PROVIDE SUFFICIENT TIDAL EXCHANGE TO MAXIMIZE BENEFITS TO THE CLAM
BAY NRPA WHILE MINIMIZING NEGATIVE ENVIRONMENTAL IMPACTS. (TH)
a. Establish guidelines to help determine when dredging is necessary
b. Minimize dredge footprint(s) to the least environmentally damaging
practicable alternative.
c. Maximize the dredge interval as much as possible while maintaining
environmental standards.
d. Provide for appropriate drainage of fresh water by maintaining internal
creeks and hand-dug channels and modifying or augmenting hand-dug
channels as needed.
4. ENSURE THE ESTUARY HAS ADQUATE TIDAL AND FRESHWATER FLOWS TO
MAINTAIN ECOLOGICAL HEALTH WITH THE CLAM BAY NRPA. (KW)
a. Identify the minimum tidal flow necessary to ensure a healthy
ecosystem.
b. Ensure appropriate freshwater inputs and drainage.
4
5. MANAGE AND IMPROVE WATER QUALITY(TH)
a. Ensure appropriate freshwater inputs and drainage
b. Coordinate with adjacent upland developments to improve upstream inputs.
c. Develop a monitoring program to build onpast data and provide basis by
which to make future water quality related decisions.
5. TO RSTSORE,ENHANCE,AND MAINTAIN THE WATER QUALITY WITH THE
CLAM BAY NRPA. (KW)
a. Develop a long-term water quality program that assesses physical,
chemical and biological processes to ensure a sustainable healthy
environment for all users.
b. Promote comprehensive programs for controlling water pollution from
point and nonpoint sources.
5
2.0 Overview of Clam Bay
Description and Map
The Clam Bay NPRA consists of approximately 420 acres of mangroves; about 115
acres of shallow bays connected by narrow meandering creeks; approximately 1.5
miles of beach; Clam Pass,and a 35-acre beachfront parcel known as Clam Pass
Park. The Clam Bay system,located along the Gulf of Mexico in Collier County,
Florida, is part of the Cocohatchee-Gordon River Transition,referred to by the
Department of Natural Resources of Collier County as Coastal Zone II. It is one of the
few estuarine systems remaining in the Cocohatchee-Gordan River Drainage system,
federally designated as an undeveloped coastal barrier system (Burch, 1990).
The estuary consists of Clam Pass and three primary bays: Upper Clam Bay(north);
Inner Clam Bay(center); and Outer Clam Bay (south), connected by a series of tidal
creeks.
Clam Pass is a small,marginally stable inlet that has migrated north and south along
the shore over the years. Prior to dredging,the average water depths of Clam Pass
were-2.5 to-1.0 feet and its width ranged from 30-50' (Collier County, 1994). The
Pass is the primary sources of tidal exchange for the Clam Bay system.
South of Clam Pass is a channel about 30 feet wide that is oriented north-south with
water depths between-1.0 to -4.0 feet that leads to Outer Clam Bay (approximately
72 acres). Outer Clam Bay connects to the Venetian Bay (northern part of the
Moorings Bay/Doctors Pass seawall system) via three 24-inch concrete culverts
under Seagate Drive. There are also three dead end canals from the south end of
Outer Clam Bay into the Seagate community.
North of Clam Pass is a long narrow(approximately 6600 feet) that leads to Inner
Clam Bay (about 32 acres). A narrow creek(approximately 5400 feet) leads north
from Inner Clam Bay to Upper Clam Bay (approximately 20 acres),the smallest and
most isolated of the primary bays.
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. The operation of motorized watercraft is limited to Idle
Speed/No Wake per Collier County Ordinance 96-16.
CLAM BAY NRPA MAP AND VITAL STATISTICS HERE.With beaches changes to
1.5 miles and Water Body ID (WBID) 3278Q1 added
5
Historical Highlights
Tidal Connection
Aerial photos taken prior to 1952 when Vanderbilt Beach Road at the north end of
the Clam Bay system was constructed showed a connection of the system at Upper
Clam Bay to Vanderbilt Lagoon and Wiggins Pass (Collier County, 1994,Tropical
Bio Industries, 1978). It is recognized that the connection was marginal at best,and
while passable at times, it was not uniformly and consistently navigable (Clam Bay
Restoration and Management Plan, 1998).
Similarly aerial photos taken before Seagate Drive was built in 1958 showed that
Outer Clam Bay was connected to the vast mangrove swamps to the south via
shallow narrow meandering creeks leading into Doctors Bay and Doctors Pass .
These creeks were navigable only by canoes and small skiffs. (Naples Waterfront by
Turrell, 2009).
In 1976 three culverts were installed under Seagate Drive because the United States
Environmental Protection Agency, concerned about the deteriorating water quality
in Moorings Bay, recommended the culverts to allow some exchange of water
between Venetian Bay and Outer Clam Bay. The USEPA suggested that the culverts
be constructed to only allow flow to the north and to set the invert of the pipes of
1.0 ft. msl to protect the seagrass meadows in Outer Clam Bay. The invert elevation
was achieved,but water flowed both ways through the culverts. This two-way flow
continues today(Tackney, 1996; Collier County, 1996;Wilson Miller et.al., 1996).
Residential Development
Pelican Bay,the 2104-acre Planned Unit Development (PUD) to the north and east
of Clam Bay,was approved in 1977 as a partnership between Collier Enterprises
and Westinghouse Communities (WCI). It was one of the first developments in
Florida that was required to save fragile coastal wetlands and associated
ecosystems. (Urban Land Institute, 1981). Its development had a limited impact on
the wetlands using about 94 acres,including 78 acres in the northwest corner of the
property near Clam Bay,leaving the mangrove forest and bays intact. As mitigation
for the these wetlands,the title for the 570 acre preserve area,including the 35-acre
beach park were transferred to Collier County in 1981 with the stipulation that
Clam Bay shall remain a conservation/preservation area in perpetuity. In 1982 WCI
deeded Clam Bay and Clam Pass Park to Collier County,and in accordance with the
Pelican Bay PUD required Collier County to seek approval of WCI or its successors
for any modifications to Clam Bay.
The development of Pelican Bay required a stormwater management system
designed to spread run-off along the eastern edge of Clam Bay (Collier County
Report 1996). A four to six foot high and 2.5 mile-long berm separates the
developed portion of Pelican Bay from the estuary,and numerous culverts through
the berm discharge water to a swale system along the eastern edge of Clam Bay.
6
The eastern edge of Pelican Bay is about 12-14 feet above sea level at U.S. Highway
41 and slopes to the west where the berm the elevation is about two feet.
Naples Cay,located south of Outer Clam Bay,is a high-rise development consisting of
eight multi-story condominium buildings. Its development began in the late 1970's
and was completed in 2002. The community has pools,tennis courts,about 33
acres of park and preserve areas,and two canoe and kayak launching piers. It
stormwater management consists of several internal detention areas before water
flows into Clam Bay.
The Seagate community,immediately south of Clam Bay,consists of about 70 single-
family homes located along three man-made dead-end canals leading from Outer
Clam Bay. Development of the community began in the 1950's,and several
undeveloped lots remain. Because of its early development,there is no community-
wide stormwater management system.
Clam Pass Park
In 1986 Collier County constructed a 2900-foot boardwalk to provide access across
Outer Clam Bay to Clam Pass Park for all County residents and visitors. The park is
located at the south end of the Clam Bay NRPA and consists of 35 acres of mangrove
forest,coastal dunes,and 3200 linear feet of beach along the Gulf of Mexico. The
Conservancy of Southwest Florida offers free nature walks along the boardwalk and
beach from December through April.
Natural Resource Protection Area
Clam Bay was designated a Natural Resource Protection Area (NRPA) by Collier
County in 1995. By making Clam Bay a NRPA, Collier County recognized the
environmental importance of the preserve area. Designation as a NRPA affords the
area the following protections... NEEDS ADD.TEXT
Mangrove Die-off and restoration
The mangrove die-off was first reported in 1978 (Tropical BioIndustires Company;
Gee and Jenson). Reports of stressed and dead mangroves continued in the 1980's
and 1990's. In 1995 a significant area (approximately 50 aces) of dead and dying
mangroves was reported (Turrell, 1996).
The Clam Bay Restoration and Management Plan (1998) was developed to address
the die-off of mangroves. The major objective of the plan was to improve the tidal
flushing of the system, including tidal flow into and out of the forest areas.This was
accomplished by dredging Clam Pass; dredging the interior channels of the system;
and constructing a network of hand-dug flushing channels throughout the original
die-off area.
In the ten years following the implementation of the CBRMP the mangrove forest
underwent a substantial recovery in which over 80% of the die-off area was re-
vegetated with new mangrove growth.
7
Clam Bay NRPA Management Plan 2014
In 2013 Collier County Commissioners returned the responsibility for advising the
County on the dredging and maintenance of Clam Pass to the Pelican Bay Services
Division. Clam Pass closed in December, 2012,so upon the recommendation of the
PBSD,the County applied for and was granted a Nationwide one-event permit to
dredge and reopen Clam Pass. The pass was opened in March, 2013,and
development of the Clam Bay NRPA Management Plan began in April, 2013.
Historical Timeline
From Jan. 3 draft
Timeline for Establishment of Clam Bay NRPA
From Jan. 3 draft
8
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1...\9845 Clam Bay\Drawings\SHEET\MANATEE-SIGNSI2013_MANATEE_SIGNS.dwg MANATEE ZONES 2/18/2014 RANDI.JONES
327.46 Boating-restricted areas.--
(1) Boating-restricted areas,including,but not limited to,restrictions of vessel speeds and vessel traffic,may
be established on the waters of this state for any purpose necessary to protect the safety of the public if such
restrictions are necessary based on boating accidents,visibility,hazardous currents or water levels,vessel
traffic congestion,or other navigational hazards.
(a) The commission may establish boating-restricted areas by rule pursuant to chapter 120.
(b) Municipalities and counties have the authority to establish the following boating-restricted areas by
ordinance:
1. An ordinance establishing an idle speed,no wake boating-restricted area,if the area is:
a.Within 500 feet of any boat ramp,hoist,marine railway,or other launching or landing facility available for
use by the general boating public on waterways more than 300 feet in width or within 300 feet of any boat
ramp,hoist,marine railway,or other launching or landing facility available for use by the general boating
public on waterways not exceeding 300 feet in width.
b.Within 500 feet of fuel pumps or dispensers at any marine fueling facility that sells motor fuel to the
general boating public on waterways more than 300 feet in width or within 300 feet of the fuel pumps or
dispensers at any licensed terminal facility that sells motor fuel to the general boating public on waterways
not exceeding 300 feet in width.
c.Inside or within 300 feet of any lock structure.
2. An ordinance establishing a slow speed,minimum wake boating-restricted area if the area is:
a.Within 300 feet of any bridge fender system.
b.Within 300 feet of any bridge span presenting a vertical clearance of less than 25 feet or a horizontal
clearance of less than 100 feet.
c.On a creek,stream,canal,or similar linear waterway if the waterway is less than 75 feet in width from
shoreline to shoreline.
d.On a lake or pond of less than 10 acres in total surface area.
3. An ordinance establishing a vessel-exclusion zone if the area is:
a.Designated as a public bathing beach or swim area.
b.Within 300 feet of a dam,spillway,or flood control structure.
(c) Municipalities and counties have the authority to establish by ordinance the following other boating-
restricted areas:
1. An ordinance establishing an idle speed,no wake boating-restricted area,if the area is within 300 feet of a
confluence of water bodies presenting a blind corner,a bend in a narrow channel or fairway,or such other
area if an intervening obstruction to visibility may obscure other vessels or other users of the waterway.
Page 1 of 2
2. An ordinance establishing a slow speed,minimum wake,or numerical speed limit boating-restricted area if
the area is:
a.Within 300 feet of a confluence of water bodies presenting a blind corner,a bend in a narrow channel or
fairway,or such other area if an intervening obstruction to visibility may obscure other vessels or other users
of the waterway.
b.Subject to unsafe levels of vessel traffic congestion.
c.Subject to hazardous water levels or currents,or containing other navigational hazards.
d.An area that accident reports,uniform boating citations,vessel traffic studies,or other creditable data
demonstrate to present a significant risk of collision or a significant threat to boating safety.
3. An ordinance establishing a vessel-exclusion zone if the area is reserved exclusively:
a. As a canoe trail or otherwise limited to vessels under oars or under sail.
b. For a particular activity and user group separation must be imposed to protect the safety of those
participating in such activity.
Any of the ordinances adopted pursuant to this paragraph shall not take effect until the commission has
reviewed the ordinance and determined by substantial competent evidence that the ordinance is necessary to
protect public safety pursuant to this paragraph.Any application for approval of an ordinance shall be
reviewed and acted upon within 90 days after receipt of a completed application.Within 30 days after a
municipality or county submits an application for approval to the commission,the commission shall advise
the municipality or county as to what information,if any,is needed to deem the application complete.An
application shall be considered complete upon receipt of all requested information and correction of any
error or omission for which the applicant was timely notified or when the time for such notification has
expired.The commission's action on the application shall be subject to review under chapter 120.The
commission shall initiate rulemaking no later than January 1,2010,to provide criteria and procedures for
reviewing applications and procedures for providing for public notice and participation pursuant to this
paragraph.
(2) Each such boating-restricted area shall be developed in consultation and coordination with the governing
body of the county or municipality in which the boating-restricted area is located and,when the boating-
restricted area is to be on the navigable waters of the United States,with the United States Coast Guard and
the United States Army Corps of Engineers.
(3) It is unlawful for any person to operate a vessel in a prohibited manner or to carry on any prohibited
activity,as defined in this chapter,within a boating-restricted area which has been clearly marked by
regulatory markers as authorized under this chapter.
(4) Restrictions in a boating-restricted area established pursuant to this section shall not apply in the case of
an emergency or to a law enforcement,firefighting,or rescue vessel owned or operated by a governmental
entity.
History.--s.7,ch.63-105;s. 1,ch.65-361;ss.25,35,ch.69-106;s.23,ch.78-95;s.7,ch.81-100;s.27,ch.99-
245;s. 16,ch.2000-362;s.13,ch.2009-86.
Page 2 of 2
s uk, b,k. ea/pc/a G�'o.-� S �u 1
Page 1 of 8 /
T'rs b c/ c6-- co / f�. ' fZ °I
v ick / *z � / /gyp
U
WHEREAS, the Florida Department of Environmental Protection ("DEP") ga
Consolidated Joint Coastal Permit, Sovereign Submerged Lands Authorization and ( J 7 7
Variance No. 0128463-001-JC (Previously 113049919) (the"1998 DEP Permit")
authorized the Pelican Bay Municipal Services and Benefit Taxing Unit known as the
Pelican Bay Services Division (the"PB SD") as permittee to implement the Clam Bay It ,
Restoration and Management Plan (the"Plan"); Pi �. r
WHEREAS, the 1998 DEP Permit and the Plan were designed to deal with the7
environmental degradation of Clam Bay that was occurring in 1998, and were not Cc
designed to change the navigational characteristics of Clam Bay; al C/
WHEREAS, there is nothing in the 1998 DEP Permit specifically dealing with
the installation of markers within Clam Bay, and, in fact, a careful review of the 1998
DEP Permit and all of the supporting findings of facts clearly indicates that the 1998 DEP `}.O
Permit required only the following markers in all of Clam Bay:
Section 3(h) (page 9/21 of the 1998 DEP Permit): "Permanent manatee Dec//_/.I.
informational signs, such as those shown in the enclosed example sheets, shall be (9
installed and maintained at the canoe boat ramp at the southern end of Outer Clam
Bay following completion of the initial dredging event." ).3 CC
141 eel
Section 5 (page 9/21 of the 1998 DEP Permit): "The Clam Bay ecosystem
contains waterways that are difficult to navigate due to shallow water depths and /O `
meandering channels lined with protruding mangroves branches and roots. To
protect the significant natural resources and water quality of the Clam Bay
ecosystem, and to provide protection to the public safety (boaters utilizing these
waters), there shall be an idle speed/no wake restriction on motorized vessels used
in the system (as stipulated in County Ordinance No. 96-16). The existing
restrictions placed upon boating activities within the Clam Bay system by County
Ordinance No. 96-16 shall remain active and enforceable for the life of this
permit. Additionally, two Florida Marine Patrol approved signs that state: "Idle
Speed-No Wake" and "Caution-Shallow Water and Natural Resources Present-
Tilt Motor Up to Prevent Prop Dredge-Damage to Natural Resources Subject to
Fines, Pursuant to Chapter 370, F.S." shall be placed at the following locations
following completion of the initial dredging event:
1) One within the entrance to Clam Pass facing boaters entering the bays;
2) One at the entrance to Outer Clam Bay facing north and easily legible
to boaters entering Outer Clam Bay;
3) One at the entrance to Inner Clam Bay facing south and easily legible
to boaters entering Inner Clam Bay;
4) One at the entrance to upper Clam Bay facing south and easily legible
to boaters entering Upper Clam Bay; and,
5) One within the upper reaches of Outer Clam Bay facing southeast and
easily legible to boaters leaving Seagate."
Page 2 of 8
WHEREAS, the United States Army Corps of Engineers (the "Corps") also
issued a permit at the same time as the 1998 DEP Permit (the"1998 Corps Permit"). The
Corps' Findings of Fact with respect to the 1998 Corps Permit also made it clear that the
1998 Corps Permit also did not contemplate any changes in navigation in Clam Bay. In
its evaluation of recreation considerations under the Public Interest Section of its findings
of Fact(Section 9.a(13), page 22/28), the Corps stated:
"(13) Recreation: The proposed Plan will not change the current recreational use
of the Bay, however, the Plan does contain a Recreational Component that will
address appropriate notification, signage, and policing of the Bay."
In its evaluation of navigation considerations under the same Public Interest
Section of its Findings of Fact(Section 9.a(11), page 22/28), the Corps stated:
(11)Navigation (33CFR320.4(o)): .... The original Plan sought to restrict the use
of motorized boats within the bay, but public outcry for historic riparian rights for pc
access to the bay caused a revision to the Plan to remove this restriction.
However, existing regulation by Collier County limits motorized vessel , /
throughout the bay to idle speed and no wake. In addition, the proposed Plan
would implement a provision for evaluation of boat traffic and any adverse
impacts to the Bay. The proposed Plan should not produce any significant
changes in navigation in the Bay."
WHEREAS, the foregoing two sections of the 1998 DEP Permit, Sections 3(h)
and 5, and Section(13) of the Corps Findings of Fact with respect to the 1998 Corps
Permit, contain the only mention of even signage in either the 1998 DEP Permit, the 1998
Corps Permit, or in any findings of fact issued by either agency in connection therewith
(collectively, the"Permit Documents"). There is no mention of markers anywhere in the
Permit Documents.
WHEREAS, the Plan did directly deal with motorized boating in Clam Bay, in
Section 3.3.2 dealing with the Proposed Recreational Component of the Plan:
Plan, pages 36-38: "For the most part, Clam Bay remains inaccessible to
the general public. . . .
Canoeing of the waterways within Clam Bay remains a popular activity for those
seeking a more intimate look at the estuary, and its wildlife or those seeking
solitude in the upper reaches of the bay. Fishing is also a frequent undertaking
from either the boardwalks or canoes. Swimming is confined to the beach area,
although there is a reasonable amount of wading in Clam Pass and back into the
estuary as much as 1,000 or so feet from the mouth of the Pass.
The use of motorized watercraft is not prohibited, and evidence of periodic use of
such is evident from observation. For the most part,the accumulation of
Page 3 of 6
sediments and the shoaling that has taken place has resulted in physically
limiting the accessibility of Clam Bay to deeper draft boats and particularly
those equipped with engines. Most, if not all of the motorized boat traffic is
believed to originate in the Seagate residential area and be confined to the area
from Outer Clam Bay to Clam Pass. [emphasis supplied]
The Management Plan would not anticipate any change to the recreational use
characteristics of Clam Bay. The contemplated widening and deepening of Clam
Pass and the interior channels leading into Outer Clam Bay will not measurably
improve navigability. Earlier assumptions to the contrary have proved to be
inappropriate as the channel itself remains very confined. Further, since no
dredging of Outer Clam Bay is proposed, accessibility across the same will
not be noticeable improved. [emphasis supplied]
Presently, Collier County has enacted Ordinance 96-16 which Ordinance provides
for the utilization of the Clam Bay area by motorized watercraft provided that
they operate at no wake and idle speed. The Management Plan recommends no /
change in that protocol. The PBSD will however, in cooperation with the County,
vigorously enforce the existing Ordinance. Further, if significant adverse impacts
to the natural resources and water quality of the Clam Bay system are confirmed
by the Collier County Department of Natural Resources, the FDEP and the Corps
environmental staffs to be directly attributable to the use of motorized boats
within the Clam Bay system, then additional restrictions or adjustments in the use
of motorized boats within the Clam Bay system shall be considered for imposition
to ensure that the ecological integrity of the Clam Bay system is preserved. . . .
Appropriate notification, signage and policing will be provided by the County and
the PBSD to ensure compliance. The signage will be strategically placed both at
the entrance to Clam Pass and in the areas around the boat ramp located at the
southern end of Clam Bay. These are intended to ensure that persons
accessing the Clam Bay system are informed of its unique ecological
characteristics, the limitations of access resulting from variations in water depth,
the existence of no wake/idle speed requirements for motorized boat operation
and importantly, the importance of staying out of areas as having maturing
seagrass beds and potential manatee habitat. Precise language to be included
in the signage will be determined in cooperation with the agencies post permit
issuance. [emphasis supplied]
WHEREAS, the only mention of markers that occurs in any document connected
with the Permit Documents is in the Plan, where, on page 38 and 39, the following
sentence occurs: "Finally, the main channel will be marked in accordance with the
requirements imposed by the United States Coast Guard to ensure that those who use
the system clearly know where the channel is and the prohibitions of operating their
water craft outside the same." [emphasis supplied]
Page 4 of 8
WHEREAS, the foregoing clearly indicates that the purpose of the referenced
markers was to protect maturing seagrass beds and potential manatee habitat in the main
channel by ensuring that those who use the system know about the importance of staying
out of such areas. [emphasis supplied]
WHEREAS, the residents of the community known as Seagate("Seagate") have
contended for several years that this single sentence in the Plan mandates the installation
of red and green navigational markers in Clam Bay, not only in the"main channel,"
which is the only area that this sentence mentions to be marked, but also through Outer
Clam Bay.
WHEREAS, the PBSD, as the original permittee of the 1998 DEP Permit and the
1998 Corp Permit, and as the author of the Plan, is fully aware that neither the 1998 DEP
Permit, the 1998 Corps Permit, nor the Plan contemplated the installation of red and
green navigational markers anywhere in Clam Bay. 9e' y
WHEREAS, the PBSD, as the original permittee of the 1998 DEP Permit and t e l
1998 Corp Permit, and as the author of the Plan, believes that the purpose of the
referenced markers was to protect maturing seagrass beds and potential manatee habitat
by ensuring that those who use the system know about the importance of staying out of
such areas.
WHEREAS, by the explicit terms of the 1998 DEP Permit and by the explicit
terms of the Plan the Plan was designed as a dynamic document that can be modified
over time:
General Condition 1 of the 1998 DEP Permit: All activities authorized by this
permit shall be implemented as set forth in the plans, specifications, and attached
drawings approved as a part of this permit, and all conditions and requirements of
this permit. The permittee shall notify the Department in writing of any
anticipated deviation from the permit so that the Department can determine
whether a modification of the permit is required.
Plan, page 4: "It is recognized that as management protocols are implemented,
monitoring conducted, and the demands on the natural ecosystem change, new
challenges and opportunities will develop beyond those presented in this plan.
The PBSD is aware that changes will occur and has development a Management
Plan that is dynamic and can be modified through time while still meeting the
PBSD's goals."
Plan, page 5: "The Report has been used to select those management protocols
that meet the goals established by the PBSD and related and interested stake
holders. The long-term goal of the Management Plan is that it be used as a tool
for evaluating new management options, as well as existing protocols as
circumstances require. It should be used minimally, on an annual basis, for
reviewing any new issues or options, as well as for evaluating existing operational
Page 5 of 8
protocols. These analysis [sic] will assist in the prioritization for implementation
in the next ensuing year. SAs new management issues develop and others are
resolved or implemented, the Management Plan can be updated to reflect the
current and future needs of Clam Bay."
Plan, pages 5-6: "The goals established by the PBSD for the Clam Bay
Management Plan are- develop operational protocols that allow the permit
holder to respond to changing circumstances under defined parameters . . . ."
Plan, page 8: "In the Section entitled the Role of the PBSD, the report discusses
a framework for the PBSD to become not only a clearinghouse and coordinator
for activities relating to Clam Bay, but also the primary manager of the
implementation protocols."
Plan, page 10: "As the official manager of the Management Plan,the PBSD will
direct and have responsibility for its implementation and operation over time. A. s—
such, the PBSD will plan and implement identified management protocols. The
objectives of these management protocols will be to protect, enhance, and
maintain the natural resources and the ecological value of Clam Bay. ----
WHEREAS, the PBSD has treated the Plan as a dynamic document and has made
changes in implementation protocols over the life of the Plan, including, among other
things, determining what markers are most appropriate for Clam Bay to protect maturing
seagrass beds and potential manatee habitat by ensuring that those who use the system
know about the importance of staying out of such areas.
WHEREAS, the Chairman of the PBSD Board participated with representatives
of the County, the City of Naples, the Pelican Bay Foundation, the Mangrove
Action Group, the Sierra Club, the Conservancy of Southwest Florida, and Seagate on a
Clam Bay Marker Working Group to attempt to determine what marking system is most
appropriate for Clam Bay.
WHEREAS, the Chairman of the PBSD Board and the Clam Bay Working
Group, with the exception of the representative of Seagate, recommended the installation
of canoe trail markers and informational signs in Clam Bay in order(i)to protect
maturing seagrass beds and potential manatee habitat by ensuring that those who use the
system know about the importance of staying out of such areas, and (ii)to provide notice
to users of the system of the presence of shoals, and (iii)to provide notice to users of the
system that the system is being used by a variety of watercraft.
WHEREAS, the Board of County Commissioners for Collier County (the
"BCC") considered on June 14, 2011 the recommendation of the Clam Bay Marker
Working Group and approved and adopted this recommendation and instructed Collier
County staff to seek to obtain a permit from the relevant authorities authorizing the
installation of these canoe trail markers and informational signs.
Page 6 of 8
WHEREAS,the Collier County Director of Coastal Zone Management applied
for and obtained on September 9, 2011, a permit from the Florida Fish and Wildlife
Conservation Commission("FWL") for the installation of these canoe trail markers and
informational signs.
WHEREAS, on October 20, 2011, the Corps notified Collier County as follows:
As long as the markers are consistent with Special condition 2 of the Corps permit
no. SAJ-1996-02789 an additional permit is not needed because the markers are
already authorized under this permit. The Corps will allow informational channel
markers instead of coast guard approved markers. The intent of this condition
within the Corps permit is to protect the resources while allowing safe passage.
The markers shown in the attached application appear to satisfy this requirement
and will bring the permit back in compliance. Please see the attached letter and
make sure to submit the requested documentation once the work is completed.
l`3
WHEREAS, on October 25, 2011, the USCG notified Collier County as follow
This email is in response to the attached State of Florida, FWC permit 11-020
dated September 9, 2011 for the establishment of information marks in Clam
Pass/Bay.
The CG has no objection for the placement of the marks per the attached permit.
WHEREAS, on November 2, 2011, the DEP gave notice of its intent to grant an
exemption and a consent to use sovereign submerged lands for the installation of these
canoe trail markers and informational signs.
WHEREAS, the PBSD considers the Plan to have been de facto amended to
provide for the installation of these canoe trail markers and informational signs by virtue
of the foregoing actions.
WHEREAS, in order to avoid any doubt regarding this fact, the PBSD Board
wishes to make it clear that the Plan has been amended to provide for the installation of
these canoe trail markers and informational signs.
WHEREAS, the PBSD has in the past assessed the residents of Pelican Bay to
fulfill its functions as the permittee under the Plan, and continues to assess the residents
of Pelican Bay to fulfill the other purposes of the PBSD with respect to Clam Bay as
outlined in Collier County Ordinance 2006-05, which include the"the maintenance of
conservation or preserve areas, including the restoration of the mangrove forest
preserve...."
Page 7 of 8
WHEREAS, the Pelican Bay Foundation, Inc. (the"Foundation")is the
homeowners association representing each of the residents of Pelican Bay who are
assessed by the PBSD.
WHEREAS, the PBSD is a dependent district of Collier County.
WHEREAS, the PBSD wishes to ensure that the residents who have been and are
being assessed by the PBSD to pay for the design and implementation of the Plan and for
ongoing matters involving Clam Bay being handled by the PBSD are represented in the
lawsuit brought by Seagate.
WHEREAS, the PBSD wishes to request that the Foundation intervene in the
lawsuit brought by Seagate in order to represent the interests of such residents.
NOW THEREFORE, the PBSD Board hereby resolves as follows:
RESOLVED, that the Plan and the 1998 DEP Permit to the extent it incorporates
the Plan have been amended in fact by the actions of(i)the Clam Bay Marker Working
Group in recommending the installation of canoe trail markers and informational signs in
Clam Bay, (ii)the BCC in approving and adopting this recommendation and in
instructing Collier County staff to obtain a permit from the relevant authorities
authorizing their installation, (iii) the FWL is permitting their installation, (iv)the Corps
in approving their installation, (v)the USCG in approving their installation, and (vi)the
DEP in providing a notice of intent to grant and exemption and consent to use sovereign
submerged lands for their installation; and be it further
RESOLVED, that in order to remove any doubt as to whether the Plan and the
1998 DEP Permit to the extent it incorporates the Plan have been amended in fact by the
actions of(i)the Clam Bay Marker Working Group in recommending the installation of
canoe trail markers and informational signs in Clam Bay, (ii)the BCC in approving and
adopting this recommendation and in instructing Collier County staff to obtain a permit
from the relevant authorities authorizing their installation, (iii) the FWL is permitting
their installation, (iv)the Corps in approving their installation, (v)the USCG in
approving their installation, and (vi)the DEP in providing a notice of intent to grant and
exemption and consent to use sovereign submerged lands for their installation, the Plan
and the 1998 DEP Permit to the extent it incorporates the Plan are hereby amended by
deleting the sentence on pages 37 and 38 of the Plan that provides"Finally, the main
channel will be marked in accordance with the requirements imposed by the United
States Coast Guard to ensure that those who use the system clearly know where the
channel is and the prohibitions of operating their water craft outside the same" and
inserting in lieu thereof the following: "Finally, Clam Bay will be marked with the canoe
trail marker and informational signs permitted by the FWL on September 9, 2011, and as
are covered by DEP's notice dated November 2, 2011, of intent to grant an exemption
and consent to use sovereign submerged lands for their installation; and be it further
Page 8 of 8
RESOLVED, that the Chairman of the PBSD Board be and hereby is instructed
to provide a copy of these resolutions duly adopted by the PBSD Board to the Collier
County Attorney for such further action by the BCC as is deemed necessary and
appropriate; and be it further
RESOLVED, that the Foundation be and hereby is requested to intervene in the
lawsuit brought by Seagate in order to ensure that the residents of Pelican Bay who have
been and are being assessed by the PBSD to pay for the design and implementation of the
Plan and for ongoing matters involving Clam Bay that are being handled by the PBSD
are represented in the lawsuit brought by Seagate.
w /
Si-t5 f C J L Mart ca Ci'tt cza-
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hEd Clam 87 6444
MARCIA CRAVENS<goldandrose@mac.com>*
Fwd: Recap of December 11-12 BCC meeting with copied/pasted excerpts of Agenda Items for PBSD to
Manage Clam Bay per exclusive Advisory role to BCC, and TH&A work order change 7
February 16, 2014 10:23 PM Fd
just a forward to myself of the email I sent Susan with copied and pasted excepts directly from the Recap record o
the Dec. 11-12, 2012 BCC meeting.
Begin forwarded message:
From: MARCIA CRAVENS<oksiandls ise r&` a m ; ;_ >
Subject: Recap of December 11-12 BCC meeting with copied/pasted excerpts of Agenda Items for PBSD
to Manage Clam Bay per exclusive Advisory role to BCC, and TH&A work order change
Date: February 16, 2014 10:21:39 PM EST
To: Susan O'Brien < >
Susan,
I've sent to you a forward of what's known as the Clerk of Court's "Recap"for BCC Actions taken at a BCC meeting--
for the BCC meeting of December 11-12, 2012 (their very long agenda took 2 days to and some items were
continued to January and later).
All three of Commissioner Hiller's PBSD, Clam Bay, and Turrell, Hall &Assoc. work order Agenda items that she
recommended are included in this Recap of that meeting. When you look at the number of pages for just the
"Recap"of that BCC meeting, you'll understand the difficulty in finding each of these items and their backup
documents in the many more pages of the regular BCC Board Meetings Records. However, I will try to take the
time to find these 3 items in the regular December 11-12 2012 BCC meeting minutes and the companion backup
documents for these items tonight before I sleep.
You may recall that the BCC meeting of December 11 - 12 had included agenda items X, Y, and AC as
recommended by Commissioner Hiller that were related to Pelican Bay MSTBU - PBSD being returned to their prior
role of advisory and stewardship for the Clam Bay NRPA. In fact, agenda item X provided a somewhat greater role
for the PBSD to exclusively advise the BCC on Clam Bay NRPA management issues, including dredging of Clam
Pass. item Y included that an amendment to the Pelican Bay Ordinance of 2002-27, as amended, would be
advertised for a future action by the BCC. Item AC was for the firm of Turrell, Hall and Associates to provide
information for a change work order to the contract they have with the County for the PBSD --to include
preparation of an update to the Clam Bay Management Plan. The exact language is as follows "to update the
existing Clam Bay Management Plan to ensure the preservation of the Clam Bay system and compliance with this
{ preserve's Natural Resource Preservation Area(`NRPA")designation; and, to establish criteria as indicators for
evaluation of dredging needs for the purpose of maintaining flushing for the environmental benefit of the Clam Bay
system".
I've copied and pasted the respective Action Items as they are recorded in the Clerk of Court's Recap that I received
in response to my request for same by staff of the Clerk of Court(the full Recap record is attached here as a PDF
and also was included in my earlier forward of the email I originally received from the Clerk of Court staff which I
believe was a .doc format attachment).
Marcia
Time Certain (Per Agenda Change Sheet)
This item to be heard at 2:30 p.m. Recommendation that effective immediately, Clam Pass be
considered part of the ongoing management responsibilities of the Pelican Bay Services Division
r
("PBSD")including but not limited to all monitoring components such as biological,tidal,and
hydrographic data collection, and,inlet dredge permitting/construction;that PBSD,exclusively,sh 11
make recommendations to the Board of County Commissioners as to when the inlet should be
dredged, and make such other recommendations related to managing the unified Clam Bay system as it
deems necessary; further,that Clam Pass,being an integral part of the Clam Bay system,is managed
as such. This is a companion to Item#10Y. (Commissioner Hiller)
Motion to accept evidence presented by Jim Hoppensteadt—Approved 5/0; Motion to accept
evidence presented by Ted Rhea—Approved 5/0;
Motion to Approve—Approved 5/0; Motion for Commissioner Hiller to send email to Linda
Elligott with Army Corp of Engineers regarding dredging permit—Approved 3/2
(Commissioner Fiala and Commissioner Coyle opposed)
Time Certain (Per Agenda Change Sheet)
This item to be heard at 2:30 p.m.Request for authorization to advertise an ordinance for future
consideration which would amend Ordinance No. 2002-27, as amended,relating to the Pelican Bay
Municipal Service Taxingand Benefit Unit. This is a Companion to Item#10X. (Commissioner
Hiller)
Approved- 3/2(Commissioner Fiala and Commissioner Coyle opposed)
Time Certain (Per Agenda Change Sheet)
AC. This item to be heard at 2:30 p.m.Recommendation to direct Turrell,Hall&Associates,Inc. to
prepare a work order under Contract#10-5571 to update the existing Clam Bay Management Plan to
ensure the preservation of the Clam Bay system and compliance with this preserve's Natural Resource
Preservation Area("NRPA")designation; and,to establish criteria as indicators for evaluation of
dredging needs for the purpose of maintaining flushing for the environmental benefit of the Clam Bay
system;to present such work order to the PBSD,the TDC,and the BCC at the first January, 2013
meeting of each of these respective boards. (Commissioner Hiller)
Motion to direct staff to prepare a work order under Contract#10-5571—Approved 3/2
(Commissioner Coyle and Commissioner Fiala opposed)
f)„,
12/11/2012 Item 10.X.
EXECUTIVE SUMMARY
Recommendation that effective immediately, Clam Pass be considered part of the ongoing
g
management responsibilities of the Pelican Bay Services Division ("PBSD") including but
not limited to all monitoring components such as biological, tidal, and hydrographic data
collection, and, inlet dredge permitting/construction; that PBSD, exclusively, shall make
recommendations to the Board of County Commissioners as to when the inlet should be
dredged,and make such other recommendations related to managing the unified Clam Bay
system as it deems necessary; further, that Clam Pass, being an integral part of the Clam
Bay system,is managed as such.
OBJECTIVE: Effective immediately, that Clam Pass be considered part of the ongoing
management responsibilities of the Pelican Bay Services Division ("PBSD") including but not
limited to all monitoring components such as biological, tidal, and hydrographic data collection,
and, inlet dredge permitting/construction; that PBSD, exclusively, shall make recommendations
to the Board of County Commissioners as to when the inlet should be dredged, and make such
other recommendations related to managing the unified Clam Bay system as it deems necessary;
further,that Clam Pass,being an integral part of the Clam Bay system, is managed as such.
CONSIDERATIONS: The purpose of the maintenance permit for the dredging of Clam Pass is
to provide adequate tidal flushing of the Clam bay system for environmental benefits. The health
and welfare of the Clam Bay system relies on adequate flushing, which starts with the inlet, yet
is closely related to the shoaling within the system, and that shoaling largely occurs from the
sand entering Clam Pass, so the two are inextricably related.
Therefore bifurcating the project, as it was originally designed and permitted for the Clam Bay
Restoration and Management Plan, into an inlet project and an interior environmental project
resulting in two separately managed projects, is not the most efficient approach to managing this
system. Clam Pass is an integral part of the Clam Bay system,and should be managed as such.
Florida statutes and administrative rules require that sand dredged from the inlet be placed along
the adjacent shorelines influenced by the inlet and experiencing erosion. The maintenance of
Clam Pass should continue to address the erosion along the beaches with the immediate vicinity
of Clam Pass and should not be considered part of the larger scale beach management program
for Collier County. Over dredging Clam Pass for the purpose of obtaining additional sand for
areas beyond the influence of Clam Pass can lead to additional localized shoreline and inlet
stability problems in the immediate vicinity of Clam Pass.
It is recommended that Clam Pass be considered part of the ongoing management responsibilities
of the PBSD including all monitoring components such as biological, tidal, and hydrographic
data collection. (The important tide monitoring portion of this plan has always remained under
PBSD's jurisdiction). PBSD shall be responsible for the inlet dredge permitting/construction.
PBSD, exclusively, shall make recommendations to the Board of County Commissioners as to
when the inlet should be dredged, and make such other recommendations related to managing
Packet Page-959-
12/11/2012 Item 10.X.
the unified system as is needed to preserve the environmental health of this Natural Resource
Protection Area ("NRPA"). The PBSD's track record in being able to successfully manage the
system through the highly successful mangrove recovery period is an indication that the PBSD is
the right entity for the important responsibility of ensuring the preservation of the restored
system.
FISCAL IMPACT: None
LEGAL CONSIDERATIONS: This item has been reviewed by the County Attorney,is legally
sufficient,and requires majority vote for approval. -JAK.
RECOMMENDATION: Effective immediately, that Clam Pass be considered part of the
ongoing management responsibilities of the Pelican Bay Services Division ("PBSD") including
but not limited to all monitoring components such as biological, tidal, and hydrographic data
collection, and, inlet dredge permitting/construction; that PBSD, exclusively, shall make
recommendations to the Board of County Commissioners as to when the inlet should be dredged,
and make such other recommendations related to managing the unified Clam Bay system as it
deems necessary; further, that Clam Pass, being an integral part of the Clam Bay system, is
managed as such.
PREPARED BY: Commissioner Georgia Hiller
Packet Page-960-
12/11/2012 Item 10.X.
COLLIER COUNTY
Board of County Commissioners l
Item Number: 10.X.
Item Summary: Recommendation that effective immediately,Clam Pass be considered
part of the ongoing management responsibilities of the Pelican Bay Services Division ("PBSD")
including but not limited to all monitoring components such as biological,tidal,and
hydrographic data collection,and, inlet dredge permitting/construction;that PBSD,exclusively,
shall make recommendations to the Board of County Commissioners as to when the inlet
should be dredged, and make such other recommendations related to managing the unified
Clam Bay system as it deems necessary; further,that Clam Pass, being an integral part of the
Clam Bay system, is managed as such. This is a companion to Item 10Y. (Commissioner Hiller)
Meeting Date: 12/11/2012
Prepared By
Name: BrockMaryJo
Title:Executive Secretary to County Manager,CMO
12/5/2012 11:06:24 AM
Submitted by
Title:Executive Secretary to County Manager,CMO
Name:BrockMaryJo
12/5/2012 11:06:25 AM
Approved By
Name: KlatzkowJeff
Title:County Attorney
Date: 12/5/2012 11:45:16 AM
Name: OchsLeo
Title:County Manager
Date: 12/5/2012 1:41:19 PM
Packet Page-961-
12/11/2012 Item 10.Y.
EXECUTIVE SUMMARY 1
Request for authorization to advertise an ordinance for future consideration which would
amend Ordinance No. 2002-27, as amended, relating to the Pelican Bay Municipal Service
Taxing and Benefit Unit.
OBJECTIVE: To obtain the Board of County Commissioners (Board's) authorization to
advertize for future Board consideration the attached amendment to Ordinance No. 2002-27, as
amended,which created the Pelican Bay Municipal Service Taxing and Benefit Unit.
CONSIDERATIONS: Collier County Ordinance No. 2002-27, as adopted on May 28, 2002,
superseded, repealed, and consolidated priorr ordinances relating to the Pelican Bay Municipal
Service Taxing and Benefit Unit. The Board subsequently amended the Ordinance through its
adoption of Ordinance Nos.2006-05 and 2009-05.
The purpose of the ordinance is to amend the Pelican Bay Municipal Service Taxing and Benefit
Unit ordinance to clarify that the Unit will be solely responsible for advising the County on
dredging and maintaining Clam Pass for the purpose of enhancing the health of the affected
mangrove forest, and will manage such activities for the County; to add a non-voting member
recommended by the Pelican Bay Foundation; and to create a system of rotating officers for this
advisory board.
FISCAL IMPACT: The cost for advertising the proposed ordinance is approximately$350.00.
GROWTH MANAGEMENT IMPACT: None.
LEGAL CONSIDERATIONS: The proposed ordinance was drafted by the County Attorney,
and is legally sufficient for Board action. A simple majority vote is required to authorize its
advertisement. -JAK
RECOMMENDATION: That the Board of County Commissioners authorizes advertisement
of the attached ordinance for future Board consideration which will amend Ordinance No. 2002-
27,as amended,relating to the Pelican Bay Municipal Service Taxing and Benefit Unit.
SUBMTTED BY: Commissioner Georgia A.Hiller.District 2
Packet Page-962-
12/11/2012 Item 10.Y.
COLLIER COUNTY / j
Board of County Commissioners
Item Number: 10.Y.
Item Summary: Request for authorization to advertise an ordinance for future
consideration which would amend Ordinance No. 2002-27, as amended, relating to the Pelican
Bay Municipal Service Taxing and Benefit Unit. This is a companion to Item 10X.
(Commissioner Hiller)
Meeting Date: 12/11/2012
Prepared By
Name: BrockMaryJo
Title:Executive Secretary to County Manager,CMO
12/5/2012 11:08:04 AM
Submitted by
Title:Executive Secretary to County Manager,CMO
Name: BrockMaryJo
12/5/2012 11:08:06 AM
Approved By
Name:KlatzkowJeff
Title:County Attorney
Date: 12/5/2012 11:45:24 AM
Name: OchsLeo
Title:County Manager
Date: 12/5/2012 1:41:35 PM
Packet Page-963-
• 12/11/2012 Item 10.AC.
EXECUTIVE SUMMARY I/
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Recommendation to direct Turrell, Hall & Associates, Inc. to prepare a work order under
Contract #10-5571 to update the existing Clam Bay Management Plan to ensure the
preservation of the Clam Bay system and compliance with this preserve's Natural Resource
Preservation Area ("NRPA") designation; and, to establish criteria as indicators for
evaluation of dredging needs for the purpose of maintaining flushing for the environmental
benefit of the Clam Bay system; to present such work order to the PBSD,the TDC,and the
BCC at the first January,2013 meeting of each of these respective boards.
OBJECTIVE: To update the existing Clam Bay Management Plan to ensure the preservation of
the Clam Bay system and compliance with the preserve's NRPA designation; and, to establish
criteria as indicators for evaluation of dredging needs for the purpose of maintaining flushing for
the environmental benefit of the Clam Bay system. This shall be accomplished through a work
order under Contract #10-5571 for a total cost not to exceed $34.000. The work order
deliverables shall include the following:
. Update the Clam Bay Management Plan to achieve the objective of `preservation' since the
'restoration' objective has been successfully achieved.
Modify the State and Federal maintenance dredging permits to incorporate the revised
Management Plan objective.
. Develop and implement an updated Monitoring Plan consistent with the revised objective of
the Management Plan.
CONSIDERATIONS: The Clam Bay Management Plan has successfully achieved the
restoration of the mangrove system within Clam Bay. The next management phase will entail
preserving the restored mangrove system. To that end, the Clam Bay Management Plan shall be
updated based on obtained monitoring data to incorporate the preservation objective. Inherent to
the preservation of the mangrove system is the need to provide adequate flushing through
maintenance dredging of Clam Pass to ensure the health of the mangroves. The update to the
Management Plan shall include a recommendation that listed monitoring data. evaluated in
totality, shall be the basis for future dredging considerations. The updated Management Plan
guidelines shall serve as the basis for the modification of the State and Federal maintenance
dredging permits. Clam Pass and Clam Bay shall be recognized and managed as a single unified
system. rather than as bifurcated systems. given that both the pass and the bay constitute the
NRPA and must be taken as a whole. Further, an updated monitoring plan shall be developed
and implemented consistent with the objectives of the updated Management plan.
FISCAL IMPACT: Funding for this work order shall be from the Tourist Development Tax
Fund 1.95;the total cost shall not exceed$34,000.
LEGAL CONSIDERATIONS: This item has been reviewed by the County Attorney, is legally
sufficient.and requires majority vote for approval. -JAK
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12/11/2012 Item 10.AC.
RECOMMENDATION: To update the existing Clam Bay Management Plan to ensure the
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preservation of the Clam Bay system and compliance with the preserve's NRPA designation; c
and. to establish criteria as indicators for evaluation of dredging needs for the purpose of . / C
maintaining
flushing for the environmental benefit of the Clam Bay system. This shall be
accomplished through a work order under Contract 410-5571 with TuneII, Hall &Associates for
a total cost not to exceed $34,000. The work order deliverables shall include the following:
. Update the Clam Bay Management Plan to achieve the objective of `preservation' since the
`restoration' objective has been successfully achieved.
. Modify the State and Federal maintenance dredging permits to incorporate the revised
Management Plan objective.
. Develop and implement an updated Monitoring Plan consistent with the revised objective of
the Management Plan.
Turell. Hall &Assoc. shall present the proposed work order to the PBSD.the TDC, and the BCC
at the first January.2013 meeting of each of these respective boards.
PREPARED BY: Commissioner Georgia Hiller
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12/11/2012 Item 10.AC.
COLLIER COUNTY
Board of County Commissioners
Item Number: 10.AC. r IF
Item Summary: Recommendation to direct Turrell, Hall&Associates, Inc.to prepare a
work order under Contract#10-5571 to update the existing Clam Bay Management Plan to
ensure the preservation of the Clam Bay system and compliance with this preserve's Natural
Resource Preservation Area ("NRPA")designation; and,to establish criteria as indicators for
evaluation of dredging needs for the purpose of maintaining flushing for the environmental
benefit of the Clam Bay system;to present such work order to the PB5D,the TDC,and the BCC
at the first January, 2013 meeting of each of these respective boards. (Commissioner Hiller)
Meeting Date: 12/11/2012
Prepared By
Name: BrockMar Jo
Title: Executive Secretary to County Manager,CM()
12/5/2012 3:28:42 PM
Submitted by
Title: Executive Secretary to County Manager.CMO
Name: BrockMarvJo
12/5/2012 3:28:43 PM
Approved By
Name: Klatzkowieff
Title:County Attorney
Date: 12/5'2012 3:38:49 PM
Name: OchsLeo
Title:Count Manager
Date: 12"'2012 4:16:07 PM
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