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efta-efta01119647DOJ Data Set 9OtherST. THOMAS EAST END RESERVES MANAGEMENT PLAN
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ST. THOMAS EAST END RESERVES MANAGEMENT PLAN
May, 2011
St. Thomas, U.S. Virgin Islands
Drafted and edited by the STEER Core Team:
Jeanne Brown, VI Coastal Program Director, The Nature Conservancy
Alexandra Holecek, Area of Particular Concern Coordinator, Division of Coastal Zone Management
January Murray, Fisheries Biologist 3, Division of Fish and Wildlife
Lihla Noori, Virgin Islands Marine Advisory Service, University of the Virgin Islands
Jean-Pierre Oriol, Acting Assistant Director, Division of Coastal Zone Management
Judy Pierce, Wildlife Chief, Division of Fish and Wildlife
Renata Platenberg, Wildlife Biologist 3, Division of Fish and Wildlife
Sandra Romano, Masters of Marine and Environmental Science program, University of the Virgin Islands
Drew Russo, Friends of Christmas Cove
Christine Settar, Virgin Islands Marine Advisory Service, University of the Virgin Islands
With valuable input from St. Thomas residents, STEER user groups, business owners, and researchers
(collectively known as STEER Stakeholders)
Contributors:
Tyler Smith, University of the Virgin Islands
Anthony D'Andrea, Oregon State University
Agathe Sector, Conservation Finance Consultant
Elena Kobrinski, Coastal Policy Intern, University of the Virgin Islands, Nova Southeastern University
Anne Marie Hoffman, The Nature Conservancy, University of Maryland
Stephen Hale, Fisheries Biologist II, Division of Fish and Wildlife
Melanie L. Feltmate, The Nature Conservancy
Photographs: Jeanne Brown; Alex Holecek; Shaun Kadison, MMES 2007; Renata Platenberg; Sybille
Sorrentino, Virgin Islands Marine Advisory Service (VIMAS)
Main cover: Judy Pierce, Sybille Sorrentino
Citation: STEER (2011) St. Thomas East End Reserves Management Plan. St. Thomas, USVI.
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The drafting of this management plan was partially funded by award NA09NMF4630112 to The Nature
Conservancy, from the National Oceanic and Atmospheric Administration, U.S. Department of
Commerce. The statements, findings, conclusions, and recommendations are those of the author(s)and
do not necessarily reflect the views of the National Oceanographic and Atmospheric Administration or
the U.S. Department of Commerce. The Department of Planning and Natural Resources Division of Fish
and Wildlife participation was funded by U.S. Fish and Wildlife Service through the Sport Fish and Wildlife
Restoration Act grants Vl-F-19-MHTBM-M and VI-W-25-P.
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STEER Management Plan (May 2011)
Table of Contents
Executive Summary
1
I. Introduction
3
1.1 Purpose and Scope
3
1.2 Legislative Authority
6
1.3 Background of STEER Designation and the 2011 Management Plan
6
1.4 Rules and Regulations of STEER
8
1.5 Location, Access and Facilities
11
1.6 Current Socio-economic Uses of STEER
13
II. Conservation Action Plan
16
2.1 Plan Development process
16
2.2 Vision
18
2.3 Goals
19
2.4 Conservation Resources
19
Mangroves
21
Seagrass Beds
23
Compass Point Salt Pond
24
Sea and Shore Birds
24
Coral Reef Communities
25
Nursery and Fisheries Resources
26
Compatible and Sustainable Use and Enjoyment
27
2.5 Threats
28
2.6 Conservation Objectives and Strategies
31
2.7 Monitoring and Evaluation of Effectiveness
62
2.8 Zone and Mooring Plan
82
III. Sustainable Financial Plan
84
3.1 Summary of the STEER Sustainable Finance Plan
84
3.2 Management Structure and Implementation
90
Establishment of a Park, Board, Capacity staffing, training, facilities, equipment
IV. References
92
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Figures
FIGURE 1
Marine Reserve Wildlife Sanctuaries and natural resources of STEER
4
FIGURE 2
Areas of Particular Concern in STEER
5
FIGURE 3
Watershed Map of STEER
11
FIGURE 4
Facilities Adjacent to STEER
12
FIGURE 5
STEER Habitats
21
FIGURE 6
Conceptual diagram showing the ecosystem services
provided by mangrove ecosystems of STEER
22
FIGURE 7
Conceptual diagram showing the ecosystem services
provided by seagrass ecosystems of STEER
23
FIGURE 8
Proposed STEER Use Zones
83
FIGURE 9
STEER Needs Assessment by Functional Area
87
Tables
TABLE 1
Summary of MRWS Rules and Regulations applicable to STEER
8
TABLE 2
STEER Threat Ranking Matrix
30
TABLE 3
STEER Objectives listed by major threat group (1-9) or management area (10, 11) 32
TABLE 4
Summary of Strategies for STEER ranked by priority, impact and feasibility
34
TABLE 5
STEER Action Steps
36
TABLE 6
STEER Monitoring Plan
64
TABLE 7
STEER Initial Research Needs
79
TABLE 8
STEER Activities Guide
83
TABLE 9
Financial Strategy Ranking for STEER
88
TABLE 10
Potential Revenue, Critical and Optimal Funding for STEER
89
Appendices
(see supplement document "STEER Management Plon: Appendices")
APPENDIX A Relevant STEER Rules and Regulations
APPENDIX B STEER Boundary Coordinates
APPENDIX C Adjacent Commercial Entities
APPENDIX D STEER Documents, Studies, and Papers
Environmental Sensitivity Index Map
Bathymetry in STEER
APPENDIX E Bridge to Nowhere Survey Results
APPENDIX F Full Sustainable Finance Plan
APPENDIX G Core Drafting Team and Stakeholders
APPENDIX H CAP Process, Timeline, Meetings and Workshops
APPENDIX I
STEER Targets: Long Versions
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STEER Management Plan (May 2011)
List of Acronyms
•
AGRRA: Atlantic and Gulf Rapid Reef Assessment
•
APC: Area of Particular Concern
•
BMPs: Best Management Practices
•
CAP (process): Conservation Action Planning
•
CRCP: Coral Reef Conservation Program
•
CWA: Clean Water Act
•
CWP: Center for Watershed Protection
•
CZM: Coastal Zone Management
•
DCCA: Department of Conservation and Cultural Affairs
•
DEE: Division of Environmental Enforcement
•
DEP: Division of Environmental Protection
•
DFW: Division of Fish & Wildlife
•
DPNR: Department of Planning and Natural Resources
•
EIS: Environmental Impact Statement
•
EPA: Environmental Protection Agency
•
FOCC: Friends of Christmas Cove
•
FTE: Full-time employee
•
GIS: Geographic Information System
•
IUCN: International Union for Conservation of Nature
•
LiDAR: light Detection and Ranging
•
MLBB: Mangrove Lagoon Benner Bay
•
MMES: Masters of Marine and Environmental Science
•
MPAs: Marine Protected Areas
•
MRWS: Marine Reserves and Wildlife Sanctuaries
•
MSA: Marine Protection, Research and Sanctuaries Act of 1972
•
MSDs: Marine Sanitation Device
•
NASA: National Aeronautics and Space Administration
•
NMFS: National Marine Fisheries Service
•
NOAA: National Oceanic and Atmospheric Administration
•
NP: Non-point source pollution
•
NPS: National Park Service
•
PA: Protected Area
•
PS: point source pollution
•
SLR: Sea level rise
•
STEER: St. Thomas East End Reserves
•
STT: St. Thomas, VI
•
STXEEMP: St. Croix East End Marine Park
•
TNC: The Nature Conservancy
•
USFWS: U.S. Fish and Wildlife Service
•
USGS: U.S. Geological Survey
•
USVI: U.S. Virgin Islands
•
UVI: University of the Virgin Islands
•
VIMAS: Virgin Islands Marine Advisory Service
•
VINE: Virgin Islands Network of Environmental Educators
•
VIRR: Virgin Islands Rules and Regulations
•
VIWMA: Virgin Islands Waste Management Authority
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EXECUTIVE SUMMARY
This Management Plan contains the roadmap for effectively conserving the coastal and marine natural
and cultural resources of the southeast end of St. Thomas. It does not contain any new rule or
regulation that does not already exist in Virgin Islands Code. By creating a new territorial marine
protected area, collectively deemed the St. Thomas East End Reserves (STEER), several existing
protected areas (Cas Cay / Mangrove Lagoon, St James, and Compass Point Marine Reserves and
Wildlife Sanctuaries) will be protected as one comprehensive management unit. In recognition of the
importance of adjacent natural and cultural resources as well as the imminent threats to them, a
collaborative planning process between the STEER community and the Virgin Islands Department of
Planning and Natural Resources (DPNR), University of the Virgin Islands (UVI), and The Nature
Conservancy (TNC) was initiated in May 2008 to develop this management plan to provide the long term
vision for the area and guide near-term (3-5 years) objectives and activities.
The intent of the STEER Management Plan is to outline the steps needed to restore and
maintain a functional coastal ecosystem that promotes sustainable recreational
opportunities and compatible commercial uses with community engagement through
effective management.
The TARGETED RESOURCES in STEER that this plan aims to
protect, enhance and restore are:
• MANGROVES
• SEAGRASS BEDS
• COMPASS POINT SALT POND
• SEA AND SHORE BIRDS
• CORAL REEF COMMUNITIES
• NURSERY AND FISHERIES RESOURCES
• COMPATIBLE AND SUSTAINABLE USE AND ENJOYMENT
The THREATS to these targets fall into nine general themes:
1. Land-based Sources of Pollution
2. Climate Change
3. Habitat Loss
4. Unsustainable or Illegal Fish Harvest
5. Predators of Sea and Shore Birds
6. Incompatible Use Issues
7. Trash and Debris
8. Physical Damage from Boats
9. Marine-based Sources of Pollution
1
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STEER Management Plan (May 2011)
STRATEGIES developed to abate these threats or restore a targeted resource revolve around:
• Improved watershed and stormwater management
• Increased coordination of permitting, regulation and enforcement of non-point and point-
source pollution and coastal development to prevent habitat loss and sedimentation
• Improving enforcement of existing coastal rules and regulations
• Community outreach
• Developing a climate change adaptation plan
• Creation of a moorings program within STEER
• Developing a Zone and Mooring Plan for recreational and commercial activities
• Improve bird nesting success and survival rates by reducing predation by introduced species
and entanglement by discarded monofilament
• Restoration activities
The primary components of this Management Plan are:
1) An outline of STRATEGIES AND ACTION STEPS aimed to abate threats to these resources or to
restore the targeted resources to acceptable and functional levels.
Page 34
2) A MONITORING PLAN to accompany the management strategies to inform managers,
researchers, funding sources, and Virgin Islanders of the effectiveness of activities to the benefit
of the resources.
Page 64
3) A SUSTAINABLE FINANCE PLAN that identifies the financial need and resources for the
management and operation of STEER.
Page 84
Appendix F
4) A ZONE AND MOORING PLAN which clearly delineates the designated allowed maritime,
recreational and commercial uses with corresponding regulations, and a mooring and anchoring
plan.
Page 82
5) Relevant BACKGROUND INFORMATION necessary for guiding the management of STEER
including legislative structure, current uses and status of the resources, studies, and involved
parties.
Page 6
Appendices C, D, E, and I
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INTRODUCTION
1.1 Purpose and Scope
This Management Plan was developed for the Cas Cay / Mangrove Lagoon, St James, and
Compass Point Marine Reserves and Wildlife Sanctuaries (MRWS) collectively referred to as
the St. Thomas East End Reserves, or "STEER". Prior to the development of this Management
Plan, the most recent plan, written in 1993, focused solely on the Cas Cay/Mangrove Lagoon
MRWS, but was not authorized by the managing authority nor has it been implemented. STEER
is one of the various forms of protected areas throughout the marine and coastal environment
of the U.S. Virgin Islands (USVI). Of the system of protected areas managed by the Territorial
Government of the USVI, this area is the most recent, along with the St. Croix East End Marine
Park (STXEEMP). As part of a larger, territory-wide system of Marine Protected Areas (MPAs),
STXEEMP and STEER are designed to protect the system of coastal resources including
mangroves, seagrass beds, coral reef communities and other critical marine habitats.
3
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STEER Management Plan (May 2011)
St. Thomas
The Living Oceans
Benthic Habitat (2001)
kleclmm densny seagrass
Bare bedrock pavement
i
5tontastraea reel
,
&Aro& fleshy 8 calcareous algae
Rubble
r
Sand
o ,
Nips
Roads
Dense gorgonians on bedrock
Dense mann* 8 encrusting
Dense seagrass
Dicyola on pavement
Sparse corals 8 high algal covet
Sparse corals 8 Du algal cover
Sand W algae
Sand ni calcareous
green algae
Sand Al sparse gorgontans
Sparse seagrass
Turf algae and Mdlepora
.Vc
Natural Resource Inventory
St Thomas East End Reserve Committee
December 4. 2008
Cabita Point
River / Gut
a
Ambient Water Dually
11. P.Ionitoring Stations (DEP) Vegetation Cover
Thicket scrub
Developed
Beach
. 4 Semi 8 Drought
Marine Reserve
deciduous forest
A Inner Mangrove Lagoon
Coasts grassland
CB Cas Cay i Mangrove Lagoon
OMITS hedge
cc St James
Mood dry shiublarvi
0
G Compass Point sag Pone
05
0 25
0 Liam
Figure 1: Marine Reserve Wildlife Sanctuaries and natural resources of STEER
Rock pavement
Mangroves
Freshwater pond (
Mixed Swamp
Salt flat I Salt pond
••••••
•••••••asa00
The MPAs described in this Plan encompass 9.6 km2 of significant coastal, marine and fisheries
resources, including mangrove forests, salt ponds, lagoons, reefs and cays. Located at the
southeastern end of St. Thomas, STEER is thought to be one of the most valuable fish nursery
areas remaining on St. Thomas. Many species of fish and shellfish, including important
commercial and sport fisheries resources, spend a portion of their life protected in the shallow
mangrove and seagrass beds while feeding and growing before populating other marine
habitats in the area. These natural resource-rich areas were declared Areas of Particular
Concern (APCs) in 1979, specifically the Mangrove Lagoon/Benner Bay APC and Vessup Bay APC
(Figure 2: Areas of Particular Concern in STEER). APCs identified in Figure 2 include both
terrestrial and marine areas.
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Figure 2: Areas of Particular Concern in STEER
This Management Plan is designed to provide the long-term vision for STEER and guide near-
term (3-5 years) objectives and activities. It does not contain any new rules or regulations that
do not already exist in the Virgin Islands Code. Components include a management activity
plan (including monitoring for effectiveness), a financial business plan, and a zone and mooring
plan. The Plan is part of an adaptive and iterative management process, ultimately leading to
the sustainable use of the coastal and marine resources in STEER. It is designed to provide
guidance in the near-term, but is also open to modifications based on periodic evaluation of
management activities and results. The monitoring program included in the Plan is designed to
provide the framework for the evaluation of the effectiveness of the management actions.
Each action undertaken by management will be evaluated to ensure that it is achieving the
objectives set forth throughout this plan. This plan should be revised with stakeholder input
after a period of five years from the time of approval and commencement of management
activities to reflect the results of the monitoring program. Specific sections, such as the strategic
actions, will be reviewed on a more frequent basis to adapt to changes.
5
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STEER Management Plan (May 2011)
1.2 Legislative Authority
The Virgin Islands Code, Title 12, Chapter 1, Section 97 grants the Commissioner of the
Department of Planning and Natural Resources (DPNR) the authority to designate or establish
marine and wildlife sanctuaries for the purposes of propagating, feeding and protecting birds,
fish and other wildlife. It is under this authority that the Cas Cay/Mangrove Lagoon, St. James
and Compass Point Pond Marine Reserves and Wildlife Sanctuaries were all established in 1994.
In 2002, Title 12, Chapter 1 of the Virgin Islands Code was amended to include the
establishment of the St. Croix East End Marine Park, and to allow for the future designation of
other marine parks. Section 98(b) of the Code grants the Virgin Islands Coastal Zone
Management Commission (the Commission) the authority to establish other marine parks in
the Virgin Islands as part of a territorial park system; further, the Commission may promulgate
rules and regulations pertaining to the management of such designated areas under the
authority of section 98(d)(3) of the VI Code.
1.3 Background of STEER Designation and the 2011 Management Plan
In 1972, the Legislature of the Virgin Islands (Legislature) passed Act 3330, Commercial Fishing
Promotion, which was aimed to develop the commercial fishing industry and recognize the
significance of the marine habitat to the industry, and its importance to the livelihood of the
people of the Virgin Islands (DCCA, 1979). As part of the Act, the Department of Conservation
and Cultural Affairs (DCCA) was mandated to establish necessary fishery management
programs. In that same year, Congress passed the Marine Protection, Research and Sanctuaries
Act of 1972 (MSA), which would allow for the designation of marine sanctuaries for "the
purpose of preserving or restoring their conservational, recreational, ecological, or aesthetic
values" (DCCA, 1979). The National Oceanic and Atmospheric Administration (NOAA)
Sanctuaries Program Office was tasked with administering the program. Criteria for
designation were commonly based on areas with distinctive and important habitat, species and
ecosystems, although sometimes areas were designated to preserve distinctive resources
where conflicts between human uses and conservation required comprehensive management
planning guidelines.
As early as 1979, the area off southeast St. Thomas was identified as a top candidate for
designation under the National Marine Sanctuary Program. Criteria used in selecting the area
included:
o Ecological value of the area
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o Value of the area for scientific research
o Ability of the area to support fisheries
o Ability to maintain recreational use of the area
It was determined that the area's ecological, cultural, recreational and aesthetic importance to
the people of the Virgin Islands would require increased management for the protection of the
multiple resource uses. Although many years have passed since the investigation into the area
off the southeast of St. Thomas, many of the concerns for the area remain today. The areas
were given some protection when designated MRWSs, but functional management of the area
has been non-existent.
In 2008, DPNR-Division of Coastal Zone
Management (CZM) received an application
submitted by WT Enterprises to moor a vessel in
Christmas Cove on Great St. James Island and
operate it as a floating bar and restaurant. There
was tremendous public outcry against the
granting of a permit for such activity. The main
reason cited was that the area was designated as
a Marine Reserve and Wildlife Sanctuary. After
reviewing the regulations, a floating bar and
restaurant were not specifically prohibited, but
most believed that such an activity could not
foster the goals outlined in the designation of the
area as a reserve. It was clear that a
management plan for the area was lacking; one that would identify a vision for the area and
prevent future applications of this type from occurring. As a result, in April 2008, DPNR, the
University of the Virgin Islands (UVI), The Nature Conservancy (TNC), and a community group
called the Friends of Christmas Cove (FOCC) partnered to create a management plan for all the
designated MRWSs on St. Thomas' east end.
Coincidentally, activities undertaken by DPNR's Division of Environmental Enforcement (DEE) to
remove derelict and unpermitted vessels from the MRWSs in the spring of 2008 drew further
attention to the need for a management plan for the area. This endeavor by DPNR's DEE
happened to coincide with the early formation of the Core Planning Team to spearhead the
drafting of a comprehensive area Management Plan for STEER and the identification of
stakeholders to provide input in the planning process. Community attention and support for a
Zone and Mooring Plan grew as a result of the highly publicized actions by DPNR's DEE.
7
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STEER Management Plan (May 2011)
By creating a management plan for the area, clear conservation goals are established, resource
management can be achieved, and the area can be managed under the Virgin Islands Territorial
Park System.
1.4 Rules and Regulations of STEER
A summary of the Virgin Islands Rules and Regulations (VIRR) and Virgin Islands Code applicable
to STEER is outlined in the table below (Table 1). The complete rules and regulations that apply
to STEER are included in Appendix A: "Relevant STEER Rules and Regulations." The applicable
rules and regulations include:
•
VIRR Title 12, Chapter 1, Subchapter 94: Islands and Cays
•
VIRR Title 12, Chapter 1, Subchapter 96: Prohibited Acts in Wildlife and Marine
Sanctuaries
•
VIRR Title 25 Navigation, Chapter 16: Mooring of Vessels and Houseboats
o Section 404 Mooring and Anchoring of Vessels in the Territory
o Section 405 Mooring Permits, Fees, Renewals and Cancellations
o Section 406 Placing of buoyed mooring; unauthorized use; reassignment;
identification
o Section 408 Unseaworthy and derelict vessels, houseboats, refuse and pollutants
o Section 408a. Prohibition of Houseboats
•
VI Code Title 12, Chapter 2, Endangered and Indigenous Species Act
Table 1. Summary of MRWS Rules and Regulations applicable to STEER
Cas Cay
Marine
Reserve and
Wildlife
Sanctuary
VIRR Title 12
Chapter 1,
Subchapter
94, Islands
and Cays
It is unlawful for any person to land on or create disturbance near
any island or cay listed in the Annex unless the person is a
governmental employee on official business, an authorized scientist,
a licensed seabird guide, or a person possessing a valid visitation
permit who is escorted by a licensed seabird guide acting within the
scope of his license. (Subchapter 94, Section 94(b)-1) (Islands and
cays listed in the Annex include Capella, Carval Rock, Cas Cay,
Cockroach, Congo, Cricket, Dog, Dutchcap, Flanagan, Flat, Frenchcap,
Kalkun, Little Flat, Pelican, Saba, Shark, Stevens', Sula, Turtledove.)
With the exception of Cas Cay which was bequeathed to the
Government of the Virgin Islands "for the exclusive use as a bird
sanctuary, and for the purpose of preserving the cay in its natural
state for the perpetual enjoyment of the people of the Virgin
Islands."
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Subchapter
96, Section
96-2
Prohibited Activities within the Cas Cay MRWS:
Except under permit or specific authorization from the
Commissioner, it is unlawful to:
•
Take or possess any bird, fish, or other wildlife (including any
living organism) or part thereof
•
Unlawful to use, possession or discharge of any firearm, air
rifle, bow and arrow, or any trap or other contrivance
designed for or capable of taking birds, fish or other wildlife
into or within the Marine Reserve and Wildlife Sanctuary.
•
Anchor beyond 7 days within the boundaries of the Marine
Reserve and Wildlife Sanctuary
•
Anchor boats without functioning sewage holding tanks
•
Use in the inner lagoon any internal combustion engine
(Inner lagoon is defined as the area within the Marine
Reserve and Wildlife Sanctuary west of a line from
Turpentine Run to the eastern end of Patricia Cay)
•
Operate any powered vessel in excess of 5 miles per hour
•
Moor any vessel after July 1, 1996. Vessels with current
mooring permits must have a functioning holding tank
capable of being discharged at a pump-out facility or beyond
3 miles at sea. (No new mooring permits will be granted for
this area)
•
Picnic in/at non-designated areas, camp hunt, use of fire
(except in self-contained charcoal-briquette or gas grill),
possession of firearms, playing of amplified music, disturbing
or removal of any plant, animal or mineral, store, repair,
maintain, or construct any vessel or vehicle
Permitted Activities within the Cas Cay MRWS:
Subchapter
96, Section
96-5
Acts permitted, provided a permit is first obtained from the
Commissioner:
•
The use of castnet with a minimum square mesh size of y.
inch to capture baitfish (fry) within 50 feet of the north and
west shorelines of Cas Cay only
Mangrove
Lagoon
Marine
Reserve and
Wildlife
Sanctuary
Subchapter
96, Section
96-2
Prohibited Activities within the Mangrove Lagoon MRWS:
Except under permit or specific authorization from the
Commissioner, it is unlawful to:
•
Take or possess any bird, fish, or other wildlife (including any
living organism) or part thereof
•
Unlawful to use, possession or discharge of any firearm, air
rifle, bow and arrow, or any trap or other contrivance
designed for or capable of taking birds, fish or other wildlife
into or within the Marine Reserve and Wildlife Sanctuary
•
Anchor beyond 7 days within the boundaries of the Marine
9
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STEER Management Plan (May 2011)
Reserve and Wildlife Sanctuary
•
Anchor boats without functioning sewage holding tanks
•
Use in the inner lagoon any internal combustion engine
Operate any powered vessel in excess of 5 miles per hour
•
Moor any vessel after July 1, 1996. Vessels with current
mooring permits must have a functioning holding tank
capable of being discharged at a pump-out facility or beyond
3 miles at sea. (No new mooring permits will be granted for
this area)
•
Picnic in/at non-designated areas, camp hunt, use of fire
(except in self-contained charcoal-briquette or gas grill),
possession of firearms, playing of amplified music, disturbing
or removal of any plant, animal or mineral, store, repair,
maintain, or construct any vessel or vehicle
Compass
Point Pond
Marine
Reserve and
Wildlife
Sanctuary
St. James
Marine
Reserve and
Wildlife
Sanctuary
VIRR Title 12,
Chapter 1,
Subchapter
96, Prohibited
Acts in
Wildlife and
Marine
Sanctuaries
Prohibited Activities within the Compass Point Pond MRWS:
•
Unlawful to use, possession or discharge of any firearm, air
rifle, bow and arrow, or any trap or other contrivance
designed for or capable of taking birds, fish or other wildlife
into or within the Marine Reserve and Wildlife Sanctuary
•
Unlawful to bring livestock, dogs, motor vehicles or to play
loud electronic music in Marine Reserve and Wildlife
Sanctuary
•
Unlawful to disturb or take and plant or animal within the
Marine Reserve and Wildlife Sanctuary
•
Unlawful to store, repair, maintain or construct any vehicle
or vessels within the Marine Reserve and Wildlife Sanctuary
Subchapter
96, Section
96-3
Prohibited Activities within the St. James MRWS:
•
It is unlawful to remove any marine or other wildlife without
a permit or specific authorization from the Commissioner
Subchapter
96, Section
96-4
Permitted Activities within the St. James MRWS:
Acts permitted, provided a permit is first obtained from the
Commissioner:
•
Scientific collecting in support of and for use in a research
project with an approved protocol
•
The use of castnet with a minimum square mesh size of Y.
inch to capture baitfish (fry) within 50 feet of the shoreline,
except for Cow and Calf rocks
•
Fishing with hook and line
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Various Federal regulations also apply to STEER including, but not limited to, the Essential Fish
Habitat Amendment to the Magnusen-Stevens Fishery Conservation and Management Act, the
Endangered Species Act, the Migratory Bird Treaty Act and the Clean Water Act.
1.5 Location, Access and Facilities
The MRWSs described in this Plan, collectively referred to as STEER, encompass 9.6 km2 of
significant coastal, marine and fisheries resources, including mangrove forests, salt ponds,
lagoons, reefs and cays (Figure 1: Marine Reserve Wildlife Sanctuaries and natural resources of
STEER). Located at the southeastern end of St. Thomas, the area spans 39 km (24 miles) of
coastline consisting of mangroves, sandy beaches, rocky headlands, rocky shores, and
developed shoreline. STEER includes the Compass Point Pond, a salt pond located near Benner
Bay. The Cas Cay/ Mangrove Lagoon MRWS has Long Point as a western boundary, Nazareth as
the eastern boundary and contains Patricia, Bovoni, Rotto and Cas Cays. The St. James MRWS
starts at the eastern boundary of the Cas Cay/ Mangrove Lagoon, to the northwestern shore of
Little St. James, encompassing Great St. James to the mean high tide watermark, and reaching
to Cabrita Point. (Please see Figure 3. Watershed map of STEER and Appendix B: STEER
Boundary Coordinates, for the boundary coordinates and descriptions of STEER and the zones
contained within.)
Legend
RIVet I Gut
•
Ambient Wailer Cateroyep,
Motets CO, . WO,
Watersheds
Property Parcels
Marine Reserve
Jetties Ray
by Zone
r jot Inn.? Mangiove Lagoon
Ss Frenchman Bay C? P
Co Can
i M nag' n'a• 189808
2,ti Roe Hook ass.
R4
CC St James
S. Smith Say
Ilhe
Co: Comensit PO4.11 San PCIINI
Figure 3: Watershed Map of STEER
Watershed & Landuse Inventory
St Thomas Emit End Reserve Committee
December 4. 2008
11
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STEER Management Plan (May 2011)
rove Lagoon,
There are five private offshore cays (Little St. James, Great St. James, Current Rock, and Patricia,
Rotto, and Fish cays), two public owned offshore keys (Cas and Bovoni cays), and Cow and Calf
Rocks within STEER. Several adjacent watersheds impact STEER, including Red Hook Bay, Jersey
Bay, and Frenchman Bay watersheds.
There are six hotels /resorts/condominium
associations along the Marine Reserves boundary
(Figure 4: Facilities Adjacent to STEER) with
reverse osmosis plants, a waste water treatment
plant, fueling facilities, back-up generators, and
public access points to the water. In addition, a
large housing community in Estate Bovoni is
located just north of the Clinton Fipps Race track,
directly north of the Mangrove Lagoon. The
municipal landfill for both St. John and St. Thomas
borders the western end of STEER.
Boaters and anglers alike can access STEER by way of nine marinas and boat yards that lie along
the southern shore of St. Thomas. This "Marine Row" was not included in the original physical
boundary of the MRWSs; however due to their proximity and access for the Marine Reserves
waters their practices are critical to this Management Plan. Some public ramps are located at
Benner Bay adjacent to Eco-Tours and Cowpet Bay.
•
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Facilities Adjacent to STEER
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1.6 Current Socio-economic Uses of STEER
Recreational use:
The luxurious beaches and coastlines of STEER are
favored sites for snorkeling and scuba diving, for both
residents and visitors, particularly at Cas Cay,
Christmas Cove, Great Bay, and Cow and Calf Rocks.
An active recreational water sports community
partakes in windsurfing, kite boarding, kayaking, and
sailing from public beach access points and swimming
areas located at condo and hotel locations such as
Vessup Beach, Ritz Carlton, Secret Harbor, Cowpet Bay
East & West, Anchorage, The Elysian, Water Point,
• STEER, R. Platenberg
Cabrita Point and Deck Point residential areas. In addition, visitors engage in sightseeing
excursions on both motor boats and sailing vessels. Bait fishing, hook and line as well as sport
fishing are limited and require DPNR permits.
Vista into Reserve, R. Platenberg
Widely known as the original boating community in the Virgin Islands, STEER is a gateway for
"down-island" and stateside voyages, where boaters can readily service their boats (Appendix
C: "Adjacent Commercial Entities"). Home to the St. Thomas Yacht Club at Cowpet Bay and the
annual ROLEX regatta, STEER is a world renowned destination for the charter boat and private
yacht industry including powerboats, sailing vessels and fishing charters. An active residential
boating community has developed in STEER, including overnight stays as well as full time and
seasonal live-aboards. Private DPNR-permitted moorings as well as personal moorings are
13
EFTA01119665
STEER Management Plan (May 2011)
Sailboats moored at
Cas Cay, R. Platenberg
found in STEER. As part of the management for the area, permanent mooring buoys will be
installed in STEER to help prevent anchor damage to coral reefs, seagrass beds and mangroves.
Commercial Use:
Many of the commercial activities within or adjacent to the
boundaries of STEER support the traditional and recreational
uses of the area. Because the southeast area of St. Thomas is
convenient to a major airport, downtown Charlotte Amalie, Red
Hook, St. John and the British Virgin Islands, a concentration of
seaside hotels, private villa rentals, condominiums, restaurants,
and yacht clubs are all concentrated around the STEER coastline.
air
n, R. Platenberg
Routes for regularly
scheduled inter-island ferry service and commercial barges pass through the St. James Reserve
within STEER.
There are powerboat, sail, water sports equipment and scuba diving
businesses. Ecotourism-based businesses also exist within STEER, one of
which provides kayak tours of the mangrove lagoon. The majority of St.
Thomas marinas and boatyards bordering the Reserves provide various
marine related services (although the marine facilities are not within the
boundaries of the Reserves, all water craft must enter and exit via the
Reserves waters). The St. Thomas Yacht Club in Cowpet Bay has moorings
available to its members on a fee basis. Limited fishing (bait fishing with
cast net as well as hook and line by permit only) occurs in STEER.
Research and Education:
STEER is convenient and easily accessible by research and
educational groups alike. Over the years, USVI resource agencies
including DPNR's CZM, Division of Fish & Wildlife (DFW), Division
of Environmental Protection (DEP), and UVI have gathered a
wealth of information related to the area's fish, turtle, bird, coral
reefs, sea grasses, salt pond dynamics, mangroves and water
quality. More recently, UVI's Center for Marine and Environmental
Studies, NOAA, Gulf of Mexico Foundation and TNC have also been
active in research, restoration and management initiatives. Most of
ionitoring in STEER,
IMES 2009
the documents associated with past research are available at the DFW Office in Red Hook or
see list of references at the end of this document and the "Appendix D: STEER Documents,
Studies, and Papers" supplemental to this report for more detailed information.
EFTA01119666
The diverse habitats in STEER provide a research opportunity for undergraduate and graduate
students, visiting researchers from off-island, as well as elementary and secondary school
students to study the relationships between the ocean, the reef, the shore, and
commercial/residential uses in the area. There is expressed interest in "citizen science"
opportunities whereby tour operators, residents, park visitors, and guests participate in
monitoring of marine habitats as part of their marine park experience.
Community Perceptions:
A survey was distributed to participants at the 2009 Earth Day clean up event located at the
locally known "bridge to nowhere," an area of land adjacent to STEER and within the Jersey Bay
watershed, and usually encumbered by large amounts of roadside waste and debris. The
purpose of the survey was to gather information about community perceptions, understanding,
and attitudes towards the Jersey Bay watershed.
), VIMAS
storm water catchment and groundwater recharge." The top issues in the Jersey Bay
watershed were "sediment run-off," "dumping," "sewage outfall," and "development." When
asked what they would do to prevent further watershed pollution if given assistance, the most
popular choices made were "volunteer for community environmental programs," "report
commercial polluters," and "plant trees" (see Appendix E: "Bride to Nowhere Survey Results" for
complete survey and results).
Out of the 60 individuals surveyed, 29 of
them indicated as living in or near the
Jersey Bay watershed. When asked why
this watershed was important, the
popular responses were: "it contains
habitat for rare St. Thomas wildlife such
as freshwater shrimp and wetland
birds," "it is home to many different
kinds of plants," and "it is an area for
While the survey was not widely distributed in the USVI, these results do indicate that there is a
concern for the current health of the STEER watershed and adjacent areas, and that residents
are interested in, and willing to participate in the conservation mission and goals of STEER.
15
EFTA01119667
STEER Management Plan (May 2011)
STEER Stakeholder meeting, VIMAS
II. CONSERVATION ACTION PLAN (CAP)
2.1 Plan Development Process
The initiative to build a comprehensive management plan for
STEER began in the spring of 2008. The development of the Plan
followed The Nature Conservancy's Conservation Action Planning
(CAP Process) as a mechanism to develop a strategic vision and
management plan for the Reserves (TNC 2007). The CAP
methodology has been utilized and tested by TNC and its partners
for over fifteen years and has resulted in effective management
plans for hundreds of protected areas around the world. CAP is
based on the principles of adaptive management and is designed to
facilitate and utilize input from stakeholders.
The CAP is implemented through a series of planning meetings and workshops with the Core Planning
Team and the Stakeholder Advisory Group. Facilitated discussions result in the development of goals,
identification of priority conservation resources and their condition, understanding of human activities
impacting the resources, and selection of objectives and strategies for improving or maintaining the
resources within STEER. The process of working through CAP for protected areas results in a
comprehensive management plan based on a solid ecological foundation focused on specific and
attainable strategies for biodiversity conservation and threat abatement. The original St. Croix East
End Marine Park Management Plan was also developed using early CAP principles. Ultimately, the
process can address capacity issues and promote a financial plan for monitoring and evaluation. Most
importantly, the CAP process results in the creation of an overall work plan for local management
authorities and related agencies to translate into annual work plans.
The sustainable financial plan for STEER as contained within this Management Plan (page 84 and
Appendix F: "Full Sustainable Finance Plan") was developed using World Wildlife Foundation's financial
modeling template and TNC's methods of Integrated Strategic and Financial Planning following
Conservation Finance Alliance methods and the Convention of Biological Diversity Programme of Work
on Protected Areas. This included a finance gap assessment, which aided in the development of a
realistic work plan, with associated costs. The resulting financial model provides comprehensive, long-
term estimates of costs of each program, as well as potential sources of revenue. The total costs,
revenue estimates and gap analyses derived from the model provide the components for developing
sustainable funding vehicles and fundraising proposals.
The Management Plan was developed by the VI-DPNR (the Management Authority), UVI, and TNC with
funding from NOAA and the US Fish and Wildlife Service (USFWS). Personnel of DPNR's Divisions of
CZM, DFW, DEP, and DEE contributed to the drafting of the plan as did faculty and students of the UVI
and Friends of Christmas Cove. This process relied heavily on community expertise, with a series of
EFTA01119668
community workshops held to generate input and ideas from the Stakeholder Advisory Group, special
interest groups, and other regional experts during consultation meetings and workshops (see Appendix
G: "Core Drafting Team and Stakeholders" for list of Core Planning Team and Stakeholder Advisory
Group members involved). A brief description of the process that guided the workshops (CAP) and the
timeline of the series of meetings and workshops held are included in Appendix H: "CAP Process,
Timeline, Meetings and Workshops."
The STEER CAP process also benefited from conducting a multitude of broad community engagement
activities including: Bridge to Nowhere Earth Day Clean-Up 2009, Reef Fest Exhibit 2009, Boating Safety
Booth, STEER/Cleansweeps Mangrove Restoration/ VI Waste Management Authority-Youth
Environmental Services summer program, UVI high school mangrove/seagrass monitoring
demonstration, several radio shows, publishing of a factsheet, inclusion in recent USVI legislators
environmental briefing book, utilization of Google Groups communication tool (STEER Stakeholders
2009), delivery of watershed socio-economic survey to resident focus group, web-based posting of
documents, and periodic newspaper articles. Conducted by Core Steering Team members and
targeted for the wider St. Thomas Community, these activities served as opportunities to build support
and awareness for the plan, a starting point for adding societal and natural resource conservation
value to the area, imperative to the successful implementation of the plan.
Bridge -2- No Where
•
Earth ➢ag Clean-Op 2009
Restoring Oar Precious Watershed TegetherMr
Thanks to the inspiration and partnership of:
nvironmental Association of St. Thomas, WI- Center for Marine and Environmental Studies, Bellows In-
national, Department of Planning and Natural Resources, Budget Marine, &
St. Thomas East End Reserve Management Planning Group
Bridge to Nowhere, Earth Day Clean•Up Poster
17
EFTA01119669
STEER Management Plan (May 2011)
r at a trash clean-up, VIMAS
2.2 Vision
The aim of STEER's vision statement is a very brief summary of what STEER management is trying to
achieve. It was based on the reason the Reserves were originally established and why they continue to
be important today. It was designed to be:
•
Relatively General - Broadly defined to encompass all possible project activities
•
Visionary - Inspirational in outlining the desired change in the state of the targets toward
which the project is working
•
Brief - Simple and succinct so that that all project participants can describe the vision
A statement of the vision the community has for STEER was collaboratively written by the Core
Steering Team and the Stakeholder group in a series of steps across two meetings. The steps included
asking participants: "What is significant about the place?" What is important to you?" and "What do
you want STEER to look like in 20 years?" A list of statements was produced, forming the basis for the
vision that was vetted at several subsequent stakeholder meetings. The resulting vision for STEER is:
'al
ith
.In action, VIMAS
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2.3 Goals
The goals for the activities planned for the management of STEER were developed using a similar
approach of stakeholder input, review, editing, and building consensus over a series of meetings. Most
of what was originally expressed in the visioning process but not captured in the vision, such as
specifically promoting research in the area, was incorporated into the goals. The resulting
management goals of STEER are:
GOAL #1 Bolster natural resource condition by utilizing ecosystem-based management
principles that aim to conserve watersheds and adjacent marine habitats critical to our island's
fishery and tourism resources.
GOAL #2 Adopt effective management models that incorporate research and planning, to
elevate STEER status into the USVI Territorial Park System marine protected area network.
GOAL #3 Inspire the community to support and participate in STEER management through
community engagement opportunities, educational activities, and a variety of communication
strategies.
GOAL #4 Fortify widespread socio-economic benefits, while respecting traditional use and
cultural values
2.4 Conservation Resources (TARGETS)
The resources within STEER that stakeholders, resource managers and experts feel are to be the
primary targets of our conservation efforts were identified in a series of workshops. These
"Targets" provide a basis for all subsequent planning steps, including the determination of indicators
and creation of monitoring plans to gauge the effectiveness of management of STEER. Conservation
targets can be thought of as the resources that are important or unique to STEER that need to be
protected whether they are natural, cultural, or socio-economic.
From a long list of all desired targets of protection, the top targets were determined to be:
• MANGROVES
• SEAGRASS BEDS
• COMPASS POINT SALT POND
• SEA AND SHORE BIRDS
• CORAL REEF COMMUNITIES
• NURSERY AND FISHERIES RESOURCES
• COMPATIBLE AND SUSTAINABLE USE AND ENJOYMENT
19
EFTA01119671
STEER Management Plan (May 2011)
All participants in the CAP process have
felt strongly that improved water
quality should be a primary target for
conservation action within STEER.
However, in subsequent steps, we
realized that improvement of water
quality, as an attribute for all of the
above listed targets, would benefit all
seven targets. Improved water quality
is thereby considered not only a target
for conservation strategies and action,
but also an overarching aim for STEER.
It also serves as an important indicator
of improvement in the status of the
targets. Participants felt confident that
water quality is a major theme of action
for this Management Plan.
Furthermore, from a long list of species
identified as targets to protect (such as
conch, fiddler crabs, certain seabirds,
parrotfish, etc.) we felt that targeting
conservation efforts on the habitats
that these species need to thrive will
likely improve the status of these
species within STEER. This can be
gauged by measuring presence,
population levels, biomass, or status of
these species as indicators of successful
management of the targets (Section 2.7 M
For comparison, the following lists important habitats and
features of STEER that were at one point identified in various
legislative, scientific and historical documents and formed the
basis for designation of the MRWSs on the east end of St.
Thomas:
o The Reserve contains six offshore coys that are considered
St. Thomas' most important assets due to their pristine
state. It was noted that the cays total almost 300 acres of
which only 15 ore public; Cas Cay was bequeathed to the VI
government.
o The mangroves in Jersey Bay are considered the most
significant mangrove area in the VI and the last remaining
such area on St. Thomas. The primary significant ecological
function of these mangroves is as nursery and feeding
ground of important finfish and invertebrate fisheries, and
as a filtering agent for the runoff from adjoining
watersheds. The mangrove system also provides valuable
shoreline protection and shelter for boots during emergency
weather events.
o Solt ponds (includes coastal salt ponds found in Great St.
James).
o Coral reefs with their important ecological and recreational
value.
o Sea grasses, also serving as nursery and feeding grounds for
fishes.
o Guts (stormwoter drainages with riparian habitat) in the
adjacent watersheds.
o Recreational resources which play a major role in the lives
of Virgin Islanders and hove become important economic
resources as well.
For a more comprehensive list of species commonly associated
with STEER, see Appendix D or The Comprehensive Wildlife
Conservation Strategy for the Virgin Islands at
vifishandwildlife.com
onitoring and Evaluation of Effectiveness page 62).
rg
10
EFTA01119672
The following describes the role of STEER conservation Targets in the ecosystem, their characteristics,
status and extent, and pressures on these resources. For more comprehensive background, studies,
and references, please see "Appendix D: STEER Documents, Studies, and Papers."
0
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2.4.1 Mangroves
(For a more extensive description of mangroves in the USVI, see Appendix 1: STEER Targets: Long Versions)
Mangroves are salt-tolerant plants that grow along tropical and sub-tropical coasts. They require
warm temperatures, calm near shore waters, and low-lying coastal land. Their unique structures serve
several important roles in marine ecosystems. The dense root system, especially prevalent in the red
mangroves, protects coral by filtering land-based sediment that would otherwise flow into the ocean
and obstruct sunlight from reaching the coral. The roots also provide nutrient-rich detritus and
protection for larvae and juvenile fish, resulting in an ideal fish and shellfish breeding ground and
nursery. Mangrove trees are also home to various species of birds. Furthermore, mangroves are
valuable to humans, especially in times of severe weather. The roots are able to absorb high levels of
wave energy; and boaters often protect their boats by docking them within the mangroves. The
mangroves also protect the land behind them from erosion and flooding.
STEER is adjacent to the largest mangrove stand on St. Thomas and includes the lagoon at the western
end of the Reserves within its boundaries (Figure 5: STEER Habitats). This lagoon not only supports
local tourism business but also is commercially important for marine related business and has
21
EFTA01119673
STEER Management Plan (May 2011)
Red Mangrove, S. Sorentino
historically been a fishing and boating hub. This region, the Mangrove Lagoon-Benner Bay (MLBB), has
been designated one of six APCs on St. Thomas due to potential threats to the ecosystem from its
location beneath the largest watershed on the island and proximity to the Bovoni landfill.
Encroachment of human activity (e.g., development) often limits the mangrove extent, particularly
along the northern edge of the mangrove lagoon. The mangrove
delta in the Inner Mangrove Lagoon was altered during the
construction of the Clinton Phipps racetrack leading to a
channelization of the Turpentine Run drainage. This has both
reduced the habitat extent of the mangroves in the northern
portion of the Mangrove Lagoon and led to much of the sediment
being delivered from the watershed down Turpentine Run and its
tributaries, bypassing most of the mangroves and resulting in
infilling of the Inner Lagoon. The western edge of the MLBB is
below the Bovoni landfill and the mangroves along this shoreline
often have debris caught within their prop roots. Leaching from
the dump also has the possibility to influence the growth and
productivity of the mangroves along this region of the Reserves.
There is an absence of invertebrate communities on the prop roots and in the sediments near the
mangroves that may reduce the number of juvenile fish and birds that can effectively use this region as
a feeding ground. Both improper mooring to mangroves and derelict vessels moved during storms and
hurricanes can damage the most shoreward portions of the mangrove stands within STEER and affect
both the recovery of the mangroves and the extension of nursery and feeding habitat available for
commercially and ecologically important species.
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EFTA01119674
2.4.2 Seagrass Beds
(For a more extensive description of seagrasses in the USV1, see Appendix 1: STEER Targets: Long Versions)
Seagrass beds are most prevalent in lagoon areas and play an integral role in the well-being of a marine
ecosystem. Seagrass beds trap and stabilize sediment, resulting in better water clarity and light
penetration that are necessary conditions for coral reefs to flourish. The extensive root system of
seagrass beds limits erosion by holding the sand substrate together, preventing extensive shifting of
sand during storms. Seagrass also provides important habitat and refuge from predators for juvenile
reef fish. Furthermore, green sea turtles, several herbivorous fish, echinoderms, mollusks, and birds
feed on the seagrass.
Seagrass beds are located throughout STEER. The
major threat to seagrass beds is direct physical
damage or disturbance done by boat anchoring in
seagrass habitat and to a lesser degree by prop
scarring by boats in the shallow waters of the
Reserves. Anchoring within seagrass beds in
particular can cause extensive damage by creating
'blowout' holes that can migrate and expand after
the initial disturbance, taking years to recover.
Coastal development can also have a major impact
on nearshore eelgrass beds, especially the
construction of docks and marinas that project into the
ve roots, R. Platenberg
shallow waters and shade any seagrass present. Activities that can alter water quality conditions are
another major threat to seagrass habitats within the Reserves. The changes in water clarity and
nutrients can favor macroalgal and epiphytic growth that reduces seagrass cover.
Tit
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Figure 7: Conceptual diagram showing the ecosystem services provided by seagrass ecosystems of STEER
23
EFTA01119675
STEER Management Plan (May 2011)
2.4.3 Compass Point Salt Pond
(For a more extensive description of Compass Point Salt Pond in the USVI, see Appendix I: STEER Targets: Long Versions)
Salt ponds and the specialized salt-tolerant vegetation
communities that they support perform a variety of
biological, hydrologic and water quality functions. These
ponds act as catchment basins for runoff, debris, and
pollutants, thus protecting coral and seagrass beds in the
marine environment. The indirect functions of salt ponds
and their associated mangrove systems include the provision
of storm protection, flood mitigation, shoreline stabilization,
.7_
and shoreline erosion control. Salt ponds provide an
essential foraging, roosting and nesting site habitat for
indigenous and migratory birds and are home to the federally endangered Virgin Islands Tree Boa.
Input from upland activities is the most significant
threat to salt pond ecosystems. Mangroves may
be affected by rising water levels as a result of
global climate change. Human encroachment
prevents the mangroves from moving up the
shore. Hurricanes can have devastating impacts
on mangroves and salt pond systems, and impacts
from hurricanes Hugo (1989) and Marilyn (1995)
are still visible today. The pond and associated
wildlife are impacted by human encroachment,
including light pollution from nearby residences,
traffic along the road encircling the pond, noise, and trash. Mammalian predators pose a significant
threat to ground nesting waterbirds. The pond is impacted by ongoing sediment runoff and changes to
the surrounding landscape, which has caused a significant degree of Willing. With the increased
development that has occurred in St. Thomas over the past thirty years, salt ponds are an endangered
habitat type in the Virgin Islands.
TEER:
eer and boas, use
lin STEER. The
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2.4.4 Sea and Shore Birds
(For a more extensive description of sea and shore birds in the USVI, see Appendix I: STEER Targets: Long Versions)
STEER is considered a biodiversity "hotspot" for bird species in part due to the existence of the rich
fisheries resources, the largest intact mangrove system in the northern Virgin Islands comprising the
Mangrove Lagoon and Jersey Bay, the presence of the Compass Point Salt Pond and the salt ponds on
Great St. James, and numerous other breeding, roosting and nesting areas. The Zenaida Dove (Zenaida
aurita), a Virgin Islands game species, nests and feeds on Cas Cay.
EFTA01119676
The primary threat to birds in this area is from predation by
introduced species, such as rats, mongooses and feral cats. Sea
and shore birds on St. Thomas are also often the victim of
entanglement by discarded fishing line and hooks. Furthermore,
loss of the mangrove and salt pond coastal habitats in STEER due
to encroachment, sedimentation, or sea level rise poses a
significant threat to the birds of STEER.
.
-
tone, R. Platenberg
2.4.5 Coral Reef and Hard-bottom Benthic Communities
(For a more extensive description of coral reef communities in the USVI, see Appendix 1: STEER Targets: Long Versions)
The network of habitats found within STEER shelter and support commercially, recreationally and
ecologically important species, and coral reefs form an important component of this network. The
shallow waters of STEER support a variety of coral reef and hard-bottom benthic communities typical
of the USVI and Lesser Antilles. Animals completing movements from juvenile settling habitats, such
as extensive mangrove areas, to adult habitats, such as offshore reefs, encounter a variety of coral reef
habitats within STEER. Also, fishes and invertebrates that forage in seagrass and macroalgae beds at
night use the reef as shelter during the daytime. Thus, coral reefs add to the richness of life within the
Reserves and the surrounding marine habitats. A high diversity of hard corals has been recorded from
numerous studies within STEER, with about 45 species known. Among the recorded species,
threatened Acropora palmata (elkhorn coral) and Acropora cervicornis (staghorn coral) are plentiful in
shallow aggregations. In 2006, the United States listed elkhorn and staghorn coral as vulnerable under the
Endangered Species Act due to their widespread decline throughout their Caribbean range. In 2009, NOAA's
National Marine Fisheries Service was petitioned to review 82 coral species, 8 of which are found in the
Caribbean, to determine whether they should be listed under the Endangered Species Act. As of the
publication date of this document, NOAA is still reviewing the listing of the following Caribbean
species: Agaricia lamarcki (lamarck's sheet coral), Montastraea annularis (boulder star coral),
Montastraea faveolata (mountainous star coral), Montastraea franksi, Dendrogyra cylindrus (pillar
coral), Dichocoenia stokesii (elliptical star coral or pineapple coral), Mycetophyllia ferox (rough cactus
coral), Ocarina varicose (large ivory coral, ivory bush coral, ivory tree coral).
25
EFTA01119677
STEER Management Plan (May 2011)
In 2005, unprecedented warm water temperatures lead to coral bleaching and a subsequent disease
outbreak that caused a 40% decrease in shallow water coral cover throughout the USVI. Corals within
STEER were also susceptible to this event with losses on the order of 15% for mixed coral communities
on hard bottom to over 50% for coral reefs composed of dense star coral (Montastraea complex).
Superimposed on these regional stressors are the local stresses arising from land-based sources of
pollution, such as sediments, to marine-based sources of pollution, such as toxins and hydrocarbons, to
direct destruction of reef habitats, such as anchor damage. As examples, a long-term coral monitoring
site at Coculus Rock is in the upper third of silt deposition rates for 17 sites across the USVI, and the
highest water concentrations in the US Caribbean of Irgarol, a marine anti-fouling chemical toxic to
corals, seagrass, and mangroves, was found in waters of the mangrove lagoon (Carbery et al. 2006). It
is not known how fishing, a recognized disturbance to the ecology of coral reefs, affects corals in
STEER, as fishing is restricted and currently unmonitored. However, regional depletion of fisheries
species may have impacts, even within marine protected area borders. Of particular concern is the
reduction in number of large parrotfish and other herbivores which keep the growth of macroalgae in
check, thus allowing for growth of new corals in an already-threatened ecosystem.
2.4.6 Nursery and Fisheries Resources
(For a more extensive description of nursery &fisheries resources in the USW, see Appendix STEER Targets: Long Versions)
STEER encompasses diverse tropical marine
ecosystems including numerous habitat types on
which a wide variety of marine species depend,
especially juvenile fish species. The diverse marine
communities situated southeast of St. Thomas form
a highly productive and ecologically significant
ecosystem whose preservation and management is
important to sustain the region's fisheries
(commercial and recreational). Several species of
enberg
The mangrove lagoon,
reef and pelagic fish spend part of their life cycle in the habitats within STEER.
which includes Bovoni Cay, Cas Cay, and Patricia Cay, is the
most extensive red mangrove system remaining in the Virgin
Islands. The area is a major nursery for many species of reef
fish of commercial and recreational value, such as snappers
and groupers. It also provides habitat for spiny lobster and
conch. Other recreational fish, such as tarpon, bonefish and
snook spend the majority of their life cycle in the STEER
lagoon. The marine sanctuary also contains large expanses of
seagrass flats and colonized hardbottom which are habitats
EFTA01119678
Recreation in the Inner Mangrove
Lagoon, R. Platenberg
for many species of juvenile fish and mollusks, such as wrasses, snappers, and conch. STEER
contributes to a viable commercial fishery and sport fishing industry by protecting a portion of the
spawning stock from exploitation.
Many factors can be attributed to the source of decline or cause concern for fishery and nursery
resources within STEER. Land based sources of pollution such as leachate from the Bovoni dump
flowing into the mangrove lagoon, marine pollution from nearby marinas, pollution flowing into the
mangrove lagoon from upland guts, direct removal of mangrove prop root shelter habitat for juvenile
fish, and illegal fishing within the area are all a major concern. Reduction of pollution and protection of
the vital mangrove habitat is critical for a stabilization of fisheries resources within STEER.
2.4.7 Compatible and Sustainable Use and Enjoyment
STEER is a busy boating destination, adjacent to several marinas and
boat supply businesses. Charter boating, eco-tourism in the form of
kayaking tours, kite surfing, SCUBA diving, swimming, wildlife viewing,
snorkeling, and sailing are all popular human uses of STEER, both by
residents and visitors.
There has been an increasing conflict of use as the density of boaters,
visitors and businesses increase in the area. The ferries from
Charlotte Amalie and St. John or the British Virgin Islands pass directly
through STEER. Traditionally, Virgin Island residents relied on the STEER area for subsistence
harvesting of baitfish, lobster, whelk, and conch that were accessible from the seashore, docks and
private jetties, although now harvest is restricted to permitted baitfish collection and hand line fishing
only. Access to STEER from the shore has been altered, limiting traditional use of the area. Further,
residents worry that a lack of transparency in the actions of the management authority (DPNR) conflict
with the peaceful enjoyment of the area. STEER Stakeholders have expressed a desire that when
dealing with people and boats in the Reserves, it is better to educate and mitigate rather than
eliminate.
27
EFTA01119679
STEER Management Plan (May 2011)
2.5 Threats
Threats to resources, also considered
impacts or risks, can be something that
directly impacts a conservation target or
indirectly impacts an ecological process
important to sustaining the conservation
target. Knowing the threats that impact the
resources forms the basis for formulating
strategies and activities for the management
of STEER.
Trash and debris in water, R. Platenberg
The threats to conservation targets were identified by two means: first the
stresses (similar to symptoms observed for a target, such as reduced nesting
success of shore birds) were carefully considered. These stresses, the impairment
Stormwater runoff,
A. Holecek
or degradation of key ecological attributes of the target, were ranked based on the severity and scope
of the stress. Then, the source of the symptom, or the threat (such as predation on nesting shorebirds
by rats), was identified. These threats
were ranked based on the contribution the
threat had in causing stress to the target
and the irreversibility of the threat. See
sidebar for more information on stresses,
threats and the criteria to rank these.
At first iteration, stakeholders, resource
managers and experts identified a long list
of impacts to STEER, including ones that
were pervasive, historical, and others later
determined to be minor or secondary
concerns. By using criteria-based ranking
of the stresses and threats, the direct
threats to targets were prioritized so that
conservation actions can be directed
where they are most needed. This is
important because in any given
management or conservation area, there
are always many activities that can be
undertaken, but what can be
accomplished to truly address critical
threats are limited by energy, resources
and time. All threats identified during the 2008-2009 CAP process have been recorded so that during
vtabbrevettedwittS
: timers occununces)
urrentarninntances
red by the savor
and mimosa
nfable
nmItmenit of resources
nst
EFTA01119680
later review and assessment of management activities, these threats can be considered for future
action if still applicable. For example, reduced tranquility within the Cas/Cay, Mangrove Lagoon area
was identified as a source of stress to sea birds in the area. This stress, and the source of the stress
(the threat of the nearby firing range, motorized boats, human disturbance, and large parties), were
later determined to not be a current critical threat to the sea and shore birds, whereas the
introduction of predators to bird nesting grounds is considered a critical threat to this target.
Many iterations later, after considering what the current critical threats are to the STEER targets, a list
of 20 direct threats was determined. These can be grouped into 9 general themes (listed in general
order of significance):
ides any
from boat yards)
The following threat matrix (Table 2), demonstrating the use of ranking of the sources of stress to
targets, shows how overall impacts to resources elevate
targets to require the most attention for conservation,
protection or restoration (e.g., the Compass Point Salt
Pond), or abatement of critical threats (e.g., land-based
pollution). Threats are ranked in the matrix based on
existing 2010-2011 knowledge and science. The threats
will be reevaluated and revised in the future according to
new information and changing conditions.
J. Brown
29
EFTA01119681
STEER Management Plan (May 2011)
Table 2. STEER Threat Ranking Matrix
TARGETS--> (7)
THREA
THEME
11Th reatsll (20)
Salt
Birds
Pond
Coral
Sea-
grass
Fish
(juv)
Use/
Access
Summar
Man- yThreat
grove
Rating
Land-based Sources of
Pollution
Impaired watershed / upland development,
Point-Source & NPS contaminated
stormwater runoff (sediment, nutrients,
toxins)
Mediu
m
di
High
High
High
Sedimentation (road building,
development, exposed soils, improper
stormwater drainage, airborne sediments,
dredging, beach nourishment with fine
sand)
High
High
High
High
4)
W
%
t4
£
5 5
Climate Change: Increased sea surface temp
High
_
I _-
Climate Change: Sea level rise, change in
precipitation
High
■
High
16:
%
r
'll
x
Direct habitat removal/ Encroachment
High
Mediu
m
High
High
Marine Expansion (slips, docks)
High
Mediu High
High
Derelict vessels and boat wrecks
(groundings)
Dredging for marina
Mediu
r
co
.?
ti: „,
x
Illegal harvest inside STEER
Mediu
m
Loss of herbivores
High
5
la
a,
er.
Predators from dump, boats, shoreline
(feral animals, rats and mongooses)
High
Medium
,/,
n
N
vi
si
Lack of public acesss
High
Medium
No transparency with DPNR
Trash and Debris
Derelict vessels and boat wrecks
(groundings)
Land-based Trash and Debris
Mediu
m
Mediu
m
Media
m
Medium
Marine debris (monofilament)
73
? 4
V- £
f es w
Anchor damage
Groundings
Marine
Pollution
Hydrocarbon pollution from commercial
vessels passing through
Mediu
m
Vessel sewage (nutrients and bacteria)
Hee II : IL.
Ini
High
High
High
High
Media
m
EFTA01119682
2.6 Conservation Objectives Strategies and Action Steps
Participants in the STEER CAP process developed objectives, strategies and action steps to address the
critical threats. This is one of the most critical sections of
the management plan and will guide activities undertaken in
the next 1-2 critical years of early implementation as well as
longer-term (5 year) intentions for conservation.
The objective is a specific statement that details the desired
accomplishments or outcomes of a particular set of activities
within a project, typically set for abatement of critical
threats and for restoration of degraded key ecological
attributes (Table 3). Core questions asked were, "What do
we need to accomplish?", and "How will our objective affect
the given threat?"
The objectives then led us to strategies for STEER (Table 4).
A conservation strategy is a broad course of action intended
to achieve a specific objective (outcome) that abates a
threat, and/or enhances the viability of a conservation
target. A strategy will include the activities required to
accomplish each objective, and the specific action steps
required to complete each strategic action (Table 5). Core
questions asked to determine what our strategies should be
were, "What is the most effective way to achieve the results
we stated in our objective?" What is the most effective way
to abate this threat (threat = source + stresses it causes) or
multiple threats?" and "Will the strategic actions accomplish the objective?"
The objectives were written to
1
be SMART which guides us
into an implementation plan
for the next five years.
SPECIFIC (What area? What
target will this benefit? Focus
on linkage to a specific threat.)
MEASUREABLE (How will we know
that we've reached our
objective?)
ACHIEVABLE, REALISTIC (Within
capacity and our timeframe?)
RESULTS ORIENTED (Success!
Gets us to the desired status
and rating for the target and
improves the target)
TIME-BOUND (establishes 5 years
to start to show progress. Can
also suggest an objective of
longer-term viability to reach
by 5-40 yrs.)
An OBJECTIVE is where you want to be. A STRATEGY is how you will get there. In some cases,
strategies or action steps were considered well before an objective was formulated. In this case, the
group determined if such strategies would still get us where we needed to be with a target, and could
we develop a SMART objective (see
box, above) to guide us.
The following tables show priority
ranked strategies for STEER and the
Objectives-Strategies-Action Steps. As
this is the meat and bones of the Management Plan; these tables need to be constantly reviewed,
updated, and likely amended to reflect new needs or other information that can feed into
management decisions. Periodic updates will be necessary as activities progress, or as priorities
change.
For now, the use of '7BD" or "r written into an
objective is acceptable until we know what our measure
for success will be; finding the answer most likely
becomes Action Step #1- a research priority.
31
EFTA01119683
STEER Management Plan (May 2011)
Table 3. STEER Objectives listed by major threat group (1-9) or management area (10, 11)
1. LAND-BASED SOURCES OF POLLUTION
Threat: Impaired watershed
I Targets: Salt Pond, Seagrass, Coral, Birds, Fishery Resources
Objective 1.1
To reduce sediment and nutrient inputs from land-based sources of pollution on the marine
environment by 15% by 2015, and reduce to within acceptable limits by 2020.
Objective 1.2
To reduce the amount of contaminants entering into the Inner Mangrove Lagoon by 15% by 2015,
and restore water clarity to a minimum of 2 meters depth by 2020.
Objective 1.3
Reduce sediment input into Compass Point Pond by _TBD % by 2015, increase resilience to climate
change, and restore balance in hydrology by 2020.
Threat: Climate Change:
sea surface temperature
sea level rise, precipitation,
Targets: Salt Pond, Corals, Seagrass, Mangroves, Fishery
Resources, Birds
Objective 2.1
By 2020, create a Climate Change Adaptation Strategy Plan for Salt Ponds, Corals, Seagrasses,
Mangroves, Birds, and Fisheries Resources for STEER.
Wrre
Threat: Coastal habitat
removal/expansion,
loss from direct habitat
Targets: Salt Pond, Seagrass, Fisheries resources, Mangroves
marine expansion, dredging.
Objective 3.1
Reduce loss of marine and adjacent shoreline habitat due to development and boat damage by 90%
by 2015.
4. UNSUSTAINABLE OR ILLEGAL FISH HARVEST
Threat: Illegal harvest inside STEER
I Targets: fish (illegal fishing), coral (loss of herbivores)
Objective 4.1
I To reduce all un-permitted take (fish, whelk, conch, lobster) in STEER waters by 2015.
Threat: Loss of he bivores
I Targets: fish (illegal fishing), coral (loss of herbivores)
Objective 4.2
To reduce overall herbivore fishing in the territory to maintain healthy populations of herbivorous
fishes inside protected areas by 2015.
S. PREDATORS OF SEA AND SHORE BIRDS
Threat: Predation on Birds
I Targets: Birds
Objective 5.1
6. INCOMPATIBLE
To reduce impact of predators (cats, rats and mongooses) on bird population during the breeding
season on Cas Cay by 50%, by Bovoni Cay by 50%, and Great St. lames by _TBD 96 by 2015
USE ISSUES
Threat: Lack of Public Access
Targets: User groups
Objective 6.1
Improve the access of shoreline re ources to the general public from _TBDJI entry points to _TBD II
of entry points by 2015 in a manner that is protective of existing coastal habitat.
Threat: Limited transparency with OPNR
I Targets: User Groups
Objective 6.2
By increasing public participation in decisions made by DPNR, public satisfaction of local
governance increases by 50% by 2015.
7. TRASH AND DEBRIS
Threat: Monofilament on bird health
I Targets: Birds, (secondarily Coral)
Objective 7.1
By 2015, reduce the incidence of entanglement by monofilament of susceptible bird aggregations
(nesting, brooding, feeding colonies) within STEER by _TBD_%, and eliminate monofilament found
entangled on corals and mangroves.
Threat: Solid waste
and vicinity
entering Compass Point Pond
Targets: Birds, Coral, Salt Pond
EFTA01119684
Objective 7.2
By 2015, eliminate solid waste in and in a perimeter of 100 meters of the Compass Point Salt Pond
by 100% on an annual, regular basis.
Threat: derelict vessels and large marine
debris.
Targets: Birds, Coral, Seagrass, Mangroves
Objective 7.3
By 2010, and every year thereafte derelict vessels and large marine debris which threaten
mangroves, seagrass beds, or cora habitat have been removed from STEER.
8. PHYSICAL DAMAGE FROM BOATS
Threat: Anchor D mage
Targets: Seagrass, Corals
Objective 8.1
Reduce the number of boats anchoring on coral and seagrass by 90% by 2015.
Threat: Accidental Groundings
I Targets: Seagrass, Corals
Objective 8.2
I Reduce the incidence of accidental groundings within STEER by 50% by 2015.
9. MARINE-BASED SOURCES OF POLLUTION
Threat: Vessel Sewage (nutrients and bacteria)
Targets: Coral, Seagrass, Fisheries Resources
Objective 9.1
Reduce the amount of pump-out (blackwater and graywater) pumped into STEER by 90% by 2015.
Objective 9.2
Reduce the input of point (illicit discharge) and non-point sources of pollution (level TBD; see below)
from marinas and boats by 2015 to improve the health of seagrass communities and the function of
nursery habitats.
Threat: Hydrocarbons from passing boats
I Targets: Fisheries Resources
a
Objective 9.3
To reduce hydrocarbons, noise, wake from larger commercial vessel by _TBD % by 2020.
10. CAPACITY/IMPLEMENTATION
Capacity / Implementation: Governance of STEER
Objective 10.1
By December, 2015, STEER is designated as a Park as part of the Territory Marine Park System.
Objective 10.2
Establish STEER Advisory Board by December 2011.
Objective 10.3
STEER Management Plan Adopted by Fall, 2011.
Objective 10.4
Develop staffing capacity for STEER
Objective 10.5
Create "Friends of STEER" non-profit organization and merge with "Friends of Christmas Cove" by
2011.
Capacity / Implementation: Enforcement
Objective 10.6
Increase the knowledge, presence and effectiveness of patrolling, surveying and enforcing
personnel in STEER by 2015 and thereby reduce the number of illegal or incompatible activities in
and adjacent to STEEER by 50%.
11. EDUCAITON AND OUTREACH PROGRAM
Education and Outreach Program
Objective 11.1
By 2011, an Education and Outreach program is established with dedicated personnel and funding
to meet the needs of STEER education and outreach to match the objectives stated above.
33
EFTA01119685
STEER Management Plan (May 2011)
Table 4. Summary of Strategies for STEER ranked by priority, impact and feasibility
Strategies identified by priority are color coded to identify rank (red= high priority, yellow=medium priority, green= low priority).
Threat
Strategy
1.A: Redesign a comprehensive USVI non-point source (NP) and point-source (PS) pollution permitting"
ed
r
ry and enforcement program
Strategy 1.1.B: Watershed and Stormwater Management: Partner with public and private sector to reduce NP
Coastal habitat
Strategy 3.1.B: Develop more stringent regulations for shoreline and insular development
loss
Strategy 3.1.A: Regulate development in STEER and nearby habitats
Strategy 4.1.A: Enforce existing regulations in STEER waters
Illegal harvest-
fish
Lack of public
access
Strategy 6.1.B: Zone Use Plan: Recreational and Commercial
Monofilament-
Strategy 7.1.C: Establish bird entanglement response network
bird
Strategy 7.1.B: Community outreach
Anchor Damage
Strategy 8.1.A: Create buoy mooring system in popular boating areas containing coral and seagrass habitat within STEER
Accidental
Devise groundings team network for rapid response
itroundinos
Impaired
watershed
Strategy 1.2.B: Improve water circulation/flow within Inner Mangrove Lagoon
Strategy 1.2.A: Determine the contaminants in the lagoon
Strategy 3.1.C: Research priority: collect baseline data: coral coverage, seagrass, mangroves, shoreline habitat
Coastal habitat
loss
Strategy 3.1.D: Reduce habitat loss on Great St. James due to development
Strategy 5.1.A: Develop shoreline predator trapping program
Predation on
Birds
EFTA01119686
Monofilament-
bird
Strategy 7.1.A: Reduce monofilament
Accidental
groundings
Remove grounded boats (See 7.3: Removal of Derelict Vessels)
Strategy 8.2.A: Groundings prevention, rapid response and removal
Vessel Sewage
Strategy 9.1.A: Establish/ Advocate on-board treatment and/or Pump-Out Program for STEER
Impaired
watershed
Strategy 1.3.A: Restoration of Compass Point Salt Pond
Coastal habitat
loss
Strategy 3.1.E: Reduce loss of mangroves due to coastal development within or adjacent to STEER
Lack of public
access
Strategy 6.1.A: Public Access Program to improve existing public access points and identify new access points
Derelict vessels
Strategy 7.3.A: Develop a derelict vessel reporting and removal system
Solid waste-
Compass Pt.
Salt Pond
Strategy 7.2.A: Develop trash prevention program
Vessel Sewage
Strategy 9.2.A: Promote Blue Flag Program (Clean Marina Program)
Hydrocarbons-
passing vessels
Strategy 9.3.A: Re-route ferry boats, barges through Great/Little St. James
35
EFTA01119687
STEER Management Plan (May 2011)
Table 5. STEER Action Steps
Strategies (listed on left column) are color coded to identify rank from high (red), to yellow (medium), to green (low) priority.
Strategy
Strategic Actions
When
Who
Outputs (mgt plan
implementation)
Measures
Other
Considerations
1. LAND-BASED SOURCES OF POLLUTION
Threat: Impaisasetershed
Targets: Salt Pond, Seagrass, Coral, Birds, Fishery Resources
Objective 1.1
To reduce sediment and nutrient inputs from land-based sources of pollution on the marine environment by 15% by 2015, and
reduce to within acceptable limits (Total Maximum Daily Load) by 2020.
Redesign a
comprehensive US
Non-Point Source a
Point Source pollutio
permitting, regulato
1
Reach out to Division
heads to discuss
watershed issues, shared
concerns, means to
improve watershed
mana ement
2012
STEER, CZM,
DEP, Health,
VIWMA, DEE,
DFW
Engaging regulatory
partners with jurisdiction
within STEER watersheds to
discuss how to improve
permitting
When completed-
Report on actions 1-3
and enforcement
program.
2
Evaluate effectiveness of
permitting, regulation
(more comprehensive,
reduce redundancies,
gaps, inefficiencies)
2012
CZM
Document inefficiencies,
make recommendations
and priorities
When completed-
Report on actions 1-3
MMES Master's project
3
Examine existing laws (fill
resources gaps and rewrite
regulations)
2012
CZM
Foster the revision of local
stormwater regulations to
decrease runoff potential
off of steep slopes
When completed-
Report on actions 1-3
MMES Master's project
4
Engage leadership
(Commissioner, Division
heads)
2010
CZM, STEER
Reallocation of resources to
Ongoing
the gaps
Initial reach completed.
outreach being
conducted.
Improve enforcement (of
regulations)
2015
DEE
1) Fewer violations,
increased compliance
2)Reduction of
contaminants (sediments,
nutrients, contaminants)
When completed
Improved water quality
in degraded areas to
enhance marine
habitat. (Link: Habitat
Loss)
EFTA01119688
Strategy
Strategic Actions
When
Who
Outputs mgt plan
(
implementation)
Measures
Other
Considerations
. . .
Watershed and
Stormwater
Management: Part
with public and
private sector
(marinas, industri
federal agencies) t
reduce non-point
source pollution
sources.
1
Partner with NOAA's Coral
Reef Conservation Program
and the National Centers
for Coastal Ocean Science
to develop a baseline
assessment of chemical
contaminants and
DP
recommendations
for
bioeffects present in
Mangrove Lagoon and
STEER (metals, nutrients,
bacteria, hydrocarbons,
etc.)
2011
NOAA (Tony
Pait), STEER,
Pait),
TNC, DEP
Multi agencies and
community members
engaged. Specific
contaminants and
bioeffects on biota
determined. NP and PS
identified
BMPs. Baseline levels
relative to water quality
standards and published
impacts on target species
(seagrass, invertebrates,
juvenile fish, bait fish)
Final report and
manuscripts on
contaminant levels and
bioeffects in STEER. Will
include a quantification
of sediment
contaminants present,
and the toxicity of those
sediments. Will also
include an assessment of
water soluble
contaminants.
NOAA Contaminants
project approved for
funding (Tony Pait, Ian
Hartwell, Andrew
Mason, Chris Jeffrey,
and Simon Pittman).
2
Create a long-term
sampling and monitoring
protocol that will be
representative of all the
possible land-based
sediment pollution
impacts, must include
parameters like chl-a
2011
As result of
Tony Pait's
project, EPA,
DEP
A cost-effective monitoring
program developed to track
changes in pollutant
concentrations annually to
semi-annually.
Report is created and
used in the Territory
Initially, there may not
be enough capacity for
this monitoring
program which may
require identifying
collaborators and/or
external funding
sources. Identify
sources of
contaminants.
3
Conduct a Watershed
Study: Partner with NOAA
Restoration Center, CWP
to do watershed and gut
assessment; identify areas
where BMPs could be
implemented to reduce
runoff
2011
NOAA Rest
Center,
Center
Watershed
Studies
Recommend BMPs, zoning
scheme, identify programs.
Identify, through studies, a
green zone (area adjacent
that affects the watershed,)
Potential point sources
of pollution identified
from baseline studies.
Define water quality
objectives (the TBD
above) from this
baseline study and
analysis
Can/should we dredge
to offset
sedimentation?
Research sediment
trapping options. Limit
bare dirt in watershed.
Find effective
construction runoff
containment. Analyze
septic systems and soil
percolation tests along
watershed, share
results of inspection,
and retrofit
37
EFTA01119689
STEER Management Plan (May 2011)
Strategy
Strategic Actions
When
Who
Outputs (mgt plan
implementation)
Measures
Other
Considerations
4
Create/change buffer-
legalize "green zone":
a. Work with the
legislature
b. Change STEER
boundaries
2015
STEER
Management
Create limited or defined
use zones around most
susceptible shallow water
seagrass and coral
communities to minimize
additional stressors to these
targets
Jurisdiction on STEER
Management expanded
Watershed
management.
Distribution of boat use
within the Reserves.
Change set back at
water's edge to 150 ft.
Stop marina expansion
in mangrove lagoon
until significant overall
habitat improvement is
made.
5
Enforcement (of
stormwater and point
source discharge,
regulations, green zone)
2015
DEE
Dedicated stormwater
discharge surveillance,
patrol
Annual reports
Inspect/regulate
reverse osmosis
discharge and
determine impact.
Objective 1.2
To reduce the amount of contaminants entering into the Inner Mangrove Lagoon by 1596 by 2015, and restore water darity to
a minimum of 2 meters depth by 2020.
Strategy 1.2.A:
Determine the
contaminants in the
lagoon.
1
See Strategy 1.1.6. Actions
1-3
Monitor if habitat
improves/degrades
Strategy 1.2.6:
Improve water
circulation/flow
within Inner
Mangrove lagoon.
1
Obtain report from Fish
and Wildlife that contains
the history of the second-
false entrance and
historical water exchange
rate
2011
DFW
Determine history of
success, lessons learned
Summary document
DFW (F16- sport fish
restoration) - has been
done before.
2
Write to Army Corps of
Engineers or other federal
agency for potential
funding and execution of
project
2011
U.S. Army
Corp of
Engineers
Initiate funding and
Permitting
When completed
Potential sources of
funding include NOAA,
ASACE
3
Create EIS for opening.
Permit requirements may
require additional studies.
2011
STEER, DFW
Meet requirements for
Permitting
Permits secured
4 Create/list scenarios for
engineering
2011
Consultant
A work plan is developed
Work Plan
Funding in place for a 2
year grant from
EFTA01119690
Strategy
Strategic Actions
When
Who
Outputs (mgt plan
implementation)
Measures
Other
Considerations
USFWS.
5 Look for funding from Fish
and Wildlife
2011
STEER, DFW
Funding in place
Completed. Funding in
place for a 2 year grant
from USFWS.
6 Open up second false
entrance
2012
Engineer
contractor
Water flow into the Lagoon
increases, allowing more
flushing of land-based
sources of pollution
Reduction in amount of
sediments,
contaminants staying in
Lagoon. Ultimately see
a shift back to seagrass.
Consider negative
impacts as well, watch
for erosion
7
Continual monitoring:
Effects on water quality
and habitat loss
2015
STEER, DFW
Monitor habitat and water
quality over time,
specifically in regards to
landfill closure and the new
Waste to Energy Plant.
Keep abreast of pending
development
Determine long-term
sustainability of actions
May increase habitat
for fish
Objective 1.3
Reduce sediment input into Compass Point Pond by _TBD % by 2015, increase resilience to climate change, and restore
balance in hydrology by 2020.
Strategy 1.3.A:
Restoration of
Compass Point Salt
Pond.
1
Determine current
sediment input and
acceptable hydrologic
ratios (salt, fresh,
sediments)
2011
DFW, visiting
researchers
Results indicate that actions
need to be taken
Contact Denise Rennis
who may have data
2
Identify the history of
projects in the area (in the
channel)
2011
DFW
Have history of success,
lessons learned
Summary document
DFW, restoration
grants
3
Determine the current
quality and extent of the
vegetative buffer and
fringe to address impacts
of climate change
2011
NOAA, DEW'
UVI
Study completed
Study completed
4
Restore the hydrology
(dredging, sediment traps,
upstream BMP's, etc.)
2015
NOAA Rest
Center
Compass Point Salt Pond is
functional - will need yearly
data collection
Water flow, sediment
i nput measured
Need to continually
open channel?
Dredge? Until have
hydrology restored
39
EFTA01119691
STEER Management Plan (May 2011)
Strategy
Strategic Actions
When
Who
Outputs (mgt plan
implementation)
Measures
Other
Considerations
i
5
Expand the mangrove
fringe—address climate
change models from
Strategy Plan
2013
STEER
Compass Point Salt Pond in
sustained state of renewal
Buffer expanded to
maximum limits
6
Remove trash, remove
invasive species, replant
wetland vegetation
Annual
STEER, DFW,
UVI,
Volunteers
Community engaged, health
of salt pond maintained
Annual reports
EFTA01119692
Strategy
Strategic Actions
When
_..n
Who
Outputs (mgt plan
implementation)
Measures
Other
Considerations
Threat: Climate Change: sea level rise, precipitation, sea
surface temperature
Targets: Salt Pond, Corals, Seagrass, Mangroves, Fishery Resources, Birds
Objective 2.1
By 2020, create a Climate Change Adaptation Strategy Plan for Salt Ponds, Corals, Seagrasses, Mangroves, Birds, and Fisheries
Resources for STEER.
Strategy 2.1: Create a
Climate Change
Adaptation Strategy
Plan.
1
Establish historical sea-
level rise, historical
shoreline erosion and
change in STEER
2011
NOAA, USGS,
NASA, TNC,
UVI
Baseline information
Report available to
researchers
UVI Master's?
Funding? NOAA's
mangrove project?
2
Conduct a resilience
survey- corals, seagrass,
mangroves
2015
NOAA Coral
Watch or
IUCN, UVI,
CZM
Resilience of coral reefs,
seagrasses, mangroves in
STEER assessed
Report presented to
managers
Funding + team of coral
and fish experts
3
Model threats- develop
spatial vulnerability and
spatial risk models and
scenarios SLR + storm
surge, precipitation and
land inputs, sea surface
temperature
2015 INC,
What
Contractor
These models will answer
the following questions:
areas are going to be
impacted? What features
are going to be impacted
and to what extent?
Scenarios Visualization
Tools- web based, maps,
report; Tools presented
to leaders, used by
advisors
MacArthur Foundation
(funding). Consider
Jersey Bay barrier
islands to mitigate
storm surge damage,
enhance fish habitats,
and protect corals and
seagrasses.
Incidentally would
protect inner mangrove
lagoon from vessels
seeking shelter further
in.
4 Conduct a vulnerability
and cost assessment
2015 INC,
Prioritization
Contractor
of vulnerable
coastal sites to SLR, precip,
temp
Study
probability surfaces
that capture refugia,
SLR, gradients and
buffering existing parks
to improve resilience
41
EFTA01119693
STEER Management Plan (May 2011)
5
Prepare recommendations
and priorities for report;
Identify CC Adaption
Measures that can be
considered a full list based
on research and survey of
climate change experts
2015
TNC,
Contractor
Possible CC adaption
measures researched,
reviewed in the literature,
surveyed
Climate Adaptation Plan:
List of potential
adaptation measures
with "no regrets",
"justified", and
"reactionary vs.
anticipatory"
6 Identify funding for
priority projects
2011
STEER, INC
Evaluate and select CC
adaption actions based on a
robust evaluation using
both science and
socioeconomic indicators
Climate Adaptation Plan:
Funding Action Plan
MacArthur Foundation
(funding)
7 Establish the need and
educate audience
2015
TNC,
Contractor
After visualizing, modeling
and describing the threat,
then the public and
government understand the
importance of
implementing CC adaption
actions.
Workshop, leaders
informed
8
Influence/recommend
policy - national
adaptation - PA Systems
2012
STEER, TNC
Advocate roll-up from
national scale to
international platform-
encourage for funding,
international policy. TNC
support will be through
capacity building and
technology transfer.
USVI Leaders attend
global Climate Change
Forums, advocate for
protection of islands
resources
EFTA01119694
Strategy
Strategic Actions
When
Who
Outputs (mgt plan
implementation)
Measures
Other
Considerations
Threat: Coastal habitat loss from direct habitat
removal/expansion, marine expansion, dredging.
Targets: Salt Pond, Seagrass, Fisheries resources, Mangroves
Objective 3.1
Reduce loss of marine and adjacent shoreline habitat due to development and boat damage by 90% by 2015.
strategy 5.1A:
l
Regulate
1 Determine current
enforcement capacity
2010
STEER
Identify existing regulations
Summary report
development in STEER
and nearby habitats.
2 Educate existing
enforcement
2012
STEER
enforcement updated on
STEER issues
DEE staff trained
3 Enforce existing
regulations
2009
DEL
Development is compatible
with STEER
Increase in number of
regulations enforced
Ongoing effort
4 Community education
2010
STEER
Local community, residents,
developers informed
Fewer incidents of
infractions
Strategy 3.1.B:
Develop more
stringent regulations
for shoreline and
insular development.
1
Research best practice
guidelines in other
jurisdictions
2011 Rutgers Study
Recommendations made
Report on regulations
2
Amend zoning laws: See
Land-Based Strategy 1.1.B,
Action Step 4
2015
DPNR
DPNR has comprehensive
land water use plan
Land and Water Use
Plan
3 Develop insular smart
growth policies
2020
DPNR
Increase wetland buffer on
permits, BMPs for sediment
reduction, Conservation
easements for habitat
protection, Clustering of
buildings, common
structures, Restrict/control
use of exotic plants, pets
Policies are
implemented
4
Develop regulations
specifically relating to
impact of docks and piers
on marine habitats
2015
DPNR, CIM
Marine protection
Regulations in place
43
EFTA01119695
STEER Management Plan (May 2011)
Strategy 3.1.C:
Research priority:
collect baseline data:
coral coverage,
seagrass, mangroves,
shoreline habitat.
1
Benthic survey/ground-
truth NOAA benthic, GIS
coastline/aerial imagery:
Las Cay, Jersey Bay,
Christmas Cove
2011 NOAA, UVI
a. Map extent seagrass,
mangroves, corals, salt
pond and compare with
historical data. a. Establish
a goal for habitat extent
based on those data
Report
Completed
2 Establishment of
monitoring plan
2011
NOAA, UVI,
STEER, TNC.
Partners
Monitor success: every 5
years repeat surveys,
acquire any new
imagery/LIDAR
Report
Strategy 3.1.D:
Reduce habitat loss
on Great St. James
due to development.
1 Collect baseline data for
St. James
2013
STEER, DFW,
UVI, NOAA
Boa, wetland bird surveys.
Verify extent of wetlands,
mangroves
Wildlife inventory,
report
2
Engage Great St. James
developers and
landowners to minimize
habitat loss
March,
2010
STEER, Dr'NR
Greater buy-in from local
landowners and developers
Summary report
any changes to
regulation to cays has
high likelihood- DFW
request to limit
development
3
Influence key decision
makers regarding offshore
Gays
2011 STEER,
Stakeholders
Amend zoning laws for
stricter guidelines for
offshore cays
Action taken by decision
makers
Urge CZM, Planning to
not allow rezoning,
sub-dividing parcels, or
variances
4 SEE 3.1.A, 3.1.B
Strategy 3.1.E: Reduce
loss of mangroves due
to coastal
development within
or adjacent to STEER.
1
Control/enforce pruning or
trimming of mangroves
around marinas, docks
2010
STEER, DEW
Signage, presence of DEE,
community buy-in
Lower incidence of
mangrove loss
Bump up Enforcement
2
Enforce no net loss of
wetlands policy
2012
DEE
Wetlands given higher
conservation consideration
Incidence of infractions
lower
EFTA01119696
1 1_, T1:911r07;311H-f 7.371;rri"
sir
Strategy
Strategic Actions
When
Who
Outputs (mgt plan
implementation)
Measures
Other
Considerations
Threat: Illegal harvest inside STEER
Targets: fish ('llegal fishing), coral (loss of herbivores)
Objective 4.1
To reduce all un-permitted take (fish, whelk, conch, obster) in STEER waters by 2015.
Enforce ex
ng
regulations in ST
waters.
Determine current level of
harvesting (legal and
illegal)
2012
DFW, MMES
grad, TNC Vol
Which groups are involved
in fishing: commercial vs.
subsistence? Which species
are being fished? Are bait
fish stocks decreasing?
Report
Funding, need to take a
tactful approach to
documenting illegal
activities. DEE issues
permits.
Publicize existing
regulations through
workshops, brochures,
PSA's
2010
STEER, C2M,
DFW, Sea
Grant, TNC
STEER users are more
informed
Pre-post attitude
surveys
Signs already exist-
need more signs?
3
4
Determine current
enforcement capabilities
2010
STEER, DEE
Assessment and
recommendations
Formal statement of the
enforcement capacity to
take to policy makers
Endorsement from
DPNR Commissioner,
no funding required
Educate current
enforcement officers
2009 '
yearly
STEER, DFW,
CZM, DEP,
DEE
Enforcement officers
trained in STEER fishery
(and other) issues
Pre-post knowledge
surveys
NOAA/NMFS? USFWS
(Mike Evans) needs to
be frequent (6 mo.)
Additional Indicator:
Increased enforcement
activity: ft stations,
patrolling hours
5
Determine feasibility of
eliminating all take
2013
STEER, DFW
Assessment and
recommendations
Report on
recommendations
Discussion occurs once
enforcement is
effective, STEER Mgt
Entity is in place, etc.
Strategy 4.1.8:
Designate STEER
waters a no take zone
by 2020 (eliminate
bait fishing and hand
lining).
1
Educate community on
benefits of no take areas
2
Work with senators to
create legislation
Eliminate bait fishing,
Eliminate hand lining
Threat: Loss of herbivores
Targets: fish (illegal fishing), coral (loss of herbivores)
Objective 4.2
To reduce overall herbivore fishing in the territory to maintain healthy populations of herbivorous fishes inside protected areas
by _TBD_% by 2015.
45
EFTA01119697
STEER Management Plan (May 2011)
S. PREDATORS OF SEA AND SHORE BIRDS
Strategy
Strategic Actions
When
Who
Outputs (mgt plan
implementation)
Measures
Other
Considerations
Threat: Predar
s
Targets: Birds
Objective 5.1
To reduce impact of predators (cats, rats and mongooses) on bird population during the breeding season on Cas Cay by 50%, by
Bovoni Cay by 50%, and Great St. James by _TBD % by 2015
Strategy 5.1: Develop
shoreline predator
trapping program.
1
Determine baseline
predator population and
sources (boats, dump,
etc.) & bird vulnerability
assessment
2012
DFW,
Master's
Student, C.C.
Baseline ti of rats, Baseline
breeding range and success
of bird species of concern
Report of predator and
bird study
Does not need to occur
in sequence, need
boat, Precise periods of
vulnerability for certain
birds (breeding period,
nesting location)
2
Develop the Participatory
Program: Training of local
businesses,
of Health Dep't, Waste
Mgt, Funding, Incentives,
outreach
2013
STEER
Engage the community and
involvement
Program,
Need
a
increase community
education
ft of businesses, and
volunteers are setting
traps
Cannot extend program
to marinas, etc. under
Federal funding, thus
support from a
motivation scheme for
businesses. Use
boaters in/adjacent to
STEER to help trap,
educate
3
DFW Program: Initiate
control efforts -tra pping ,
poisons
09
Dec 09
(Cc s)
w
Reduce rats, other
predators on Cays, Cas first
(predator impact on birds
reduced)
# predators trapped
Restricted scope of
funding, trapping will
control but not
eliminate, proximity to
landfill is issue for
total eradication
EFTA01119698
,
TIBLE USE ISSUES
_ _
_,,
Strategy
Strategic Actions
When
Who
Outputs (mgt plan
implementation)
Measures
Other
Considerations
Threat: Lack of Public Access a
u ser groups
Objective 6.1
Improve the access of shoreline resources to the general public from TBD ti entry points to TBD ft of entry points by 2015.
Strategy 6.1.A: Public
Access Program to
improve existing
public access points,
identify new access
points.
Determine current access
points, parking, boat
launch, public information
displays
2009
STEER, am
Completed document with
recommendations. Ensure
that existing habitat is not
adversely impacted by new
entry points.
Document with map
VI Government purchase
coastal easements (CELP)
2015
DPNR- CZM
CZM has management of
significant natural and
cultural coastal areas
Purchase of key STEER
coastal parcels
3
Renovate and restore
public access ramps to the
sea and create more.
2012
DPNR- DFW
Public has better access to
the resources of STEER
XX of boat ramps, other
access points improved
DFW, boat ramp
money
Strategy 6.1.B: Zone
Use Plan:
Recreational an.
Commerc
Develop map with
stakeholders
2009
STEER, am
A map that stakeholders
agree upon sets out clear
use areas that reduces
conflict and established
equality in use of resources
Map with accompanying
plan
There are already
zones as defined by
STXEEMP Act
(Territory's Marine
Protected Areas).
2
2012
Limit Use to carrying
capacity
DPNR,
STEER, DEE
Resources protected,
aesthetics maintained
Reports on average ft
people using resource
(Cas Cay, X-Mas Cove)
Need carrying capacity
study. Assumption:
people comply
Education (i.e. snorkel
awareness)
2012
STEER, CM
Public practices
conservation while in STEER
X of people reached
i.e. snorkel awareness
education
Threat: Limited transparency with DPNR
Targets: Use groups
Objective 6.2
By increasing public participation in decisions made by DPNR, public satisfaction of local governance increases by 50% by 2015.
Strategy 6.2:
Permitting, moorings, boat
registration computerized
DL L
Ease in getting permits
4/
EFTA01119699
STEER Management Plan (May 2011)
7. TRASH AND DEBRIS
Strategy
Strategic Actions
When
Who
Outputs (mgt plan
implementation)
Measures
Other
Considerations
•
.
: I
i
.F1 .:
I
Targets: Birds, (secondarily Coral)
Objective 7.1
By 2015, reduce the incidence of entanglement by monofilament of susceptible bird aggregations (nesting, brooding, feeding
colonies) and other wildlife within STEER by _TBD %, and eliminate monofilament found entangled on corals and other
habitat.
Strategy 7.1.A:
Reduce
monofilament.
Determine amount and
distribution of
monofilament, etc. (such
as polypropylene float
lines and netting) found
in the shoreline habitats
and STEER in conjunction
with clean-up
2013
Volunteers,
Sea Grant,
UM, DFW,
STEER, INC,
removal
UVI (MMES)
Map of density of
monofilament, etc.,
of
Current level of
entanglement of birds in
STEER, Nibs removed
Certain bird species or
behaviors making them
more susceptible to
entanglement in STEER.
2
In-water research
(general) Permit
conditions made to also
document monofilament
and debris
2013
DFW, CZM
(coral
collecting)
Increased
information/documentation
of the presence and
location of threats (lionfish,
debris, bleaching,
monofilament)
Reporting system in
place and information
made available to STEER
Contact DFW permits:
inform of the changes
Mapping of the most
popular access points for
hook and line fishing as
source of monofilament
2013
CZM,
stakeholder
input, DFW,
MMES grad,
TNC Vol
See fishing impact study
Study
As part of 4.1 Fishing
Assessment
4
Receptacles for
discarded/unwanted
monofilament
2011
VIWMA,
DFW
(Aquatic
Education)
Increased proper discarding
of monofilament etc.
#lbs in trash receptacles
Follow up: pick up of
trash (VIWMA,
Volunteers, Reef
Rangers)
48
EFTA01119700
Strategy 7.1.6:
Community outreac
Provide information to
shore fishermen, sport
fishing (commercial,
charter, recreational),
boaters about the
dangers of monofilament
to bird populations and
provide alternatives and
a reporting system,
alternatives to avoid this
threat.
2009
DFW
Identifying the shore,
commercial, recreational
and charter fishermen.
Pre and post surveys to
determine how
informed and involved
fishermen are.
Ongoing.
Strategy 7.1.C:
Establish bird
entanglement
response network.
Identify and train
personnel in proper
disentanglement of birds
Oct-10
Volunteers,
DFW,
Humane
Soc,
Rehabers FL,
Coral World
-Fishing outside the
Reserves:
P of people trained
Was done for STJ.
Follow up with
Humane Soc- rehab
center: sites, logistics.
FUNDING: other
sources than Feds
2
Establish response
system
ongoing
Volunteers,
DFW,
Humane
Soc,
Rehabers FL,
Coral World
commercial red, mu b t
fishing
bird rehab to include
entanglement
3
Monitor shoreline and
marine areas for
entangled birds
Volunteers,
DFW,
Humane
Soc ,
activity
Rehabers FL,
Coral World
charter recreational sport
fishing NOAA Restoration
Center
at same time as
1 above
49
EFTA01119701
STEER Management Plan (May 2011)
Threat: Solid
nd and vicinity Targets: Birdsaal, Salt Pond
Objective 7.2
By 2015, eliminate solid waste in and in a perimeter of 100 meters of the Compass Point Salt Pond by 100% on an annual,
regular basis.
Strategy 7.2.A:
Develop trash
prevention program.
Identify source of trash
2012
viWMA,
STEER
Collection of VIWMA dots,
understanding of source of
trash, reduce trash
Obtain VIWMA
documentation, target
sources
Ed/outreach. need
additional resources.
clean ups are possible
2
2012
Engage VIWMA,
Community associations,
Compass Point Marina
for prevention
STEER
More compliance, less
trash
before and after # lbs
trash
Determine existing
regulations and
management agency
that is responsible.
Need dumpsters along
Compass Point Pond
Road, from Good Luck
Grocery to Red Hook.
Improve regulation/
enforcement for local
business,
Secure support and
funding for twice-annual
trash clean-ups
(minimum)
March and
Sept,
Schools,
annual
Volunteers,
Community
Service
Dedicated program to pick-
up trash
# of people u .(olved, #
lbs trash
VIWMA- summer kids
program (YES), East
End beautification
program. Check with
Sea Grant Outreach
Coordinator. Have
private enterprises pay
for garbage collection.
Provide trash and
recycling deposits, a pick-
up system, follow up of
pick up
2011
STEER,
VIWMA
Deposited trash is removed
No overflowing trash
receptacles
Limited space
available. Go door-to-
door along Compass
Pt. Road
5
Community education
including informational
signs.
2012
STEER, CZM,
DFW, Sea
Grant, TNC
Informed community
Compliance (visual
surveys # of incidents of
throwing trash pre and
post)
Include in overall Ed
and Outreach. Engage
school groups, local
businesses,
landowners, and
boaters
50
EFTA01119702
Threat: derel
By 2010, and every year thereafter,
habitat have been removed
derelict
Targets:
, Coral, Seagrass, Mangroves
Objective 7.3
vessels and large marine debris which threaten mangroves, seagrass beds, or coral
m STEER.
Strategy 7.3.A:
Develop a derelict
vessel reporting and
removal system.
1
Provide reporting system
for the documentation of
derelict vessels
2011
STEER,
Contractor,
DEE, DFW,
CZM
Derelict vessels reported
Central reporting
system in place, is being
used
Need to know if
operable: what is the
call tree? DEE, Coast
Guard (notified)
2
Secure funding for
regular marine debris
removal as necessary
2013
Sea Grant,
Gov's Office,
NOAA, Sea
Tow
(through
NOAA
grant)?
funding, rapid response to
remove threat
ii of SS available
Coast Guard funding?
Sometimes DEE has
funding. NOAA? Gulf
Mex Foundation?
3
3
Remove existing derelicts
ongoing
DPNR, Sea
Tow
Reduction of incidence of
derelict vessels
tt of derelict vessels
removed vs. remaining
Need to be careful
about removal
damage- Depends on
mechanism, payment,
priority on case-by-
case
Provide training to DEL
2009
DEE
completed
NOAA FL
training
DEE trained, applied
methods to removal
DEE remove x
derelict /year
DEE follows paper trail,
determine owner, put
up for auction.
4
Determine before-
impacts and after-
benefits.
as needed
STEER, DEE,
DFW, UVI,
CZM, TNC
Measure impact of threat
and effectiveness of
removal
Documentation of
improvement of
resources
need long-term
monitoring to gauge
slow recovery
51
EFTA01119703
STEER Management Plan (May 2011)
8. PHYSICAL DAMAGE FROM BOATS
Strategy
Strategic Actions
When
Who
Outputs (mgt plan
implementation)
Measures
Other
Considerations
Threat: Anchor Damage
Targets: Seagrass, Corals
Objective 8.1
Reduce the number of boats anchoring on coral and seagrass by 90% by 2015.
to
buoy moon
tern
8.1.A:
tern in popular
boating areas
containing coral an ,
seagrass habitat
1
Conduct survey of boat
use patterns and coral
and seagrass affected by
anchoring
2010
DFW, STEER
Monitoring of high use
areas to look for further
damage, Determine
priority sites for mooring
buoys
Report
Carrying capacity of
boaters in area, Extent
of coral damaged,
Post-removal effects
on seagrass at Cas
(from Oct '08)
within STEER.
2
3
Development of
Moorings Plan or
Recommendations/
Policies
2009
STEER, DEE
Better policies for
protection of seagrass and
coral
If changes
recommended,
legislative approval,
then the Plan is in place
Keep separate from
STEER MP. System for
determining use of
moorings, collecting
fees. Need to consider
repercussions from
stakeholders.
Reporting means and
penalties for
infractions? (EX.
Lovango: lsq ft. coral =
$250 (?))
Development of
Moorings Plan:
Placement
2010
STEER, DEE,
Stakeholders
Identified placement for
future buoy installation
Plan
95% of plan will be
accepted, except for
Cas Cay- will depend
on what policies
change? Information
from baseline survey
will contribute.
4
Buoy installation
2009
NW, CZM
Mooring (and boundary)
buoys in place, enhanced
mooring capacity
X # of buoys installed
Buoys installed in
Christmas Cove.
Bovoni Cay Hurricane
Mooring System
installed
52
EFTA01119704
5
Public outreach
regarding proper use of
moorings, guidelines,
etc.
2010
DFW, Sea
Grant, CZM,
TNC
Buoys used, less anchoring
X It of buoys used vs.
anchoring on
seagrass/coral
Public awareness
6
Semi-annual
maintenance of moorings
continuous
DFW,
Contractor
Continuous maintenance
Maintenance log: #'s of
buoys checked, needing
repair, repairs occurring
Funding
Monitoring of activities
and coral in affected
areas post buoy
installation
continuous
DFW, UVI,
TNC,
Volunteers,
DEP
Effectiveness measures
Incidence of coral,
seagrass damaged
Continuous
monitoring, DEP RARE
funding
8
Engage "Host Boar in
spreading message,
reporting on compliance
STEER
Bay host system
established. Increased
enforcement, outreach
# of boat owners
reached
Following formation of
STEER Mgt Committee.
Keeps records, collects
fees if any, work with
enforcement
Threat: Accidental Groundings
Targets: Seagrass, Corals
W
Objective 8.2
Reduce the incidence of accidental groundings within STEER by 50% by 2015.
Strategy 8.2.A:
Groundings
prevention, rapid
response and
removal.
1
2
Prevent groundings with
installation of
navigational buoys
and/or daymark system
on pilings for channel
2012
DFW,
Contractor,
CZM
Mooring (and boundary)
X It of buoys installed
buoys in place
Coast Guard inspection
required
Devise groundings team
network for rapid
response
2011
DPNR
Groundings
Team
Team response is
immediate
Response time
Clear identification of
call tree, including CG
in case of hazmat, VI
Reef Resilience Plan
3
Remove grounded boats
(See 7.3: Removal of
Derelict Vessels)
ASAP
DPNR
Groundings
Team, CZM,
DFW,
contractor
Threat removed quickly
with least amount of
damage
ft
a
of days grounded,
assessment of damages
Restoration of
damaged corals. Need
tobe careful about
removal damage-
DEPENDS on
mechanism, payment,
priority on case-by-
case.
53
EFTA01119705
STEER Management Plan (May 2011)
9. MARINE-BASED POLLUTION
Strategy
Strategic Actions
When
Who
Outputs (mgt plan
implementation)
Measures
Other
Considerations
Vesse
e (nutrients and bacteria)
Targets: Coral, Seagrass, Fisheries Resources
Objective 9.1
Reduce the amount of pump-out tblackwater and graywater) pumped into STEER by 90% by 2015.
Strategy 9.1.A:
Establish/ Advocate
on-board treatment
and/or Pump-Out
Program for STEER.
1
Assess existing pump-out
facilities, boats with on-
board treatment, transfer
options to understand
needs
2011 CZM, UVI
Existing pump out facilities
within STEER identified
(capacity and potential
need, determined by
number of boats)
Pump-out at Compass
Pt.
Understanding of why
boaters do not use
existing pump out
facilities. Disposal of
pump-out is an issue.
2
Develop incentives for
boats to get composters
or MSD (III).
2011
STEER,
DPNR, CZM
UVI
Boaters are compliant
report # of boats being
registered with on-board
tanks
3
Determine alternatives
for facilities, assess costs,
funding?
2011
STEER,
DPNR, CZM
UVI
Funding identified for pump
out business
Funding sought
Find funding/partners
for additional pump-
out facilities. EPA
Beach Grant: funding
for pump out vessel?
4 Establish additional
pump-out facilities
2020
STEER,
DPNR, CZM
UVI
an appropriate number of
pump-out stations to
accommodate the quantity
and spatial distribution of
boaters in STEER
Additional pump-out
in/near STEER
STEER as non-profit to
provide funding for
mobile and land-based
pump outs with fixed
sizes and rates
5
Discuss with enforcement
the establishment of
regulations regarding
vessel registration with
proof of receipts and
functional holding tanks,
and alternatives to
holding tanks- including
composting, incinerating
2012
STEER,
DPNR, CZM
UVI
Enforcement with
education
Pamphlet given at
registration with
locations listed and
potential fines
Enforcement will link
future boat
registration (Aug '10)
with on-board- STEER
can do- grant
submission thru DFW?
Mandate pump out
facilities (full time
access) to any marina
EFTA01119706
or other non-discharge
systems( all considered
Type3 MSDs), as well as
treated discharge systems
(Types 1 & 2 MSDs)
with more than xfl of
slips or XII of sq. ft. of
submerged lands.
Clearly state whether
treated discharge is
permitted.
6
Keep records of use to
gauge effectiveness
(increase in pump-out
facility use = decrease in
illegal pump-out?)
2012
STEER,
pump-out
facility
owner
Record kept
Records
7
Incorporate incentives for
marinas to have pump
out facility for public, as
part of Clean Marina
Program
2012
STEER,
DPNR, CZM
UVI
Businesses buy-in to
program
Marinas have pump-out
facilities
Private funding? Post
reasonable prices for
pump out and/or
gallons. Encourage
composters or other
non-discharge
treatment.
Objective 9.2
Reduce the input of point (iircit discharge) and non-point sources of pollution by _TBD% from marinas and boats by 2015 to
improve the health of seagross communities and the function of nursery habitats.
Strategy 9.2.A:
Promote Blue Flag
Program and Clean
Marina Program.
1
Adopt Clean Marina
Program Plans to STEER
2015
NOAA
(financial
incentive
program),
EPA (CWA),
Plan outlines ways marinas
are involved in the
protection of the
environment
a of marinas
participating
Understand that Clean
Marina Program
already required
(federal). Oppose
further marina
expansion
2
Assess the threat and
issues arising from
marinas in STEER- why
aren't marinas
compliant?
2011 STEER
Information on how to
proceed
Summary report
Why it's working and
what we need to do?
3
Engage marinas and
enforcement
2012
STEER, DEE
Marinas adjacent to STEER
active in VI's CM Program,
have spill response plans
and solutions to issues such
as bilge cleaning facilities.
ft of infractions decrease
and Blue Flag members
increase
Create incentives or
compliance programs
(fly a flag, get a
plaque). Provide
reporting or info chain
55
EFTA01119707
STEER Management Plan (May 2011)
from public to STEER to
law enforcement.
Provide means for
community to assist in
clean-up.
Ensure containment:
filters, treatment, booms,
fuel cups, spill equipment
at docking stations
2015
STEER, DPNR
Speedy response of
enforcement to diesel or oil
slicks, Spills cleaned up.
Summary report
Env sub-committee of
HTA completed Blue
Flag feasibility study.
Blue Flag "National
Jury". Organizations
on board include
DPNR, Megan's, etc.
Marinas in STEER can
join.
Threat: Hydrocarbons from passing boats
Targets: Fisheries Resources
Objective 9.3
To reduce hydrocarbons, noise, wake from larger commercial vessels
Strategy 9.3: Re-route
ferry boats, barges
through Great/Little
St. James-
1
Begin to address ferries,
speed boats, large
tankers and barges. Also
option to limit speed vs.
rerouting
Would fall under
existing regulations?
Need enforcement.
Perhaps a citizen-led
initiative
56
EFTA01119708
10. CAPACITY/IMPLEMENTATION
Strategy
Strategic Actions
When
Who
Outputs (mgt plan
implementation)
Measures
Other
Considerations
Capacity / Implementation: Governance of STEER
Objective 10.1
By December, 2015, STEER is designated as a Pork as part of the Territory Marine Park System.
Strategy 10.1:
Designate as Park
1
Draft justification
document
2015
STEER Core
Draft Justification
Document:
1) Enforcement- need
structure to give
attention to needs of
the area
2) Cultural resource- will
be more accepted as
such
3) As a Park, can
consider making Cas
Cay decent
campground with
controlled visitation
4) Enhance designation
will elevate
importance of
watershed
management
5) Gets departments to
work together ("how
are you going to
contribute to make
this a healthy Park?)
6) Unifies the 3 MRWS's
7) More leverage
document ready
2
Discuss with CZM
Director
2015
CZM
Director comments,
approves
ready for commissioner
3
CZM to Commissioner
2015
CZM
Commissioner approves
57
EFTA01119709
STEER Management Plan (May 2011)
Director
4
CZM takes to CZM
Commission
2015
Commission
er
5
Governor Approval
Before
election
s
CZM-
through
DPNR
process
Park established
Capacity/ Implementation: Governance of STEER
Objective 10.2
Establish STEER Advisory Board by July, 2011.
Strategy 10.2:
Establish interim
STEER management
group.
1
Establish STEER
management group (such
as Friends of STEER?)
2011
Raise funds
for STEER
staff
Board? Such as
Magen's Bay MA?
Friends of STEER?
2
Meet Quarterly,
Monthly?
2011
Use of
Advisory
Board/
Committee
3
Develop a business plan
for the agency
2012
Capacity / Implementation: Governance of STEER
Objective 10.3
STEER Management Plan Adopted by Fall, 2011.
Strategy 10.3:
Management Plan
through Government
House.
1
Finish draft
Sept
2010
Completed
2
Public Input
Oct
2010
Completed
3
Submit to CZM
Commission
2011
CZM signs off on Mgt
Plan
Capacity / Implementation: Governance of STEER
Objective 10.4
Develop staffing capacity for STEER
Strategy 10.4:
Staffing.
1
Coordinator hired for
Territorial Park System
2011
STEER Coordinator hired by
TNC.
Completed.
Overall coordinator for
the Territory's Parks
(STXEEMP, STEER)
OR: Coordinator for
EFTA01119710
b LL !
2 Rangers (4)
Rangers/surveillance
staff:
IDEAL: up to 4
($200,000)
Need to get
enforcement training
(CZM staff- can issue
cease and desist
orders)
3 Education /Outreach
Specialist
delved out to CZM
Outreach Eventually have a
Full Time Employee (FTE)
Build 20% into CZM
outreach position?
Could possibly
coordinate with VINE to
make STEER outreach a
special project of theirs
until FTE is hired
4
STEER Marine Biologist
Eventually have a FTE on
this- funding from
5
Bayhosts
Capacity / Implementation: Governance of STEER
II6
a
Objective 10.5
Create "Friends of STEER" non-profit organization and merge with "Friends of Christmas Cove" by 2011
Strategy 10.5: Create
"Friends of STEER".
1
Identify mechanism for
Friends of STEER
2011
2
Engage public
2011
3
Develop a charter for
Friends of STEER
2011
Made up of a civilian
review board?
Capacity / Implementation: Enforcement
) I I
I
Increase the knowledge, presence and effectiveness of patrolling, surveying and enforcing personnel in STEER by 2015 and
thereby reduce the number of illegal or incompatible activities in and adjacent to STEEER by 50%.
59
EFTA01119711
STEER Management Plan (May 2011)
Strategy 10.6:
Increase enforcement
program in STEER.
1
Raise funds for STEER
rangers
2
Get funding for
enforcement
infrastructure (dock,
boat, office, vehicles, dive
gear)
Raise funds for STEER patrol
boat's
Already is a dedicated
slip at Compass Pt.
Marina
3 Establish effective patrol
practices
Educated on STEER
regulations, issues
Create a list of
infractions/threats-
illegal activity —database
used as an indicator for
measuring education
and outreach efforts or
effectiveness of the park
in general, see below
Add or enhance citizen
enforcement role.
4
Establish STEER
enforcement plan
Study STEER infractions
Identify priority for
enforcement
ID what rangers can do,
what Bayhosts can do, rest
to DEE
5
Have at least (1)
dedicated enforcement
officer for STEER
Can build dedicated
FTE into grants for DEE,
then officers work with
Rangers
(STXEEMP did fund 2 34
time officers)
60
EFTA01119712
11.
0
•
•
•
9 •
'
•
"•G'•M
Strategic Actions
Strategy
When
Who
Outputs (mgt plan
i mplementation)
Measures
Other Considerations
Education and Outreach Program
)bjective 11.1
By 2011, an Education and Outreach program is established with dedicated personnel and funding to meet the needs of STEER
education and outreach to match the objectives stated above.
Strategy 11.1:
Increase
stakeholder
awareness (give
change their
behavior). Target
residents and
tourists (boat
rentals, charter
yacht.
Pamphlets on moorings
and anchoring zones
(where they are, why they
people
a chance
to
1 Jun
-10
DFW
need to be used,
regulations, how to
anchor properly, etc.)
Public informed of critical
habitat, ways to protect
resources , mooring
program, rules and regs
Pamphlets distributed
to boaters, public.
COMPLETED.
DFW is doing this as part
of grant- may limit the
amount or rules/regs
that can be included.
Recommendation to
require boaters
docked/moored in
STEER to read signs and
materials
2
Other outreach: STEER
website; don't step on
corals; reduce use of
oxybenzone containing
sunscreens when in water
near corals, video, radio
2012
STEEER
Heightened sense of
awareness by public of
STEER, increased access to
STEER information.
STEER media materials
Dependent on STEER
staff? Funding? Target
outreach to tourists-
inform of usage zones,
buoys, use of kayak or
sailboats, damage of
corals from walking or
groundings
3
STEER logo competition
2011 STEER
Engage local school groups,
Logo
raise awareness of STEER
determined
4 Create Volunteer
Monitoring Program
2011 STEER
Community Outreach
Volunteer network
established
Part of Friends of
STEER?
5
Develop Education and
Outreach Strategic Plan
2011 STEER, i N.0
Strategic plan outlining
Ed/Outreach needs,
funding, schedule, etc.
Plan in place
Need to reach youth.
6
7
Signage in shore side and
in watershed
In heavy use areas to
help control/direct
traffic
Adopt a Road program
Beautification
Engage Boy Scouts
61
EFTA01119713
STEER Management Plan (May 2011)
2.7 Monitoring and Evaluation of Effectiveness
A Monitoring Plan was developed to assess the status of the resources STEER aims to protect
and to evaluate the effectiveness of some of the strategies proposed in this Management Plan.
This involved deciding how STEER management will measure results. Having a plan for
monitoring will enable managers to see whether a strategy is working as planned and thus
whether adjustments will be needed. It also helps keep an eye on those targets or threats we
are not acting on at the moment, but may need to consider in the future. This Plan needs to be
constantly reviewed, updated, and likely amended to reflect new needs or other information
that can feed into management decisions. Periodic updates will be necessary as cost estimates,
funding, and results are determined.
The Plan contains essential elements needed to track the resources and strategies; indicators,
methods, frequency and timing, and costs (among others). These are tied back to the
Objectives and Strategies of the Plan (see section 2.6 Conservation Objectives Strategies and
Action Steps).
Indicators can be quantitative measures or qualitative observations. Good indicators meet the
following criteria:
• Measurable: Able to be recorded and analyzed in quantitative or in discreet qualitative
terms.
• Clear: Presented or described in such a way that its meaning will be the same to all people.
• Sensitive: Changing proportionately in response to actual changes in the condition or item
being measured.
Methods are specific techniques used to collect data to measure an indicator. Good methods
meet the following criteria:
• Accurate: Gives minimal or no error.
• Reliable: Results obtained using the method are consistently repeatable.
• Cost-Effective: Not overly expensive for the data the method yields or for the resources
available to the project.
• Feasible: Project team has people who can use the method, as well as the material and
financial resources to use the method.
• Appropriate: Appropriate to the environmental, cultural, and political context of the
project.
Table 6. STEER Monitoring Plan, shows monitoring needs as listed in order of importance. The
status assessment for each of the seven STEER Targets is listed first (in blue boxes), and then
other monitoring for strategy or program effectiveness follows. When using the plan, please
62
EFTA01119714
pay particular attention to the priority monitoring needs, the frequency of monitoring, and the
status of this activity. Contact persons are members of the Core Planning Team (Appendix G:
"Core Drafting Team and Stakeholders") or others the Core Planning Team will know how to
contact.
Additionally, Initial Research Needs were determined and recorded in the following table.
Research that is needed may provide baseline data prior to implementation of STEER strategies
or data that will help guide other monitoring methods.
A note on water quality testing: DPNR Division of Environmental Protection has 13 Ambient
Water Quality Monitoring Stations within the various Reserves boundaries. Water is sampled
quarterly and field measurements include pH, salinity, dissolved oxygen, turbidity, temperature,
and any unusual sights or smells. Likewise, samples are tested at Ocean Systems Laboratory,
for fecal coliforms, enterococci bacteria, as well as turbidity. Chlorophyll a was identified as a
measurement of water quality. Combined EPA and VI code ambient water quality standards
indicate that fecal coliform counts over 70µg/L are unsuitable for swimming. STEER waters are
designated as Class B, or suitable for contact recreation. However, the waters have been listed
as "impaired" by the EPA and have some restrictions concerning temporal exposure to humans
after significant storm events.
Testing should focus on the following areas:
• Cas Cay — to get baseline, currently no boats allowed
• Marina — detect any improvement when Pump Out requirements start
• Inner lagoon — baseline for opening of channel, or dump closure, energy plant, etc.
• Christmas Cove — baseline
• Others — salinity at desalinization outfall points
The document listing the sources for Mangrove Lagoon and Benner Bay's Impaired Water Body
Listing can be found at:
http://www.dpnr.gov.vi/dep/pubs/17602-FINAL MLBB TMDL 05 24 05.pdf
For more background information see:
h ttp://www.e pa.gov/wate rscience/sta ndards/wqsli bra ry/te rri tori es/usvi wqs. pdf and
http://dpnr.gov.vi/dep/1-dec-intent.htm
Another thrust of monitoring for effectiveness of the Reserves, in terms of residents' attitudes,
behaviors, perceptions, knowledge, etc. of the Reserves' mission and goals, and of the STEER
environment, prior to and post-installation of STEER. This could be a major duty of the
Education and Outreach staff- coordinating an awareness campaign and evaluating how
humans are/are not changing in relation to this STEER establishment.
63
EFTA01119715
STEER Management Plan (May 2011)
Table 6. STEER Monitoring Plan
STEER MONITORING PLAN (2010-2015)
Target(s)
Threat(s)
Category
Strategy
or
Program
Indicator
Methods
Status
(already
being
done?
Complete
d?)
FE o
0.0
E
—
E
iz:
-O c
ru
41
>..
u
c
G) =
CT
2
Ia.
a
O
ra u
O
_,
Inner
Mangro
ye
Lagoon,
Benner
Bay
2 o
.c
3
vi —
u
8 2
E g
O u
E
O
-c
3
UVI
MMES
(Tyler
Smith),
voluntee
n
c
co
a)
-O ..,
CU
0) o
c c.,
,
0) u
'
iO
to ti
cc
-$500
a,u
5-O
00 ,
'E
LL
C
UVI-
MMES
C
(C
a
4-
.c ,,,
7.
O
--- O
C "O 'Ca
O 2 ro
E cu •ti-
-
"O
O.
a E
ro
rec
g
k a
Last updated summary/
to m
analysis report (date +
(A
citation)
Mangrove
Climate
change
(sea level
rise),
direct
removal
of derelict
boats,
developm
ent
(sediment
), boats
tied up to
roots,
toxins,
trash
Status of
resource
Density,
diameter,
biomass,
spatial
representatio
n
Field
measurem
ents,
tagging
studies of
seedlings,
infrared
mapping.
Permanen
t plots
(randomly
chosen in
Spring
2009)
lx
complete
d MMES
spring
2009.
Next
update in
2011.
Every
other
year
(need to
check
for
plots'
tags
every
year)
MMES
2009
64
EFTA01119716
STEER MONITORING PLAN (2010-2015)
Do
i—
Threat(s)
Category
Strategy
°r
Program
Indicator
Methods
Needs/
Status
(already
being
done?
Complete
d?)
t10
c
E
i=
-0
c
co )-u
c
G) a
a-
?...)
is.
o
r)
m u
o
_,
2
.0
0
3
,,, —
,_ u
lo,
E g
o u
E o
•E
3
C
M13-6
G)
-0 ....
(Li
tn
(I)
0
,
v.
G) u
5'
2
a,u
5
o
u-,
tO
c
'5
C a
u_
C
t13
71- +
oz ;2
_ co
8
-E-•
.... a
E -0 r.,
0 a
E a, r
e
13
2 E
— o
2
a)
0
Last updated summary/
analysis report (date +
citation)
Seagrass
Water
quality,
sediments
tion,
tion,
climate
change
rise),
anchor
damage,
habitat
loss,
trash/deb
ris
resource
Diversity,
shoot density,
distribution,
seagrass:algae
ratio
Field
measurem
ents,
permanen
quadrats
(randomly
chosen),
photo-
CPE,
indicators
of
algae:seag
rass ratio
at certain
locations
(Inner
Mangrove)
1x
complete
d MMES
spring
2009.
Next
update in
2011.
DFW to
conduct
benthic
habitat
survey on
X-Mas
Cove
twice a
year for 3
years.
MMES:
Every
other
year
year in
X-Mas
Cove,
start
June
2010
Selected
perman
ent sites
UVI -
MMES
(Tyler
Smith),
DPNR-
DFW
voluntee
rs
MMES
Students
-$1000.
(SCUBA,
days/pe
ople)
DFW
Survey
Annual
Cost:
-$14,30
0.
(survey,
supplies,
staff
time.)
UVI-
MMES
USFWS
Sport
Fish
Restore
tion
"Steer'
grant
MMES
2009
MMES
2009
65
EFTA01119717
STEER Management Plan (May 2011)
STEER MONITORING PLAN (2010-2015)
r,
r,
tio
co
i—
Threat(s)
Category
Strategy
or
Program
Indicator
Methods
Needs/
Status
(already
being
done?
Complete
d?)
t ri
(3
liZ
Q.
CA
c
—
E
i=
-0
to›..
u
c
CD = -
T.
LL
c
o
rti u
o
_i
2
0
.c
3
— —
vi — u
8 ru
.— .C.
Co
E o
•E
To
D
c c
n3
-ci
G)
-0 ...
CU
0
cu 0
c L.,
0,
CD u
'5
9.
w
cc
a, u
I5
o
in
to
c
'5
C
D
u_
c
0
71- +
0.0 22
c co
o-
c
E -0 '47..
0 0
n3
E ti ',51
13a E
-.
o
cia)
Last updated summary/
analysis report (date +
citation)
Corals
Water
quality,
sediment,
climate
change
(sea level
rise and
increase
sea
surface
temperate
re),
anchor
and
grounding
damage,
loss of
herbivores
trash,
vessel
sewage
Status of
resource
Species
composition,
% live coral
cover, disease,
partial
mortality,
herbivory,
lionfish
presence,
water
temperature
Entrant
Field
measurem
ents
(AGRRA,
UVI,
Bio
monitorin
0 ,
permanen
a
t
quadrats
X-Mas
Cove
study
(Nemeth
and
Kadison,
March
2008),
germane
nt
monitori
stations,
ng
EPA
few
at a
locations
(March
2009)
4x/yr.
(Smith),
every
Smith
,
year
(MMES)
Perman
ent
sites: X-
Mas
Cove,
Secret
Harbor,
Cas Cay
Cay,
Great
Bay,
False
e,
Cowper
Bay
Tyler
.
Tyler
NEEDS
EPA, UVI,
MMES
Scuba,
days/pe
,
boats:
$5000?
UVI-
MMES,
EPA
AGRRA,
TSmith,
EPA
TO BE
COMPI
LED
66
EFTA01119718
STEER MONITORING PLAN (2010-2015)
CO
I—
Threat(s)
Category
Strategy
or
Program
Indicator
Methods
Needs/
Status
(already
being
done?
Complete
d?)
irc
(3
'1Z
Q.
to
. c
E
i
-a c
to
›..
u c
G) =
o-
2.)
LL
c
o
«.
to
cso
-i
2
o
.c
3
— —
ii, —
8 2
E O
O
u
E o
-E
To c
c
to
G)
-0 .
IV
uto
ru o
c c.,
un
G)
i.,
5'
2
w
cc
U
'5
O
vl
to
c
'5
c
=
u_
c
to
it 4-
c -O
O •—•
c
4 ,
E -O r.,
O a
E Tu. .ti
-O O. u
a E
— o
co t,
i; -
o
Last updated summary/
analysis report (date +
citation)
.o
H
LL
WQ,
sediment,
habitat
loss,
illegal
fishing,
vessel
sewage
resource
1) Juvenile fish
diversity
2) #
areas
3) baitfish
biomass
1) traps
2)
lobster/co
nch
surveys
3) lunar
sampling
DFW
(Shenell
NEEDS
TO BE
DONE
Every
year
(ideal,
but
labor
intensiv
e)
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ye area,
base it
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and
study
(see
research
needs)
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voluntee
rs
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intensive
: DFW
juvenile
fish
survey
cost at
least
$40,000
but it
could be
much
greater
USFWS
Sport
fish
tion
Grant
DFW
survey
from July
2008
until June
completi
on report
submitte
d in
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r 2009
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COMPI
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in
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reduced
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loss of
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success, 3)
migratory bird
counts
1) lx
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depends
on
location,
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survey
DFW
NEEDS
TO BE
DONE
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2) 1
time 3)
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Cays
DFW
55-10K
USFWS
grants?
NEEDS
TO BE
DONE
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STEER MONITORING PLAN (2010-2015)
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sediment
testing
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contamin
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study
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every 3-
5 years
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s Pt.
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time, $
2,000
(-$54,00
0 for
restorati
on
includes
staff
time,
geologist
, and
dredging
for FY10)
USFWS
and
NOAH
Jerecki
2003,
Rennis et
aL 2006,
Stengal
1998
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TO BE
COMP1
LED
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STEER MONITORING PLAN (2010-2015)
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STEER MONITORING PLAN (2010-2015)
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preventi
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regulatio
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load in fish,
invertebrates
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lx
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$$.
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year of
project
(if
funded)
would
NOAA
CRCP
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proposal,
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d
contamin
ants
NEEDS
TO BE
DONE
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EFTA01119722
STEER MONITORING PLAN (2010-2015)
7
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disturbance
1) benthic
mapping
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extent
1999
NOAA
maps,
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oceans
maps.
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NEEDS
TO BE
DONE
lx
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then 2-3
years or
after
disturba
nce
event
STEER,
or at
disturba
nce
event
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Pitman)
NOAA
NOAA
Corals
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increase
sea
surface
temperatu
re
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response
plan
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measure
the extent
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partial
mortality
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be done
when
have
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suspecte
d
bleaching
event
Its
.c At
bleachin
g event
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location
s (see
status
or
k NOAA?
monitori
ng for
corals)
Bleachin
g
response
team
(TNC,
UVI,
DPNR)
Scuba,
days/pe
ople,
boats:
$5000?
TNC?
Florida
Reef
Resilience
71
EFTA01119723
STEER Management Plan (May 2011)
STEER MONITORING PLAN (2010-2015)
Do
3,-
Threat(s)
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ment
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Who? Where?
When?
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public role in
monitoring
- volunteer,
organize
watchers,
multiple call
in points
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permits
records,
create
summary
report,
observatio
nal study
(optional)
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TO BE
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sc
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time
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ment—
Student
project?
—Aquatic
heritage
(Simon,
Shaun,
Chris)
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NEEDS
TO BE
DONE
72
EFTA01119724
STEER MONITORING PLAN (2010-2015)
1:7
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(DFW)
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after
restorati
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annually
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action
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students
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?
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?
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2003,
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1998
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TO BE
DONE
to-
a
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boat
grounding
1)
groundin
gs
removal
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/recent
mortality
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document,
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accidental
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Mas
Cove
X-Mas
Cove, at
disturba
nce,
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Buoys
program
, DPNR
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days/pe
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boats :
DFW
Buoys
grants,
NOAA
In DFW
buoy
proposal:
following
NPS-
Tom
Kelly-
has
73
EFTA01119725
STEER Management Plan (May 2011)
STEER MONITORING PLAN (2010-2015)
w,
Threat(s)
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damage
2) Buoys
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(corals,
seagrass)
2) Seagrass
shoot density
in anchoring
areas vs.
adjacent to
newly
established
buoys
damage
2)
underwate
r sampling
with
transects,
quadrats
at
randomly
selected,
permanen
t sampling
locations
(X-Mas
Cove
being
done by
DFW) Sea
Tow or
Sophia
has data?
mooring
installati
on +
benthic
survey
every 6
months
for 3
years.
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disturbs
nce
event
followin
g
removal
of
derelict
vessels
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e (Will
Coles,
Kent,
Coast
Guard),
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ngs),
voluntee
rs
$5000?
restorat
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new
STEER
grant#
F-25-1,
Project
#FZ0SF,
DFW
could
write
grant to
continu
e with a
long-
term
study of
this
area.
Rafe
Boulon
NPS ST.I
protocols,
FL
methods
for
groundin
g removal
records
for
years
before
moorin
gs
74
EFTA01119726
STEER MONITORING PLAN (2010-2015)
TS
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vessel
removal
# of derelict
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response time
to removal
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Tow,
Enforceme
nt records
NEEDS
TO BE
DONE
lx/yr. at
year
end
STEER
Enforce
ment
Cheap
DFW
might
be able
to write
a grant
or add
it to the
USFWS
STEER
grant F-
25-1 for
derelict
vessel
removal
in
STEER
via
USFWS
or
NOAA
funds.
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ent?
75
EFTA01119727
STEER Management Plan (May 2011)
STEER MONITORING PLAN (2010-2015)
r;
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Climate
Change:
sea level
rise
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Change
adaptati
on plan
1)Extent of
possible
migration 2)
species
composition
1) Model
SLR 2)
studies on
mangrove
reaction to
SLR
1) TNC
will be
working
on this 2)
Compilati
on of
past data
needed +
new
project
by Simon
Pittman
1) lx 2)
over an
extende
d period
of time
STEER
TNC
(Jeanne),
NOAA
(Simon),
DEP
(Noorhas
an)
$$$
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TNC
Florida/P
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SLR
studies,
IUCN
Mangrov
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resilience
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Trapping
Program
Drop in # rats,
mongoose,
cats following
trapping
How bad is
the rat
Track the
number
caught in
traps per
month
until
eradicated
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be done
as
internshi
p
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tion of
data
that is
constan
tly
collecte
Cas Cay,
Bovoni
coy
DFW,
Voluntee
rs
Cheap
NEEDS
TO BE
DONE
76
EFTA01119728
STEER MONITORING PLAN (2010-2015)
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ment
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h,
tracking
monofila
ment
threat
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incidents of
monofilament
entanglement
2) source of
monofilament
- how much
collected?
Where?
1) Compile
reports of
survey &
photo
document
ation of
monofilam
ent
entanglem
ent of
birds in
the area
2) Keep
spatial
record of
monofilam
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be done
as
internshi
p
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tion of
data
that is
constan
tly
collecte
d
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and
surroun
ding
bird
areas of
STT, Ritz
cleanup
of shore
DFW
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topic will
be
addresse
d at all
(or most)
of the
recreatio
nal
fishing
tournam
ents
captains
meetings
to make
fishers
Cheap
require
monofila
ment
reporting
in
permittin
g for
research
NEEDS
TO BE
DONE
77
EFTA01119729
STEER Management Plan (May 2011)
STEER MONITORING PLAN (2010-2015)
Threat(s)
Category
Strategy
or
Program
Indicator
Methods
Needs/
Status
(already
being
lej
done?
if.
Complete
d?)
Frequency and Timing
C O
o
2
D
C
o
c
..c
ro
3
.6
O t
(1)
"0
4....
8 tm
CU
CU
O
C
O
C.,
C
V
O U
IA
E
u
o
'5
-C
o
In
Q.
CC
Funding Source
ent
collected
in trash
clean ups
3)
interview
fishermen-
aware of
the
problem
78
EFTA01119730
Table 7. STEER Initial Research Needs
STEER INITIAL RESEARCH NEEDS (2010)
Target(s)
Strategy
Threat
Or
Category
Program
Indicator
Methods
Needs/
Status
›.
(already
1.-
cc
being
O
done?
c.-a
0.
Complete
d?)
-o c
CO
>. Da
° .!
5 E
3 P
cr
cu
u.
C
o
7..
et,
Who monitors (who
to contact)
Resources needed,
annual cost
Funding Source
Detailed monitoring
plan completed?
(date + citation)
Last updated summary/
analysis report (date +
citation)
Birds, mangrove, seagrass
Disturbance
Baseline:
Carrying
Capacity
@ Cas
Cay and
Mangrov
e Lagoon
Acceptable # of
visitors/day
Conduct
observation on
given day +
during peak use:
get record of
number of
people/boats at
Cas Cay, Inner
Lagoon.
Record Ecotours
effect, if any, on
resource
including: birds
flushing,
proximity to
nests,
inexperienced
snorkelers
damaging
resources (corals,
Increase
sedimentation
from people
Need to
obtain
standards
from
similar
studies
(NPS?), in
VI code?
How did
DEE
determine
CC in
Secret
harbor?
Managem
ent
recomme
ndations
for
regulating
number of
people,
limits of
1 time
Cas
Cay,
adja
cent
man
grov
es
MMES
Stude
nts
cheap
UVI?
NPS?
79
EFTA01119731
STEER Management Plan (May 2011)
STEER INITIAL RESEARCH NEEDS (2010)
;-
a.)
,,c4
(—
Threat
Category
Strategy
or
Program
Indicator
Methods
Needs/
Status
(already
being
done?
Complete
d?)
PRIORITY
Frequency and
Timing
Location
Who monitors (who
to contact)
Resources needed,
annual cost
Funding Source
Detailed monitoring
plan completed?
(date + citation)
Last updated summary/
analysis report (date +
citation)
churning up
bottom, etc.,
incidence of
pulling boats
ashore Cas Cay
disturbanc
e, etc.
tg
Disturbance
, anchoring,
trash
Baseline:
Carrying
Capacity
@
Christmas
Cove
Acceptable # of
boats, visitors/
day
Conduct
observation on
given day +
during peak use,
determine
preferred sites
Obtain
standards
from
similar
studies
(NPS?)
1 time
Chri
stm
as
Coy
e
Kostas
?
Drew?
cheap
UVI?
NPS?
ALL Targets
Impaired
watershed
Baseline:
Watershe
d Study
Baseline study of
flow and source of
inputs,
recommended
BMPs
Need watershed
study done via
NOAA /CWP,
Restoration
recommendation
s
NEEDS
TO BE
DONE
1 time
STE
ER
wat
ersh
ed
CZM:
NOAA
or
CWP
$?
NOA
A?
2
„,
i,
Harvest,
habitat loss,
pollution
Baseline:
need
monitorin
g plan for
nursery,
baitfish
ID where to
monitor
Do background
research on
recruitment
frequency,
reproductive
periods & test in
field
Backgroun
d
references
=
= lx
STE
ER
Stude
nt
projec
t
80
EFTA01119732
STEER INITIAL RESEARCH NEEDS (2010)
Target(s)
Threat
Category
Strategy
or
Program
Indicator
Methods
Needs/
Status
(already
being
done?
Complete
d?)
>.
b-
cc
c)
c1.
-o c
m ). tv)
u .c
5 E
g P
tu
u.
Location
Who monitors (who
to contact)
Resources needed,
annual cost
Funding Source
Detailed monitoring'
plan completed?
(date + citation)
Last updated summary/
analysis report (date +
citation)
Birds
Predators,
monofilame
nt
Baseline:
populatio
n study
1) ID where birds
3) migratory
species
Conduct bioblitz
inventory with
volunteers or
contract for a
study
Needs to
be done
1)
lx/yr.
study
2) lx
3)
2x/yr.
(sprin
g, fall)
STE
R
DFW
Volunte
er or
contract
DFW
?
Compass Point Salt
Pond
Watershed,
habitat loss,
climate
change
Baseline:
indicator
species
Seasonal
difference in
indicator species
(Fiddler crabs)
Do background
research, field
study
Needs to
be done
lx
Corn
pass
Poin
t
Salt
Pon
d
DFW
Student
DFW
?
Coral
Groundings,
climate
change
Restorati
on
Suitable hard
bottom-
.
potential/historica
I critical habitat
NOAA benthic
mapping,
ground-truthing
NEEDS
TO BE
DONE
3
op
—i
.....
/
2
lx,
then
2-3
years
STE
ER
81
EFTA01119733
STEER Management Plan (May 2011)
2.8 Zone and Mooring Plan
A Proposed Zoning and Mooring Plan was compiled from an inventory of the natural resources
within STEER as well as with stakeholder input. Channels are marked for boating traffic to assist
with minimizing wake; however additional signage and moorings will be added to assist users
with locations designated for certain types of permitted activities within STEER.
Stakeholders at work, J. Brown
The Zones include:
General Use Zone: Area where surface waters are kept clear for recreational and transit uses.
Anchoring and extraction of resources are prohibited.
Low-Impact Use Zone: Area where anchoring is allowed with a permit for a maximum of seven
[7] days. Extraction of resources is prohibited as is tying to mangroves.
Preservation Zone: Area where motorized watercraft, extraction of any resource, and
anchoring is prohibited. Area designated for ecological sensitivity compatible with non-
motorized craft and passive recreational activities.
Emergency Anchor / Hurricane Mooring Zone: Area where hurricane moorings are located and
temporary anchorages are allowed only during major storm events as this zone is kept in
Preservation otherwise.
82
EFTA01119734
Gem
•
9
•
• JirnP6
et
Figure 7: Proposed STEER Use Zones
,Vile Y
Jamt
0
Mr kat gutty
toning
Genets Una
MB Low Impact Jet
ME Pres arvatton
F annuity Anchecilluitkana Mooring
Table 8. STEER Activities Guide
Activity
General Use Low-Impact
Use
Preservation Emergency
Anchor
Motorized watersports
I
I
x
x
Non-motorized watersports
I
1
i
i
Baitfishing
Permit'
Permit'
x
x
Handline fishing
Permits
Permit'
x
x
Anchoring
1
1
x
1
Harvesting (whelk, conch, lobster)
x
x
x
x
Scientific research
Permit
Permit'
2
Permit'
Permit
7
Picnicking
i
1
1
./-
Hunting
x
x
x
x
Spearfishing
x
x
x
x
Transit
1
x
x
x
Camping
x
x
x
x
I.Contact Division of Environmental Enforce men : (340) 774.3320, 2. C mad Division of Fish and Wildlife: (340)775.6762
83
EFTA01119735
STEER Management Plan (May 2011)
III. SUSTAINABLE FINANCIAL PLAN
3.1 Summary of the STEER Sustainable Finance Plan
(Full Sustainable Finance Plan can be found in Appendix F.)
INTRODUCTION
Although the MRWSs that make up STEER are legally protected entities, they have had little
management and oversight. The various divisions of DPNR are stretched thin and in some cases
receive federal funding only for certain activities that do not include protected area
management. It is proposed that STEER be established as a marine park with a dedicated
management body to enforce the laws, conduct scientific monitoring and habitat restoration
and educate and engage stakeholders. One of the main obstacles to creating STEER is a lack of
financial and human resources. The Sustainable Finance Plan uses business planning
methodology, adapted for protected areas, to address these issues and lays the foundation for
achieving financial sustainability. The plan identifies the operational and investment needs of
STEER, the available resources if any and proposes a portfolio of financial mechanisms to fund
these needs. The funding will have to come from a variety of sources including government,
concessions and private donations as well as larger scale fund raising programs down the road.
The cost will be significant but conservation of the STEER area is in the best interest of the
residents, the private sector and the government as it contributes enormously to the tourism
industry, which is the main economic activity of the island, and also provides ecosystem
services that are extremely costly if not impossible to replace and that benefit the entire St.
Thomas community.
MARKET ANALYSIS
Direct Use Benefits
According to the U.S. Virgin Islands 2004-2005 Visitor Exit Survey for Air Visitors and Cruise
Visitors, "Tourism is the largest industry in the USVI and the major source of income and
employment. The industry generates some $4 billion in total economic impact and accounts for
30% of the workforce. Direct gross expenditure by visitors was $1.5 billion." (Dorsett, 2005, p.
xi). The average expenditure of a cruise visitor was $306 (Dorsett, 2005, pp. xi-xii). Much of the
tourism activity in St. Thomas occurs in the East End. The beautiful setting is a major draw for
sailors and other tourists who go snorkeling, diving, kayaking, or who stay in the hotels along
the coastline.
About 24% of all air visitors chose to stay in a hotel operating adjacent to the Reserves (Dorsett,
2005, p. 32). Christmas Cove, one of the most popular sailing spots, is also a popular spot for
local residents, boaters from the BVI's and Puerto Rico and other tourists. Observational data
84
EFTA01119736
compiled from people who live and work in STEER estimate that about 20 boats per day anchor
at Christmas Cove during the high season (Nemeth and Kadison, 2008) and three to four charter
boats use the area with an average of 45 people per day. The VI Eco Tours operates within the
Cas Cay Mangrove Lagoon Sanctuary and has about 10,000 visitors per year mostly from cruise
ships but also including 1,000 students. The yacht clubs and other private mooring areas that
operate within STEER boundaries generate revenue for the government in the form of mooring
permit fees and boat registration fees as well as in membership dues that support the clubs.
The various private moorings, which total 150 within STEER, and the dock slips provide revenue
for the DEE as do the boat permits for CZM. This information however is not digitized and
neither the DEE nor CZM were able to provide the figures.
Indirect Use Benefit
Coral reefs, mangroves, seagrass beds, and salt ponds provide important habitat for marine and
terrestrial wildlife but they also provide important ecosystem services that keep the waters
clean and clear, protect the coastline against erosion and waves, and offer nursery grounds for
fish and other marine life to develop. It is these outcomes that the tourism and fishing
industries depend on. The following section outlines the estimates of their economic value in
the form of the subsequent tourism and fishing revenue they support, as well as their other
functions.
Estimates of the economic value of coral reefs range from $100,000 to $600,000 per sq km and
between $200,000 to $900,000 per sq. km for mangroves. (Wells, 2006, p. 5). This range
depends on how close the reefs and mangroves are to developed centers of tourism, fishing
etc. The value of seagrass beds are estimated at $350,000 per sq. km (Loney, 2009). Data on
sq. km area for STEER are limited to coral reef/colonized hard bottom and seagrass beds. Using
these estimates of coral reef and seagrass cover, the lower bound (partial) value of STEER
totals $3.4 million per year. The valuation techniques are based on many assumptions and do
not include other values that are very hard to quantify such as the aesthetic value of the ocean
to residents, the potential pharmaceutical values of coral reefs, the value of biodiversity, and
the replacement costs of the ecosystem services. What is known is that the value of the marine
resources within STEER is immensely important to the tourism industry in St. Thomas due to
the ecosystem services they provide free of charge. It is in the USVI's interest to invest in STEER
so that these resources are better protected today so that future generations will be able to
enjoy and benefit from them.
85
EFTA01119737
STEER Management Plan (May 2011)
FINANCIAL ANALYSIS
Historical Expenditure and Funding
STEER has had some scientific monitoring and other conservation activities within its
boundaries by the DFW, DEP, UVI and other groups but it has never had a management agency
of its own. It is difficult to track historical expenditure as many of the programs implemented
by DFW or DEP were part of larger island wide or territory wide programs where the
expenditure within STEER was not tracked. DFW staff estimated that $100,000 has been spent
on STEER within their department over the last 10 years, and up to $233,000 in current grant
spending is going toward STEER projects.
Once STEER is set up with a managing body, it is recommended that it have its own financial
system, with its own line item in the USVI government rather than having it be part of CZM's
financial accounts. It is also recommended that STEER track the funding received, any revenue
generated and expenditure in annual budgets. These budgets should be structured using the
activity based accounting system which is an accounting method used to determine
expenditure by specific activities or program areas rather than along more traditional budgeting
structures. This provides a view into how money is spent in the various functions of the
management agency. It includes staff and operating expenses (recurrent) as well as investment
expenditure organized by functional area. Please refer to Annex I, Table I in the full Sustainable
Finance Plan to better understand the various functional areas. (Appendix F)
Financial Needs Analysis
It is assumed that the Divisions of DPNR that have been working in the area will continue to do
so and their budgets will remain the same so any funding needs for STEER will be in addition
and separate from that work. The following presents the needs of STEER described by various
stakeholder interviews. The needs analysis uses the Activity Based Accounting method and
determines the operational needs at a critical and optimal level. Mission critical can be defined
as the level of operations and the amount of resources that are necessary to meet the most
important of the park's goals and objectives. Mission optimal is defined as the level of
operations and the amount of resources that are necessary to fully meet the goals and
objectives of the park's program areas.
STEER needs a management entity and an operational structure. This requires the hiring of
staff, office space and many other investments to get the park up and running. The following
chart provides the recurring needs of the system at the critical and optimal level. The needs are
greatest in the resource management and protection category and the management and
administration category. The former category includes activities related to patrol and
enforcement, scientific monitoring and research, as well as wildlife management and habitat
86
EFTA01119738
restoration. The total needs for the park total $808,000 at a critical level and $976,000 at an
optimal level. This includes 7.5 full time staff at the critical level made up of a marine park
director, a marine biologist, an education and outreach coordinator, an administrative
assistant, two and a half interpretive ranger positions and a full time DEE officer. The figure
increases to 9 full time staff at the optimal level by increasing interpretive rangers from 2.5 to
4. If investments are included the figures increase to $1.8 million and $2.5 million respectively.
Included in investments are several large baseline studies that will help in monitoring the
natural resources and conservation efforts of STEER. The Financial Summary Table is in Annex I,
Table II found in the full Sustainable Finance Plan in Appendix F. For the list of investments
please refer to Annex I, Table III.
STEER Needs Assessment by Functional Area
$320,000
$280,000
$240,000
$200,000
$160,000
$120,000
$80,000
$40,000
$0 1 1
1 1
Resource
Tourism and
Commercial
Management
Community
Facility
Management
Recreation
Commodity
and
Development Operations and
and Protection
Uses
Administration and Outreach
Maintenance
■ Current Expenditure
■ Mission Critical
■ Optimal State
Figure 8: STEER Needs Assessment by Functional Area
The financial needs analysis can be projected forward ten years based on an estimate of the
recurrent costs adjusted for inflation and based on an estimate of when the investments will be
implemented. In ten years, STEER will need $1.1 million at a critical level and $1.3 million at an
optimal level, however the first three years when the major infrastructural and research
investments will need to be made will require much more. Year 1 requires $1.7 million (critical)
and $2.3 million (optimal).
87
EFTA01119739
STEER Management Plan (May 2011)
FINANCIAL STRATEGY
STEER has many basic needs and will require a diverse source of revenue to meet its
conservation goals. In developing a sustainable financial strategy one of the first areas to
examine is the feasibility of potential financial mechanisms. The feasibility of any potential
source of funding is evaluated by examining how difficult it would be to implement, the
certainty or volatility of the revenue stream and the potential revenue generation. The cost
recovery must not exceed the total revenue generated. Any financial mechanism must also
comply with the goals and objectives of the Park. In analyzing the financial mechanisms in the
context of STEER, ten were identified as having potential. They were then rated by the above
criteria. The following table presents the results.
Table 9. Financial Strategy Ranking for STEER
Financial Mechanism
Potential for
revenue
generation
Certainty of
revenue
stream
Complexity of
implementation
Overall
Value
Rating (1 is low, 2 is
medium, 3 is high)
1, 2, 3
1, 2, 3
-1, -2, -3
Fines
1
2
-1
2
Government Contribution 3
3
-2
4
Membership Dues
2
2
-1
3
Park User Fees
2
2
-2
2
PA Trust
3
3
-2
4
Payments for
Environmental Services
1
1
-3
-1
Environmental Entrance
Fee
3
2
-3
2
Concession fees, Permits
and Licenses
1
3
-1
3
Private donations
2
2
-1
3
Special Commercial Uses
1
2
-1
2
88
EFTA01119740
Feasibility Analysis and Potential Revenue Projections
The most potential financial mechanisms were determined through research as well as a
stakeholder review. Federal Funding, PA Trust, Concession Fees, Permits and Licenses,
Membership Dues and Private Donations to a fiduciary body such as Friends of STEER were
seen to be the most feasible by stakeholders and an Environmental Entrance Fee was
determined to have high revenue generation potential. The establishment of a protected area
trust was seen as an important tool to mitigate volatility in revenue generation and act as a
pass through for all revenue generated by the marine park ensuring that this revenue is re-
invested into conservation activities. Revenue projections for the most feasible financial
mechanisms total $645,000 per year and $4.6 million per year for future, more complex
financial mechanisms. The former does not cover the critical recurrent needs of $808,000 nor
the investment costs. Therefore, the local government will also have to contribute and other
potentially more difficult financial mechanisms will have to be implemented. The following
table summarizes the potential revenue projections and compares the projections to the critical
and optimal funding gap.
Table 10. Potential Revenue, Critical and Optimal Funding for STEER
Funding Mechanisms
Fee $
No. of people
Total
Membership Dues
20
5,000
100,000
Private Donations
1000, 10000
50, 10
150,000
Fines
1000
5
5000
Permits for research, photography, filming, special events
250
10
2,500
Concessions: Tours, Vending
300
5
1,500
Concessions: Hotels, Condo Complexes, Rentals Co's
1,200
30
36,000
Federal Funding
25
500
350,000
Total
645,000
Future Potential Funding Mechanisms for a PM
Cruise Ship Environmental Fee
1
1,918,000
1,918,000
Air Tourism Environmental Fee
5
511,000
2,555,000
Protected Area Trust
150,000
Total
4,623,000
Critical Gap of STEER including investments
1,772,000
Optimal Gap of STEER including investments
2,513,000
89
EFTA01119741
STEER Management Plan (May 2011)
3.2 Management Structure and Implementation:
Establishment of a Park, Board, Capacity and Staffing
Based on input and suggestions from stakeholders, one of the best means to get started on
building a management structure for STEER in the near-term is to develop a Friends of STEER
voluntary, non-governmental group which is organized with a board that functions based on
performance standards. This group would start by writing proposals for grants to set up a
funding mechanism, and develop the protected area trust for long-term financing. A head tax
from visitors could be used to seed the PA Trust.
Suggested staff for STEER:
1) Coordinator:
a. Overall coordinator for the Territory's Parks (STXEEMP, STEER)
b. OR: Coordinator for STEER
2) Rangers/surveillance staff:
a. IDEAL: up to 4 ($200,000)
• Need to get enforcement training (CZM staff- can issue cease and desist orders)
b. can build dedicated FTE into grants for DEE, then officers work with Rangers
•
(STXEEMP did fund 2 % time officers- didn't work)
3) Education and Outreach:
a. Eventually have a Full Time Employee (FTE) on this
b. Build 20% into the St. Thomas CZM education and outreach coordinator position? Could
possibly coordinate with VINE to make STEER outreach a special project of theirs until
FTE is hired
4) Marine Biologist
a. Eventually have a FTE on this
5) Bayhosts
CHALLENGES TO IMPLEMENTATION
One of the main challenges to implementation of a sustainable finance plan for STEER is the
negative view local stakeholders have of governmental management and their reticence to pay
fees. The negative view is affirmed in studies such as the "History of Protected Area Initiatives
in the U.S. Virgin Islands" (Towle, 2003) that outlines the difficulties the USVI has had in
implementing effective protected area systems and the NOAA review of the Coastal Zone
Management Program (Office of Ocean and Coastal Resource Management, 2009), which
highlights staffing and project implementation issues. Hiring staff has been a major challenge
for the STXEEMP in the past. The process is long and laborious and many qualified applicants
cannot wait such a long time to be hired. The same may happen for STEER. If a semi-
autonomous body were created, perhaps they could implement a different hiring procedure
90
EFTA01119742
that improves upon the government hiring process. In addition, applicants for the Interpretive
Ranger positions are supposed to be fishermen and other users of the area but often times they
do not have the academic qualifications. More training needs to be available for fishermen to
be able to qualify for conservation type jobs.
The Wildlife Sanctuaries and Marine Reserves in the East End are currently more like "paper
parks" with very little conservation and protection. It will likely take quite a number of years
for STEER to be a well functioning and effective protected area, especially if hiring issues are
not resolved. This may discourage stakeholders from paying fees or donating money in that
they may not "see" any tangible benefits from the establishment of STEER and its managing
entity. Already local residents, especially business owners, feel that they already pay too much
in fees to the government. Marine users feel they are unfairly targeted for revenue generation
in parks despite the fact that they are not the main polluters but rather protectors of the
marine environment. The load should be shared by marine and terrestrial users and by those
having the greatest impact on the marine resources. Before implementing any fees, STEER and
CZM will have to have significant stakeholder participation in the development of the fee
system. The establishment of a semi-autonomous body to manage STEER, with a financial
system set up to ensure that money raised for the park goes towards conservation efforts,
would help in raising support.
The establishment of a semi-autonomous body to manage all territory wide protected areas
under local government control could streamline conservation efforts but new legislation
would have to be passed to create the agency as well as to create a PA Trust for marine as well
as terrestrial protected areas. This could be a long process, especially if there is resistance from
local government bodies. In addition, a semi-autonomous body would have to generate its own
revenue and this too would require strong government support and cooperation as well as
support from local residents. It would also require an investment of time and resources to get
the financial mechanisms implemented. This means that conservation efforts and protected
area initiatives would have to be priorities for the government, which is challenging even in the
best of times when governments have competing interests such as education and economic
development.
91
EFTA01119743
STEER Management Plan (May 2011)
IV. REFERENCES
Carbery K, Owen R, Frickers T, Otero E, Readman, J. 2006. Contamination of Caribbean coastal waters
by the antifouling herbicide Irgarol 1051. Marine Pollution Bulletin 52:635-644
STEER Stakeholders. 2009. Google Groups. http://groups.google.co.vi/grouo/steer-stakeholder
TNC. 2007. Conservation Action Planning Handbook: Developing Strategies, Taking Action and
Measuring Success at Any Scale. The Nature Conservancy, Arlington, VA.
http://conserveonline.org/workspaces/cbdgateway/cap/practices
USVI Department of Planning and Natural Resources. 1981. Preliminary Candidate Marine Sanctuary
Site Evaluation: Southeastern St. Thomas, St. Thomas
Monitoring and Research Protocols References:
Jarecki, L.L. 2003. Salt ponds of the British Virgin Islands: investigations in an unexplored ecosystem.
Doctoral dissertation, University of Kent at Canterbury.
MMES. 2009. Assessment of Mangrove and Seagrass Resources within the St. Thomas East End Reserve
(STEER) Boundary. MMES Student Report, Natural Resources Management, University of the
Virgin Islands.
Nemeth, RS, Kadison, E. 2008. Environmental Marine Survey of Christmas Cove, St. James Island, St.
Thomas, US Virgin Islands. University of the Virgin Islands, St. Thomas 21pp
Rennis, D.S., D.M. Finney, and B.E. Devine. 2006. Evaluating the sediment retention function of salt
pond systems in the US Virgin Islands. Water Resources Research Institute, University of the
Virgin Islands, St. Thomas.
Smith, TB, Blondeau,l, Taylor, M, Nemeth, RS, Calnan, 1M, Tyner, E. 2007. Continuation and Expansion
of the Territorial Biological Monitoring Program. Final Report. Submitted to the USVI
Department of Environmental Protection. Center for Marine and Environmental Studies.
University of the Virgin Islands 69pp
Smith, TB, Nemeth, RS, Blondeau,l, Calnan, 1M, Kadison, E, Herzlieb, S. 2008. Assessing coral reef
health across onshore to offshore stress gradients in the US Virgin Islands. Marine Pollution
Bulletin 56:1983-1991
Stengel, C. A. 1998. The survey of the salt ponds of the U.S. Virgin Islands. Department of Planning
and Natural Resources Division of Fish and Wildlife, St. Thomas, US Virgin Islands.
USVI Territorial Coral Reef Monitoring Program, unpublished data
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APPENDICES
See accompanying document:
STEER (2011) St. Thomas East End Reserves Management Plan: Appendices. St. Thomas, USVI
93
EFTA01119745
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Domain
pa.govDomain
vifishandwildlife.comPhone
(340) 774.3320Phone
(340)775.6762Phone
4630112SWIFT/BIC
INFORMATIONURL
http://conserveonline.org/workspaces/cbdgateway/cap/practicesURL
http://dpnr.gov.vi/dep/1-dec-intent.htmURL
http://groups.google.co.vi/grouo/steer-stakeholderURL
http://www.dpnr.gov.vi/dep/pubs/17602-FINALWire Ref
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