HABITAT EQUIVALENCY ANALAYSIS

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HABITAT EQUIVALENCY ANALAYSIS

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Title: HABITAT EQUIVALENCY ANALAYSIS


1
HABITAT EQUIVALENCY ANALAYSIS
Determining Compensation for Coral Reef Injuries
Overview of Habitat Equivalency Analysis Approach
Richard Dodge, Kevin Kohler, David Gilliam,
Brian Walker, Alison Moulding Nova Southeastern
University Oceanographic Center National Coral
Reef Institute Vladimir Kosmynin Florida
Department Environmental Protection
2
HEA ? A Method for Determining Compensation for
Lost Natural Resources
  • (As in our case study,) a coral reef is injured
    by a dredging related activity
  • Injury area large Severity varies
  • The injury (loss), after primary restoration,
    will take time (years) for recovery to return to
    its previous level of services
  • How much of a Compensatory Action should there be
    to replace these lost services (in order to
    adequately compensate the Resource Trustee)?

3
Case Study Review of Reef InjuryThe Problem
  • Nov 02 during channel improvement operation at
    Hillsboro inlet (SE FL USA) steel tow cables
    (from a tug to barge) dragged over a coral reef
    causing extensive biological resource

injuries in 12-25 m depths.
  • Impacts included dislodged scleractinian corals
    and gorgonian corals as well as sheared sponges
    (mostly Xestospongia muta).
  • Reef framework was not fractured.

4
Cable Drag Reef Injuries
Overturned Hard Corals
5
Managing the Challenge Injury Assessment
  • Video survey identified reef injury areas
  • Divers qualitatively assessed severity
  • Mapped larger injury areas using GPS buoy
  • Smaller injury areas using measuring tape.
  • Injury areas processed into a GIS polygons
  • Planar areas estimated.

6
Triage Organism Reattachment
Nevertheless..
  • Many reef organisms killed, injured
  • Time needed to recover
  • Resource Trustee wanted Compensation for loss

7
Addressing Compensation for Loss Habitat
Equivalency Analysis (HEA) can be a Useful
Solution
  • Determines How much of a Compensatory Action
    there should be to replace these lost services
    (in order to adequately compensate the Resource
    Trustee)
  • HEA balances the services lost and gained over
    TIME.

8
HEA Principles
  • Natural resources are viewed as natural assets
    that provide services throughout lifetime.
  • Total value of such a natural asset present
    value of the future stream of all services
    (DISCOUNTED) over time.
  • Discounting is simply the willingness to pay more
    for something now than in the future.

9
Discounting is Key HEA Concept
  • What would you rather have 1,000 today or
    1,000 1 year from now? (hint.take it now)
  • If 3 discount rate, 1K 1yr from now is only
    970!
  • Translating this into the HEA
  • Total value of natural asset (present) value of
    the future stream of all services (discounted)
    over time.

S



LATER
NOW
10
Basic Procedure of HEA
  • Assess the injury to natural resources (after
    primary restoration).
  • Determine services lost from injury until
    recovery or equilibrium state.
  • Decide on restoration action (type or kind) and
    level of services to be gained (i.e., amount of
    services that it will provide over time).
  • From this information, HEA determines amount of
    that compensatory action to be created such that
    services GAINED (provided by) the compensation
    over its lifetime services LOST from the
    injury.
  • Time history of services is critical.

11
Types of HEA
  • Landscape
  • Traditional method
  • Uniform landscapes little difference in
    biological functions across the injured area.
  • Use keystone species, e.g., sea grass, A.
    palmata.
  • Population approach (Milon and Dodge, 2001)
  • Injury area allocated into portions based on
    contribution of the organism / categories of
    interest.
  • Several, e.g., hard corals, gorgonians, sponges.
  • Individual HEA for each using its allocated area.
  • Results for each species (category) are summed.

12
HEA Structured framework for providing
considering important biological parameters
  • INPUT
  • Amount of Injury (area)
  • Nature of Natural Recovery (Amount, Duration,
    Shape)
  • Nature of Compensatory Action (trajectory towards
    equilibrium, persistence)
  • Ratio of Services
  • Discount Rate ()
  • OUTPUT
  • Amount (area) of Compensatory Action (area) today
    to compensate for the loss of services of injury
    over time

13
Calculating Compensatory Habitat How does it
work?
L(OSS) Total Services (area-yr) of Injured Area
Lost from injury
G(AIN) Total Services (area-yr) Gained by
compensatory action
Injury Occurs
Injury Recovers
100
Compensation complete
Services
L
G
0
Compensation Action begins
14
HEA Formulations
  • Formulas are published
  • by NOAA and others
  • Somewhat formidable

15
HEA Software to Assist Visual_HEA
  • Kohler, K.E. and R.E. Dodge 2006. Visual_HEA
    Habitat Equivalency Analysis software to
    calculate compensatory restoration following
    natural resource injury. Proceedings of the 10th
    International Coral Reef symposium. Okinawa,
    Japan. pp. 1611-1616.
  • Facilitates the complex HEA calculations
  • Free for non-commercial use, Spanish version
    available
  • GUI (Graphical User Interface)
  • Full time histories of input/output services
  • Allows quick examination of alternate scenarios
  • Used in our CASE Study ? ? ? ? ? ?

For more information on Visual_HEA, visit
www.nova.edu/ocean/visual_hea/
16
SPONGES HEA
4,064m2
921m2
100
75
L
50
25
2017
2002
100
75
G
50
25
2018
2003
2010
2020
2030
2040
2050
2000
17
HEA Components CASE STUDY
Population HEA Results
18
SPONGES HEA
4,064m2
921m2
100
75
L
50
25
2017
2002
100
75
G
50
25
2018
2003
2010
2020
2030
2040
2050
2000
19
SPONGES HEA
4,064m2
2,570m2
100
75
L
50
25
2017
2002
100
75
G
50
25
2033
2003
2010
2020
2030
2040
2050
2000
20
What Worked HEA Utility
  • HEA calculated amount of compensatory area due as
    a result of an injury.
  • Allowed comparison of restoration alternatives
    under multiple scenarios of injury recovery,
    service levels, and restoration type (speeded by
    software).
  • Focused on reef processes, services parameters,
    not .
  • While are important, reef biology, geology, and
    functionality dictated restoration
    considerations. These are used as HEA input.
  • HEA useful in direct and indirect use cases,
    e.g., lost services are biological uses
    substrate, habitat, pollution sinks, wave breaks,
    habitat, etc.

21
Lessons from Case Experience
  • Early action by RP for triage and primary
    restoration of injury resources avoided higher
    restoration requirements.
  • HEA calculated compensation scenarios focused
    RT on Reef Restoration as an essential management
    tool.
  • RT agreed to a comprehensive monitoring and
    research program to provide valuable information
    on hard coral, soft coral, and sponge
    reattachment techniques and on reef recovery
    rates (useful for other HEAs).
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