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Why Restore Coastal Habitats?
David M. Burdick


Associate Research Professor

Jackson Estuarine Laboratory

Department of Natural Resources & the Environment

University of New Hampshire

Durham, NH 03824


david.burdick@unh.edu
Why Restore Coastal Habitats?
Outline

1) 
2) 
3) 
4) 

Habitats, Values and Threats, including
Climate Change
Impacts, Perception and Action
Benefits, Ecosystem Services Case
Study: Little River Marsh
Take home messages
Southeastern Masschusetts is endowed with a
rich mosaic of coastal habitats

Beaches and Dune Systems

Photo: Sean Woods
Salt Marshes
Sand and Mudflats


Photo: Sean Woods
Shellfish Beds and Reefs

Photo:
Nathan
Johnson,

Orion
Photo
Produc3ons

Seagrass Meadows


Photo: Fred Short, UNH
Rivers flowing into bays (estuaries)
Functional values associated with these habitats:
•  Plant growth to support grazing
and detritus-based food webs
• 
• 
• 
• 
• 
• 

Secondary production
Plant structure to provide habitat 
Support of biodiversity
Protection from flooding 
Protection from coastal erosion
Removal of sediments and excess
nutrients
•  Aesthetic, Recreational & Educational
values
•  Self-sustaining ecosystems
Courtesy, Bob Ulanowitz
Functional values associated with these habitats:
•  Plant growth to support food webs

•  Secondary production,
including finfish and shellfish

Photo: Lawrence Taylor

Plant structure to provide habitat 
Support of biodiversity
Protection from flooding 
Protection from coastal erosion
Removal of sediments and excess
nutrients
•  Aesthetic, Recreational & Educational
values
•  Self-sustaining ecosystems
• 
• 
• 
• 
• 
Functional values associated with these habitats:
•  Plant growth to support food webs
•  Secondary production

•  Plant structure to provide
habitat for nursery, refuge and
foraging (dunes, tidal marshes,
seagrass meadows, algal beds
and artificial habitats)
• 
• 
• 
• 

Support of biodiversity
Protection from flooding 
Protection from coastal erosion
Removal of sediments and excess
nutrients
•  Aesthetic, Recreational & Educational
values
•  Self-sustaining ecosystems
Functional values associated with these habitats:
•  Plant growth to support food webs
•  Secondary production
•  Plant structure to provide habitat 

•  Support of local and regional
biodiversity
Courtesy Joe Luczkovich

•  Protection from flooding 
•  Protection from coastal erosion
•  Removal of sediments and excess
nutrients
•  Aesthetic, Recreational & Educational
values
•  Self-sustaining ecosystems

Courtesy Robert Buchsbaum
Functional values associated with these habitats:
• 
• 
• 
• 

Plant growth to support food webs
Secondary production
Plant structure to provide habitat 
Support of biodiversity

•  Protection from flooding 
•  Protection from coastal erosion
•  Removal of sediments and excess
nutrients
•  Aesthetic, Recreational & Educational
values
•  Self-sustaining ecosystems

Photo: Dick Nicholson
Functional values associated with these habitats:
• 
• 
• 
• 
• 
• 

Plant growth to support food webs
Secondary production
Plant structure to provide habitat 
Support of biodiversity
Protection from flooding 
Protection from coastal erosion

•  Removal of sediments and excess
nutrients (marshes, seagrasses) to
increase habitat stability and
improve water quality
•  Aesthetic, Recreational & Educational
values
•  Self-sustaining ecosystems

Photo: Sean Woods
Functional values associated with these habitats:
•  Plant growth to support food webs
•  Secondary production
•  Plant structure to provide habitat 
•  Support of biodiversity
•  Protection from flooding 
•  Protection from coastal erosion
•  Removal of sediments and excess nutrients
Photo: Wellfleet Shellfish Dep’t.

•  Aesthetic, Recreational &
Educational values
•  Self-sustaining ecosystems

Photo: Fred Short
Functional values associated with these habitats:
•  Plant growth to support food webs
 •  Protection from flooding 
•  Secondary production

•  Protection from coastal erosion

•  Plant structure to provide habitat 

•  Removal of sediments and excess nutrients

•  Support of biodiversity

•  Aesthetic, Recreational & Educational
values

•  Self-sustaining ecosystems

Photo: Sean Woods
Processes that contribute to the Habitats:

Coastal Features

Coastal Processes


Gulf of Maine
Rivers

C
u
s
p


Barrier Beach
Eelgrass bed
Salt Marsh
Step
 Spit
Inlet
Fan

S
t
o
r
m
s







Plate Tectonics

Evolution

US
ACoE



Glaciers
Oceanic
Currents



Succession






soils



Gulf of Maine
Processes that contribute to the Habitats:

•  Primary Production
•  Growth
•  Herbivory
•  Predation
•  Decomposition
•  Secondary Production

Photo: Don DesJardin

•  Migrations of fish (herring, eel, bass) and birds (terns)
Processes that contribute to the Habitats:

•  Complex Food Webs - a characteristic of a healthy
diverse ecosystem - some have already lost complexity as
a result of: 
Michael Moore
– 
– 
– 
– 

Over-fishing and over-harvesting specific species
Introductions of invasive non-native species
Human alterations to the landscape
Eutrophication

Fred Short, UNH
Wellfleet Shellfish Dep’t.
Joe Luczkovich

P. Erickson, MIT SeaGrant
Threats to Ocean Resources:
• 
• 
• 
• 
• 
• 
• 

Overfishing
Invasive species 
Pollution, especially runoff
Habitat alteration 
Coastal development
Aquaculture 
Climate change
•  Pew Oceans Commission

Restoration is about reversing the
effects of all of these impacts
Threats to Coastal Processes and Habitats
•  Over- Fishing / Harvesting: examples Northern Right
Whale; cod declines; bird and turtle eggs; scallops

Photo: Lawrence Taylor



Photo: Michael Moore
Threats to Coastal Processes and Habitats
•  Introductions of non-native, invasive species: codium,
green crab, Japanese shore crab, others
Photo: P. Erickson,
MIT SeaGrant

Photo: Ch. Schubart
Threats to Coastal Processes and Habitats
•  Pollution: 

Photo: Vincent DeWitt

•  Contaminants (metals, organic pesticides)
•  Bacterial Pathogens
•  Nutrient over enrichment and the
cascading effects of eutrophication

Photo: Fred Short
Threats to Coastal Processes and Habitats
•  Human alteration of Habitat 
•  Restricting or blocking tidal exchange

•  Interruption of sediment supply and transport 
•  Artificial Habitats

Town of Wellfleet Web Site

Courtesy Robert Buschbaum, MAS
Threats to Coastal Processes and Habitats
•  Human alteration of Habitat
•  Restricting or blocking tidal exchange

•  Interruption of sediment supply and transport
(dredging, erosion control) 
•  Artificial Habitats - from development, aquaculture

Photo: Sean Woods
Threats to Coastal Processes and Habitats
Climate Change Impacts (Tidal Marshes)
•  Increased sea level – retreat of high marsh?
•  Increased storm activity - Seaward edges will retreat
•  Temperature increases - Vegetation Changes: 
•  Range expansions, loss of forb pannes?

•  Increased rainfall
•  Vegetation change due to Decreased salinity?
Our Climate is Changing:
Our Climate Continues to Change:

Global:

Surface temperatures +0.74°C

Arctic temperatures 2X
Snow and Ice: 

Snow cover decreasing

Glaciers shrinking

Arctic sea-ice decreasing

Ice shelf losses 
Thermal expansion of the oceans: 

SLR has increased from 1.7 to 

3.0 mm/yr
Our LOCAL Climate is Changing:
Seasons changing (shorter, warmer winters, ice-out sooner)

More info at: 
http:/
/CarbonSolutionsNE.org
Our LOCAL Climate is Changing:
Local precipitation increased 20% since ’30s (42 in/year)
Precipitation events larger
Tomas (19th named storm in 2010) 

Mean Decadal Trend 1”
Precipitation Events
1948-2007
Adapting to Climate Change
•  Increasing SLR threatens tidal wetlands
–  Allow tidal marshes to grow with SLR in elevation
–  Allow marshes to migrate landward (no barriers)

from
Smith
2006

What did we have?
What are we left with?

•  Depauperate system
–  70% of tidal marshes, almost if not all with
varying degrees of recurring human impacts
–  Tiny bits of seagrass
–  Shellfish beds overfished and predated by
invasive species (green crab)
–  Most rivers dammed, fish ladders have declining
anadromous runs
Impacts from tidal
restrictions:
• Loss of fisheries
(esp. anadromous spp.)

• Vegetation change
• Subsidence
• Exotic invaders
• Mosquito problems
• Loss of self-maintenance
• Fish passage  trophic export
from: Portnoy, J. and M. Reynolds. 1997. Wellfleet’s Herring River: the case for 
habitat restoration. Environment Cape Cod 1:35-43.
Nekton Production and Export: 
the Trophic Relay


Ethan Nedeau, Biodrawversity
Fish caught in minnow traps marked and
released upstream and downstream of culverts

young resident
nekton
adult resident
nekton

young
transient
nekton
adult transient
nekton

Vegetated
marsh

Alyson Eberhardt et al.

Intertidal
channels

Subtidal
channels

Open
estuary

Ocean
Recapture results of fish marking study:

Fish Passage Rate

Passage rate

0.3

Restricted
Restored
Reference

0.2

0.1

y=-0.1558x+0.2478
r2=0.8517 p0.0001

0.0

0.0

0.2

0.4

0.6

0.8

1.0

1.2

1.4

1.6

Water velocity (m s-1)
Alyson Eberhardt et al. 2011

1.8
NEED: New functional indicators: Nekton
Production and Export

young resident
nekton
adult resident
nekton

young
transient
nekton
adult transient
nekton

Vegetated
marsh

Alyson Eberhardt et al. 2011

Intertidal
channels

Subtidal
channels

Open
estuary

Ocean
Why can’t we see the difference?

•  Loss of connection to coastal resources 
–  Out of sight
–  Don’t care

•  Acceptance of environmental degradation
•  Shifting Baselines http://www.shiftingbaselines.org/lenticulars/index.html
–  ‘better than New Jersey’
–  We have more important things to deal with 

 


– its not broken . . . yet

•  Change is cryptic  removed from fundamental
causes - increased runoff from impervious surfaces
Why don’t we act?

Loss of connection to coastal resources 
Acceptance of environmental degradation
Shifting Baselines
Change is cryptic and removed from
fundamental causes
•  Multiple Stable States:
change to alternative state
is sudden and difficult to
reverse
• 
• 
• 
• 
Why bother?

•  Climate Change is coming, we must adapt
•  So many attempts fail – but not all are equal
–  Great track records for success:
•  Tidal Marsh Restoration 
•  Dam Removal (e.g., Wiswall Dam)

–  Fair to poor success / Room for improvement
and learning:
•  Shellfish Beds 
•  Seagrass Meadows
So, keep the pressure on!

•  New restorations of all kinds
•  Integrate habitats
So, keep the pressure on!

•  New restorations of all kinds
•  Integrate habitats
Habitat Interactions
Reduce
suspended
sediments


Absorb
excess
nutrients



Salt
Marshes


Seagrass
Meadows


Reduce
suspended




sediments


Absorb
excess





nutrients


High
3de
refuge



Selement
sites


Preda3on
refuge


Prevent
Brown
3des


Reduce
suspended



sediments


Shellfish
Beds

and
Reefs


Reduce
plankton


Low
3de
refuge


Reduce
waves



Gulf
of
Maine




Calm
physical
stresses

Improve
water
quality

Provide
alternate
habitat

Reduce
eutrophicaBon

So, keep the pressure on!

•  New restorations of all kinds
•  Integrate habitats

•  Measure results
–  Critical for Adaptive Management (site)
–  Improve knowledge and future projects (regional)
–  Share information (international)
–  Demonstrate value 
•  Case Study: Little River Marsh
Case Study:
Little River
Marsh, NH
Case Study:
Little River
Marsh, NH
Restoration can be costly – is it worth it?
Assessment: 
Structural indices
(hydrology, soils,
vegetation, nekton)
Goals: 
To restore natural
functions 
To provide benefits or
values to people
-a disconnect
Functional values associated with tidal marshes: 
•  Plant growth to support food webs
•  Secondary production
•  Plant structure to provide habitat
•  Support of biodiversity

•  Removal of sediments and excess
nutrients
•  Aesthetic, Recreational 
Educational values

•  Protection from flooding

•  Self-sustaining ecosystems

•  Protection from coastal erosion

•  Long term carbon storage
Gulf of Maine “GPAC” Protocols
•  Hydrology
Tidal Signal (WL Recorders), Elevation

•  Soils and Sediments
Salinity (and Sulfide, Eh, %C, accretion)

•  Vegetation
Abundance, Composition, Invasive spp, Ht.

•  Nekton
ID, Density, Length, Biomass, Richness

•  Birds
Abundance, Richness, Behavior

Neckles et al. 2002.
Restoration Ecology. 10(3)
:556-563.

Konisky et al. 2004.
RPI – An Evaluation Tool

Reference
Marsh
Value
Restoration
Restoration Trajectory
Starting
Point
Calculates % Change towards Reference
/Project Goal
Normalizes actual data into a relative index
score
Value of Tidal Marsh Ecosystem
Services per Annum per Hectare

• 
• 
• 
• 

Costanza et al. 1987: $9,900
In 2008 $ (Gedan et al. 2009): $14,400
Carbon sequestration (European market): $135
Denitrification (Piehler and Smyth 2011): $6,128
New Valuation Strategy


Take:

Ecological
Valua3on
‐
structural
and
func3onal

indicators
used
to
measure
marsh
response
to

restora3on


Set
it
equal
to:

Economic
Valua3on
–
ecosystem
service
values
of

Costanza
et
al.
1997
(2008:
$14,400/ha/yr)

Reference
Marsh

100%


100% =
$14,400 /yr

Impacted
Marsh

39%


39% =
$5,600 /yr

Time

Restored
Marsh

89%


89% =
$12,800 /yr

Net Gain in
Ecosystem
Services =
$7200/ha/yr
RPI Scores for Little River Marsh

Calcula3on
of
Value
of
Net
Benefits
from
Ecosystem
Services

RPI
=
0.91
in
Year
7;


Value
lost
due
to
impacts
from
Bdal
restricBon
=
41%

Year
7
value
relaBve
to
reference
marsh
=
0.91%

SO
.
.
Restored
benefits
=
$14,
400/ha
*
0.41
*
0.91
*
70
ha








































=
$376,000

RPI Calculations for Little River Marsh
OVER first 5 years (2001-2005) = $1.2 million
OVER next 6 years (2006-2011) = $2.2 million
Cost $1.3 million 
From:
Chapter 15:
Tidal
RestoraBon:
a

Synthesis
of
Science

and
Management

Charles
Roman



David
Burdick,
editors

ISLAND
PRESSS

Summer
2012

So, Why restore coastal habitat?

• 
• 
• 
• 
• 

Investment in Natural Capital (self maintenance)
Increases Resilience (Climate Change is coming)
Improves functions of adjacent habitats
Reconnects public to local resources
Returns value to economy every year (no
depreciation)

•  $$ goes to hire more people (30 / $million)
–  RAE
Quantifying Ecosystem Services of
Restored Tidal Marshes
July 29-August 4, 2012
A Natural History Field
Seminar at Eagle Hill on
the Eastern Maine Coast

An Interactive, Intensive Seminar
with Susan C. Adamowicz and David Burdick

Humboldt Field Research
Institute
PO Box 9, Steuben, ME 04680-0009
207-546-2821, Fax 207-546-3042
office@eaglehill.us www.eaglehill.us

Information is available on . . .
• other natural history science seminars
• graduate and undergrad university credits
• continuing education units/recert. credits

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Why Restore Coastal Habitats?

  • 1. Why Restore Coastal Habitats? David M. Burdick Associate Research Professor Jackson Estuarine Laboratory Department of Natural Resources & the Environment University of New Hampshire Durham, NH 03824 david.burdick@unh.edu
  • 2. Why Restore Coastal Habitats? Outline 1)  2)  3)  4)  Habitats, Values and Threats, including Climate Change Impacts, Perception and Action Benefits, Ecosystem Services Case Study: Little River Marsh Take home messages
  • 3. Southeastern Masschusetts is endowed with a rich mosaic of coastal habitats Beaches and Dune Systems Photo: Sean Woods
  • 6. Shellfish Beds and Reefs Photo:
Nathan
Johnson, 
Orion
Photo
Produc3ons

  • 8. Rivers flowing into bays (estuaries)
  • 9. Functional values associated with these habitats: •  Plant growth to support grazing and detritus-based food webs •  •  •  •  •  •  Secondary production Plant structure to provide habitat Support of biodiversity Protection from flooding Protection from coastal erosion Removal of sediments and excess nutrients •  Aesthetic, Recreational & Educational values •  Self-sustaining ecosystems Courtesy, Bob Ulanowitz
  • 10. Functional values associated with these habitats: •  Plant growth to support food webs •  Secondary production, including finfish and shellfish Photo: Lawrence Taylor Plant structure to provide habitat Support of biodiversity Protection from flooding Protection from coastal erosion Removal of sediments and excess nutrients •  Aesthetic, Recreational & Educational values •  Self-sustaining ecosystems •  •  •  •  • 
  • 11. Functional values associated with these habitats: •  Plant growth to support food webs •  Secondary production •  Plant structure to provide habitat for nursery, refuge and foraging (dunes, tidal marshes, seagrass meadows, algal beds and artificial habitats) •  •  •  •  Support of biodiversity Protection from flooding Protection from coastal erosion Removal of sediments and excess nutrients •  Aesthetic, Recreational & Educational values •  Self-sustaining ecosystems
  • 12. Functional values associated with these habitats: •  Plant growth to support food webs •  Secondary production •  Plant structure to provide habitat •  Support of local and regional biodiversity Courtesy Joe Luczkovich •  Protection from flooding •  Protection from coastal erosion •  Removal of sediments and excess nutrients •  Aesthetic, Recreational & Educational values •  Self-sustaining ecosystems Courtesy Robert Buchsbaum
  • 13. Functional values associated with these habitats: •  •  •  •  Plant growth to support food webs Secondary production Plant structure to provide habitat Support of biodiversity •  Protection from flooding •  Protection from coastal erosion •  Removal of sediments and excess nutrients •  Aesthetic, Recreational & Educational values •  Self-sustaining ecosystems Photo: Dick Nicholson
  • 14. Functional values associated with these habitats: •  •  •  •  •  •  Plant growth to support food webs Secondary production Plant structure to provide habitat Support of biodiversity Protection from flooding Protection from coastal erosion •  Removal of sediments and excess nutrients (marshes, seagrasses) to increase habitat stability and improve water quality •  Aesthetic, Recreational & Educational values •  Self-sustaining ecosystems Photo: Sean Woods
  • 15. Functional values associated with these habitats: •  Plant growth to support food webs •  Secondary production •  Plant structure to provide habitat •  Support of biodiversity •  Protection from flooding •  Protection from coastal erosion •  Removal of sediments and excess nutrients Photo: Wellfleet Shellfish Dep’t. •  Aesthetic, Recreational & Educational values •  Self-sustaining ecosystems Photo: Fred Short
  • 16. Functional values associated with these habitats: •  Plant growth to support food webs •  Protection from flooding •  Secondary production •  Protection from coastal erosion •  Plant structure to provide habitat •  Removal of sediments and excess nutrients •  Support of biodiversity •  Aesthetic, Recreational & Educational values •  Self-sustaining ecosystems Photo: Sean Woods
  • 17. Processes that contribute to the Habitats: Coastal Features Coastal Processes Gulf of Maine Rivers C u s p Barrier Beach Eelgrass bed Salt Marsh Step Spit Inlet Fan S t o r m s Plate Tectonics Evolution US ACoE Glaciers Oceanic Currents Succession soils Gulf of Maine
  • 18. Processes that contribute to the Habitats: •  Primary Production •  Growth •  Herbivory •  Predation •  Decomposition •  Secondary Production Photo: Don DesJardin •  Migrations of fish (herring, eel, bass) and birds (terns)
  • 19. Processes that contribute to the Habitats: •  Complex Food Webs - a characteristic of a healthy diverse ecosystem - some have already lost complexity as a result of: Michael Moore –  –  –  –  Over-fishing and over-harvesting specific species Introductions of invasive non-native species Human alterations to the landscape Eutrophication Fred Short, UNH Wellfleet Shellfish Dep’t. Joe Luczkovich P. Erickson, MIT SeaGrant
  • 20. Threats to Ocean Resources: •  •  •  •  •  •  •  Overfishing Invasive species Pollution, especially runoff Habitat alteration Coastal development Aquaculture Climate change •  Pew Oceans Commission Restoration is about reversing the effects of all of these impacts
  • 21. Threats to Coastal Processes and Habitats •  Over- Fishing / Harvesting: examples Northern Right Whale; cod declines; bird and turtle eggs; scallops Photo: Lawrence Taylor Photo: Michael Moore
  • 22. Threats to Coastal Processes and Habitats •  Introductions of non-native, invasive species: codium, green crab, Japanese shore crab, others Photo: P. Erickson, MIT SeaGrant Photo: Ch. Schubart
  • 23. Threats to Coastal Processes and Habitats •  Pollution: Photo: Vincent DeWitt •  Contaminants (metals, organic pesticides) •  Bacterial Pathogens •  Nutrient over enrichment and the cascading effects of eutrophication Photo: Fred Short
  • 24. Threats to Coastal Processes and Habitats •  Human alteration of Habitat •  Restricting or blocking tidal exchange •  Interruption of sediment supply and transport •  Artificial Habitats Town of Wellfleet Web Site Courtesy Robert Buschbaum, MAS
  • 25. Threats to Coastal Processes and Habitats •  Human alteration of Habitat •  Restricting or blocking tidal exchange •  Interruption of sediment supply and transport (dredging, erosion control) •  Artificial Habitats - from development, aquaculture Photo: Sean Woods
  • 26. Threats to Coastal Processes and Habitats Climate Change Impacts (Tidal Marshes) •  Increased sea level – retreat of high marsh? •  Increased storm activity - Seaward edges will retreat •  Temperature increases - Vegetation Changes: •  Range expansions, loss of forb pannes? •  Increased rainfall •  Vegetation change due to Decreased salinity?
  • 27. Our Climate is Changing: Our Climate Continues to Change: Global: Surface temperatures +0.74°C Arctic temperatures 2X Snow and Ice: Snow cover decreasing Glaciers shrinking Arctic sea-ice decreasing Ice shelf losses Thermal expansion of the oceans: SLR has increased from 1.7 to 3.0 mm/yr
  • 28. Our LOCAL Climate is Changing: Seasons changing (shorter, warmer winters, ice-out sooner) More info at: http:/ /CarbonSolutionsNE.org
  • 29. Our LOCAL Climate is Changing: Local precipitation increased 20% since ’30s (42 in/year) Precipitation events larger Tomas (19th named storm in 2010) Mean Decadal Trend 1” Precipitation Events 1948-2007
  • 30. Adapting to Climate Change •  Increasing SLR threatens tidal wetlands –  Allow tidal marshes to grow with SLR in elevation –  Allow marshes to migrate landward (no barriers) from
Smith
2006

  • 31. What did we have? What are we left with? •  Depauperate system –  70% of tidal marshes, almost if not all with varying degrees of recurring human impacts –  Tiny bits of seagrass –  Shellfish beds overfished and predated by invasive species (green crab) –  Most rivers dammed, fish ladders have declining anadromous runs
  • 32. Impacts from tidal restrictions: • Loss of fisheries (esp. anadromous spp.) • Vegetation change • Subsidence • Exotic invaders • Mosquito problems • Loss of self-maintenance • Fish passage trophic export from: Portnoy, J. and M. Reynolds. 1997. Wellfleet’s Herring River: the case for habitat restoration. Environment Cape Cod 1:35-43.
  • 33. Nekton Production and Export: the Trophic Relay Ethan Nedeau, Biodrawversity
  • 34. Fish caught in minnow traps marked and released upstream and downstream of culverts young resident nekton adult resident nekton young transient nekton adult transient nekton Vegetated marsh Alyson Eberhardt et al. Intertidal channels Subtidal channels Open estuary Ocean
  • 35. Recapture results of fish marking study: Fish Passage Rate Passage rate 0.3 Restricted Restored Reference 0.2 0.1 y=-0.1558x+0.2478 r2=0.8517 p0.0001 0.0 0.0 0.2 0.4 0.6 0.8 1.0 1.2 1.4 1.6 Water velocity (m s-1) Alyson Eberhardt et al. 2011 1.8
  • 36. NEED: New functional indicators: Nekton Production and Export young resident nekton adult resident nekton young transient nekton adult transient nekton Vegetated marsh Alyson Eberhardt et al. 2011 Intertidal channels Subtidal channels Open estuary Ocean
  • 37. Why can’t we see the difference? •  Loss of connection to coastal resources –  Out of sight –  Don’t care •  Acceptance of environmental degradation •  Shifting Baselines http://www.shiftingbaselines.org/lenticulars/index.html –  ‘better than New Jersey’ –  We have more important things to deal with – its not broken . . . yet •  Change is cryptic removed from fundamental causes - increased runoff from impervious surfaces
  • 38. Why don’t we act? Loss of connection to coastal resources Acceptance of environmental degradation Shifting Baselines Change is cryptic and removed from fundamental causes •  Multiple Stable States: change to alternative state is sudden and difficult to reverse •  •  •  • 
  • 39. Why bother? •  Climate Change is coming, we must adapt •  So many attempts fail – but not all are equal –  Great track records for success: •  Tidal Marsh Restoration •  Dam Removal (e.g., Wiswall Dam) –  Fair to poor success / Room for improvement and learning: •  Shellfish Beds •  Seagrass Meadows
  • 40. So, keep the pressure on! •  New restorations of all kinds •  Integrate habitats
  • 41. So, keep the pressure on! •  New restorations of all kinds •  Integrate habitats
  • 43. So, keep the pressure on! •  New restorations of all kinds •  Integrate habitats •  Measure results –  Critical for Adaptive Management (site) –  Improve knowledge and future projects (regional) –  Share information (international) –  Demonstrate value •  Case Study: Little River Marsh
  • 46. Restoration can be costly – is it worth it? Assessment: Structural indices (hydrology, soils, vegetation, nekton) Goals: To restore natural functions To provide benefits or values to people -a disconnect
  • 47.
  • 48. Functional values associated with tidal marshes: •  Plant growth to support food webs •  Secondary production •  Plant structure to provide habitat •  Support of biodiversity •  Removal of sediments and excess nutrients •  Aesthetic, Recreational Educational values •  Protection from flooding •  Self-sustaining ecosystems •  Protection from coastal erosion •  Long term carbon storage
  • 49. Gulf of Maine “GPAC” Protocols •  Hydrology Tidal Signal (WL Recorders), Elevation •  Soils and Sediments Salinity (and Sulfide, Eh, %C, accretion) •  Vegetation Abundance, Composition, Invasive spp, Ht. •  Nekton ID, Density, Length, Biomass, Richness •  Birds Abundance, Richness, Behavior Neckles et al. 2002. Restoration Ecology. 10(3) :556-563. Konisky et al. 2004.
  • 50. RPI – An Evaluation Tool Reference Marsh Value Restoration Restoration Trajectory Starting Point Calculates % Change towards Reference /Project Goal Normalizes actual data into a relative index score
  • 51. Value of Tidal Marsh Ecosystem Services per Annum per Hectare •  •  •  •  Costanza et al. 1987: $9,900 In 2008 $ (Gedan et al. 2009): $14,400 Carbon sequestration (European market): $135 Denitrification (Piehler and Smyth 2011): $6,128
  • 53. RPI Scores for Little River Marsh Calcula3on
of
Value
of
Net
Benefits
from
Ecosystem
Services
 RPI
=
0.91
in
Year
7;

 Value
lost
due
to
impacts
from
Bdal
restricBon
=
41%
 Year
7
value
relaBve
to
reference
marsh
=
0.91%
 SO
.
.
Restored
benefits
=
$14,
400/ha
*
0.41
*
0.91
*
70
ha
 





































=
$376,000

  • 54. RPI Calculations for Little River Marsh
  • 55. OVER first 5 years (2001-2005) = $1.2 million OVER next 6 years (2006-2011) = $2.2 million Cost $1.3 million From: Chapter 15: Tidal
RestoraBon:
a 
Synthesis
of
Science 
and
Management
 Charles
Roman


 David
Burdick,
editors
 ISLAND
PRESSS
 Summer
2012

  • 56. So, Why restore coastal habitat? •  •  •  •  •  Investment in Natural Capital (self maintenance) Increases Resilience (Climate Change is coming) Improves functions of adjacent habitats Reconnects public to local resources Returns value to economy every year (no depreciation) •  $$ goes to hire more people (30 / $million) –  RAE
  • 57. Quantifying Ecosystem Services of Restored Tidal Marshes July 29-August 4, 2012 A Natural History Field Seminar at Eagle Hill on the Eastern Maine Coast An Interactive, Intensive Seminar with Susan C. Adamowicz and David Burdick Humboldt Field Research Institute PO Box 9, Steuben, ME 04680-0009 207-546-2821, Fax 207-546-3042 office@eaglehill.us www.eaglehill.us Information is available on . . . • other natural history science seminars • graduate and undergrad university credits • continuing education units/recert. credits