Transcript Document

OPTIMAL STRATEGIES FOR ECOLOGICAL RESTORATION UNDER CLIMATE CHANGE
Koel Ghosh, James S. Shortle, and Carl Hershner *
Agricultural Economics and Rural Sociology, Pennsylvania State University
* Center for Coastal Resources Management, Virginia Institute of Marine Science
A Introduction
B Purpose of Study
Natural ecosystems like forest, wilderness, and
wetlands provide valuable habitat and ecological
services intimately linked with sustenance of life
on earth. The survival of species depends on the
availability of migration corridors and the
existence or emergence of suitable habitats.
Climate change will affect fundamental
ecological processes and the spatial distribution
of terrestrial and aquatic species. A crucial issue
in facilitating ecosystem adaptation to climate
change is managing land use and landscapes to
preserve migration corridors and potentially
emergent habitats.
The study determines optimal
strategies for natural resource
adaptation under climate
change using the Submerged
Aquatic Vegetation (SAV)
Restoration Program in the
lower Chesapeake Bay as a
case study.
E Study Region
Fig. 5: The study region is Hampton Roads in southeast Virginia. The right-hand
map divides the region into segments for the study.
CASE STUDY
C Submerged Aquatic Vegetation
F Methodology Steps
The diverse assembly of underwater grasses
found in the shallow water of the Chesapeake
bay are called Submerged Aquatic Vegetation
(SAV). SAV provides important habitat for the
fish and shellfish population of the bay and
contributes to improving water quality by
removing excess nutrients.
Fig. 1: Eelgrass (Zostera marina)
dominates the lower Chesapeake Bay.
The increased nutrient and sediment input from
development in the surrounding watershed
resulted in a dramatic bay wide decline in all
SAV species in the late 1960’s and 1970’s.
Compared to historical estimates of 200,000
acres, a 1984 aerial survey of the bay
documented only 38,000 acres—prompting a
SAV restoration plan that would ensure the
future of SAV in the Chesapeake Bay.
1. Understand the impact of sea-level rise on existing SAV and future SAV
restoration opportunities.
2. Identify adaptation strategies for SAV restoration under climate change-strategies are a portfolio of choices regarding extent of restoration at current
sites and future sites.
3. Account for uncertainty in future sea-level rise. This is done by considering
alternative scenarios of sea-level rise that can occur in the future. Associated
with each state is the likelihood of that state occurring.
4. Account for the social cost of other land and water uses excluded by SAV
restoration.
5. Bring it all together in a mathematical model.
6. Solve the model using Discrete Stochastic Programming (DSP).
Fig. 2: The blue crab, symbolic of the life
and culture in the Chesapeake Bay region,
uses the bay grass beds as nursery area.
D Climate Change and SAV restoration
• The distribution of SAV is influenced by salinity, temperature, light penetration, water
depth, water wave and current actions, and bottom sediment. Climate change can affect
any of these conditions, either by itself or by interacting with other environmental
stressors.
• This study looks at the impact of climate-induced sea-level rise on SAV distribution and
restoration opportunities. Sea level rise will alter the water depth at current SAV sites.
Existing SAV will migrate from the deeper waters to the shallower waters near the shore.
• As the sea moves inland, current tidal marshes on the coast may become suitable as SAV
growing sites.
• There is incomplete information regarding both the magnitude and the likelihood of sealevel rise. These uncertainties must be reflected in the methodological framework.
G Data
Bathymetry maps
points of equal water
depth. Data was
obtained by combining
bathymetry information
(from the Chesapeake
Bay Program) with GIS
data coverage of
current and historic
SAV, suitable shellfish
aquaculture area, and
tidal marsh inventory
data (from Virginia
Institute of Marine
Science) in GIS
software ArcInfo.
Fig. 4: The bathymetry bands and coverage area of existing SAV, historic SAV,
tidal marshlands, and aquaculture suitable areas are shown for segment 6.
MHW:Mean High Water
MTL: Mean Tide Level
H Usefulness of the study
MLW: Mean Low Water
T: Low Tide
L: Light
Fig.3: The suitable water depth for SAV is below the low tide line (T) to about 2 meters in depth (L). The SAV
fringe (arrow) decreases as the tidal range increases with sea-level rise. Source: Chesapeake Bay Program
1. This methodological framework also can be used for research on the
economics of planned ecosystem adaptation to climate change (in
addition to SAV).
2. The study is of practical value as it will aid Chesapeake Bay region
planners in evaluating ecological restoration strategies and
developing forward-looking land-use plans that enhance autonomous
adaptability of marine ecosystems.
Acknowledgements:1. Support is provided by the Global Change Research Program, Office of Research and Development, U.S. Environmental Protection Agency (Cooperative
Agreement R-83053301). 2. Tamia Rudnicky at Virginia Institute of Marine Science helped organize the GIS data for the analysis.