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Project Description:
Human-induced
changes in the world’s natural ecosystems have caused
unprecedented declines in species and genetic diversity, leading to
declines in
ecosystem health including their
capacity to cope with environmental
fluctuations. Such declines are especially prevalent in
estuaries such as the
Chesapeake Bay where reductions of submersed aquatic vegetation (SAV)
abunda nce
have
both been caused by and led to declines in water quality and associated
fisheries. SAV cover has increased substantially in recent years but is
still only a fraction of the 80,000 hectares that are estimated to have
existed before Hurricane Agnes in 1972 (see right; data from Virginia
Institute of Marine Science). The far-reaching consequences of SAV
decline have focused attention
on effective ways of restoring the Bay’s living resources.
Resulting
restoration efforts of SAV in the Chesapeake Bay have been impressive;
however,
success has been undeniably mixed and is leading us to ask what
role genetic
diversity and sources of restoration stock may have in enhancing
restoration
success and long-term health of the Bay’s resources.
Background:
When degraded areas are
restored, they should
contain an adequate species complement to withstand environmental
fluctuations.
All available evidence indicates that it is equally important to
preserve
genetic diversity within species in conservation and restoration
efforts. Recent
modeling efforts indicate that
genotypic diversity within species allows individuals to occupy
different
niches and promotes species coexistence and thus community diversity (Vellend 2006).
These
modeling results are supported by empirical evidence that genotypes of Zostera marina showed differential
resistance to herbivory by geese (Hughes & Stachowicz
2004) and V.
americana genotypes have differential tolerance of pollutants
(Biernacki &
Lovett-Doust 1997). Our project explores three
levels of genetic
diversity that may be important in conferring a greater chance that a
restoration
effort will be successful:
levels of inbreeding within
individuals, levels of diversity among individuals (e.g.,
numbers of alleles, genotypes, and phenotypes),
and the adaptation of individuals to local environments.

We focus on V.
americana because it was once a dominant species in the
Chesapeake Bay, it
is considered an important food resource for wildfowl, it does not interfere
with recreational uses of waterways, and it is used in restoring
freshwater
portions of the Bay by a variety of
groups. As with many aquatic species, V.
americana is a dioecious submersed aquatic macrophyte that is capable
of
both clonal growth and sexual reproduction with vegetative expansion often
being the dominant form of propagation.
It is not known how past population
bottlenecks and restoration activities may have affected the natural
genetic
diversity of freshwater SAV growing in the Chesapeake Bay. However,
this
information is needed to effectively monitor the health of this
important
living resource which is not stable from year to year and can
conceivably
re-enter a period of decline if environmental conditions worsen due to
unforeseen weather events. The amount and structure of genetic
diversity within
and among populations of V. americana
in the Chesapeake Bay will depend on a combination of relative amounts
of
vegetative versus sexual reproduction, patterns of seed dispersal,
nature of a
seed bank, and population history.
Predictions:
Without
considering genetic diversity when selecting restoration stock,
a nursery
may mass-produce one or a few clones from one site that are then used
to restore areas throughout the Bay.
This may cause restoration efforts to fail
if that clone is not adapted to grow at many of the planting sites. Even if restoration is
successful in the
short-term, environmental fluctuations or directional change may cause
all
restored populations to catastrophically fail if populations cannot
adapt to
the new conditions. Taking these issues into consideration, we predict
that
genetic diversity plays a role in the chances of restoration success.
Specifically we predict that 1) individuals with higher levels of
heterozygosity will have higher rates of survival and growth than
highly
homozygous individuals; 2)
genotypically diverse plantings will have higher survival and growth
rates than
monotypic stands; and 3) propagules that are collected close to the
planting
sites will have higher survival and growth rates than propagules
collected from
more distant locations. Testing
these
predictions will allow us to make recommendations to restoration
agencies managing
natural resources in the Chesapeake Bay, and in coastal ecosystems in
general,
how and when it is important to consider to genetic diversity when
restoring
SAV beds.
Biernacki, M., and J.
Lovett-Doust. 1997.
Vallisneria americana (Hydrocharitaceae) as a biomonitor of aquatic
ecosystems:
Comparison of cloned genotypes. American Journal of Botany 84:1743-1751.
Hughes, A. R., and J. J.
Stachowicz. 2004.
Genetic diversity enhances the resistance of a seagrass ecosystem to
disturbance. Proceedings of the National Academy of Sciences of the
United
States of America 101:8998-9002.
Vellend, M. 2006. The
consequences of genetic
diversity in competitive communities. Ecology 87:304-311.
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