Climate change futures: health, ecological and economic dimensions
Climate change futures: health, ecological and economic dimensions
Climate change futures: health, ecological and economic dimensions
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CASE STUDIES 84 | NATURAL AND MANAGED SYSTEMS<br />
Dermo disease caused extensive oyster mortalities in<br />
the Gulf of Mexico in the late 1940s. Later, it caused<br />
chronic <strong>and</strong> occasionally massive mortalities in the<br />
Chesapeake Bay. Since 1990, Dermo has been<br />
detected in Delaware Bay, Long Isl<strong>and</strong> Sound,<br />
Massachusetts, Rhode Isl<strong>and</strong> <strong>and</strong> Maine.<br />
MSX (multi-nucleated spore unknown) is now known to<br />
be caused by the parasite Haplospordium nelsoni.<br />
MSX caused massive oyster mortalities in Delaware<br />
Bay in 1957 <strong>and</strong> two years later in Chesapeake Bay.<br />
The parasite has been found from Florida to Maine,<br />
but has not been associated with mortalities in all<br />
areas. MSX was found in oysters from Connecticut<br />
waters 30 years ago. MSX disease is suppressed by<br />
low salinities <strong>and</strong> low temperatures. As described by<br />
the Connecticut Department of Agriculture, there is low<br />
oyster mortality during the winter months <strong>and</strong> the<br />
prevalence <strong>and</strong> intensity of the disease decreases. A<br />
second mortality period occurs in late winter <strong>and</strong> early<br />
spring (Ford <strong>and</strong> Tripp 1996).<br />
THE ROLE OF CLIMATE<br />
As with human diseases, the sequential occurrence of<br />
events, such as a warm winter followed by a warm,<br />
dry summer, can result in disease prevalence <strong>and</strong><br />
intensities greater than normal (Hofmann et al. 2001).<br />
The intensification of Dermo disease coincided with a<br />
period of sustained drought, diminished freshwater<br />
inflow to the Chesapeake Bay, <strong>and</strong> warmer winters.<br />
The drought <strong>and</strong> warmer temperatures, which cause<br />
increased evaporation, combined with the reduced<br />
freshwater input, resulted in increased salinity of the<br />
Bay waters. The increased salinity allowed the disease-causing<br />
parasite to increase in prevalence <strong>and</strong><br />
intensity. The milder winters allowed the parasite to survive<br />
<strong>and</strong> remain at high levels in the oyster population.<br />
Reduction <strong>and</strong>/or cessation in harvesting pressure<br />
have not resulted in significant recovery of the stocks.<br />
The mitigation strategies were too late <strong>and</strong> did not<br />
anticipate the increase <strong>and</strong> spread of Dermo disease<br />
that has occurred as the climate has warmed.<br />
NORTHWARD MOVEMENT<br />
From the late 1940s when Dermo disease was first<br />
identified (Mackin et al. 1950) until the 1990s,<br />
Dermo disease was found primarily from Chesapeake<br />
Bay south along the Atlantic coast of the United States<br />
<strong>and</strong> into the Gulf of Mexico. In 1990 <strong>and</strong> 1991 the<br />
parasite causing this disease was found in locations<br />
from Delaware Bay, NJ, to Cape Cod, MA. It is now<br />
found in oyster populations in Maine <strong>and</strong> southern<br />
Canada, where it has caused epizootics (epidemics<br />
among animals — in this case, shellfish) that have devastated<br />
oyster populations <strong>and</strong> the oyster fishery.<br />
Several hypotheses have been suggested for the<br />
observed expansion in range of this disease. The one<br />
that is most consistent with the available evidence is<br />
that this parasite was introduced into various northern<br />
locations where it remained at low levels until the<br />
recent warming climate allowed it to proliferate (Ford<br />
1996). In particular, above-average winter temperatures<br />
during the 1990s along the eastern United States<br />
<strong>and</strong> Canada (Easterling et al. 1997) have allowed<br />
the parasite that causes Dermo disease to become<br />
established (Ford 1996; Cook et al. 1998). Also, the<br />
interannual variation in prevalence <strong>and</strong> intensity of<br />
Dermo disease in oysters along the Gulf of Mexico<br />
has been shown to be related to shifts in the ENSO<br />
cycle (Kim <strong>and</strong> Powell 1998), also an indication that<br />
climate is a strong contributor. This relationship arises<br />
through <strong>change</strong>s in temperature <strong>and</strong> salinity that result<br />
from the ENSO cycle, which directly affect Perkinsus<br />
marinus growth <strong>and</strong> development. The disease is much<br />
more intense <strong>and</strong> prevalent throughout the Gulf of<br />
Mexico during La Niña events, which produce warmer<br />
<strong>and</strong> drier conditions <strong>and</strong> often drought (Kim <strong>and</strong><br />
Powell 1998).<br />
HEALTH AND ECOLOGICAL IMPACTS<br />
Oysters <strong>and</strong> other bivalves (clams <strong>and</strong> mussels), in<br />
addition to serving as food for humans <strong>and</strong> shorebirds,<br />
are filter-feeders. Each oyster can pull in many gallons<br />
of water a day, filtering out the nutrients <strong>and</strong> plankton<br />
for its own nourishment. In this way, they provide a critical<br />
<strong>ecological</strong> service: controlling the nutrient <strong>and</strong><br />
algae level in bays <strong>and</strong> estuaries. Without bivalves,<br />
these coastal waters would turn murky, <strong>and</strong> contaminated,<br />
<strong>and</strong> algal mats would create hypoxic or anoxic<br />
conditions. Such waters become less productive for<br />
fish, shellfish <strong>and</strong> sea grasses that support the fish, <strong>and</strong><br />
shellfish can die off <strong>and</strong> the few fish left tend to