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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

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