Conserving Freshwater and Coastal Resources in a Changing Climate
Conserving Freshwater and Coastal Resources in a Changing Climate
Conserving Freshwater and Coastal Resources in a Changing Climate
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Photography by Avi Hesterman<br />
lake is remixed <strong>in</strong> late fall. If a lake bottom conta<strong>in</strong>s a<br />
greater amount of rott<strong>in</strong>g biomass, oxygen depletion occurs<br />
more rapidly (Kevern et al., 1996).<br />
There is a balance between spr<strong>in</strong>g mix<strong>in</strong>g, fall mix<strong>in</strong>g<br />
<strong>and</strong> summer stratification. If the summer stratification<br />
period lasts too long, summerkill can occur, where<br />
higher mortality <strong>and</strong> lower production rates can lead to<br />
fish deletion from a lake (Fang et al., 2004). As w<strong>in</strong>ters<br />
get shorter with a chang<strong>in</strong>g climate, spr<strong>in</strong>g remix<strong>in</strong>g<br />
occurs earlier which leads to a longer period of summer<br />
stratification <strong>and</strong> <strong>in</strong>creased risk of oxygen depletion <strong>and</strong><br />
deep-water dead zones (Kl<strong>in</strong>g et al., 2005).<br />
Shift<strong>in</strong>g Thermal Regions<br />
As water temperatures change, lake habitats will change<br />
<strong>in</strong> their ability to support aquatic life. Fish depend on specific<br />
ranges of temperature with<strong>in</strong> which physiological<br />
functions, such as growth, activity, <strong>and</strong> swimm<strong>in</strong>g performance,<br />
are maximized. In some <strong>in</strong>stances, a specific<br />
life stage will have an optimum temperature (Coutant,<br />
1990), especially the reproductive stages. Cold-water<br />
fish have a niche centered around 15° C, cool-water<br />
fish around 24° C, <strong>and</strong> warm-water fish around 28° C<br />
(Shuter & Meisner, 1992). When optimum temperatures<br />
are not available, fish will move to the best alternative<br />
conditions, a change that may result <strong>in</strong> a decrease <strong>in</strong><br />
metabolic efficiency (Coutant, 1990).<br />
Changes <strong>in</strong> thermal habitats are not uniform across<br />
lake types. Very large lakes like the Great Lakes that<br />
are deep <strong>and</strong> large are anticipated to experience an <strong>in</strong>crease<br />
<strong>in</strong> suitable thermal habitats for all species with<br />
an <strong>in</strong>crease of temperature. This is because there will<br />
be <strong>in</strong>creased areas of warmer waters while the fish <strong>and</strong><br />
other species <strong>in</strong> the deeper layers of water will benefit<br />
from the slight warm<strong>in</strong>g. In smaller,<br />
shallower lakes the warmer water<br />
will reduce the habitat available for<br />
cold water fish (Poff, et al., 2002).<br />
In a comprehensive series of<br />
studies that looked at 27 lake types<br />
<strong>in</strong> 209 locations <strong>in</strong> the cont<strong>in</strong>ental<br />
United States, Fang et al. evaluated the<br />
differ<strong>in</strong>g effects of chang<strong>in</strong>g thermal<br />
niches on warm, cool, <strong>and</strong> cold-water<br />
fish (2004a, b & c). The number of<br />
locations that can support cold-water<br />
fish (five types of salmon, four types<br />
of trout <strong>and</strong> one variety of whitefish)<br />
habitat is projected to decrease by<br />
38%, result<strong>in</strong>g <strong>in</strong> fewer lakes able to<br />
support cold water fish. Additionally,<br />
the area of lakes that cannot support<br />
cold-water fish is expected to extend significantly further<br />
north (Fang et al., 2004b).<br />
The study found that for lakes of medium depth <strong>and</strong><br />
size, warm-water fish (four species of bass, shad, carp<br />
<strong>and</strong> catfish among others) could survive <strong>in</strong> all 209 locations<br />
despite potential <strong>in</strong>creases <strong>in</strong> temperature. Some<br />
lakes <strong>in</strong> the south central <strong>and</strong> southeastern United States<br />
are expected to experience a loss of cool-water fish due<br />
to <strong>in</strong>creased summerkill, the highest percentage of<br />
which will occur <strong>in</strong> shallow lakes (Fang et al., 2004a).<br />
Lower Lake Levels<br />
Earlier runoff, <strong>in</strong>creased evaporation, <strong>and</strong> changes <strong>in</strong><br />
stream <strong>in</strong> flow are predicted to lower lake levels <strong>in</strong> the<br />
mid-Atlantic <strong>and</strong> northeastern United States (Kl<strong>in</strong>g et<br />
al., 2005). Even large lake systems, like the Great Lakes,<br />
may experience decreased lake levels that are greater<br />
<strong>in</strong> magnitude than the anticipated rate of sea level rise.<br />
Issues related to permanent lower<strong>in</strong>g of lake levels<br />
<strong>in</strong>clude isolation of lake-fr<strong>in</strong>g<strong>in</strong>g wetl<strong>and</strong>s, possibly<br />
17<br />
<strong>Conserv<strong>in</strong>g</strong> <strong>Freshwater</strong> <strong>and</strong> <strong>Coastal</strong> <strong>Resources</strong> <strong>in</strong> a Chang<strong>in</strong>g <strong>Climate</strong>