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2015 <strong>Puget</strong> <strong>Sound</strong> Factbook Book | v3.0<br />
breakwaters/jetties, overwater structures, roads within 25 m of <strong>the</strong> shoreline, active &<br />
inactive railroads within 25 m of <strong>the</strong> shoreline.<br />
a. Only 31.3% of <strong>the</strong> length of <strong>Puget</strong> <strong>Sound</strong>’s shoreline has not been modified (i.e.,<br />
none of <strong>the</strong> stressors occurs) (Fresh et al., 2011).<br />
b. Negligible historically, artificial shoreline now represents about 9.5% of <strong>the</strong><br />
shoreline (Fresh et al., 2011).<br />
4. Armoring is clearly <strong>the</strong> most frequently occurring stressor, observed in along 74–78% of<br />
shoreline segments studied (Fresh et al., 2011), followed by nearshore fill (62%) and<br />
overwater structures (30%) (Schlenger et al., 2011).<br />
a. Armoring occurs along 27% of <strong>the</strong> length of <strong>the</strong> shoreline (1070 of 3969 km)<br />
(Schlenger et al., 2011).<br />
b. The percent of armored shoreline varies considerably (10 to 63 percent) across<br />
<strong>the</strong> sub-basins in <strong>the</strong> study area (Schlenger et al., 2011).<br />
5. An estimated 34.6% of shorelines lack natural vegetation (Simenstad et al., 2011).<br />
a. Riparian vegetation overhanging <strong>the</strong> intertidal zone occurs along only 440 miles<br />
of <strong>the</strong> shoreline of <strong>Puget</strong> <strong>Sound</strong> (Clancy et al., 2009).<br />
b. Loss of overhanging vegetation can alter <strong>the</strong> microclimate of beaches for<br />
incubating eggs of intertidal spawning fish (Rice, 2006).<br />
c. Loss of vegetation reduces <strong>the</strong> supply of terrestrial insects falling into nearshore<br />
waters, an important food source for migrating juvenile salmonids (Brennan &<br />
Culverwell, 2004).<br />
6. Fragmentation of nearshore marine habitat by frequent separate smaller anthropogenic<br />
shoreline alterations can reduce biological productivity beyond <strong>the</strong> effects of fewer but<br />
larger alterations (Gaydos et al., 2009).<br />
7. The South Central <strong>Puget</strong> <strong>Sound</strong> sub-basin is <strong>the</strong> most impacted sub-basin in <strong>the</strong> <strong>Puget</strong><br />
<strong>Sound</strong> Basin, with 51% of <strong>the</strong> nearshore zone area developed (Schlenger et al., 2011).<br />
a. Only 1% of <strong>the</strong> shoreline segments in this sub-basin had not been modified (Fresh<br />
et al., 2011).<br />
b. The Hood Canal sub-basin is <strong>the</strong> least impacted, with 10 percent of <strong>the</strong> nearshore<br />
zone area developed (Schlenger et al., 2011).<br />
8. Projections suggest that approximately 19 % of nearshore segments studied in <strong>Puget</strong><br />
<strong>Sound</strong> will become more degraded in <strong>the</strong> future (Schlenger et al., 2011). The segments<br />
forecast to degrade comprise 20 % of <strong>the</strong> shoreline length.<br />
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