Central Pacific coastal forests
The Central Pacific coastal forests stretch from southern Oregon in the USA to the northern tip of Vancouver Island, Canada. Chief habitats of this varied ecoregion include a mosaic of sea stacks, sandy beaches, rocky coastal cliffs, coastal headlands, tidepools, mudflats, salt marshes, estuaries, streams, various sized rivers , grass balds and a gamut of forest types.
There are a total of 324 vertebrate taxa recorded in the ecoregion, implying a modest level of faunal species richness. The Pacific coastal coniferous forests are classified within the Temperate Coniferous Forests biome, and also designated as ecoregion NA0510. The Columbia River is the river of largest volume that drains the Central Pacific coastal forests.
Influenced by cool moist air from the ocean, the Central Pacific coastal forests experience frequent clouds and fog, with most precipitation occurring in the winter. Generally, precipitation is greater in the western half of the ecoregion. Annual rainfall ranges from 2000 to 4080 millimeters, with higher coastal mountain areas receiving the highest of this precipitation. Mean annual temperature is around 13°C. Vancouver Island, for example, experiences a mean annual temperature of 8.5°C, averaging 13.5°C in the summer, and 3.5°C in the winter. The climate on the island is marked by warm summers and mild winters, being one of the mildest areas in Canada. Rainfall varies between 1500 and 3500 mm per year. Precipitation in the eastern side of the island ranges from 800 to 2500 mm per year. Climate in this ecoregion is a combination of alpine, subalpine, and maritime south Pacific Cordilleran.
The forests of the Central Pacific Coast are among the most productive in the world, characterized by large trees, substantial woody debris, luxuriant growths of mosses and lichens, and abundant ferns and herbs on the forest floor. The major forest complex consists of Douglas-fir (Pseudotsuga menziesii) and Western hemlock (Tsuga heterophylla), encompassing seral forests dominated by Douglas-fir and massive old-growth forests of Douglas-fir, Western hemlock, Western red cedar (Thuja plicata), and other species. These forests occur from sea level up to elevations of 700-1000 meters in the Coast Range and Olympic Mountains. Such forests occupy a gamut of environments with variable composition and structure and includes such other species as Grand fir (Abies grandis), Sitka spruce (Picea sitchensis), and Western white pine (Pinus monticola).
On Vancouver Island, low-elevation coastal forest cover includes stands of Western hemlock, Douglas-fir and Pacific silver fir (Abies amabilis). Western hemlock, Douglas-fir and Grand fir characterize most forests of eastern Vancouver Island. Drier sites support stands of Western hemlock and Western red cedar. The driest areas in eastern Vancouver Island are comprised of mixed stands of Douglas-fir and Western hemlock with occasional Garry oak (Quercus garryana), Pacific dogwood (Cornus nuttallii) and Pacific madrone (Arbutus menziesii). The subalpine forests are composed of Mountain hemlock (T. mertensiana) and Pacific silver fir, with some Yellow cedar (Chamaecyparis nootkatensis) and Western hemlock in high elevation areas in eastern Vancouver Island.
Coastal areas of British Columbia are best characterized as hydro-riparian forest ecosystems, such that the hydrologic cycle is the most important ecological process influencing forest dynamics. High winds, sea salt spray and fog strongly influence forest dynamics. Fires are not as important as in other areas.
Although Douglas-fir is the most abundant tree taxon at lower elevations in the region, Western hemlock is the chief climax species. Douglas-fir typically dominates young forest because of its relatively large and hardy seedlings and rapid growth rate. Western hemlock and several other species of fir are more tolerant of shade, however, and in mature forest Douglas-fir cannot regenerate appreciably.
While hemlock and fir dominate much of the ecoregion, the cool, wet conditions along the coast create a narrow band of forests distinguished by Sitka spruce. With its high tolerance of salt spray, in areas near the ocean Sitka spruce may form nearly pure forests or co-dominate with Lodgepole pine (Pinus contorta). The Sitka spruce zone–in which hemlocks also occur in large numbers–may be only a few kilometers in width and generally occurs below 150 meters. Where mountains abut the coast, however, Sitka spruce forests may extend up to 600 m. The alluvial rainforests of the western Olympic Peninsula are outstanding examples of the spruce-hemlock forest.
Riparian forests of this ecoregion are quite distinct from the Douglas-fir/hemlock forests. Broadleaf species such as black cottonwood (Populus trichocarpa) and red alder (Alnus rubra) replace the otherwise ubiquitous conifers along the many rivers and streams of the Pacific Northwest. Occasional grasslands, sand dune, and strand communities, rush meadows and marshes, and Western red cedar and alder swamps, these last often formed by beaver activity, breaking up the conifer forests.
The Central Pacific coastal forests are among the richest temperate coniferous forests in North America for amphibians and birds. Gray’s Harbor in Washington, for example, is a critical migratory stopover site for shorebirds. Rare and endangered species found in this ecoregion include California condor (Gymnogyps californianus), Hoary elfin butterfly (Incisalia polios obscurus), Seashore plantain (Plantago macrocarpa), and possibly the Pacific fisher (Martes pennanti).
Other characteristic wildlife include Elk (Cervus elaphus), Black-tailed Deer (Odocoileus hemionus), Coyote (Canis latrans), Black Bear (Ursus americanus), Mink (Mustela vison), and Raccoon (Procyon lotor).
The following anuran species occur in the Central Pacific coastal forests: Coastal tailed frog (Ascaphus truei); Oregon spotted frog (Rana pretiosa VU); Northern red-legged frog (Rana pretiosa); Pacific chorus frog (Pseudacris regilla); Cascade frog (Rana cascadae NT), generally restricted to the Cascade Range from northern Washington to the California border; Foothill yellow-legged frog (Rana boylii) and the Western toad (Anaxyrus boreas NT). A newt found in the ecoregion is the Rough skinned newt (Taricha granulosa).
Salamanders within the ecoregion are: Del Norte salamander (Plethodon elongatus NT); Van Dyke's salamander (Plethodon vandykei); Western redback salamander (Plethodon vehiculum); Northwestern salamander (Ambystoma gracile); Olympic torrent salamander (Rhyacotriton olympicus VU), whose preferred habitat is along richly leafed stream edges; Long-toed salamander (Ambystoma macrodactylum), whose adults are always subterranean except during the breeding season; Dunn's salamander (Plethodon dunni), usually found in seeps and stream splash zones; Clouded salamander (Aneides ferreus NT), an aggressive insectivore; Monterey ensatina (Ensatina eschscholtzii), usually found in thermally insulated micro-habitats such as under logs and rocks; Pacific giant salamander (Dicamptodon tenebrosus), found in damp, dense forests near streams; and Cope's giant salamander (Dicamptodon copei), usually found in rapidly flowing waters on the Olympic Peninsula and Cascade Range.
There are a small number of reptilian taxa that are observed within this forested ecoregion, including: Pacific pond turtle (Emys marmorata); Common garter snake (Thamnophis sirtalis), an adaptable snake most often found near water; Northern alligator lizard (Elgaria coerulea); and the Western fence lizard.
Numerous avian species are found in the ecoregion, both resident and migratory. Example taxa occurring here are the Belted kingfisher (Megaceryle alcyon); Wild turkey (Meleagris gallopavo); and the White-headed woodpecker (Picoides albolarvatus) and the Trumpeter swan (Cygnus buccinator), the largest of the North American waterfowl. Also found here are Grouse (Dendragapus spp.), and a range of seabirds, shorebirds and waterfowl.
Human activity, particularly clearcut logging, plantation forestry, road building, agriculture, and development have heavily altered the Central Pacific coastal forests. Only about four percent of the region remains as intact habitat. Some ecosystem types, such as the coastal temperate rain forests in Oregon, have been virtually destroyed.
Remaining blocks of intact habitat
Several relatively large blocks of more or less intact habitat remain, as do a number of smaller patches. Important blocks include:
- Strathcona Provincial Park - southwestern British Columbia - 2,193 square kilometers (km2)
- Olympic National Park - northwestern Washington - 1,200 km2 (assuming that roughly half the park is forested) N.B.: Forests at the upper elevations of the park are Cascadian in nature and fall within the North Cascades Forest Ecoregion.
- Brooks Peninsula Provincial Park - southwestern British Columbia - 380 km2
- Tahsish watershed - southwestern British Columbia
Degree of Fragmentation
Degree of Protection
The only protected habitats in this ecoregion are in national and provincial parks. Several of those protected areas, however, are relatively large and contain undisturbed forests. Human activities have significantly altered nearly all habitats outside the parks.
- Olympic National Park - northwestern Washington
- Strathcona Provincial Park - southwestern British Columbia - 2193.04 km2
- Pacific Rim National Park - southwestern British Columbia - 499.6 km2
- Checleset Bay Ecological Reserve - southwestern British Columbia - 346.5 km2
- Brooks Peninsula Provincial Recreation Park - southwestern British Columbia - 287.8 km2
- Pacific Rim-West Coast Trail National Park - southwestern British Columbia - 263.3 km2
- Megin Watershed Provincial Park - southwestern British Columbia - 213 km2
- Brooks-Nasparti Provincial Park - southwestern British Columbia - 212.98 km2
- Cape Scott Provincial Park - southwestern British Columbia - 150.7 km2
- Pacific Rim - Broken Islands Group National Park - southwestern British Columbia - 106.5 km2
- Tahshish - Kwois Provincial Park - southwestern British Columbia - 106.27 km2
Type and severity of threats
Little intact habitat remains outside national and provincial parks that conversion of the Central Pacific Coastal Forests has ceased to be an important issue for conservationists. Degradation from water pollution, overgrazing, burning, introduced species, road building, and excessive recreational impacts is causing significant mortality in some native plant communities.
Priority activities to enhance biodiversity conservation
- Establish protected areas where ecological gaps remain in the protected areas system, for example, in Clayoquot Sound.
- Extend Olympic National Park to connect coastal and upland sections.
The following areas in the Oregon Coast Range are high priorities for protection and restoration. All require consolidation, road closures, and revegetation. These areas contain substantial old-growth and other late-successional forests, are of high value to fisheries and aquatic biodiversity, support numerous spotted owl (Strix occidentalis) nesting sites, and form important natural linkages in a network of significant sites:
- Cummins Creek/Rock Creek - 427 km2
- Drift Creek - 229 km2
- Mount Hebo/Nestucca River - 506 km2
- Mary’s Peak/Grass Mountain - 141 km2
- Elliott State Forest - 364 km2
These five areas are among 31 proposed high priority reserves that together cover 5065 km2, or over 23 percent of the Oregon Coast Range Bioregion. The high priority reserves by themselves are too small to conserve viable populations of wide ranging species or to maintain natural disturbance regimes. The high priority areas must be linked and insulated by reserves under slightly less strict protection and by multiple-use buffer zones. Together, these three classes of reserves would form a continuous network through the Coast Range.
- More protected areas are required that represent the middle and lower elevation coastal rainforest communities.
- Proper enforcement of the British Columbia Forest Practices Code is required. Further damage to remaining salmon (Oncorhynchus spp.) habitat must be avoided and other riparian habitats restored.
- Canadian Parks and Wilderness Society, British Columbia Chapter
- Clayoquot Biosphere Project
- Friends of Ecological Reserves
- Friends of Strathcona Park
- Friends of the Stikine
- Islands Trust
- The Nature Conservancy, British Columbia
- Nature Trust of British Columbia
- Northwest Wildlife Preservation Society
- Victoria Natural History Society
- Western Canada Wilderness Committee
- World Wildlife Fund Canada
Relation to other classification schemes
Bailey combines the Central Pacific coastal forests and the Cascades into a single province. We follow Omernik by distinguishing the regions on the basis of climate, elevation, and dominant communities. Herein, the treatment further divides the area by delineating two ecoregions within the Cascades: British Columbia Mainland Coastal Forests, which run from central Washington to northern British Columbia; and the Central and Southern Cascades Forests which run from Washington almost to the Oregon/California border. Although the mountains of the Olympic Peninsula fall entirely within the coastal ecoregion, like Omernik, the present treatment includes the higher elevation forests with the North Cascades ecoregion. Conservation strategies for the coastal and montane forests would be unwieldy if managed as a single large unit stretching nearly from California to the Yukon Territory.
The Canadian portion of the Central Pacific Coastal Forests rests on Vancouver Island (TEC 193 and 194). In addition to Southern and Northern Pacific Coast vegetation, Vancouver Island also exhibits Coastal Subalpine forests.
The following ecoregions are adjacent to the Central Pacific coast forests:
- British Columbia mainland lowland forests, to the north
- Puget lowland forests, to the west, north of the Columbia River
- Willamette Valley forests, to the west, south of the Columbia River
- Northern California coastal forests, to the south
- Ellen Morris Bishop, 2003. In Search of Ancient Oregon: A Geological and Natural History. Portland, Oregon: Timber Press. ISBN 978-0-88192-7894
- R. H. Guthrie. 2005. Geomorphology of Vancouver Island (electronic resource); mass wasting potential. BC Ministry of Environment, Victoria BC Report No RR01. PDF ISBN 0-7726-5468-9
- Derek Hayes. 1999. Historical Atlas of the Pacific Northwest: Maps of Exploration and Discovery. Seattle, Washington: Sasquatch Books . ISBN 1-57061-2153.
- C. Michael Hogan. 2008. Douglas-fir: Pseudotsuga menziesii, iGoTerra, ed. Nicklas Strõmberg
- W. Kaye Lamb, ed. 1984. The Voyage of George Vancouver 1791-1795, Volume 1, Hakluyt Society
- R. C. Stebbins. 1985. A Field Guide to Western Reptiles and Amphibians. Houghton Mifflin, Boston
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