Index of Species Information
SPECIES: Alnus rubra
Introductory
SPECIES: Alnus rubra
AUTHORSHIP AND CITATION :
Uchytil, Ronald J. 1989. Alnus rubra. In: Fire Effects Information System, [Online].
U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station,
Fire Sciences Laboratory (Producer). Available:
https://www.fs.usda.gov/database/feis/plants/tree/alnrub/all.html [].
ABBREVIATION :
ALNRUB
SYNONYMS :
Alnus oregona
Alnus incana var. rubra
Alnus rubra var. pinnatisecta
SCS PLANT CODE :
ALRU2
COMMON NAMES :
red alder
Oregon alder
western alder
Pacific Coast alder
TAXONOMY :
The currently accepted scientific name of red alder is Alnus rubra Bong.
[31,34,40]. There are no recognized subspecies, varieties, or forms.
LIFE FORM :
Tree
FEDERAL LEGAL STATUS :
No special status
OTHER STATUS :
NO-ENTRY
DISTRIBUTION AND OCCURRENCE
SPECIES: Alnus rubra
GENERAL DISTRIBUTION :
Red alder is confined to the Pacific Coast region from southeast Alaska
to southern California. Although there is an isolated population
growing along streams in northern Idaho, it ordinarily occurs no further
inland than 100 miles (160 km) at elevations below 2,500 feet (762 m)
[16,24,33]. Red alder is cultivated in Hawaii [71].
ECOSYSTEMS :
FRES20 Douglas-fir
FRES21 Ponderosa pine
FRES22 Western white pine
FRES23 Fir - spruce
FRES24 Hemlock - Sitka spruce
FRES27 Redwood
FRES28 Western hardwoods
STATES :
AK CA HI ID OR WA BC
BLM PHYSIOGRAPHIC REGIONS :
1 Northern Pacific Border
2 Cascade Mountains
3 Southern Pacific Border
8 Northern Rocky Mountains
KUCHLER PLANT ASSOCIATIONS :
K001 Spruce - cedar - hemlock forest
K002 Cedar - hemlock - Douglas-fir forest
K003 Silver fir - Douglas-fir forest
K005 Mixed conifer forest
K006 Redwood forest
K012 Douglas-fir forest
K013 Cedar - hemlock - pine forest
K025 Alder - ash forest
K029 California mixed evergreen forest
SAF COVER TYPES :
210 Interior Douglas-fir
221 Red alder
222 Black cottonwood - willow
223 Sitka spruce
224 Western hemlock
225 Western hemlock - Sitka spruce
226 Coastal true fir - hemlock
227 Western redcedar - western hemlock
228 Western redcedar
229 Pacific Douglas-fir
230 Douglas-fir - western hemlock
231 Port Orford-cedar
232 Redwood
244 Pacific ponderosa pine - Douglas-fir
SRM (RANGELAND) COVER TYPES :
NO-ENTRY
HABITAT TYPES AND PLANT COMMUNITIES :
Red alder communities, both upland and riparian, generally are found
within coniferous forests dominated by Douglas-fir (Pseudotsuga
menziesii), western redcedar (Thuja plicata), western hemlock (Tsuga
heterophylla), grand fir (Abies grandis), and Sitka spruce (Picea
sitchensis) [18,19,67], or as components of deciduous forests of
floodplains or swamps [18,19]. Generally, five types of red alder
communities have been described [18,19,21,32,67]:
(1) Upland, pure even aged stands of red alder, with a dense shrub
undergrowth dominated by salmonberry (Rubus spectabilis) or
elderberry (Sambucus melanocarpa), occurring within coniferous
forests.
(2) Upland mixed stands of red alder/other deciduous trees and
shrubs/conifers within coniferous forests less than 100 years
old, with red alder occurring as a dominant or codominant.
(3) Riparian red alder communities within coniferous forests.
(4) Mixed stands within deciduous riparian forests, red alder
occurring as codominant with black cottonwood (Populus trichocarpa)
and bigleaf maple (Acer macrophyllum).
(5) In swamps often occurring with, or codominant with, western
redcedar. In this type of community, red alder appears to be a
climax species.
Red alder communities were primarily restricted to streams and wet areas
during presettlement times. Since then, disturbances such as logging
have provided an abundance of open sites with bare mineral soil, which
favor red alder colonization. Today red alder communities are common
throughout much of coastal Oregon and Washington.
Published classification schemes listing red alder as an indicator
species or as a dominant part of the vegetation in community types (cts)
or plant associations (pas) are presented below:
Area Classification Authority
AK general veg. cts Viereck & others 1992
CA hardwood forest & Barbour 1987
woodland cts
CA general veg. cts Thorne 1976
s CA general veg. cts Paysen & others 1980
nw CA,w Or,w WA general veg. cts Franklin 1979
OR: Siuslaw NF general veg. pas Hemstrom & Logan 1986
OR postburn veg. cts Bailey & Poulton 1968
s OR: Cascade Mtns forest pas Atzet & McCrimmon 1990
OR, WA general veg. cts Franklin & Dyrness 1973
Pacific NW general veg. cts Hall 1984
MANAGEMENT CONSIDERATIONS
SPECIES: Alnus rubra
WOOD PRODUCTS VALUE :
Red alder is considered the most important commercial hardwood of the
Pacific Northwest. The fine even texture and moderate density of red
alder wood make it easy to work with. It sands and polishes easily,
holds paints and coatings well, stains readily, and seldom splits
[3,38]. Due to these favorable characteristics, and the fact that it is
much less expensive than other hardwoods used in furniture
manufacturing, red alder wood is extensively for furniture making and
cabinetry [55]. It is also used in the manufacture of novelties, trim,
paneling, pallets, veneers, plywoods, and paper roll plugs [3,67].
Smaller manufactured items include brush handles, spools, trays, shoe
soles, and boxes. Red alder is an important source of pulp for paper
products. Research is being conducted to determine the feasibility of
producing 4x8 foot (1.2-2.4 m) sheets of waferboard from chips [29].
Trees less than 8 inches (20.3 cm) in diameter are generally chipped or
cut for fuel wood. Sawmill logs need to be greater than 7 or 8 inches
(17.8-20.3 cm) in diameter at the small end and over 30 feet (9.1 m)
long [29].
Red alder is also an important source of firewood.
IMPORTANCE TO LIVESTOCK AND WILDLIFE :
Red alder grows rapidly, often reaching heights of 35 feet (10 m) in 10
years; therefore, only young plants are available as browse. Leaves and
twigs of saplings are eaten by cattle, sheep, and goats [64], sometimes
in preference to other fairly good browse [57]. Deer and elk eat the
leaves, twigs, and buds of young red alder trees in fall, winter, and
early spring. Beavers eat the bark, and build dams and lodges with the
stems [64]. Alder (Alnus spp.) seeds are eaten by redpolls, siskins,
and goldfinches [42]. Red alder seeds are an important food for deer
mice, especially when other primary foods are difficult to obtain.
Seeds eaten off the snow after being dispersed [66].
PALATABILITY :
The leaves and young twigs of red alder are generally considered to be a
fair browse for cattle and sheep [11]. Red alder may be slightly less
palatable to cattle than to sheep or goats. However, cattle make
greater use of red alder, as they tend to frequent moist sites where red
alder occurs [64]. The degree of use shown by livestock and wildlife
species for red alder is rated as follows [30,57]:
CA OR
Cattle fair-poor ----
Sheep fair-poor ----
Horses fair-poor ----
Mule deer fair-useless fair
NUTRITIONAL VALUE :
NO-ENTRY
COVER VALUE :
Red alder dominated early seral communities within recently clearcut
Douglas-fir forests are favorable habitat for black-tailed deer. Red
alder/thimbleberry (Rubus parviflorus) stands in Oregon are preferred by
black-tailed deer during the summer and early fall when daytime
temperatures are highest [30]. These stands are generally avoided in
the winter.
VALUE FOR REHABILITATION OF DISTURBED SITES :
Red alder is useful for erosion control on steep slopes where soil has
been disturbed because the heavy cover and litter layer which forms
within 3 to 5 years effectively protects the soil [67]. Plants may be
established by direct seeding or transplanting, but not by cuttings, as
they seldom root [16]. To obtain seed, proven seed collection and seed
extraction procedures should be followed [36,58]. Transplanted
container-grown seedlings have shown a first year survival rate of about
75 to 80 percent [36]. Carefully dug wild seedlings also transplant well
[29].
Recent research suggests that cuttings from 1- to 3-year-old plants can
be induced to root by dipping the cutting for 10 seconds in a 8,000 p/m
solution of indole-3 butyric acid and then dusting with 10 percent
benomyl [47]. However, cuttings took 6 weeks to root in a warm
greenhouse environment between 72 and 77 degrees F (22-25 deg C).
OTHER USES AND VALUES :
Native Americans of the Pacific Northwest extracted a red dye from the
inner bark of red alder, which was used to dye fish nets, making the net
"invisible" to fish. Red alder contains salicin, which chemically is
closely related to acetylsalicylic acid (commonly known as aspirin).
This is probably why Native Americans used various preparations for
medicinal purposes. Native Americans also used the wood for various
utensils. Red alder coals are currently used in the Northwest to smoke
salmon [1].
OTHER MANAGEMENT CONSIDERATIONS :
Although long-term economic returns are higher with conifer crops than
red alder, under certain conditions red alder should be considered as an
alternative forest crop [29]. Upland sites too wet for Douglas-fir and
hemlock (Tsuga spp.) are well suited for red alder. Red alder may also
be planted onto areas infected with laminated root rot fungus, since
hardwoods are immune to this infection. In Oregon, before an area can
be reforested with red alder, regulations require that permission be
obtained from the Oregon Department of Forestry.
Due to red alder's ability to symbiotically fix atmospheric nitrogen, it
has been proposed for use as a rotation crop before growing conifers
[12,44]. Soil nitrogen accretion rates have shown increases ranging from
40 to 300 pounds per acre (45-355 kg/ha) per year under red alder stands
[25]. Conifer stands which follow red alder exhibit increased growth and
yields [2,67]. Studies have shown that Douglas-fir grown with red alder
had increased heights and diameters compared to Douglas-fir grown
without alder [43]. Research on aboveground biomass accretion rates in
red alder stands suggests that for crop rotations, red alder should be
harvested before age 20 [69]. This is because maximum annual
productivity occurs between 10 and 15 years, and stands older than 20
years show signs of deterioration. Red alder stands reach an
aboveground biomass plateau between ages 40 and 50.
Herbicides have been used both to promote the growth of alder and to
kill alder to promote the growth of conifers. To achieve desired
stocking and distribution in potentially harvestable red alder stands,
thinning and culling of selected red alder trees may be desirable.
Numerous chemical applications are available to control red alders which
are competing with Douglas-fir or other valuable conifers. Stands
may be aerially sprayed, or individual trees can be spot sprayed or
injected. The most common chemicals used for control of red alder are
2,4-D, Tordon 101, triclopyr ester, and triclopyr amine [9,29,49].
Proper guidelines for the use and application of chemicals should be
followed [9,29,49,62].
BOTANICAL AND ECOLOGICAL CHARACTERISTICS
SPECIES: Alnus rubra
GENERAL BOTANICAL CHARACTERISTICS :
Red alder is the largest American alder. It is a rapidly growing,
short-lived, medium-sized, deciduous tree, generally with one straight
distinct trunk. Red alder reaches a maximum height of about 120 feet
(37 m) with a maximum trunk diameter of about 32 inches (80 cm).
However, mature trees are typically from 80 to 100 feet (24-30 m) tall
and 14 to 18 inches (36-46 cm) in diameter [14,25,34,59]. Maximum age is
one hundred years [58]. Trees growing in the Puget Sound area exhibit
the following age-growth characteristics [14,34]:
Age Height Diameter Breast Height
(years) (feet/meters) (inches/centimeters)
5 18 / 5.5 ------
10 40 / 12.2 ------
20 65 / 19.8 ------
30 82 / 25.0 11 / 27.9
40 90 / 27.4 13 / 33.0
50 98 / 29.9 16 / 40.6
60 105 / 32.0 18 / 45.7
Red alder has thin (less than 0.75 inch [1.9 cm]), smooth gray-whitish
mottled bark, which is often covered with green moss. The root system
is shallow, but wind throw is seldom a problem, since the leaves are
absent during winter and early spring when winds are the strongest and
when soils are saturated with moisture [59]. Male and female flowers
occur on the same tree in catkins. The drooping staminate catkins are
up to 5 inches (12 cm) long and clustered near the end of a twig. The
pistillate catkins are erect, 0.6 to ).8 inch (1.5-2 cm) long, turning
woody and conelike at maturity [14,26].
Red alder is closely related to white alder (Alnus rhombifolia), and the
two species are difficult to differentiate when growing together.
However, their distribution and habitats do not overlap to any great
extent. In the summer, leaf characteristics can be used to separate
these alders, but in the winter proper identification is based on many
subtle points. Several keys exist for proper identification.
RAUNKIAER LIFE FORM :
Phanerophyte
REGENERATION PROCESSES :
Sexual reproduction: Red alder regenerates primarily by seed. Plants
are monoecious and are primarily wind pollinated. Flowering generally
occurs from late February to early May depending on latitude and climate
[36]. After fertilization female catkins develop into woody cones about
0.5 to 1 inch (1.2-2.5 cm) long, containing 50 to 100 small, flattened,
winged, nutlike seeds [16,67].
Seed dispersal and production: Seed dispersal begins soon after
ripening in late summer, but most seeds are shed during fall and winter
[14,66]. The seeds are very lightweight (about 666,000/pound
[1,465,000/kg]) and are normally carried up to several hundred yards in
the direction of the prevailing winds. Seed production begins at about
10 years [58] (but sometimes sooner), and continues throughout maturity,
with optimum production at about 25 years of age [36]. A prolific
seeder, red alder produces peak crops about every 4 years, with moderate
to light crops produced in between [36]. Total seed crop failure is
very rare; however, a total crop failure did occur following a severe
freeze in November 1955 [16,36].
Germination: Under natural conditions, germination occurs in the
spring. Germination is best on moist mineral soil in full sunlight
[14,36]. Seed also germinates well on rotten wood and duff [45], and to
a lesser extent on soil organic horizons and on rock-surfaced logging
roads, but the roots must quickly penetrate to a moist nutritious
substrate if seedlings are to survive [14]. Sunlight is required for
germination [36]. Seeds under thick vegetation or buried deeply in the
soil, will not germinate until the site is disturbed, exposing the seeds
to sunlight. Germination percentages range from 59 to 84 percent
[52,58]. Germination rates of stratified and nonstratified seeds are
about equal. Low germination percentages may be due to a high
proportion of empty seeds known to occur in red alder [52]. Seeds
remain viable in storage for about 3 years [25].
Seedling establishment: Generally, exposed mineral soil is needed for
seedling establishment. Seed production is normally so prolific that
dense stands quickly develop on exposed soils of logging roads,
clearcuts, and burned over areas [25]. These areas may have from
several hundred thousand to several million red alder seedlings per
hectare in the spring of the first year after the disturbance [69].
Regeneration and establishment in dense, thick, brush fields is
infrequent due to the lack of exposed sights, but any disturbance which
removes the brush and exposes the soil will favor red alder
establishment [67]. Plants often reach 6 to 18 inches (15-45 cm) in 1
year and may reach 18 feet (5.5 m) in 5 years [16]. This rapid juvenile
growth gives the shade-intolerant red alder a competitive edge over
conifers, as it quickly overtops them.
Vegetative reproduction: Red alder will sprout following an injury to a
stem, but in the absence of disturbance, sprouting is infrequent. Red
alder's sprouting ability following cutting is summarized as follows
[25,27]:
(1) Sprouting vigor is greatest on trees 1 to 3 years old. Vigor falls
off dramatically after 15 years. Trees 15 years or older
rarely have live sprouts 2 years after cutting.
(2) The average number of sprouts per cut stem increases significantly
as stump height is increased.
(3) Stumps with the cut surface facing south or west have the least
mortality and are most likely to sprout.
(4) Level cuts have higher mortality and fewer sprouts than angled
stumps.
(5) Stems cut in January have the lowest mortality; stems cut during the
growing season, especially July or August, have the highest
mortality.
(6) The number of sprouts per cut stem is not affected by the season of
cutting.
Propagation: Cuttings of red alder do not root easily [66].
SITE CHARACTERISTICS :
Historical evidence suggests that the distribution of red alder was much
more restricted than it is today; it occurred chiefly along streams and
in other wet areas [18]. Continual disturbance over the past 100 years,
primarily from logging, has created an abundance of open areas with bare
mineral soil (both are required for seedling establishment) which red
alder has colonized, thus increasing its acreage dramatically. This is
especially true of uplands, where it was previously infrequent.
Red alder is found primarily within Douglas-fir, western hemlock,
western redcedar, Sitka spruce, and grand fir forests in the Pacific
Northwest [16,66,67]. Individual trees or clumps of trees may occur to
varying degrees of mixture within these coniferous forests, but stand
development is best along streams, moist bottomlands, and moist lower
slopes [14,35,66,67]. In these mesic locations, pure stands are nearly
always even-aged. Along the southern portion of its range in California
and in the dry interior valleys of Washington and Oregon, red alder is
restricted to riparian deciduous forests [8,19]. In these areas it may
mix with white alder.
Soils: Red alder occurs on a wide variety of soil types ranging from
well-drained gravels and sands to poorly drained clay or organic soils
[25]. The best stands are found on deep, well-drained loams or sandy
loams of alluvial origin [14,16]. Stands also grow well on residual or
colluvial soils of volcanic origin [14]. Soils under red alder stands
develop higher available and total nitrogen contents than soils under
adjacent coniferous stands because of red alder's ability to fix
nitrogen. Nitrogen accretion rates vary with stand location, vigor,
age, and density, with rates varying from 40 to 300 pounds of nitrogen
per acre (45-355 kg/ha) per year [14,25]. As soil nitrogen increases,
soil pH under red alder stands drops. In coastal Oregon, pure alder
stands had soil pH values averaging 4.3 to 4.4, while adjacent conifer
stands had pH values averaging 5.3 [20]. Red alder leaves also contain
significant amounts of nitrogen. Leaves decompose rapidly, forming a
deep humus and thus improving soil structure [16].
Climate: Red alder grows in humid coastal climates characterized by
cool wet winters and warm dry summers. Mean annual precipitation ranges
from 16 to 220 inches (40-560 cm) [25]; precipitation occurs chiefly as
rain during the winter. Trees need more than 25 inches (64 cm) of
precipitation annually, and most stands are located on sites receiving
in excess of 40 inches (102 cm) [16].
Coniferous forest associates: Red alder grows both in pure stands and
in mixtures with native conifers [67]. Pure and mixed stands are mostly
even aged. Trees generally become established in forest openings
created from a disturbance. As stands develop and trees mature, they
prevent other red alder seedlings from becoming established, due to the
seedlings' shade intolerance. Common coniferous associates include:
Douglas-fir, western redcedar, western hemlock, grand fir, and Sitka
spruce. Red alder communities within coniferous forests contain a
number of deciduous trees and shrubs also. Deciduous trees and shrubs
include bigleaf maple, vine maple (Acer circinatum), Pacific willow
(Salix lasiandra), and bitter cherry (Prunus emarginata). Understory
shrubs and herbs include salmonberry, western thimbleberry, American
devilsclub (Oplopanax horridus), black elderberry (Sambucus racemosa),
trailing blackberry (Rhubus ursinus), Siberian minerslettuce (Montia
sibirica), and false lily-of-the-valley (Maianthemum dilatatum)
[19,21,67].
Deciduous riparian forest associates: In California, red alder chiefly
occurs in riparian forests where it often codominates with Sitka spruce,
redwood (Sequoia sempervirens), black cottonwood, bigleaf maple, and
Pacific willow [54,56]. Along larger rivers in Oregon and Washington,
red alder typically codominates with bigleaf maple, Oregon ash (Fraxinus
latifolia), black cottonwood, and willows (Salix spp.) [18,19]. Other
deciduous forest associates include Pacific wax-myrtle (Myrica
californica), Pacific red elder (Sambucus callicarpa), and California
laurel (Umbellularia californica) [18,56].
Elevation: Red alder is generally found no farther inland than 100
miles, at elevations below 2,500 feet. Elevational ranges for several
western states are presented below [16,33,34,48,66]:
from sea level to 500 feet (0-152 m) in CA
1,030-3,600 feet (314-1,097 m) in ID
sea level to 2,500 feet (0-762 m) in OR
sea level to 2,500 feet (0-762 m) in WA
SUCCESSIONAL STATUS :
Red alder is common on many disturbed areas. Many of the stands which
exist today were created because of the pioneering habit of red alder.
Red alder quickly invaded lands clearcut and burned during the 1920's to
1940's [3,39]. In 1920 there was an estimated 1/3 of a billion board
feet of red alder, but by the mid 1960's, red alder acreage increased
dramatically, containing an estimated 12 billion board feet [39]. By
1988, red alder covered an estimated 13 percent of commercial forest
lands along the Pacific Coast of Washington and Oregon [55].
Red alder is an early seral species. It quickly invades forest
openings, such as those created from fires, logging, wind throws, or
road cuts, and it also pioneers volcanic mud flows [19,46]. Red alder
and Douglas-fir are reported as the principal pioneer tree species of
lower and middle elevation forests from southwestern British Columbia to
northwestern California [41]. Thus they often dominate the first
postfire community in the Pacific Northwest. Disturbed areas are
naturally seeded by numerous wind-dispersed seeds, resulting in stands
that start out with several thousand alder trees per acre [3]. Due to
red alder's shade intolerance, stands are self-thinning; trees that do
not maintain their height in the canopy die, resulting in even-aged
stands [17,66]. Conifers such as Douglas-fir that become established at
the same time are quickly overtopped by this extremely fast growing
species. These early seral red alder communities suppress competing
conifers, but after about 25 years, conifers equal red alder height and
begin to overtop them. After about 40 years, Douglas-fir becomes
dominant. Few red alder trees remain in stands past 60 years [16,67].
SEASONAL DEVELOPMENT :
Red alder is a deciduous tree. Flowers begin to form in the spring
before the leaves expand. Flowering in Oregon and Washington generally
begins in late February and continues until early May [58]. Fruits
ripen in late summer and early fall; seeds are dispersed during fall and
winter [58] and can often be seen on fresh snow. The following dates
have been recorded for phenological events in Oregon and Washington
[16]:
Phenological Event 17 locations throughout Snohomish County
Oregon and Washington Washington
Leaf bud bursts March 21 - April 23 April 3
Completely leafed out April 9 - May 16 May 2
Flowering begins February 19 - May 4 March 29
Flowers all fallen March 18 - June 5 April 12
Fruit ripe August 5 - October 29 August 27
Leaves mostly fallen September 18 - November 24 November 13
In the Cascade Mountains of Oregon, red alder is one of the first
deciduous trees to lose its leaves. The majority of leaves fall during
October, with virtually all leaves lost by the first week in November
[10].
FIRE ECOLOGY
SPECIES: Alnus rubra
FIRE ECOLOGY OR ADAPTATIONS :
Red alder's bark, although thin, is sufficiently fire resistant to
protect trees from light surface fires. The foliage and leaf litter do
not carry fires well [1,16]. Red alder stands often lack flammable
understory debris and are often on moist sites which burn infrequently
[14,16]. Red alder revegetates burned areas via seed from off-site plants
[35].
FIRE REGIMES :
Find fire regime information for the plant communities in which this
species may occur by entering the species name in the FEIS home page under
"Find Fire Regimes".
POSTFIRE REGENERATION STRATEGY :
Tree with adventitious-bud root crown/soboliferous species root sucker
Initial-offsite colonizer (off-site, initial community)
FIRE EFFECTS
SPECIES: Alnus rubra
IMMEDIATE FIRE EFFECT ON PLANT :
Information regarding the effects of fire on red alder is lacking.
DISCUSSION AND QUALIFICATION OF FIRE EFFECT :
NO-ENTRY
PLANT RESPONSE TO FIRE :
Red alder is an early seral species which quickly invades burned areas.
Off-site plants inhabiting fire resistant draws and streambeds provide
an abundance of seed, which reportedly can travel several hundred yards
via wind. Thus red alder quickly colonizes soils exposed after forest
fires. Red alder along with Douglas-fir are often the dominant postfire
vegetation on low to middle elevation sites throughout the Pacific
Northwest [41]. Red alder may dominate and suppress conifers following
a fire for 20 to 25 years, after which the conifers overtop the alder
[68].
Information regarding the sprouting response of red alder after
aboveground plant parts have been killed by fire is lacking. However,
responses after cutting show that red alder tends to sprout at the root
collar or along the lower stem no matter where the stem is cut [27]. For
detailed information regarding the sprouting response of red alder after
cutting, refer to the Regeneration Slot.
DISCUSSION AND QUALIFICATION OF PLANT RESPONSE :
NO-ENTRY
FIRE MANAGEMENT CONSIDERATIONS :
Fire hazard is generally low in red alder stands. Stands may be used as
natural fire breaks [67]. The thin litter permits easy construction of
firelines.
REFERENCES
SPECIES: Alnus rubra
REFERENCES :
1. Arno, Stephen F.; Hammerly, Ramona P. 1977. Northwest trees. Seattle,
WA: The Mountaineers. 222 p. [4208]
2. Atkinson, William A.; Hamilton, Willard I. 1978. The value of red alder
as a source of nitrogen in Douglas-fir/alder mixed stands. In: Briggs,
David G.; DeBell, Dean S.; Atkinson, William A., compilers. Utilization
and management of alder: Proceedings of a symposium; 1977 April 25-27;
Ocean Shores, WA. Gen. Tech. Rep. PNW-70. Portland, OR: U.S. Department
of Agriculture, Forest Service, Pacific Northwest Forest and Range
Experiment Station: 337-351. [21618]
3. Atterbury, Toby. 1978. Alder characteristics as they affect utilization.
In: Briggs, David G.; DeBell, Dean S.; Atkinson, William A., compilers.
Utilization and management of alder: Proceedings of a symposium; 1977
April 25-27; Ocean Shores, WA. Gen. Tech. Rep. PNW-70. Portland, OR:
U.S. Department of Agriculture, Forest Service, Pacific Northwest Forest
and Range Experiment Station: 71-81. [21619]
4. Atzet, Thomas; McCrimmon, Lisa A. 1990. Preliminary plant associations
of the southern Oregon Cascade Mountain Province. Grants Pass, OR: U.S.
Department of Agriculture, Forest Service, Siskiyou National Forest. 330
p. [12977]
5. Bailey, Arthur W.; Poulton, Charles E. 1968. Plant communities and
environmental interrelationships in a portion of the Tillamook Burn,
northwestern Oregon. Ecology. 49(1): 1-13. [6232]
6. Barbour, Michael G. 1987. Community ecology and distribution of
California hardwood forests and woodlands. In: Plumb, Timothy R.;
Pillsbury, Norman H., technical coordinators. Proceedings of the
symposium on multiple-use management of California's hardwood resources;
1986 November 12-14; San Luis Obispo, CA. Gen. Tech. Rep. PSW-100.
Berkeley, CA: U.S. Department of Agriculture, Forest Service, Pacific
Southwest Forest and Range Experiment Station: 18-25. [5356]
7. Bernard, Stephen R.; Brown, Kenneth F. 1977. Distribution of mammals,
reptiles, and amphibians by BLM physiographic regions and A.W. Kuchler's
associations for the eleven western states. Tech. Note 301. Denver, CO:
U.S. Department of the Interior, Bureau of Land Management. 169 p.
[434]
8. Bolsinger, Charles L. 1988. The hardwoods of California's timberlands,
woodlands, and savannas. Resour. Bull. PNW-RB-148. Portland, OR: U.S.
Department of Agriculture, Forest Service, Pacific Northwest Research
Station. 148 p. [5291]
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