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Bigcone Douglas Fir

Pseudotsuga macrocarpa (Vasey) Mayr

Comments

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Pseudotsuga macrocarpa , a tree of scattered occurrence and of no concern for timber, is valuable for esthetics and watershed protection. The northernmost stands of the species, in Kern County, are about 35 kilometers east of the closest approach of P . menziesii .
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Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
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Flora of North America Vol. 2 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
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Description

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Trees to 25 m tall; trunk to 1.3 m d.b.h.; bark reddish brown, aging dark blackish gray, scaly, longitudinally fissured; branchlets pendulous, reddish brown or pale brown, aging gray-brown, slender, flexible, slightly pubescent; winter buds reddish brown, ovoid-conical or fusiform-conical, acute. Leaves 2.5-4 cm × ca. 2 mm, stomatal bands 2, abaxial, grayish white, base strongly twisted, apex acute. Seed cones greenish yellow when immature, ripening to dull brown, ovoid-cylindric, 9-13(-18) × 4-6 cm. Seed scales at middle of cones broadly cuneate-flabellate, thick, transversely convex, 2-2.5 × 3-3.5 cm, often resinous, puberulent when young, soon glabrous, faintly striate abaxially. Bracts exserted, not reflexed, lingulate, cusp longer than lateral lobes. Seeds brown, ovoid-conical, 1-1.2 cm × ca. 6 mm; wing pale brown, obovate, 1-1.4 cm.
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Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of China Vol. 4: 38 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
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Flora of China @ eFloras.org
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Wu Zhengyi, Peter H. Raven & Hong Deyuan
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Description

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Trees to 44m; trunk to 2.3m diam.; crown broadly conic. Twigs slender, glabrous or pubescent. Leaves (20--)25--45 × 1--1.5mm, bluish green, apex mucronulate. Pollen cones pale yellow. Seed cones 9--20 × 4--7cm. Seeds 9--12mm. 2 n =24.
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Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of North America Vol. 2 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of North America @ eFloras.org
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Flora of North America Editorial Committee
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eFloras.org
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Habitat & Distribution

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Cultivated. Jiangxi (Lu Shan) [native to W United States]
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Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of China Vol. 4: 38 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of China @ eFloras.org
editor
Wu Zhengyi, Peter H. Raven & Hong Deyuan
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eFloras.org
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Habitat & Distribution

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Slopes, cliffs, and canyons, in chaparral and mixed coniferous forests; 200--2400m; Calif.
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Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of North America Vol. 2 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of North America @ eFloras.org
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Flora of North America Editorial Committee
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eFloras.org
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Synonym

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Abies macrocarpa Vasey, Gard. Monthly & Hort. 18: 21. 1876 (Jan.); Pseudotsuga californica Flous; P. douglasii (Lindley) Carrière var. macrocarpa (Vasey) Engelmann
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Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of North America Vol. 2 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of North America @ eFloras.org
editor
Flora of North America Editorial Committee
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eFloras.org
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Synonym

provided by eFloras
Abies macrocarpa Vasey, Gard. Monthly & Hort. 18: 21. 1876.
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copyright
Missouri Botanical Garden, 4344 Shaw Boulevard, St. Louis, MO, 63110 USA
bibliographic citation
Flora of China Vol. 4: 38 in eFloras.org, Missouri Botanical Garden. Accessed Nov 12, 2008.
source
Flora of China @ eFloras.org
editor
Wu Zhengyi, Peter H. Raven & Hong Deyuan
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eFloras.org
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eFloras

Common Names

provided by Fire Effects Information System Plants
bigcone Douglas-fir
bigcone spruce
bigcone Douglas-spruce
hemlock
false hemlock
desert fir
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bibliographic citation
Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Description

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Bigcone Douglas-fir is a native evergreen conifer from 50 to 100 feet
(15-30 m) in height and 22 to 62 inches (56-155 cm) in DBH. Its growth
form is straight and pyramidal. The deeply ridged bark is composed of
thin, woodlike plates separating heavy layers of cork [3,10]; bark of
trees over 40 inches (102 cm) in DBH is from 6 to 8 inches (36-64 cm)
thick [31]. Main branches are long and pendulous, spreading from 20 to
50 feet (6-15 m) [1,3,15,18,21]. Side branches are few. The needles,
from 0.8 to 1.2 inches (2-3 cm) long, are shed about every 5 years
[10,24]. Female cones are from 4 to 7 inches (10-18 cm) long [28,24].
Seeds are large and heavy, each having a short rounded wing [18]. Roots
are described as strong and spreading [18]. The largest known bigcone
Douglas-fir is 91 inches (231 cm) DBH, 173 feet (53 m) tall, and is
estimated to be from 600 to 700 years of age [10].
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bibliographic citation
Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Distribution

provided by Fire Effects Information System Plants
Bigcone Douglas-fir occurs in mountains of southern California. It is
distributed from the Santa Ynez Mountains in eastern Santa Barbara
County and the Tehachapi Mountains of southwestern Kern County south to
Julian, San Diego County [3,18]. It is cultivated in Hawaii [33].
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bibliographic citation
Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Fire Ecology

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More info for the terms: fire regime, herbaceous, litter, mesic, tree

Bigcone Douglas-fir is one of only a few western conifers capable of
sprouting following fire. Mature trees sprout vigorously from the
branches and bole after burning. The trunk and main branches of bigcone
Douglas-fir have many dormant adventitous buds, which are insulated from
fire beneath thick bark. Fire or other damage to the tree stimulates
cell division and growth in these buds. Consequently, epicormic stems
grow from the axils of branches or from branch stubs along the trunk
from the middle or upper one-third of the crown [10,18].

Bigcone Douglas-fir growing at low elevation often escapes fire damage
because the mesic sites where it grows are not fire-prone [15].
Potential fuels at higher-elevation sites are sparse because understory
vegetation is killed as trees mature and canopies close [31]. Litter
layers of bigcone Douglas-fir forests are usually poorly developed due
to the paucity of herbaceous understory and the sparse fall of needles
from trees [14]. Survival of bigcone Douglas-fir is enhanced in rough
terrain such as talus gullies and rugged canyons; such topography often
impedes the momentum and intensity of spreading fires [23]. Rates of
deforestation by slope class range from 84 percent for slopes of less
than 10 degrees to 51 percent for slopes between 30 and 39 degrees. On
slopes greater than 40 degrees, bigcone Douglas-fir survival is 75
percent [22].

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".
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bibliographic citation
Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Fire Management Considerations

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More info for the terms: density, woodland

Despite its ability to develop new crowns, bigcone Douglas-fir is not
favored by frequent fire. Repeated fire depletes energy reserves and
enlarges old wounds, and mortality is high in trees subjected to such
FIRE REGIMES [18]. Bolton and Vogl [3] speculate that trees subjected
to frequent fire loose their ability to sprout. In contrast to most
conifers, however, fire-damaged trees are usually free from bark beetle
attacks [10]. Bigcone Douglas-fir is adapted to a regime of long,
fire-free intervals [7]. Frequent fire increases the number and density
of the chaparral and woodland species in the spaces between bigcone
Douglas-fir trees [14]. Occasional circumstances of stand defoliation,
however, select in its favor because of its sprouting habit [23]. The
interfaces of chaparral and bigcone Douglas-fir forests are in constant
flux as environmental factors of fire, drought, precipitation, and
erosion assert themselves [32].

The desiccating Santa Ana foehn winds that sweep the Santa Ana and San
Jacinto mountains represent a fire danger to bigcone Douglas-fir trees.
Santa Ana winds are capable of carrying fire downward from upslope mixed
coniferous forests [28,32].
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bibliographic citation
Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Growth Form (according to Raunkiær Life-form classification)

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More info for the term: phanerophyte

Phanerophyte
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bibliographic citation
Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Habitat characteristics

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More info for the terms: cover, shrub

Climate: Bigcone Douglas-fir grows in a mediterranean climate,
characterized by hot summers and wet, mild winters. Annual rainfall
during a 30-year period on a bigcone Douglas-fir site in the San Gabriel
Mountains averaged 30 inches (762 mm) and ranged from 10 to 49 inches
(254-1,245 mm).

Elevation: Bigcone Douglas-fir occurs between 2,000 and 8,000 feet (610
and 2,720 m) [10,24].

Soil and topography: Bigcone Douglas-fir grows in a wide variety of
soil types [10]. At low elevation, it occurs near streams in moist,
shaded canyons and draws where aspects are mostly north and east. At
elevations from 4,440 to 5,600 feet (1,350-1,700 m), aspects include
south- and east-facing slopes. At these elevations, bigcone Douglas-fir
also grows on sloping hillsides, ridges, and benches. At higher
elevations, it occurs on south and west aspects on all types of terrain.
The average angle of slope on which bigcone Douglas-fire grows is 34.5
degrees. Slope angles range from 2 to 90 degrees, although these
extremes are uncommon [3].

Plant associations: The number of plant associates in bigcone
Douglas-fir communities is usually small [14]. Common overstory
associates not listed under SAF Cover Types or Habitat Types and Plant
Communities include bigleaf maple (Acer macrophyllum), California bay
(Umbellularia californica), Digger pine (Pinus sabiniana), and white
alder (Rhombus rhombifolia) [1,4,7,10,19]. Shrub associates include
bigpod ceanothus (Ceanothus megacarpus), red shank (Adenostoma
sparsifolium), Eastwood manzanita (Arctostaphylos glandulosa), toyon
(Heteromeles arbutifolia), white sage (Salvia apiana), black sage (S.
mellifera), purple sage (S. leucophylla), and California scrub oak
(Quercus dumosa) [5,10]. Ground cover is usually sparse and may include
California buckwheat (Eriogonum fasciculatum), wild onion (Allium spp.),
scarlet beardtongue (Penstemon ternatus), chainfern (Woodwardia
fimbriata), and western brackenfern (Pteridium aquilinium var.
pubescens [10].
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bibliographic citation
Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Habitat: Cover Types

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This species is known to occur in association with the following cover types (as classified by the Society of American Foresters):

243 Sierra Nevada mixed conifer
245 Pacific ponderosa pine
246 California black oak
247 Jeffrey pine
248 Knobcone pine
249 Canyon live oak
255 California coast live oak
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bibliographic citation
Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Habitat: Ecosystem

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This species is known to occur in the following ecosystem types (as named by the U.S. Forest Service in their Forest and Range Ecosystem [FRES] Type classification):

FRES21 Ponderosa pine
FRES28 Western hardwoods
FRES34 Chaparral - mountain shrub
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bibliographic citation
Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Habitat: Plant Associations

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This species is known to occur in association with the following plant community types (as classified by Küchler 1964):

More info for the term: forest

K005 Mixed conifer forest
K030 California oakwoods
K033 Chaparral
K034 Montane chaparral
K035 Coastal sagebrush
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cc-publicdomain
bibliographic citation
Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Immediate Effect of Fire

provided by Fire Effects Information System Plants
More info for the terms: fire severity, moderate-severity fire, severity

Fire kills bigcone Douglas-fir seeds. Most authorities claim that
seedlings and saplings are killed by fire [10,14,18]. One study,
however, showed that small burned trees sprouted following a fire of
unreported severity in the Transverse Ranges [23]. The immediate effect
of fire on young trees is therefore unclear, but mortality rates
probably vary according to fire severity [22]. Pole- and
sawtimber-sized trees are fire resistant. Aerial photographs of burns
in the eastern Transverse Ranges show that 60 percent of bigcone
Douglas-fir escaped defoliation during the period from 1938 to 1975
[23]. An additional 15 percent were scorched but not killed.
Twenty-five percent of the trees were killed outright.

The branchlets of defoliated trees are usually killed. Large main
branches generally survive moderate-severity fire, but may be killed
when severely burned. Trunks of severely burned trees are often
protected from fatal damage by their thick bark [18]. Bigcone
Douglas-firs growing sympatrically with canyon live oaks suffer less
fire damage than other bigcone Douglas-firs. These oak seems to act as
a buffer against the intense heat of chaparral fires burning into the
bigcone Douglas-fir community [22,23].
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bibliographic citation
Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Importance to Livestock and Wildlife

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Bigcone Douglas-fir stands provide habitat for black-tailed deer, black
bear, and various small animals. These trees provide preferred spring
habitat for black bear in the San Bernardino Mountains [18]. The seeds
are eaten by various rodents and birds [10].
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bibliographic citation
Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Key Plant Community Associations

provided by Fire Effects Information System Plants
More info for the terms: codominant, cover, forest, natural, xeric

Low elevation ( less than 3,500 feet [1,067 m]) bigcone Douglas-fir forest
communities are disjunct, surrounded by extensive areas of chamise
(Adenostoma fasciculatum) chaparral or coastal sage scrub [4,22,13]. In
canyon bottoms, bigcone Douglas-fir communities intergrade with riparian
forest [11]. From 3,500 to 4,500 feet (1,067-1,372 m), stands are more
widespread. Canyon live oak (Quercus chrysolepis) is sympatric with
bigcone Douglas-fir at these elevations. Together they form a
two-layered forest consisting of a subcanopy of canyon live oak and an
overstory of bigcone Douglas-fir [14,21]. Coulter pine (Pinus coulteri)
replaces bigcone Douglas-fir on more xeric sites at these elevations
[1]. From 4,500 to 5,500 feet (1,372-1,676 m), canyon live oak thins
and bigcone Douglas-fir becomes increasingly abundant. At higher
elevations, bigcone Douglas-fir decreases in importance and the bigcone
Douglas-fir forest type is gradually replaced by mixed evergreen forest.
Codominant species at higher elevations not listed as SAF Cover Types
include incense-cedar (Calocedrus decurrens), California white fir
(Abies concolor var. lowiana), singleleaf pinyon (Pinus monophylla),
sugar pine (P. lambertiana), and interior live oak (Q. wislizeni)
[18,32].

Publications listing bigcone Douglas-fir as a dominant or indicator
species are as follows:

Terrestrial natural communities of California [11].
Vegetation types of the San Bernardino Mountains [14].
Vegetation of the San Bernadino Mountains [21].
A vegetation classification system applied to southern California [26].
An introduction to the plant communities of the Santa Ana and San
Jacinto Mountains [32].
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bibliographic citation
Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Life Form

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More info for the term: tree

Tree
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Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Management considerations

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More info for the term: tree

Bigcone Douglas-fir populations are currently stable, with favorable
rates of reproduction [3]. The tree is being considered for more
extensive plantings in semiarid locales. Its favorable qualities
include resistance to drought, fire, insects, decay, and damage from
ozone [18,20]. The needles of older trees sometimes fade to yellow,
drop, and trees appear dead only to sprout with renewed vigor within 2
years. The reason is unknown, although drought or insects may be
possible causes [10].

Some bigcone Douglas-fir x Douglas-fir hybrids show promise for
outplanting on drier sites in the Douglas-fir region [10,18]. These
hybrids produce wood of comparable quality to that of Douglas-fir
and have the drought tolerance of bigcone Douglas-fir [6].
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Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Occurrence in North America

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CA HI
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Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Phenology

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More info for the terms: cone, seed

Bigcone Douglas-fir undergoes the following seasonal development:

cone buds form: September to October [10]
pollination: early March to mid-April [18]
seed germination: March to May [10]
cones mature: August to September [18]
seed released: September to October {18}
needles fall: September to October [10]
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bibliographic citation
Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Plant Response to Fire

provided by Fire Effects Information System Plants
More info for the terms: crown fire, natural, seed, surface fire

Most sprouting occurs on trees scorched by surface fire. Trees
subjected to crown fire rarely sprout [22]. Aerial photographs taken
over the Meyer and Bear Burns of the Transverse Ranges at postfire years
1 and 2 showed that scorched stands with persistent dead foliage
sprouted, but severely burned stands were killed. Field study of stands
in the Village Burn (severity unreported) near Mount Baldy in the
Transverse Ranges revealed sprouting in pole-sized trees and saplings as
small as 10 feet (3 m) in height. All sprouts died on a number of such
smaller individuals after postfire year 1, but other trees regained full
crowns within 2 to 3 years [23]. The seed-producing ability of bigcone
Douglas-fir is impaired for years [19].

Postfire natural regeneration generally takes decades. A survey of
Transverse Range burns showed natural regeneration was almost
nonexistent in recent burns. No offspring were found in burns less than
19 years old. Seedlings and saplings were most evident in burned areas
free of further fire for 50 or more years. Bigcone Douglas-fir probably
requires the development of an overstory before shade-tolerant seedlings
will establish. Seed dispersal into these shaded areas is usually a
reproductive barrier following stand-replacing fires where all potential
parent trees are killed. Long-distance seed dispersal is inefficient in
bigcone Douglas-fir [23].
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bibliographic citation
Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Post-fire Regeneration

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Secondary colonizer - off-site seed
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bibliographic citation
Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Regeneration Processes

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More info for the terms: epigeal, litter, root crown, seed, tree

Sexual: The male strobili of an individual tree usually sheds pollen
before female strobili open, preventing self-pollination [10]. Seed
production begins at about 20 years of age; full seed production occurs
at about age 40. Insect larvae destroy some immature seed. At times,
they will destroy most of the crop. Heavy seed crops are rare. Seeds
fall under the parent tree and only during high winds is wider seed
dissemination possible [18]. Rodents and birds play a minor role in
seed dispersal. Deer mouse, Merriam chipmunk, California ground
squirrel, and western grey squirrel consume considerable portions of the
seed crop [10]. Seed quality tends to be poor. In one laboratory test,
seeds given cold-stratification treatment for 28 days proved 31 percent
viable [18].

Seedbed requirements are broad. Seeds will germinate successfully on
bare mineral soil or deep litter, although some seedling mortality from
damping-off fungi occurs in deep litter. Germination is epigeal [18].
Bigcone Douglas-fir does not reproduce well where fires are frequent
[3,18]. It reproduces best in locales undisturbed for at least 50
years, where emergents are shaded by canyon live oak. Survival is low
on open sites unless soil remains moist, but seedlings surviving on
these open sites attain top growth more rapidly than shaded seedlings
[18,31]. With time, continuous shade becomes a liability. A span of 40
to 70 years commonly is required for bigcone Douglas-fir to penetrate
through 16.5- to 27-foot (5-9 m) overstories of canyon live oak.
Seedlings on higher elevation south or west slopes, however, enter the
sapling-size class within 3 to 5 years [10].

Vegetative: Vegetative reproduction occurs after injury. Bigcone
Douglas-fir does not sprout from the root crown, but intermediate-aged
trees will sprout from the bole. In the Santa Ana Mountains, coppice
sprouts developed in trees that were 5 to 45 inches (13-114 cm) in DBH
and 25 to 300 years old [3]. Pole- and sawtimber-sized trees often
regrow burned crowns (see Plant Response to Fire). Seedlings and
saplings appear to have this ability as well [23]. Sprouting in young
trees is not well documented, however. Some authorities claim that
seedlings and saplings are not usually capable of sprouting following
injury [14,18].
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Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Regional Distribution in the Western United States

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This species can be found in the following regions of the western United States (according to the Bureau of Land Management classification of Physiographic Regions of the western United States):

3 Southern Pacific Border
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Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Successional Status

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More info for the terms: climax, forest, shrubs, succession

Bigcone Douglas-fir seedlings are shade tolerant, while mature trees are
intolerant [18]. The bigcone Douglas-fir forest is a climax type. In
the absence of fire or other disturbance, bigcone Douglas-fir invades
and dominates surrounding chaparral and oak communities [19]. Chaparral
shrubs remain the dominant vegetation type of their zone because
succession is constantly interrupted by drought accompanied by fire.
Trees usually do not grow large enough during the fire-free period to
become fire resistant [3,13]. Return of bigcone Douglas-fir to
chaparral sites following disturbance probably requires centuries [14].
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Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Taxonomy

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The currently accepted scientific name of bigcone Douglas-fir is
Pseudotsuga macrocarpa (Vasey) Mayr [10,24]. There are no subspecies,
varieties, or forms [3,10]. Bigcone Douglas-fir and Douglas-fir
(Pseudotsuga menziesii) do not naturally hybridize because their ranges
do not overlap. They readily hybridize, however, under laboratory
conditions (see Management Considerations) [6].
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Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Value for rehabilitation of disturbed sites

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More info for the terms: restoration, seed, tree

Bigcone Douglas-fir is used for watershed restoration. Radke and
McDonald [18] reported that the Los Angeles County Department of
Forestry has extensively planted the tree over a 50-year period for that
purpose. Survival rates are not detailed. Bigcone Douglas-fir is
recommended for reforestation of north-facing slopes within its range.
Seed collecting and processing methods are detailed in the literature
[25].

Trees planted on road cuts are often illegally harvested for use as
Christmas trees [12].
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Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Wood Products Value

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More info for the term: fuel

There is no current commercial market for bigcone Douglas-fir wood due
to limited distribution and access [18]. It is heavy, hard, and fine
grained but not durable. There is less sapwood than heartwood, and the
latter contains pockets of resin. In the past, the wood was used
locally for fuel and lumber [29].
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Howard, Janet L. 1992. Pseudotsuga macrocarpa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: http://www.fs.fed.us/database/feis/

Associated Forest Cover

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Bigcone Douglas-fir has been listed in at least three vegetation classifications. One author placed the species in the California Coast Range forest, considering it an endemic and relic species. Another suggested that, in the San Bernardino Mountains at least, bigcone Douglas-fir was a member of the Live Oak Woodland and the Bigcone Douglas-fir vegetation types (4). Among forest cover types, bigcone Douglas-fir is listed as a common associate in Canyon Live Oak (Society of American Foresters Type 249) (5).

Bigcone Douglas-fir occupies an intermediate position between the lower elevation chaparral zone and the higher elevation mixed-conifer forest. It ranges downward into the chaparral as far as moisture conditions permit, and upward among the pines and firs as far as severe climate allows. Bigcone Douglas-fir does not extend solidly between the two types, however. The species is found in patches, in groups, and as single trees scattered among the oaks and chaparral. The continuity of stands also is broken by cliffs, slides, and areas of adverse soil.

Evidence suggesting that bigcone Douglas-fir has long occupied its present natural range is available from the fossil record. A likely progenitor of the species has been found in both the Pliocene and Pleistocene epochs (6).

Fire, or its absence, greatly influences the extent and makeup of bigcone Douglas-fir stands. In general, repeated fires kill bigcone Douglas-fir, leaving only oaks or chaparral. Less frequent, but more catastrophic fires limit bigcone Douglas-fir to scattered large trees. When fires are infrequent, stands with several size and age classes develop; when fires are absent, multi-aged stands having at least some regeneration evolve (7).

In recent large fires in the eastern Transverse Range, nearly 60 percent of the trees escaped defoliation and 15 percent sprouted later, for a survival rate of 75 percent. Trees appear to have survived primarily because they were growing with large tree-size canyon live oaks (Quercus chrysolepis), and in rough, broken terrain. Large canyon live oaks apparently act as a buffer against severe combustion characteristics of the chaparral nearby, and rough terrain impedes the speed and intensity of a conflagration. Survival of bigcone Douglas-fir on slopes of less than 20 degrees was only 37 percent. On slopes greater than 40 degrees, survival was more than 90 percent (10).

Throughout its natural range, bigcone Douglas-fir is almost inseparable from canyon live oak. They form a community that is remarkably stable, self-perpetuating, somewhat exclusive, and probably climax in terms of succession. In the future, only minor shifts in species composition within the community are likely (7).

In addition to canyon live oak, other tree associates, particularly at high elevations, are ponderosa pine (Pinus ponderosa var. ponderosa), Jeffrey pine (P. jeffreyi), singleleaf pinyon (P. monophylla), and sugar pine (P. lambertiana), incense-cedar (Libocedrus decurrens), and California white fir (Abies concolor var. lowiana). At middle elevations, tree associates are Coulter pine (Pinus coulteri), Digger pine (P. sabiniana), California black oak Quercus kelloggii), two-petal ash (Fraxinus dipetala), and California-laurel (Umbellularia californica). Singleleaf pinyon and knobcone pines (Pinus attenuata), as well as curlleaf (Cercocarpus ledifolius) and birchleaf mountain-mahogany (C. betuloides) also are locally present. At lower elevations bigcone Douglas-fir, along with bigleaf maple (Acer macrophyllum) and white alder (Alnus rhombifolia), is found in riparian settings, often in deep ravines, where it escapes fire. Coast live oak (Quercus agrifolia), toyon (Heteromeles arbutifolia), California scrub oak Quercus dumosa), birchleaf mountain-mahogany, laurel sumac (Rhus laurina), sugar sumac (R. ovata), and occasionally southern California walnut (Juglans californica) are associates of bigcone Douglas-fir (3) at lower elevations, mostly in nonriparian settings.

Many woody shrubs are found with bigcone Douglas-fir (table 1). At middle and high elevations, although scarce beneath bigcone Douglas-fir and canyon live oak crowns, they flourish in open spaces between trees or on edges of thickets. At low elevations, shrubs become abundant and well developed around scattered large firs.

Table 1- Principal shrub associates of bigcone Douglas-fir in three elevational zones Elevation Scientific name Common name 274 to 1067 m or Adenostoma fasciculatum Chamise   900 to 3,500 ft Artemisia californica California sagebrush Ceanothus leucodermis Chaparral whitethorn C. spinosus var. palmeri Greenbark ceanothus Dendromecon rigida Bush poppy Eriogonum fasciculatum California buckwheat Salvia spp. White sage Yucca whipplei Chaparral yucca 1097 to 1676 m or Adenostoma sparsifolium Red shanks   3,600 to 5,490 ft Arctostaphylos glauca Bigberry manzanita A. patula Greenleaf manzanita Ceanothus cuneatus Wedgeleaf ceanothus C. integerrimus Deerbrush C. leucodermis Chaparral whitethorn C. oliganthus Hairy ceanothus C. spinosus var. palmeri Greenbark ceanothus 1707 to 2438 m or Arctostaphylos glauca Bigberry manzanita   5,600 to 7,900 ft A. patula Greenleaf manzanita Castanopsis sempervirens Sierra chinkapin Ceanothus crassifolius Hoary-leaf ceanothus C. cuneatus Wedgeleaf ceanothus Chrysothamnus nauseosus Rubber rabbitbush Penstomon ternatus Scarlet beardtongue Rhamnus californica California buckthorn R. crocea Hollyleaf buckthorn A number of herbaceous species are scattered beneath bigcone Douglas-fir trees. Plants are relatively scarce and small because necessary nutrients, moisture, and light, already captured by the taller and deeper-rooted species, often are not available.

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Climate

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The bigcone Douglas-fir habitat has long hot summers and cool moist winters. Extremes of annual precipitation vary from less than 250 mm (10 in) to 1270 mm (50 in), with 510 to 1020 mm (20 to 40 in) more common. The 30-year average at 1325 m (4,350 ft) elevation on a north aspect in the San Gabriel Mountains near Glendora, CA, was 610 mm (24 in). The lowest annual precipitation recorded was 250 mm (9.9 in) and the highest 1240 mm (49 in).

Snowpacks persist rarely in the range of the species, except at high elevations. Snow may fall, however, as early as October, or as late as May. During the rainy season, fog has been reported to add to the moisture available for tree growth (14,15). During the summer, thunderstorms, hailstorms, or cloudbursts are common on higher mountains. Because much of this precipitation quickly evaporates, it does not foster tree growth (15).

Specific temperature data within the range of bigcone Douglas-fir have not been reported other than for one station at 730-m (2,400-ft) elevation in the San Gabriel Mountains. The 22-year average mean for November through April was 9° ± 2° C (49° ± 3.7° F). Highs of above 27° C (80° F) and lows of below freezing were recorded in each of the 6 months. Annual temperatures at low to middle elevations in the mountain ranges of southern California where bigcone Douglas-fir grows seldom exceed 41° C (106° F) or drop below -12° C (10° F).

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Damaging Agents

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Fire is the most injurious agent of bigcone Douglas-fir. In spite of its ability to develop new crowns after complete defoliation, and its thick bark (15 to 20 cm or 6 to 8 in for trees more than 100-cm or 40-in d.b.h.), trees die from fire, and particularly from repeated fires that deplete energy reserves and enlarge old wounds.

Damage by insects and disease is not reported. The California flatheaded borer (Melanophila californica) has been observed in the wood of a few trees. Even trees damaged by fire seem free of bark beetle attacks. A hard pitchy wood is given as a possible reason for lack of damage from these agents. A needle-cast fungus (Rhabdocline pseudotsugae) has been observed on bigcone Douglas-fir needles (8). Older trees occasionally lose most of their needles, apparently from a physiological disorder, but epicormic branching along the bole usually replaces the lost crown. Damage to needles from ozone is another potential injury. However, in a sensitivity study, seedlings of bigcone Douglas-fir ranked low (11th of 13 conifer species and hybrids) in susceptibility to ozone injury (9).

Many species of animals are associated with bigcone Douglas-fir, especially deer, rabbits, and woodrats. Browsing of seedlings is a major damage. Bigcone Douglas-fir stands are preferred spring habitat for black bears in the San Bernardino Mountains (12). After the sapling stage, animal damage is negligible.

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Flowering and Fruiting

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Throughout most of its natural range, bigcone Douglas-fir flowers from early March through mid-April. Male flowers generally shed pollen before female flowers become receptive-a mechanism that facilitates cross-pollination and prevents selfing. The plant is monoecious. Pollination in a given locality lasts 2 to 3 weeks. Fertilized conelets begin to enlarge in mid-July and are easily seen soon after.

Cones generally begin to dry and turn brown in August or September and most seed is released in September and October. Seeds are large and heavy and each has a rounded wing about 13 mm. (0.5 in) long. Mature cones are rich dark brown and range from 11 to 17 em (4 to 7 in) long. Some cones fall during winter, but others remain on the tree for at least a year.

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Genetics

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Varieties or natural hybrids of bigcone Douglas-fir are not known, but an artificial cross of bigcone Douglas-fir and coast Douglas-fir was achieved in 1956 at Oregon State University, Corvallis. Hybrid seedlings indicated low mortality, good height growth, and a dense fibrous root system. They showed promise for outplanting on drier sites in the Douglas-fir region (2).

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Growth and Yield

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In deep shade, growth of bigcone Douglas-fir seedlings and saplings is suppressed severely. Saplings may be only 60 cm (24 in) tall when 40 to 50 years old (10). Growth rings often are indistinguishable. Bigcone Douglas-fir trees break through the oak overstory when 4 to 9 m (13 to 30 ft) tall and 40 to 70 years old. Breast-height diameter at this age ranges from 10 to 20 cm (4 to 8 in). Once above the oak foliage and into sunlight, growth of bigcone Douglas-fir accelerates. Annual height increment may exceed 30 cm (12 in).

In more open stands, bigcone Douglas-fir seedlings and saplings develop more quickly. Height of saplings may average 1 to 3 m (3 to 10 ft) at age 20 and from 4 to 15 m (13 to 50 ft) at age 40. From 40 to 100 years, annual increments of height and diameter may be uniform, even though amounts of annual precipitation vary. Trees in favorable growing conditions often produce thick tapering boles and long drooping branches.

In the Santa Ana Mountains, diameter growth rates seem to be correlated to steepness of slope, with the average diameter of trees of a given age increasing as the angle of slope decreases. The largest trees of a given age, therefore, grow on level sites. The average d.b.h. of 20-year-old trees on level ground was 20 cm (7.8 in), but only 6 cm (2.2 in) on 60 to 90 degree slopes. A possible explanation of the difference is that little, if any, soil and litter are found on steep slopes, and water holding capacity and nutrients usually are low (1).

Tree heights are affected by many variables, especially position on the slope. Trees generally are tallest at the base of slopes and shortest near the ridgeline. Trees at base of slopes commonly are straight and tall, averaging 24 to 30 m (80 to 100 ft) in height, but trees on upper slopes more often are gnarled and branchy and only 9 to 15 m (30 to 50 ft) tall.

The lifespan of bigcone Douglas-fir is as long as its coniferous associates, or longer. In the Santa Ana Mountains, trees 250 or more years old are commonplace. The oldest tree sampled was 622 years old and 140 cm (55 in) in d.b.h. A 157-cm (62-in) d.b.h. monarch of indeterminate age is nearby (1). The largest living bigcone Douglas-fir grows near San Antonio Canyon on the Angeles National Forest in southern California. At 231 cm (91 in) in d.b.h. and 44.2 m (145 ft) in height, this tree deserves its name "Old Glory."

Bigcone Douglas-fir is well known for its ability to grow a new crown after severe burning. This ability has helped to sustain the species in its present natural range. New tissue, which leads to new branches, develops from the upper surface of defoliated limbs in the upper portions of the tree. Large sawtimber-sized trees, therefore, can develop new crowns, but seedlings, saplings, and overmature sawtimber usually cannot.

Boles also produce new shoots after fire, mechanical, or physiological injury. Vigorous intermediate-aged trees are particularly noted for this capability. In the Santa Ana Mountains, new shoots developed in trees that were from 13 to 114 cm (5 to 45 in) in d.b.h. and from 25 to 300 years old (1).

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Reaction to Competition

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In its seedling stage, bigcone Douglas-fir requires at least some shade. In moist sheltered situations, however, it reproduces successfully in the open. Saplings and small poles need increasing amounts of light for best development. Mature trees usually are found in open stands, probably as a consequence of having adequate light and moisture. In general, bigcone Douglas-fir may be classed as intolerant of shade.

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Rooting Habit

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The species is described as having a strong spreading root system.

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Seed Production and Dissemination

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Cone crops of bigcone Douglas-fir usually are small. Bumper crops are infrequent. Small amounts of seed, however, are borne on a few trees nearly every year. The minimum cone-bearing age of the species is about 20 years, but cones are rare on trees younger than 40 years. Most seeds fall beneath tree crowns and only during high winds is wider dissemination possible.

Insect larvae destroy some seeds in each cone crop and, at times, most of the crop. Rodents and birds consume seeds and aid in dispersal by distributing them beyond existing stands. Deer mice, chipmunks, ground squirrels, and the western gray squirrel eat large amounts of available seeds. The squirrels often bury seeds; some of these escape notice and eventually germinate.

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Seedling Development

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Natural seedbed requirements for germination are broad. Seeds of bigcone Douglas-fir have been observed to germinate successfully on the bare mineral soils of rocky outcrops and geomorphically active areas. They also germinate well in deep litter, usually beneath an overstory of oak and bigcone fir, but heavy losses from damping-off fungi often take their toll of tiny seedlings in this environment. Germination is epigeal.

Time of germination varies with elevation. In the chaparral zone, germination begins in late March. At higher elevations, germination ends in late May, or occasionally, early June.

Seed quality tends to be poor, as indicated in such early descriptions as "large number imperfect" and 49 a considerable percentage not fertile" (14,15). In a laboratory test of seed stratified for 28 days in moist vermiculite with a day temperature of 30° C (86° F) and night temperature of 20° C (68° F), 31 percent of seeds germinated.

Weather, especially rainfall, can be critical to germination and early abundance of bigcone Douglas-fir seedlings. In the Santa Ana Mountains, 24,700 seedlings per hectare (10,000/acre) were present after a rainy period preceded by a year of above-average precipitation. The seedling environment, however, was not reported. New seedlings were absent during dry years (1).

Bigcone Douglas-fir does not reproduce in stands having frequent fires, nor do badly damaged stands seed back to bigcone Douglas-fir, except during a series of wet years after a severe fire. Infertile seed, destruction of seed by fire, consumption of seed by birds and rodents, and lack of suitable microsites are possible reasons for scanty reproduction. Lack of shade could be another reason. Throughout its range, bigcone Douglas-fir reproduces most abundantly in locales undisturbed for at least 50 years, especially if shaded by canyon live oak trees. Where present, seedlings ranged in density from 140 to 1,030/ha (56 to 416/acre), with an average of 330/ha (132/acre). Advance reproduction, plants smaller than 2.5 cm (1.0 in) in d.b.h., was similar in mean and range of density (7).

Artificial regeneration of bigcone Douglas-fir began in 1905, with outplantings in Los Angeles County. Survival was about 1 percent. The species was planted extensively (9,880 seedlings per hectare or 4,000/acre) for watershed rehabilitation from 1925 to 1930 by the Los Angeles County Forestry Department. From 1953 to 1975, this Department outplanted some bigcone Douglas-firs in all but 4 years (13). Survival, unfortunately, is unknown.

Additional information on artificial regeneration of bigcone Douglas-fir is scanty. One small trial took place on a harsh site in Shasta County. Seed was germinated in a greenhouse in 1.9-liter (0.5-gal) milk cartons and 20 seedlings were outplanted as plugs when 1 year old. After five growing seasons in the field, survival was 65 percent and height averaged 53 cm (21 in) with a range of 18 to 76 cm (7 to 30 in).

Early height growth of bigcone Douglas-fir seedlings is slow, especially in deep shade. The species develops a taproot in early years, possibly at the expense of shoot growth.

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Soils and Topography

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Soils on which bigcone Douglas-fir grows are derived from a wide variety of parent materials. Of 16 stands sampled throughout the range of the species, 4 grew on metasedimentary parent materials (sandstone and schist), 10 on granitics, and 2 in contact zones where the parent material was primarily granitic. The soil orders where bigcone Douglas-fir is most frequently found are Inceptisols and occasionally Alfisols. Soil series on metasedimentary material are probably Laughlin and Friant; in contact zones, Oak Glen; and on granitics, Tollhouse, Cieneba, Crouch, and two others that resemble Tish Tang and Neuns. Soils show a broad range of depth and development (7). Some are shallow and poorly developed; others are deeper and better developed. Many are droughty. Bigcone Douglas-fir is capable of becoming established on soils too dry for other conifers.

Topography where the species is found is variable. Much of the terrain is rough and steep, strongly dissected by permanent and ephemeral streams. Slopes vary from 1 to 93 percent. Some stands occupy precipitous slopes of sheltered canyons, others are found on mostly steep broken slopes intermixed with cliffs and avalanche chutes, and still others thrive on gentler slopes and level ground. For all stands in the Santa Ana Mountains, average angle of slope is 34.5 degrees (1). The species is well represented on all aspects, north slopes in particular.

Elevations of the bigcone Douglas-fir habitat range from 275 m (900 ft) on cool moist north slopes of canyon bottoms to 2400 m (7,875 ft) on warm southfacing plateaus. As elevations increase, the aspect best suited to bigcone Douglas-fir shifts from cooler to warmer. Many combinations of slope, aspect, soil, and elevation, therefore, support bigcone Douglas-fir.

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Special Uses

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The wood of bigcone Douglas-fir is heavy, hard, and close grained, but not durable (15). It has less sapwood than heartwood, the latter containing pockets of resin. In the past, bigcone Douglas-fir was used locally for fuel and to a small extent for coarse lumber. Currently, it has value in watersheds and wildlife habitats for its scenic beauty.

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Vegetative Reproduction

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Bigcone Douglas-fir does not sprout from the root crown after cutting or fire. It has been propagated by grafting.

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Brief Summary

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Pinaceae -- Pine family

Philip M. McDonald

Distinct in appearance and conspicuous among its usually shorter associates, bigcone Douglas-fir (Pseudotsuga macrocarpa) provides contrast and variability to the southern California landscape. The wood of the species, although suitable for coarse lumber, is scarcely utilized because the trees are scattered and are more valuable for esthetics and watershed protection.

Because the taxonomic characteristics of bigcone Douglas-fir are similar to those of its northern "cousin," Douglas-fir, it was at least twice assigned to the genus Abies. Commonly, the species has been called hemlock, false hemlock, and desert fir. Colloquially, it is often referred to as bigcone-spruce, probably because its drooping lower branches, stiff needles, and upright cones remind the observer of the spruce tree. The species' accepted common name, bigcone Douglas-fir, stresses its Pseudotsuga lineage and the extraordinary size of its cones.

The species has been grown successfully outside the continental United States. It was unknown in Europe until the seedlings were raised at Bayfordbury, England, in 1910. Trees also have been reported growing in Sussex and North Ireland, where they reached heights of more than 18 m (60 ft) and crown spread of 12 m (40 ft) (3).

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Distribution

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The range of bigcone Douglas-fir is about 217 km (135 mi) from north to south and about 338 km (210 mi) from east to west. Distribution of the species, in general, is confined to the Transverse and Peninsular Ranges of southern California. It is found on Mount Pinos, technically in the Tehachapi Mountains but considered transitional between them and the Transverse Ranges. Northern limits are near Mount Pinos in Kern County, and the headwaters of Labrea Creek in Santa Barbara County. Westernmost limits are Mission Canyon in the Santa Ynez Mountains, and Zaca Peak in the San Rafael Mountains. Older publications claimed that bigcone Douglas-fir grew in central Baja California, Mexico; a more recent publication verifies that it does not (11). The southern limit of the species is near Julian, San Diego County.


- The native range of bigcone Douglas-fir.

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Physical Description

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Tree, Evergreen, Monoecious, Habit erect, Trees without or rarely having knees, Tree with bark rough or scaly, Young shoots 3-dimensional, Buds not resinous, Leaves needle-like, Leaves alternate, Needle-like leaf margins entire (use magnification), Leaf apex mucronulate, Leaves < 5 cm long, Leaves < 10 cm long, Leaves blue-green, Scale leaf glands not ruptured, Needle-like leaves flat, Needle-like leaves not twisted, Needle-like leaf habit erect, Needle-like leaf habit drooping, Needle-like leaves per fascicle mostly 1, Needle-like leaf sheath early deciduous, Needle-like leaf sheath persistent, Twigs pubescent, Twigs not viscid, Twigs with peg-like projections or large fascicles after needles fall, Berry-like cones orange, Woody seed cones < 5 cm long, Woody seed cones > 5 cm long, Bracts of seed cone exerted, Bracts of seed cone included, Seeds tan, Seeds brown, Seeds winged, Seeds unequally winged, Seed wings prominent, Seed wings equal to or broader than body.
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Pseudotsuga macrocarpa

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Pseudotsuga macrocarpa, commonly called the bigcone spruce or bigcone Douglas-fir, is an evergreen conifer native to the mountains of southern California. It is notable for having the largest (by far) cones in the genus Pseudotsuga, hence the name.

The tree occurs from the San Rafael Mountains in central Santa Barbara County and the Tehachapi Mountains of southwestern Kern County, south through the Transverse Ranges, to the Cuyamaca Mountains in San Diego County. The tree is shade-tolerant and prefers to grow on slopes.

Name

Pseudotsuga macrocarpa is a Douglas-fir. The name "bigcone spruce", though confusing as it is not a spruce species, is often still used,[3][4] and occurs in place names.[5]

Description

Pseudotsuga macrocarpa typically grows from 15–30 m (49–98 ft) in height and 56–155 cm (1 ft 10 in – 5 ft 1 in) in trunk diameter.[6] The growth form is straight, with a conical crown from 12–30 m (39–98 ft) broad, and a strong and spreading root system. The bark is deeply ridged, composed of thin, woodlike plates separating heavy layers of cork; bark of trees over 1 m (3.3 ft) in diameter is from 15–20 cm (5.9–7.9 in) thick. The main branches are long and spreading with pendulous side shoots.

The leaves are needle-like, 2.5–4.5 cm (0.98–1.77 in) long,[7] and are shed when about five years old. The female cones are from 11–17 cm (4.3–6.7 in) long,[4] larger and with thicker scales than those of other douglas-firs, and with exserted tridentine bracts. The seeds are large and heavy, 10 mm long and 8 mm broad, with a short rounded wing 13 mm long;[4] they may be bird or mammal dispersed as the wing is too small to be effective for wind dispersal. Trees start producing seeds at about 20 years of age.

The largest known individual of this species is 53 m (174 ft) tall, 231 cm (91 in) in diameter, and is estimated to be from 600 to 700 years of age.

Distribution

Pseudotsuga macrocarpa is restricted to the California montane chaparral and woodlands and California coastal sage and chaparral ecoregions of California. It prefers a Mediterranean climate, characterized by hot dry summers and wet, mild winters. Annual rainfall during a 30-year period on a bigcone Douglas-fir site in the San Gabriel Mountains averaged 75 cm (30 in) and ranged from 25–125 cm (9.8–49.2 in).

Bigcone Douglas-fir occurs between 300–2,700 m (980–8,860 ft). At low elevation, it occurs near streams in moist, shaded canyons and draws where aspects are mostly north and east. At elevations from 1,350–1,700 m (4,430–5,580 ft), aspects include south- and east-facing slopes. At these elevations, it also grows on sloping hillsides, ridges, and benches. At higher elevations, it occurs on south and west aspects on all types of terrain. The average angle of slope on which it grows is 35 degrees, ranging from level to 90 degrees, although these extremes are uncommon.

Ranges the tree is found in, south to north, include:[8][9]

Bigcone Douglas-fir cone (left), with a coast Douglas-fir cone for comparison

Ecology

Pseudotsuga macrocarpa, has several features to tolerate and survive wildfire, notably the very thick bark, and the presence of numerous adventitious buds on the upper side of the branches; this enables the trees to survive even crown fires which burn off all the branchlets, the apparently dead trees becoming green again the following spring. Wildfire frequencies in the chaparral habitats in which it often grows typically range from 15 to 50 year intervals. Bigcone Douglas-fir is closely associated with canyon live oak (Quercus chrysolepis) and often establishes itself in its shade; after about 50 years, it emerges above the oak canopy.

Pseudotsuga macrocarpa showing branch regeneration after a crown fire through epicormic shoots. Note the charred tree trunks.

The number of plant associates in bigcone Douglas-fir communities is usually small.

Fire ecology

Pseudotsuga macrocarpa populations are suspected to be declining due to possibly larger and more extreme wildland fires with greater frequencies. Major wildfires within its range, since 2003, have clearly proven a reduced extent when compared to early 1930s extents derived from historical aerial photos. Although historical information has provided the opportunity to detect stand level patch changes, post-fire resprouting of older more mature trees and natural regeneration and recruitment of the species into higher canopy has yet to be adequately quantified.

One tree species in direct competition with bigcone is Calocedrus decurrens, with preliminary post-fire regeneration of this species exponentially greater than bigcone. One or two years after the Station fire in 2009 on the Angeles National Forest, there was an estimated 20:1 cedar:bigcone seedling density in fixed radius plots on Mount Wilson. It may be more appropriate to perform population stability estimates up to five years or much later (i.e. 20 yrs) after a large conflagration due to the potential for immediate and delayed post-fire sprouting and regeneration and interplant competition, as well as the well-noted strategy of seed germination in shrub understories, which is likely to escape detection by surveyors until much later in its life.

Research related to the role of mycorrhizae and its relationship to seed establishment needs evaluated in these vegetation communities due to the suspected role it has with the relationship with water, especially in water-limited systems such as those in the wildlands of southern California. In addition, an aggressive seed cone collection strategy should be drafted for this species which includes extensive collection during large cone production years such as 2013, and should include a tracking system to determine correlations to climatic conditions in order to develop a foundation from which to perform species viability assessments w/ varying future climate scenarios.

This tree is being considered for more extensive plantings in semiarid locales. Its favorable qualities include resistance to drought, fire, insects, decay, and damage from ozone, and its aggressive rooting system and tolerance to variable growing medium. The needles of older trees sometimes fade to yellow, drop, and trees appear dead only to sprout with renewed vigor within two years. The reason is unknown, although drought or insects may be possible causes.

Uses

Wildlife

Bigcone Douglas-fir stands provide habitat for black-tailed deer, black bear, and various small animals. These trees provide preferred spring habitat for black bear in the San Bernardino Mountains.

The seeds are eaten by various rodents and birds.

Restoration species

Bigcone Douglas-fir is used for watershed and habitat restoration. The Los Angeles County Department of Forestry has extensively planted the tree over a 50-year period for that purpose.

Some hybrids of Pseudotsuga macrocarpa (Bigcone Douglas-fir) × Pseudotsuga menziesii (Coast Douglas-fir) show promise for planting on drier restoration sites within the P. menziesii−Douglas-fir natural range. These hybrids produce wood of comparable quality to that of Douglas-fir and have the drought tolerance of bigcone Douglas-fir.

Timber

There is no current commercial market for bigcone Douglas-fir wood due to limited distribution and access. It is heavy, hard, and fine grained but not durable. There is less sapwood than heartwood, and the latter contains pockets of resin.

In the past, the wood was used locally for fuel and lumber.

See also

References

  1. ^ Farjon, A. (2013). "Pseudotsuga macrocarpa". IUCN Red List of Threatened Species. 2013: e.T34025A2840746. doi:10.2305/IUCN.UK.2013-1.RLTS.T34025A2840746.en. Retrieved 12 November 2021.
  2. ^ Conifer Specialist Group (1998). "Pseudotsuga macrocarpa". IUCN Red List of Threatened Species. 1998. Retrieved 11 May 2006.old-form url
  3. ^ Bailey, L.H.; Bailey, E.Z.; the staff of the Liberty Hyde Bailey Hortorium (1976). Hortus third: A concise dictionary of plants cultivated in the United States and Canada. New York: Macmillan. ISBN 978-0-02-505470-7.
  4. ^ a b c McDonald 1990. sfn error: no target: CITEREFMcDonald1990 (help)
  5. ^ "Topoquest".
  6. ^ Howard 1992. sfn error: no target: CITEREFHoward1992 (help)
  7. ^ Flora of North America.
  8. ^ Calflora: Los Angeles County distribution map
  9. ^ Calflora: Ventura County distribution map

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Pseudotsuga macrocarpa: Brief Summary

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Pseudotsuga macrocarpa, commonly called the bigcone spruce or bigcone Douglas-fir, is an evergreen conifer native to the mountains of southern California. It is notable for having the largest (by far) cones in the genus Pseudotsuga, hence the name.

The tree occurs from the San Rafael Mountains in central Santa Barbara County and the Tehachapi Mountains of southwestern Kern County, south through the Transverse Ranges, to the Cuyamaca Mountains in San Diego County. The tree is shade-tolerant and prefers to grow on slopes.

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