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被子植物
Arbutus
EOL Text
Arbutus menziesii is found in British Columbia extending south through Washington, Oregon, California and Baja California. The California range includes northwestern California, High Cascade Range, north and central High Sierra Nevada, central western California, the north Channel Islands (Santa Cruz Island), Western Transverse Ranges, San Gabriel Mountains and Peninsular Ranges.
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Rights holder/Author | C. Michael Hogan, C. Michael Hogan |
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The Pacific madrone is a spectacular tree. Its showy bark, flowers and berries along with the gracefully crooked branches inspired Bret Harte to compose a poem about its loveliness (see Parsons 1966). But, alas, they can be difficult to grow. These trees should only be planted in very well drained soils in areas with non-alkaline water. Although generally started from seed, Pacific madrone may also be propagated from cuttings, grafting, or layers.
To start from seed, gather the fruits from the trees when they are ripe—generally from October to December. Soften the berries by soaking them in water and then separate the seeds from the pulp. Completely dry the seeds before storing. Dried seeds may be stored for up to 2 years at room temperature. For best germination, use seeds that have been stratified by pre-chilling for one to two months at 2 to 5 degrees C. Plant the seeds, in either spring or fall, in containers that have been filled with a mix of peat, sand, and gravel. Allow the seedlings to reach at least two feet in height before transplanting. Established trees can live up to 200 years or more and do not transplant well, so select a site where the tree can remain permanently. Choose a place with full sun to partial shade well away from lawns and other plants that require summer watering. Deeply irrigate the seedlings once a month during the summer months until established. Do not splash water upon the trunk or leaves while watering, as the trees are susceptible to fungus that resides in the soil. Once established, the trees will require only infrequent, deep irrigation during unusually dry summers. The trees develop an underground, woody organ called a ‘burl’ that re-sprouts if the stem is destroyed.
More info for the terms: cover, tree
A review indicates that Pacific madrone is a major component of Douglas-fir-tanoak
(Pseudotsuga menziesii-Lithocarpus densiflorus)-Pacific madrone forests.
These forests are characterized by an
overstory of Douglas-fir with tanoak and Pacific madrone sharing the secondary
canopy in varying proportions. Pacific madrone is a minor component in a variety
of cover types, commonly intermingling with redwood (Sequoia sempervirens),
western hemlock (Tsuga heterophylla), Oregon white oak (Quercus
garryana var. garryana), and Pacific ponderosa pine (Pinus
ponderosa var. ponderosa) throughout its distribution [92].
In British Columbia, Pacific madrone grows with lodgepole pine (Pinus contorta) [73].
The open woodlands of the San Juan Islands are characterized by Douglas-fir and
Pacific madrone in a fescue (Festuca spp.) matrix. Other tree species that may be found on such
sites include Rocky Mountain juniper (Juniperus scopulorum), lodgepole pine, and
Oregon white oak [43].
Pacific madrone is a dominant species in the following vegetation types.
California:
coast live oak (Q. agrifolia)-Pacific madrone/California
hazelnut-blackberry (Corylus cornuta var. californica-Rubus spp.)
interior live oak (Q. wislizenii)-Pacific madrone/poison-oak (Toxicodendron diversilobum)
California black oak (Q. kelloggii)-Pacific madrone-coast live oak [8]
Oregon and northern California:
Pacific madrone-Oregon white oak
Pacific madrone-tanoak [104]
Douglas-fir-tanoak-Pacific madrone Society of American Foresters cover type [123]
Gifford Pinchot National Forest, Washington:
western hemlock-Douglas-fir-Pacific madrone [137]
Puget Trough, Washington:
Douglas-fir-Pacific madrone/pink honeysuckle (Lonicera hispidula) [25]
Sucia Island, Puget Sound, Washington:
Douglas-fir-Pacific madrone/American vetch (Vicia americana)
Douglas-fir-Pacific madrone/salal (Gaultheria shallon)
Pacific madrone-lodgepole pine/salal[39]
More info on this topic.
Pacific madrone typically bears flowers in May, but may flower in March and April at low elevations [13,82,92]. It flowers from April to May on the Willamette, Mt Hood, and Siuslaw National Forests of western Oregon [138]. In June, the second-year leaves turn orange to red and begin to fall shortly after the new crop of leaves has fully grown. Bark is shed all summer. Berry clusters ripen in autumn and persist into December [13]. On the Challenge Experimental Forest, Pacific madrone berries mature from mid-September to mid-October [87]. The table below gives generalized seasonal development of southern and northern populations of Pacific madrone.
Generalized trends in the phenological development of Pacific madrone [40] | ||
Southern range | Northern range | |
Leaf bud swelling begins | February | late March |
Flower bud swelling begins | March | May |
Flowering begins | March | May |
Full bloom | April | June |
Second-year leaves fall | June | June-July |
Bark exfoliates | June-July | June-September |
Fruits mature | September-October | October |
Despite its regular shedding of both bark and leaves, Pacific madrone is a highly ornamental species, prized for its crooked beauty, colorful bark, showy flowers, and brightly colored fruits [33,40]. Trees are cultivated for landscaping in both the United States and Europe [91,140]. Pacific madrone is a well-known bee plant [13,33]. Past commercial uses of Pacific madrone included utilization of the bark for tanning leathers and the wood for making charcoal for gunpowder [91,140].
Historically, West Coast tribes ate Pacific madrone berries and fashioned eating utensils from the bulbous roots [13,56]. The leaves have been reported to possess medicinal properties [33]. Fruit of Pacific madrone can be eaten raw, boiled, or steamed. Berries can be stored for a long time if boiled and dried [53].
In western British Columbia, Washington, and Oregon, the climate best suited to Pacific madrone is characterized by mild temperatures with prolonged cloudy periods, narrow diurnal fluctuation, and limited extremes. Average January temperatures range from 2° to 8° C (36° to 46° F) and average July temperatures from 10° to 20° C (50° to 68° F). Winters generally are wet and mild, and summers cool and relatively dry with long frost-free seasons. Average annual precipitation is usually abundant, ranging from 790 to more than 3000 mm (31 to 118 in), 75 to 85 percent of which is received between October 1 and March 1, mostly as rain.
In the interior valleys and hills of the Klamath Mountains and lower west slopes of the southern Cascades, average January temperatures range from 2° to 5° C (36° to 41° F) and average July temperatures from 17° to 25° C (62° to 77° F). Average annual precipitation varies between 760 and 890 mm (30 and 35 in). The average January temperature in the heart of the Pacific madrone range in the Sierra Nevada is 5° C (41° F), and the average July temperature is 22° C (72° F). Average annual precipitation is 1730 mm (68 in).
In the Coast Ranges of California, temperatures where Pacific madrone grows average 2° to 5° C (36° to 41° F) in January and 15° to 20° C (59° to 68° F) in July. Average precipitation varies between 1140 and 1650 mm (45 and 65 in) yearly in the north to 640 to 760 mm (25 to 30 in) in the south. Some fog usually is present throughout this region.
Within the total range of this species, temperature extremes are from -21° to 46° C (-6° to 115° F) and annual rainfall from 460 to 4220 mm (18 to 166 in) (30).
Pacific madrone reproduces mainly by sprouting. Sprouts arise from dormant buds formed at or just above the root collar and tend to be numerous. More than 300 sprouts were counted on a single low 10-inch-diameter Pacific madrone stump in the northern Sierra Nevada.
Low stumps generally produce more sprouts than high stumps. High stumps sometimes support undesirable stool sprouts that form on the edge of the cut surface or, less commonly, on the vertical portion of the stump between the ground and the top. Stool sprouts tend to become infected with heart rot at an early age and are more susceptible, to dieback and death than sprouts from the root crown. Stool sprouts that survive seem to grow well, but their longevity is unknown.
Pacific madrone sprouts grow rapidly. On a site of medium quality in the Klamath Mountains, 3-yearold sprout clumps averaged 13 members per clump, 3.1 in (10 ft) in height, and 2.3 in (7.6 ft) in width (22). In the northern Sierra Nevada on a good site, the annual enlargement of sprout clumps was measured in both a clearcut and a shelterwood. After 10 years, sprouts were taller, 6.7 vs 3.0 in (22 vs 10 ft); wider, 3.1 vs 2.1 in (10.1 vs 7.0 ft); contained more sprouts (15 vs 7); and possessed more volume, 52.1 vs 19.8 cm³ (1,840 vs 700 ft³) (12). In both locations, annual growth of 1.5 in (5 ft) on 2- to 5-year-old sprouts was observed for particularly vigorous members of a clump. Seven years after cutting and burning in southwest Oregon, dense stands of madrone sprout clumps spaced 2.7 by 2.7 in (9 by 9 ft) had a basal area of about 22 m²/ha (96 ft²/acre), 84 percent cover, and an above-ground biomass of 25,000 kg/ha (22,500 lb/acre) (9). This rapid early growth, both in height and crown width, allows Pacific madrone to dominate conifer and shrub associates for many years. It also means that understory species of grasses, forbs, and shrubs are quickly excluded from madrone sprout stands following disturbance (9), in spite of a leaf canopy that is more open than that of tanoak and giant chinkapin (Castanopsis chrysophyl1a) (16).
New information is available for forecasting site occupancy of Pacific madrone for up to 6 years after disturbance. It includes equations that relate width and area of sprout clumps originating from trees greater than 1 inch d.b.h. to size of parent stem and time since cutting (28), and equations that predict potential leaf area and biomass by parent tree diameter class (7).
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Pacific madrone has excellent value for erosion control and slope stabilization [93,103]. It was an important component in a tree community along Magnolia Bluff, Seattle, Washington, that played an important role in preventing more serious landslides along the bluff in 1995 and 1996 [103].
Barcode of Life Data Systems (BOLDS) Stats
Public Records: 2
Specimens with Barcodes: 6
Species With Barcodes: 1