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BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Pinus ponderosa var. ponderosa | Pacific Ponderosa Pine
GENERAL BOTANICAL CHARACTERISTICS : Pacific ponderosa pine has the potential for achieving large dimensions. Stems of 103.5 inches (263 cm) in d.b.h. and 232 feet (70.7 m) in height have been recorded. Diameters at breast height of 30 to 50 inches (76-127 cm) and heights of 90 to 130 feet (27.4-39.6 m) are common throughout its range [5]. Trees often reach ages of 300 to 600 years [48]. Needles are typically in bundles of three. They are 5 to 10 inches (12.5-25.0 cm) long and form tufts at the end of each branch. Cones are oval and 3 to 6 inches (7.5-15.0 cm) long. The bole is typically straight and at maturity is clear of lower branches. The bark of mature trees is composed of broad, irregular scaly-plates that fit together like jigsaw puzzle pieces. The crown is conical and composed of stout branches [38,48]. RAUNKIAER LIFE FORM : Phanerophyte REGENERATION PROCESSES : Pacific ponderosa pine reproduces sexually. It does not regenerate naturally by vegetative methods. It can be propagated by rooting and grafting, but success decreases rapidly when scions are taken from trees older than 5 years [48]. Seedling development: Successful natural regeneration of Pacific ponderosa pine is accomplished by a combination of heavy seed crops, favorable weather during the growing season, soil texture, low competition, and exposed mineral seedbeds [26,39]. Moisture-stress reduces seed germination as well as initial seedling survival and development. Pacific ponderosa pine has the capacity for root growth in relatively dry soil. Nursery stock removed in January from California had appreciable root elongation even when planted in soil with very low water potential. Shrub competition reduces the height and diameter growth of seedlings planted in northern California and Oregon. On the western slopes of the Sierra Nevada, growth starts noticeably later with each 2,000 foot (610 m) increase in elevation. Rates of height and radial growth do not vary with elevation during the growing season [48]. Seed production and dissemination: Seed production varies with geographic distribution. There are generally 6,900 to 23,000 clean ponderosa pine seed per pound (6,210-20,700 per kg) [36]. In California west of the Sierra Nevada, medium seed crops are borne on an average of every 2 to 3 years. The average interval between heavy cone crops is 8 years; in the Pacific Northwest it is every 4 to 5 years. Twenty-three years of data show Pacific ponderosa pine to be a poor seeder in western Montana. It bears cones as early as 7 years and continues to produce good cone crops up to at least 350 years. Optimum seed viability is produced by trees 60 to 160 years old. In California, trees greater than 25 inches (64 cm) d.b.h. were the most dependable seed producers. Recommended cold stratification period is 30 to 60 days for stored seeds at 33 to 41 degrees F (1-5 deg C). Pacific ponderosa pine seeds do not naturally disseminate beyond about 100 feet (31 m) from the seed source. In central Oregon, the amount of seeds reaching the ground at 132 feet (40 m) into a clear-cut was only 22 percent that of those measured at the timber's edge. At 528 feet (161 m) it was only 8 percent. Nearly all seeds are disseminated by early November. In a good seed year, as many as 345,080 seeds per acre (852,050 seeds per hectare) may reach the ground [48,79]. Seedling mortality and predation: Many variables are responsible for seedling mortality. Seedlings younger than 36 days old are more susceptible to minimum night temperatures cooler than 23 degrees F (-5 deg C) than are lodepole pine (Pinus contorta) seedlings. During winters with little snowcover, 1- and 2-year-old seedlings may suffer damage and frost kill. Also, 1- to 3-month-old seedlings are killed by stem temperatures of 130 degrees F (54 deg C) and higher. Pacific ponderosa pine seeds are consumed by a number of birds and small mammals. Squirrels and porcupines clip many of the cone-bearing twigs, hence destroying flowers and conelets. Rabbits and hares injure or kill many seedlings by nibbling young stems, while pocket gophers may decimate an entire population of seedlings. Repeated browsing by deer may stunt seedling growth for up to 50 years [13]. Livestock also damage seedlings and saplings by trampling, bedding, and browsing. Many species of insects and disease affect Pacific ponderosa pine. See MANAGEMENT CONSIDERATIONS for futher discussion [48]. SITE CHARACTERISTICS : Throughout its range, Pacific ponderosa pine is dependent upon several site variables such as soils, elevation, and climate [68]. Soil moisture is the variable most often limiting growth, especially in the summer months when rainfall is deficient [48]. Climate: Pacific ponderosa pine is typically found on warm, dry sites. The climate is characterized by a short growing season and minimal summer precipitation. The mean annual precipitation ranges from 11 to 17 inches (28-43 cm), with summer precipitation averaging 5 to 10 inches (13-25 cm). Average annual precipitation ranges from about 14 to 30 inches (35-75 cm) on Pacific ponderosa pine sites in Oregon and Washington, and is typically in the form of snow [18]. The western slope of California's northern Sierra Nevada may be the wettest area supporting Pacific ponderosa pine, with an annual rainfall reaching 69 inches (173 cm). In contrast, this species occupies areas in California where extreme rainfall deficiencies occur [July and August precipitation about 1 inch (2.5 cm) or less] [48]. Soil and topography: Pacific ponderosa pine occurs on a wide variety of soils ranging from glacial till, glacio-fluvial sand and gravel, dune, basaltic rubble, colluvium, to deep loess or volcanic ash. This pine develops best on wet, deep, sandy gravel and clay loams with pH between 6.0 and 7.0. Throughout its extensive range, however, it will most often be found on a variety of loams, loamy sand, and gravel; with a pH from 4.9 to 9.1 [68,74]. Many studies have shown better survival and growth rates on coarse-textured clayey soils where extensive root proliferation is possible [18]. In Oregon, Pacific ponderosa pine soils are typically less than 40 inches (100 cm) deep and formed from loess and basalt colluvium and bedrock materials. Surface layers have silt loam to silty clay loam textures with greater than 35 percent rock fragments by volume. Surface rocks usually exceed 10 percent cover [33]. Pacific ponderosa pine has been found on a variety of sites from steep slopes in the plateau region of northern Idaho and Oregon to the flat coastal plains of California [7,48]. Elevation: Elevational ranges of Pacific ponderosa pine are as follows [68]: State Mean ft (m) Range ft (m) ----- ------------- ----------------------------- California 3,242 (988) 348 to 6,520 (106-1,987 m) Oregon (eastern) 5,400 (1,646) 1,800 to 9,000 (549-2,743 m) Oregon (western) 2,800 (853) 2,200 to 3,400 (670-1,036 m) Washington 2,625 (800) 330 to 4,950 (100-1,510 m) Associated forest cover: Pacific ponderosa pine is associated with a rich variety of tree species. Only five of these, however, western juniper (Juniperus occidentalis), Rocky Mountain juniper (J. scoparium), quaking aspen (Populus tremuloides), lodgepole pine, and Oregon white oak (Quercus garryana), are common associates in climax stands [18]. Understory associates can be catagorized into two groups: a shrub- and forb-rich group and a drier bunchgrass-dominated group. The climax shrub-dominated undergrowth generally includes ninebark (Physocarpus malvaceus), common snowberry, and bitterbrush. Seral site shrubs generally include blue huckleberry (Vaccinium globulare) and bearberry (Arctostaphylos uva-ursi) [9,49,63]. SUCCESSIONAL STATUS : Historically, fire has played the greatest role in the successional status of Pacific ponderosa pine. See FIRE ECOLOGY for further discussion. In many areas of the Pacific Northwest, the first zone above the grasslands is the Pacific ponderosa pine climax. This tree species is shade intolerant and grows most rapidly in near full sunlight [18,74]. There is a strong tendancy for climax pine stands to be even-aged in small groups rather than being truly uneven-aged. Heavy grazing induces effects opposite those of fire. Removal of the grass cover by grazing tends to favor shrub communities. Logging is usually done by a selection-cut method. Older trees are taken first, leaving younger, more vigorous trees as growing stock. This method substantially accelerates the successional trend toward a more climax dominant tree species. Logging also impacts understory species by machine trampling or burial by slash. Clear-cutting generally results in dominance by understory species present before logging, with invading species playing only a minor role in postlogging succession [18,39]. The successional status of Pacific ponderosa pine can be expressed in terms of its successional role, which ranges from seral to climax depending on specific site conditions. It plays a climax role on sites toward the extreme limits of its environmental range and becomes increasingly seral with more favorable conditions. On sites with more favorable moisture, pine encounters greater competition and must establish itself opportunistically. On moist sites it is usually seral to Douglas-fir and the true firs (mainly grand fir and white fir). On severe sites it is climax by default because other species cannot establish. On such sites, establishment is likely to be highly dependent upon the cyclical nature of large seed crops and favorable weather conditions [62]. SEASONAL DEVELOPMENT : In California, Pacific ponderosa pine flowers from April to June; cone ripening and seed dispersal occur from August to September [48].

Related categories for Species: Pinus ponderosa var. ponderosa | Pacific Ponderosa Pine

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Information Courtesy: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory. Fire Effects Information System

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