You are here
Quercus taxonomy
Quercus kelloggii Newb.
EOL Text
There are two habitat or plant ''Q. kelloggii'' may be the dominant tree in certain stands, and is ofassociation types where ''Quercus kelloggii'' primarily occurs. First is the Mediterranean California Lower Montane Black Oak-Conifer Forest as far north as the Klamath Mountains of southwest Oregon and as far south as California's North Coast Ranges and lower western Sierra slopes.
The second type of habitat is defined by North Pacific Oak Woodland plant association, which is found as far north as the Puget Trough, extending through the Willamette Valley and to the Klamath Range of Northern California.
License | http://creativecommons.org/licenses/by-nc/3.0/ |
Rights holder/Author | C. Michael Hogan, C. Michael Hogan |
Source | No source database. |
Calif., Oreg.
License | http://creativecommons.org/licenses/by-nc-sa/3.0/ |
Rights holder/Author | eFloras.org Copyright © Missouri Botanical Garden |
Source | http://www.efloras.org/florataxon.aspx?flora_id=1&taxon_id=233501052 |
California black oak is a component of six forest cover types (11). It is the prime constituent of California Black Oak (Society of American Foresters Type 246) and a major component in two others: Douglas-Fir-Tanoak-Pacific Madrone (Type 234) and Pacific Ponderosa Pine-Douglas-Fir (Type 244). Black oak becomes important in Sierra Nevada Mixed Conifer (Type 243) and Pacific Ponderosa Pine (Type 245) after severe disturbance or fire. The oak is a minor component in Canyon Live Oak (Type 249).
The successional status of California black oak is not clear. It has been implied that the species was climax because the type in which it was a part represented a degree of mesophytism between that of the chaparral and the conifer forest (7). The species was also thought to be more a persistent subclimax than climax.
California black oak, or its fossilized equivalent (Quercus pseudolyrata), was much more widespread in past ages than now. Fossil remains indicate that the species was abundant in sedimentary deposits near Spokane and Ellensburg, WA, in the John Day Valley and Blue Mountains of Oregon, and in northwestern Nevada (6). These deposits date back to the Miocene epoch of 12 to 26 million years ago. Increasing aridity is the probable cause for the smaller natural range of black oak today.
The most common botanical associate of black oak is ponderosa pine (Pinus ponderosa var. ponderosa). The two species intermingle over vast acreages, except that black oak is found at lower elevations, on sites too poor to support pine, and in certain areas within the redwood region of California where pine does not grow. Another exception is that this oak is rarely found in Interior Ponderosa Pine (Type 237) (11). In California and Oregon, therefore, where the natural ranges of the two species coincide, ponderosa pine sites generally are fertile ground for black oak. And black oak sites are almost always fertile ground for ponderosa pine.
At lower elevations, black oak often serves as a nurse tree to conifers. Ponderosa pine, Douglas-fir (Pseudotsuga menziesii), and incense-cedar (Libocedrus decurrens) seedlings often become established beneath the sheltering crowns of large black oaks while adjacent ground remains bare (2).
A rule-of-thumb is that black oak never grows through a stand of ponderosa pine but can grow through brush (9). Without disturbance, black oak is eventually crowded out of the best sites and remains only as scattered remnants in mixed-conifer forests. Here it often exists on "islands" of soil or terrain not favorable for natural regeneration of conifers.
Black oak grows individually or in groves, some of which are quite extensive. Usually each grove is of one age-class, the result of sprouting after fire (34). Rarely does it exist as an understory, especially beneath a closed canopy. The species is usually a component of hardwood stands or of mixed hardwood and conifer forests. Tanoak (Lithocarpus densiflorus) and Pacific madrone (Arbutus menziesii) are the most common hardwood associates of black oak. Other hardwood associates at lower elevations are Oregon white oak (Quercus garryana), interior live oak (Q. wislizenii), coast live oak (Q. agrifolia), Engelmann oak (Q. engelmannii), and blue oak (Q. douglasii). At higher elevations Pacific dogwood (Cornus nuttallii), bigleaf maple (Acer macrophyllum), California-laurel (Umbellularia californica), and canyon live oak (Quercus chrysolepis) intermix with California black oak.
Besides ponderosa pine, conifer associates at low elevations are knobcone pine (Pinus attenuata), Monterey pine (P. radiata), Digger pine (P. sabiniana), and redwood (Sequoia sempervirens). At intermediate elevations within the natural range of California black oak are California white fir (Abies concolor var. lowiana), grand fir (A. grandis), incense-cedar, Coulter pine (Pinus coulteri), sugar pine (P. lambertiana), giant sequoia (Sequoiadendron giganteum), Douglas-fir, California torreya (Torreya californica), and bigcone Douglas-fir (Pseudotsuga macrocarpa). At higher elevations black oak intermingles with western juniper (Juniperus occidentalis) and Jeffrey pine (Pinus jeffreyi).
Shrub associates include at least 30 species, some of the most important of which are greenleaf manzanita (Arctostaphylos patula), whiteleaf manzanita (A. viscida), deerbrush (Ceanothus integerrimus), bear-clover (Chamaebatia foliolosa), oceanspray (Holodiscus discolor), Brewer oak (Quercus garryana var. breweri), Sierra coffeeberry (Rhamnus rubra), Sierra gooseberry (Ribes roezlii), and poison-oak (Toxicodendron diversilobum). In parts of Shasta and Trinity Counties, and perhaps elsewhere, black oak itself takes a shrub form. The stands so formed usually are dense and tangled-ideal habitat for deer and upland game.
Except on the fringe of black oak's natural range, especially at the lowermost elevations, most shrubs generally are not competitive, nor particularly abundant over most of the forest land where black oak grows. After heavy cutting or fire, however, some of the more aggressive shrubs often compete strongly with black oak sprouts.
When compared with 15 of its most common shrub associates in the Klamath Mountains of northern California, black oak ranked ninth in need of soil moisture, third in demand on soil nutrients, eighth in terms of tolerance, and first in rapidity of sprouting (32). The species is able to withstand high moisture stress (37) and to become established and grow well on harsh sites where few other species are capable.
Flowering late spring.
License | http://creativecommons.org/licenses/by-nc-sa/3.0/ |
Rights holder/Author | eFloras.org Copyright © Missouri Botanical Garden |
Source | http://www.efloras.org/florataxon.aspx?flora_id=1&taxon_id=233501052 |
More info for the terms: competition, cover, frequency, litter, mast, presence, tree
California black oak is a critical species for wildlife. Oaks (Quercus spp.) may be the single most important genus used by wildlife for food and cover in California forests and rangelands [60,253], and California black oak occupies more total area in California than any other oak species [31]. Its acorns are the largest of the western oaks [27], and are heavily consumed by livestock, mule deer, feral pig, rodents, mountain quail, wild turkey, jays, and woodpeckers [87,139]. California black oak and mixed-oak woodlands are important wildlife habitat. In riparian oakwoods of the Central and North Coast Ranges, for example, California black oak and associated oaks form riparian corridors within agricultural areas. A night-camera survey in a mixed-oak riparian woodland in Napa County's wine country showed that many predators, including striped skunk, bobcat, coyote, gray fox, and mountain lion, used the oak woodland corridors extensively. Predator usage was significantly greater (P=0.03) in wide, undisturbed corridors compared to narrow or denuded corridors [99].
The leaves and berries of Pacific mistletoe, which commonly infects California black oak, are important foods for a variety of birds and small mammals (review by [76]).
Cattle make heavy use of California black oak for food and cover [180,212]. They browse California black oak leaves and stems, and forage for acorns on trees and on the ground [212]. California black oak-mixed oak woodlands are important rangelands [245]. A Blodgett Forest Research Station study of forage use by free-range cattle found consumption of California black oak peaked in June (17.8% of diet), with use extending to August (10.2% of diet) [113]. Cattle may consume much of the California black oak acorn crop in some years. To reduce competition for acorns between mule deer and cattle, Kie and Loft [114] recommend removing cattle from oak rangelands during acorn drop.
Mule deer: California black oak woodlands and forests provide mule deer (Columbian black-tailed deer) cover and habitat [118]. Mule deer browse California black oak [207,212], and acorns are important mule deer forage. Mule deer use of California black oak browse peaks in summer and is lowest in winter [131]. They rely on the acorns after acorn drop: California black oak acorns constitute an average of 50% of the fall and winter diets of Columbian black-tailed deer in high mast years [195]. Fawn survival rates generally increase or decrease with the size of California black oak acorn crops [42]. Mule deer eat the acorns from fall through spring. On the Tehama Deer Range of California, California black oak acorns constituted a mean of 27.8% of the October mule deer diet and 21% of the April diet [147]. California black oak acorns are especially important in early spring just before and during snowmelt [147], when new green forage is still scarce.
Other large mammals: American black bear use California black oak forest types heavily for spring, summer, and fall cover [42]. American black bears and northern raccoons eat California black oak acorns [139]. Ponderosa pine-California black oak forests provide habitat for mountain lions and other large predators [221]. Foothill oak woodlands with a California black oak component provide prime mountain lion hunting grounds [52].
Small mammals: Chipmunks and squirrels make heavy use of acorns (Quercus spp.) [139]. California black oak acorns comprise about 50% of the fall and winter diets of western gray squirrel during high mast years [195]. Plant communities with a substantial California black oak component are good habitat for rodents. California black oak and white fir are the principal tree species associated with northern flying squirrels in the San Bernardino Mountains, where the squirrels are at the southern edge of their range. On the Plumas National Forest, 37% of long-eared chipmunk, 54% of Townsend's chipmunk, 36% of yellow-pine chipmunk, and 50% of golden-mantled ground squirrel habitat use was on early seral conifer burns where the dominant vegetation was California black oak and mixed chaparral species [253]. California black oak provides cover for dusky-footed woodrats, a major prey item for California spotted owls [270].
Birds: Many seed predators consume California black oak acorns, and California black oak is a preferred foraging substrate for many birds [5,166]. Acorn-consuming songbirds include blackbirds, chickadees, crows, goldfinches, larks, Clark's nutcrackers, nuthatches, sapsuckers, and thrashers [139]. California black oak acorns form a majority of the acorn woodpecker's diet in some areas [137,205]. The acorns are important in the fall diet of band-tailed pigeons [173,223], comprising 3.2% of their September diet and 7.7% of their November diet [147]. All of 68 bird species observed in oak woodlands of the Tehachapi Mountains of California used California black oak for part of their foraging activities. The acorn woodpecker, the northern oriole, and the Nashville warbler showed greatest preference for California black oak [29]. In a mixed-conifer forest on the Blodgett Research Station, red-breasted and chestnut-back chickadees foraged on California black oak significantly more than expected (P<0.05) based upon California black oak's frequency [1,39]. A Blodgett Forest Research Station study of bark-foraging birds showed the pileated woodpecker made high use of California black oak branches while hawking [166]. As a guild, insect-gleaning birds preferred (preference value L=0.05) California black oak more than expected based on availability [5]. Morrison and others [39] express concern that managing only for pines in mixed-conifer forests may reduce population densities of chickadees and other gleaning birds that depend on California black oak and other hardwoods for food and cover.
Protected animals: California black oak woodlands are important habitat for several rare and threatened species. California black oak provides diversity and nesting and other cover for California spotted owls [164,228,265] and flammulated owls [146]. A Sierra National Forest-Sequoia Kings Canyon National Park study showed California spotted owls in mixed-oak woodlands nested in California black oaks more often than expected (P<0.05) based on California black oak's relative abundance [175]. In a study of Sierra Nevada fisher populations, fishers in mixed-conifer-California black oak habitat had smaller home ranges than fishers in Sierra lodgepole pine (Pinus contorta var. murrayana) or Jeffrey pine habitats. The authors suggested that fisher home range requirements were smaller in mixed forest because California black oak and other montane oaks increased habitat quality [270,276]. Stewart and others [237] discuss habitat needs of sensitive-listed southern California herptiles in mixed-conifer forests with a California black oak component.
Arthropods: The bole and limbs of California black oak are habitat for many arthropods species. Some of these arthropods are important to gleaning and other insectivorous birds [39]. Schowalter and Zhang [217] provide a compilation of arthropod family assemblages found on branches of California black oak and associated woody species on the Teakettle Experimental Forest.
Tree cavities filled with rainwater or detritus form unique habitat for aquatic- or detritus-based invertebrate communities. Mosquitoes are among the insects that live in rain-filled California black oak cavities during the larval stage. Some invertebrates are largely or entirely restricted to cavities in California black and other oaks during a portion of their life cycle. Woodard and others [274] detail invertebrate species presence and food chains in cavities of California black and other oaks in Mendocino County, California.
Palatability/nutritional value: California black oak browse is highly palatable to cattle and mule deer, but is less valuable for other ungulates [212]:
Palatability of California black oak foliage |
|
Animal | Rating |
mule deer | good to excellent |
cattle | poor to good |
domestic sheep | poor to fair |
horses | useless to poor |
California black oak acorns have a high concentration of lipids [149]. They provide little nutrition for herbivore growth and bone-building but are an excellent source of energy due to the high fat content [212]. California black oak leaves may provide the highest food value of all the western oak browse for fattening cattle [136].
California black oak acorns are highly palatable to livestock and mule deer. In a study in the Cuyamaca Mountains of southwestern California, mule deer preferred California black oak acorns over any other forage. Mule deer would search through forest litter for acorns even during spring, when new, palatable sprouts and herbs were readily available [37]. Mean nutritional values of California black oak acorns are given below (review by [59]):
Percent (%) composition of California black oak acorns |
|
crude protein | 3.43 |
crude fiber | 14.07 |
fat | 11.05 |
ash | 1.14 |
calcium | 0.09 |
phosphorus | 0.06 |
tannins | 1.81 |
Scrivner and others [218] provide a mineral analysis of California black oak acorns collected on the Hopland Field Station.
Cover value: Wildlife use California black oak heavily for cover. California black oak provides valuable shade for livestock and wildlife during the hot summer months [59]. Cavities in California black oak provide den or nest sites for owls, woodpeckers, tree squirrels, and American black bears [60,271]. Cavity nesters also use oracle oak [271]. For further information, see Importance to Livestock and Wildlife.
For current distribution, please consult the Plant Profile page for this species on the PLANTS Web site. The tree ranges from Baja, California on the south up into southwestern Oregon. Mountain ranges where it is found include the San Bernardino, San Jacinto, Agua Tibia Mountains, and the Tehachapi Mountains in southern California, the Santa Cruz and Santa Lucia Mountains in central California, the Sierra Nevada, and the Klamath and Cascade Mountains of northern California and southern Oregon. It spans an elevation of 200 to 2400 m. and takes a shrubby form at higher elevations. It can be found in northern oak woodlands, mixed conifer forests and mixed evergreen forests.
Fire is black oak's worst enemy. Crown fires kill trees of all ages and ground fires are often fatal. Only a little radiative heat kills the cambium and only a small amount of flame along the trunk leaves long vertical wounds. Bark thickness on mature trees varies from 2 to 5 cm (1 to 2 in), but even the thickest bark provides little insulation to fire. Scars from burning can become a point of entry for fungi. On larger trees, repeated fires often enlarge old scars, sometimes toppling the tree. Fluctuations in weather also cause injury. Heavy, wet snow breaks branches and stems, particularly at forks, and sudden high temperatures following cool wet weather severely injure leaves (25).
California black oak is especially susceptible to fungi. Heart rot of the bole and large limbs of living trees, caused mainly by two pathogens, Inonotus dryophilus and Laetiporus sulphureus, is the principal damage (24). These rots enter the tree through broken branches or open wounds resulting from fire or logging. Both fungi often reduce the bole and large limbs of older, decadent trees to mere shells. The hedgehog fungus (Hydnum erinaceus) also is found in the heartwood of living trees and Polyporus adustus in the sapwood, though neither is prevalent.
By the time a natural black oak stand is 85 years old, the proportion of infected trees begins to increase rapidly. Almost 40 percent of trees 110 to 120 years old show incipient heart rot (21). Rotation age of stands grown for wood products could be influenced by this incidence-age relationship.
Another serious pathogen, Armillaria mellea, causes decay of the roots and butt of older decadent black oak. Sometimes it weakens the root system so much that the tree topples over on a perfectly calm, still day (36). This pathogen is indigenous in black oak, but younger vigorous trees do not seem to be affected by it.
A comparatively recent damaging agent to black oak in the San Bernardino Mountains of southern California is air pollution. Although the oak appears less susceptible to air pollution damage than associated conifers, radial growth has decreased in some trees (12). Where high ambient oxidant air pollution levels are chronic, damage to California black oak is expected to be significant (26).
One virulent pathogen that black oak escapes, and indeed is resistant to, is Heterobasidion annosum (14). For this reason, California black oak is being planted in numerous infection centers in southern California forests where conifers are dead or dying.
California black oak is prone to several leaf diseases including the oak leaf fungus (Septoria quercicola), oak anthracnose (Gnomonia veneta), powdery mildews (Microsphaera and Sphaerotheca spp.), a leaf blister fungus (Taphrina caerulescens), a leaf rust (Cronartium spp.), and true mistletoe (Phoradendron villosum subsp. villosum). Damage from each of these pests has not been determined but loss of growth increment probably is minor.
Animal damage to black oak is mostly from browsing. Foliage is eaten during all seasons, but especially in spring when new growth is tender and in winter when twigs are eaten. Deer eat acorns, seedlings, sprouts, and foliage. Even in midsummer, newly germinated seedlings with acorns attached often are consumed (8). Occasionally, browsing is fatal. In Mendocino County, CA, for example, a deer population of 1/2.4 ha (1/6 acres) almost eliminated oak over large areas of the Coast Range. Cattle also browse black oak, but in national forests, at least, their numbers are declining.
Many insects derive sustenance from black oak. The damage is usually secondary, reducing growth but seldom killing trees. Among sucking insects, the pit scales (Asterolecanium minus and A. quercicola) have the greatest potential for damage (4). The most destructive insect, however, is probably the carpenterworm (Prionoxystus robiniae), whose larvae mine the wood of trunk and limbs and cause injuries that appear later as defects in lumber (16).
Other insects are capable of heavy damage, especially when infestations become epidemic. The Pacific oak twig girdler (Agrilus angelicus) is the most damaging insect to oak in southern California during drought years (4). In northern California, the California oakworm (Phryganidia californica) is noted for defoliating trees. So is the fruit-tree leafroller (Archips argyrospila) which, in 1968, caused heavy damage throughout a wide area in the Sacramento River drainage.
California black oak sprouts profusely after trees are cut or burned. Most sprouts develop from latent buds, which lie under the bark at, or slightly above, the root collar. Other sprouts originate from the top of the stump or between the top and the ground. These are called stool sprouts and are undesirable for two reasons. They are weakly attached to the parent stump and frequently broken off by wind and snow, and are prone to heart rot at an early age.
The size and vigor of the parent tree determine the number of sprouts and their height and crown spread. In general, stumps from larger trees produce a larger number of sprouts and more vigorous ones. Only old, moribund trees fail to produce sprouts after cutting.
Low stumps of nearly all diameters produce many more sprouts than high stumps. High-stumping an older, larger tree yields undesirable stool sprouts, and often no sprouts from below ground.
Root crown sprouts grow vigorously, especially in full sunlight. Forty-nine stumps were studied in stands on a good site in the northern Sierra Nevada. Sprout density, height, and crown width were evaluated in clearcuttings and in shelterwood stands where 50 percent of the basal area had been removed (22). Number of sprouts, crown width, and especially height growth were consistently greater in the clearcuttings (table 1).
Table- Development of California black oak stump sprouts in a northern Sierra Nevada forest 10 years after cutting Year after cutting Sprouts per stump Height Crown width Clearcut Shelterwood Clearcut Shelterwood Clearcut Shelterwood no. m 0 55+ 28 -- -- -- -- -- 2 55+ 23 1.2 0.9 1.2 0.7 4 35 17 2.4 1.2 1.8 1 6 23 15 3.7 1.5 2.3 1.2 8 18 13 4.9 1.8 2.6 1.6 10 15 12 6 2.1 2.9 2.2 no. ft 0 55+ 28 -- -- -- -- 2 55+ 23 4 3 4 2 4 35 17 8 4 6 3 6 23 15 12 5 8 4 8 18 13 16 6 9 5 10 15 12 20 7 10 7 The environment typical of shelterwood cuttings apparently is more favorable to a cynipid gall wasp (Callirhytis perdens) than that in clearcuttings. Damage to terminal shoots by this pest is greater under shelterwood stands, accounting in part for the poorer height growth of sprouts. Thinning sprouts to three or four per stump at age 4 showed no gain in height but resulted in undesirable damage to the bole from sunscald and increased forking of stems (22).
Young black oak sprouts grow faster in height than other vegetation, including coniferous associates. Consequently, they remain dominant for many years. Although black oak seedlings extend the species into new areas, sprouts keep the oak in the same area and are responsible for regenerating many more stands than seedlings. Only after the living crown has moved considerably up the bole does black oak begin its role as a nurse tree, aiding conifers to become established and grow to equal or dominant positions in the stand.
Propagation by layering, rooting of cuttings, or grafting has not been reported. But the wartime shortage of cork in the 1940's stimulated grafting of cork oak (Quercus suber) to black oak stocks. In a greenhouse trial, 70 percent of the grafts were successful (27).
Several attributes qualify the wood of California black oak for commercial use: attractive grain and figure for paneling and furniture, hardness and finishing qualities for flooring, and strength properties for pallets, industrial flooring, and other uses (19). The forks of open-grown black oaks were put to good use in the 1870-80's in Mendocino County.
Those of specific dimensions were used as "naturally assembled" ship keels and ribs. Wood products currently produced are high grade lumber and pallets, industrial timbers, sawdust for mulching, and bulk and prepackaged firewood. The wood is prized for fuelwood and in some areas unrestricted cutting is eliminating oak stands.
Although not presently utilized, black oak acorns, high in edible oils, are a potential source for thousands of tons of human food (38).
More info for the terms: frequency, natural, root crown, tree
This description provides characteristics that may be relevant to fire ecology, and is not meant for identification. Keys for identification are available (for example, [66,98,100]).
Form: California black oak is typically 30 to 80 feet (9-25 m) in height and 1 to 4.5 feet (0.3-1.4 m) DBH at maturity. Large trees may exceed 120 feet (36 m) in height and 5 feet (2 m) DBH. On open, fertile sites form is tall and straight, with a clean bole and a broad, rounded crown [188]. The champion tree, on the Siskiyou National Forest of Oregon, is 124 feet (38 m) tall, 338 inches (859 cm) in circumference, and has a 115-foot (35 m) spread [9]. California black oak's lower branches may nearly touch the ground, form a browse line, or be clear from the bole for 10 to 40 feet (3-12 m) above ground [188]. In closed stands, the crown is narrow and slender in young trees and irregularly broad in old trees. Trunks are usually free of branches for 20 to 40 feet (6-12 m) in closed stands. Old trees often have forked trunks that are decayed and hollow [193]. California black oak sometimes grows in scrub form on dry, infertile sites [42,147].
Aboveground morphology: California black oak has thin, smooth bark when young. Bark becomes moderately thick, deeply fissured, and platy with age. Bark of mature trees is 0.75 to 2 inches (1.9-5.1 cm) thick [98,170]. California black oak is the only western oak species in the red oak subgenus that is deciduous [275]. The deeply lobed leaves are typically 4 to 8 inches (10-20 cm) long [170]. Flowers are unisexual. Staminate flower clusters (catkins) emerge from the leaf axils of the previous year's growth [33,147]. Pistillate flowers are solitary and develop from current-year leaf axils [33]. Acorns are relatively large in this species, from 1 to 1.2 inches (2.5-3 cm) long and 0.6 to 0.7 inch (1.5-1.8 cm) wide [6,98,170].
Oracle oak resembles California black oak. It is readily identified in winter by its sparse evergreen foliage, which contrasts with California black oak's winter-deciduous character [147].
Roots: California black oak grows from one to several taproots that may penetrate to bedrock. It has large, laterally spreading roots that extend from vertical ones, and many surface roots. Trees on shallow soils tend to have more vertical roots than trees on deep soils [149]. California black oaks on shallow or fine-textured soils may have vertical roots and no apparent taproot. Taproots of trees on clay or other fine-textured soils usually decay [149]. Roots often graft when root crown sprouts are thick, forming a dense, interclonal mass of roots [149,209].
Physiology: California black oak is highly drought tolerant. A Hastings Natural History Reservation study found that among 5 associated oak species, California black oak and blue oak were the most drought tolerant based on xylem water potentials [120].
Stand and age class structure: California black oak occurs in pure stands, mixed stands, and scattered groves. Pure stands usually indicate sites unfavorable to conifer growth or repeated disturbance such as fire or logging [62,147]. In pure stands, California black oak is usually even-aged, originating from sprouts after a top-killing event such as logging or fire. Such stands are usually less than 125 years old. Some seedlings may occur in these mostly even-aged stands [148]. |
|
© Br Alfred Brousseau, Saint Mary's College |
Age class structure varies in mixed stands with a California black oak component. In stands where fire has been excluded, there is a trend towards mostly mature (>50 years) California black oaks, few seedlings and sprouts, and almost no saplings [17]. In a Placer County, California, mixed-conifer-California black oak stand, mean California black oak age was 148 years, ranging from 58 to 356 years [75]. Disturbance history of the site was not available. Age class structure is not always skewed toward old trees, however. Tree coring on the Hall Canyon Research Natural Reserve in the San Jacinto Mountains of California showed a California black oak age class structure dominated by true seedlings (not sprouts), with a mean frequency of 290 seedlings/900 m². The next largest age class was 60- to 79-year-old "saplings", with mean frequency of 8.5 saplings/900 m². Trees in the 120- to 139-year-old age class, the oldest represented, were slightly more abundant than trees in the sapling class (mean frequencies of 2 trees/900 m² and 2.5 trees/900 m² for 120- and 139-year old trees, respectively). There were no dead California black oaks. Study sites were logged in the early 1900s, and fire had been excluded since logging [213] (see Size class recruitment for further information).
Individual California black oaks may live 500 years or more [42,147,227], although 100 to 200 years is more typical [225].