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Introductory

SPECIES: Quercus agrifolia | Coast Live Oak
ABBREVIATION : QUEAGR SYNONYMS : NO-ENTRY SCS PLANT CODE : QUAG COMMON NAMES : coast live oak encina California live oak TAXONOMY : The currently accepted scientific name for coast live oak is Quercus agrifolia Nee. It has been placed in the black oak subgenus (Erythrobalanus) [10,33,35,46,58]. Recognized varieties are as follows: Q. agrifolia var. agrifolia [18] Q. agrifolia var. frutescens Engelm. [35,58] Q. agrifolia var. oxyadenia (Torr.) J. T. Howell [35,46,58] Quercus agrifolia variety frutescens is a shrubby chaparral form of coast live oak. Quercus agrifolia variety oxyadenia has densely stellate leaves and occurs in interior cismontane regions of Riverside and San Diego counties, California [58]. Coast live oak may hybridize with California scrub oak (Q. dumosa), but the cross is not definite [58]. The following crosses have been determined: (1) Q. agrifolia x Q. kelloggii (California black oak) = Q. XChasei McMinn This hybrid produces acorn that mature in the second year and is found in Monterey and Santa Cruz counties [58]. (2) Q. agrifolia var. oxyadenia x Q. kelloggii = Q. XGanderi C. B. Wolf This hybrid produces acorns that mature in 1 year and occurs in San Diego County [10,46,58]. (3) Q. agrifolia var. frutescens x Q. wislizenii (interior live oak) [10,35,85]. LIFE FORM : Tree, Shrub FEDERAL LEGAL STATUS : No special status OTHER STATUS : The California walnut (Juglans californica) woodland, where coast live oak frequently codominates, is severely threatened by urbanization. The Nature Conservancy, in cooperation with the state of California, has listed it as one of California's rare and imperiled natural communities [4,11,34]. COMPILED BY AND DATE : Janet L. Howard, 1992 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Howard, Janet L. 1992. Quercus agrifolia. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Quercus agrifolia | Coast Live Oak
GENERAL DISTRIBUTION : Coast is distributed along the Coast, Transverse, and Peninsular ranges and the Sierra de Juarez from Sonoma County, California south to Canada El Piquillo, Baja California [5,35,54,58]. Limited inland populations occur along watercourses in the Central Valley [38,42]. Coast live oak is also found on the Channel Islands of Santa Rosa and Santa Cruz [18,65]. ECOSYSTEMS : FRES20 Douglas-fir FRES21 Ponderosa pine FRES28 Western hardwoods FRES34 Chaparral - mountain shrub FRES42 Annual grasslands STATES : CA MEXICO ADMINISTRATIVE UNITS : CHIS PAAL PINN PORE SAMO BLM PHYSIOGRAPHIC REGIONS : 3 Southern Pacific Border KUCHLER PLANT ASSOCIATIONS : K006 Redwood forest K009 Pine - cypress forest K029 California mixed evergreen forest K030 California oakwoods K033 Chaparral K035 Coastal sagebrush K048 California steppe SAF COVER TYPES : 221 Red alder 231 Port-Orford-cedar 232 Redwood 234 Douglas-fir - tanoak - Pacific madrone 244 Pacific ponderosa pine - Douglas-fir 245 Pacific ponderosa pine 246 California black oak 248 Knobcone pine 249 Canyon live oak 250 Blue oak - Digger pine 255 California coast live oak SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : Coast live oak is the most conspicuous tree in lower elevation woodlands of southern California [33]. The southern oak woodland, describing various woodlands of southern California, contains many phases in which coast live oak is dominant or codominant. The coast live oak phase varies in structure from dense stands to open savannas [17,19]. Coast live oak woodland may be monospecific or mixed. Frequent codominants include bigcone Douglas-fir (Pseudotsuga macrocarpa) and Engelmann oak (Quercus engelmannii) [32]. Southern California coast live oak woodland also has a chaparral phase, dominated by shrubby coast live oak subjected to frequent fire. Canyon live oak (Q. chrysolepis) is a common chaparral codominant [39]. Coast live oak frequently codominates in California walnut woodland [32]. Coast live oak is a frequent dominant or codominant of mixed evergreen forests of northern and southern California [33,79], where these oaks codominate with valley oak (Q. lobata), blue oak (Q. douglasii), California black oak, interior live oak, California bay (Umbellularia californica), and Digger pine (Pinus sabiniana) [17]. In riparian areas, it codominates with western sycamore (Plantus racemosa), white alder (Alnus rhombifolia), and red alder (A. rubra). Classifications naming coast live oak as a dominant or indicator species are as follows: A classification system for California's rangelands [1]. Blue oak communities in California [2]. California valley grassland [11]. Association types in the North Coast Ranges of California [17]. Plant communities of Santa Rosa Island, Channel Islands National Park [18]. Plant communities of Ring Mountain Preserve, Marin County, California [27]. Oak woodland [34]. Preliminary descriptions of the terrestrial natural communities of California [37] Vegetation types of the San Bernadino Mountains [39]. The southern California islands [65]. Mixed evergreen forest [79].

VALUE AND USE

SPECIES: Quercus agrifolia | Coast Live Oak
WOOD PRODUCTS VALUE : Canyon live oak wood is primarily used for fuel. Some commercial charcoal is made from the wood. It is unsuitable for lumber, as it cracks easily and warps badly [67]. IMPORTANCE TO LIVESTOCK AND WILDLIFE : This species provides critical wildlife habitat. Coast live oak woodlands are preferred habitat for black bear and black-tailed deer [69]. They are also preferred by the federally endangered least Bell's vireo [60]. Western sycamore-coast live oak communities in the South Coast Ranges provide wintering grounds for 32 species of birds, at a density of 251 birds per acre (620/ha) [25]. The federally endangered least tern nests within this community [44]. Coast live oak provides browse for black-tailed deer and various rodents and lagomorphs [77]. Roots are eaten by feral pig and pocket gopher [63]. Acorns are heavily consumed by black bear, feral pig, black-tailed deer, rodents, and various upland game and nongame birds [77]. Coast live oak litter provides excellent hunting opportunities for the insectivorous vagrant and ornate shrews [69]. Cattle eat coast live oak sprouts [64]. Most livestock do not readily browse mature foliage, although goats will eat it year-round [31]. Livestock readily consume the acorns [77]. PALATABILITY : The palatability of coast live oak foliage has been rated useless for cattle and horses, poor to useless for sheep, and fair to poor for black-tailed deer [77]. NUTRITIONAL VALUE : Nutritional information on coast live oak foliage is scant. One study found the protein content of leaves was 4.6 percent in December. Springtime protein levels were not determined. However, protein content of interior live oak, a closely related species, was 17.6 percent in May [8]. Percent composition of coast live oak acorns is 9 percent water, 6.26 percent protein, 16.75 fat, and 54.57 percent carbohydrate [3]. COVER VALUE : NO-ENTRY VALUE FOR REHABILITATION OF DISTURBED SITES : Coast live oak is favored for use in rehabilitation projects in the Coast Ranges. It is used for watershed improvement, restoration, and wildlife rehabilitation projects [29,40,64]. In the Sepulveda Wildlife Reserve of Los Angeles County, nursery seedlings were planted for slope stabilization and wildlife habitat improvement. Survival of these seedlings was between 40 to 75 percent after 3 years [61]. Transplants along the Santa Margarita River in San Diego County have also shown good survival [72]. In eastern Ventura County, coast live oak was planted to help restore the ecotone between saltbush (Atriplex spp.), black sage (Salvia mellifera), and annual grassland communities [62]. Coast live oak is also established by acorn plantings. In the Berkeley Hills, seedlings grown from locally collected acorns showed 75 percent survival in their first year. Seedlings were hand-watered twice during summer because of drought conditions [73]. Seedling survival is enhanced by weeding competitors, providing protection against herbivores and acorn predators with above- and belowground wire caging, and providing microsite shading. Acorns are collected from local oaks in late fall. Planting density recommendations and other cultivation methods have been detailed [59,81]. Large oak trees slated for removal because of roadway or other construction have been successfully transplanted onto favorable sites using heavy equipment [20]. OTHER USES AND VALUES : NO-ENTRY MANAGEMENT CONSIDERATIONS : North coast populations of this tree are stable, but the species is in decline in southern California [57,80]. Threats to this oak include urban and rural development, increased recreational use of oak woodlands, and the cutting of trees for firewood [67,80]. Factors hampering seedling recruitment are discussed under regeneration. Diseases: Trees watered during summer may be invaded by root (Armillaria mellea) and crown (Phytophthora spp.) rots. During drought, the fungus Diplodia quercina can cause branch dieback. Pit scale insects (Asterolecanium minus) damage foliage [36].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Quercus agrifolia | Coast Live Oak
GENERAL BOTANICAL CHARACTERISTICS : Coast live oak is a native, drought-resistant, evergreen tree. It is typically from 20 to 40 feet (6-12 m) tall, occasionally reaching up to 80 feet (24 m) in height. Trees usually range from 1 to 4 feet (0.3-1.2 m) in d.b.h. Open-grown crowns are broad and dense, with foliage often reaching the ground. Trunks are usually short, forking into large, wide-spreading branches. Trees in dense stands have irregular crowns and few lower branches. The bark of young trees is smooth, developing deep furrows with age. The inner bark and cork layers are thick [22,67]. The root system is composed of a deep taproot, usually nonfunctional in large trees; several deep main roots tapping groundwater; extensive horizontal root branches; and surface-feeding roots [19,66]. Coast live oak stands are typically from 40 to 110 years of age [22]. Individual trees may live over 250 years [67]. RAUNKIAER LIFE FORM : Phanerophyte REGENERATION PROCESSES : Flowering of coast live oak is triggered by warm temperature. This is in contrast to many other black oaks, which flower in response to photoperiod [85]. Trees are wind pollinated. Information on the age of sexual maturity and maximum production of acorns is lacking. Coast live oak retains its acorns longer than other California oaks. Most of its acorns are dropped in fall, but some remain attached to trees until spring. This is an adaptive advantage because these acorns are less likely to be consumed by ground-dwelling seed predators. Animals such as squirrels, magpie, and scrub jay, however, consume tree-borne acorns. Acorns fall beneath the parent plant or are disseminated by various birds and rodents. Seed-caching animals such as scrub jay and California ground squirrel are important to species survival, as acorns buried by these animals are most likely to develop into seedlings [15]. Coast live oak is the only black oak in California whose acorns develop in 1 year [10,67]. There is no dormancy requirement, and acorns germinate 15 to 50 days after falling [12,32,55]. Reports of seed viability vary. Griffin [32] found 100 percent viability of acorns collected in Carmel Valley, while Mirov and Kraebel [55] reported 73 percent germination in acorns collected in Berkeley. Acorns with low moisture content show higher rates of germination and produce taller seedlings than do acorns with high moisture content, but unviable seed is not a serious problem for this species [41,59]. Predation of fallen acorns, however, is very high, and loss of potential trees is considerable. Acorn predators may consume 100 percent of a year's mast. Acorn predation and loss of seedlings to herbivory have been cited as the primary cause of current recruitment failure in southern California populations of coast live oak [59]. Seedling survival rates are low. At sites on the Central and South Coast ranges, the current sapling-to-tree ratios are 1:3 or worse [57]. Seedling top-growth is slow under natural conditions, with early development concentrated on rapid, early root growth [49]. Black-tailed deer cause considerable mortality of young trees. Griffin [32] found seedlings on the most favorable sites at the Hastings Natural History Reservation of Carmel Valley required a minimum of 20 years to grow above the browse line. Livestock also limit recruitment. Natural establishment of coast live oak resumed in Solstice Canyon Park in the Santa Monica Mountains once cattle were removed [64]. Mortality also results from root hebivory by pocket gopher and feral pig, and from drought [15,63]. At the Hastings Natural History Reservation, survival of 2-year-old seedlings protected from herbivory was 69 percent. By the fourth year, however, 100 percent of these seedlings had succumbed to drought [32]. Recruitment is best among germinants growing in shade. Eighty percent of seedlings found on sites in the Santa Ynez Valley of Santa Barbara County were growing under purple sage (Salvia leucophylla) or California sagebrush (Artemisia californica). Another 15 percent were under mature coast live oak. Mortality due to herbivory was considerably higher among seedlings under parent trees [13]. Under ideal conditions, coast live oak is capable of rapid growth. Nursery seedlings have attained heights of 5 to 8 feet (15.2-24.4 m) in 2 years [81]. Vegetative: Coast live oak sprouts from the root crown and trunk following cutting or burning [22,66,67]. SITE CHARACTERISTICS : Coast live oak occurs in a mediterranean climate, characterized by mild, wet winters and hot, dry summers. Climate severity is modified near the coast, where trees receive more annual precipitation than do inland populations [22]. Trees generally occur on mesic sites such as north slopes, alluvial terraces, and canyon bottoms [11]. In riparian areas, coast live oak occurs in swales or on upper banks [24,51]. Soil textures vary with site. Low-elevation coastal populations of coast live oak generally grow in loam, while higher elevation coastal populations are associated with shaley clay-loam soil. Inland populations are found in sandy soil [22]. Trees on the southern California islands grow in clay or clayey loam [18]. Coast live oak will tolerate serpentine soils [27]. The elevational range for northern populations of coast live oak is sea level to 3,000 feet (914 m) and for southern populations, sea level to 5,000 feet (1,524 m). Associated overstory species not previously mentioned include tanoak (Lithocarpus densiflora), birchleaf mountain-mahogany (Cerocarpus betuloides), Monterey pine (Pinus radiata), and California boxelder (Acer negundo ssp. californicum) [1,9,14,26,53]. Understory associates: Common shrub associates include California blackberry (Rubus ursinus), poison-oak (Toxicodendron diversilobum), ocean spray (Holodiscus discolor), coffeeberry (Rhamnus californica), toyon (Heteromeles arbutifolia), chamise (Adenostoma fasciculatum), California scrub oak (Quercus dumosa), manzanita (Arctostaphylos spp.), California wild grape (Vitis californica), California sagebrush, and jimbush ceanothus (Ceanothus sorediatus). Herbaceous associates include black sage, purple sage, brakenfern (Pteridium aquilinum), California buckwheat (Eriogonum fasciculatum), brome (Bromus spp.), wild oat (Avena fatua), Mediterranean barley (Criteston marinum spp. gussoneanum), smallflower melicgrass (Melica californica), gland cinquefoil (Potentilla glandulosa), and common yarrow (Achillea millefolium) [1,19,29,30,70]. Micorrhizal associates: Coast live oak is commonly infected with Dothiorelli querci and Phytophthora cinnamomi [82]. SUCCESSIONAL STATUS : Facultative Seral Species Coast live oak is tolerant of shade throughout its life [67]. Its successional status varies. Where their ranges overlap, deciduous trees such as blue and California black oaks are seral to coast live oak, and coast live oak represents the climax stage of coastal oak woodlands [6]. McBride [50] , however, reported that coast live oak is seral to the evergreen California bay in some areas of coastal northern California. In mixed evergreen forest, the coast live oak phase is seral to a coniferous element that was removed by logging or fire. On steep slopes or poor sites within this belt, coast live oak represents a topographic or edaphic climax [4]. SEASONAL DEVELOPMENT : The seasonal development of coast live oak is as follows: growth begins: February [56] catkins emerge: March - April [56,58] leaves emerge: February - April [56,58] old leaves shed: after new leaf emergence in spring [67] acorns ripen: September - October [55] damaged acorns aborted: August - October [59] acorns drop: from onset of winter storms through May [15,56]

FIRE ECOLOGY

SPECIES: Quercus agrifolia | Coast Live Oak
FIRE ECOLOGY OR ADAPTATIONS : Coast live oak is the most fire resistant of all California oaks. Adaptations to fire include evergreen leaves, thick bark, and sprouting. Evergreen leaves allow coast live oak to allocate greater amounts of energy to regeneration than to leaf growth. Evergreens are often better able to conserve available nutrients than deciduous species, and are favored in fire-prone settings [52]. Coast live oak bark is mainly composed of live inner bark with little dead outer tissue [68]. The vascular cambium is usually protected. Even where heavily charred, damage typically extends only 0.5 to 0.8 inch (1.3-1.9 cm) into the bark [67]. Because of this, trees are often able to survive crown fire. Trees may sprout from the main trunk and upper crown even after severe burning [68]. When trees are top-killed, they sprout from the root crown [22,66]. Vigorous sprouting is supported by food reserves stored in the extensive root system [19]. Historically, the woodlands in which these trees are prominent burned frequently. Vogl [85] estimates a frequency of approximately one fire per year in grassland savannas and coastal foothills. Fire ecology: These oaks generate a deep litter layer except on steep slopes [39]. Leaves contain large amounts of flammable ether extracts [75]. POSTFIRE REGENERATION STRATEGY : Tree with adventitious-bud rootcrown/ soboliferous species root sucker Tall shrub, adventitious-bud rootcrown Ground residual colonizer (onsite, initial community) Secondary colonizer - offsite seed

FIRE EFFECTS

SPECIES: Quercus agrifolia | Coast Live Oak
IMMEDIATE FIRE EFFECT ON PLANT : Coast live oak seedlings and saplings less than 2 inches (5 cm) in d.b.h. are top-killed by moderate-severity fire, and severe fire may kill trees of this size [24,66]. Saplings between 2 to 6 inches (5-15 cm) in d.b.h. are top-killed by severe fire. Larger trees are usually not top-killed by severe fire. The Soboba Fire on the San Bernadino National Forest, classified as an extremely hot crown fire, killed only 4 percent of burned coast live oak. Ninety percent of the oaks less than 3 inches (7.6 cm) in d.b.h. were top-killed, and 2 percent were killed. Of trees greater than 6 inches (15.2 cm) in d.b.h., the trunks and crowns of all but 5 percent survived the fire. Of this 5 percent, 3 percent were top-killed, and 2 percent suffered complete kill [66]. Roots are protected by an outer corky layer and the soil itself. Coast live oak roots generally suffer little direct heat damage except feeder roots near the soil surface [66]. Acorns on the soil surface are killed by low-severity fire, while animal-buried acorns usually survive moderate-severity fire. Severe fire, however, may kill even buried acorns. Following a severe fire in Ventura County, burned sites supported no coast live oak germinants supported no germinants the following spring, while adjacent unburned areas produced new seedlings [21]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : Mortality of coast live oak is greater when there is a considerable shrub understory or when trees are adjacent to chaparral. Coast live oak in the Santa Monica Mountains were killed in large numbers when a hot chaparral fire burned into the oak woodland [78]. PLANT RESPONSE TO FIRE : Coast live oak generally recovers well from fire, although severely burned crowns, trunks, and root crowns may require several years to sprout. Oaks are more likely to be damaged by fall fire than earlier fires. The most common fire damage to the trunk is a basal wound resulting in cambium death. Small wounds less than a few inches may eventually heal with no accompanying heart rot, but larger wounds are subject to fungal disease and insect attack [76]. Winter fire causes the least damage [67]. Recovery of trees on the Soboba Burn was as follows [66]: Tree condition, May 1979 Number of Basal Basal and Crown Tree diameter charred trees, Dead sprouts crown sprouts (d.b.h., in.) Aug. 1974 only sprouts only ________________Percent________________ 0- 3 90 2 88 1 9 3- 6 54 11 26 28 35 6-12 65 1 5 52 42 12-18 24 0 0 62 38 18+ 22 4 5 50 41 Crown density typically reaches 80 percent of preburn level in 10 years on favorable sites [39]. Low-severity fire apparently favors regeneration. Coast live oak populations were increased from preburn levels following a low-severity fire in Cuyamaca State Park [45,48]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : FIRE MANAGEMENT CONSIDERATIONS : Use of fire is recommended for managing coast live oak [66]. The outstanding fire resistance of this species ensures that few large trees will be killed by moderate-severity prescribed fire. Natural regeneration has improved following prescribed burning [48]. Fire will eliminate competing conifers from areas where they are invading oak woodland [39]. Regeneration is also favored because scrub jays prefer burns as acorn-caching sites [59]. Large trees do not always sprout at the first postfire growing season, and Plumb and Gomez [67] recommend waiting at least one growing season, possibly up to three, before cutting large trees with uncertain potential for crown survival. The following guide suggests when to harvest coast live oak, based upon tree size and degree of trunk char* [66]: Less than 6 in. d.b.h. 6-12 in. d.b.h. More than 12 in. d.b.h. ______________________ ______________________ _______________________ Light Medium Heavy Light Medium Heavy Light Medium Heavy char char char char char char char char char Lv Lv Cut Lv Lv Lv Lv Lv Lv ____________________________________________________________________________ *Assumes that 100% of trunk circumference is affected, as follows: Light=spotty char or scorch, scattered pitting; Medium=continuous charring, areas of minor reduction in bark thickness; Heavy=continuous charring and pronounced reduction in bark thickness with wood sometimes exposed. Lv means the tree should be left uncut for 3 yrs; Cut means the tree can be cut immediately. Fire managers in southern California have made fire control lines in coast live oak woodland when planning broadcast burning of adjacent chaparral. Potential control line sites are selected from nearby riparian woodland areas, where the understory is burned in order to make a fuelbreak [24].

REFERENCES

SPECIES: Quercus agrifolia | Coast Live Oak
REFERENCES : 1. Allen, Barbara H.; Holzman, Barbara A.; Evett, Rand R. 1991. A classification system for California's hardwood rangelands. Hilgardia. 59(2): 1-45. [17371] 2. Allen-Diaz, Barbara H.; Holzman, Barbara A. 1991. Blue oak communities in California. Madrono. 38(2): 80-95. [15424] 3. Bainbridge, David A. 1987. The use of acorns for food in California: past, present, future. In: Plumb, Timothy R.; Pillsbury, Norman H., technical coordinators. Proceedings of the symposium on multiple-use management of California's hardwood resources; 1986 November 12-14; San Luis Obispo, CA. Gen. Tech. Rep. PSW-100. Berkeley, CA: U.S. Department of Agriculture, Forest Service, Pacific Southwest Forest and Range Experiment Station: 453-458. [5395] 4. Barbour, Michael G. 1987. Community ecology and distribution of California hardwood forests and woodlands. In: Plumb, Timothy R.; Pillsbury, Norman H., technical coordinators. Proceedings of the symposium on multiple-use management of California's hardwood resources; 1986 November 12-14; San Luis Obispo, CA. Gen. Tech. Rep. PSW-100. Berkeley, CA: U.S. Department of Agriculture, Forest Service, Pacific Southwest Forest and Range Experiment Station: 18-25. [5356] 5. Barbour, Michael G. 1988. Californian upland forests and woodlands. In: Barbour, Michael G.; Billings, William Dwight, eds. North American terrestrial vegetation. Cambridge; New York: Cambridge University Press: 131-164. [13880] 6. Bartolome, James W.; Muick, Pamela C.; McClaran, Mitchel, P. 1987. Natural regeneration of Californian hardwoods. In: Plumb, Timothy R.; Pillsbury, Norman H., technical coordinators. Proceedings of the symposium on multiple-use management of California's hardwood resources; 1986 November 12-14; San Luis Obispo, CA. Gen. Tech. Rep. PSW-100. Berkeley, CA: U.S. Department of Agriculture, Forest Service, Pacific Southwest Forest and Range Experiment Station: 26-31. [5357] 7. Bernard, Stephen R.; Brown, Kenneth F. 1977. Distribution of mammals, reptiles, and amphibians by BLM physiographic regions and A.W. Kuchler's associations for the eleven western states. Tech. Note 301. Denver, CO: U.S. Department of the Interior, Bureau of Land Management. 169 p. [434] 8. Bissell, Harold D.; Strong, Helen. 1955. The crude protein variations in the browse diet of California deer. California Fish and Game. 41(2): 145-155. [10524] 9. Bolsinger, Charles L. 1988. The hardwoods of California's timberlands, woodlands, and savannas. Resour. Bull. PNW-RB-148. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station. 148 p. [5291] 10. Brophy, William. 1973. Evolution and ecology in Quercus: a study of hybridization and introgression between Quercus agrifolia Nee. and Q. wislizenii A. DC. Hayward, CA: California State University. 97 p. Thesis. [6858] 11. Brown, David E. 1982. Californian evergreen forest and woodland. In: Brown, David E., ed. Biotic communities of the American Southwest--United States and Mexico. Desert Plants. 4(1-4): 66-69. [8887] 12. Burcham, L. T. 1974. Fire and chaparral before European settlement. In: Rosenthal, Murray, ed. Symposium on living with the chaparral: Proceedings; 1973 March 30-31; Riverside, CA. San Francisco, CA: The Sierra Club: 101-120. [4669] 13. Callaway, Ragan M.; D'Antonio, Carla M. 1991. Shrub facilitation of coast live oak establishment in central California. Madrono. 38(3): 158-169. [17102] 14. Capelli, Mark H.; Stanley, Stephen J. 1984. Preserving riparian vegetation along California's south central coast. In: Warner, Richard E.; Hendrix, Kathleen M., eds. California riparian systems: Ecology, conservation, and productive management. Berkeley, CA: University of California Press: 673-686. [5868] 15. Carmen, William J.; Koenig, Walter D.; Mumme, Ronald L. 1987. Acorn production by five species of oaks over a seven year period at the Hastings Reservation, Carmel Valley, California. In: Plumb, Timothy R.; Pillsbury, Norman H., technical coordinators. Proceedings of the symposium on multiple-use management of California's hardwood resources; 1986 November 12-14; San Luis Obispo, CA. Gen. Tech. Rep. PSW-100. Berkeley, CA: U.S. Department of Agriculture, Forest Service, Pacific Southwest Forest and Range Experiment Station: 429-434. [5390] 16. Childers, Christian A.; Piirto, Douglas D. 1991. Cost-effective wilderness fire management: a case study in southern California. In: Nodvin, Stephen C.; Waldrop, Thomas A., eds. Fire and the environment: ecological and cultural perspectives: Proceedings of an international symposium; 1990 March 20-24; Knoxville, TN. Gen. Tech. Rep. SE-69. Asheville, NC: U.S. Department of Agriculture, Forest Service, Southeastern Forest Experiment Station: 179-186. [16649] 17. Clark, Harold W. 1937. Association types in the North Coast Ranges of California. Ecology. 18: 214-230. [11187] 18. Clark, Ronilee A.; Halvorson, William L.; Sawdo, Andell A.; Danielsen, Karen C. 1990. Plant communities of Santa Rosa Island, Channel Islands National Park. Tech. Rep. No. 42. Davis, CA: University of California at Davis, Institute of Ecology, Cooperative National Park Resources Studies Unit. 93 p. [18246] 19. Cooper, W. S. 1922. The broad-sclerophyll vegetation of California. Publ. No. 319. Washington, DC: The Carnegie Institution of Washington. 145 p. [6716] 20. Cross, Richard D. 1980. Oak tree banks and relocation. In: Plumb, Timothy R., technical coordinator. Proceedings of the symposium on the ecology, management, and utilization of California oaks; 1979 June 26-28; Claremont, CA. Gen. Tech. Rep. PSW-44. Berkeley, CA: U.S. Department of Agriculture, Forest Service, Pacific Southwest Forest and Range Experiment Station: 176-177. [7034] 21. 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