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You are here >1Up Info > Wildlife, Animals, and Plants > Plant Species > Shrub > Species: Quercus chrysolepis | Canyon Live Oak
 

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FIRE CASE STUDIES

SPECIES: Quercus chrysolepis | Canyon Live Oak
CASE NAME : Marble - Cone SEASON/SEVERITY CLASSIFICATION : August 1977/severe. STUDY LOCATION : The study site is located in the Ventana Wilderness Area of California and includes the north slope of Junipero Serra Peak. Two primary areas were considered: 1) Summit Forest, and 2) Slope Forest. PREFIRE VEGETATIVE COMMUNITY : Montane forest were dominated by sugar pine (Pinus lambertiana). These forests were surrounded by shrubby mixed hardwoods and chaparral. On steep slopes Coulter pine (P. coulteri), canyon live oak (Quercus chrysolepis), and eastwood manzanita (Arctostaphylos glandulosa) were important vegetative components on some plots. Important herbs and subshrubs included rockcress (Arabis breweri), Indian paintbrush (Castilleja foliosa), lipfern (Cheilanthes covillei), bedstraw (Galium angustifolium), bedstraw (G. clementis), hawkweed (Hieracium argutum var. parishii), deervetch (Lotus argophyllus var. fremontii), Abrams lupine (Lupinus abramsii), lupine (L. hirsutissimus), red beardstongue (Penstemon corymbosus), western swordfern (Polystichum munitum), and crested stipa (Stipa coronata). Density of canyon live oak was estimated at 73 percent, with a basal areas of approximately 30 percent. On gentler slopes within the summit forest, sugar pine, Coulter pine and canyon live oak were dominant, with scattered eastwood manzanita. Common herbs included dusky onion (Allium campanulatum), fleabane (Erigeron petrophyllus), biscuitroot (Lomatium macrophyllum), oceanspray (Holodiscus microphyllus), needlegrass (Stipa spp.), bedstraw (Galium clementis), Micranth alumroot (Heuchera micrantha var. pacifica), and western swordfern. Basal area of canyon live oak was 6 percent, with an estimated density of 23 percent. TARGET SPECIES PHENOLOGICAL STATE : not reported. SITE DESCRIPTION : Slope Forest - slope - average 57 percent preburn vegetation - sparse topography - broken and steep elevation - average 5,215 feet (1,590 m) Summit Forest - slope - moderate, average 42 percent preburn vegetation - no more than 25 percent cover elevation - average 5,576 feet (1,700 m) FIRE DESCRIPTION : Fire crowned in some parts of the Summit Forest. Fire changed from a crown-type fire to a surface fire below 5,412 feet (1,650 m). Here the burn was somewhat patchy. Portions of the canyon bottom characterized by steep, rocky slopes or mineral soil remained unburned. FIRE EFFECTS ON TARGET SPECIES : Nearly all canyon live oaks in burned areas were killed. However, burned stems sprouted vigorously and on some slope plots acorns also germinated. Prefire and postfire constancy and cover values are as follows: constancy - (%) /modal cover - abundance values Slope Forest Summit Forest preburn postburn preburn postburn from sprouts - 20 / + 100 / 1 60 / + 100 / + from seed - -- 100 / 1 -- 100 / 1 FIRE MANAGEMENT IMPLICATIONS : Canyon live oak sprouted prolifically after fire. In some areas seedlings were also present. Response suggests a relatively rapid recovery after fire.

FIRE CASE STUDIES

SPECIES: Quercus chrysolepis | Canyon Live Oak
CASE NAME : Village Fire, California SEASON/SEVERITY CLASSIFICATION : November, 1975/not reported STUDY LOCATION : The study site is located in the Angeles National Forest of California. PREFIRE VEGETATIVE COMMUNITY : Preburn vegetation consisted of an almost pure stand of canyon live oak (Quervcus chrysolepis). Most trees ranged between 6 and 12 inches (15-31 cm) d.b.h. TARGET SPECIES PHENOLOGICAL STATE : presumably dormant. SITE DESCRIPTION : not reported. FIRE DESCRIPTION : not reported. FIRE EFFECTS ON TARGET SPECIES : The basal 1 to 5 feet (0.8-1.5 m) of most trunks were charred and one-third to two-thirds of the leaves in the crown were killed. Many leaves close to the ground were killed by heat but were not actually consumed. The bark of some trees was burned through exposing the wood beneath. Larger trees often exhibited crown kill over a relatively long period of time. Approximately 55 percent of the larger trees were still alive at the end of 18 months. During the next 18 months, 50 percent of the trees with "live crowns" turned brown. Many more were expected to die later. Results were as follows: condition of trees 1-1/2 years after basal trunk damage - tree number apparently basal basal sprouting live crown diameter of dead sprouting + live only (dbh in.) trees (%) only (%) crown (%) (%) 0-3 10 10 90 0 0 3-6 59 3 73 22 2 6-12 97 1 25 70 4 decline over a 3 year period in % of living crown - tree diameter # of trees % alive after % alive after (dbh in.) 18 months 36 months 0-3 10 0 0 3-6 59 24 15 6-12 97 74 46 FIRE MANAGEMENT IMPLICATIONS : Aboveground vegetation of canyon live oak is sensitive to fire. Even low intensity ground fires can create high heat intensity on the surface of the trunk due to the flammability and heat conductivity of the flaky, outer bark. A correct determination of fire damage is important in assessing postfire survival potential of canyon live oak stems (See Discussion and Qualification of Fire Effect). Crowns and trunks of larger canyon live oak with only light to medium char sometimes survive. However, several growing seasons may be necessary to determine the actual degree of damage. Postfire harvest of smaller trees, or those suffering greater trunk char, is generally recommended since survival of stems is unlikely.

Related categories for Species: Quercus chrysolepis | Canyon Live Oak

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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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