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You are here >1Up Info > Wildlife, Animals, and Plants > Plant Species > Graminoid > SPECIES : Bromus hordeaceus | Soft Chess
 

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FIRE EFFECTS

SPECIES : Bromus hordeaceus | Soft Chess
IMMEDIATE FIRE EFFECT ON PLANT : Fire has little direct effect on soft chess. Wildland and prescribed fires usually occur after soft chess has dried and shattered seed [44,45,46]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Fire may reduce soft chess in the short term [48]. Species composition in the postfire plant community is difficult to predict, however. Year-to-year plant composition in annual grassland is highly dependent upon local weather patterns, and even slight differences in annual precipitation can alter species assemblages [61]. Fall weather patterns, especially interactions of precipitation and temperature after rainfall, appear to be overriding factors in soft chess establishment [45,46,57]. Fire affects plant species composition in annual grasslands largely by removing mulch, which affects germination and seedling establishment rates of soft chess relative to associated herbaceous species. Bartolome [7,9] found that soft chess reached highest densities when mulch biomass was at intermediate levels. Little quaking grass (Briza minor) was favored when mulch biomass was low, as it would be in the immediate postfire environment. Fescues (Vulpia and Festuca spp.) were favored when mulch biomass was high. Heady [45] reported that without heavy grazing the mulch layer usually recovers by postfire year 3, and soft chess and other annual bromes regain dominance. Decreases with fire: Hansen [40] found that fall prescribed fire in Tulare County, California, significantly increased dominance of annual forbs relative to soft chess. Greatest reduction soft chess and other annual grasses (and greatest increase of annual forbs) was achieved by 3 years of successive fall burning. Response of native grasses was similar to that of soft chess: Native grasses were reduced by fall burning, with greatest reduction achieved after 3 years of consecutive fall burning. Percent cover of soft chess the spring after fall burning follows. unburned single twice- thrice- control burn burned burned ________ ______ ______ _______ 1982 10 <1 -- -- 1983 8 5 2 -- 1984 23 44 16 2 1985 12 23 15 10 A July 1947 prescription fire reduced soft chess on ungrazed annual grassland near Berkeley, California. Precipitation in the fall and winter of 1947-1948 was slightly below average for the area (20.4 inches with the average being 22.6 inches). Average height and yield of soft chess on two burned and two unburned sites in May of 1948 was as follows [48]: burned unburned ______ ________ height (cm) exclosure I 29.9 29.9 exclosure II 35.0 39.1 yield (g) exclosure I 0.8 3.1 exclosure II 4.6 13.9 Mixed effects: Chaparral and oak woodland - Density of soft chess increased greatly from prefire levels 5 years after prescribed fall burning in a nonsprouting manzanita-Lemmon ceanothus (Arctostaphylos spp.-Ceanothus lemmonii) community in Mendocino County. However, density of soft chess had changed little 5 years after prescribed fall fires in nearby nonsprouting manzanita (Arctostaphylos spp.)-Lemmon ceanothus and interior live oak-blue oak (Quercus wislezenii-Q. douglasii) woodland communities. Average density (plants/milacre) of soft chess was [80]: Postfire year ______________________________ Community Prefire 1 2 3 4 5 _____________________________________________________________ nonsprouting manzanita-ceanothus 0.0 2.8 7.3 11.2 24.6 30.3 sprouting manzanita-ceanothus 0.3 4.1 6.5 3.8 5.1 2.8 live oak-blue oak 1.5 6.6 6.7 5.8 3.0 1.3 No effect: Neither spring nor fall prescribed fire had significant effect on soft chess in annual grassland of Sequoia National Park, California. Precipitation averaged about 200 percent of normal during postfire years 1 to 4. Soft chess formed an important component of the vegetation (between 10 and 27%) on plots measured before fire and on spring-burned, fall-burned, and unburned plots measured 4 years after fire [75]. Sagebrush steppe - In central Idaho, fire had little effect on soft chess coverage in either the long term or the short term. A long-term study was conducted above the Snake River Canyon, after a July wildfire occurred 1961 in a rubber rabbitbrush (Chrysothamnus nauseosus)-cheatgrass community. At postfire year 12, soft chess had declined on both burned and adjacent unburned plots. (Weather data were not given.) Soft chess coverage was as follows [24]: Unburned Burned ____________________ ___________________ Postfire year 2 4 12 2 4 12 ____ ____ _____ _____ _____ _____ 4.80 1.45 trace trace trace trace A short-term study was conducted nearby when an August 1972 wildfire occurred in a rubber rabbitbrush-cheatgrass stand within the Snake River Canyon. The following spring, soft chess frequency was 21 percent on unburned plots and 18 percent on burned plots [24]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : California: annual grassland - Use of prescribed fire to increase the balance of natives relative to non-natives such as soft chess has had mixed results. In all cases, "remnant" California prairie contains exotic annuals, and attempts to eliminate the exotics have been unsuccessful [61]. However, fire sometimes tips the balance toward natives. Perennial bunchgrasses are well adapted to frequent fire [20,94]. Some authors have reported that fire favors native bunchgrassses over exotic annuals [1,70]. However, Garcia and Lathrop [33] reported no increase in purple needlegrass after burning, and Lathrop and Martin [66] found that native deer grass (Muhlenbergia rigens) decreased under some burning regimes. In view of the differences in phenology and life histories between perennial bunchgrasses and annual grasses such as soft chess, it would be instructive to know how burning in different seasons affects the ratio of native to non-natives. Since annual grasses produce seed about a month earlier than perennial grasses, precise timing of burning may alter the balance of reproductive success between annual and perennial grasses [61]. When used with prescribed grazing, fire may favor purple needlegrass and reduce soft chess and other annual grasses. Langstrotti [65] found that on the Jepson Prairie (a relict perennial grassland reserve in Solano County, California), short-term, intensive grazing by domestic sheep in early spring (late March or early April) combined with late summer (early September) prescribed fire favored tillering and seedling establishment of purple needlegrass over exotic annual grasses including soft chess. Purple needlegrass had been declining on the reserve for a number of years. Frequency of soft chess was significantly reduced (p=0.05) by early spring grazing and late summer fire. The treatments reduced soft chess cover to less than 2 percent. Early spring grazing reduced average seed mass, and the number of soft chess seeds was reduced by 76 percent (p=0.25). Late summer fire reduced soft chess cover by 50 percent (p<0.001). Summer grazing and late summer fire also reduced soft chess, but not as much. Data from the spring grazing/late summer fire treatments follow. grazed- ungrazed- burnt unburnt _______ __________ soft chess frequency (%) 39.7 3.0 soft chess seeds/sq dm 198 1,343 soft chess seed mass (mg) 0.57 0.97 Effects of postfire seeding of ryegrass on soft chess: Seeding Italian ryegrass (Lolium multiflorum) to reduce postfire erosion had little effect on postfire growth of soft chess and other exotic bromes in southern California chaparral. Coverage of annual bromes was similar on unseeded plots and on plots seeded with Italian ryegrass [15]. Oregon: big sagebrush - Prescribed fire had little effect on soft chess in a basin big sagebrush/bluebunch wheatgrass community in John Day Fossil Beds National Monument, Oregon. Weather patterns occurring after fire greatly influenced plant community composition, however. One study area was prescribed burned on September 25, 1987; an adjacent study area was prescribed burned on May 24, 1988. Prescription burning was followed by 3 years of drought, which appeared to greatly reduce soft chess cover. By the third postfire year, soft chess was absent from all treatments including the unburned control. Density of other annual grass species was also greatly reduced on all treatments including the unburned control. Density of annual forbs increased on all plots, and density of native perennial grasses did not change. Density of woody shrub species was greatly reduced on burned plots but did not change on control plots. Average density of soft chess (plants/sq m) on unburned control, fall-burned, and spring-burned plots is given below. Numbers in parenthesis are the standard errors of the mean; different letters denote a significant difference between years (p<0.1) [82]. 1987 1988 1989 _________ _______ ______ control 160a (87) 0b (0) 0b (0) fall burn 82a (28) 10b (8) 0b (0) spring burn -- 37a (16) 0b (0) FIRE CASE STUDIES : NO-ENTRY

Related categories for SPECIES : Bromus hordeaceus | Soft Chess

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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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