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You are here >1Up Info > Wildlife, Animals, and Plants > Plant Species > Graminoid > Species: Aristida purpurea | Purple Threeawn
 

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FIRE EFFECTS

SPECIES: Aristida purpurea | Purple Threeawn
IMMEDIATE FIRE EFFECT ON PLANT : Threeawns (Aristida spp.) are readily harmed by fire because their rootcrowns are close to or above the soil surface [63]. Purple threeawn cover is generally reduced by fire [52,62,63]. Purple threeawn produces relatively large, densely culmed, fine-leaved bunches. Since it is grazed very little, litter usually accumulates around bunches. Wright and Bailey [63] stated that bunchgrasses with this growth habit may continue to burn for 2 or 3 hours after fire has passed. Such prolonged burning transfers heat downward and damages roots. Basal cover may be greatly reduced or plants may be killed. Fire-induced mortality varies, however. Evans [15] reported that only a few purple threeawn were killed by spring prescribed fire in southern Idaho. Small purple threeawn bunches were killed by a second fire 2 years later. Large bunches were not killed by repeated burning but split into several small bunches. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Fire reduced blue threeawn in a desert mountain shrub community near Big Bend National Park, Texas. Wildfire burned the community in November, 1975. Prefire vegetation was dominated by sotol (Dasylirion leiophyllum), lechuguilla (Agave lechuguilla), blue threeawn, and sideoats grama (Bouteloua curtipendula). Precipitation was above average in postfire years 1 and 2. At postfire year 2, blue threeawn cover on burned plots averaged 0.42 percent while blue threeawn cover on adjacent unburned plots averaged 4.09 percent. Grasses and succulents had decreased at the expense of forbs and subshrubs. Forb and subshrub cover on burned plots was 650 percent greater than on unburned plots [3]. Wright's and purple threeawn (Aristida purpurea var. purpurea) were slightly to greatly reduced for at least two growing seasons following chaining and burning in a redberry juniper (Juniperus erythro- carpa)-mixed grassland community in King County, Texas. In 1979 or 1980, plots were chained, chained and broadcast burned in March, or left untreated (control). Fine fuel loads averaged 2,264 lbs/acre (2,573 kg/ha) in 1979 and 1,327 lbs/acre (1,508 kg/ha) in 1980. Weather conditions were: relative humidity 25 to 40 percent, temperature 68 to 78 degrees Fahrenheit (20-26 deg C), and winds 7.7 to 14.4 miles/hour (12-24 km/hr). Fire spread was "excellent" in both years, with nearly 100 percent coverage. Precipitation following the 1979 fire was above average; drought followed the 1980 fire. Combined yield of Wright's and purple threeawn was [47]: _________________________________________________________________________ | 1979 Treatments (wet year) | 1980 Treatments (dry year)| |___________________________________________|___________________________| | 1st growing 2nd growing | 1st growing 2nd growing| | season season | season season | |___________________________________________|___________________________| |control 63a 63a* | 57a 25b | |chained 92a 113a | 85a 37b | |chained & burned 47a 56a | 12a 6b | |_______________________________________________________________________| *Values within a treatment year identified by the same letter are not significantly different (p > 0.05). Prescribed fire on the Texas Technological College Research Farm near Amarillo had little effect on Fendler threeawn size but stimulated seedstalk production. Six plots were used. Two plots were burned in fall, 1965 (1 with and 1 against the wind); two plots were burned in spring, 1966 (1 with and 1 against the wind); one plot was burned summer, 1966 (with the wind); and one plot was not burned (control). There were no significant differences in soil moisture between plots at the time of the fall or spring fires. Basal diameters of Fendler threeawn plants decreased between 1966 and 1967 on plots burned 2 years in succession, but either maintained or increased in size on the unburned control plot and plots burned only once the previous year. Height and seedstalk production decreased between 1966 and 1967 regardless of treatment. Relative to the control plot, fire had little effect on seedstalk numbers the first growing season after fire. However, in the second growing season (1967), Fendler threeawn seedstalk numbers were greater on all burned plots compared to the control plot. Average seedstalk production and average maximum height of Fendler threeawn was [52]: Number of Fendler Threeawn Seedstalks |----------------------Treatment-------------------------| |Control Fall Fall Spring Spring Summer| Year | 1965 1965 & 66 1966 1966 & 67 1966 | _______________|________________________________________________________| 1965* | 115 135 107 55 115 127 | 1966 | 40 105 82 25 67 37 | 1967 | 39 45 55 43 48 55 | _______________|________________________________________________________| *before burning Height (cm) |----------------------Treatment-------------------------| |Control Fall Fall Spring Spring Summer| Year | 1965 1965 & 66 1966 1966 & 67 1966 | _______________|________________________________________________________| 1965* | 33 32 30 27 27 35 | 1966 | 25 23 20 20 20 20 | 1967 | 12 11 10 11 11 11 | _______________|________________________________________________________| *before burning Fendler threeawn was reduced following wildfire in a cheatgrass stand in north-central Utah. Vegetation had been sampled at the end of the 1955 growing season. The wildfire occurred in summer 1956. Precipitation in 1957 (the only year for which precipitation data are given) was near average. Fendler threeawn cover and importance percentages were as follows [6]: Year ---------------------------------------- 1955 1957 1958 1960 1961 ---------------------------------------- cover (%) 11.5 3.4 6.2 9.9 5.0 importance (%) 17.7 4.2 8.6 11.6 5.9 DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : NO-ENTRY

Related categories for Species: Aristida purpurea | Purple Threeawn

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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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