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You are here >1Up Info > Wildlife, Animals, and Plants > Plant Species > Forb > Species: Rumex acetosella | Sheep Sorrel
 

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FIRE EFFECTS

SPECIES: Rumex acetosella | Sheep Sorrel
IMMEDIATE FIRE EFFECT ON PLANT : Sheep sorrel is probably top-killed by fire. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Sheep sorrel probably sprouts from rhizomes following fire and establishes from on-site seed [14,21,26]. Several studies describe establishment or increase of sheep sorrel after fire. Very severe fire may kill sheep sorrel. In New Brunswick a woodlot was clearcut in the fall of 1949 and prescribed burned in April 1951. The number of stems of sheep sorrel per area present in June 1949, 1950, 1951, and 1952 were 0, 0, 18, and 28, respectively [31]. In New Brunswick understory layers of 11 mixed hardwood stands representing an age sequence of 7 to 57 postfire years were examined. Sampling occurred in July and August 1973 and 1974. Sheep sorrel was found in stands 7, 10, 13, 17, and 25 years old. It did not occur in some 7-year-old stands, or in stands 18, 20, 29, and 37 years old [58]. In Idaho seral brushfields in a grand fir/pachistima habitat type were prescribed burned on May 14, 1975, and a portion was seeded on May 15, 1975. Sheep sorrel was present on the burn-only area, but did not occur on the burn-and-seed site. Frequency (out of 10 possible plots) of sheep sorrel was as follows [53]: Prefire Postfire year July 3, 1974 1 2 4 control 1 2 3 3 burn only 0 0 5 4 burn and seed 0 0 0 0 In Idaho a wildfire burned a ponderosa pine (Pinus ponderosa) forest and adjacent montane grassland on August 10, 1973 for 43 days. Fourteen sites were examined in June 1974 and June 1976. Percent cover and frequency of sheep sorrel on burned and unburned sites were as follows [65]: 1974 1976 burned unburned burned unburned cover +/- SD t* +/- 1 t +/- t 2 +/- 3 1 +/- 2 frequency +/- SD 1 +/- t t +/- 1 2 +/- 4 1 +/- 2 *t = trace In Washington on the Mount Adams huckleberry (Vaccinium spp.) fields, an experimental area was prescribed burned from October 3-7, 1972. Average understory cover (%) of sheep sorrel from 1972 to 1977 was as follows [66]: 1972 (before treatment) 1973 1974 1975 1977 unburned, uncut 0.2 0.2 0.3 0.3 0.2 thin, underburn 0.2 0.6 0.9 1.2 1.5 clearcut and burn 0.2 0.9 1.9 1.0 1.6 In Great Britain severe fires in late summer 1976 killed all surface vegetation. Sheep sorrel first appeared in burned areas in October 1985, postfire year 9 [59]. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : Some research describes no change in cover or frequency in sheep sorrel after fire. In California the effects of a late fall burn on a mountain meadow in Grover Hot Springs State Park were evaluated. Both wet and dry meadow plots were prescribed burned by a low- to moderate-intensity fire in mid-November 1987. Sheep sorrel was found only on dry plots before burning and did not increase following fire [8]. In Connecticut experimental tracts were set up in a little bluestem grassland in 1967. Tract A was prescribed burned annually from 1968-1976, and in 1978, 1980, 1983, and 1985. Tract B was prescribed burned annually from 1968-1975, and in 1978, 1980, 1983, and 1985. Sheep sorrel percent cover and frequency in two burns and 2 control plots on each tract were as follows [69]: Tract A Tract B 1967 1985 1967 1985 cover freq cover freq cover freq cover freq treatment Burn <1 9 2 6 <1 29 <1 5 Control <1 22 0 0 1 65 <1 27 FIRE MANAGEMENT CONSIDERATIONS : NO-ENTRY

Related categories for Species: Rumex acetosella | Sheep Sorrel

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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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