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You are here >1Up Info > Wildlife, Animals, and Plants > Plant Species > Shrub > Species: Symphoricarpos occidentalis | Western Snowberry
 

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FIRE EFFECTS

SPECIES: Symphoricarpos occidentalis | Western Snowberry
IMMEDIATE FIRE EFFECT ON PLANT : Western snowberry is top-killed or killed by severe fires [4,5,60,94]. In the northern Great Plains, "hot" fires in late summer and early fall have severely burned roots of western snowberry [60]. In Minnesota in a partially burned colony of western snowberry, all stems were killed and all stem bases charred. By the fall of the same year, an average of 2.5 sprouts per stem base was observed [94]. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Western snowberry sprouts from the root crown following fire [100]. Several studies have reported rapid recovery and postfire increases in western snowberry densities [5,11,43,100], although decreases have been reported [3,4,11,45]. In quaking aspen parklands in Alberta, western snowberry sprouted 2 weeks after spring fire; by 3 months its canopy cover was greater on burned sites than on control plots [5]. In Saskatchewan a prescribed fire occurred in October 1976 in native fescue grassland; western snowberry was top-killed. By postfire year 1, western snowberry live stem density was similar in burned and unburned areas [97]. In North Dakota an October 1976 fire burned mixed-grass prairie and wooded draw plant communities. Average densities (stems/sq m) of western snowberry in the summers of 1977 and 1978 were higher on burned than unburned transects in wooded draws [142]: 1977 1978 lower draw-burned 41.2 31.5 upper draw-burned 68.6 38.8 unburned ---- 12.5 In Saskatchewan eight prescribed fires were set from October 1986 to April 1988 to reduce western snowberry encroachment into native grassland. Two plots were burned with headfires at each of the following times: mid-October 1986, mid-October 1987, early May 1987, and late April 1988; two additional blocks were left as control sites. All plots were monitored for 4 years after burning. Average western snowberry stem densities (stems/sq m) were higher on burned than unburned plots [100]: growing season control autumn spring standard error prefire 36 39 38 8.1 postfire year 1 39a* 72ab 122b 14.6 postfire year 2 43a 67ab 111b 12.3 postfire year 3 46 62 95 12.9 postfire year 4 46 57 51 5.5 *Different letters within a year indicate means are significantly different (P< or =0.05). A similar letter or no letter within a year indicates means are not significantly different (P> or =0.05) Western snowberry density was significantly greater on spring-burned plots than on autumn-burned or control plots. In Alberta two prescribed burns were conducted on May 8, 1970 and May 11, 1971. Western snowberry was the dominant shrub on unburned sites. All western snowberry stems were killed by the fires, but plants started sprouting 2 weeks after fire. Stem densities (stems/sq m) for western snowberry during three growing seasons following spring 1970 burning were as follows [5]: year unburned burned 1970 86 236 1971 65 199 1972 66 170 Western snowberry stem densities increased significantly (P<0.05) following fire. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : In South Dakota a May 1, 1974 prescribed fire was conducted in native grassland. Stem density (stems/sq m) and average height (cm) of western snowberry were reduced following fire. Results were as follows [45]: prefire postfire (Ocotber 15, 1973) (June 28, 1974) stem density 79 55 stem height 61 24 In Alberta early spring burning in fescue grassland was conducted annually for 24 years. Stem densities (stem/sq m) were 17.8 and 25 in burned and unburned areas, respectively. Frequency and cover of western snowberry in July 1976 after the last fire were as follows [3,4]: frequency (%) cover (%) unburned 56 31 burned 52 2 Western snowberry canopy cover declined greatly on burned sites, but frequency and stem density did not change significantly. In Minnesota prescribed spring fires were conducted annually from 1983 to 1987. Western snowberry shoot height decreased from 3.3 to 1.6 feet (1-0.5 m) on burned sites [11]. FIRE MANAGEMENT CONSIDERATIONS : In the absence of fire, western snowberry has become the dominant native shrub on mixed-grass prairies in the northern Great Plains [111]. Annual burning may restrict expansion of western snowberry colonies onto native prairie grasslands, whereas periodic burning may enhance the spread of western snowberry [5,60,94,100]. Periodic burning could create even-aged, youthful stands of western snowberry, which may be more productive of wildlife forage and provide better cover [100]. In North Dakota two prescribed fires in mid-June 1982 and 1984 top-killed most western snowberry. Unburned vegetation ("skips") within burn areas mostly occurred in dense patches of western snowberry. Gadwalls started nesting in these "skips" 4 days after the burns, where dead stems of western snowberry were still standing [75].

Related categories for Species: Symphoricarpos occidentalis | Western Snowberry

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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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