Species: Symphoricarpos albus
Snowberry
Species
Show on Lists
Encyclopedia of Puget Sound
SYMPHORICARPOS ALBUS is a finely-branched, erect, perennial shrub.
Classification
Kingdom
Plantae
Phylum
Anthophyta
Class
Dicotyledoneae
Order
Dipsacales
Family
Caprifoliaceae
Genus
Symphoricarpos
NatureServe
Classification
Other Global Common Names
Common Snowberry - common snowberry - symphorine blanche
Informal Taxonomy
Plants, Vascular - Flowering Plants - Honeysuckle Family
Formal Taxonomy
Plantae - Anthophyta - Dicotyledoneae - Dipsacales - Caprifoliaceae - Symphoricarpos
Ecology and Life History
SYMPHORICARPOS ALBUS is a finely-branched, erect, perennial shrub.
Short General Description
SYMPHORICARPOS ALBUS is a finely-branched, erect, perennial shrub.
Reproduction Comments
Common snowberry spreads mainly by vegetative means through sprouting (Willard and McKell 1973). It reproduces by rhizomes as well as by seed and resprouts after fire or cutting (Tisdale and Hironaka 1981).
Ecology Comments
S. ALBUS and related species provide important winter and summer browse for game animals and for sheep and cattle in areas where grasses have cured or where grass cover is less abundant. Several range and forest management studies have looked at encouraging common snowberry growth and monitoring effects of browsing (Willard and McKell 1973, Szukiel 1981). <br><br>Another group of studies has looked at the invasion of this species into grasslands (McLean 1969, Anderson and Bailey 1979, Agee and Dunwiddie 1984). Most research on the species has involved manipulations of individual plants and/or communities, and little literature exists on plant reproduction or ecology in unmanipulated settings. <br><br>Willard and McKell (1973) clipped SYMPHORICARPOS VACCINIOIDES for five years to simulate browsing. Treatments involved clipping at the same time each year, under deferred-rotation, alternate rest, and rest rotation grazing systems, each at three intensities (30%, 60%, and 90%) of herbage removal. Sprout numbers were higher in all of the clipping treatments, increasing with increased percent herbage removal. However, sprout mortality increased propor- tionately. Carbohydrate reserves were lowered by annual clipping in July. Future production of twigs, leaves and seeds was reduced by annual 60-90% herbage removals in early or mid-season. However, 30% herbage removal stimulated future production of leaves and twigs. <br><br>George and McKell (1978a, 1978b) studied seasonal patterns in car- bohydrate reserves in S. OREOPHILUS. Nonstructural carbohydrate reserves were lowest in May due mainly to a reduction in nonstruc- tural carbohydrate (NC) reserves in small roots and old stems. Carbohydrate levels in large roots and root crowns remained relatively stable seasonally. NCs for leaf production appear to come from stems rather than roots and followed a declining trend in plants fully defoliated at two-week intervals from June 1 to July 15, and on May 15, May 30, and June 15 the second year (George and McKell 1978a). Plants receiving this treatment died at the end of two years. <br><br>McLean (1969) categorized species based on their fire resistance by looking at rooting characteristics. The root system of S. ALBUS is described as fibrous with rhizomes which grow between 5 and 13 cm below the mineral soil surface and which show signs of being able to regenerate from those depths. It was predicted to be a fire-resistant plant because roots penetrate below depths that experience the greatest increases in temperature during fire. <br><br>Anderson and Bailey (1980) conducted burns in grass and shrublands annually for 24 years. Burns were conducted in April when soil moisture was high. The percent cover of SYMPHORICARPOS OCCIDEN- TALIS was much lower in burned plots than unburned plots; however, there was no difference in frequency. In Kansas, annual early spring burning reduced stem densities of S. ORBICULATUS, while late-spring burning eliminated the species entirely (Smith and Owensby 1972). <br><br>Westcott (1982) describes a species of tephritid fly, RHAGOLETIS ZEPHYRIA, the snowberry maggot, that oviposits on snowberry fruits. However, no estimates of infestation rates or effects on seed production were given. Because snowberry spreads mostly by vegetative growth and sprouting (Willard and McKell 1973), it is unlikely that reduction of seed production by flies would result in significant decline in snowberry populations.
Conservation Status
NatureServe Global Status Rank
G5
Global Status Last Reviewed
2003-02-28
Global Status Last Changed
1984-09-06
Distribution
Conservation Status Map
<img src="http://www.natureserve.org/explorer/servlet/GetMapGif?CA.AB=S5&CA.BC=SNR&CA.MB=S5&CA.NB=SE&CA.NF=SE&CA.NT=SNR&CA.NS=SE&CA.ON=S5&CA.PE=SE&CA.QC=S3&CA.SK=S5&US.AK=S2&US.CA=SNR&US.CO=SNR&US.CT=SNR&US.DE=SE&US.DC=SNR&US.ID=SNR&US.IL=SNR&US.IN=SNR&US.IA=S1&US.KY=S1&US.ME=SE&US.MD=S1&US.MA=SNR&US.MI=SNR&US.MN=SNR&US.MO=SNR&US.MT=S5&US.NE=S1&US.NH=SNR&US.NJ=SNR&US.NM=SNR&US.NY=SNR&US.NC=SNR&US.ND=SNR&US.OH=SNR&US.OR=SNR&US.PA=SNR&US.RI=SE&US.SD=SNR&US.TN=SNR&US.UT=SNR&US.VT=S3&US.VA=S3&US.WA=SNR&US.WV=S2&US.WI=SNR&US.WY=S3" alt="Conservation Status Map" style="width: 475px; height: auto;" />
Global Range
It is distributed throughout North America with the exception of Mexico. The plant may be found associated with FESTUCA IDAHOENSIS or CRATAEGUS on north-facing slopes in the Palouse region of eastern Washington and northern Idaho (Daubenmire 1970, Allen et al. 1980). In the Blue Mountains of northeastern Oregon, S. ALBUS is found with FESTUCA IDAHOENSIS, AGROPYRON SPICATUM, POA SANDBERGII, and CAREX GEYERI in grasslands and as an element of the understory in Ponderosa pine forests (Holechek et al. 1982). S. ALBUS also occurs in Douglas fir zones of southern British Columbia (McLean 1969). Agee and Dunwiddie (1984) found S. ALBUS in two habitats on Yellow Island in Puget Sound, Washington: (1) in woodlands associated with madrone, Oregon white oak, and invading Douglas fir and (2) as an element of the understory in Douglas fir- madrone-grand fir forests. According to Munz and Keck (1968), S. ALBUS is found on banks and flats in canyons and near streams below 4,000 feet in mixed evergreen forests, foothill woodlands, yellow pine forests, etc., of the Coast Ranges of California from Monterey County north and northern Sierra Nevada to Alaska.

