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VALUE AND USE

SPECIES : Ceanothus integerrimus | Deerbrush
IMPORTANCE TO LIVESTOCK AND WILDLIFE : Deer brush provides high-quality, palatable, and often abundant forage for livestock and wildlife, especially deer [1,22,65]. On Arizona chaparral of the Tonto National Forest, deer brush was one of three principle browse species used by white-tailed deer in fall [50]. In California, deer brush is the most important summer browse species for mule deer and livestock in the ponderosa pine belt. Mule deer also make moderate to heavy use of it on California's winter ranges [22,48]. Porcupine browse deer brush stems. Gambel quail have been observed eating large quantities of the seed [13]. PALATABILITY : Deer brush is highly palatable to ungulates [65,72]. NUTRITIONAL VALUE : Deer brush leaves are high in protein, and calcium levels are high in both leaves and twigs. However, based on the nutritional standard for lactating cows, deer brush provides inadequate levels of phosphorus and digestible energy. Overall, browse quality decreases from late spring to late summer. On the Sierra National Forest, nutritional quality of deer brush browse varied significantly by year, but not by shrub age or degree of overstory canopy closure. Average nutritional content of deer brush, collected every 2 weeks from June 1 to September 8, 1982 and 1983, follows. Data are means (standard errors) [42]. Variable Year Leaves Twigs _______________________________________________________________________ neutral-detergent fiber (%) 1982 33.66 (1.92) 65.48*(2.25) 1983 25.38 (1.39) 53.17*(1.05) acid-detergent fiber (%) 1982 19.85*(1.71) 48.42*(2.02) 1983 14.65*(0.89) 38.95*(0.88) in-vitro digestible dry matter 1982 53.93*(3.64) 33.49 (1.70) 1983 63.60*(1.38) 35.14 (1.40) digestible energy (kcal/g) 1982 2.42*(0.18) 1.48 (0.08) 1983 2.93*(0.06) 1.56 (0.06) crude protein (%) 1982 18.15*(0.43) 8.22*(0.34) 1983 16.92*(0.30) 7.77*(0.23) calcium (%) 1982 3.66*(0.47) 1.27*(0.10) 1983 2.33*(0.10) 1.07*(0.05) phosphorus (%) 1982 0.18 (0.01) 0.16*(0.01) 1983 0.19 (0.01) 0.12*(0.01) _______________________________________________________________________ *Significant (p<0.05) difference with respect to year of collection Average protein content of deer brush collected from various California locations varied seasonally as follows [11]: April August October ------ ------ ------- 25.2 % 13.7 % 8.9 % COVER VALUE : NO-ENTRY VALUE FOR REHABILITATION OF DISTURBED SITES : Deer brush is recommended for use on restoration projects due to its nitrogen-fixing ability [25]. Transplanting wild 1-, 2-, and 3-year-old shrubs has been successful in the Sierra Nevada [13]. Growing stock from seed has shown good results, although seed requires several months of pregermination treatment. Reed [63] has compiled procedures for germinating seed in the laboratory. OTHER USES AND VALUES : Deer brush has attractive white, lilac, or pink flowers and is planted as an ornamental [46]. It is also a valuable honey plant [72]. Miwok Indians of California made baskets from deer brush branches [5]. MANAGEMENT CONSIDERATIONS : Bartolome and Kosco [8] and Minore and others [56] have developed models for predicting growth and browse production of deer brush. Deer brush can outcompete conifer seedlings for root space, water, and nutrients. Plantation conifers have generally shown better growth with deer brush control [27,34,51]. Deer brush may not adversely affect natural conifer regeneration, however. Griffin [28] reported that after severe, stand-replacing wildfire on the Los Padres National Forest, sugar and Coulter pine establishment was more successful in the presence of deer brush than on sites where deer brush was absent. Control: Amitrole (95-98 %), 2,3,6-TBA (80-95 %), 2,4,5-T (85-100 %), and 2,4-D (90-100 %) give good to excellent control of deer brush [68,86]. (Percent control obtained on Oregon brushfields and timberlands is given in parenthesis [68].) Biological control: Grazing cattle or domestic sheep on conifer plantations has given good control of deer brush stems [49,57,51]. Prescribed grazing may not result in conifer seedling release, however. On the Tahoe National Forest, a 9-year study on the effects of grazing domestic sheep on a ponderosa pine plantation showed that although domestic sheep significantly (p=0.05) reduced aboveground deer brush biomass, deer brush still remained competitive. After 9 years, height and stem diameter of ponderosa pine were not statistically different between grazed and ungrazed control plots, while ponderosa pine on grubbed plots was significantly (p=0.05) taller and larger in stem diameter than on control plots [53].

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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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