Botanical composition of the diet of eight Spanish goats was studied o
n the Northern Great Basin Experimental Range during two stages of pla
nt phenology (active growth in early July and cured forage in mid-Augu
st) to assess their potential for the control of sagebrush (Artemisia
tridentata sspp, wyomingensis Nutt.) and western juniper (Juniperus oc
cidentalis Hook.) and their nutritional status on sagebrush-steppe ran
gelands. Diets were quantified by documenting the number of visits to
each species, the bites harvested and time expended prating each forag
e over 4 consecutive days in each period, Forage chemical characterist
ics evaluated included: CP, NDF, ADF, ADL and IVDMD, Diet composition
and forage quality indices varied significantly (P < 0.05) with change
s in plant phenology. Vegetation cover averaged 52% in the pasture and
consisted of 36% grasses, 8% forbs, 7% shrubs and 0.6% trees, Availab
le herbage (excluding woody plants) was 534 kg ha(-1) during active gr
owth trials and 572 kg ha(-1) when forages had cured. When forages wer
e green goats acquired 28% of their total bites from grasses, 71% from
forbs, 0.3% from shrubs and 0.9% from juniper trees. After forages ha
d cured values were 35% from grasses, 56% from forbs, 0.1% from shrubs
and 8.8% from juniper. The browsing of juniper (both foliage and bark
), after herbaceous forages had cured, was the only substantive use of
woody plants, Sagebrush was only lightly used (0.2% of total bites) w
hen herbaceous forages were actively growing. Available herbage was of
relatively high quality during both trials. When forages were activel
y growing; CP of grasses ranged from 8.9 to 5.6%, forbs from 17.7 to 8
.5%, sagebrush scored at 8.5%, juniper foliage at 8.1% and juniper bar
k at 3.2%. After herbaceous forages had cured, grass CPs ranged betwee
n 6.2 and 3.1%, forbs from 10.4 to 4.4%, shrubs were not sampled and j
uniper foliage averaged 7.6%, Given the low levels of browsing exhibit
ed by goats on sagebrush and juniper we see little opportunity for con
trol of these woody plants when pastures provide a diverse (N = 25 spe
cies) array of readily available (534-572 kg ha(-1)) and nutritious fo
rages and pastures are lightly stocked (0.63 goats ha(-1) month(-1)).
We do need, however, to further explore their potential for control of
these species under several other regimes. These include extended tri
als on more deteriorated rangelands, trials during seasons or conditio
ns where forage is limited and the animal's selective opportunity is r
estricted and trials in high quality environments on newly established
sagebrush and juniper seedlings.