Restoring coal mined land to pie-mining shrub cover, density height, commun
ity composition, and diversity to renew wildlife habitat quality is a prior
ity for reclamation specialists. Long-term shrub reestablishment success on
reclaimed mined land in Wyoming and suitability of these lands for wildlif
e habitat are unknown. Fourteen reclaimed study sites, 10 yr old or older,
were selected on 8 mines in Wyoming to evaluate shrub reestablishment and w
ildlife habitat value for antelope (Antilocapra americana) and sage grouse
(Centrocercus urophasianus). Five sites were categorized as fourwing saltbu
sh (Airplex canescens) sites and 9 as fourwing saltbush/big sagebrush (A. c
anescens/Artemisia tridentata spp. wyomingensis) sites. Published data desc
ribing antelope and sage grouse-preferred habitat requirements in sage-brus
h-grassland ecosystems were used to evaluate shrub community value of sampl
ed sites for wildlife habitat. Mean shrub canopy cover, density, and. heigh
t for fourwing saltbush sites were 5.8%, 0.23 m(-2), and 41.6 cm, respectiv
ely compared to 5.6%. 0.61 m(-2), and 31.1 cm for fourwing saltbush/big sag
ebrush sites. Two fourwing saltbush and 4 fourwing saltbush/big sagebrush s
ites provided sufficient cover for antelope, while 2 fourwing saltbush and
a fourwing saltbush/big sagebrush sites were adequate for sage grouse. Only
1 fourwing saltbush/big sagebrush site provided high enough shrub densitie
s for sage grouse. One fourwing saltbush and 7 fourwing saltbush/big sagebr
ush sites provided ample shrub heights For antelope, while 1 fourwing saltb
ush and 8 fourwing saltbush/big sagebrush sites were sufficient for sage gr
ouse, One fourwing saltbush and 1 fourwing saltbush/big sagebrush site prov
ided enough grass, forb,, and shrub composition for antelope, while no site
in either reclamation type was satisfactory for sage grouse. Shrub diversi
ty was 3 times higher for fourwing saltbush/big sagebrush sites (0.984) tha
n for fourwing saltbush sites (0.328). Individually, sites seeded with mult
iple shrub species had higher canopy cover, density, and diversity compared
with single-species shrub seedings. Achieving pre mining shrub cover, dens
ity, height, community composition, and diversity within existing bond-rele
ase time frames is unrealistic, considering that some native shrublands req
uire 30-60 yr to reach maturity.