Knowledge of the rate woody plant canopy cover increases is essential for u
nderstanding the ecology of rangeland plant communities, determining the ec
onomic feasibility of brush management practices, and for scheduling initia
l and maintenance control practices. We determined rates of change in redbe
rry juniper (Juniperus pinchotti Sudw.) canopy cover from the mid 1950s thr
ough the late 1990s at 5 locations in western Texas on rangeland that had b
een chained or grubbed for juniper control and on adjacent untreated areas.
Juniper cover was estimated from aerial photographs by the line intercept
method using a 10-X monocular lens with a vernier. Juniper cover increased
at 0.35 +/- 0.06 percentage units year(-1) on untreated sites and at 1.01 /- 0.07 percentage units year(-1) following chaining or grubbing. Juniper c
over returned to pre-treatment levels in an average of 20 years (range 11 t
o 25) following chaining or grubbing. Herbage production on untreated range
land was predicted to decline slowly (2.4 to 5.0 kg ha(-1) year(-1)) as jun
iper cover increased from 6 to 14% and rapidly (> 8 kg ha(-1) year(-1)) as
juniper cover increased from 30 to 38%. Herbage production was predicted to
decline at a constantly increasing rate following mechanical control of ju
niper, from < 2 kg ha(-1) year(-1) in year 1 to 23 kg ha(-1) year(-1) in ye
ar 29. Potential additional livestock carrying capacity due to juniper cont
rol would be under estimated by more than 40%, assuming forage production w
ithout treatment remained constant during the entire planning horizon of an
economic analysis. To avoid significant reductions in livestock carrying c
apacity, redberry juniper control should be implemented before its canopy c
over exceeds about 20%.