Mj. Samuel et Rh. Hart, 61 YEARS OF SECONDARY SUCCESSION ON RANGELANDS OF THE WYOMING HIGH-PLAINS, Journal of range management, 47(3), 1994, pp. 184-191
The slow and uncertain rate of recovery of plant communities after sev
ere disturbance is a major problem on rangelands. Earlier studies sket
ched the outline of secondary succession on mixed-grass prairie, but w
ere based on 1 or 2 years of observation on different areas disturbed
at different times in the past, or several years of observation of a s
ingle area. To provide a more complete picture of succession over deca
des, we began observations in 1977 on 4 areas disturbed from 1 to 51 y
ears previously, and on undisturbed areas of the same 2 soil types wit
h and without grazing. Observations continued for 11 years. Secondary
succession proceeded through the usual stages: annual forbs, perennial
forbs and annual grasses, short-lived perennial grasses, and long-liv
ed grasses. Western wheatgrass [Pascopyrum smithii (Rydb.) A Love] was
an exception because it appeared much earlier and in much greater abu
ndance than other long-lived perennial grasses. Blue grama [Bouteloua
gracilis (H.B.K.) Lag ex. Steud.] may be another exception; total reco
very of this grass may require centuries. Time of appearance in succes
sion seemed to be related to availability of propagules and ease of es
tablishment; persistence of species was related to competitive ability
. Abundance of many species fluctuated widely from year to year, but f
luctuations did not appear to be related to precipitation. After 61 ye
ars, secondary succession had not returned plant communities to the cl
imax state.