Pinus contorta understory vegetation dynamics following clearcutting in west-central Alberta, Canada

Abstract A sequence consisting of 143 post-clearcut ( 1 m tall) cover and stand age. Species composition and abundance data were obtained from stands by plot sampling. The abundance of understory plants designated as early-seral species was not correlated with stand age and was only weakly correlated with overstory cover. The relative abundance of early-seral plants decreased linearly in response to increasing overstory cover (r = −0.502, P  A 100-year chronosequence of Pinus contorta clearcut and unmanaged stands differed from a recognized model of natural forest development, due to the lack of a stem exclusion and a subsequent understory reinitiation stage. These differences in development were probably related to the low density of planted trees and the correspondingly open overstory that occurred during the early stages of stand development. Despite these differences, the composition of the understory vegetation within clearcuts appeared to be changing toward that of the unmanaged stands, although the initially more open overstory may have prolonged the presence of early-seral understory species. An overstory cover-based sequence suggests that growth-form cover and composition vary in response to the degree of understory shading. Understory vegetation that developed beneath a 30–70% overstory cover reflected characteristics of a tolerance interaction model, whereas greater overstory cover inhibited the development of ericaceous shrubs. Models of early forest community development should be stratified according to both the amount of overstory cover and the stand age to appropriately represent understory development trends.

[1]  I. Corns,et al.  A comparison of mature with recently clear-cut and scarified lodgepole pine forests in the Lower Foothills of Alberta , 1976 .

[2]  J. Francis Statistica for Windows , 1995 .

[3]  D. H. Knight,et al.  Aims and Methods of Vegetation Ecology , 1974 .

[4]  K. Stadt,et al.  Growth of understory Piceaglauca, Calamagrostiscanadensis, and Epilobiumangustifolium in relation to overstory light transmission , 1994 .

[5]  G. Bradfield,et al.  Succession in sub-boreal forests of West-Central British Columbia , 2003 .

[6]  A. M. Olson,et al.  SPECIES REPLACEMENT DURING EARLY SECONDARY SUCCESSION: THE ABRUPT DECLINE OF A WINTER ANNUAL , 1997 .

[7]  D. Coxson,et al.  Lichen chronosequences (postfire and postharvest) in lodgepole pine (Pinus contorta) forests of northern interior British Columbia , 2001 .

[8]  C. T. Dyrness Early Stages of Plant Succession Following Logging and Burning in the Western Cascades of Oregon , 1973 .

[9]  K. Stadt,et al.  Age structure and growth of understory white spruce under aspen , 1996 .

[10]  L. E. Anderson,et al.  List of the Mosses of North America North of Mexico , 1990 .

[11]  Charles B. Halpern,et al.  Early Successional Patterns of Forest Species: Interactions of Life History Traits and Disturbance , 1989 .

[12]  V. Lieffers,et al.  Seasonal changes in carbohydrate storage and regrowth in rhizomes and stems of four boreal forest shrubs: Applications in picea glauca understorey regeneration , 1997 .

[13]  Charles B. Halpern,et al.  Plant Species Diversity in Natural and Managed Forests of the Pacific Northwest , 1995 .

[14]  S. Payette,et al.  Postfire lichen–spruce woodland recovery at the limit of the boreal forest in northern Quebec , 1989 .

[15]  R. Alexander Major habitat types, community types, and plant communities in the Rocky Mountains / , 1985 .

[16]  W. Strong Lodgepole pine/Labrador tea type communities of western Canada , 2002 .

[17]  S. Haeussler,et al.  Plant community responses to mechanical site preparation in northern interior British Columbia , 1999 .

[18]  Charles B. Halpern,et al.  Overstory influences on herb and shrub communities in mature forests of western Washington, U.S.A. , 2000 .

[19]  G. Roi,et al.  Root density-soil relationships in selected boreal forests of central Alberta, Canada , 1985 .

[20]  S. Eversman,et al.  Recolonization of burned substrates by lichens and mosses in Yellowstone National Park , 2004 .

[21]  Louis De Grandpré,et al.  Long‐term post‐fire changes in the northeastern boreal forest of Quebec , 2000 .

[22]  J. Connell,et al.  Mechanisms of Succession in Natural Communities and Their Role in Community Stability and Organization , 1977, The American Naturalist.

[23]  Frank E. Egler,et al.  Vegetation science concepts I. Initial floristic composition, a factor in old-field vegetation development with 2 figs. , 1954, Vegetatio.

[24]  A. McKee,et al.  Species Composition and Diversity During Secondary Succession of Coniferous Forests in the Western Cascade Mountains of Oregon , 1988, Forest Science.

[25]  Victor J. Lieffers,et al.  Ecology of and control strategies for Calamagrostiscanadensis in boreal forest sites , 1993 .

[26]  G. Wetherill,et al.  Intermediate Statistical Methods , 1982 .

[27]  W. Strong Secondary vegetation and floristic succession within a boreal aspen (Populus tremuloides Michx.) clearcut. , 2004 .

[28]  J. H. Archibald,et al.  Field Guide to Ecosites of West-Central Alberta , 2002 .

[29]  F. Clements Scientific Books: Plant Succession. An Analysis of the Development of Vegetation , 2009 .

[30]  Y. Bergeron,et al.  CANOPY GAP CHARACTERISTICS AND TREE REPLACEMENT IN THE SOUTHEASTERN BOREAL FOREST , 1998 .

[31]  C. Oliver Forest development in North America following major disturbances , 1980 .

[32]  L. De Grandpré,et al.  Early understory successional changes following clearcutting in the balsam fir-yellow birch forest , 2000 .