Seed abundance versus substrate limitation of seedling recruitment in northern temperate forests of British Columbia

We examine the influence of (i) the spatial distribution and abundance of parent trees (as seed sources) and (ii) the abundance and favourability of seedbed substrates, on seedling recruitment for the major tree species in north - western interior cedar-hemlock forests of British Columbia, under four levels of canopy openness (full canopy, partial canopy, large gap, and clearcut). Substrate distribution varied with canopy openness, and substrate favourability was a function of both canopy openness and seedling species. Lack of suitable substrates was the predominant factor limiting seedling density under full canopies. Partial canopy and gap sites provided a broad range of favourable substrates in close proximity to parent trees, resulting in the highest observed seedling densities. There was much higher effective dispersion of seedlings away from parent trees in gaps than in the partially cut stands. Seedling dispersion to clearcut sites was poor with seedlings being tightly restricted to a narrow band along the forest edge. Thus, seedling recruit - ment in these forests was a reflection of the interaction between the abundance of seed and substrate favourability, and the relative importance of these factors varied significantly with canopy structure.

[1]  S. Pacala,et al.  SEEDLING RECRUITMENT IN FORESTS: CALIBRATING MODELS TO PREDICT PATTERNS OF TREE SEEDLING DISPERSION' , 1994 .

[2]  C. Augspurger,et al.  Arrival and Survival in Tropical Treefall Gaps , 1989 .

[3]  Yuan Ji,et al.  Fecundity and Dispersal in Plant Populations: Implications for Structure and Diversity , 1995, The American Naturalist.

[4]  D. Stoyan,et al.  Estimating the fruit dispersion of anemochorous forest trees , 2001 .

[5]  D. Minore Germination and early growth of coastal tree species on organic seed beds , 1972 .

[6]  R. C. Dobbs White Spruce Seed Dispersal in Central British Columbia , 1976 .

[7]  M. B. Clark Seed production of Hemlock and Cedar in the interior wet belt region of British Columbia related to dispersal and regeneration. , 1970 .

[8]  K. Coates,et al.  Models of sapling mortality as a function of growth to characterize interspecific variation in shade tolerance of eight tree species of northwestern British Columbia , 1997 .

[9]  K. Coates Tree recruitment in gaps of various size, clearcuts and undisturbed mixed forest of interior British Columbia, Canada , 2002 .

[10]  Jerry F. Franklin,et al.  Tree Seedlings on Logs in Picea‐Tsuga Forests of Oregon and Washington , 1989 .

[11]  J. Macmahon,et al.  SEED ENTRAPMENT IN ALPINE ECOSYSTEMS: EFFECTS OF SOIL PARTICLE SIZE AND DIASPORE MORPHOLOGY' , 1991 .

[12]  S. Pacala,et al.  Forest models defined by field measurements : Estimation, error analysis and dynamics , 1996 .

[13]  D. Greene,et al.  Wind Dispersal of Seeds from a Forest Into a Clearing , 1995 .

[14]  N. Barton,et al.  GENETIC ANALYSIS OF A HYBRID ZONE BETWEEN THE FIRE‐BELLIED TOADS, BOMBINA BOMBINA AND B. VARIEGATA, NEAR CRACOW IN SOUTHERN POLAND , 1986, Evolution; international journal of organic evolution.

[15]  C. M. Berntsen Seedling distribution on a spruce-hemlock clearcut. , 1955 .

[16]  W. Leak,et al.  Seed fall in an oldgrowth northern hardwood forest , 1992 .

[17]  James S. Clark,et al.  STAGES AND SPATIAL SCALES OF RECRUITMENT LIMITATION IN SOUTHERN APPALACHIAN FORESTS , 1998 .

[18]  D. Meidinger,et al.  Biogeoclimatic ecosystem classification in British Columbia , 1987 .

[19]  Charles D. Canham,et al.  Species variability in growth response to light across climatic regions in northwestern British Columbia , 1998 .

[20]  Charles D. Canham,et al.  Interspecific variation in susceptibility to windthrow as a function of tree size and storm severity for northern temperate tree species , 2001 .

[21]  C. Augspurger,et al.  MORPHOLOGY AND DISPERSAL POTENTIAL OF WIND‐DISPERSED DIASPORES OF NEOTROPICAL TREES , 1986 .

[22]  C. Canham,et al.  Measurement and modeling of spatially explicit variation in light transmission through interior cedar-hemlock forests of British Columbia , 1999 .

[23]  Charles B. Halpern,et al.  Controls on conifer regeneration in managed riparian forests: effects of seed source, substrate, and vegetation , 2001 .

[24]  T. Fahey,et al.  Seed dispersal and colonization in a disturbed northern hardwood forest , 1988 .

[25]  O. Sexton,et al.  Ecology of mast-fruiting in three species of North American deciduous oaks. , 1993 .

[26]  J. H. Smith,et al.  GROWTH AND SURVIVAL OF ENGELMANN SPRUCE AND ALPINE FIR ON SEED SPOTS AT BOLEAN LAKE, B.C., 1954-59 , 1960 .

[27]  C. Augspurger Offspring recruitment around tropical trees: changes in cohort distance with time , 1983 .

[28]  Robert L. Heilbroner,et al.  Growth and Survival , 1972 .

[29]  F. Ronco Engelmann Spruce seed dispersal and seedling establishment in clearcut forest openings in Colorado: a progress report. , 1970 .

[30]  L. Isaac Seed Flight in the Douglas Fir Region , 1930 .

[31]  K. Geier-Hayes Occurrence of conifer seedlings and their microenvironments on disturbed sites in central Idaho , 1987 .

[32]  Stephenie P. Joyner SAS/STAT guide for personal computers, version 6 edition , 1985 .

[33]  K. Coates,et al.  Regeneration from seed of six tree species in the interior cedar-hemlock forests of British Columbia as affected by substrate and canopy gap position , 1998 .

[34]  S. Eis ESTABLISHMENT AND EARLY DEVELOPMENT OF WHITE SPRUCE IN THE INTERIOR OF BRITISH COLUMBIA , 1967 .

[35]  D. Greene,et al.  LONG-DISTANCE WIND DISPERSAL OF TREE SEEDS , 1995 .

[36]  M. Andersen Mechanistic Models for the Seed Shadows of Wind-Dispersed Plants , 1991, The American Naturalist.

[37]  S. Payette,et al.  Seed dynamics of Betula alleghaniensis in a deciduous forest of north-eastern North America. , 1990 .

[38]  L. J. Anderson,et al.  Germination as a determinant of seedling distributions among natural substrates in Picea engelmannii (Pinaceae) and Abies lasiocarpa (Pinaceae) , 1996 .