Ecology Lab WETLANDS COMMUNITY THEORY GRASSLANDS OTHER FORESTS BRYOPHYTES. Steve Henstra Glen Porter Alison Campbell

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WETLANDS Steve Henstra Glen Porter Alison Campbell GRASSLANDS Robbie Lee FORESTS Scott Black Kaeli Stark Gary Lewis Tania Perzoff Andre Arsenault Andrea Lawson Rosemary Mason Daniel Gagnon Bradfield Plant Ecology Lab BRYOPHYTES Kella Sadler Lyn Baldwin Pat Williston Norm Kenkel Research examples from my lab COMMUNITY THEORY Elizabeth Binney Alfred Brulisauer Paul Drewa OTHER Eduardo Jovel Shannon Hagerman Stephan Kesting Qiwei Liang Bob Bandringa John Binns Nick Page Eva Downarowicz

Gary the early years to conifer forests From coastal marshes

What s going on? Stability: the capacity for communities to persist in the same state after disturbance Community assembly: deterministic vs stochastic processes, role of the seedbank, etc. Vegetation-environment relationships: tidal flooding, soil, climate

PCA application: intertidal marsh creation at the Campbell River estuary

PCA application: intertidal marsh creation at the Campbell River estuary

Experimental design 4 islands 23 transects planted vs unplanted 1m vs.5m spacing 1981 Vegetation monitoring Island construction 1982 1983 1984 1985 1986 1988 1994

Conceptual model Range of Natural Variability Apparent Range Of Variability Management Target Present Condition [Source: Wong, C., & K. Iverson. 2003]

Conceptual model PCA 2 Full range of variability in coastal marshes Apparent range of variability at CR Management Target (after X years) 1982 veg plugs PCA 1

Early planting success on Island 1 1982 1983 1984 1985

Longer term success on Island 4 1982 1983 1985 1986 1988 1994

Also some concerns Island 3 (low elev.) Island 1 (Carex dieback) 1988 1994 1994

Aerial view of dieback zones

Plant community dynamics 1983-1994 Nunn s Island PCA trajectories of transects 1983-1994 Species richness Vegetation cover Mid marsh Low Marsh (Target) Island 1 Island 3 Island 2 Island 4

Summary of Coastal Conceptual model Marsh Research Range of Natural Variability Apparent Range Of Variability Management Target [Wong, C., & K. Iverson. 2003.] Present Condition

Summary of Coastal Conceptual model Marsh Research We re getting there Range of Natural Variability Apparent Range Of Variability Management Target Present Condition

PCA application: bryophyte community dynamics Most forest floor bryophyte associations are transient

PCA application: bryophyte community dynamics General Question: Do forest floor bryophyte communities show transience? Community-unit Low TAD (strong V-E coupling) Individualistic High TAD (weak V-E coupling) Environmental gradient

PCA application: bryophyte community dynamics Unstable - slope >25 o - small twigs & branches Forest floor stability gradient Stable - slope <25 o - compressed needles Q: How measure transience?

Conceptual model PCA 2 A microplots plot (400m 2 ) Within-plot bryophyte heterogeneity A > B B PCA 1

Conceptual model PCA 2 A microplots bryophytes B environment Strong V-E coupling (low TAD) PCA 1

Conceptual model PCA 2 A Weak V-E coupling (high TAD) B PCA 1

PCA application: bryophyte community dynamics Steps in data analysis Divide plots into 2 groups based on environmental (microhabitat) stability. Use PCA to calculate within-plot heterogeneity. Do separately for bryophyte vegetation (V) and environment (E). Compare V-E for the 2 stability groups: - strong V-E => low transience - weak V-E => high transience

PCA application: bryophyte community dynamics PCA environment 3 PCA bryophytes 20 stable 2 unstable 10 1-3 -1 1 3-10 10 20-1 -2-10 symbols show 400m 2 study plots symbol size indicates degree of heterogeneity for each plot

PCA application: bryophyte community dynamics 1.0 0.5 stable r 2 =0.25 p=0.01 (low transience) Log Bryo Area 0.0-0.5 unstable r 2 =0.03 p=0.49 (high transience) -1.0-1.0-0.5 0.0 0.5 Log Env Area symbols show 400m 2 study plots Conclusion: TAD may be an important community structuring mechanism