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Communities
Page history last edited by Anonymous 2 yrs ago
- Dr. Wayne R. Hawthorn, B1 280, 888-4567 ext. 32117, e-mail: wrhawtho@uwaterloo.ca
- Krebs, C. J. 2001. Ecology: The experimental analysis of distribution and abundance. 5th edition. Benjamin Cummings. San Francisco, CA. 695 pp. ISBN 0-321-04289-1
marks
- assignments 3x10% = 30%
- uwace quizzes best 3 of 5 x 2% = 6%
- midterm 24% 50 mins
- final 40% 2.5 hours
- community: assemblage of interacting species and their relationships
- community characteristics: biodiversity, relative abundance, growth form physical structure, trophic structure, temporal dynamics (succession, non-equilibrium dynamics)
- ecosystem function: processes that keep an ecosystem working/changing (eg primary production, nutrient cycling, decomposition)
- Rivet Hypothesis (species proportional to functions) vs Redundancy Hypothesis (after N species, functions level off)
- super organism (no) vs Individualistic School (yes)
- supported by community association analyses, complexity of plant associations due to environmental gradients, paleopollen data
- ecotone: transition area between communities
- measuring species independence
- 2x2 contingency table (species 1 vs species 2, present/absent)
a b
c d
- chi2: (ad-bc)2N/(a+b)(c+d)(a+c)(b+d)
- ad > bc = positive association; ad < bc = negative association
- disarticulation: past communities members occurred in very different proportions and combinations than today (ugh, not real definition...)
- refuge: shelter from trouble
- measuring place similarities
- 2x2 contingency table (place 1 vs place 2, # species present/absent)
- x = column 1 sum, y = row 1 sum
- measure with binary, proportional, or quantitative similarity coefficients
- Jaccard: a/(a+b+c)
- Sorensen: 2z/(x+y) (z=a)
- probs: influenced by sample size (number of individuals) and species richness
- measuring abundance: density, frequency (chance of finding a given species within a sample), cover/dominance (plants' vertical projection onto ground)
- proportional/percent similarity coefficient: takes species abundance into account
- PS = sum of lowest % over all species in a pair of stands
- quantitative similarity coefficients
- distance coefficient: 1-sqrt(sum of squares of differences between sites)
- Morisita (1959)/Horn (1966) index of similarity: best one since relatively independent of sample size
- dendrogram: one axis of similarity, connect sites together
- indicator species: to use one/few species for community identification, to assess community health
- criteria: stable taxonomy, natural history known, ease of surveying, niche, associated with other species
- rarely can be a single species, eg. tree swallows (guilds may be better)
- some eg. butterflies may be just visiting
- good choices: earthworms, benthic insects (ephemeroptera+plecoptera+trichoptera)
- target species: ones you're interested in
- choosing target species: umbrella species (those needing big ranges), charismatic (aka flagship), keystone (impact > biomass)
- usually important (politics, economics, etc.)
- succession: community developing by it acting on the environment leading to new species there; one community replacing another
- initial floristic composition model: all spp there from start (seeds/roots = propagule pool/seed bank); individualistic; short-lived fast-growers then opposite
- null model: Lawton, 1987
- Connel and Slatyer 1997
- facilitation model: species increase favourability for other species (until they don't)
- previously supported by Glacier Bay (N-fixers then N-needers); however N-needers germination inhibited, seedling growth facilitated early
- inhibition model: spp fight competition (replaced when die or external factors), seen as main process for when "who is first" is important
- perhaps supported by lake michigan water level fall's sand dunes, some inhibition by oaks
- one study shows inhibition allowing change through disease
- r (fast growth, many small seeds, short lives) vs K (slow growth (near carying capacity), few big seeds, long lives)
- fish species in 3space: age at maturity, fecundity, juvenile survivorship
- Grime's model
| disturbance intensity | stress intensity | | low | high | | low | competitive (K) | stress-tolerant | | high | ruderal/weed (r) | none |
- C-S-R model: 3space of competitive, ruderal, stress-tolerant in triangle (0-100%)
- problems
- ST plants are C plants under low resources... C-ST is artificial distinction
- some climax trees are ST when young, C when old
- trade-offs: stuff can't be good at everything, but not everything conforms and/or may not be obvious (1 big loss=many small gains)
- could divide succession into colonization, maturation, senescence
- succession doesn't necessarily have same climax as before disturbance
- eg fires in indonesia lead forests to savanna then grassland
- markov process: ignores most stuff, just looks at what saplings replace trees (replacement probabilities)
species
- Ambrosia is the genus for ragweed
- hardwood = deciduous, softwood = coniferous
know some things from the succession characteristics table
things with numbers
- species associating: significance via chi-square, +/- via data
- stand similarity: binary (species presence/absence), proportional, quantitiative
Communities
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