R* & niches (and the meaning of everything) Ecology Club 11 Mar 10 Markus Eichhorn Niches Revision – Classical theory – Modern objections Empirical niches – – – – Tilman’s R* ZNGIs Impact vectors Supply points Coexistence criteria Parallel definitions Species requirements for survival – Grinnell (1917), Hutchinson (1957) Impacts on the environment – Elton (1927), MacArthur & Levins (1967) Hutchinson (1957) Fundamental niche – Seldom observed Realised niche Dimension 2 – What remains – Implies competition Dimension 1 n-dimensional hypervolume MacArthur & Levins (1967) Empirical frame – – – – Gause’s principle Lotka-Volterra models Maximum overlap Niche packing Little support – Not falsifiable – Requires evidence of trade-offs – Predation & stress not included What they say… No concept in ecology has been more variously defined or more universally confused than “niche” Real & Levin (1991) I believe that community ecology will have to rethink completely the classical nicheassembly paradigm from first principles Hubbell (2001) Let’s consider the concept of niche – If I knew what it meant I’d be rich. It’s dimensions are n But a knowledge of Zen Is required to fathom the b***h Cottam & Parkhurst in Hurlbert (1981) Reductionism Plant coexistence – 3 main resources – High local SR – How to differentiate? Liebig’s Law (1840) – Most limiting → GR – Animals – usually N Other forces – Main predators – Environmental stress Often few factors Per capita effects Birth rates Resource availability (R) Death rates Predator density (P) Per capita effects R* (Tilman 1982) R* R*2 Resource availability (R) R* definition Minimum R level – Birth rate = death rate – dN/dt = 0 – Population persists Competition – Lower R* wins – Reduces resources Other factors – Predation (P*) – Stress (S*) Per capita effects Predation P* P*2 Predator abundance (P) Resource B Predator B Predator A Stress (S) Predator (P) Resource A Resource (R) Resource (R) Niche features Zero net growth isocline (ZNGI) – Describes organism’s response to environment – Equivalent to Hutchinson’s niche Impact vectors (I) – Per capita effect of organism on the environment Supply vectors Resource B Predator B Predator A Stress (S) Predator (P) Resource A Resource (R) Resource (R) Resource B Predator B Predator A Stress (S) Predator (P) Resource A Resource (R) Resource (R) Wins Resource B Coexist Wins Resource A Wins Resource B Either wins Wins Resource A Predator B Each species has a stronger impact on the predator to which it is most vulnerable Wins Coexist Wins Predator A Predator (P) Better defended species (P*↑) must be a poorer resource competitor (R*↓) Wins Wins Coexist Resource (R) Stress (S) More efficient competitor (R*↑) more affected by stress Wins Wins Resource (R) Coexisting species ZNGIs must intersect 1. • • Otherwise one spp. always wins Each has an R* advantage Impact vectors must α ZNGIs 2. • • • Stronger impact on most limiting R Likely for optimal foraging species Expend more effort on limiting R Intermediate supply vector 3. • • Depends on position of supply point Intraspecific competition > interspecific Implications No. spp. = no. limiting resources / predators – Local coexistence only – –ve feedback between requirements & impacts Regional coexistence through habitat heterogeneity Predictions 1. 2. 3. 4. 5. 6. 7. Spp. with lowest R* best competitor for that R Dominance varies with ratio of 2 R No. spp. ≤ no. limiting R R supply vector → outcome Impact vectors → outcome Coexistence along a gradient through trade-offs Highest SR at intermediate ratio of 2 R Few tests in animal systems Most in plants / microbes R* evaluation Supported? Producer 1° consumer Detritivore Yes 22.5 5.5 3 No 8.5 1.5 1 Miller et al. (2007) Plant v. animal ecologists – Difference largely due to tradition & inertia – Predictions supported but more evidence needed 41 R* tests → 39:1:1 (Wilson et al. 2007) Tilman (1977) 5 Cyclotella and Asterionella 4 PO4 (μM) 2 essential Rs 3 2 1 0 20 40 60 SiO2 (μM) 80 100 Tilman (1982) Park Grassland Experiment Grasshopper diets Same diet, different optima Behmer & Joern (2008) Serengeti browsers Leaf Topi v. Wildebeest – unstable equilibrium Stem Cell contents biomass Serengeti ungulates Large species win when lots of cell wall Small species when high quality forage Cell wall biomass Murray & Baird (2008) Resource B Resource A Resource B Resource A Resource B Resource A Excluded species Invasive species Predator B Predator A Coexistence through variable predator densities Predator Resource Predator Gradient replacement due to either P or R Resource Stress No effect of varying R Resource e.g. rocky shore seaweed species & desiccation Light Pioneers Competitors Nitrogen The successional niche Light Facilitation Nitrogen Light Increased light competition Nitrogen New niche theory 1. Joint description of the environmental conditions that allow a local population to persist and the per capita effects on the environment 2. The ZNGI of an organism, combined with the impact vectors on the ZNGI in the multivariate space defined by the environmental factors Chase & Leibold (2003)