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Invasions and resident communities Richard Law University of York, UK
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Invasions in a community context Hieracium pilosella Mimulus guttatus Cytisus scoparius Pinus
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Invasions in a community context invasions are stochastic invasion depends on propagule pressure invasion implies persistence (usually) invasion resistance and regional processes invasion depends on resident community Invasion: arrival of some propagules at some location, leading to local population, large enough for the probability of extinction by demographic stochasticity to be small increasing speculation!
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Invasions are stochastic theory microcosms field
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theory: from birth-death processes Probability P(n,N) that a population starting with n independent individuals reaches a size N before it goes to extinction (Bailey 1964; Goel and Richter-Dyn 1974) where b and d are constant probabilities per unit time of giving birth and of death (b > d ) Can think of an inoculum of n individuals, rare enough not to interact, added to a resident community
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theory: probability of establishment Warren, Law and Weatherby (2006) In M. W. Cadotte, et al. n r/b P(n)P(n) depends on r/b how important is r? To get established, require N to be large enough for stochastic effects to be small. For d < b, large N
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microcosms: protists Weatherby, Warren & Law 1998. Journal of Animal Ecology 67, 554-566 controlled experiments short time scales high replication but not a substitute for field work
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Warren, Law & Weatherby 2003. Ecology 84:1001-1011. microcosms: background A. persistent sets of species B. which absent species can invade persistent sets C. the new community which emerges from invasion Gives a graph showing invasions, and changes in communities. Can build a map of community assembly Experimental work looks for:
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microcosms: initial growth of Blepharisma Law, Weatherby & Warren 2000. Oikos 88, 319-326. stochasticity is important in establishment Blepharisma introduced to Paramecium microcosms Example of stochasticity
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field: releases of a hemipteran to control broom in New Zealand 5 (100)5270 8 (80)1090 6 (60)1030 4(40)10 3 (30)104 2 (20)102 No. (%) colonies extant after 1 year No. of sites Intended release size hemipteran: Arytainilla spartiophila (European specialist on broom) Memmott et al 2005 JAE 74:50-62 many other examples demonstrate stochasticity
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Invasion depends on propagule pressure theory microcosms field
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theory: propagule pressure n r/b P(n)P(n) Warren, Law and Weatherby (2006) In M. W. Cadotte, et al. assuming independence but there may not be independence e.g. Allee effect, founder effects, local interactions in space
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field: biocontrol of broom in NZ Memmott et al 2005 JAE 74:50-62 5 (100)5270 8 (80)1090 6 (60)1030 4(40)10 3 (30)104 2 (20)102 No. (%) colonies extant after 1 year No. of sites Intended release size release of hemipteran: Arytainilla spartiophila (European specialist on broom) increasing propagule pressure increasing probability of colony survival
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Invasion implies persistence (usually) theory microcosms field
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theory: permanence all orbits starting in the skin move further into the interior boundary is a repellor skin of finite thickness x1x1 x2x2 permanence: from dynamical-systems theory (not well known)
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theory: permanence: Lyapunov functions fixed point test by Lyapunov-like methods extends to multispecies systems with k species, but have to check 2 k subsystems boundary of phase space 2D phase plane
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theory: invasion implies persistence resident community invading species augmented community invading species persists augmented community permanent Case A: collapse to a subset S of aug. comm. augmented community not permanent Case B:
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theory: invasion implies persistence can S be the resident community? no: new species can invade it can S be a subset of the resident community? no: resident community is permanent and contains no attracting subsystem leaves only subsets which contain new species invasion implies persistence caveats resident community not permanent heteroclinic cycles
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microcosms: exceptions: invaders as catalysts of change: {B,P} {P} E prop. microcosms new species established prop. microcosms new species persisted invasion usually implies persistence
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field: Exceptions? rabbits on islands biological control agents others?
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invasion depends on resident community theory microcosms field
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theory = Can think of the resident community as providing an environment E, into which a new species is introduced
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omnivore: feeds on bacteria and small protists eats T as well as competing with it holds its own in competition with C microcosms: introducing Blepharisma Law, Weatherby & Warren 2000. Oikos 88, 319-326. struggles to compete with P
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microcosms: initial rate of increase GLM i : effect of resident communities i : effect of introduced species ij : introduction x resident interaction a lot depends on idiosyncrasies of particular ecological interactions
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field: invasion resistance less invasion into species-rich communities: more niches filled (Elton 1958 etc) treating every invasion as a special case not very helpful attempts to generalise not obvious why introduced species should be a weaker competitor than resident species
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field: confusion? At large spatial scales more exotic species get into species-rich communities (e.g. Lonsdale 1999) At small spatial scales, species-rich communities less readily invaded (e.g. Naeem et al 2000)
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Invasion resistance and regional processes speculations about species pools speculation: evolution of biotic interactions theory: community assembly and invasion-resistance
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theory: community assembly algorithm Law & Morton 1996. Ecology 77:762-775. {1} {1,3} 3 {2} 2 4 {1} species pool new species resident comm {1,2,3,4…}
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theory: community assembly and invasion resistance Law & Morton 1996. Ecology 77:762-775. invasion resistance increases invasion resistance: prop. species from pool unable to invade community statistical result invasion resistance depends on history of community, not on its species richness
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speculations about invasion resistance and species pools larger species pools get communities closer to invasion-resistant states richness of pool matters more than richness of community size of species pool: composition of species pool species pool lacking major parts of a flora/fauna unlikely to be near invasion resistant states communities from such species pools are especially vulnerable to invasions by introduced species
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evolution of biotic interactions differences in specificity of mutualistic symbionts and enemies where do the rhizobia come from? mycorrhizal fungi? etc
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Conclusions invasions and extinctions are part of the natural turnover process in communities community context is crucial for understanding invasions NZ species pool is special
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