Disturbance: Introduction, with a terrestrial bias Peter White, Biology/Ecology 255, Sept 9, 2005

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Disturbance: Introduction, with a terrestrial bias Peter White, Biology/Ecology 255, Sept 9, 2005 Slide 2 Outline A personal history Definition and significance Importance Search for generality Discussion Slide 3 Outline A personal history Definition and significance Importance Search for generality Discussion IDH, niche and neutrality; Large scale behavior: Criticality, HRV, Resilience; Legacy and History matters; Top-down and bottom-up control and the Healthy Forest Initiative; Restoration Slide 4 Dartmouth, 1970s Slide 5 William S. Cooper ESAs Cooper Award Cooper, W.S. 1926. The fundamentals of vegetation change. Ecology 7:391-413. Slide 6 Cowles Slide 7 CowlesCooper Slide 8 CowlesCooperBuell Slide 9 CowlesCooperBuellReiners Slide 10 CowlesCooperBuellReinersME! Slide 11 CowlesCooperBuellReinersME! W.A.R. Slide 12 Watt, A.S. 1947. Pattern and process in the plant community. Journal of Ecology 35:1-22. Slide 13 Pattern and process in a forested ecosystem Pattern and process in cliff ecosystems Pattern and process in mangrove ecosystems Pattern and process in neotropical secondary rain forests Pattern and process in the dynamics of seed banks Pattern, process, and prediction in aquatic ecology. Spatial pattern and process in plant-pathogen interactions Pattern, process, and predictability: the use of neutral models for landscape analysis Landscape ecology: the effect of pattern on process. Slide 14 Watt, A.S. 1923. On the ecology of British beechwoods with special reference to their regeneration. Journal of Ecology 11:1-48. Slide 15 The Leopold Report, 1963 Slide 16 Excitements! Succession did not start from equally blank slatesSuccession did not start from equally blank slates Slide 17 Excitements! Disturbance was inevitableDisturbance was inevitable Slide 18 27 Cove Trees of Joyce Kilmer Memorial Forest Ma Mt MfLt Ar As Th Ap Qr Cd Cg Fa Af Ns Io Fg Ba Bl Cf Ps Al Im Ca Hv Tc Hc Dv +10 more Slide 19 Excitements! Succession did not start from equally blank slatesSuccession did not start from equally blank slates Disturbance was inevitableDisturbance was inevitable Diversity dependent on recurrent disturbanceDiversity dependent on recurrent disturbance Slide 20 Excitements! Succession did not start from equally blank slatesSuccession did not start from equally blank slates Disturbance was inevitableDisturbance was inevitable Diversity dependent on recurrent disturbanceDiversity dependent on recurrent disturbance Chance and transient dynamicsChance and transient dynamics Slide 21 Shakespeare, hes in the alley --Bob Dylan, Stuck Inside of Mobile with the Memphis Blues Again, Blonde on Blonde Slide 22 Slide 23 Death of The Climax Missouri Botanical Garden, 1978 Slide 24 Henry Cowles 1899 Lake Michigan Sand Dunes Slide 25 Death of The Climax Missouri Botanical Garden, 1978 b. Chicago, Illinois, 1899 d. St.Louis, Missouri, 1978 Climax Slide 26 Slide 27 Changes Academic lineage questionAcademic lineage question Language requirementsLanguage requirements Slide 28 Changes Academic lineage questionAcademic lineage question Language requirementsLanguage requirements Reprint request cardsReprint request cards Slide 29 Changes Academic lineage questionAcademic lineage question Language requirementsLanguage requirements Reprint request cardsReprint request cards Nature of the thesisNature of the thesis New journalsNew journals Slide 30 Subscriptions to journals and journal loyalty -- we read more now but less in any one journal, and typically in digital format. And, our method of discovery is altogether different Bob Peet www.unc.edu/scholcomdig/whitepapers/peet.pdf www.unc.edu/scholcomdig/whitepapers/peet.pdf Slide 31 Species response to disturbance (from Vogl 1974) IncreasersIncreasers DecreasersDecreasers InvadersInvaders RetreatersRetreaters IntegratorsIntegrators Neutral speciesNeutral species Slide 32 Questions for the Semester What have we learned?What have we learned? What generalities can we make?What generalities can we make? What are the obstacles to generality?What are the obstacles to generality? What are the interesting and important questions?What are the interesting and important questions? Slide 33 First announcement: Disturbance and restoration in forest ecosystems Course for the PhD-programme in Biodiversity and Forestry, Vrdns, Linkping, Feb 13 17, 2006. Course leaders: Mats Niklasson, Southern Swedish Forest Research Centre, SLU Per-Anders Esseen, Ecology & Env Science, UMU Invited teachers: prof Peter White,Biology Univ of North Carolina, USA prof Sylvie Gauthier, Canadian Forest Service, Quebec Lars- Owe Wikars, Entomology SLU Uppsala Lars stlund, Forest Vegetation Ecology, SLU Ume and more Slide 34 Outline A personal history Definition and significance Importance Search for generality Discussion Slide 35 Disturbance definitions Absolute:Absolute: A discrete event in time that disrupts ecosystem, community, or population structure and changes resources, substrate availability or the physical environment (White & Pickett 1985) Grime: a loss of biomass Slide 36 Slide 37 Relative Definition: Displacement from normal dynamics Patch dynamicsPatch dynamics Quantitative & qualitative equilibriumQuantitative & qualitative equilibrium Historic Range of Variation, Natural Range of VariabilityHistoric Range of Variation, Natural Range of Variability CriticalityCriticality ResilienceResilience Slide 38 Importance BiodiversityBiodiversity Exotic invasionsExotic invasions Effects on value, healthEffects on value, health Ecosystem use, harvestEcosystem use, harvest Climate changeClimate change Land-use and hazard insuranceLand-use and hazard insurance Environmental ethics in a patch dynamic worldEnvironmental ethics in a patch dynamic world Slide 39 The 17 Ten Greatest Hits 2000+ Papers Obstacles to Generality Slide 40 Patch & Multipatch Scales Patch scale Multipatch scale Slide 41 Thinking about disturbance SpacePatchMultipatch(Landscape) Slide 42 Space/TimeEventMultievent PatchMultipatch(Landscape) Slide 43 Thinking about disturbance Space/TimeEventMultievent Patch1. P-E2. P-ME Multipatch 3. MP-E4. MP-ME (Landscape) Slide 44 Thinking about disturbance Space/TimeEventMultievent Patch1. P-E2. P-ME Multipatch 3. MP-E4. MP-ME (Landscape) Slide 45 Thinking about disturbance Space/TimeEventMultievent Patch1. P-E2. P-ME Multipatch 3. MP-E4. MP-ME (Landscape) Easiest to study Slide 46 Thinking about disturbance Space/TimeEventMultievent Patch1. P-E2. P-ME Multipatch 3. MP-E4. MP-ME (Landscape) Biodiversity, Sustainability Slide 47 Thinking about disturbance #1 Patch-Event Scale Legacy matters Empirical detail matters Specificity matters Slide 48 Disturbances within one ecosystem vary Appalachian Fir Forest Slide 49 Slide 50 A family of successions differing in legacy because of difference in severity Slide 51 Fire intensity & effects on soils --from Ryan 2002 Slide 52 FIRE SEVERITY Organic Soil Depth & Coarse Wood Long Term Drying Short Term Drying & Wind Canopy Height & Mass of Fine Fuel Site Factors Weather Factors Fireline Intensity (Flame Length) Depth of Burn UnburnedLightModerateDeep Unburned Low Moderate High Extreme 19 Ground Fire with Total Duff Consumption Time (hours) 0 Temperature (C) 1100 Savannah Grass Fire without Duff Consumption Time (minutes) 4 Temperature (C) 325 0 Crown Fire without Duff Consumption Time (minutes) 10 25 Temperature (C) 0 1100 016 Crown Fire with Total Duff Consumption Time (hours) Temperature (C) 1100 Slide 53 Slide 54 Richter et al. 1996 Slide 55 Specificity & structure NoneNone Drought, landslide, dune movement, freeze-thaw, salinity incursions, crown fire Large, dominant individualsLarge, dominant individuals Ice storm, wind Small individualsSmall individuals Surface fire, flood, falling trees Slide 56 Disturbance specificity aAbB Succession Disturbance Slide 57 Disturbance specificity: Setting succession back aAbB Succession Disturbance Slide 58 Disturbance specificity: Advancing succession aAbB Succession Disturbance Slide 59 Disturbance specificity: Holding succession in check aAbB Succession Disturbance Slide 60 Disturbance specificity: Maintaining late successional species aAbB Succession Disturbance Slide 61 Thinking about disturbance #2 Space/TimeEventMultievent Patch1. P-E2. P-ME Multipatch 3. MP-E4. MP-ME (Landscape) History matters Interactions matter Slide 62 Clark 1996 Disturbance density in time Slide 63 Disturbance Regime: Synergisms Feedback between community state & disturbanceFeedback between community state & disturbance Feedback between time since disturbance & the next disturbanceFeedback between time since disturbance & the next disturbance Disturbance interactionsDisturbance interactions Slide 64 Disturbances interact: history matters + promote subsequent disturbance - inhibit subsequent disturbance Fire-fire (Covington & Moore 1994)Fire-fire (Covington & Moore 1994) Fire-insect (Flamm et al. 1993)Fire-insect (Flamm et al. 1993) Fire-grazing (Vinton et al. 1993)Fire-grazing (Vinton et al. 1993) Wind-fungi-insects (Matlack et al. 1993)Wind-fungi-insects (Matlack et al. 1993) Avalanche-fire-insects (Veblen et al. 1994)Avalanche-fire-insects (Veblen et al. 1994) Slide 65 Hardwoods White pine % Damage 20 40 Age (yr) 80 100 Hurricane damage increases with age & is greater in successional pine stands than hardwoods at any age -- Foster 1988 Slide 66 Disturbance Regime: Synergisms Feedback between time since disturbance & the next disturbanceFeedback between time since disturbance & the next disturbance Suppression decreases frequency BUT increases severity Slide 67 Feedback with time since disturbance: fire From Niklasson & Granstrom Slide 68 Gustafson et al. 2004 Management influence on risk of crown fire to towns FIRE SUPPRESSION DECREASES CROWN FIRE RISK! Slide 69 Thinking about disturbance #3 Space/TimeEventMultievent Patch1. P-E2. P-ME Multipatch 3. MP-E4. MP-ME (Landscape) Slide 70 Climate, site drive disturbance regime Process creates pattern Pattern creates process Slide 71 Disturbance-climate relations Regional synchronicityRegional synchronicity Climate systems & spatial autocorrelation Stress on management Violation of independence for otherwise isolated populations that we had hoped were independent Southern Oscillation & fire --Swetnam & Betancourt 1990 Slide 72 Bekker & Taylor 2001 Slide 73 Rollins et al. 2002 In the S, more fire on NW, N, NE slopes In the N, more fire on SW, W slopes Slide 74 Process creates pattern + Fire often increases heterogeneity - Succession often decreases heterogeneity Slide 75 Heterogeneity Higher Lower Slide 76 Hi Meadow, CO 4,422 ha Viveash, NM 11,017 ha Bobcat Gulch, CO 3,059 ha High burn Low/ Unburned Image from S. Kotliar, USGS Heterogeneity is important in recovery: distance, size, seed source, legacy Slide 77 Pattern also creates process + Fire spread from more to less flammable stands - Fire absent from flammable stands because of fire breaks Slide 78 Islands in boreal forest lakes Bergeron & collaborators Isolated from large, high intensity mainland fires Lightning ignitions increase as island size, elevation, & isolation increase Frequent low intensity fires maintain island populations of Red Pine that could not persist in the mainland crown fire regime Slide 79 Fuel Connectedness & Fire Cape Canaveral Duncan & Schmalzer 2004 Slide 80 Connectedness & Fuel Moisture Slide 81 Turner and Romme 1994 * * high fuel moisture e.g., typical spring * * low fuel moisture e.g. typical late-summer low flammability high flammability burned * lightning strike very low fuel moisture and wind e.g. 1988 WIND * * Slide 82 Pattern & Process Pattern controls process at low to medium fire intensities Process overwhelms pattern at high fire intensities Agee 1998 Slide 83 Pattern & Process Pattern controls process at low to medium fire intensities Process overwhelms pattern at high fire intensities Agee 1998 TOP DOWN vs. BOTTOM UP CONTROL Top Down = Climate Bottom Up = Fuels Slide 84 Thinking about disturbance #4 Space/TimeEventMultievent Patch1. P-E2. P-ME Multipatch 3. MP-E4. MP-ME (Landscape) Dynamic equilibrium Historic range of variation Slide 85 Frequency vs. Magnitude Gaps in Japanese deciduous forest --Tanaka & Nakashizuka 1998 Slide 86 Two definitions of dynamic equilibrium 1. Quantitative equilibrium % Time Slide 87 Two definitions of dynamic equilibrium 2. Qualitative or persistence equilibrium BOUNDED VARIATION % Time Slide 88 Minimum dynamic area An area large enough to contain all the patch types and to result in the sustained dynamics of the ecosystem Slide 89 Minimum dynamic area An area large enough to contain all the patch types and to result in the sustained dynamics of the ecosystem Rules of Thumb Maximum disturbance