LECTURE 23 CONSERVATION BIOLOGY 2 + RESTORATION ECOLOGY MAJOR CONCEPTS 1. Conservation Biology relates to land use and landscape structure. 2. Habitat destruction and fragmentation cause 67% of all cases of recent extinctions. 3. Hotspots for immediate conservation: high # species + high # endemic species 4. Plan areas/habitats to preserve: A) if large uniform area available: SLOSS: single large better than equal size of separate small 5. Plan areas/habitats to preserve: B) if diversity of area available: Several small diverse better than one large uniform. 6. Plan for migration via corridors and ‘stepping stones’ in both types. 7. Consider community structure (e.g. top-down control, cascade effects, keystone sp.). 8. Large nearby subpopulations may rescue a small population from going extinct. 9. Chance events may cause small populations to go extinct. Conservation Biology: Relate to Land Use and Landscape Structure Conservation Planning: Approach 1: Single Species Focus on rare, endangered species. Focus on dynamics and genetics of small populations Conservation Planning: Approach 2 Preserve areas/habitats Hotspots: high # species + high # endemic species (only found there) Deterministic causes of extinctions: the ‘evil quartet’ Habitat destruction and fragmentation (67% of all cases) Problems associated with fragmentation Introduction of exotic species Eliminate native species and alter ecosystem function Islands, disturbed habitats, and those near people especially vulnerable Overexploitation Often changes species composition Chains of linked extinctions Principles of design planning 1: (for large expanse of uniform habitat) Larger area better than small Why larger better? SLOSS: single large better than equal size of separate small Plan for migration via corridors and ‘stepping stones’ Advantages? Disadvantages? Circular (> interior/edge ratio) better than rectangular Principles of design planning 2: (for creating out of diverse area) Several small diverse better than one large uniform Plan for migration via corridors and ‘stepping stones’ Consider community structure Top-down control of trophic abundances Cascade effects: indirect effects extended through multiple levels Can have chain of extinctions if highly dependent Keystone organisms must be preserved Non-redundant species, key species that maintain stability/diversity Population level…. Small populations: greater risk of extinction due to Stochastic events Subpopulations more isolated Subpopulations with more synchronized fluctuations Deterministic models Based on large size; no variation in average birth and death rates Stochastic (random) models Randomness affects populations Catastrophe Temporal variation in environment Stochastic (random sampling) processes Chance events may cause small populations to go extinct Probability of extinction increases over time decreases with larger initial population size Small populations can go extinct due to random fluctuations in population size. Rescue effect: immigration from large subpopulation keeps a declining population from inbreeding and going extinct (source provides emigrants to sink) Need corridors to connect source and sink Summary 6-16 RESTORATION ECOLOGY MAJOR CONCEPTS 1. Restoration ecology is an applied discipline dependent on firm understanding of basic ecological processes. 2. It also is tightly embedded in a social context. 3. All subdisciplines of ecology from population through ecosytem contain principles relevant for enhancing success of restoration projects. Restoration Ecology: use research to understand ecological processes in highly disturbed ecosystems apply understanding to: enhance their complexity and long-term persistence increase diversity reintroduce ecosystem function biomass (energy flow; productivity) + nutrient content (cycles) reestablish characteristic species, community structure + function Relevant disciplines: Population, Community, Landscape, Ecosystem Ecology Intertwined dimensions: Society, Politics, Economics, Policy Ecological Theory Relevant to Restoration: Population level – Vulnerability of small populations Stochastic extinction Genetic variation/inbreeding depression Minimum population viable size Metapopulation dynamics Use of locally adapted genotypes Community Ecology Species-Area relationship Island Biogeography Theory Fragmentation and patch size requirements of different groups of organims Disturbance dimensions Intermediate disturbance hypothesis Succession Species-Species Interactions as they influence community development Facilitation Inhibition Tolerance Causes of succession: site availability species availability species performance Contributing processes: disturbance dispersal ecophysiology propagules life history resources stress competition allelopathy herbivory Community Assembly Model of restoration as managing succession: design a disturbance, control colonization, control species performance Community Structure and Stability Top-down control of trophic abundances Trophic cascade effects: indirect effects extended through multiple levels Chain of extinctions if highly dependent Keystone organisms must be preserved Non-redundant species, key species that maintain stability/diversity Increase in structural diversity of vegetation increases species diversity. Full restoration of native plant communities sustains diverse animal populations. High diversity of plant species year-round food supply for greatest diversity of animals Landscape Ecology Take into account: Patch size + longevity, disturbance frequency, habitat requirements Spatial concepts; Large areas sustain more species than small areas. Many small patches in an area will help sustain regional diversity. Patch shape is as important as size. Fragmentation of habitats, communities, and ecosystems reduces diversity. Isolated patches sustain fewer species than closely associated patches. Species diversity in patches connected by corridors > than for disconnected patches. A heterogeneous mosaic of community types sustains more species & is more likely to support rare species than a single homogeneous community. Ecotones between natural communities support a variety of species from both communities and species specific to the ecotone. Ecosystem Ecology Must have strong productivity to ensure sufficient energy flow to higher trophic levels. Must ensure functional nutrient cycles Must consider sources and sinks for energy flow and nutirent cycles