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ECOLOGICAL ASPECTS OF CONSERVATION
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ECOLOGICAL ASPECTS OF CONSERVATION
OBJECTIVES OF CONSERVATION BIOLOGY 1. Maintain genetic diversity for a) adapting to changing environments b) Representative samples of species and habitats for future generations 2. Preserve rare species 3. Understanding how natural ecosystems work 4. Act as baselines for assessing human disturbance
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ECOLOGICAL ASPECTS OF CONSERVATION
USING PROTECTED AREAS FOR CONSERVATION e.g. national parks Protecting: 1.High diversity areas – richness hotspots - centre of endemism 2. Endangered and threatened species 3. Fragile habitats – e.g. wetlands 4. Species that cannot live with humans – large predators
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ECOLOGICAL ASPECTS OF CONSERVATION
DESIGN OF A PROTECTED AREA FOR CONSERVATION 1. AREA – single large v several small 2. SOURCES and SINKS- positive rate of increase 3. SHAPE – ratio of edge to centre 4. CORRIDORS – fragmentation and the need for connections 5. BIOLOGICAL ASPECTS
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West Australia forest fragmentation
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BIOLOGICAL ASPECTS Food webs and Co-evolved links
Protection of a species requires maintaining the essential components of the food web -Kaka parrots in New Zealand forests Some species have evolved tight coevolved linkages to other species -Hibiscadelphus plants and honeyeaters in Hawaii -Calvaria trees and Dodo on Mauritius
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FOOD WEB – needs to be intact Kaka New Zealand beech forests
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Mountain beech Habitat of special adaptations for kaka
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Scale insect tubes that exude honey dew
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Kaka holes to reach beetle larvae
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Hybiscadelphus - Hawaii - extinct. - Depended on pollinators
CO-EVOLEVED LINKS - need to conserve both elements Hybiscadelphus - Hawaii - extinct. - Depended on pollinators
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Moho species - Hawaian honeycreeper pollinators all extinct
Pratt et al. 1991
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Calvaria major - Mauritius almost extinct
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Dodo - a flightless pigeon of Mauritius extinct
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Keystone species Keystones determine the rest of the Species community
e.g. Wildebeest in the Serengeti e.g Pisaster in the intertidal
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Habitat patchiness Habitats can be patchy – sources and sinks
not always obvious e.g. Heliconius butterflies in Amazon e.g. Kokako in NZ forests Habitats can be reduced to the extent that species go extinct – major reason for species loss. Largely due to agriculture
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Heliconius butterflies in South America – showing the patchwork distribution
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New Zealand Beech forests Patches of suitable habitat
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Kokako Presumed extinct, rediscovered in 1960s in patches of forest
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Ecosystem Disturbance
Communities are both shaped by disturbance e.g fire, flooding, herbivory ( e.g. Beavers) and changed by disturbance e.g wahine storm e.g earthquakes in Chobe Park, Botswana
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Ecosystem Disturbance
Communities are shaped by disturbance e.g fire in Canal Flats, nr Kimberley,BC, Rocky Mountain trench -seen from fire scars e.g. Protection from disturbance changes the Plant community – Milroy Rangelands, East Kootenay
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FIRE SCARS, LARCH – show a frequency of 1 per 40 years
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Grassland with grazing
Disturbance Same area in 1995 after 44 years protection from grazing. Too little disturbance results in change to a Ponderosa Pine community
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Ecosystem Disturbance
Communities are changed by disturbance – too much or too great a disturbance e.g wahine storm e.g earthquakes in Chobe Park, Botswana e.g. exotic predators – cause extinction
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Black swans on Lake Ellesmere, New Zealand
CHANGE IN STATE: Black swans on Lake Ellesmere, New Zealand
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Exotic predators Excessive predation occurs when endemic species have evolved without predators – they have no antipredator behaviour. Extinction follows
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Exotic predators – feral cats and stoats
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Black Stilt New Zealand Endangered by exotic predators such as ferrets, stoats
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Pebble beaches in New Zealand rivers – nest sites of Black stilt
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Rifleman wren Endemic species in New Zealand - endangered by stoats that can climb trees
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New Zealand moss forest - Habitat of kiwi
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Kiwi and egg
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Laughing owl - extinct
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Huia - extinct
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Pleistocene tundra mammoth - grazer
Ten thousand years ago our ecosystems were dominated by megaherbivores – exterminated by newly arrived humans
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change in nutrient dynamics of New Zealand forests
MOA – all species extinct by the 1700s due to a change in nutrient dynamics of New Zealand forests
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Moa species – extinct in New Zealand
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Disturbance and scale effects
Spatial scale Protection is not extensive enough to cover the scale of disturbance e.g. Giant Pandas and their bamboo foods
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Current Range for Giant Pandas
RANGE OF GIANT PANDA
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GIANT PANDA food supply collapses over large areas when Bamboo flowers synchronously at periods of several decades conservation requires reserves of bamboo over very large spatial scales
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Reintroductions Breeding programs Reintroduced animals in wild
Chatham Island Black Robin Captive breeding Takehe, Kakapo, Arabian oryx
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Islet off Chatham Islands New Zealand
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Old Blue The last remaining Female Black Robin
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Crossfostering Placing Black Robin eggs in Tomtit nest
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Crossfostering – Tomtit (left) feeding young Black robin (right)
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Takehe Rediscovered in 1949 after presumed extinct Breeding in captivity and released
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Kakepo Flightless parrot now being bred on offshore islands free of rats, cats and stoats
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Oryx – bred in zoos and reintroduced to Arabia
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RESTORATION The active management of habitats to return them to a previous state for conservation reasons
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1. RESTORATION Managing Garry Oak Ecosystems on Vancouver island
Managing Okanagan Grassland Ecosystems for Burrowing Owls by creating nesting holes originally made by badgers
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2. RESTORATION – using history to judge whether change is
A natural succession. Wildhorse River, Rockies of S.E. BC shows change from conifer forest to aspen stands Such change would be natural 2.
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3. RESTORATION – creating artificial habitats. Islands of
Wetland in the Campbell River estuary, BC 3.
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