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    Copyright 2005 Pearson Education, Inc. publishing as Benjamin Cummings

    PowerPoint Lectures for

    Biology, Seventh Edition

    Neil Campbell and Jane Reece

    Lectures by Chris Romero

    Chapter 55

    Conservation Biology and

    Restoration Ecology

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    Overview: The Biodiversity Crisis

    Conservation biology integrates the following fieldsto conserve biological diversity at all levels

    Ecology

    Evolutionary biology

    Physiology

    Molecular biology

    Genetics

    Behavioral ecology

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    Restoration ecology applies ecological

    principles In an effort to return degraded ecosystems to

    conditions as similar as possible to their

    natural state

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    Tropical forests

    Contain some of the greatest concentrations ofspecies

    Are being destroyed at an alarming rate

    Figure 55.1

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    Throughout the biosphere, human activities

    Are altering ecosystem processes on which weand other species depend

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    Concept 55.1: Human activities threaten

    Earths biodiversity Rates of species extinction

    Are difficult to determine under natural

    conditions

    The current rate of species extinction is high

    And is largely a result of ecosystemdegradation by humans

    Humans are threatening Earths biodiversity

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    The Three Levels of Biodiversity

    Biodiversity has three main components

    Genetic diversity

    Species diversity

    Ecosystem diversity

    Genetic diversity in a vole population

    Species diversity in a coastal redwood ecosystem

    Community and ecosystem diversity

    across the landscape of an entire region

    Figure 55.2

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    Genetic Diversity

    Genetic diversity comprises

    The genetic variation within a population

    The genetic variation between populations

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    Species Diversity

    Species diversity

    Is the variety of species in an ecosystem orthroughout the biosphere

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    An endangered species

    Is one that is in danger of becoming extinctthroughout its range

    Threatened species

    Are those that are considered likely to become

    endangered in the foreseeable future

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    Conservation biologists are concerned about

    species loss Because of a number of alarming statistics

    regarding extinction and biodiversity

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    Harvard biologist E. O. Wilson has identified

    the Hundred Heartbeat Club Species that number fewer than 100

    individuals and are only that many heartbeats

    from extinction(a) Philippine eagle

    (b) Chinese riverdolphin

    (c) Javan

    rhinocerosFigure 55.3ac

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    Ecosystem Diversity

    Ecosystem diversity

    Identifies the variety of ecosystems in thebiosphere

    Is being affected by human activity

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    Biodiversity and Human Welfare

    Human biophilia

    Allows us to recognize the value of biodiversityfor its own sake

    Species diversity

    Brings humans many practical benefits

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    Benefits of Species and Genetic Diversity

    Many pharmaceuticals

    Contain substances originally derived fromplants

    Figure 55.4

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    The loss of species

    Also means the loss of genes and geneticdiversity

    The enormous genetic diversity of organisms

    on Earth

    Has the potential for great human benefit

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    Ecosystem Services

    Ecosystem services encompass all the

    processes Through which natural ecosystems and the

    species they contain help sustain human life

    on Earth

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    Ecosystem services include

    Purification of air and water

    Detoxification and decomposition of wastes

    Cycling of nutrients

    Moderation of weather extremes

    And many others

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    Four Major Threats to Biodiversity

    Most species loss can be traced to four major

    threats Habitat destruction

    Introduced species

    Overexploitation

    Disruption of interaction networks

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    Habitat Destruction

    Human alteration of habitat

    Is the single greatest threat to biodiversitythroughout the biosphere

    Massive destruction of habitat

    Has been brought about by many types of

    human activity

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    Many natural landscapes have been broken up

    Fragmenting habitat into small patches

    Figure 55.5

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    In almost all cases

    Habitat fragmentation and destruction leads toloss of biodiversity

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    Introduced species that gain a foothold in a

    new habitat Usually disrupt their adopted community

    (a) Brown tree

    snake, intro-

    duced to Guam

    in cargo

    (b) Introduced kudzu thriving in South Carolina

    Figure 55.6a, b

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    Overexploitation

    Overexploitation refers generally to the human

    harvesting of wild plants or animals

    At rates exceeding the ability of populations of

    those species to rebound

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    The fishing industry

    Has caused significant reduction in populationsof certain game fish

    Figure 55.7

    Di i f I i N k

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    Disruption of Interaction Networks

    The extermination of keystone species by

    humans

    Can lead to major changes in the structure of

    communities

    Figure 55.8

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    Concept 55.2: Population conservation focuses

    on population size, genetic diversity, and

    critical habitat

    Biologists focusing on conservation at the

    population and species levels Follow two main approaches

    S ll P l ti A h

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    Small-Population Approach

    Conservation biologists who adopt the small-

    population approach

    Study the processes that can cause very small

    populations finally to become extinct

    Th E i i V

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    The Extinction Vortex

    A small population is prone to positive-

    feedback loops

    That draw the population down an extinction

    vortexSmall

    population

    InbreedingGenetic

    drift

    Lower

    reproduction

    Higher

    mortality Loss of

    genetic

    variabilityReduction in

    individual

    fitness and

    population

    adaptability

    Smaller

    population

    Figure 55.9

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    The key factor driving the extinction vortex

    Is the loss of the genetic variation necessary toenable evolutionary responses to

    environmental change

    C St d Th G t P i i Chi k d th

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    Case Study: The Greater Prairie Chicken and theExtinction Vortex

    Populations of the greater prairie chicken Were fragmented by agriculture and later

    found to exhibit decreased fertility

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    As a test of the extinction vortex hypothesis

    Scientists imported genetic variation bytransplanting birds from larger populations

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    The declining population rebounded

    Confirming that it had been on its way down anextinction vortex

    EXPRIMENTResearchers observed that the population

    collapse of the greater prairie chicken was mirrored in a reduction in

    fertility, as measured by the hatching rate of eggs. Comparison of

    DNA samples from the Jasper County, Illinois, population with DNAfrom feathers in museum specimens showed that genetic variation

    had declined in the study population. In 1992, researchers began

    experimental translocations of prairie chickens from Minnesota,

    Kansas, and Nebraska in an attempt to increase genetic variation.

    RESULTSAfter translocation (blue arrow), the viability of

    eggs rapidly improved, and the population rebounded.

    CONCLUSIONThe researchers concluded that lack of genetic

    variation had started the Jasper County population of prairie

    chickens down the extinction vortex.

    Numberofmalebirds

    (a) Population dynamics

    (b) Hatching rate

    200

    150

    100

    50

    0

    1970 1975 1980 1985 1990 1995 2000

    Year

    Eggshatched(%)

    100

    90

    80

    70

    60

    50

    40

    30

    1970-74 1975-79 1980-84 1985-89 1990 1993-97

    Years

    Figure 55.10

    Mi i Vi bl P l ti Si

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    Minimum Viable Population Size

    The minimum viable population (MVP)

    Is the minimum population size at which aspecies is able to sustain its numbers and

    survive

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    A population viability analysis (PVA)

    Predicts a populations chances for survivalover a particular time

    Factors in the MVP of a population

    Effective Population Size

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    Effective Population Size

    A meaningful estimate of MVP

    Requires a researcher to determine theeffective population size, which is based on the

    breeding size of a population

    Case Study: Analysis of Grizzly Bear Populations

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    Case Study: Analysis of Grizzly Bear Populations

    One of the first population viability analyses

    Was conducted as part of a long-term study ofgrizzly bears in Yellowstone National Park

    Figure 55.11

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    This study has shown that the grizzly bear

    population

    Has grown substantially in the past 20 years

    Num

    berofindividuals

    150

    100

    50

    01973 1982 1991 2000

    Females with cubs

    Cubs

    Year

    Figure 55.12

    Declining Population Approach

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    Declining-Population Approach

    The declining-population approach

    Focuses on threatened and endangeredpopulations that show a downward trend,

    regardless of population size

    Emphasizes the environmental factors thatcaused a population to decline in the first place

    Steps for Analysis and Intervention

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    Steps for Analysis and Intervention

    The declining-population approach

    Requires that population declines be evaluatedon a case-by-case basis

    Involves a step-by-step proactive conservation

    strategy

    Case Study: Decline of the Red Cockaded

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    Case Study: Decline of the Red-CockadedWoodpecker

    Red-cockaded woodpeckers Require specific habitat factors for survival

    Had been forced into decline by habitat

    destruction

    (a) A red-cockaded woodpecker perches at the

    entrance to its nest site in a longleaf pine.

    (b) Forest that can

    sustain red-cockaded

    woodpeckers has

    low undergrowth.

    (c) Forest that cannot sustain red-cockaded

    woodpeckers has high, dense undergrowth that

    impacts the woodpeckers access to feeding grounds.Figure 55.13ac

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    In a study where breeding cavities were

    constructed

    New breeding groups formed only in these

    sites

    On the basis of this experiment

    A combination of habitat maintenance and

    excavation of new breeding cavities has

    enabled a once-endangered species torebound

    Weighing Conflicting Demands

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    Weighing Conflicting Demands

    Conserving species often requires resolving

    conflicts

    Between the habitat needs of endangered

    species and human demands

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    Concept 55.3: Landscape and regional

    conservation aim to sustain entire biotas

    In recent years, conservation biology

    Has attempted to sustain the biodiversity of

    entire communities, ecosystems, andlandscapes

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    One goal of landscape ecology, of which

    ecosystem management is part

    Is to understand past, present, and future

    patterns of landscape use and to make

    biodiversity conservation part of land-use

    planning

    Landscape Structure and Biodiversity

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    Landscape Structure and Biodiversity

    The structure of a landscape

    Can strongly influence biodiversity

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    As habitat fragmentation increases

    And edges become more extensive,biodiversity tends to decrease

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    Research on fragmented forests has led to the

    discovery of two groups of species

    Those that live in forest edge habitats and

    those that live in the forest interior

    Figure 55.15

    Corridors That Connect Habitat Fragments

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    Corridors That Connect Habitat Fragments

    A movement corridor

    Is a narrow strip of quality habitat connectingotherwise isolated patches

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    In areas of heavy human use

    Artificial corridors are sometimes constructed

    Figure 55.16

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    Movement corridors

    Promote dispersal and help sustainpopulations

    Establishing Protected Areas

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    Establishing Protected Areas

    Conservation biologists are applying their

    understanding of ecological dynamics

    In establishing protected areas to slow the loss

    of biodiversity

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    Much of the focus on establishing protected

    areas

    Has been on hot spots of biological diversity

    Finding Biodiversity Hot Spots

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    i di g iodive sity ot Spots

    A biodiversity hot spot is a relatively small area

    With an exceptional concentration of endemicspecies and a large number of endangered

    and threatened species

    Terrestrial

    biodiversity

    hot spots

    Equator

    Figure 55.17

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    Biodiversity hot spots are obviously good

    choices for nature reserves

    But identifying them is not always easy

    Philosophy of Nature Reserves

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    p y f

    Nature reserves are biodiversity islands

    In a sea of habitat degraded to varyingdegrees by human activity

    One argument for extensive reserves

    Is that large, far-ranging animals with low-

    density populations require extensive habitats

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    In some cases

    The size of reserves is smaller than the actualarea needed to sustain a population

    Biotic boundary for

    short-term survival;

    MVP is 50 individuals.

    Biotic boundary for

    long-term survival;

    MVP is 500 individuals.

    Grand Teton

    National Park

    Wyoming

    Idaho

    43

    42

    41

    40

    0 50 100

    Kilometers

    SnakeR

    .

    Yellowstone

    NationalPark

    Shoshone R.

    Montana

    Wyoming

    Montana

    Idaho

    MadisonR.

    GallatinR.

    YellowstoneR.

    Figure 55.18

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    Zoned reserves

    Are often established as conservation areas

    (a) Boundaries of the zoned reserves are indicated by black outlines.

    (b) Local schoolchildren marvel at the diversity of life in one of

    Costa Ricas reserves.

    Nicaragua

    Costa

    Rica

    Panam

    aNational park land

    Buffer zone

    PACIFIC OCEAN

    CARIBBEAN SEA

    Figure 55.19a, b

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    Some zoned reserves in the Fiji islands are

    closed to fishing

    Which actually helps to improve fishing

    success in nearby areas

    Figure 55.20

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    Concept 55.4: Restoration ecology attempts to

    restore degraded ecosystems to a more natural

    state

    The larger the area disturbed

    The longer the time that is required forrecovery

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    Whether a disturbance is natural or caused by

    humans

    Seems to make little difference in this size-

    time relationship

    Recoverytime(years)

    (logscale)

    104

    1,000

    100

    10

    1

    103 102 101 1 10 100 1,000 104

    Natural disasters

    Human-caused disasters

    Natural OR human-

    caused disastersMeteor

    strike

    Groundwater

    exploitationIndustrial

    pollution

    Urbanization Salination

    Modern

    agriculture FloodVolcanic

    eruptionAcidrain

    Forest

    fire

    Nuclear

    bomb

    Tsunami

    Oilspill

    Slash& burn

    Land-slide

    Tree

    fallLightning

    strike

    Spatial scale (km2)(log scale)

    Figure 55.21

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    One of the basic assumptions of restoration

    ecology

    Is that most environmental damage is

    reversible

    Two key strategies in restoration ecology

    Are bioremediation and augmentation of

    ecosystem processes

    Bioremediation

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    Bioremediation

    Is the use of living organisms to detoxifyecosystems

    Biological Augmentation

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    Biological augmentation

    Uses organisms to add essential materials to adegraded ecosystem

    Exploring Restoration

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    The newness and complexity of restoration

    ecology

    Require scientists to consider alternative

    solutions and adjust approaches based on

    experience

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    Exploring restoration worldwide

    Truckee River, Nevada. Kissimmee River, Florida.

    Equator

    Figure 55.22

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    Tropical dry forest, Costa Rica. Succulent Karoo, South Africa.

    Rhine River, Europe. Coastal Japan.Figure 55.22

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    Concept 55.5: Sustainable development seeks

    to improve the human condition while

    conserving biodiversity

    Facing increasing loss and fragmentation of

    habitats

    How can we best manage Earths resources?

    Sustainable Biosphere Initiative

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    The goal of this initiative is to define and

    acquire the basic ecological information

    necessary

    For the intelligent and responsible

    development, management, and conservation

    of Earths resources

    Case Study: Sustainable Development in Costa

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    Rica

    Costa Ricas success in conserving tropical

    biodiversity

    Has involved partnerships between the

    government, other organizations, and private

    citizens

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    Human living conditions in Costa Rica

    Have improved along with ecologicalconservation

    Infantm

    ortality(per1,000livebirths)

    200

    150

    100

    50

    0

    1900 1950 2000

    80

    70

    60

    50

    40

    30

    Year

    Life expectancy

    Infant mortality

    Lifeexpectancy(years)

    Figure 55.23

    Biophilia and the Future of the Biosphere

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    Our modern lives

    Are very different from those of early humanswho hunted and gathered and painted on cave

    walls

    (a) Detail of animals in a Paleolithic mural, Lascaux, FranceFigure 55.24a

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    But our behavior

    Reflects remnants of our ancestral attachmentto nature and the diversity of life, the concept

    of biophilia

    (b) Biologist Carlos Rivera Gonzales examining a tiny tree frog in

    PeruFigure 55.24b

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    Our innate sense of connection to nature

    May eventually motivate a realignment of ourenvironmental priorities