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Chapter 55 Conservation Biology and Restoration Ecology

Chapter 55 Conservation Biology and Restoration Ecology

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Page 1: Chapter 55 Conservation Biology and Restoration Ecology

Chapter 55Chapter 55

Conservation Biology and Restoration Ecology

Page 2: Chapter 55 Conservation Biology and Restoration Ecology

The Biodiversity Crisis• Conservation biology integrates the following fields

to conserve biological diversity at all levels

– Ecology

– Evolutionary biology

– Physiology

– Molecular biology

– Genetics

– Behavioral ecology

Page 3: Chapter 55 Conservation Biology and Restoration Ecology

• Restoration ecology applies ecological principles

– in an effort to return degraded ecosystems to conditions as similar as possible to their natural state

Page 4: Chapter 55 Conservation Biology and Restoration Ecology

• Tropical forests

– contain some of the greatest concentrations of species

– are being destroyed at an alarming rate

Figure 55.1

Page 5: Chapter 55 Conservation Biology and Restoration Ecology

• Throughout the biosphere, human activities

– are altering ecosystem processes on which we and other species depend

Page 6: Chapter 55 Conservation Biology and Restoration Ecology

• Concept 55.1: Human activities threaten Earth’s biodiversity

• Rates of species extinction

– are difficult to determine under natural conditions because of immigration/emigration.

• The current rate of species extinction is high

– and is largely a result of ecosystem degradation by humans

• Humans are threatening Earth’s biodiversity Due to human activity.

Page 7: Chapter 55 Conservation Biology and Restoration Ecology

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 diversityacross the landscape of an entire regionFigure 55.2

Page 8: Chapter 55 Conservation Biology and Restoration Ecology

Genetic Diversity

• Genetic diversity comprises

– the genetic variation within a population

– the genetic variation between populations

Genetics create a variation of species in a population. This may help you adapt to certain conditions. Disease resistance is also due to genetic variation.

Page 9: Chapter 55 Conservation Biology and Restoration Ecology

Species Diversity

• Species diversity

– is the variety of species in an ecosystem or throughout the biosphere

Page 10: Chapter 55 Conservation Biology and Restoration Ecology

• An endangered species

– is one that is in danger of becoming extinct throughout its range. This species is a species in danger of becoming extinct.

• Threatened species

– are those that are considered likely to become endangered in the foreseeable future

Page 11: Chapter 55 Conservation Biology and Restoration Ecology

• Conservation biologists are concerned about species loss

– because of a number of alarming statistics regarding extinction and biodiversity

Page 12: Chapter 55 Conservation Biology and Restoration Ecology

• 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 river dolphin

(c) Javan rhinocerosFigure 55.3a–c

12% of known 10,000 bird species & 24% of 5,000 known species of mammals are going extinct.

Page 13: Chapter 55 Conservation Biology and Restoration Ecology

Ecosystem Diversity

• Ecosystem diversity

– identifies the variety of ecosystems in the biosphere

– is being affected by human activity

Page 14: Chapter 55 Conservation Biology and Restoration Ecology

Biodiversity and Human Welfare

• Human biophilia

– allows us to recognize the value of biodiversity for its own sake

– This is our connection to nature. This is something within us that wants us to care and appreciate nature.

• Species diversity

– brings humans many practical benefits

Page 15: Chapter 55 Conservation Biology and Restoration Ecology

Benefits of Species and Genetic Diversity

• Many pharmaceuticals

– contain substances originally derived from plants. Rosey Periwinkle. This plant contains alkaloids.

Figure 55.4

now 25% of all tropical plants may be gone in next 30 years14% of vascular plants endangered

Page 16: Chapter 55 Conservation Biology and Restoration Ecology

• The loss of species

– also means the loss of genes and genetic diversity

• The enormous genetic diversity of organisms on Earth

– has the potential for great human benefit

Page 17: Chapter 55 Conservation Biology and Restoration Ecology

• Biodiversity is crucial natural resource, & species that are threatened could provide crops, fibers, & medicines for human use

• Of top 150 drugs in U.S., 118 based on natural sources: 74% on plants, 18% on fungi,5% on bacteria, 3% on one vertebrate (snake) venom

• 80% human population depends on traditional medicine; 85% of traditional medicine involves use of plant extracts

Page 18: Chapter 55 Conservation Biology and Restoration Ecology

• Human history have used 7,000 plant species for food

– but, 70,000 plants have edible parts

– currently 82 plant species contribute to 90% of food plants

– about 15 species provide bulk of calories consumed by humans

– Does this leave us vulnerable?

– What if there is a change in climate?

Page 19: Chapter 55 Conservation Biology and Restoration Ecology

• Last ice age (about 20,000 years ago) much of Europe and N. America covered by mile-thick ice

• Global climate has been relatively stable since agriculture was invented about 10,000 years ago

– life has played a role in buffering climate change

– How?

• ecosystems can help prevent overheating of Earth by removing greenhouse CO2 from atmosphere

Page 20: Chapter 55 Conservation Biology and Restoration Ecology

The decomposers• 130 billion tons of waste processed each year

• 30% from human activities

• Conversion of complex organic molecules to simple one

• includes industrial wastes like detergents, pesticides, oil, acids, paper

• Soils return simple inorganic molecules to plants as nutrients

• depends on activity of bacteria, fungi, algae, worms, crustaceans, insects

• bacteria fix nitrogen, fungi make nutrients available, worms are mechanical blenders

Page 21: Chapter 55 Conservation Biology and Restoration Ecology

• Under square metre of pasture soil is inhabited by 50,000 earthworms, 50,000 insects & mites, 12 million roundworms

• What about soil microorganisms?

– teaspoon of soil contains about 30,000 protozoa, 500,000 algae, 400,000 fungi, billions of individual bacteria

– They don’t need us but we need them

Page 22: Chapter 55 Conservation Biology and Restoration Ecology

Ecosystem Services

• Ecosystem services encompass all the processes

– through which natural ecosystems and the species they contain help sustain human life on Earth

Page 23: Chapter 55 Conservation Biology and Restoration Ecology

• Ecosystem services include

– Purification of air and water

– Detoxification and decomposition of wastes

– Cycling of nutrients

– Moderation of weather extremes

– And many others

Page 24: Chapter 55 Conservation Biology and Restoration Ecology

Four Major Threats to Biodiversity

• Most species loss can be traced to four major threats

– Habitat destruction

– Introduced species

– Overexploitation

– Disruption of “interaction networks”

Page 25: Chapter 55 Conservation Biology and Restoration Ecology

Habitat Destruction

• Human alteration of habitat

– is the single greatest threat to biodiversity throughout the biosphere

• Massive destruction of habitat

– has been brought about by many types of human activity. Like:

– Clear cutting

– Population

– Mining… agriculture

Page 26: Chapter 55 Conservation Biology and Restoration Ecology

• Many natural landscapes have been broken up

– fragmenting habitat into small patches… Could be natural or manmade.

Figure 55.5

Page 27: Chapter 55 Conservation Biology and Restoration Ecology

• In almost all cases

– habitat fragmentation and destruction leads to loss of biodiversity

Page 28: Chapter 55 Conservation Biology and Restoration Ecology

Introduced Species

• Introduced species

– are those that humans move from the species’ native locations to new geographic regions

Page 29: Chapter 55 Conservation Biology and Restoration Ecology

• 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 CarolinaFigure 55.6a, b

Page 30: Chapter 55 Conservation Biology and Restoration Ecology

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 (hunting animals, logging for furniture)

Page 31: Chapter 55 Conservation Biology and Restoration Ecology

• The fishing industry

– has caused significant reduction in populations of certain game fish, codfish.

Figure 55.7

Page 32: Chapter 55 Conservation Biology and Restoration Ecology

Disruption of Interaction Networks

• The extermination of keystone species by humans

– can lead to major changes in the structure of communities. This bat is a keystone species because its lack of presence has resulted in a decrease of plants, due to lack of pollination.

Figure 55.8

Page 33: Chapter 55 Conservation Biology and Restoration Ecology

• 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

Page 34: Chapter 55 Conservation Biology and Restoration Ecology

Small-Population Approach

• Conservation biologists who adopt the small-population approach

– study the processes that can cause very small populations finally to become extinct

Page 35: Chapter 55 Conservation Biology and Restoration Ecology

The Extinction Vortex

• A small population is prone to positive-feedback loops

– that draw the population down an extinction vortex

Smallpopulation

InbreedingGenetic

drift

Lower reproduction

Higher mortality

Loss ofgenetic

variabilityReduction inindividual

fitness andpopulationadaptability

Smallerpopulation

Figure 55.9

Page 36: Chapter 55 Conservation Biology and Restoration Ecology

• The key factor driving the extinction vortex

– is the loss of the genetic variation necessary to enable evolutionary responses to environmental change

Page 37: Chapter 55 Conservation Biology and Restoration Ecology

Case Study: The Greater Prairie Chicken and the Extinction Vortex

• Populations of the greater prairie chicken

– were fragmented by agriculture and later found to exhibit decreased fertility

Page 38: Chapter 55 Conservation Biology and Restoration Ecology

• As a test of the extinction vortex hypothesis

– scientists imported genetic variation by transplanting birds from larger populations

Page 39: Chapter 55 Conservation Biology and Restoration Ecology

• The declining population rebounded

– confirming that it had been on its way down an extinction vortex

EXPRIMENT Researchers 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 DNA from 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.

RESULTS After translocation (blue arrow), the viability of eggs rapidly improved, and the population rebounded.

CONCLUSION The researchers concluded that lack of genetic variation had started the Jasper County population of prairie chickens down the extinction vortex.

Num

ber

of m

ale

bird

s

(a) Population dynamics

(b) Hatching rate

200

150

100

50

01970 1975 1980 1985 1990 1995 2000

Year

Egg

s ha

tche

d (%

)

100

90

80

70

60

50

40

301970-74 1975-79 1980-84 1985-89 1990 1993-97

Years

Figure 55.10

Page 40: Chapter 55 Conservation Biology and Restoration Ecology

Minimum Viable Population Size

• The minimum viable population (MVP)

– is the minimum population size at which a species is able to sustain its numbers and survive

Page 41: Chapter 55 Conservation Biology and Restoration Ecology

• A population viability analysis (PVA)

– predicts a population’s chances for survival over a particular time

– factors in the MVP of a population

Page 42: Chapter 55 Conservation Biology and Restoration Ecology

Effective Population Size

• A meaningful estimate of MVP

– requires a researcher to determine the effective population size, which is based on the breeding size of a population

Page 43: Chapter 55 Conservation Biology and Restoration Ecology

Case Study: Analysis of Grizzly Bear Populations• One of the first population viability analyses

– was conducted as part of a long-term study of grizzly bears in Yellowstone National Park

Figure 55.11

Page 44: Chapter 55 Conservation Biology and Restoration Ecology

• This study has shown that the grizzly bear population

– has grown substantially in the past 20 yearsN

umb

er o

f in

div

idua

ls

150

100

50

01973 1982 1991 2000

Females with cubs

Cubs

YearFigure 55.12

Page 45: Chapter 55 Conservation Biology and Restoration Ecology

Declining-Population Approach

• The declining-population approach

– focuses on threatened and endangered populations that show a downward trend, regardless of population size

– emphasizes the environmental factors that caused a population to decline in the first place

Page 46: Chapter 55 Conservation Biology and Restoration Ecology

Steps for Analysis and Intervention

• The declining-population approach

– requires that population declines be evaluated on a case-by-case basis

– involves a step-by-step proactive conservation strategy

Page 47: Chapter 55 Conservation Biology and Restoration Ecology

Case Study: Decline of the Red-Cockaded Woodpecker

• 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 55.13a–c

Page 48: Chapter 55 Conservation Biology and Restoration Ecology

• 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 to rebound

Page 49: Chapter 55 Conservation Biology and Restoration Ecology

Weighing Conflicting Demands

• Conserving species often requires resolving conflicts

– between the habitat needs of endangered species and human demands

Page 50: Chapter 55 Conservation Biology and Restoration Ecology

• 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, and landscapes

Page 51: Chapter 55 Conservation Biology and Restoration Ecology

• 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

Page 52: Chapter 55 Conservation Biology and Restoration Ecology

Landscape Structure and Biodiversity

• The structure of a landscape

– can strongly influence biodiversity

Page 53: Chapter 55 Conservation Biology and Restoration Ecology

Fragmentation and Edges

• The boundaries, or edges, between ecosystems

– are defining features of landscapes

(a) Natural edges. Grasslands give way to forest ecosystems in Yellowstone National Park.

(b) Edges created by human activity. Pronounced edges (roads) surround clear-cuts in this photograph of a heavily logged rain forest in Malaysia.Figure 55.14a, b

Page 54: Chapter 55 Conservation Biology and Restoration Ecology

• As habitat fragmentation increases

– and edges become more extensive, biodiversity tends to decrease

Page 55: Chapter 55 Conservation Biology and Restoration Ecology

• 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

Page 56: Chapter 55 Conservation Biology and Restoration Ecology

Corridors That Connect Habitat Fragments

• A movement corridor

– is a narrow strip of quality habitat connecting otherwise isolated patches

Page 57: Chapter 55 Conservation Biology and Restoration Ecology

• In areas of heavy human use

– artificial corridors are sometimes constructed

Figure 55.16

Page 58: Chapter 55 Conservation Biology and Restoration Ecology

• Movement corridors

– promote dispersal and help sustain populations

Page 59: Chapter 55 Conservation Biology and Restoration Ecology

Establishing Protected Areas

• Conservation biologists are applying their understanding of ecological dynamics

– in establishing protected areas to slow the loss of biodiversity

Page 60: Chapter 55 Conservation Biology and Restoration Ecology

• Much of the focus on establishing protected areas

– has been on hot spots of biological diversity

Page 61: Chapter 55 Conservation Biology and Restoration Ecology

Finding Biodiversity Hot Spots

• A biodiversity hot spot is a relatively small area

– with an exceptional concentration of endemic species and a large number of endangered and threatened species

Terrestrial biodiversity hot spots

Equator

Figure 55.17

Page 62: Chapter 55 Conservation Biology and Restoration Ecology

• Biodiversity hot spots are obviously good choices for nature reserves

– but identifying them is not always easy

Page 63: Chapter 55 Conservation Biology and Restoration Ecology

Philosophy of Nature Reserves

• Nature reserves are biodiversity islands

– in a sea of habitat degraded to varying degrees by human activity

• One argument for extensive reserves

– is that large, far-ranging animals with low-density populations require extensive habitats

Page 64: Chapter 55 Conservation Biology and Restoration Ecology

• In some cases

– the size of reserves is smaller than the actual area needed to sustain a population

Biotic boundary forshort-term survival;MVP is 50 individuals.

Biotic boundary forlong-term survival;MVP is 500 individuals.

Grand TetonNational Park

Wyo

min

g

Idah

o

43

42

41

40

0 50 100

Kilometers

Snake R.

Yellowstone National Park

Shoshone R.

Montana

Wyoming

Montana

Idaho

Mad

ison

R.

Gal

latin

R.

Yellowstone R.

Figure 55.18

Page 65: Chapter 55 Conservation Biology and Restoration Ecology

Zoned Reserves

• The zoned reserve model recognizes that conservation efforts

– often involve working in landscapes that are largely human dominated

Page 66: Chapter 55 Conservation Biology and Restoration Ecology

• 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 Rica’s reserves.

Nicaragua

CostaRica

Pan

amaNational park land

Buffer zone

PACIFIC OCEAN

CARIBBEAN SEA

Figure 55.19a, b

Page 67: Chapter 55 Conservation Biology and Restoration Ecology

• Some zoned reserves in the Fiji islands are closed to fishing

– which actually helps to improve fishing success in nearby areas

Figure 55.20

Page 68: Chapter 55 Conservation Biology and Restoration Ecology

• 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 for recovery

Page 69: Chapter 55 Conservation Biology and Restoration Ecology

• Whether a disturbance is natural or caused by humans

– seems to make little difference in this size-time relationship

Rec

over

y tim

e (y

ears

)(lo

g sc

ale)

104

1,000

100

10

1

103 102 101 1 10 100 1,000 104

Natural disasters

Human-caused disasters

Natural OR human-caused disasters

Meteorstrike

Groundwaterexploitation

Industrialpollution

Urbanization Salination

Modernagriculture Flood

Volcaniceruption

Acidrain

Forestfire

Nuclearbomb

Tsunami

Oilspill

Slash& burn

Land-slide

Treefall

Lightningstrike

Spatial scale (km2)(log scale)

Figure 55.21

Page 70: Chapter 55 Conservation Biology and Restoration Ecology

• 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

Page 71: Chapter 55 Conservation Biology and Restoration Ecology

Bioremediation

• Bioremediation

– is the use of living organisms to detoxify ecosystems

Page 72: Chapter 55 Conservation Biology and Restoration Ecology

Biological Augmentation

• Biological augmentation

– uses organisms to add essential materials to a degraded ecosystem

Page 73: Chapter 55 Conservation Biology and Restoration Ecology

Exploring Restoration

• The newness and complexity of restoration ecology

– require scientists to consider alternative solutions and adjust approaches based on experience

Page 74: Chapter 55 Conservation Biology and Restoration Ecology

• 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 Earth’s resources?

Page 75: Chapter 55 Conservation Biology and Restoration Ecology

Sustainable Biosphere Initiative

• 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 Earth’s resources

Page 76: Chapter 55 Conservation Biology and Restoration Ecology

Case Study: Sustainable Development in Costa Rica

• Costa Rica’s success in conserving tropical biodiversity

– has involved partnerships between the government, other organizations, and private citizens

Page 77: Chapter 55 Conservation Biology and Restoration Ecology

• Human living conditions in Costa Rica

– have improved along with ecological conservationIn

fan

t m

ort

alit

y (p

er

1,0

00

live

birt

hs)

200

150

100

50

01900 1950 2000

80

70

60

50

40

30

Year

Life expectancyInfant mortality

Life

exp

ect

an

cy (

yea

rs)

Figure 55.23

Page 78: Chapter 55 Conservation Biology and Restoration Ecology

Biophilia and the Future of the Biosphere

• Our modern lives

– are very different from those of early humans who hunted and gathered and painted on cave walls

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

Page 79: Chapter 55 Conservation Biology and Restoration Ecology

• But our behavior

– reflects remnants of our ancestral attachment to nature and the diversity of life, the concept of biophilia

(b) Biologist Carlos Rivera Gonzales examining a tiny tree frog in PeruFigure 55.24b

Page 80: Chapter 55 Conservation Biology and Restoration Ecology

• Our innate sense of connection to nature

– may eventually motivate a realignment of our environmental priorities