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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 54

    Ecosystems

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    Overview: Ecosystems, Energy, and Matter

    An ecosystem consists of all the organismsliving in a community

    As well as all the abiotic factors with whichthey interact

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    Ecosystems can range from a microcosm, such

    as an aquarium To a large area such as a lake or forest

    Figure 54.1

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    Regardless of an ecosystems size

    Its dynamics involve two main processes:energy flow and chemical cycling

    Energy flows through ecosystems

    While matter cycles within them

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    Concept 54.1: Ecosystem ecology emphasizes

    energy flow and chemical cycling Ecosystem ecologists view ecosystems

    As transformers of energy and processors of matter

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    Ecosystems and Physical Laws

    The laws of physics and chemistry apply to

    ecosystems Particularly in regard to the flow of energy

    Energy is conserved

    But degraded to heat during ecosystemprocesses

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    Trophic Relationships

    Energy and nutrients pass from primary

    producers (autotrophs) To primary consumers (herbivores) and then to

    secondary consumers (carnivores)

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    Energy flows through an ecosystem

    Entering as light and exiting as heat

    Figure 54.2

    Microorganismsand other

    detritivores

    Detritus

    Primary producers

    Primary consumers

    Secondaryconsumers

    Tertiaryconsumers

    Heat

    Sun

    Key

    Chemical cycling

    Energy flow

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    Nutrients cycle within an ecosystem

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    Decomposition

    Decomposition

    Connects all trophic levels

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    Detritivores, mainly bacteria and fungi, recycleessential chemical elements

    By decomposing organic material and returningelements to inorganic reservoirs

    Figure 54.3

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    Concept 54.2: Physical and chemical factors

    limit primary production in ecosystems Primary production in an ecosystem

    Is the amount of light energy converted tochemical energy by autotrophs during a giventime period

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    Ecosystem Energy Budgets

    The extent of photosynthetic production

    Sets the spending limit for the energy budgetof the entire ecosystem

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    The Global Energy Budget

    The amount of solar radiation reaching the

    surface of the Earth Limits the photosynthetic output of ecosystems

    Only a small fraction of solar energy

    Actually strikes photosynthetic organisms

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    Gross and Net Primary Production

    Total primary production in an ecosystem

    Is known as that ecosystems gross primaryproduction (GPP)

    Not all of this production

    Is stored as organic material in the growingplants

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    Net primary production (NPP)

    Is equal to GPP minus the energy used by theprimary producers for respiration

    Only NPP

    Is available to consumers

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    Different ecosystems vary considerably in their netprimary production

    And in their contribution to the total NPP on Earth

    Lake and stream

    Open oceanContinental shelf

    Estuary

    Algal beds and reefsUpwelling zones

    Extreme desert, rock, sand, ice

    Desert and semidesert scrubTropical rain forest

    SavannaCultivated land

    Boreal forest (taiga)

    Temperate grassland

    Tundra

    Tropical seasonal forest

    Temperate deciduous forestTemperate evergreen forest

    Swamp and marsh

    Woodland and shrubland

    0 10 20 30 40 50 60 0 500 1,000 1,500 2,000 2,500 0 5 10 15 20 25

    Percentage of Earths netprimary production

    Key

    Marine

    Freshwater (on continents)

    Terrestrial

    5.20.30.10.1

    4.7

    3.53.32.92.7

    2.41.8

    1.71.6

    1.5

    1.31.00.4

    0.4

    125360

    1,500

    2,500

    5003.090

    2,200

    900600

    800600

    700

    1401,600

    1,2001,300

    2,000250

    5.61.2

    0.90.1

    0.040.9

    22

    7.99.1

    9.6

    5.4

    3.50.6

    7.1

    4.93.8

    2.30.3

    65.0 24.4

    Figure 54.4ac

    Percentage of Earthssurface area

    (a) Average net primaryproduction (g/m 2 /yr)

    (b) (c)

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    Overall, terrestrial ecosystems

    Contribute about two-thirds of global NPP andmarine ecosystems about one-third

    Figure 54.5

    180 120 W 60 W 0 60 E 120 E 180

    North Pole

    60 N

    30 N

    Equator

    30S

    60 S

    South Pole

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    Primary Production in Marine and FreshwaterEcosystems

    In marine and freshwater ecosystems Both light and nutrients are important in

    controlling primary production

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    Light Limitation

    The depth of light penetration

    Affects primary production throughout thephotic zone of an ocean or lake

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    Nutrient Limitation

    More than light, nutrients limit primary

    production Both in different geographic regions of the

    ocean and in lakes

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    A limiting nutrient is the element that must be

    added In order for production to increase in a

    particular area

    Nitrogen and phosphorous

    Are typically the nutrients that most often limitmarine production

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    Nutrient enrichment experiments

    Confirmed that nitrogen was limiting phytoplanktongrowth in an area of the ocean

    EXPERIMENT Pollution from duck farms concentrated near Moriches Bay adds both nitrogen and phosphorus to the coastal water off Long Island. Researchers cultured the phytoplankton Nannochloris

    atomus with water collected from several bays.

    Figure 54.6

    Coast of Long Island, New York. The numbers on the map indicatethe data collection stations.

    L o n g I s

    l a n d

    G r e a t S o u

    t h B a y

    Shinnecock

    BayMoriches Bay

    Atlantic Ocean

    30 21

    19

    151154

    2

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    Figure 54.6

    (a) Phytoplankton biomass and phosphorus concentration (b) Phytoplankton response to nutrient enrichment

    GreatSouth Bay

    MorichesBay

    ShinnecockBay

    Startingalgal

    density

    2 4 5 11 30 15 19 21

    30

    24

    18

    12

    6

    0

    Unenriched control

    Ammonium enrichedPhosphate enriched

    Station number

    P h y t o p

    l a n

    k t o n

    ( m i l l i o n s o f c e

    l l s p e r m

    L )

    876543210

    2 4 5 11 30 15 19 21

    87

    654

    3210

    I n o r g a n

    i c p

    h o s p

    h o r u s

    ( g a

    t o m s

    / L )

    P h y t o p

    l a n

    k t o n

    ( m i l l i o n s o

    f c e

    l l s / m L )

    Station number

    CONCLUSION Since adding phosphorus, which was already in rich supply, had no effect onNannochloris growth, whereas adding nitrogen increased algal density dramatically, researchersconcluded that nitrogen was the nutrient limiting phytoplankton growth in this ecosystem.

    Phytoplankton

    Inorganicphosphorus

    RESULTS Phytoplankton abundance parallels the abundance of phosphorus in the water (a). Nitrogen,however, is immediately taken up by algae, and no free nitrogen is measured in the coastal waters. Theaddition of ammonium (NH 4

    + ) caused heavy phytoplankton growth in bay water, but the addition of

    phosphate (PO 43 +

    ) did not induce algal growth (b).

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    Experiments in another ocean region

    Showed that iron limited primary production

    Table 54.1

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    The addition of large amounts of nutrients tolakes

    Has a wide range of ecological impacts

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    In some areas, sewage runoff

    Has caused eutrophication of lakes, which canlead to the eventual loss of most fish species fromthe lakes

    Figure 54.7

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    Primary Production in Terrestrial and WetlandEcosystems

    In terrestrial and wetland ecosystems climaticfactors

    Such as temperature and moisture, affect

    primary production on a large geographic scale

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    The contrast between wet and dry climates

    Can be represented by a measure calledactual evapotranspiration

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    Actual evapotranspiration

    Is the amount of water annually transpired by plantsand evaporated from a landscape

    Is related to net primary production

    Figure 54.8Actual evapotranspiration (mm H 2O/yr)

    Tropical forest

    Temperate forest

    Mountain coniferous forest

    Temperate grassland

    Arctic tundra

    Desertshrubland

    N e

    t p r i m a r y p r o

    d u c t

    i o n

    ( g / m 2 / y r )

    1,000

    2,000

    3,000

    0500 1,000 1,5000

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    On a more local scale

    A soil nutrient is often the limiting factor in primaryproduction

    Figure 54.9

    EXPERIMENT Over the summer of 1980, researchers addedphosphorus to some experimental plots in the salt marsh, nitrogento other plots, and both phosphorus and nitrogen to others. Someplots were left unfertilized as controls.

    RESULTS

    Experimental plots receiving justphosphorus (P) do not outproducethe unfertilized control plots.

    CONCLUSION

    L i v e ,

    a b o v e - g r o u n

    d b i o m a s s

    ( g d r y w

    t / m

    2 )

    Adding nitrogen (N)boosts net primaryproduction.

    300

    250

    200

    150

    100

    50

    0June July August 1980

    N + P

    N only

    Control

    P only

    These nutrient enrichment experimentsconfirmed that nitrogen was the nutrient limiting plant growth inthis salt marsh.

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    Concept 54.3: Energy transfer between trophiclevels is usually less than 20% efficient

    The secondary production of an ecosystem

    Is the amount of chemical energy inconsumers food that is converted to their ownnew biomass during a given period of time

    d i ffi i

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    Production Efficiency

    When a caterpillar feeds on a plant leaf

    Only about one-sixth of the energy in the leaf is used for secondary production

    Figure 54.10

    Plant materialeaten by caterpillar

    Cellular respiration

    Growth (new biomass)

    Feces 100 J

    33 J

    200 J

    67 J

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    The production efficiency of an organism

    Is the fraction of energy stored in food that isnot used for respiration

    T hi Effi i d E l i l P id

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    Trophic Efficiency and Ecological Pyramids

    Trophic efficiency

    Is the percentage of production transferredfrom one trophic level to the next

    Usually ranges from 5% to 20%

    P id f P d i

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    Pyramids of Production

    This loss of energy with each transfer in a food chain

    Can be represented by a pyramid of net production

    Figure 54.11

    Tertiaryconsumers

    Secondaryconsumers

    Primaryconsumers

    Primaryproducers

    1,000,000 J of sunlight

    10 J

    100 J

    1,000 J

    10,000 J

    P id f Bi

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    Pyramids of Biomass

    One important ecological consequence of lowtrophic efficiencies

    Can be represented in a biomass pyramid

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    Most biomass pyramids

    Show a sharp decrease at successively higher trophic levels

    Figure 54.12a

    (a) Most biomass pyramids show a sharp decrease in biomass atsuccessively higher trophic levels, as illustrated by data froma bog at Silver Springs, Florida.

    Trophic level Dry weight

    (g/m2

    )

    Primary producers

    Tertiary consumers

    Secondary consumers

    Primary consumers

    1.5

    11

    37809

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    Certain aquatic ecosystems

    Have inverted biomass pyramids

    Figire 54.12b

    Trophic level

    Primary producers (phytoplankton)

    Primary consumers (zooplankton)

    (b) In some aquatic ecosystems, such as the English Channel,a small standing crop of primary producers (phytoplankton)supports a larger standing crop of primary consumers (zooplankton).

    Dry weight(g/m 2)

    21

    4

    P id f N b

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    Pyramids of Numbers

    A pyramid of numbers

    Represents the number of individualorganisms in each trophic level

    Figure 54.13

    Trophic level Number of individual organisms

    Primary producers

    Tertiary consumers

    Secondary consumers

    Primary consumers

    3

    354,904

    708,624

    5,842,424

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    The dynamics of energy flow throughecosystems

    Have important implications for the humanpopulation

    Eating meat

    Is a relatively inefficient way of tappingphotosynthetic production

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    Worldwide agriculture could successfully feedmany more people

    If humans all fed more efficiently, eating onlyplant material

    Figure 54.14

    Trophic level

    Secondaryconsumers

    Primaryconsumers

    Primaryproducers

    The Green World Hypothesis

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    The Green World Hypothesis

    According to the green world hypothesis

    Terrestrial herbivores consume relatively littleplant biomass because they are held in checkby a variety of factors

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    Most terrestrial ecosystems

    Have large standing crops despite the largenumbers of herbivores

    Figure 54.15

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    The green world hypothesis proposes severalfactors that keep herbivores in check

    Plants have defenses against herbivores

    Nutrients, not energy supply, usually limit

    herbivores Abiotic factors limit herbivores

    Intraspecific competition can limit herbivore

    numbers Interspecific interactions check herbivore

    densities

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    Concept 54.4: Biological and geochemicalprocesses move nutrients between organic andinorganic parts of the ecosystem

    Life on Earth

    Depends on the recycling of essential chemicalelements

    Nutrient circuits that cycle matter through anecosystem

    Involve both biotic and abiotic components andare often called biogeochemical cycles

    A General Model of Chemical Cycling

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    A General Model of Chemical Cycling

    Gaseous forms of carbon, oxygen, sulfur, andnitrogen

    Occur in the atmosphere and cycle globally

    Less mobile elements, including phosphorous,potassium, and calcium

    Cycle on a more local level

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    A general model of nutrient cycling

    Includes the main reservoirs of elements andthe processes that transfer elements betweenreservoirs

    Figure 54.16

    Organicmaterialsavailable

    as nutrients

    Livingorganisms,detritus

    Organic

    materialsunavailableas nutrients

    Coal, oil,peat

    Inorganicmaterialsavailable

    as nutrients

    Inorganicmaterials

    unavailableas nutrients

    Atmosphere,soil, water

    Mineralsin rocksFormation of

    sedimentary rock

    Weathering,erosion

    Respiration,decomposition,excretion

    Burningof fossil fuels

    Fossilization

    Reservoir a Reservoir b

    Reservoir c Reservoir d

    Assimilation,photosynthesis

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    All elements

    Cycle between organic and inorganicreservoirs

    Biogeochemical Cycles

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    Biogeochemical Cycles

    The water cycle and the carbon cycle

    Figure 54.17

    Transportover land

    Solar energy

    Net movement of water vapor by wind

    Precipitationover ocean

    Evaporationfrom ocean

    Evapotranspirationfrom land

    Precipitationover land

    Percolationthroughsoil

    Runoff andgroundwater

    CO 2 in atmosphere

    Photosynthesis

    Cellular respiration

    Burning of fossil fuelsand wood Higher-level

    consumersPrimaryconsumers

    DetritusCarbon compoundsin water

    Decomposition

    THE WATER CYCLE THE CARBON CYCLE

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    Water moves in a global cycle

    Driven by solar energy

    The carbon cycle

    Reflects the reciprocal processes of photosynthesis and cellular respiration

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    The nitrogen cycle and the phosphorous cycle

    Figure 54.17

    N2 in atmosphere

    Denitrifyingbacteria

    Nitrifyingbacteria

    Nitrifyingbacteria

    Nitrification

    Nitrogen-fixingsoil bacteria

    Nitrogen-fixingbacteria in rootnodules of legumes

    Decomposers

    Ammonification

    Assimilation

    NH3 NH4+

    NO 3

    NO 2

    Rain

    Plants

    Consumption

    Decomposition

    Geologicuplift

    Weatheringof rocks

    Runoff

    SedimentationPlant uptakeof PO 43

    Soil

    Leaching

    THE NITROGEN CYCLE THE PHOSPHORUS CYCLE

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    Most of the nitrogen cycling in naturalecosystems

    Involves local cycles between organisms andsoil or water

    The phosphorus cycle

    Is relatively localized

    Decomposition and Nutrient Cycling Rates

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    Decomposition and Nutrient Cycling Rates

    Decomposers (detritivores) play a key role

    In the general pattern of chemical cycling

    Figure 54.18

    Consumers

    Producers

    Nutrientsavailable

    to producers

    Abioticreservoir

    Geologicprocesses

    Decomposers

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    The rates at which nutrients cycle in differentecosystems

    Are extremely variable, mostly as a result of differences in rates of decomposition

    Vegetation and Nutrient Cycling: The Hubbard

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    Vegetation and Nutrient Cycling: The HubbardBrook Experimental Forest

    Nutrient cycling Is strongly regulated by vegetation

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    Long-term ecological research projects

    Monitor ecosystem dynamics over relativelylong periods of time

    The Hubbard Brook Experimental Forest

    Has been used to study nutrient cycling in aforest ecosystem since 1963

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    The research team constructed a dam on thesite

    To monitor water and mineral loss

    Figure 54.19a

    (a) Concrete dams and weirs built across streams atthe bottom of watersheds enabled researchers tomonitor the outflow of water and nutrients from theecosystem.

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    In one experiment, the trees in one valley werecut down

    And the valley was sprayed with herbicides

    Figure 54.19b(b) One watershed was clear cut to study the effects of the loss

    of vegetation on drainage and nutrient cycling.

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    Net losses of water and minerals were studied

    And found to be greater than in an undisturbed area

    These results showed how human activity

    Can affect ecosystems

    Figure 54.19c(c) The concentration of nitrate in runoff from the deforested watershed was 60 times

    greater than in a control (unlogged) watershed.

    N i t r a

    t e

    c o n c e n

    t r a

    t i o n

    i n r u n o f f

    ( m g

    / L )

    Deforested

    Control

    Completion of tree cutting

    1965 1966 1967 1968

    80.060.040.020.0

    4.03.02.01.0

    0

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    Concept 54.5: The human population isdisrupting chemical cycles throughout thebiosphere

    As the human population has grown in size

    Our activities have disrupted the trophicstructure, energy flow, and chemical cycling of ecosystems in most parts of the world

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    Agriculture and Nitrogen Cycling

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    g g y g

    Agriculture constantly removes nutrients fromecosystems

    That would ordinarily be cycled back into the soil

    Figure 54.20

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    Nitrogen is the main nutrient lost throughagriculture

    Thus, agriculture has a great impact on thenitrogen cycle

    Industrially produced fertilizer is typically usedto replace lost nitrogen

    But the effects on an ecosystem can be

    harmful

    Contamination of Aquatic Ecosystems

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    q y

    The critical load for a nutrient

    Is the amount of that nutrient that can beabsorbed by plants in an ecosystem withoutdamaging it

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    Sewage runoff contaminates freshwater ecosystems

    Causing cultural eutrophication, excessivealgal growth, which can cause significant harmto these ecosystems

    Acid Precipitation

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    Combustion of fossil fuels

    Is the main cause of acid precipitation

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    North American and European ecosystemsdownwind from industrial regions

    Have been damaged by rain and snow containingnitric and sulfuric acid

    Figure 54.21

    4.6

    4.64.3

    4.14.3

    4.6

    4.64.3

    Europe

    North America

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    By the year 2000

    The entire contiguous United States was affected byacid precipitation

    Figure 54.22

    Field pH 5.3

    5.25.35.15.25.05.14.95.04.84.94.74.84.64.74.54.64.44.54.34.4< 4.3

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    Environmental regulations and new industrialtechnologies

    Have allowed many developed countries toreduce sulfur dioxide emissions in the past 30years

    Toxins in the Environment

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    Humans release an immense variety of toxicchemicals

    Including thousands of synthetics previouslyunknown to nature

    One of the reasons such toxins are so harmful Is that they become more concentrated in

    successive trophic levels of a food web

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    In biological magnification

    Toxins concentrate at higher trophic levelsbecause at these levels biomass tends to be lower

    Figure 54.23

    C o n c e n

    t r a

    t i o n o

    f P C B s

    Herringgull eggs124 ppm

    Zooplankton0.123 ppm

    Phytoplankton0.025 ppm

    Lake trout4.83 ppm

    Smelt1.04 ppm

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    In some cases, harmful substances

    Persist for long periods of time in anecosystem and continue to cause harm

    Atmospheric Carbon Dioxide

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    One pressing problem caused by humanactivities

    Is the rising level of atmospheric carbondioxide

    Rising Atmospheric CO 2

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    Due to the increased burning of fossil fuels andother human activities

    The concentration of atmospheric CO 2 has beensteadily increasing

    Figure 54.24

    C O

    2 c o n c e n

    t r a

    t i o n

    ( p p m

    )

    390

    380

    370

    360

    350

    340

    330

    320

    310

    3001960 1965 1970 1975 1980 1985 1990 1995 2000 2005

    1.05

    0.90

    0.75

    0.60

    0.45

    0.30

    0.15

    0

    0.15

    0.30

    0.45

    T e m p e r a

    t u r e v a r i a

    t i o n

    ( C )

    Temperature

    CO 2

    Year

    How Elevated CO 2 Affects Forest Ecology: The

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    FACTS-I Experiment

    The FACTS-I experiment is testing how elevated CO 2

    Influences tree growth, carbon concentration in soils,and other factors over a ten-year period

    Figure 54.25

    The Greenhouse Effect and Global Warming

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    The greenhouse effect is caused byatmospheric CO 2

    But is necessary to keep the surface of theEarth at a habitable temperature

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    Increased levels of atmospheric CO 2 aremagnifying the greenhouse effect

    Which could cause global warming andsignificant climatic change

    Depletion of Atmospheric Ozone

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    Life on Earth is protected from the damagingeffects of UV radiation

    By a protective layer or ozone moleculespresent in the atmosphere

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    Satellite studies of the atmosphere

    Suggest that the ozone layer has been graduallythinning since 1975

    Figure 54.26

    O z o n e

    l a y e r

    t h i c k n e s s

    ( D o b s o n u n

    i t s )

    Year (Average for the month of October)

    350

    300

    250

    200

    150

    100

    50

    01955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005

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    Copyright 2005 Pearson Education, Inc. publishing as Benjamin Cummings

    The destruction of atmospheric ozone

    Probably results from chlorine-releasingpollutants produced by human activity

    Figure 54.27

    1

    2

    3

    Chlorine from CFCs interacts with ozone (O 3),forming chlorine monoxide (ClO) andoxygen (O 2).

    Two ClO moleculesreact, formingchlorine peroxide (Cl 2O 2).

    Sunlight causesCl2O 2 to breakdown into O 2 and freechlorine atoms.The chlorineatoms can beginthe cycle again.

    Sunlight

    Chlorine O 3

    O 2

    ClO

    ClO

    Cl2O 2

    O 2

    Chlorine atoms

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    Scientists first described an ozone hole

    Over Antarctica in 1985; it has increased insize as ozone depletion has increased

    (a) October 1979 (b) October 2000