Impacts of the Nitrogen Cascade on Ecosystems Presentation to - - PowerPoint PPT Presentation

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Impacts of the Nitrogen Cascade on Ecosystems Presentation to - - PowerPoint PPT Presentation

Impacts of the Nitrogen Cascade on Ecosystems Presentation to NYSERDA October 8, 2003 William Moomaw Fletcher School, Tufts University Reactive N and Unreactive N 2 Unreactive N is N 2 (78% of earths atmosphere) Reactive N (Nr)


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SLIDE 1

Impacts of the Nitrogen Cascade on Ecosystems

Presentation to NYSERDA

October 8, 2003 William Moomaw Fletcher School, Tufts University

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SLIDE 2

Reactive N

and Unreactive N2

‹ Unreactive N is N2 (78% of earth’s atmosphere) ‹ Reactive N (Nr) includes all biologically, chemically and physically

active N compounds in the atmosphere and biosphere of the Earth

‹ N controls productivity of most natural ecosystems ‹ N2 is converted to Nr by biological nitrogen fixation (BNF) ‹ N2 is converted to Nr by humans fossil fuel combustion, the Haber

Bosch process, and cultivation-induced BNF.

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SLIDE 3

Reactive N

and Unreactive N2

‹ Unreactive N is N2 (78% of earth’s atmosphere) ‹ Reactive N (Nr) includes all biologically, chemically and physically

active N compounds in the atmosphere and biosphere of the Earth

‹ N controls productivity of most natural ecosystems ‹ N2 is converted to Nr by biological nitrogen fixation (BNF) ‹ N2 is converted to Nr by humans fossil fuel combustion, the Haber

Bosch process, and cultivation-induced BNF.

‹ Bottom Lines

– Humans create more Nr than do natural terrestrial processes. – Nr is accumulating in the environment. – Nr accumulation contributes to most environment issues of the day. – Challenge is to reduce anthropogenic Nr creation.

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SLIDE 4

Reactive N

and Unreactive N2

‹ Unreactive N is N2 (78% of earth’s atmosphere) ‹ Reactive N (Nr) includes all biologically, chemically and physically

active N compounds in the atmosphere and biosphere of the Earth

‹ N controls productivity of most natural ecosystems ‹ N2 is converted to Nr by biological nitrogen fixation (BNF) ‹ N2 is converted to Nr by humans fossil fuel combustion, the Haber

Bosch process, and cultivation-induced BNF.

‹ Bottom Lines

– Humans create more Nr than do natural terrestrial processes. – Nr is accumulating in the environment. – Nr accumulation contributes to most environment issues of the day. – Challenge is to reduce anthropogenic Nr creation.

‹ But, this is complicated by fact that Nr creation sustains most of

the world’s food needs.

– The real challenge is how can we provide food (and energy) while also reducing Nr creation rates and arresting the nitrogen cascade?

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SLIDE 5

zyxwvutsrqponmlkjihgfedcbaWUTSRPONMLKJIHGFEDCBA Reactive Nitrogen Cuts Across Multiple Global Issues and Environmental Agreements

‹ Regional air quality (LRTAP) ‹ Climate change (UNFCCC & Kyoto Prot.) ‹ Ozone Depletion (Montreal Protocol) ‹ Biodiversity loss (CBD) ‹ Transboundary water quality (Non-navigational

Uses of International Water Courses

‹ Estuary damage (Regional Seas) ‹ Fisheries loss (Law of the Sea?)

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SLIDE 6

Need for an Integrated Analytical Policy Approach to Reactive Nitrogen

‹First explain history of human alteration of

nitrogen cycle

‹Identify the reasons why reactive nitrogen

cascades through so many segments of the global ecosystem

‹Describe the International Nitrogen

Initiative

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SLIDE 7

The History of Nitrogen

  • -Global Population & Discovery of N--

1750 1800 1850 1900 1950 2000 2050

Humans, millions

1,000 2,000 3,000 4,000 5,000 6,000 7,000

N-Discovered

Galloway JN and Cowling EB. 2002; Galloway et al., 2002a

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SLIDE 8

The History of Nitrogen

  • -Major N processes--

1750 1800 1850 1900 1950 2000 2050

Humans, millions

1,000 2,000 3,000 4,000 5,000 6,000 7,000

N-Discovered N-Nutrient BNF

Galloway JN and Cowling EB. 2002; Galloway et al., 2002a

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SLIDE 9

Nr Creation by Cultivation

  • -So that’s why we plant soybeans--

1750 1800 1850 1900 1950 2000 2050

Humans, millions Legumes/Rice, Tg N

1,000 2,000 3,000 4,000 5,000 6,000 7,000 50 100 150 200

N-Discovered N-Nutrient BNF

Galloway JN and Cowling EB. 2002; Galloway et al., 2002a

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SLIDE 10

zyxwvutsrqponmlkjihgfedcbaWVUTSRQPONMLIHGFEDCBA

Nr Creation by Fossil Fuel Combustion

  • -Nr produced by accident--

1,000 2,000 3,000 4,000 5,000 6,000 7,000 50 100 150 200

N-Discovered N-Nutrient BNF N2 + O2

  • -> 2NO

1750 1800 1850 1900 1950 2000 2050

Humans, millions Legumes/Rice, Tg N NOx emissions, Tg N

Galloway JN and Cowling EB. 2002; Galloway et al., 2002a

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SLIDE 11

zyxwvutsrqponmlkjihgfedcbaWVUTSRQPONMLIHGFEDCBA

The History of Nitrogen

  • -A British chemists view--

1,000 2,000 3,000 4,000 5,000 6,000 7,000 50 100 150 200

N-Discovered N-Nutrient BNF N2 + O2

  • -> 2NO

World is running out of N*

1750 1800 1850 1900 1950 2000 2050

Humans, millions Legumes/Rice, Tg N NOx emissions, Tg N

*1898, Sir William Crookes, president of the British Association for the Advancement of Science

Galloway JN and Cowling EB. 2002; Galloway et al., 2002a

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SLIDE 12

zyxwvutsrqponmlkjihgfedcbaWVUTSRQPONMLIHGFEDCBA

The History of Nitrogen

  • -German science at the forefront--

1,000 2,000 3,000 4,000 5,000 6,000 7,000 50 100 150 200

N-Discovered N-Nutrient BNF N2 + O2

  • -> 2NO

N2 + 3H2

  • -> 2NH3

1750 1800 1850 1900 1950 2000 2050

Humans, millions Legumes/Rice, Tg N NOx emissions, Tg N

Galloway JN and Cowling EB. 2002; Galloway et al., 2002a

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SLIDE 13

zyxwvutsrqponmlkjihgfedcbaWVUTSRQPONMLIHGFEDCBA

Nr Creation by Haber-Bosch

  • -most used for fertilizer--

1,000 2,000 3,000 4,000 5,000 6,000 7,000 50 100 150 200

N-Discovered N-Nutrient BNF N2 + O2

  • -> 2NO

N2 + 3H2

  • -> 2NH3

H-B

1750 1800 1850 1900 1950 2000 2050

Humans, millions Haber Bosch Legumes/Rice, Tg N NOx emissions, Tg N

Galloway JN and Cowling EB. 2002; Galloway et al., 2002a

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SLIDE 14

Nr Creation by Food and Energy Production

1750 1800 1850 1900 1950 2000 2050

Humans, millions Energy Production Food Production

1,000 2,000 3,000 4,000 5,000 6,000 7,000 50 100 150 200

N-Nutrient N-Discovered BNF H-B

Galloway JN and Cowling EB. 2002; Galloway et al., 2002a

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SLIDE 15

Nr Creation by Food and Energy Production

1,000 2,000 3,000 4,000 5,000 6,000 7,000 1750 1800 1850 1900 1950 2000 2050 50 100 150 200

Humans, millions Total N Fixed, Tg

Galloway JN and Cowling EB. 2002; Galloway et al., 2002a

N-Nutrient N-Discovered BNF Nr, natural

{

H-B

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SLIDE 16

Grain Production Meat Production Energy Production

N Drivers in 1860

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SLIDE 17

NO NOy

y

N N2

2

NH NHx

x

5 5

The Global Nitrogen Budget in 1860 and mid-1990s, TgN/yr 1860

120 120

Galloway et al., 2002b

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SLIDE 18

0.3 0.3 15 15

NO NOy

y

N N2

2

NH NHx

x

5 5

The Global Nitrogen Budget in 1860 and mid-1990s, TgN/yr 1860

120 120

Galloway et al., 2002b

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SLIDE 19

6 6 7 7 8 8 0.3 0.3 6 6 9 9 11 11 8 8 15 15 27 27

NO NOy

y

N N2

2

NH NHx

x

5 5 6 6

The Global Nitrogen Budget in 1860 and mid-1990s, TgN/yr 1860

120 120

Galloway et al., 2002b

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SLIDE 20

Grain Production Meat Production Energy Production

Nitrogen Drivers in 1860 & 1995

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SLIDE 21

NO NOy

y

N N2

2

NH NHx

x

5 5

The Global Nitrogen Budget in 1860 and mid-1990s, TgN/yr 1860 mid-1990s

110 110

Galloway et al., 2002b

6 6 7 7 8 8 0.3 0.3 6 6 9 9 11 11 8 8 15 15 27 27

NO NOy

y

N N2

2

NH NHx

x

5 5 6 6 120 120

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SLIDE 22

NO NOy

y

N N2

2

NH NHx

x

25 25 5 5 33 33 100 100

N2 + 3H2 2NH3

The Global Nitrogen Budget in 1860 and mid-1990s, TgN/yr 1860 mid-1990s

110 110

Galloway et al., 2002b

6 6 7 7 8 8 0.3 0.3 6 6 9 9 11 11 8 8 15 15 27 27

NO NOy

y

N N2

2

NH NHx

x

5 5 6 6 120 120

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SLIDE 23

6 6 7 7 8 8 0.3 0.3 6 6 9 9 11 11 8 8 15 15 27 27

NO NOy

y

N N2

2

NH NHx

x

5 5 6 6

NO NOy

y

N N2

2

NH NHx

x

21 21 25 25 16 16 25 25 5 5 33 33 23 23 26 26 6 6 39 39 48 48 18 18 100 100

N2 + 3H2 2NH3

The Global Nitrogen Budget in 1860 and mid-1990s, TgN/yr 1860 mid-1990s

110 110 120 120

Galloway et al., 2002b

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SLIDE 24

zyxwvutsrqponmlkjihgfedcbaWVUTSRQPONMLIHGFEDCBA

zyxwvutsrqponmlkjihgfedcbaWUTSRPONMLKJIHGFEDCBA

Nr Riverine Fluxes 1860 (left) and 1990 (right)

TgN/yr

8.3 21.8

  • > all regions increase riverine fluxes
  • > Asia becomes dominant

2 2.1 5 9.1 4.4 7.8 7.4 9.7 7.7 8.5

Galloway et al, 2002b; Boyer et al., in preparation

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SLIDE 25

zyxwvutsrqponmlkjihgfedcbaWUTSRPONMLKJIHGFEDCBA

1860 1993

Nitrogen Deposition Past and Present

mg N/m2/yr

5000 2000 1000 750 500 250 100 50 25 5

Galloway and Cowling, 2002; Galloway et al., 2002b

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SLIDE 26

Mid-Course Summary

Summary

‹ Humans mobilize ~50%

more Nr than natural terrestrial ecosystems.

– Food production accounts for 75%

‹ Nr is widely dispersed

– Atmospheric Nr emissions have increased 3-fold since 1860; NH3 twice as important as NOx

‹ Nr is accumulating in

ecosystems and the atmosphere. Next Questions

‹ What are the consequences

  • f Nr accumulation?

‹ What is projected for future? ‹ How can science and policy

respond?

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SLIDE 27

Nr and Agricultural Ecosystems

‹ Haber-Bosch has facilitated

agricultural intensification

‹ 40% of world’s population is

alive because of it

‹ An additional 3 billion people

by 2050 will be sustained by it

‹ Most N that enters

agroecosystems is released to the environment.

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SLIDE 28

Nr and the Atmosphere

‹ NOx emissions contribute to

OH, which defines the

  • xidizing capacity of the

atmosphere

‹ NOx emissions are responsible

for tens of thousands of excess- deaths per year in the United States

‹ O3 and N2O contribute to

atmospheric warming

‹ N2O emissions contribute to

stratospheric O3 depletion

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SLIDE 29

Nr and Terrestrial Ecosystems

‹ N is the limiting nutrient in

most temperate and polar ecosystems

‹ Nr deposition increases and

then decreases forest and grassland productivity

‹ Nr additions probably decrease

biodiversity across the entire range of deposition

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SLIDE 30

Nr and Freshwater Ecosystems

‹ Surface water

acidification

– Tens of thousands of lakes and streams – Significant biodiversity losses – Negative feedbacks to forested ecosystems

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SLIDE 31

‹ ‹ Nr inputs intoco

coastalreg regionsresu result i in neut eutr ro

  • phi

phicat cati ion,

  • n,

bi bio

  • d

di iv ver ersi sit ty y lo losse sses, s,e em missio ission ns sof

  • fN

N2

2O

Oto to th the e at atm mo

  • s

spher phere e. . Mos Most tco coas ast ta al reg l regi ions

  • nsar

are imp e impacted. acted. Nr inputs into astal ions lt

‹ ‹

Nr and Coastal Ecosystems

‹ Riverine and atmospheric deposition

are significant Nr sources to coastal systems

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SLIDE 32

There are significant effects

  • f Nr accumulation within each

reservoir These effects are linked temporally and biogeochemically in the Nitrogen Cascade

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SLIDE 33

Atmosphere

Terrestrial Ecosystems Aquatic Ecosystems

Human Activities

The Nitrogen Cascade

Galloway et al., 2002a

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SLIDE 34

Atmosphere

Terrestrial Ecosystems Aquatic Ecosystems

Human Activities

Energy Production

Ozone Effects NOx

The Nitrogen Cascade

Galloway et al., 2002a

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SLIDE 35

Atmosphere

Terrestrial Ecosystems Aquatic Ecosystems

Human Activities

Energy Production

PM & Visibility Effects Ozone Effects NOx

The Nitrogen Cascade

Galloway et al., 2002a

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SLIDE 36

Atmosphere

Terrestrial Ecosystems Aquatic Ecosystems

Human Activities

Energy Production

PM & Visibility Effects Ozone Effects NOx

The Nitrogen Cascade

Forests & Grassland Soil

Galloway et al., 2002a

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SLIDE 37

zyxwvutsrqponmlkjihgfedcbaWUTSRPONMLKJIHGFEDCBA

Atmosphere

Terrestrial Ecosystems Aquatic Ecosystems

Human Activities

Groundwater Effects Surface water Effects

Energy Production

PM & Visibility Effects Ozone Effects NOx

The Nitrogen Cascade

Forests & Grassland Soil

Galloway et al., 2002a

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SLIDE 38

zyxwvutsrqponmlkjihgfedcbaWUTSRPONMLKJIHGFEDCBA

Atmosphere

Terrestrial Ecosystems Aquatic Ecosystems

Human Activities

Groundwater Effects Surface water Effects Coastal Effects

Energy Production

PM & Visibility Effects Ozone Effects NOx

The Nitrogen Cascade

Forests & Grassland Soil

Galloway et al., 2002a

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SLIDE 39

zyxwvutsrqponmlkjihgfedcbaWUTSRPONMLKJIHGFEDCBA

Atmosphere

Terrestrial Ecosystems Aquatic Ecosystems

Human Activities

Groundwater Effects Surface water Effects Coastal Effects

Energy Production

PM & Visibility Effects Ozone Effects NOx

The Nitrogen Cascade

Forests & Grassland Soil Ocean Effects

Galloway et al., 2002a

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SLIDE 40

zyxwvutsrqponmlkjihgfedcbaWUTSRPONMLKJIHGFEDCBA

Atmosphere

Terrestrial Ecosystems Aquatic Ecosystems

Human Activities

Groundwater Effects Surface water Effects Coastal Effects

Energy Production

PM & Visibility Effects Ozone Effects Agroecosystem Effects NHx

Food Production

NOx Crop Animal

People (Food; Fiber)

Soil

The Nitrogen Cascade

Norg Forests & Grassland Soil Ocean Effects

Galloway et al., 2002a

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SLIDE 41

zyxwvutsrqponmlkjihgfedcbaWUTSRPONMLKJIHGFEDCBA

Atmosphere

Terrestrial Ecosystems Aquatic Ecosystems

Human Activities

Groundwater Effects Surface water Effects Coastal Effects

Energy Production

PM & Visibility Effects Ozone Effects Agroecosystem Effects NHx

Food Production

NOx NOx Crop Animal

People (Food; Fiber)

Soil NO3

The Nitrogen Cascade

NH3 Norg Forests & Grassland Soil Ocean Effects

Galloway et al., 2002a

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SLIDE 42

Atmosphere

Terrestrial Ecosystems Aquatic Ecosystems

Human Activities

Groundwater Effects Surface water Effects

Energy Production

PM & Visibility Effects Ozone Effects Agroecosystem Effects NHx

Food Production

NOx NOx Crop Animal

People (Food; Fiber)

Soil NO3

The Nitrogen Cascade

NH3

  • -Indicates denitrification potential

Norg Forests & Grassland Soil Coastal Effects Ocean Effects

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SLIDE 43

Atmosphere

Terrestrial Ecosystems Aquatic Ecosystems

Human Activities

Groundwater Effects Surface water Effects Coastal Effects Stratospheric Effects

Energy Production

PM & Visibility Effects Ozone Effects Agroecosystem Effects NHx

Food Production

NOx NOx Crop Animal

People (Food; Fiber)

Soil NO3

The Nitrogen Cascade

NH3

  • -Indicates denitrification potential

Norg Forests & Grassland Soil Ocean Effects

N2O

GH Effects

N2O

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SLIDE 44

THE BIG PICTURE

‹ Food and energy production results in creation of ~160 Tg

N of new Nr, most of which is released to the environment.

‹ We know where some of it goes and we generally know

what it does when it gets there.

‹ We do not know:

– How much is stored in ecosystems vs. how much is denitrified to N2. – How to feed and fuel the global population without releasing excess N to environmental reservoirs.

‹ We know another thing--Nr creation will increase in

the future, as will Nr accumulation and an intensification of the N Cascade--but how much?

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SLIDE 45

Nr Creation Rates by Food and Energy Production in 2050

12 10 8 6 4 2

today 2050

1000 1100 1200 1300 1400 1500 1600 1700 1800 1900 2000 2100

Year

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SLIDE 46

Nr Creation Rates 1995

TgN/yr

Nr creation by food and energy production

60 5 32 10 32 2

after Galloway and Cowling, 2002

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SLIDE 47

Nr Creation Rates 1995 (left) and 2050 (right)

TgN/yr

60 92 5 13 32 27 10 17 32 42 2 3

2050 rates scaled by:

  • > population increase relative to 1995

after Galloway and Cowling, 2002

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SLIDE 48

Nr Creation Rates 1995 (left) and 2050 (right)

TgN/yr

60 568 5 190 32 67 10 87 32 42 2 5

2050 rates scaled by:

  • > population increase relative to 1995
  • > N. Amer. percapita Nr creation in 1995

after Galloway and Cowling, 2002

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SLIDE 49

10,000 8,000 6,000 4,000 2,000 1750

The Future of Nitrogen

  • -Nr Creation, Total--

1000 800 600 400 200 1800 1850 1900 1950 2000 2050 2100

?

Humans, millions Total Nr Fixed, Tg N

Possible trajectories of future Nr creation

after Galloway and Cowling, 2002

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SLIDE 50

The Issues of Nitrogen

♦ We need food; we need energy.

♦ How do we get it without Nr accumulation?

♦ Create less Nr by:

♦ increasing N use efficiency in food production, ♦ Reducing NOx emissions from fossil fuel combustion.

‹ Convert Nr to N2 before environmental release.

While both are possible, an integrated N management strategy is required.

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SLIDE 51

The Challenge to all Parties

Maximize food and energy production while maintaining environmental and human health!

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SLIDE 52

The Clean Air Act

‹ The Clean Air Act favors existing plants in three

ways:

– In attainment areas, new plants must meet NSPS and PSD; existing plants face no comparable requirements. – In non-attainment areas, new plants must meet NSPS and NSR; existing plants face much weaker standards. – The SO2 trading system gives free allowances to existing plants, based on 1980s fuel consumption;

  • thers must buy allowances.

‹ Half of coal plant capacity was built before 1975,

a quarter before 1965. More than half of all sulfur emissions nationwide, and a large part of nitrogen emissions, come from pre-1975 coal plants.

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SLIDE 53

1996 NOx Emissions by Vintage

0.0 0.2 0.4 0.6 0.8 1.0 1.2 1.4 1.6 1.8 2.0 1996 NOX Emission Rate (lb/MMBtu)

  • --- Pre-1975 Average
  • --- Post-1975 Average
  • --- New plant standard

1930 1940 1950 1960 1970 1980 1990 2000 Unit Vintage

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SLIDE 54

Cost of new gas plant Coal plant operating costs

Cost ($/MWh)

Coal vs. gas: current

100

conditions

90 80 70 60 50 40 30 20 10 10 20 30 40 50 60 70 80 90 100 Capacity Factor (%)

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SLIDE 55

Cost of new gas plant Coal plant operating costs

Cost ($/MWh)

Coal vs. gas: Comparable

100

emissions

90 80 70 60 50 40 30 20 10 10 20 30 40 50 60 70 80 90 100 Capacity Factor (%)

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SLIDE 56

Cost of new gas plant Coal plant operating costs

Cost ($/MWh)

Comparable emissions plus CO2

100

tax

90 80 70 60 50 40 30 20 10 10 20 30 40 50 60 70 80 90 100 Capacity Factor (%)

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SLIDE 57

The economics of coal plants

‹ No one wants to build a new coal plant -- and no

  • ne wants to close an old one.

‹ The key cost comparison: how do operating costs

  • f existing coal plants compare to capital plus
  • perating costs of a new gas combined cycle

plant?

‹ Three versions of this comparison:

– Current conditions: > 99% of coal is cheaper than gas. – Comparable emissions scenario (meeting new plant standards industry-wide): 94% of coal remains cheaper than gas. – Comparable emissions plus $10/ton CO2 tax: 64% of coal remains competitive.

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SLIDE 58
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SLIDE 59
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SLIDE 60

N Fertilizer Produced N Fertilizer Consumed N in Crop N Harvested N in Food N Consumed

  • 6
  • 47
  • 12

100 14 47 94 26 31

  • 5
  • 16

The Fate of Haber-Bosch Nitrogen

14% of the N produced in the Haber-Bosch process enters the human mouth……….if you are a vegetarian.

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SLIDE 61

N Fertilizer Produced N Fertilizer Applied N in Crop N In Feed N in Store N Consumed

  • 6
  • 47
  • 3

100 4 47 94 7 31

  • 24
  • 16

The Fate of Haber-Bosch Nitrogen

4% of the N produced in the Haber-Bosch process and used for animal production enters the human mouth.