THE 2011 NATIONAL ACID PRECIPITATION ASSESSMENT PROGRAM REPORT TO - - PowerPoint PPT Presentation

the 2011 national acid precipitation assessment program
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THE 2011 NATIONAL ACID PRECIPITATION ASSESSMENT PROGRAM REPORT TO - - PowerPoint PPT Presentation

THE 2011 NATIONAL ACID PRECIPITATION ASSESSMENT PROGRAM REPORT TO CONGRESS Douglas Burns, Jason Lynch, Jack Cosby, Mark Fenn, Jill Baron, U.S. EPA Clean Air Markets Division Status of Report Fifth NAPAP report(s) previous in 2005


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THE 2011 NATIONAL ACID PRECIPITATION ASSESSMENT PROGRAM REPORT TO CONGRESS

Douglas Burns, Jason Lynch, Jack Cosby, Mark Fenn, Jill Baron, U.S. EPA Clean Air Markets Division

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Status of Report

 Fifth NAPAP report(s) – previous in 2005  Through peer review and review by Air Quality

Research Subcommittee of Committee for Environ., Natural Resour. and Sustainability

 Currently with Office of Science and Technology

Policy for final review

 Hopeful of late 2011 publishing date

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Content

 Executive Summary and Introduction  Chapter 1 – Overview of Acid Rain Program, costs

and benefits

 Chapter 2 – Trends emissions and deposition, critical

loads

 Chapter 3 – State-of-science, ecosystem effects of acid

deposition

 Chapter 4 – Modeling future ecosystem effects,

emissions/deposition scenarios

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Acid Rain Program (ARP)

 EPA program that implements Title IV 1990 Clean

Air Act Amendments

 SO2 – Cap-and-trade, 8.95 Mt cap by 2010  NOX – Traditional emissions control, averaging  Human health benefits – $174 to $427 billion/yr in

2010, primarily PM2.5 and secondarily O3

 Costs – $1 to $3 billion/yr

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Additional Benefits of ARP

 Ecological and visibility improvement benefits not

well quantified

 Adirondack case study - Banzhaf et al., 2006,

ecological benefits of $336 - $749 million/yr

 Recent EPA study - visibility benefits $40 billion/yr  More research needed to better quantify complete

set of benefits – ecosystem services

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SLIDE 6

SO2 Emissions

Year

1940 1950 1960 1970 1980 1990 2000 2010 Title IV SO2 Utility Emissions (millions tons/yr) 2 4 6 8 10 12 14 16 18 20

65% decline since 1994

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NOx Emissions

Year

1980 1990 2000 2010 ARP NOx Emissions (millions tons/yr) 1 2 3 4 5 6 7

65% decline since 1995

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Air Quality – Ambient SO2

1989-91 2007-09

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Air Quality – Ambient NO3

1989-91 2007-09

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Wet Deposition SO4

2-

40%+ decline since early 1990s

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SLIDE 11

Wet Deposition Inorganic N

20% to 25% decline since early 1990s except mid-west Role of NH3/NH4

+

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Ecosystem Recovery

 More complex and nuanced story  Aquatic ecosystems

1.

SO4

2- decreasing everywhere except SE

2.

NO3

  • decreases at many sites, but less than SO4

2- and no

decreases at some sites

3.

ANC – increasing in NE, but not in SE

 Terrestrial ecosystems – most studies show no recovery,

continued declines in soil base saturation

 Little evidence to evaluate species recovery – limited

evidence that aquatic ecosystems beginning to recover

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Trends in lake and Stream Water Chemistry at LTM Sites, 1990-2008,

Sulfate lon Concentration (!leq/Uyr)

Source: EPA. 2010

  • 1990-2008 Sulfate lon Concentration
  • Increasing significant trend
  • Increasing non-significant trend

0 Decreasing non-significant trend

  • Decreasing significant trend
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Trends in lake and Stream Water Chemistry at LTM Sites, 1990·2008, Nitrate lon Concentration (peq/Uyr)

Soun;e: EPA 2010

  • 199G-2008 Nitrate lon

Concentration

  • Increasing significant trend
  • Increasing non-significant trend
  • No change

~

Decreasing non-significant trend

  • Decreasing significant trend
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Trends in lake and Stream Water Chemistry at LTM Sites, 1990-2008,

Source: EPA, 2010

ANC Levels (peq/Uyr)

1990- 2008 Acid Neutralizing Capacity (ANC)

e Increasing significant trend

0 Increasing non-significant trend 0 Decreasing non-significant trend

e Decreasing significant trend

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Trend Magnitude by Region

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Critical Loads

 First NAPAP report to extensively discuss CLs  Case studies steady-state CLs

1.

ADK lakes – 45% lakes in exceedance in 1989-91, 30% in exceedance in 2006-08

 Report emphasizes value of critical loads as policy-

informing tool

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Future Deposition Scenario Modeling to 2020 - MAGIC

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Model Results – Year 2050

Year 2050 Simulations

ANC < 0 ANC 0 - 50 ANC 0 - 50

Percent Lakes & Streams

2 4 6 8 10

Percent Lakes & Streams

10 20 30 40 50 Base Scenario A Scenario B Scenario C

Can’t get there from here

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Ecosystem Recovery - Hysteresis

Relative Measure of Stream Acidity Relative Measure of Pre-Acidification Biological Community Acidification R e c

  • v

e r y t

  • D

a t e Likely Range of Future Recovery

Point 1 Point 2 Point 3 Point 4 Less Acidic More Acidic Healthy Acid Impacted

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Acid Deposition & Climate Change

 Challenging to make quantitative predictions –

numerous interactions

 Temperature sensitive biogeochemical processes  Water/moisture availability – rapid oscillations  Role of N deposition as regulator of C uptake  Climate change another source of ecosystem stress  Global change should be considered in future forecasts

  • f S and N deposition effects
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Take Home Messages

 Title IV of CAA a huge success – goals have been

exceeded

 Ecosystems – not there yet

 Aquatic – chemistry recovering  Terrestrial – no evidence of recovery, little data

available

 A more in-depth discussion of recovery would be

helpful – expectations, restoration needed?, climate change

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Cross-State Air Pollution Rule

 Rule finalized by EPA July 6, 2011  Implementation would begin Jan. 1, 2012 – fully

implemented by 2014

 Affects SO2 and NOx emissions in 27 states  SO2 emissions reduced by 73% (2005)  NOx emissions reduced by 54% (2005)  Most similar to Scenario A from NAPAP report –

emissions reductions less, but faster