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    Acetaldehyde in the Central Valley

    of California

    Steven WalshSARP 2009WAS Group

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    Outline

    - Overview

    - Photochemistry

    - Relationships

    - Implications/conclusions- Future work

    - References

    - Acknowledgments

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    Overview

    Acetaldehyde is an important resultant photochemicalspecies that is not believed to have a ground basedemission source.

    Acetaldehyde and ethanol correlate well with eachother when examining all collected flight data.

    Acetaldehyde to ethanol ratios do not correlate withdistinct observed acetaldehyde concentrations.

    Does biomass burning affect acetaldehydeoccurence?

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    Conceptual model

    Dairy FarmWinery/vineyard

    most?

    AcetaldehydeCentralValley

    PhotolysisHOx

    Ethanol

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    Acetaldehyde photochemistry

    ETHANOL - OH REACTION

    C2H5OH(g)

    +OH(g)

    .

    H2O(g)

    5% CH2CH2OH(g)

    90% CH3CHOH(g)

    .

    .

    5% CH3CH2O(g)

    .

    +O2(g)

    HO2(g).

    CH3CHO(g)Ethanol Acetaldehyde

    Jacobson, 2002

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    Ethanol vs. Acetaldehyde

    y = 0.1185x + 161.47

    R2

    = 0.6864

    y = 0.1047x + 215.76

    R2

    = 0.6995

    0

    200

    400

    600

    800

    1000

    1200

    1400

    1600

    0 2000 4000 6000 8000 10000 12000

    Ethanol (pptv)

    Ethanol-AcetaldehydeFlight 1Ethanol-AcetaldehydeFlight 2Flight 1

    Flight 2

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    Acetaldehyde vs. A/E

    0.0000

    0.2000

    0.4000

    0.6000

    0.8000

    1.0000

    1.2000

    1.4000

    1.6000

    0 200 400 600 800 1000 1200

    Acetaldehyde (pptv)

    Acetaldehyde

    vs. A/E Flt1

    Acetaldehydevs. A/E Flt2

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    Ethanol correlates to acetaldehyde but why isthere variability?

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    Flight 1 Acetaldehyde distribution

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    Flight 2 Acetaldehyde distribution

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    Can biomass burning affect theobservation of Acetaldehyde?

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    Automated Biomass BurningAlgorithm(ABBA GOES-8) on day July 222009-Flight 1.

    Automated Biomass BurningAlgorithm(ABBA GOES-8) on day July 242009-Flight 2.

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    Flight 1 CH3Cl

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    Flight 2 CH3Cl

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    CH3Cl vs. Acetaldehyde

    0

    200

    400

    600

    800

    1000

    1200

    550 560 570 580 590 600 610 620 630 640

    CH3Cl (pptv)

    Flight 1

    Flight 2

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    CH3Cl vs. Acetaldhyde

    y = 8.0122x - 3940.5

    R2

    = 0.9345

    y = 6.1925x - 3102.8

    R2

    = 0.8496

    0

    200

    400

    600

    800

    1000

    1200

    560 570 580 590 600 610 620 630 640

    CH3Cl (pptv)

    Flight1

    Flight 2

    Linear (Flight 2)

    Linear (Flight1)

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    CH3Cl vs. Methane

    R2

    = 0.9094

    1.88

    1.9

    1.92

    1.94

    1.96

    1.98

    2

    2.02

    2.04

    560 570 580 590 600 610 620 630 640

    CH3Cl (pptv)

    Flight 1

    Flight 2

    Linear (Flight 2)

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    Methane vs. Acetaldehyde

    R2

    = 0.9589

    0

    200

    400

    600

    800

    1000

    1200

    1.88 1.9 1.92 1.94 1.96 1.98 2 2.02 2.04

    Methane (ppmv)

    Flight 1

    Flight 2

    Linear (Flight 2)

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    Ethanol vs. Acetaldehyde

    R2

    = 0.3053

    300

    400

    500

    600

    700

    800

    900

    1000

    1100

    2000 3000 4000 5000 6000 7000 8000

    Ethanol (pptv)

    Flight 1+2suspect points

    Linear (Flight1+2 suspect

    points)

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    Interpretation of suspect biomassburning samples

    Distal evidence of BiomassBurning event

    High ethanol source-Dairy?

    Proximal tobiomass burningevent

    High ethanolinfluence

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    Sample Methane (ppmv) Acetaldehyde (pptv) CH3Cl (pptv) A/C

    Distal samples711 1.894 426 572 0.745

    722 1.931 446 577 0.773

    1104 1.894 575 570 1.009

    Proximal samples

    1116 2.019 1015 615 1.6501103 1.999 1008 621 1.623

    1118 1.951 851 600 1.418

    1115 1.93 765 579 1.321

    710 1.909 769 609 1.263

    707 1.918 729 629 1.159

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    Future work

    - More projects on the interaction betweenbiomass burning and secondary photochemicalproducts.

    - Continue to assess the impact of biomassburning against other sources of pollution.

    - Continue conducting airborne missions becauseof their ability to detect secondaryphotochemical products.

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    References

    Jacobson, M., Z. (2002). Atmospheric pollution: history, science, and regulation.Cambridge: Cambridge University Press. 109-111.

    Seinfeld, J., H. and Pandis, S., N. (1998), Atmospheric chemistry and physics:From air pollution to climate change. Canada: John Wiley & Sons, Inc. 286-288.

    Carter, W.P.L (1994) Development of ozone reactivity scales for volatileorganic compounds, J. Air Waste Manag. Assoc., 44, 881-899.

    Steiner, A. L., Cohen, R. C., Harley, R. A., Tonse, S., Millet, D. B., Schade, G. W.,and Goldstein, A. H. (2008), VOC reactivity in central California:comparing an air quality model to ground-based measurements,Atmos. Chem. Phys., 8, 351-368.

    Holzinger, R., C. Warneke, A. Hansel, A. Jordan, W. Lindinger, D. H. Scharffe, G. Schade,and P. J. Crutzen (1999), Biomass burning as a source of formaldehyde, acetaldehyde,methanol, acetone, acetonitrile, and hydrogen cyanide,Geophys. Res. Lett., 26(8), 11611164.

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    Acknowledgments

    NASADC8 Crew

    NSERC

    UCIDr. Sherwood Rowland

    Dr. Donald Blake

    Dr. Melissa Yang

    SARP WAS Group