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Injection height for biomass burning emissions from boreal forest fires

Fok-Yan Leung

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April 12, 2007.

Harvard University

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Special thanks to:

Jennifer Logan, Rokjin Park, and Dominic Spracklen (Harvard)

Edward Hyer and Eric Kasischke (UMD)

Leonid Yurganov

David Diner, Dominic Mazzoni, David Nelson, and Ralph Kahn (NASA/JPL)

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Funding from the NSF and EPA

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On opponents of greenhouse gas abatement: "Your political base will melt away as surely as the polar ice caps... You will become a political penguin on a smaller and smaller ice floe that is drifting out to sea. Goodbye, my little friend! That's what's going to happen." – Arnold Schwarzenegger

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We began by looking at emissions estimates for 1998 boreal fires, which vary significantly.

KAS05 emissions

2x as large as KAJ02

emissions

KAJ02

emissions

“Interannual” emissions

Derived using TOMS-AI

(for 1998)

“Climatological”

emissions

Discrepancies between KAS05 and KAJ02 stem primarily from differences in assumptions about belowground burning

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Comparison of surface and column data from 1998 with results of GEOS-Chem simulations

KAJ02

emissions

baseline

emissions

KAJ02

emissions

data - 1998

data - average

KAS05

emissions

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During intense boreal fires, intense heat can result in lofting of emissions well above the boundary layer

  • In GEOS-Chem, all biomass burning emissions are injected in boundary layer by default.
  • Base initial parameterization on assumptions that:
    • The majority of emissions from crown fires are more likely to be lofted into the free troposphere.
    • Crown fires are prevalent during highest burning months
  • Based on the above, and the work of Kasischke, (2005), we injected:
    • 40% of all emissions in boundary layer
    • 60% into free troposphere

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  • Putting large fraction of emissions in free troposphere reconciled model results with both surface and column data
  • For both surface and column data (anomaly data): KAS05 seems to perform better in capturing the CO behavior using parameterization

KAS05 – 60% of emissions

in FT, 40% in BL

Anomaly = 1998 - baseline

KAS05 – 100% of

Emissions in BL

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Conclusions from study of 1998 study:��Injection of biomass burning emissions in the free troposphere are necessary to reconcile ground and column data��Injection of biomass burning emissions in free troposphere results in higher tropospheric ozone throughout the northern hemisphere due to longer sequestration of NOx by PAN formation.��Preliminary studies suggest that model results are not particularly sensitive to the exact fractional split of emissions (Turquety et al., [2007], and unpublished work)��We were motivated to move beyond the “sensitivity analysis” level, and to our ongoing study of plume heights using the MISR instrument

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Using the MISR Instrument

  • Satellite instrument aboard TERRA platform
  • 4-5 days repeat time at high latitudes
  • Visual and infrared cameras at 9 different angles allows heights of clouds, smoke plumes, terrain, etc... to be calculated at 0.5 km vertical resolution
  • can distinguish smoke from clouds or other aerosols

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  • We look at discrete plumes from fires. Algorithm of Mazzoni and Nelson:
    • Detects plumes by trained plume shape recognition algorithm
    • Uses MODIS hotspots to narrow down number of plumes
    • Determines the maximum plume height
  • Using the algorithm, 66 discrete plumes were found in Alaska and Northern Canada during summer of 2002
  • Example of algorithm at work…

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Left: August 17, 2002

NW corner =(73 ˚N,130 ˚E)

SW corner =(60 ˚N,130 ˚E)

0 5 10

km

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Kahn et al, [2006] observed clear relationship between atmospheric stability and observed plume heights.��We compare the stability profiles calculated using the coarser GEOS4 data with the finer resolution BRAMS data, at the 66 sites

GEOS4

  • 1°x1.25° horizontal resolution
  • 30 vertical levels in troposphere
  • Reanalysis product.
  • Pressure is instantaneous pressure
  • Temperature is 6 hour average

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BRAMS (courtesy Marcos Longo)

  • 45 km horizontal resolution
  • 150 km vertical resolution in troposphere
  • Boundary and initial conditions use GFS analysis
  • Mesoscale model “nudged” by GFS
  • Pressure and temperature are instantaneous

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Stability profiles: BRAMS (courtesy Marcos Longo) and GEOS4: “Neutral” profiles and profiles with regions of high stability

    • In general, same vertical structural characteristics in BRAMS and GEOS4 stability profiles
    • Vertical “Offset” between GEOS4 and BRAMS profiles

“Neutral”

“High stability”

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Example of plume in trapped in a layer of high stability

From data courtesy David Nelson, 2007

Example of plume distributed in the free troposphere

2 (3%)

Below

35 (53%)

11 (17%) of plumes are distributed throughout the column

In

18 (27% of 66 cases)

Above

Stable layer present

Neutral

  • If there is a layer of high stability, plumes to tend become trapped in it
  • If plumes in a “neutral” atmosphere, they tend to be disperse

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Directions: Moving forward

  • Preliminary results suggests that stability profiles may provide a way to parameterize injection heights
    • First pass analysis of coarser grid, 2°x2.5° data show very similar stability profiles to those calculated using data from 1°x1.25° grid.

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  • Ultimately interested in relationship between plume heights and height of diffuse smoke
  • We are moving towards a parameterization for injection heights of emissions from boreal forest fires in GEOS-Chem

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S1: Modeling fire plumes is actually a quite well defined problem

  • Essentially plume rise is governed by the characteristics of the fire itself (rate fuel consumption determines buoyant energy) and on local meteorology (wind direction, convection, stability of the atmosphere)
  • However, challenge is in parameterizing plume injection height on a coarse grid
  • In a coarse grid
    • Meteorology is averaged over a large geographical area.
    • Other factors are highly uncertain at best (e.g. fuel loading)
  • Need a statistical method, preferably one that can be done online during simulations

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S2: Effect of PAN on ozone chemistry

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Implications for ozone chemistry – the effect of PAN carried aloft.

The Ox anomaly (primarily ozone) in September 1998 for simulation

KAS05.D2 at the surface (left) and at ~500 hPa (right) in ppb.

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S3: Comparing 66 plume histograms to stability profiles derived from GEOS4 data:

13 (19%)

5 (7%)

8 (12%)

Plume mostly OUT of stability level

35 (52%)

6 (9%)

0

Plume mostly IN stability level

Levels of higher stability (>5)

Level of lower stability (<3)

“Neutral profile”

i.e. increasing or nearly constant stability throughout troposphere

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S4: Comparing 66 plume histograms to stability profiles derived from BRAMS data:

12 (18%)

6 (9%)

9 (13%)

Plume mostly OUT of stability level

33 (49%)

7 (10%)

0

Plume mostly IN stability level

Levels of higher stability (>5)

Level of lower stability (<3)

“Neutral profile”

i.e. increasing or nearly constant stability throughout troposphere

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S5:Comparing 66 plume histograms to stability profiles derived from BRAMS and GEOS4 data: BRAMS/GEOS4

12 (18%)/13 (19%)

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6 (9%)/5 (7%)

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9 (13%)/8 (12%)

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Plume mostly OUT of stability level

33 (49%)/35 (52%)

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7 (10%)/6 (9%)

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0

Plume mostly IN stability level

Levels of higher stability (>5)

Level of lower stability (<3)

“Neutral profile”

i.e. increasing or nearly constant stability throughout troposphere

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S6: GEOS4 vs. BRAMS stability profiles

  • Generally, similar vertical structures
  • More levels of high stability at lower latitudes in GEOS4
  • Tropopause tends to be higher in BRAMs data
  • Both stability profiles calculated by simple forward method – however, BRAMS has higher vertical resolution (150m) and horizontal resolution (40km)
  • Assumption of standard US atmosphere in calculation of GEOS4 data
  • Difference in terrain levels not sufficient to account for “vertical shift”