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Assessing the Ecological Impact of the Antarctic Ozone Hole Using Multisensor Satellite Data

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Dan Lubin, Scripps Institution of Oceanography ... Grazing by Krill (Euphausia superba) Higher Predators (leopard seals, orcas) ... – PowerPoint PPT presentation

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Title: Assessing the Ecological Impact of the Antarctic Ozone Hole Using Multisensor Satellite Data


1
Assessing the Ecological Impact of the Antarctic
Ozone HoleUsing Multi-sensor Satellite Data
Dan Lubin, Scripps Institution of
Oceanography Kevin Arrigo, Dept. of Geophysics,
Stanford University Osmund Holm-Hansen, Scripps
Institution of Oceanography
2
Enhancement of UV Flux at Antarctic Surface
  • Measured since 1988
  • NSF UV Monitoring Program
  • Palmer Station
  • McMurdo Station
  • Ushuaia, Argentina
  • Barrow, AK
  • San Diego, CA
  • http//www.biospherical.com

3
The Antarctic Marine Food Web
Higher Predators (leopard seals, orcas)
Grazing by Krill (Euphausia superba)
Primary Production
4
Field Work on Ecological Effects
  • Began in late 1980s, primarily at Palmer Station,
    west of Antarctic Peninsula
  • Smith et al. (Science, 1990) ICECOLORS 2-4
    reduction in primary production in marginal ice
    zone (MIZ)
  • Holm-Hansen et al. (Photochem. Photobiol., 1993),
    reduction lt 1 integrated over entire Southern
    Ocean

5
Need for Satellite-Based Assessment
  • Comprehensive field work is expensive, limited in
    time and place.
  • Previous estimates of total impact on Southern
    Ocean primary production are rough extrapolations
    from point measurements to larger areas.
  • Satellite data now offer complete coverage of the
    Southern Ocean for evaluating key forcing factors.

6
Surface UVR Algorithm Developmentco-locating
TOMS, AVHRR, SSM/I in 3 regions
  • Sea ice more influential than clouds on TOA UV
    radiance.
  • Parameterization of UV sea ice albedo as function
    of sea ice concentration.
  • Method developed to use TOMS and SSM/I alone.
  • see Lubin and Morrow, JGRd (2001).

7
AVHRR cloud ID using near-IR (3.5 mm) channel
8
Seasonal variability in sea ice concentration
9
Total Column Ozonefrom TOMS
10
Sea Ice Concentrationfrom SSM/I
11
Cloud Effective Optical Depthfrom TOMS
Reflectivity
12
UV-A (315-400 nm) Fluxfrom d-Eddington model
13
UV-B (280-315 nm) Fluxfrom d-Eddington model
14
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15
Biologically Weighted Flux(photoinhibition in
phytoplankton)
16
Comparison with Palmer Station UV Monitor Data
17
Geographic Assessment of Enhanced UV Fluxes
  • Spectral flux weighted by action spectrum for
    photoinhibition in Antarctic phytoplankton
  • Define climatological UVR
  • in terms of mean cloud attenuation, sea ice, 1979
    total ozone
  • evaluate 20-year standard deviation s
  • Enhancement where photoinhibition flux exceeds
    climatological mean by 2s or more
  • Geographically significant enhancement where the
    enhanced fluxes intersect biomass as determined
    by SeaWiFS
  • Lubin et al., GRL 2004

18
UVR Enhancement at Palmer Station, Spring 1992
19
Use of SeaWiFS to Locate Phytoplankton Biomass
20
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21
UVR Enhancements by Southern Ocean SectorLubin
et al., GRL 2004
22
Spectral Flux at the Sea Surface
  • Edd and Edi are direct and diffuse components
  • surface reflection divided into direct and
    diffuse components, both of which are sum of
    specular reflection and reflectance from sea foam
  • sea foam reflectance a function of wind stress
  • Fresnels law for specular reflection

23
In-Water Optics
  • Beers law for spectral flux penetration
  • Diffuse attenuation coefficient Kd(z) partitioned
    into components describing attenuation by pure
    water, phytoplankton, detritus, and chromophoric
    dissolved organic matter.

24
In-Water Optics - Components
  • Pure Water coefficents from Smith Baker (1981)
  • Plankton (chlorophyll) from Sathyendranath et al.
    (1989)
  • Detritus from work by Arrigo et al. (1998)
  • CDOM from work by Mitchell and Holm-Hansen
    (1991) Arrigo et al. (1998)

25
Phytoplankton Production
  • G is phytoplankton growth rate (d-1) calculated
    from temperature and light availability
  • C/Chl a is the phytoplankton CChl a mass ratio
    (50)
  • Beff is effective phytoplankton concentration
  • G is modeled in terms of a temperature-dependent
    maximum rate and a light limitation term

26
Cumulative Exposure to UVR
  • Throughout the day, the physiological
    inactivation of algal biomass (effective biomass
    Beff) is expressed by reducing Beff with
    increasing UVR exposure.
  • At dawn, Beff(z,t) is set Chl a (z,t)
  • Vertical mixing simulated by averaging Beff over
    MLD, then applying this average to each layer
    within MLD

27
Comparison with Field Observations decrease in
C-fixation relative to no UVR
28
Station A59.19 S, 56.89 E04 October
  • Photoinhibition dose Hinh varies with time and
    depth, 30 greater in exp. run than control at
    surface
  • Assess individual contributions of UV-B and UV-A
  • Substantial UV-A contribution to Hinh and Beff
  • Panel B 1979 (control)
  • Panel C 1992 (exp.)

29
Total Change in Primary Production
30
Temporal Variation in Primary Production Loss
over Southern Ocean
31
Major Conclusion of Small Impact
  • Surface UVR-induced losses of primary production
    can be several percent, with large UV-B component
  • When integrated to 0.1 light depth, loss of
    primary production throughout Southern Ocean, due
    to enhanced UV-B, is lt 0.25
  • Major reasons strong UV-B attenuation with
    depth, location of most ozone depletion over
    Antarctic continent, temporal mismatch between
    maximum ozone loss and maximum phytoplankton
    abundance
  • Several sensitivity analyses did not alter this
    conclusion
  • changing MLD and mixing time
  • temperature dependence of primary production
  • Photoacclimation parameter Ek, specifying
    saturation of photosynthesis
  • detrital and CDOM absorption
  • phytoplankton absorption
  • variability in Action Spectrum
  • Instantaneous versus cumulative exposure to UVR

32
Necessary Future Work
  • Improve parameterizations throughout model
  • in-water radiative transfer, processes very near
    sea ice
  • Repeat experiments for even deeper and
    longer-lasting ozone holes of late 1990s
  • Consider regional ecosystem effects
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