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TRansport and Atmospheric
Chemistry near the Equator-Atlantic (TRACE-A) and Southern African
Fire/Atmosphere Research Initiative (SAFARI)
Contributed by Meinrat O. Andreae, Biogeochemistry
Department, Max Planck Institute for Chemistry, Mainz, Germany
and Jack Fishman, NASA Langley Research Center, Hampton, Virginia,
USA
Regional meteorology and transport
of pyrogenic emissions and their reaction products
Meteorological and climatological work in SAFARI was focused
on defining the fields of motion at various scales, from the
turbulent to the synoptic and planetary, which influence fires
and determine the dispersion and transport of pyrogenic emissions.
During spring, anticyclonic flow is dominant over the subcontinent
south of 15°S, and the atmosphere is characterized by inversions
and stable layers that inhibit the development of penetrative
moist convection and thus trap pyrogenic material in the lower
atmosphere. Once burning products break through the mixed layer
they are again trapped by mid-tropospheric stable layers (Garstang
et al., 1996). In many instances, smoke laden airmasses in the
region were quite old and had recirculated for several days over
the continent before being advected to the Indian or Atlantic
Oceans (Swap et al., 1996; Tyson et al., 1996). Emission to the
Indian Ocean tended to be at higher altitudes, whereas the flow
to the Atlantic was usually trapped in the lower few kilometers
of the troposphere.
Flights over the tropical South Atlantic were conducted to
answer the overriding question of how much of the ozone enhancement
is a result of in situ generation and how much is the result
of advection from either South America or southern Africa, or
both. Photochemical calculations were performed using the in
situ DC-8 measurements as input. Calculations near the source
regions indicate that photochemical generation of ozone in the
lower atmosphere on the regional scale (100-1000 km) near sources
of biomass burning are comparable to the amount of regionally
generated ozone over industrialized regions at temperate middle
latitudes during summertime (Mauzerall et al., 1998).
Table1. "Best guess" emisson
factors and emission ratios for savanna fires, and estimates
for emissions fromAfrican and global savanna fires, all biomass
burning, and all anthropogenic sources (including biomass burning).
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Perhaps the most important finding is the ubiquitous nature
of ozone generation in the upper tropical troposphere, where
integrated ozone production is calculated to be >1 x 1011
mol. cm-2 s-1 between 8-12 km. This large
net photochemical production in the upper troposphere offsets
the photochemical destruction of ozone within the tropical marine
boundary layer. Correlation of NOy with CO suggests
that biomass burning was an important source of NOx
at all altitudes during TRACE-A. There is also evidence that
NOx throughout the TRACE-A region was recycled from
its oxidation products rather than directly transported from
its primary sources. The low HNO3 mixing ratios observed
above 8 km suggest a rapid mechanism of HNO3 to NOx
conversion, not usually considered in current models Jacob et
al., 1996). Mixing ratios of peroxides and formaldehydes (byproducts
of hydrocarbon oxidation and indicators of the oxidizing capacity
of the troposphere) were fairly well simulated by the photochemical
calculations. Discrepancies between the calculated mixing ratios
and ratios among the species point to possible deficiencies in
our understanding of the chemical mechanisms by which these compounds
are generated in the atmosphere.
Satellite remote sensing of fires and
vegetation.
The remote sensing activity in SAFARI-92 was designed to develop
and test algorithms for fire detection, to assist in estimating
fuel loads, to supply inputs to transport modeling studies, and
to assess the potential contribution of satellite data to regional
trace gas emission estimates. Most fires were found to occur
in the period July-September 1992, with a peak in August, placing
the SAFARI-92 field campaign well within the main burning season
(Justice et al., 1996). Comparison with a wetter year (1989)
showed that burning was reduced by approximately 50 per cent
in 1992 in the area between 20° and 30°S, a result ascribed
to the effect of the severe drought of 1991/92 on available biomass.
A related study (Scholes et al.) reported the development
of a method for estimating biomass consumed by fire in the tropics,
based on some known fuel-constraining factors and using satellite
data to estimate the area burned. The new estimates of the average
quantity of biomass burned annually in Africa south of the equator
are considerably lower than previous estimates based on extrapolation
from point data. These findings highlight the importance of developing
new approaches to the measurement of the amounts of biomass burned
on a regional scale for future assessments of the environmental
impact of biomass burning.
Beyond STARE
The SAFARI-92 campaign in southern Africa was followed by
a series of flight missions to characterize the regional atmospheric
chemistry outside of the burning season (SAARI) and by
experiments in Zambia and Kenya (AFARI) to investigate emissions
from fires in savanna types which had not been sampled during
SAFARI. Studies on soil and plant emissions of trace gases have
also continued in the region, to obtain a more comprehensive
coverage of ecosystems and soil types, and to understand variability
at longer time scales. A future study, SAFARI-2000, is in the
planning stage; details can be found later in this newsletter.
In subsequent large-scale atmospheric chemistry studies, a
NASA DC-8 mission was conducted in September-October 1996 to
investigate the atmospheric chemistry over the tropical Pacific
Ocean, which had been assumed a priori be one of the cleanest
regions on the planet. A particularly surprising observation,
however, was the pervasiveness of biomass burning plumes in the
middle troposphere (6-8 km) throughout the southern Pacific region.
Initial analysis suggests that many of these plumes, containing
unexpectedly high concentrations of O3 and other trace
gases associated with emissions from biomass burning, originate
from Africa and extend all the way to Easter Island (27°S,
110°W) in the eastern Pacific (Vay et al., 1998). Thus, the
impact of burning in the South America and southern Africa truly
has a measurable impact on the composition of the atmosphere
throughout the entire Southern Hemisphere troposphere.
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and N.J. Blake, Aerosols from biomass burning over the tropical
South Atlantic region: Distributions and impacts, J. Geophys.
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savanna fires, In Fire in the Southern African Savanna: Ecological
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