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Characterisation of Cape Town brown hazeWalton, Nicola Maria 16 November 2006 (has links)
Faculty of Science
School of Geography And Archaeology and Enviromental Studies
9905693x
Nicola@crg.bpb.wits.ac.za / The Cape Town brown haze is a brown-coloured smog that is present over the Cape
Town atmosphere during the winter months due to the accumulation of gaseous and
particulate pollutants. The main aim of this research was to evaluate the impact of
atmospheric pollutants to visibility impairment by the brown haze through visibility
modelling of major pollution sources around the City of Cape Town. The screening
model, VISCREEN, the Plume Visibility model, PLUVUE II and the CALPUFF
Modelling System were employed to model the visual impact of emissions from the
major sources. Two point sources, Caltex Oil Refinery and Consol Glass, and three
area sources, Cape Town Central Business District (CBD), Cape Town International
Airport and the townships of Khayelitsha and Mitchell’s Plain were identified as the
major sources. An initial screening analysis indicated that emissions from the two
industrial sources would be visible and would result in a yellow-brown discolouration
of the atmosphere. Detailed modelling using PLUVUE II identified the area sources
of Cape Town CBD and the townships to be the significant contributors to visibility
impairment over Cape Town. Plume perceptibility is primarily dependant upon
particulate emissions while NOx emissions influence the colouration of the
atmosphere. CALPUFF was employed to assess the distribution of NOx, SO2 and
PM10 concentrations over the area and the associated visibility impairment on a nonhaze
(13 August 2003) and haze day (22 August 2003). Pollutant concentrations were
considerably reduced on the non-haze day compared to the haze day. The Cape Town
CBD was an important source of all the major pollutants with the townships
contributing significantly to the aerosol loading over Cape Town. Pollutant
concentrations are particularly elevated during the late evening and early morning
periods, particularly between 7 am and 8 am. Visibility impairment is greatest on the
haze day, particularly over the central Cape Town region and the townships. The
greatest reduction in visibility is experienced between midnight and 9 am which
corresponds with the periods of elevated atmospheric pollutant concentrations.
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PHYSICAL AND CHEMICAL PROPERTIES OF AEROSOL PARTICLES IN THE TROPOSPHERE: AN APPROACH FROM MICROSCOPY METHODSGwaze, Patience 26 February 2007 (has links)
Student Number : 0318623R -
PhD thesis -
School of Geosciences -
Faculty of Science / Physical and chemical properties of atmospheric particles are fundamental but not necessarily
easily accessible parameters. Uncertainties in these parameters are responsible for
some uncertainties associated with radiative impacts of aerosol particles in global climate
models. The uncertainties pertain to limitations of sampling and measurement devices,
difficulties in modelling aerosols (source strengths, spatial and temporal variability) and in
understanding microphysical and optical properties of aerosol particles. Physical and chemical
properties can be obtained at single-particle level by microscopy analyses of individual
particles. Using refined analytical and interpretative techniques to derive some of these
fundamental properties, aerosol particles collected in various field campaigns and laboratory
experiments were investigated using two high resolution microscopes. The particles
were collected during the LBA-EUSTACH, Large-Scale Biosphere-Atmosphere Experiment
part of European Studies on Trace Gases and Atmospheric Chemistry; SMOCC campaign,
Smoke Aerosols, Clouds, Rainfall and Climate; CTBH II, Cape Town Brown Haze II campaign;
and a controlled combustion experiment. Microscopy techniques were compared and
complemented with conventional techniques to characterise particle sizes, shapes, chemical
compositions and mixing states.
Particle size distributions were compared between geometric equivalent sizes measured from
microscopes and aerodynamic equivalent diameters, while taking into account particle densities.
Large differences were found between the particle sizing techniques. Microscopy
sizes (3D) were systematically lower than expected, and depended on the relative humidity
during particle sampling. Differences were attributed to loss of mass, presumably water
adsorbed on particles. Losses were high and could not be accounted for by known humidity
growth factors suggesting losses of other volatile compounds adsorbed on particles as well.
Findings suggest that there are inherent problems in defining particle sizes with different
sizing techniques, despite accounting for humidity growth of particles and particle density.
For collected particles, there are mass losses on individual particles, as opposed to particle
losses to walls during sampling. These losses will inevitably bias observed mass distributions
derived from collected particles and hence their number-size distributions.
Relatively young aggregated soot particles from wood combustion were investigated for
particle morphology (fractality, specific mass) and dynamic properties. Based on a procedure
that has been validated on modelled aggregates, several important parameters to
characterise geometry and drag-to-mass relationship of aggregates were derived. Three techniques were used to derive fractal dimension of soot aggregates. Averaged fractal dimension
was found to be Df = 1.82 ± 0.08. Dynamic shape factors of soot particles were
1.7 to 2.5 and increasing with mass of aggregates. In the regime 0.2 < Kn < 0.7 (Knudsen
number, Kn = 2#21;/dmob) the mobility diameter dmob was observed to be proportional to the
radius of gyration with a ratio dmob/2Rg = 0.81 ± 0.07. Specific surface area of aggregates
was determined to be 70 ± 10 m2g−1 based on SEM image analysis. These parameters can
be used directly in modelling microphysical behaviour of freshly formed soot particles from
biomass combustion with fractal dimension of Df ≈ 1.80.
Chemical composition and size distributions of particles were investigated on filter samples
collected during intense winter brown haze episodes in Cape Town. The sampling
technique offered the capability to characterise highly heterogeneous aerosols over a polluted
urban environment. Based on morphology and elemental composition, particles were
categorised into seven particle groups of: aggregated soot particles, mineral dust, sulphates
(SO2−
4 ), sea-salt, tar balls/fly ash, rod-shaped particles associated with soot agglomerates
and those that could not be attributed to any of these groups were labelled as ‘others’.
Apportionments of chemical species were highly variable both spatially and temporally.
These variations indicate lack of lateral mixing and dependence of particle chemical compositions
on localised and point sources within the Cape Town area. Sulphate and aggregated
soot particles were externally mixed with fractional number concentrations of 0− 82% and
11%−46%, respectively. Aerosol complex refractive indices were derived from the chemical
apportionment and particle abundance determined in microscopy analyses. The refractive
indices were combined with in-situ measurements of number-size distribution to determine
optical properties of aerosols. Single scattering albedo, !0, varied from 0.61 to 0.94 with a
mean value of 0.72±0.08. The !0 is much lower than is generally reported in literature, and
this was attributed to high concentrations of highly absorbing anthropogenic soot observed
in SEM analysis. The mean extinction coefficient #27;ep was 194 ± 195 Mm−1. #27;ep and !0
clearly demonstrated and explained quantitatively the visibility reduction due to particles
in the Cape Town atmosphere, reduction observed as the brown haze phenomenon. In all
the three case studies, microscopy single particle analysis played a critical role in advancing
knowledge of understanding properties of aerosol particles in the atmosphere.
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