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STATE OF AIR POLLUTION

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INTRODUCTION
Air pollution in Greater Johannesburg differs according to area. In poor residential areas
like Soweto, Westbury, Riverlea, Eldorado Park, Orange farm and Alexandra, coal and wood
burning for space heating and cooking is the major source of smoke and SO2 pollution. In urban areas around the CBD
and higher income areas such as Sandton, Randburg, Melville and Southgate, lead from
vehicle emissions and dust from mines (for the southern areas) cause pollution. In the
inner city, SO2 and O3 levels are especially high in winter. In
urban areas and the inner city, TSP (Total Suspended Particle) levels are also high due to
exhaust emissions and re-suspended dust from vehicles. All pollution levels rise in the
winter due to pollutants from vehicle emissions, coal fires, industries and mining areas
being trapped close to the surface by temperature inversion layers. Circulation patterns
over South Africa in the winter also do not disperse pollutants in a wavelike fashion as
in summer.
A selected measurement of
air pollution has been done in the former Johannesburg City Council area.
ANALYSIS OF AIR POLLUTION ACCORDING TO MAJOR SOURCES
- The worst affected area is around the Johannesburg CBD, which
includes the industrial areas from Denver in the east to Industria North and Industria
West in the west. These industries also lie mostly along the main rail and road commuter
ways, which also experiences pollution from vehicle emissions. Traffic also converges in
the CBD from the rest of Greater Johannesburg during the daytime. Morning and afternoon
pollution levels along major roads coming into and leaving the CBD are consequently bad,
with high primary (NO, CO and hydrocarbons) and secondary (ozone and NO2)
pollutant levels.
The Newtown monitoring station that covers the CBD
shows an increase in average annual ozone levels from 0,012 to 0,013 ppm, as well as CO
levels from 2,33 to 2,51 ppm during 1995/1996. A rise in ozone levels of 2-3 ppb per annum
is estimated in the inner city. Carbon monoxide (CO) levels at Newtown is also much higher
than at the other three monitoring stations, mainly due to vehicle emissions, and exceeds
the national guideline during winter. Newtown further shows a decrease in NOx,
NO2 and NO annual averages from 1995-1996 (GJMC Photochemical Smog Monitoring
Program, 1996). Hourly averages of non-methane hydrocarbons at Newtown show an increase in
winter. Levels rose from 0,4 ppm (which was below the national average hourly limit) in
January 1999, to 7 ppm in February, then 21 ppm in March, 34 ppm in April, 46 ppm in May,
92 ppm in June and 54 ppm in July. This is due to the increase in coal fires, as well as
seasonal circulation patterns and the temperature inversion level, which occur in autumn
and winter.
Pollution in the CBD is further affected by wind
blown dust from the mining belt, which increases TSP levels. Dust levels, measured as
particulate matter (PM10 of size 10 um in ug/m3) exceeded the average daily
guideline at Newtown once in February 1999, twice in April, 15 times in May, 10 times in
June and 4 times in July 1999. This underlines the fact that winter circulation patterns
in South Africa do not disperse pollutants due, in addition, to the role of inversion
layers.
- To the south of the CBD through to Southgate, pollution comes mainly
from the mining belt, as well as the large industrial areas such as City Deep, Booysens,
Electron, Tulisa Park and Aeroton. The City Deep (industrial) monitoring station shows the
second highest levels of CO after Newtown. Vehicle emissions and the burning of rubbish
also affects this area. At the South Hills (suburban / residential) monitoring station,
ozone levels are much higher than at the other stations, and exceeds the national average
of 0,01 ppm during winter. This may be due to the fact that over 91% of the population
here uses gas as a source of lighting, The burning of petroleum gas, as well as other
fossil fuels increases primary and secondary (ozone) pollutants. The industries
surrounding the area worsen the situation.
Annual average ozone levels decreased from 1984-1986
from 0,037 ppm to 0,016 ppm, then steadily increased to 0,033 ppm in 1990, and has since
decreased and levelled out around 0,028 ppm. Annual average NO2 levels at South
Hills dropped from 0,1 ppm in 1984 to 0,02 ppm in 1985, and have since mainly fluctuated
around this level. Annual average SO2 levels have been fluctuating around 0,006
ppm.
- Air quality in the whole area surrounding Soweto is bad, where
excessive amounts of coal is being burned. The worst affected areas are Diepkloof,
northwest of Soweto, the whole area from Devland to Nancefield southeast of Soweto, where
industries and informal settlements play a role, and the informal settlements from
Klipspruit to Protea South. Use of energy rises here from June to September, and
concentrations are only dissipated after the spring rains and when summer wind circulation
patterns return. This explains why the national guideline for particulate matter (mostly
smoke) is exceeded 20-30% of the time (in the winter months) in these coal-burning
residential areas. Dust from untarred roads, refuse burning and bad odours from the
Goudkoppies Landfill site, the Orlando Power station and informal industries also
contribute to air pollution.
According to UNEP (1996) the coarse fraction of
particulate matter (15>PM<2,5um) is the highest at lowest elevation sites and
informal shanty areas in Soweto, where population densities are the highest and coal
burning is excessive. Levels are the highest at Dhlamini, Jabavu and Chiawelo, which are
at low to middle elevations, and low to middle socio-economic levels. Levels are the
lowest at Diepkloof and Meadowlands to the north, which have a middle-high elevation and
middle to high socio-economic status (Sithole et al, 1994, in UNEP, 1996). The particulate
matter is derived from coal burning, dust, burning of garbage (lead, nickel, copper,
zinc), vehicles (lead), biomass burning and secondary production of sulphates.
- In the formal residential areas of Lenasia and Ennerdale, and the
informal settlements of Zakariyya Park, Vlakfontein, Elandsfontein and Lawley, pollution
comes mainly from dust from untarred roads, rubbish and coal burning, and light
industries. The worst affected areas are the informal settlements of Zakariyya Park,
Thembelihle, Vlakfontein and Hospital Hill south of Lenasia, where excessive coal burning
takes place. The Grasmere, Finetown and Weilers Farm areas east of Ennerdale, also burn
excessive amounts of coal, and also lie next to the N1 and other major roads where vehicle
emissions play a role. In the southern most part of the metropolitan area pollution is bad
at the Poortjie settlement and to the east of Orange Farm. Excessive amounts of coal
burning, vehicle emissions and dust from gravel roads and open land or agricultural
activities are the causes.
In the areas to the north of Soweto, dust from gravel and mine dumps
(especially Doornkop), roads, smoke and CO from coal burning pollutes the air. West of
Roodepoort the Roodepoort West industrial area, CBD activities, dust from mine dumps, and
excessive coal burning in informal settlements contribute to bad air pollution levels.
- In the Randburg area pollution levels in the formal residential areas
are much lower due to the minimal use of coal. Problem areas exist in the Randburg and
Sandton CBDs mostly due to vehicle emissions, light industries and commercial
activities. The Wynberg / Kew industrial area west of Alexandra causes pollution together
with the informal settlements in the area, where moderate to excessive amounts of coal is
used, and thus increases SO2 levels especially in the winter months. In the
northern parts of the metropolitan area the informal settlements of Diepsloot, Rietvallei
and Zevenfontein use excessive amounts of coal which causes pollution. The Northern Works
(sub-rural) monitoring station at the Northern sewage works, shows a slight increase in
annual levels of NOx (0,015-0,024 ppm), NO2 (0,008-0,013 ppm) and NO
(0,002-0,012 ppm) from 1985-1989, whilst a decrease in ozone (0,033-0,015 ppm) and
hydrocarbons (0,329-0,283 ppm) were observed (GJMC Photochemical Smog Monitoring Program,
1996).
CONCLUSION AND RECOMMENDATIONS
- The major sources of air pollution over Greater Johannesburg are
vehicle emissions, dust from mine dumps and untarred roads, excessive burning of coal
especially in informal settlements, industries and CBD activities.
- Very little and incomplete information exists on air pollution and
only limited monitoring is done.
- The 1950-dust pollution problem from sand and slimes dumps was only
partially solved due to the planting of surface covers like indigenous grasses and reeds.
New mine dumps and the reprocessing of slimes, are aggravating the problem.
- Pollution from incomplete combustion of fossil fuels in vehicles is a
problem that will only get worse due to the rising prices of new vehicles, and the
increasing amount of old and poorly maintained vehicles on roads. Increased use of private
vehicles, because of inadequate and inefficient public transport, will also increase air
pollution.
4. REFERENCES
GJMC, 1996: Photochemical Smog Monitoring Program.
Greater Johannesburg Metropolitan Council : Johannesburg.
UNEP 1996: Air Quality Management and Assessment
Capabilities in 20 Major Cities. UNEP: London. |
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