SECTION
5 ASSIMILATIVE CAPACITY CAPITAL STOCK
5.4 |
Assimilative
Capacity of Air (including Noise) |
|
|
|
|
5.4.1.12 |
The
table shows that for each of the pollutants
NO2, TSP and RSP there is a clear pattern
of non-compliant monitoring locations from
1994 to 1997, although there were fewer
non-compliances in 1998 than previous years.
For nitrogen dioxide, the daily AQO was
exceeded between 1994 and 1997 at Mong Kok
and the severity of the non-compliance (the
percentage of the AQO for the highest exceedence)
increased over this period, reversing a
trend of improvements in NO2 levels during
the late 1980s. The annual AQO for TSP has
been regularly breached at Kwun Tong, Sham
Shui Po, Central/Western and Mong Kok, with
the greatest exceedences all recorded at
Mong Kok. The same locations have shown
non-compliances with the annual AQO for
RSP (except for Central/Western which was
compliant in 1996), although the pattern
changed in 1998 where a non-compliance was
picked up at the new roadside station in
Causeway Bay.
|
|
|
5.4.1.13 |
There
were no continuous AQO exceedences for sulphur
dioxide between 1993 and 1998. Although
a number of exceedences of the 24 hour AQO
were recorded in the late 1980s, from 1990
onwards, following regulations to limit
sulphur content in solid and liquid fuel
oil(), there have been no further exceedences
of the 24 hour AQO (and the last one hour
exceedence was in 1994). SO2 levels have
also fallen due to the decline in the number
of major industrial sources of pollution
(eg incinerators at Kwai Chung and Kennedy
Town). The principal remaining sources of
this pollutant are from the coal-fired power
stations at Lamma Island and Castle Peak,
both of which have been fitted with pollution
abatement equipment.
|
|
|
5.4.1.14 |
In
order to determine trends in longer term
levels of air pollution in Hong Kong, data
are presented in Annex
G2 for annual average concentrations
of the pollutants monitored at each station
and for the territory overall. Long term
trends in both roadside and ambient levels
for six major pollutants (SO2, NO2, TSP,
RSP, CO and O3) are also shown graphically
in Figures 5.4b-d,
Figures 5.4e-g
(sourced from EDP 1998d) with respect to
their relevant annual air quality objective.
These data show increasing trends in the
Hong Kong annual average (ambient) concentrations
for NO2, though SO2 levels continue to decline
at ambient (urban and new town stations).
Ambient levels of particulates (both TSP
and RSP) have remained consistently high
over the last 10 years with both pollutants
close to their respective permissible AQO
limits. Whilst annual average concentrations
of ozone have only risen slightly, there
were two exceedences of the hourly AQO in
1996 and the highest level recorded in 1998
(at Tap Mun) of 239 ug m-3 was just slightly
lower than the hourly AQO of 240ugm-3. Although
the results for ozone since 1996 have been
greatly affected by the inclusion of data
from additional monitoring stations, rising
levels of this pollutant (along with NO2)
are a cause for increasing concern over
the formation of photochemical smog, although
additional data is required to establish
the long term trend of the background ozone
level.
|
|
|
5.4.1.15 |
The
data also show that roadside levels of RSPs
and NO2 are following an increasing trend
though roadside levels are also significantly
higher than the average territorial levels.
Although roadside levels of TSP declined significantly
between 1997 and 1998, they continue to exceed
the AQO. Roadside levels of CO remain low
and well within the permissible limits. |
|
|
5.4.1.16 |
Another
study (EPD's Saturation Monitoring Project
as reported in CTS3) has found that poor air
quality at many roadside locations can readily
be attributed to vehicle emissions. Road transport
emissions typically include oxides of nitrogen
(which in turn influences NO2 emissions),
RSPs (particularly from diesel vehicles),
CO as well as various toxic air pollutants.
In the CTS3 survey of roadside pollutants
in December 1996, a monthly average concentration
in excess of 150 ug m-3 was used to designate
sites as having 'high' NO2 concentrations.
A total of 11 out of the 15 sites monitored
recorded NO2 levels above this threshold.
Nine of these sites were either in the Kowloon
Peninsula area or along the north side of
Hong Kong Island. Roadside RSP was also monitored
and the daily average AQO for RSP (of 180
ug m-3) was breached a total of 38 times over
the month at 10 monitoring stations. Road
transport, in particular diesel vehicles,
have been identified as the most significant
contributors to the total quantity of RSP
emitted in urban areas. |
|
|
5.4.1.17 |
Ambient
levels of air pollution are also influenced
by emissions from the power generation sector
through the combustion of fossil fuels such
as coal and natural gas. These sources typically
give rise to oxides of sulphur and nitrogen
(including SO2 and NO2) as well as carbon
dioxide (see section on greenhouse gases,
starting Paragraph 5.4.1.23). Data from the
air quality monitoring stations operated by
the Hong Kong Electric Co Ltd and China Light
& Power Co Ltd for 1998 suggest that emissions
of SO2 and NO2 close to the utilities' plants
are well within AQO limits, although projected
increases in future energy demand in Hong
Kong will increase emissions and the requirement
to introduce energy efficiency and pollution
control measures (see Paragraph 3.6.2.4).
Potential development of waste-to-energy plants
in the SAR will also have implications for
air pollution and assimilative capacity for
both criteria and toxic air pollutants, although
such plant would require detailed EIAs and
appropriate mitigation measures would need
to be implemented. |
|
|
|