香港特別行政區政府 環境保護署
香港品牌形象
搜尋 網頁指南 聯絡我們
圖像
主頁
環評與規劃
環境影響評估條例
網上環評
關於環評與規劃
策略性環境評估
環境管理工具
指引與參考資料
搜尋此部份
環境保護互動中心 部門刊物 環保標準及統計資料
空氣 廢物 環評與規劃
噪音 水質 環境保育
空白 主目錄 空白

研究報告

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.

 

Back to topBackTable of ContentNext

 

   
 
2005 版權標誌| 重要告示

最近修訂日期: 二零零五年十二月二十二日