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Carriage, Handling and Storage of Dangerous Goods along

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130 RECOMMENDATIONS<br />

There is no single analytical method to characterise oil pollution due to its complex nature, or<br />

alterations in the environment. Fluorescence spectroscopy is an appropriate analytical technique<br />

for determining organic micropollutants having aromatic rings (s) in their molecules. Therefore,<br />

fluorescence properties <strong>of</strong> petroleum hydrocarbons can be used in oil pollution monitoring <strong>and</strong><br />

research. Fluorescence fingerprints have been successfully used for characterising petroleum-related<br />

contamination in the Danube River 3 . Further investigation is required to determine an effective water<br />

quality monitoring in the Mekong River Basin.<br />

6.3.2 Pollution Hotspots<br />

RECOMMENDATION<br />

Member Countries establish short-term water-quality programmes downstream from navigation<br />

activities <strong>and</strong> pollution hotspots.<br />

CHALLENGE<br />

To determine the impacts on increased water quality, further monitoring <strong>and</strong> analysis is required<br />

in pollution hotspots <strong>and</strong> areas with navigation activities <strong>and</strong> transport <strong>and</strong> storage <strong>of</strong> dangerous<br />

goods. The MRC WQM recommends that benchmark stations should be located at the six following<br />

sites:<br />

1. Lao/China border (LS3) on the Mekong River;<br />

2. Vientiane (LS5) on the Mekong River;<br />

3. Prek Kdam (CP17) on the Tonle Sap;<br />

4. Neak Luong (CS19) on the Mekong River;<br />

5. Tan Chau (VP2) on the Mekong River; <strong>and</strong><br />

6. Chau Doc (VS21) on the Bassac River.<br />

If short-term monitoring is undertaken to determine the impacts <strong>of</strong> navigation, the Member Countries<br />

requested that an additional seven stations should be included for pollution hotspot monitoring.<br />

These are Luang Prabang, the Lao/Cambodian border, Kratie, Tonle Sap (Tonle Sap Lake), Can Tho<br />

(Bassac), My Tho (Mekong) <strong>and</strong> Dong Thap (Mekong)<br />

The Risk Analysis <strong>and</strong> national consultation meetings determined that further monitoring should<br />

also be undertaken on the Mekong <strong>and</strong> Bassac Rivers in Viet Nam to determine potential sources <strong>of</strong><br />

threats to water quality in the Mekong Delta where IWT <strong>and</strong> the transport <strong>and</strong> storage <strong>of</strong> dangerous<br />

goods is most extensive.<br />

6.3.3 Pollution Modelling<br />

RECOMMENDATION<br />

Future pollution modelling should determine the extent <strong>and</strong> possible trans-boundary impacts <strong>of</strong><br />

water quality pollution including oil spills.<br />

CHALLENGE<br />

The potential for major oil spills is highest in Cambodia <strong>and</strong> Viet Nam due to the size <strong>of</strong> the<br />

petroleum terminals <strong>and</strong> tankers operating. Further analysis <strong>and</strong> hydrodynamic modelling is required<br />

to determine the possible trans-boundary impacts. The location <strong>of</strong> ports <strong>and</strong> terminals in relation to<br />

important wetl<strong>and</strong>s, vulnerable areas, water intake (drinking) <strong>and</strong> public infrastructure also needs

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