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concept EIA-rapport - Staatsolie

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SRK Consulting: Project No: 439414 <strong>Staatsolie</strong> Pipeline <strong>EIA</strong> – Draft <strong>EIA</strong> Report Page 72<br />

With the implementation of mitigation measures listed below, the risks of substantial sub-surface<br />

contamination or aquifer contamination following a leak is considered minimal.<br />

Pollution of surface water and areas<br />

The risk of any spill reaching the surface is higher in areas where the pipeline lies above ground or<br />

shallow underground, as there is little or no overlying material that could prevent or slow the rise of<br />

fuel and exert counter pressure on the pipeline. However, shallow underground pipeline sections are<br />

expected to be specially protected by a plate inserted above them and thicker pipeline walls.<br />

The majority of the pipeline lies embedded in a clay layer up to 30 m underneath the Suriname<br />

River, and is further encased by the bentonite drilling mud that remains in the drill hole and congeals.<br />

The clay layer and congealed bentonite mud are relatively impermeable, and any leaks, particularly<br />

gasoline or diesel, would be expected to only slowly leak upwards through fissures in the ground.<br />

Leakage that occurs within a compact clay layer would thus be very localised 38 . These sections of<br />

the pipelines are also well protected from external interference, and the risk of an incident and/or the<br />

leaked material causing widespread pollution is lower.<br />

Based on the calculations undertaken in the QRA to evaluate pipeline risks, the maximum individual<br />

risk is low, i.e. generally well below 1x10 -6 per year risk of a fatality (meaning there is a one in a<br />

million chance of a fatality per year). The highest risk was calculated for the areas where pipeline<br />

sections HDD2 and HDD3 connect and the SOL and OGANE offtakes, where the fatality risk was<br />

calculated at a still very low 1.6x10 -6 per year. Based on international guidelines, this risk is<br />

considered to be acceptable without any further mitigation.<br />

The potential impact of an incident depends on the type of fuel that is spilled and the environment in<br />

which the spill occurs, as described in Table 6-12.<br />

Table 6-12: Potential impacts from pipeline leaks in various environments<br />

Product<br />

Location<br />

Suriname<br />

River<br />

LPG spill Diesel/gasoline spill<br />

An LPG spill is likely to reach the surface<br />

(river bed) more quickly, as the LPG is<br />

much lighter than its surrounding<br />

material.<br />

It is expected that an LPG incident in the<br />

Suriname River would have no long-term<br />

environmental damage as the gas<br />

evaporates rapidly with little or no impact<br />

to surroundings.<br />

The main hazard associated with the<br />

LPG pipeline is loss of containment<br />

resulting in a gas release, which could be<br />

ignited by a vessel in the vicinity. The<br />

resultant fire could engulf the vessel and<br />

cause fatalities to the crew and<br />

passengers on board, either directly due<br />

to the fire or due to the vessel sinking (in<br />

the worst case).<br />

A gasoline or diesel spill, if / once it has worked its<br />

way up from the pipeline, forms a layer on the<br />

water surface and therefore has a higher potential<br />

impact to the bio-physical environment than LPG.<br />

Diesel and gasoline will be transported with the<br />

river flow (ebb and flow conditions), with the<br />

influence of wind drag.<br />

Evaporation occurs immediately after release. As<br />

the surface slick spreads, more of the diesel and<br />

gasoline are exposed to the atmosphere, causing<br />

the evaporation rate to increase. Since gasoline is<br />

considerably more volatile, it would evaporate<br />

much more readily than diesel. Evaporation is the<br />

most significant physical-chemical process<br />

causing the reduction in the spill volume.<br />

Diesel and gasoline plumes may reach the<br />

riverbanks, with deposition along the shoreline, to<br />

be later re-entrained into the river current.<br />

Some of the suspended oil droplets may also sink<br />

to the riverbed. The oil deposited on the channel<br />

bottom may be transported laterally or<br />

resuspended, or undergo further biological or<br />

physical-chemical reaction.<br />

38 As opposed to leakage within a sandy substrate, in which the fuel could easily spread over a large area before reaching the<br />

river, resulting in extensive sub-surface contamination<br />

REUT/DALC 439414_<strong>Staatsolie</strong>Pipeline<strong>EIA</strong>_Draft <strong>EIA</strong> Report_Final June 2012

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