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Environmental Statement - Maersk Oil

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6.3.1. STOCHASTIC MODELLING<br />

6 ‐ 6<br />

Balloch Field Development <strong>Environmental</strong> <strong>Statement</strong><br />

Section 6 Accidental Spills<br />

Stochastic modelling involves using a variety of wind and current data to simulate the most realistic<br />

probability outcomes of a spill event. For the blowout scenario the stochastic models were run for<br />

the time it is expected to take to drill a relief well (90 days), with an additional 30 days added in order<br />

to model the fate of the oil after the spill has been controlled (total = 120 days).<br />

A stochastic analysis of the uncontrolled flow rate during the two blowout scenarios and loss of diesel<br />

inventory was undertaken by modelling 40 scenarios utilising a broad range of weather and current<br />

data. Table 6‐5 shows the locations and main parameters for modelling undertaken at each of the<br />

drilling locations.<br />

Table 6‐5 Main parameters used for modelling of oil spills.<br />

Scenario Coordinates Volume Gas:<strong>Oil</strong> Ratio API<br />

Diesel<br />

inventory<br />

loss<br />

Balloch well<br />

blowout<br />

58 o 22’18.035’’N<br />

00 o 53’03.319’’E<br />

58 o 22’18.035’’N<br />

00 o 53’03.319’’E<br />

6.3.2. DETERMINISTIC MODELLING<br />

8,642 bbls<br />

(in 1 hour)<br />

124,000<br />

bbl/d<br />

Release diameter<br />

(inches)<br />

‐ 36.4 ‐<br />

87.3 scm/scm 40 9 5 / 8<br />

In addition to the stochastic analysis, a deterministic analysis was also undertaken for the worst case<br />

scenario of oil beaching identified in the stochastic modelling, in order to gain a more detailed insight<br />

into the fate of oil and to understand the water column and sediment distribution of the oil.<br />

Additionally, the fate of hydrocarbons in the presence of unvarying offshore and onshore winds at<br />

30 knots was modelled for both cases to determine the fate of each spill, according to DECC<br />

requirements. Air and water temperatures from January were assumed in order to represent worst<br />

case parameters.<br />

6.3.3. IMPACT ASSESSMENT CRITERIA<br />

The environmental resources within the vicinity of the Balloch field have been identified and assessed<br />

for their susceptibility to oil spills. Seabirds and fisheries are not normally affected by routine<br />

offshore oil and gas operations, but are among the environmental aspects most at risk in the unlikely<br />

event of an oil spill. The overall impact of spilt oil on the marine environment will vary seasonally due<br />

to variations in species abundance and behaviour. Potential effects on fish populations from spilt oil<br />

will be greatest during periods of fish spawning. In the event of a very large oil spill, fisheries may be<br />

closed as a result of fish ‘tainting’. Seabirds spending time on the sea surface are also vulnerable to<br />

oiling following a spill. Cetaceans passing through the area may also be vulnerable to oil spills.<br />

Drilling of the Balloch well is currently scheduled to begin in Q4 2012. <strong>Environmental</strong> sensitivities<br />

noted within the block during this time are:<br />

Fish nursery/spawning periods for Nephrops, Norway pout and blue whiting;<br />

The Offshore Vulnerability Index (OVI) for seabirds in the area is very high in<br />

November.<br />

The assessment criteria used to evaluate the environmental sensitivities in this section are<br />

outlined in Table 6‐6 and Table 6‐7.

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