A Spill Risk Assessment of the Enbridge Northern Gateway Project
A Spill Risk Assessment of the Enbridge Northern Gateway Project
A Spill Risk Assessment of the Enbridge Northern Gateway Project
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<strong>of</strong> a collision spill exceeding 20,000 m 3 and 50,000 m 3 is 10% and 0.3%, respectively<br />
(Brandsæter and H<strong>of</strong>fman 2010 p. 6-‐81 -‐ 6-‐85).<br />
DNV estimates unmitigated spill return periods for each type <strong>of</strong> tanker incident based<br />
on scaled incident frequencies, conditional probabilities, <strong>the</strong> length <strong>of</strong> each segment,<br />
and <strong>the</strong> number <strong>of</strong> times <strong>the</strong> route is travelled per year. DNV presents unmitigated risk<br />
as a return period, which is <strong>the</strong> number <strong>of</strong> years between spill events, and is an<br />
alternative to stating <strong>the</strong> annual probability <strong>of</strong> a spill. According to DNV, an<br />
unmitigated tanker incident will result in an oil/condensate spill once every 78 years<br />
(see Table 6). DNV also estimates unmitigated return periods for various oil spill sizes<br />
and, based on Method 2 <strong>of</strong> <strong>the</strong> consequence assessment, DNV estimates that a spill<br />
exceeding 5,000 m 3 will occur every 200 years while a spill exceeding 40,000 m 3 , will<br />
occur every 12,000 years (see Table 7).<br />
DNV conducts a sensitivity analysis in its marine shipping QRA examining impacts <strong>of</strong><br />
several parameters on spill probabilities. The sensitivity analysis tests <strong>the</strong> impact <strong>of</strong><br />
changes in parameters on all three potential routes separately under <strong>the</strong> assumption<br />
that all 220 tankers forecast to call at Kitimat Terminal use <strong>the</strong> route being tested<br />
exclusively. Therefore, <strong>the</strong> spill probabilities do not account for using a combination <strong>of</strong><br />
routes. Results from <strong>the</strong> sensitivity analysis suggest that return periods change<br />
modestly compared to baseline return periods (Table 4).<br />
Table 4: Summary <strong>of</strong> Sensitivity Analysis on <strong>Spill</strong> Return Periods (years)<br />
Sensitivity Parameter North Route<br />
South Route<br />
via<br />
Caamano<br />
Sound<br />
South Route<br />
via<br />
Browning<br />
Entrance<br />
Baseline 69 83 84<br />
Sensitivity 1: Increase in Scaling Factors for Grounding 59 71 71<br />
Sensitivity 2: Increase in Traffic Density for Collisions 67 81 82<br />
Sensitivity 3a: Decrease to 190 Tankers per year 80 96 97<br />
Sensitivity 3b: Increase to 250 Tankers per year 61 73 74<br />
Sensitivity 4: 200 nm Extension to Segments 5 and 8* 67 81 82<br />
* DNV does not provide overall return periods for <strong>the</strong> trip extension sensitivity analysis and thus return periods were calculated<br />
based on Brandsæter and H<strong>of</strong>fman (2010).<br />
The next step in <strong>the</strong> DNV analysis estimates <strong>the</strong> impact <strong>of</strong> various mitigation measures<br />
on spill return periods. DNV examines several risk reduction measures qualitatively<br />
including enhanced navigational aids, vessel traffic management system, environmental<br />
limits for safe operation, and <strong>the</strong> establishment <strong>of</strong> places <strong>of</strong> refuge along tanker routes.<br />
The marine shipping QRA only quantitatively evaluates a single mitigation measure: <strong>the</strong><br />
tug escort plan. DNV obtains <strong>the</strong> risk reducing effect <strong>of</strong> escort tugs from a confidential<br />
study it completed in 2002 and applies <strong>the</strong> downward adjustments directly to powered<br />
grounding, drift grounding, and collision incidents for <strong>the</strong> ENGP (Table 5).<br />
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