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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amount to <strong>the</strong> omission <strong>of</strong> over 624,000 nm to Asia markets and over 147,000 nm<br />
to markets in <strong>the</strong> US per year.<br />
Table 20: Differences in Nautical Miles used to Estimate Tanker <strong>Spill</strong>s and Actual Nautical<br />
Miles to Key Export Markets<br />
Key Export Market<br />
One-‐way<br />
Distance to<br />
Market<br />
(in nm)<br />
Average One-‐<br />
way Distance<br />
in Study Area<br />
(in nm)<br />
One-‐Way<br />
Distance<br />
Shortfall Per<br />
Tanker<br />
(in nm)<br />
Total<br />
Distance<br />
Shortfall Per<br />
Year<br />
(in nm)<br />
Asia Markets<br />
Shanghai, China* 4,865<br />
4,631 690,044<br />
Yokohama, Japan*<br />
Ulsan, South Korea*<br />
4,041<br />
4,363<br />
233<br />
3,808<br />
4,129<br />
567,342<br />
615,246<br />
Average<br />
US Markets<br />
4,423 4,189 624,211<br />
San Francisco** 1,051<br />
818 121,832<br />
Los Angeles** 1,391 233<br />
1,158 172,492<br />
Average 1,221 988 147,162<br />
Source: Brandsæter and H<strong>of</strong>fman (2010 p. 3-‐1); <strong>Enbridge</strong> (2010b Vol. 2 App. A p. 13); http://sea-‐distances.com/<br />
* We calculate nautical miles as half <strong>of</strong> <strong>the</strong> round-‐trip distance to all three regions in <strong>Enbridge</strong> (2010b Vol. 2 App A. p. 13).<br />
** We calculate nautical miles from Kitimat to San Francisco and Los Angeles using <strong>the</strong> calculator from http://sea-‐<br />
distances.com/<br />
Failure to consider spills outside <strong>the</strong> study region is contrary to CEAA, which<br />
requires an assessment <strong>of</strong> environmental effects that would occur “outside<br />
Canada” (CEAA Sec. 5). Thus, DNV’s methodological approach that ignores <strong>the</strong><br />
majority <strong>of</strong> <strong>the</strong> distance sailed by tankers to key export markets significantly<br />
underestimates spill likelihood and prohibits decision-‐makers from determining<br />
significant adverse environmental effects <strong>of</strong> <strong>the</strong> ENGP outside Canada required<br />
under CEAA.<br />
2. Failure to adjust tanker incident frequency data to correct for underreporting<br />
Literature in peer-‐reviewed sources suggests that vessel accident data reported in<br />
<strong>the</strong> LRFP database, which DNV uses to determine tanker incident frequencies in<br />
<strong>the</strong> marine shipping QRA, have serious deficiencies. Hassel et al. (2011) examine<br />
<strong>the</strong> LRFP database for underreporting <strong>of</strong> foundering, fire/explosion, collision,<br />
wrecked/stranded, contact with a pier, and hull/machinery accidents for merchant<br />
vessels exceeding 100 gross tonnes registered in particular states (flag states)<br />
including Canada, Denmark, Ne<strong>the</strong>rlands, Norway, Sweden, United Kingdom, and<br />
<strong>the</strong> US from January 2005 to December 2009. Using various statistical methods,<br />
<strong>the</strong> researchers estimate that reporting performance by LRFP ranges between 4%<br />
and 62% for select flag states compared to actual accident occurrences, suggesting<br />
that as few as one in 25 accidents were reported in <strong>the</strong> LRFP database for a<br />
particular flag state over a five-‐year period 17 . In <strong>the</strong> best-‐case scenario for vessel<br />
17 Hassel et al. (2011) suggest that results should be interpreted with caution due to assumptions and<br />
estimation methods used by <strong>the</strong> authors. However, according to Hassel et al. (2011), <strong>the</strong>ir findings are<br />
consistent with those made in <strong>the</strong> study by Psarros et al. (2010).<br />
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