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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 />

32

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