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A Spill Risk Assessment of the Enbridge Northern Gateway Project

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(Brandsæter and H<strong>of</strong>fman 2010 p. 5-­‐49). This lack <strong>of</strong> transparency raises concerns<br />

related to <strong>the</strong> number and types <strong>of</strong> tanker incidents included in <strong>the</strong> data set and<br />

whe<strong>the</strong>r <strong>the</strong> analysts altered any <strong>of</strong> <strong>the</strong> LRFP data based on undisclosed<br />

assumptions. Fur<strong>the</strong>r, LRFP data likely reflects jurisdictions where marine safety<br />

measures such as those announced by <strong>the</strong> Canadian government and mitigation<br />

measures such as escort tugs are already enforced. Thus incident frequencies<br />

potentially double count <strong>the</strong> use <strong>of</strong> escort tugs that DNV incorporates into LRFP<br />

data to reduce <strong>the</strong> likelihood <strong>of</strong> tanker spills although it is impossible to determine<br />

without access to <strong>the</strong> proprietary data (potential double-­‐counting <strong>of</strong> mitigation<br />

measures discussed on p. 33).<br />

Second, DNV fails to support assumptions used in <strong>the</strong> development <strong>of</strong> tanker<br />

incident frequencies. DNV claims that assumptions used in <strong>the</strong> development <strong>of</strong><br />

base incident frequencies per nm are based on information from tanker operators<br />

and captains, as well as studies <strong>of</strong> vessel operating patterns (Brandsæter and<br />

H<strong>of</strong>fman 2010 p. 5-­‐50) yet <strong>the</strong>re is no evidence provided to support <strong>the</strong>se<br />

assumptions. Two <strong>of</strong> <strong>the</strong> four assumptions used to estimate <strong>the</strong> average distance<br />

travelled by a tanker per year are supported with reference to a study completed<br />

for <strong>the</strong> liquefied natural gas terminal Rabaska (Rabaska 2004 as cited in<br />

Brandsæter and H<strong>of</strong>fman 2010 p. 5-­‐51). However, detailed information or<br />

discussion comparing <strong>the</strong> similarities and differences between Rabaska and <strong>the</strong><br />

ENGP is absent from <strong>the</strong> report and <strong>the</strong> Rabaska study is not appended to DNV’s<br />

study nor is it found in <strong>the</strong> project’s public registry database on <strong>the</strong> NEB website.<br />

Fur<strong>the</strong>rmore, assumptions related to <strong>the</strong> amount <strong>of</strong> time tankers sail in areas<br />

where a grounding could occur and <strong>the</strong> amount <strong>of</strong> time tankers sail in open water<br />

where foundering can occur are not supported with any evidence or references nor<br />

are any <strong>of</strong> <strong>the</strong> assumptions calibrated with historical data or expert opinion.<br />

Incident frequencies are <strong>the</strong> basis for estimating spill return periods in <strong>the</strong> ENGP<br />

application. Since return periods are <strong>the</strong> product <strong>of</strong> incident frequencies,<br />

conditional probabilities, <strong>the</strong> distribution <strong>of</strong> tanker routes travelled, <strong>the</strong> length <strong>of</strong><br />

each tanker route, and mitigation measures, any uncertainty or errors in incident<br />

frequencies will carry through to <strong>the</strong> final result. Thus, given <strong>the</strong> importance <strong>of</strong><br />

incident frequencies as a critical data input, DNV must effectively disclose all<br />

adjustments, assumptions, and uncertainties in a transparent manner. The lack <strong>of</strong><br />

evidence in <strong>the</strong> ENGP regulatory application makes it impossible to assess <strong>the</strong><br />

validity <strong>of</strong> <strong>the</strong>se values.<br />

2. Insufficient evidence supporting conditional probabilities for tanker spills<br />

The consequence assessment portion <strong>of</strong> <strong>the</strong> marine shipping QRA fails to<br />

adequately disclose any supporting information used to estimate conditional<br />

probabilities that an incident will result in a spill. DNV uses two different methods<br />

to estimate conditional spill probabilities: <strong>the</strong> first method determines conditional<br />

spill probabilities based on LFRP data; <strong>the</strong> second method estimates spill<br />

quantities for bottom and side damages for groundings and collisions based on <strong>the</strong><br />

International Marine Organization International Convention for <strong>the</strong> Prevention <strong>of</strong><br />

18

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