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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(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 />
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