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Commercial Marine Shipping Accidents Understanding Risks Canada

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48 <strong>Commercial</strong> <strong>Marine</strong> <strong>Shipping</strong> <strong>Accidents</strong>: <strong>Understanding</strong> the <strong>Risks</strong> in <strong>Canada</strong><br />

Box 4.2<br />

Factors That Influence Impacts: The Explosion and Fire of PETROLAB<br />

On July 19, 1997, the crew of a 41m tanker named PETROLAB was<br />

washing the ship’s cargo oil tanks in preparation for a loading<br />

of stove oil while alongside Newfoundland’s St. Barbe wharf. At<br />

about 7:30 p.m., an explosion of accumulated petroleum vapours<br />

occurred below deck, resulting in two deaths. Two other crew<br />

members were seriously injured. This accident was made worse<br />

by the subsequent fire and is illustrative of how the degree of<br />

impact can be influenced by factors that arise after the accident<br />

itself. According to the TSB (2013), “[t]he ensuing fire was limited<br />

to the ship’s stores burning in the ‘tween-deck until, some two<br />

to three hours after the explosion, the paint on the outer hull<br />

began to burn and spread fire to the creosote impregnated dock<br />

pilings.” The fire would continue to burn for another 60 hours,<br />

during which time part of the town of St. Barbe was evacuated<br />

out of concern that the fire might spread from the wharf to<br />

the adjacent tank farm. In the end, in addition to the onboard<br />

deaths and injuries, the entire wharf, ferry ramp, and pipelines<br />

were destroyed.<br />

In their investigation report, the Transport Safety Board found<br />

that, while the wharf served both oil tankers and passenger<br />

vessels, the local volunteer fire department had neither shipboard<br />

firefighting training nor the necessary foam to fight petroleum<br />

fires. Despite these inadequacies they were being relied upon<br />

for emergencies by the terminal operator, Ultramar, as set out in<br />

their own contingency plan. Thus, when several local volunteer<br />

fire departments responded, they were reluctant to fight the<br />

fire with water. As for onboard firefighting equipment, although<br />

in compliance with regulatory requirements, much of it was<br />

left inoperable after the explosion disabled the ship’s service<br />

generator. Thus, for two to three hours, no effort was made to<br />

fight the fire while it was contained below deck. It took the arrival<br />

of the Canadian Coast Guard in the morning of July 20 th before<br />

a major firefighting effort began, at which point the dock was<br />

ablaze and the mooring lines had burned through, casting the<br />

ship adrift before it grounded across the harbour. The impacts<br />

could have been greater. A passenger ferry had been sharing the<br />

wharf for 90 to 135 minutes on the day of the explosion, with<br />

passengers embarking and disembarking, all while PETROLAB was<br />

conducting hazardous operations and with minimal precautions<br />

to separate such activities from ferry passengers.<br />

(TSB, 2013)<br />

Box 4.2 discusses a particular accident that occurred at a<br />

wharf in St. Barbe, in northwest Newfoundland, in 1997.<br />

The impact of the accident was worsened by an inadequate<br />

contingency plan set out by the terminal operator, insufficient<br />

training and resources for local firefighters, damage of<br />

onboard firefighting equipment during the accident, and<br />

a delayed response. Some of the regulations and voluntary<br />

initiatives described in Chapter 2 have led to improvements<br />

since this time.<br />

4.4 CONCLUSION<br />

The potential environmental impacts of a spill are heavily<br />

dependent on the nature and volume of the cargo, the<br />

local physical and social environment, the time of year, the<br />

location, and the response capacity. <strong>Marine</strong> spills can create<br />

significant challenges for respondents due to both the volume<br />

of cargo being moved by ships today and the challenges of<br />

conducting clean-up operations.<br />

Oil dominates the marine pollution landscape in <strong>Canada</strong> in<br />

many ways: it is the most common type of pollution spilled<br />

in Canadian waters; it is the substance for which environmental<br />

impacts — and the resulting social, cultural, health, and<br />

economic impacts — have been most heavily documented<br />

and studied; and the potential impacts of an oil spill are great.<br />

Most impacts have been reported as the consequence of large<br />

spills, although smaller spills occurring much more frequently<br />

may be associated with cumulative chronic impacts. There<br />

are gaps in understanding the behaviour and impacts of oil<br />

spills in cold and freshwater environments. In addition, little<br />

is known about other potentially dangerous cargo types such<br />

as HNS. Other types of impacts (socio-economic and health)<br />

have been subject to less analysis, and these are more likely<br />

to depend on the activities that are important to the region’s<br />

economy or survival (e.g., commercial fishing in Atlantic<br />

<strong>Canada</strong> and subsistence fishing in the North). Overall, there<br />

are many knowledge gaps surrounding the potential impacts<br />

of spills resulting from marine shipping accidents.

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