Report - Agence canadienne d'évaluation environnementale
Report - Agence canadienne d'évaluation environnementale
Report - Agence canadienne d'évaluation environnementale
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Impacts on the inhabited area and human activities<br />
According to the proponent, the measured sound levels (Leq 1 h), varied between<br />
40 and 62 dBA during the day and between 33 and 58 dBA at night in the inhabited<br />
areas. Rue Vitré is the quietest spot at night. Traffic not only on Highway 132 and<br />
Expressway 20, but also on the rue de l’Anse (western access to Expressway 20) and<br />
Lallemand Road (eastern access to Expressway 20) and the chemin Saint-Roch is<br />
the main cause of noise. Some other selected noise sources were itemized, but<br />
without influencing hourly measurements.<br />
According to the proponent, the sound climate are already disturbed in the zone<br />
considered for the gas pipeline area by industrial activity, an airport, railways,<br />
Expressway 20 and several stretches of road.<br />
♦ Finding — The Panel notes that the present sound environment occasionally<br />
exceeds the criteria set by the ministère du Développement durable, de<br />
l’Environnement et des Parcs close to the main roadways on the basis of Leq 1 h.<br />
The rue Vitré area is described as quiet at night.<br />
Noise impact related to the LNG terminal<br />
Noise impact during construction<br />
Projected sound levels during construction and operation were calculated using the<br />
method described in the standard ISO 9613-2. This makes it possible to predict sound<br />
level in weather conditions that are favourable to the spread of noise, such as a<br />
carrying wind (i.e., from the source toward the receiver) or with a moderate<br />
temperature inversion like that which commonly occurs at night. The method takes<br />
into account the sound power, the dampening effect of obstacles (buildings, drop in<br />
terrain level, etc.), geometric dispersion, absorption by air, ground effects and<br />
reflection off surfaces. (PR3.3.1, p. 6.89).<br />
The main sound impacts during terminal construction would be due to machinery on the<br />
building site – mechanical shovels, cement mixers, cranes, and trucks, as well as pile<br />
driving at the jetty. In the main, these activities would be spread out over about 24 months,<br />
including slowdowns and halts during winter periods. Construction of LNG storage tanks<br />
would be carried out continually 24 hours a day while pile driving for construction of the jetty<br />
would take place only during the day (PR3.3.1, p. 4.103, 4.104 and 6.95).<br />
Over and above the noise impacts of trucks on the site, the noise impacts of trucks<br />
moving along public arteries near the site, either Lallemand Road, rue de l’Anse, or<br />
Highway 132, were also assessed. Along with construction site noise, the intensity of<br />
noise effects from truck traffic on public arteries was described as average (ibid.,<br />
p. 6.99-6.101; PR5.1, p. 2.7).<br />
Rabaska Project – Implementation of an LNG Terminal and Related Infrastructure 183