Pierre River Mine Project
Pierre River Mine Project
Pierre River Mine Project
- TAGS
- pierre
- river
- project
- www.ceaa.gc.ca
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TERRESTRIAL AENV SIRS 44 – 78<br />
Section 13.1<br />
Response 72a Shell incorrectly mentioned the Albian Sands <strong>Mine</strong> External Tailings<br />
Containment Facility when referring to the proposed external tailings disposal<br />
area (ETDA). The response to the May 2009 <strong>Pierre</strong> <strong>River</strong> <strong>Mine</strong>, Supplemental<br />
Information, Volume 2, SIR 461d should have referenced Shell’s <strong>Pierre</strong> <strong>River</strong><br />
<strong>Mine</strong> ETDA. The corrected response to the original question follows.<br />
In the early stages of ETDA construction and use, mammals, amphibians and<br />
reptiles are unlikely to interact with the <strong>Pierre</strong> <strong>River</strong> <strong>Mine</strong> external tailings<br />
disposal area (ETDA) shoreline from surrounding undisturbed areas. Terrestrial<br />
wildlife will be further discouraged from accessing the <strong>Pierre</strong> <strong>River</strong> <strong>Mine</strong> ETDA<br />
because the dyke surrounding the ETDA will be about 7 m high before any<br />
tailings are released.<br />
As discussed in EIA, Volume 5, Section 7.5.3.2, residual impacts from activities<br />
associated with the interaction of wildlife with project infrastructure, such as<br />
mortality associated with the ETDA, after mitigation measures are applied (see<br />
EIA, Volume 5, Section 7.1.3) are predicted to have a low environmental<br />
consequence rating for yellow rail and black-throated green warbler, and a<br />
negligible rating for all other key indicator resources (KIRs), such as Canadian<br />
toad, barred owl, moose, black bear, Canada lynx, fisher marten and beaver (see<br />
EIA, Volume 5, Section 7.5.3.2, Table 7.5-36). Interactions with infrastructure<br />
are reasonably well understood but lack quantification. Therefore, prediction<br />
confidence was rated as moderate. From 2003 to 2008, the Muskeg <strong>River</strong> <strong>Mine</strong><br />
recorded 70 avian mortalities because of oiling, averaging 11.6 birds per year.<br />
Total avian mortalities at the Muskeg <strong>River</strong> <strong>Mine</strong> from 2003 to 2008 are 119,<br />
averaging 19.8 birds per year. Regional environmental consequences in the<br />
Planned Development Case for interactions with infrastructure are predicted to be<br />
negligible. Shell is continuing to manage its bird deterrent systems to mitigate the<br />
effects of the ETDA on birds.<br />
Request 72b What design features and mitigation measures will Shell implement to<br />
substantially reduce the potential for wildlife to become contaminated during the<br />
early stages of tailings pond construction and use?<br />
Response 72b In the early stages of the external tailings disposal area (ETDA) construction no<br />
tailings will be present. Before tailings are eventually released into the ETDA, a<br />
7 m-high dyke surrounding the ETDA will be constructed, further discouraging<br />
terrestrial wildlife from accessing the <strong>Pierre</strong> <strong>River</strong> <strong>Mine</strong> ETDA.<br />
Shell will continue to manage its bird deterrent systems to mitigate the effects of<br />
the ETDA on birds. Sensory disturbance from the waterfowl deterrent system<br />
may also deter other wildlife potentially utilizing the area. Surrounding<br />
vegetation will be managed to remove all remnant patches of natural habitat to<br />
ensure that animals are not attracted to the area. If shoreline vegetation growth<br />
occurs in the ETDA after production begins, the vegetation will be removed with<br />
herbicide, and muskeg mats that rise to the ETDA surface will be covered with<br />
tarpaulins until they sink. A zero tolerance policy for wildlife feeding on site will<br />
help to reduce animal habituation and reduce the removal of nuisance wildlife.<br />
April 2010 Shell Canada Limited 13-67<br />
CR029