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Pierre River Mine Project

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TERRESTRIAL AENV SIRS 44 – 78<br />

rail, Olive-sided flycatcher and Rusty blackbird), indicate when Shell will<br />

conduct the surveys and prepare the population estimates.<br />

Section 13.1<br />

Response 59a Population estimates with confidence intervals for each species currently listed<br />

under Schedule 1 of the Species at Risk Act (SARA) and current Committee on<br />

the Status of Endangered Wildlife in Canada (COSEWIC)-listed species known<br />

to occur in the local study area (LSA) cannot be calculated based on the surveys<br />

conducted to date and the low numbers detected. Additional surveys to obtain<br />

population estimates with confidence intervals within the LSA are beyond the<br />

scope of an environmental impact assessment.<br />

Shell has met the requirements of the Canadian Environmental Assessment Act<br />

(CEAA), the SARA and the Terms of Reference (TOR) in assessing the effects<br />

of the project on listed species through the assessment of wildlife indicator<br />

species and their habitat. Neither the CEAA nor the SARA implicitly or<br />

explicitly require that species-specific population surveys be conducted. Rather,<br />

the CEAA requires that an assessment of the environmental effects of a project<br />

include any change that the project may have on a “listed wildlife species, its<br />

critical habitat or the residences of individuals of that species”. SARA requires<br />

that, when conducting an environmental assessment, any adverse effects of the<br />

project on the listed wildlife species and its critical habitat must be identified,<br />

and, if the project is carried out, must ensure that measures are taken to avoid or<br />

lessen those effects and to monitor them. Shell has done this.<br />

The TOR require an impact assessment for wildlife, including endangered<br />

species and species at risk, as well as a discussion of how populations may be<br />

impacted by the project, which Shell has done. As part of this impact assessment,<br />

the TOR specifically asks for a description of existing wildlife resources, and as<br />

part of that description, Shell is required to discuss current field data. In EIA,<br />

Volume 5, Section 7.3.4, Shell has provided a discussion of current field data<br />

through the use of indicator species. Nothing in the TOR expressly precludes the<br />

use of wildlife indicator species and, in fact, the use of wildlife indicators in<br />

assessing impacts on wildlife, including endangered species and species at risk, is<br />

a recognized protocol, and was recently considered by the Joint Review Panel<br />

reviewing the Mackenzie Gas <strong>Project</strong> application. The Panel found that the use of<br />

indicator or surrogate species for the assessment of other species, including<br />

SARA-listed species, was an acceptable method of impact assessment and<br />

provided sufficient evidence to enable the Panel to review the potential impacts.<br />

Shell has conducted the appropriate studies for the indicator species in<br />

compliance with the TOR and that information is appropriate for assessing the<br />

impacts on listed species. Accordingly, the studies conducted for the<br />

environmental assessment and the information contained in the EIA comply with<br />

both the TOR and the federal statutes.<br />

However, although Shell’s EIA provides sufficient data to assess the potential<br />

impacts to all relevant species, including SARA-listed species, Shell has<br />

proposed a wildlife monitoring program for the pre-development, operation and<br />

reclamation phases of the project, which will be developed in consultation with<br />

ASRD as described in EIA, Volume 5, Appendix 5-6, Section 6. During the<br />

13-24 Shell Canada Limited April 2010<br />

CR029

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