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Pierre River Mine Project

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WATER AENV SIRS 15 – 43<br />

Reference<br />

Section 12.1<br />

Aquatic plants and algae are recognized as important features of the aquatic<br />

ecosystem, and as such, have been proposed as components of the conceptual<br />

monitoring plan for lakes (see EIA, Volume 4B, Aquatic Resources Appendices,<br />

Appendix 4-9, Section 5.2.5.1 and Section 5.2.5.2). For stream monitoring, the<br />

presence of submergent vegetation and percent of instream cover are common<br />

variables used for habitat suitability index (HSI) models for most species present<br />

within the project area and have been included in the Jackpine <strong>Mine</strong> – Phase 1<br />

monitoring program to support the validation of the HSI models. However, in the<br />

typical stream habitat in the project area, the scientific literature indicates that<br />

allochthonous organic carbon inputs from riparian vegetation and bogs is the<br />

largest component of the organic matter inputs and strongly affects the character<br />

of the heterotrophic food chain. For example, Jonsson et al. (2006) found that<br />

aquatic primary production was an insignificant input of organic carbon relative<br />

to terrestrial organic carbon in the aquatic environment in boreal forest in<br />

Sweden. The use of algae and aquatic plants as a separate KIR (outside of the<br />

consideration of fish habitat) for the purpose of completing the EIA was not<br />

considered necessary for assessing project-related effects on fish and fish habitat.<br />

Further details on monitoring aquatic plants will be developed in consultation<br />

with regulators and stakeholders in the development of the detailed NNLP<br />

compensation monitoring program.<br />

Jonsson, A., G. Algesten, A.-K. Bergstrom, K Bishop, S. Sobek, L.J. Tranvik and<br />

M. Jansson. 2006, Integrating aquatic carbon fluxes in a boreal<br />

catchment carbon budget. J Hydrology 334:141-150.<br />

Request 41c Provide a list of appropriate KIR’s for non-fish bearing shallow lakes and<br />

wetlands including plant and animal species.<br />

Response 41c Wetlands, such as bogs, fens and marshes, were assessed as part of the Terrestrial<br />

Resources Assessment (EIA, Volume 5, Section 7.5.1, 7.5.2 and 7.5.3). The key<br />

indicator resource (KIR) selection process for terrestrial resources is described in<br />

the EIA, Volume 5, Section 7.6.7.2; this assessment considers wetlands,<br />

vegetation and wildlife resources. Wetland KIRs include peatlands (fens and<br />

bogs), patterned fens, rare and special plant communities (i.e., lenticular<br />

patterned fen) and riparian communities, as they are associated with wetlands in<br />

many cases. Wildlife KIRs associated with wetlands include Canadian toad,<br />

yellow rail and beaver. The KIRs for shallow, non-fish bearing lakes would<br />

include benthic invertebrates and their habitat.<br />

12-62 Shell Canada Limited April 2010<br />

CR029

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