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Pierre River Mine Project

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TERRESTRIAL AENV SIRS 44 – 78<br />

Western (Boreal) Toad<br />

Wood Bison<br />

Woodland Caribou<br />

Section 13.1<br />

order to quantify the change in total area and proportion of area of each<br />

ecosite phase or wetlands type between Base Case and Closure (see Table<br />

AENV 59-1). Habitat associations of federally-listed species were primarily<br />

derived from direct observations from baseline surveys conducted for the<br />

project from 2005 to 2007 (Wildlife Environmental Setting Report,<br />

Volume 5, Table 5.2-1) or from historic wildlife survey results in the Oil<br />

Sands Region. These associations are equated with ecosite phases and<br />

wetlands types in the LSAs as defined by vegetation mapping produced for<br />

the Terrestrial Vegetation, Wetlands and Forest Resources impact assessment<br />

(Volume 5, Section 7).<br />

Three boreal toads were detected during amphibian surveys conducted within<br />

the LSAs (Terrestrial Environmental Setting Report, Section 5.5.5.1). These<br />

observations occurred in wooded fen (FTNN) and wooded bog (BTNN)<br />

wetlands types. Additionally, historical data from the Oil Sands Region<br />

indicate boreal toads have been detected within a variety of habitat types<br />

(e.g., shrubby fen [FONS], marsh [MONG], lichen jack pine [a1], Labrador<br />

tea-subhygric black spruce-jack pine [g1]; Golder 2000; Canadian Natural<br />

2006; Rio Alto 2002; Table AENV 59-1). Using information from project<br />

surveys and historical surveys, the net gain of habitat types from Base Case<br />

to Closure for western toad is approximately 120 ha (less than 1% of the<br />

LSAs, as shown in Table AENV 59-1).<br />

Two incidental observations of wood bison were recorded within the <strong>Pierre</strong><br />

Rive <strong>Mine</strong> LSA. These observations occurred in lichen jackpine (a1) and<br />

Labrador tea-mesic jack pine–black spruce (c1) ecosite phases (Terrestrial<br />

Environmental Setting Report, Appendix T). Historical survey data on other<br />

habitat associations for wood bison were not available for the Oil Sands<br />

Region. Using information from project surveys, the net gain of habitat types<br />

from Base Case to Closure for wood bison is approximately 4,780 ha (9% of<br />

the LSAs; see Table AENV 59-1).<br />

A single woodland caribou track was recorded during winter tracking<br />

surveys in graminoid fen (FONG) on the Jackpine <strong>Mine</strong> Expansion LSA<br />

(Terrestrial Environmental Setting Report, Section 5.3.1.4). Historical survey<br />

observations for caribou in the Oil Sands Region occur across a wide variety<br />

of upland and wetland habitat types (e.g., wooded fen [FTNN], marsh<br />

[MONG], shrubby fen [FONS], low-bush cranberry aspen-white spruce [d2],<br />

Labrador tea-mesic jack pine-black spruce [c1], Labrador tea-subhygric<br />

black spruce-jack pine [g1], and lichen jack pine [a1]) (MEG 2005; Canadian<br />

Natural 2006; Golder 2003). Using information from project surveys and<br />

historical surveys, the net gain of habitat types from Base Case to Closure for<br />

woodland caribou is approximately 2,795 ha (6% of the LSAs; see Table<br />

AENV 59-1).<br />

13-26 Shell Canada Limited April 2010<br />

CR029

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