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Pierre River Mine Project

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TERRESTRIAL AENV SIRS 44 – 78<br />

References<br />

Question No. 78<br />

Section 13.1<br />

Accordingly, if Mike Russell’s RSF model were to be implemented in this<br />

assessment, it is very unlikely that the model would result in a change to the<br />

environmental consequence for the effect of the project on barred owl habitat.<br />

First, proximity to disturbance would likely have little effect on model output<br />

(Russell 2010, pers. comm.). Second, avoidance of disturbed areas in the model<br />

is likely a reflection of the landscape in which the model was developed. Data for<br />

model development was collected in an agricultural landscape with large open<br />

fields (Russell 2008). Barred owls were likely avoiding open fields because such<br />

areas have relatively high densities of great horned owls, which are predators of<br />

barred owls (Russell 2008). In contrast, industrial disturbances created by the<br />

project are unlikely to result in productive foraging habitat for great horned owls.<br />

Therefore, barred owls may avoid edges created by industrial disturbance less<br />

than they avoid edges created by agricultural or forestry activity.<br />

Russell, M.S. 2008. Habitat selection of barred owls (Strix varia) across multiple<br />

spatial scales in a boreal agricultural landscape in north-central Alberta.<br />

M.Sc. Thesis. University of Alberta, Edmonton.<br />

Personal Communication. Russell, M. 2010. Telephone communication with<br />

Brock Simons (Golder Associates Ltd.). January 13, 2010.<br />

Personal Communication. Russell, M. 2009. Email communication with Brock<br />

Simons (Golder Associates Ltd.). November 2, 2009.<br />

Request Volume 2, SIR 486-490, Page 23-188.<br />

Shell states that formal validation of HSI models through additional data<br />

collection is unnecessary to adequately characterize the impacts of the project.<br />

Models are simply tools and without data to support an HSI for species where<br />

habitat use knowledge is limited, confidence in the impacts predictions are<br />

necessarily suspect.<br />

78a How does Shell support its impact predictions for indicators where the HSI is<br />

unvalidated and there are insufficient data to assess whether the model is<br />

predicting appropriately?<br />

Response 78a Data for black bear, beaver and yellow rail are not available. Therefore, the<br />

habitat suitability index (HSI) models for these species could not be validated<br />

with empirical data. However, as rational, explicit expressions of the well<br />

understood habitat associations for these species, these expert-based HSI models<br />

have been conceptually validated and are therefore useful assessment tools.<br />

Validation of habitat suitability models with empirical data may be performed<br />

13-74 Shell Canada Limited April 2010<br />

CR029

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