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Revised Final Environmental Study Report (24 MB) - Gold Canyon ...

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<strong>Gold</strong> <strong>Canyon</strong> Resources Inc.<br />

Springpole <strong>Gold</strong> Access Corridor Project<br />

<strong>Final</strong> <strong>Environmental</strong> <strong>Study</strong> <strong>Report</strong><br />

Screening Criteria<br />

Net Effect<br />

Negative (1) Nil Unk<br />

Positive (1)<br />

High Med Low Low Med High<br />

Natural Environment Considerations<br />

Table 2-2: Effects Analysis for Eastern Corridor<br />

Comments and Rationale<br />

Air quality X<br />

Water quality or quantity X<br />

Species at risk or their<br />

habitat<br />

X<br />

Maintain equipment in accordance with manufacturer recommendations. No material impacts associated with the Project (fugitive dust,<br />

emission from combustion equipment).<br />

Road development and installation of water crossings and eventual decommissioning would conform to the MNR and DFO guidance<br />

documents referenced herein, as well as AOC prescriptions in the FMP. Erosion and sediment control plan to be developed and<br />

followed, as per MNR (1995). Post construction FOIP audit and monitoring post construction is planned, as per Section 8. Beyond the<br />

FMP Approved Road, this corridor requires seven (7) water crossings, one of which is a clear span bridge over the Birch River (refer to<br />

Figure 2-1). The FMP Approved Road, which would be constructed by the SFL holder in accordance with the 2009-2019 FMP regardless<br />

of GCU’s activities, requires seven (7) crossings, including a clear span bridge over Dead Dog Creek. Additional engineering details are<br />

provided in Appendix 7, beyond the major water crossings locations that are shown on Figure 2-1.<br />

The access corridor would be a linear development through a caribou range. Based on the Caribou Screening Tool and DST (2012), this<br />

corridor is regarded as having a lesser impact on the range than the western corridor. Refer to DST (2012) in Appendix 4 for discussion<br />

of potential impacts to caribou and wolverine.<br />

Significant earth or life<br />

science features<br />

X None identified to date.<br />

Fish or other aquatic<br />

species, communities or<br />

their habitat (including<br />

movement of resident or<br />

migratory species)<br />

X<br />

Through installation of modern, monitored gates, there should be minimal increased public access to lakes, which would increase fishing<br />

pressure. Road development and installation of water crossings and eventual decommissioning would conform to the MNR and DFO guidance<br />

documents referenced herein, as well as AOC prescriptions in the FMP.<br />

Land subject to natural or<br />

human made hazards<br />

X<br />

None identified to date.<br />

Recovery of a species<br />

under special<br />

management program<br />

X<br />

The access corridor would be a linear development through a caribou range. Based on the Caribou Screening Tool and DST (2012), this<br />

corridor is regarded as having a lesser impact on the range. Refer to DST (2012) in Appendix 4 and DST (2013) in Appendix 5 for<br />

discussion.<br />

Ecological integrity X<br />

The access corridor would be a linear development through an area of historic exploration and would largely follow the 2011 burn area<br />

and area of FMP-approved activities. Refer to DST (2012) for further discussion.<br />

Terrestrial wildlife<br />

(including numbers,<br />

diversity and movement<br />

of resident or migratory<br />

species)<br />

Natural vegetation and<br />

terrestrial habitat linkages<br />

or corridors through<br />

fragmentation, alteration<br />

and/or critical loss<br />

X<br />

X Refer to Section 6.4 for discussion.<br />

Potential for an increase in road mortalities of a variety of terrestrial wildlife species. This threat has the potential for mitigation and is<br />

dependent on the intensity of road use. Refer to DST (2012) for further discussion. The eastern corridor stays outside of the red tail hawk<br />

standard 20m AOC. The road is located within the 100m Critical Breeding AOC (refer to Figure 2-1), as per Table 4.2e of MNR (2010).<br />

Standards and guidelines for common stick-nesting bird nest sites and unknown stick nests (page 82 and 83) because the road will be<br />

constructed outside the critical breeding time for red-tailed hawks.<br />

July 2013 Page 14

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