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

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

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Gold Canyon Resources Inc: Final Environmental Study Report Review March 30, 2013 Recommendation: The OMNR needs to investigate the safety of the Wenasaga road, and determine the large truck allowance for the seasonal corridor. 5.2.1 Study Area Dimensions The below terminology is used throughout the GCU ESR and Technical Reports to describe the areas in which field work or desk-top surveys were conducted. For each Technical Report, and depending on what was being assessed, study area dimensions differ. Despite the fact that there are varied study areas, the same terminology is used throughout all ESR documents to describe these areas. The maps provided by GCU to depict where the study areas are located are of poor quality and have low resolution, limiting ones ability to actually read any land base descriptions. Study Area Terminology Used: Regional study area Local study area Study site Springpole study area - general Throughout the ESR and Technical Reports there is one reference to the actual amount of land surveyed for wildlife: It was stated that 81 km 2 was surveyed during the aerial wildlife fieldwork study (Draft Springpole Terrestrial Baseline Report 2011 What is not discussed are the specific land quantums for any of the above listed “study areas”, nor rationale to justify/explain the why the area and amount of land was selected. In most cases, the field study work was conducted in overlapping locations within 1km of the primary Springpole camp site, a location which the drills operate 24 hours a day. After review of the study areas used by GCU, it appears as though only small local study areas were selected from within the Springpole study area in order to dilute the impact of potential findings to make them appear insignificant. Furthermore, the location of all the local study areas used to for the baseline studies, are located nowhere near the intended corridor. Recommendation: GCU needs to explicitly define each study area used within all baseline technical reports for which fieldwork and desktop analysis was conducted in, and indicate within the ESR where exactly the baseline studies were conducted in relation to the eastern corridor. Recommendation: GCU needs to conduct a Class D Environmental Assessment specific for the eastern corridor. 18

Gold Canyon Resources Inc: Final Environmental Study Report Review March 30, 2013 5.2.2 Eastern Corridor Dimensions Throughout the ESR there is little discussion of the actual dimensions to be used for the anticipated corridor. There is reference to the road having dimensions appropriate for a forestry road, however they are not specified. Only after requesting the information from GCU, did they indicate that the corridor would be 15 m wide by 43 km in length, equalling 645 km 2 in total area to be cleared. It was not stated within the ESR nor Technical Reports, on the true extent of land to be cleared by GCU for the corridor. It was stated that a 500 m buffer zone was used to determine corridor impact to large furbearers; woodland caribou, however it is not clear if this same buffer zone was applied for other wildlife calculations. Recommendation: GCU needs to clearly identify eastern corridor dimensions in all GCU eastern corridor related documents, stating that 645 km 2 of land needs to be cleared for the project. Recommendation: GCU needs to provide an explanation for how the impact/buffer zone area was determined. 5.3 Terrestrial Baseline Report Deficiencies The terrestrial baseline studies conducted were intended to assess a limited area within the broader Springpole study area, and do not reflect the true environmental conditions. Baseline studies are designed to establish what environmental parameters currently exist in the area, without industrial pressure, so as to determine the degree of impact that the intended industrial activity will introduce. The bulk of terrestrial baseline field-work studies were conducted within roughly a 3 km radius of the primary Springpole campsite. The primary Springpole campsite is an area of high anthropogenic activity and noise, causing it to be a site of environmental disturbance. Conducting baseline environmental assessments for wildlife in an area with noisy industrial activity, would predisposed the study to finding little wildlife in the area: at the outset of the studies, there is already experimental bias introduced. The methodology employed for all studies lacks scientific significance and statistical analysis: many were only conducted only once, and in an area not reflective of the eastern corridor. Therefore, the ESR is misleading in presenting that there will be minimal impact to wildlife, as the baseline studies were biased, and fraught with defects as highlighted in the corresponding sections below. In some instances, the desktop analysis conducted for the entirety of the regional project study area, used outdated database information. 19

<strong>Gold</strong> <strong>Canyon</strong> Resources Inc: <strong>Final</strong> <strong>Environmental</strong> <strong>Study</strong> <strong>Report</strong> Review<br />

March 30, 2013<br />

5.2.2 Eastern Corridor Dimensions<br />

Throughout the ESR there is little discussion of the actual dimensions to be used for the<br />

anticipated corridor. There is reference to the road having dimensions appropriate for a<br />

forestry road, however they are not specified.<br />

Only after requesting the information from GCU, did they indicate that the corridor would<br />

be 15 m wide by 43 km in length, equalling 645 km 2 in total area to be cleared. It was<br />

not stated within the ESR nor Technical <strong>Report</strong>s, on the true extent of land to be cleared by<br />

GCU for the corridor.<br />

It was stated that a 500 m buffer zone was used to determine corridor impact to large<br />

furbearers; woodland caribou, however it is not clear if this same buffer zone was applied<br />

for other wildlife calculations.<br />

Recommendation: GCU needs to clearly identify eastern corridor dimensions in all GCU<br />

eastern corridor related documents, stating that 645 km 2 of land needs to be cleared for the<br />

project.<br />

Recommendation: GCU needs to provide an explanation for how the impact/buffer zone<br />

area was determined.<br />

5.3 Terrestrial Baseline <strong>Report</strong> Deficiencies<br />

The terrestrial baseline studies conducted were intended to assess a limited area within<br />

the broader Springpole study area, and do not reflect the true environmental conditions.<br />

Baseline studies are designed to establish what environmental parameters currently exist<br />

in the area, without industrial pressure, so as to determine the degree of impact that the<br />

intended industrial activity will introduce.<br />

The bulk of terrestrial baseline field-work studies were conducted within roughly a 3 km<br />

radius of the primary Springpole campsite. The primary Springpole campsite is an area of<br />

high anthropogenic activity and noise, causing it to be a site of environmental disturbance.<br />

Conducting baseline environmental assessments for wildlife in an area with noisy<br />

industrial activity, would predisposed the study to finding little wildlife in the area:<br />

at the outset of the studies, there is already experimental bias introduced.<br />

The methodology employed for all studies lacks scientific significance and statistical<br />

analysis: many were only conducted only once, and in an area not reflective of the eastern<br />

corridor. Therefore, the ESR is misleading in presenting that there will be minimal impact<br />

to wildlife, as the baseline studies were biased, and fraught with defects as highlighted in<br />

the corresponding sections below.<br />

In some instances, the desktop analysis conducted for the entirety of the regional<br />

project study area, used outdated database information.<br />

19

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