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 ...
Gold Canyon Resources Inc. Springpole Gold Project Road Alternatives Assessment Environmental Effects and Mitigation Literature suggests that linear corridors (e.g. roads, transmission lines, seismic lines, etc) can have an adverse effect on caribou populations (Leblond et al. 2011, Weir et al 2006, James and Stuart-Smith 2000), as they facilitate access to caribou habitat by predators, which in turn increases predation. Caribou have exhibited avoidance of linear developments resulting in the functional loss of suitable habitat (Latham et al. 2011). Wolves in particular are known to use linear corridors in order to increase their access to prey populations (Latham et al. 2011). Caribou Collar Data An investigation of caribou use of the landscape was completed through an analysis of caribou collar data provided by the MNR in order to help determine the potential impacts to caribou and caribou habitat, mitigation and avoidance strategies and the resulting residual impacts that would cause the need for an Overall Benefits permit. Collar locations were separated into 5 seasons as determined by Ferguson and Elkie (2004) (Table 3.5.1). After the collar location data were separated into seasons, an investigation was conducted in order to determine what areas of the proposed road corridor had the potential to cause negative environmental effects to caribou. Table 3.5.1 Dates of caribou seasonal movement patterns for analysis (from Ferguson and Elkie 2004). Season Date Range 1 (Late Winter) January 21 - March 5 2 (Spring) March 6 - May 6 3 (Calving) May 7 - July 14 4 ( Post-calving) July 15 - November 14 5 (Early Winter) November 15 - January 20 The area around Springpole Lake has been recognized as a caribou wintering area, as well as an area which has provided caribou calving locations in the past. The determination of this use by caribou was derived from a combination of visual observations as well as caribou collar locations. Historical visual observations were made primarily in relation to wintering activity due to the fact that caribou and caribou tracks are more visible during the winter months. Recent GPS collar location data has revealed areas of seasonal use by caribou within the past year. In a landscape scale context, none of the collared caribou were found in close proximity to the potential road corridors during winter (early and/or late winter), but were found throughout the proposed road corridor area during spring, calving and post-calving. The OMNR has also observed caribou on the western side of Durkin Lake in the winter. Late Winter The area to the north of the eastern arm of Springpole Lake, and immediately south of Springpole Lake are considered caribou wintering areas, as evidenced by the historical sightings of caribou during the winter. The current functionality of this area to provide winter
Gold Canyon Resources Inc. Springpole Gold Project Road Alternatives Assessment habitat is questionable based on the fact that a large fire burned this area in 2011. According to the caribou collar data, none of the collared caribou used this area during late winter, but some animals did use the fringe of the burned area in early winter following the fire of 2011. At least four of the collared animals congregated in a wintering area between Okanse Lake and Perrigo Lake. Caribou also spent late winter east of Fawcett Lake and west of Snelgrove Lake. The construction of road Option A is not expected to have any negative environmental effect on any of these late wintering areas. Spring During the spring season, the collared caribou disbursed throughout the study area and were found in a wide variety of habitat types including the area burned in 2011. Of the collared animals in the study area, 3 were located in close proximity (5 km) to the proposed road Option A. One collared animal was found in the Dead Dog Lake area, another on the north and south shores of the eastern end of Springpole arm, and a third animal was found between Springpole Lake and Dole Lake near the Springpole camp. The construction of Road Option A could negatively affect caribou in two ways; through sensory disturbance; and increased predation risk. Sensory disturbance will be mitigated by enforcing strict timing restrictions on the use of the road during the spring period. For the most part, traffic will be eliminated during spring, with the exception of medical or other emergency use. Predation by wolves and black bears is considered to be the proximate cause of caribou mortality, particularly on calves (Lambert et al. 2006), with the majority of mortality events occurring in late winter. In order to reduce predation risk to caribou, alternate prey populations in the area need to be kept to a minimum. Wolves are known to be moose specialists, taking caribou opportunistically, therefore, by reducing favourable habitat for moose in an area, the likelihood of increased predation risk for caribou should be lowered. Moose populations will be kept to a minimum by reducing the amount of area converted to early successional vegetation and developing a vegetation management plan for the road corridor in consultation with the OMNR. Calving/Post-calving Caribou calving and post-calving seasons are considered critical times for caribou as calves can be highly susceptible to predation and maternal females can exhibit a lower tolerance for disturbance than other times of the year. The caribou collar data for the study area clearly shows animals disbursing from each other and spacing out during calving. With regard to the proposed road corridor (Option A), two collared animals spent the calving season in close proximity, with one female splitting the calving season between Dead Dog Lake and Fawcett Lake, and another female spending the calving season on the south and north shores of the eastern arm of Springpole Lake. Long-term, objective studies of the effects of development on calving caribou are rare due to the difficulty of obtaining data, costs and long timelines required to fully understand potential effects. In one study of a caribou calving ground in Alaska (Dau and Cameron 1986), the number of
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- Page 177 and 178: APPENDIX 5 FIELD REPORT FROM DST (D
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- Page 184 and 185: APPENDIX 7 7A: WATER CROSSINGS ENGI
- Page 186 and 187: The 25-year flood (Q 25 ), determin
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- Page 192 and 193: Table 2 - Water Crossing Hydrology
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<strong>Gold</strong> <strong>Canyon</strong> Resources Inc.<br />
Springpole <strong>Gold</strong> Project<br />
Road Alternatives Assessment<br />
habitat is questionable based on the fact that a large fire burned this area in 2011. According to<br />
the caribou collar data, none of the collared caribou used this area during late winter, but some<br />
animals did use the fringe of the burned area in early winter following the fire of 2011. At least<br />
four of the collared animals congregated in a wintering area between Okanse Lake and Perrigo<br />
Lake. Caribou also spent late winter east of Fawcett Lake and west of Snelgrove Lake. The<br />
construction of road Option A is not expected to have any negative environmental effect on any<br />
of these late wintering areas.<br />
Spring<br />
During the spring season, the collared caribou disbursed throughout the study area and were<br />
found in a wide variety of habitat types including the area burned in 2011. Of the collared<br />
animals in the study area, 3 were located in close proximity (5 km) to the proposed road Option<br />
A. One collared animal was found in the Dead Dog Lake area, another on the north and south<br />
shores of the eastern end of Springpole arm, and a third animal was found between Springpole<br />
Lake and Dole Lake near the Springpole camp.<br />
The construction of Road Option A could negatively affect caribou in two ways; through sensory<br />
disturbance; and increased predation risk. Sensory disturbance will be mitigated by enforcing<br />
strict timing restrictions on the use of the road during the spring period. For the most part, traffic<br />
will be eliminated during spring, with the exception of medical or other emergency use.<br />
Predation by wolves and black bears is considered to be the proximate cause of caribou<br />
mortality, particularly on calves (Lambert et al. 2006), with the majority of mortality events<br />
occurring in late winter. In order to reduce predation risk to caribou, alternate prey populations in<br />
the area need to be kept to a minimum. Wolves are known to be moose specialists, taking<br />
caribou opportunistically, therefore, by reducing favourable habitat for moose in an area, the<br />
likelihood of increased predation risk for caribou should be lowered. Moose populations will be<br />
kept to a minimum by reducing the amount of area converted to early successional vegetation<br />
and developing a vegetation management plan for the road corridor in consultation with the<br />
OMNR.<br />
Calving/Post-calving<br />
Caribou calving and post-calving seasons are considered critical times for caribou as calves can<br />
be highly susceptible to predation and maternal females can exhibit a lower tolerance for<br />
disturbance than other times of the year. The caribou collar data for the study area clearly<br />
shows animals disbursing from each other and spacing out during calving. With regard to the<br />
proposed road corridor (Option A), two collared animals spent the calving season in close<br />
proximity, with one female splitting the calving season between Dead Dog Lake and Fawcett<br />
Lake, and another female spending the calving season on the south and north shores of the<br />
eastern arm of Springpole Lake.<br />
Long-term, objective studies of the effects of development on calving caribou are rare due to the<br />
difficulty of obtaining data, costs and long timelines required to fully understand potential effects.<br />
In one study of a caribou calving ground in Alaska (Dau and Cameron 1986), the number of