NEPA--Environmental Assessment
NEPA--Environmental Assessment
NEPA--Environmental Assessment
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CUMULATIVE IMPACTS<br />
Global warming is a contentious issue with a great deal of uncertainty about what likely outcomes<br />
might be. However, there is little doubt that plants and animals found almost exclusively in the<br />
alpine zone may be the first to decline or go extinct as a result of changes in global climate. Most<br />
predictions about global climate change predict a gradual loss of alpine habitats as treeline moves<br />
upward in response to a generally warming climate. For white-tailed ptarmigan, the effects of global<br />
warming have the potential to have far greater consequences than the combined effects of grazing,<br />
recreation, mining, and other human impacts. As such, global climate change may be the most<br />
serious threat to long-term persistence of ptarmigan populations in the Silverton landscape.<br />
More immediate and localized threats to alpine species, including ptarmigan, wolverine, and bighorn<br />
sheep, include mining, water development, and motorized and non-motorized recreation. While<br />
alpine ecosystems are hardy and resilient to natural environmental factors, they are particularly<br />
vulnerable to human related disturbances and may require decades to recover. Although substantial<br />
progress has been made in developing techniques to restore damaged alpine landscapes, this<br />
technology is still not capable of restoring alpine plant communities to their pre-disturbance<br />
condition (Hoffman 2006).<br />
One of the largest impacts on the environment in this landscape has been past mining activities and<br />
other activities associated with mining, such as road building (see watershed section above). One<br />
hundred years of surface and subsurface mining operations have likely contributed to substantial<br />
cumulative effects to habitat for sensitive. Some of the impacts of past mining activities have been<br />
reduced or mitigated through natural re-vegetation of formerly impacted areas, and substantial<br />
improvements in downstream water quality have been achieved as abandoned mines have been<br />
reclaimed. Bighorn sheep populations around active mining areas were likely heavily impacted by<br />
miners hunting for food before hunting restrictions were adopted in the early 1900’s.<br />
The Colorado Division of Wildlife (CDOW) continues to manage the S33 Pole Mountain/Upper<br />
Lake Fork bighorn sheep herd for possibility of providing hunting opportunities. Between 1982 and<br />
1990 CDOW issued between 2 and 5 ram tags annually. S33 was closed to hunting between 1991<br />
and 2005, then re-opened in 2006 with 3 ram tags issued annually since then. Hunting success rate<br />
averages 30% for this unit (Diamond 2005). No ewe licenses have ever been issued for this herd.<br />
The CDOW opened S71 for hunting for the first time in 2007 with 1 ram tag issued annually.<br />
As the number of off-highway vehicles (OHV’s) continues to increase on most roads in the Silverton<br />
Landscape, the potential for disturbance to bighorn sheep using areas that are adjacent to popular<br />
OHV routes also continues to increase each year. The continual annual increase in OHV use<br />
observed over the past 5-10 years is likely to continue for the foreseeable future. Increased<br />
motorized disturbance to bighorn sheep in places such as Minnie Gulch may force animals away<br />
from preferred foraging areas and into areas with lower quality forage or areas where animals are<br />
more vulnerable to predation, leading to increased predation or mortality.<br />
White-tailed ptarmigan populations in the southwest Colorado ore belt, roughly between Telluride,<br />
Silverton and Lake City, including most of the Silverton Landscape, are thought to not be self<br />
sustaining. The cause of low ptarmigan populations appears to be cadmium toxicity induced renal<br />
failure and brittle bones that significantly reduces adult female over-winter survivorship (Larison et<br />
al. 2000). Cadmium naturally occurs in high concentrations in the Colorado ore belt and is readily<br />
mobilized by mining. Cadmium is taken up by willows and biomagnified in the buds which are the<br />
primary fall and winter food source for ptarmigan (Braun et al. 1976). Larison et al. (2000) found<br />
adult female survivorship in the southwest Colorado ore belt was reduced by more than half causing<br />
highly skewed sex ratios and low productivity. They also documented high rates of immigration<br />
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