Environmental Assessment
Environmental Assessment
Environmental Assessment
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AFFECTED ENVIRONMENT & ENVIRONMENTAL CONSEQUENCES CHAPTER 3<br />
accumulate. These accumulations can result in morality of trees that would usually not be killed by low<br />
to moderate intensity fire events. The buildup at the base of trees can result in fire starts that burn with<br />
such intensity that root systems are damaged and the tree cambium destroyed thus killing the tree.<br />
Nearly all existing old growth stands contain continuous vertical fuels; wildfires in such stands would<br />
result in crown fires and subsequent mortality. The height from the ground to the base of the live crown<br />
would remain between five (5) and 31 feet. This would maintain the risk of a surface fire climbing into<br />
the canopy and becoming a crown fire. Tree crowns would also be closer together allowing a crown fire<br />
to spread more easily at lower wind speeds. Crown fires would also increase mortality levels.<br />
In mixed pine stands (lodgepole and ponderosa), similar fuel accumulations and conditions would<br />
continue to exist. Dense lodgepole pine regeneration would continue to create undesirable stand densities<br />
(ladder fuels) that pose continuing and increasing risks to the survival of the larger ponderosa pine during<br />
a wildfire event.<br />
The effects of uncharacteristic wildfire on forest health, wildlife habitat, soils, water quality and<br />
recreational values and as well as the safety of firefighters and the public, would continue to increase. No<br />
safety corridors would be established along Roads 18, 2017, 23, 25, or 2510. Fuels would continue to<br />
accumulate adjacent to or near high use/value special use developments and recreational use areas such as<br />
the Pine Mountain Observatory, the BPA Sand Springs compensation station, and the EFR OHV trail<br />
system.<br />
The risk of wildfire with the potential for loss of critical mule deer winter forage and both hiding and<br />
thermal cover would remain high and increase over time under this alternative. It would forgo the<br />
opportunity to reduce the risk of wildfire occurring in big game hiding and thermal cover which is at high<br />
risk of loss in the event of wildfire. Additionally, uncharacteristic wildfire would also likely result in<br />
habitat losses within OGMA areas as well as the loss of wildlife habitat associated with old growth<br />
ponderosa pine.<br />
Continued transition to an infrequent and intense fire regime would occur in fire dependent ecosystems<br />
that historically experienced frequent, low intensity fire events. In these areas, fire starts that escape<br />
initial suppression action would cycle a high portion of the landscape to an early seral stage. This<br />
includes most of the planning area except areas dominated by lodgepole pine.<br />
No natural fuel reduction activities would be implemented under Alternative 1 and the risk to important<br />
resources and resource values would continue and would increase over time with increasing fuel loadings.<br />
Suppression actions would continue to be hazardous for firefighters. Suppression options would be<br />
eliminated due to lack of escape routes and safety zones. Fireline intensity would prevent direct attack<br />
with ground forces. The effectiveness of aerial delivered retardants would be limited due to long range<br />
spotting. Dozer rather than hand line construction would be necessary due to fire intensity. Public safety<br />
would be compromised due to limited evacuation routes.<br />
The increased risk and probability of a high intensity, uncharacteristic wildfire associated with increasing<br />
fuel loadings would result in the increasing likelihood of the complete lost of understory and overstory<br />
vegetation. Large contiguous areas of dense shrubs, needle cast and grasses have developed in the<br />
absence of the low intensity wildfire historically characteristic of the planning area. These highly<br />
flammable shrubs have the potential for flame lengths of up to 20 to 30 feet. With existing shrub<br />
conditions, the potential exists for fire spread into the canopy of trees allowing for high intensity, stand<br />
replacement crown fire. Although past fuel treatments (i.e. mechanical shrub treatments, mowing, and<br />
prescribed fire) have occurred in the planning area, large contiguous areas of dense shrubs remain.<br />
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