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severity areas, due to conditions favorable to accelerated growth and reproduction, and release <br />from competition with native plant communities. In addition, the unintentional introduction and <br />dispersal of invasive weeds into areas disturbed by fire suppression and rehabilitation has the <br />potential to establish persistent weed populations. It is expected that most native vegetation will <br />recover if weed invasions are minimized. <br />There is an emergency situation for the recovery of native <br />vegetation due to significant threats from noxious weed <br />establishment and/or spread affecting natural plant community <br />integrity, wildlife habitats, and watershed values. <br />Wildlife: Critical Habitat or Suitable Occupied Habitat <br />The fire appears to have resulted in minor consequences to Preble's critical habitat and other <br />suitable Preble's habitat. As described above, the majority of riparian vegetation within Preble's <br />habitat appears to have been unburned or lightly burned by the fire. Additionally, where riparian <br />herbaceous or shrub vegetation was moderately burned or killed, this vegetation should grow <br />back within about 1 to 3 years approximately. This also should be the case for herbaceous and <br />shrub vegetation in the adjacent upland Preble's habitat zone as well. Some riparian vegetation <br />may be covered by ash and sediment during flood events, but this would be a fairly temporary <br />condition not resulting in long -term impacts to Preble's habitat. On private lands any proposed <br />treatments that could have an adverse effect on Preble's habitat will go through the proper federal <br />and/or state review process before treatments are implemented. <br />For the mapped lynx habitat, the majority of this forest area was killed by crown fire. This forest <br />habitat will take a few to several decades to grow back to a condition where it may provide <br />suitable lynx habitat. However, as described in the wildlife report, it's questionable how much of <br />this area actually provided suitable lynx habitat because it is likely that much of it was dry lodge <br />pole pine or single -story lodge pole that lacked dense horizontal cover, which is a key component <br />for lynx habitat. Also, the polygon of mapped lynx habitat was isolated by lower elevation <br />unsuitable habitat from the main body of both the Poudre and Estes LAUs. Crown fire in this type <br />of ecosystem is a natural disturbance process that ultimately provides different age classes of <br />forest for lynx habitat. <br />Based on the discussion presented above, it is determined that <br />there is no emergency for either Preble's or lynx habitat within <br />the High Park Fire area. <br />Fisheries <br />The streams that will see potential adverse impacts from post fire run -off events associated with <br />thunderstorm and overland flow events identified during the BAER process were: main stem <br />Cache La Poudre River, South Fork Cache La Poudre River, Buckhorn Creek, Bennett Creek, <br />and Young Gulch. We anticipate adverse post -fire effects to alter aquatic habitats and disrupt <br />aquatic life for three to five years. Recovery of aquatic ecosystems will occur as erosion rates <br />diminish and flushing flows route fire contrived fine sediment from main channels. <br />Because there are no fish that are threatened or endangered <br />found in the area within the fire boundary or directly downstream <br />that would experience adverse post fire effects, there is no <br />emergency determination for fisheries. Similarly, as the Arapaho <br />Snow fly is only a species under consideration for listing and not <br />an officially listed species, there is not an emergency <br />determination. <br />High Park Fire Emergency Stabilization Plan Page 14 <br />