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From: on behalf of Panel Registry Subject: FW: TNG registration of ...

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In sum, the combinati<strong>on</strong> <strong>of</strong> beetle kill and forest fires will be the most significant impact from<br />

climate change to be addressed in the XGCA. The Canadian Forest Service predicts that 80 percent<br />

<strong>of</strong> the pine will be infected with beetle kill by 2012 (see Box 2). As a result, not <strong>on</strong>ly will the forest<br />

fire<br />

hazard increase in terms <strong>of</strong> frequency, but more intense fires are projected as well (see Box 3).<br />

In<br />

additi<strong>on</strong>,<br />

the main specific impacts <strong>on</strong> the forest and vegetati<strong>on</strong> will likely be:<br />

• Pine, subalpine fir will no l<strong>on</strong>ger be well suited to the XGCA envir<strong>on</strong>ment<br />

• Aspen presence will likely decline, but will remain <strong>on</strong> moister slopes and draws<br />

• Douglas‐fir, and many P<strong>on</strong>derosa Pine <strong>on</strong> dry sites,<br />

may be more successful, due to changes<br />

in frost c<strong>on</strong>diti<strong>on</strong>s<br />

• There will be more grasslands <strong>on</strong> marginal sites<br />

• Invasive species, such as knapweed, will increase<br />

• While some culturally important plants will decrease, others might actually increase within<br />

the XGCA, such as the Soopolsllie and Choke Cherry, as areas get drier and warmer.<br />

Interior Douglas­fir (IDF) z<strong>on</strong>e<br />

The IDF z<strong>on</strong>e is characterized by warm dry summers and cool dry winters. It comprises about 22%<br />

<strong>of</strong> the forested areas <strong>of</strong> the study area (Figure 2). Two IDF subz<strong>on</strong>es occur in the study area ‐ the<br />

IDFdk4 (dry cool) and IDFdw (dry warm). The IDFdk4 occurs in the Nemiah, Elkin, Taseko River<br />

and Lower Chilko River Valleys. It also occurs as a wide crescent shape band from Cheolquoit Lake<br />

to Tatla Hill within the North Trapline area. The elevati<strong>on</strong> range is from about 950 to 1200m.<br />

Climax stands <strong>on</strong> z<strong>on</strong>al (mesic) sites typically have multi‐aged Douglas‐fir canopy with abundant<br />

regenerati<strong>on</strong>. Dominant seral species include lodgepole pine, trembling aspen willow ad rose. Cold<br />

air accumulati<strong>on</strong> areas have lodgepole pine forests similar to those <strong>on</strong> z<strong>on</strong>al sites in the Sub Boreal<br />

Pine Spruce xc (very dry cold). Drier sites are dominated by Douglas‐fir, comm<strong>on</strong> and Rocky<br />

Mountain<br />

juniper, bluebunch wheatgrass, Rocky Mountain fescue and lichens, while moister sites<br />

have hybrid white spruce, black twinberry, palmate colt’s foot and comm<strong>on</strong> horsetail.<br />

The IDFdw subz<strong>on</strong>e occurs at low elevati<strong>on</strong>s al<strong>on</strong>g the Chilko and Tatlayoko Lakes. Due to the<br />

influence <strong>of</strong> coastal air masses, the IDFdw has a warmer moister climate relative to most other<br />

parts <strong>of</strong> the IDF z<strong>on</strong>e in the Cariboo Chilcotin. Climax stands are dominated by multi‐aged Douglas‐<br />

fir and pine grass, with some lodgepole pine and the occasi<strong>on</strong>al subalpine fir, while moist areas<br />

have hybrid spruce.<br />

Climate impacts: Climate change will result in hotter and drier summers, warmer winters with<br />

less snow and more rain in the fall and winter in both the IDFdw and IDFdk4. Lower elevati<strong>on</strong>s and<br />

southern exposures will experience greater drought stress with associated reducti<strong>on</strong>s in tree vigor<br />

and increases in mortality. On northern and moister sites, there will be stands <strong>of</strong> Douglas‐fir with<br />

scattered<br />

openings from pine and possibly spruce mortality. Fire is a c<strong>on</strong>cern in the remaining<br />

lodgepole pine stands in the near term.<br />

These subz<strong>on</strong>es will become much less suited to growing lodgepole pine. Increased drought stress<br />

will lower vigour and increase susceptibility to western gall rust, terminal weevil, dwarf mistletoe<br />

and possibly bark beetles. This increased mortality al<strong>on</strong>g with warmer summers will create a high<br />

risk <strong>of</strong> large intense fires. 54 Lodgepole pine established <strong>on</strong> cooler aspects will have a better chance<br />

<strong>of</strong> survival. Douglas‐fir, P<strong>on</strong>derosa<br />

pine and spruce should be well adapted up to 2050; however the<br />

KFFS ( 2009) indicates that by 2080,<br />

most <strong>of</strong> the lodgepole pine regenerated in the early century<br />

54 KFFS 2009.<br />

35

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