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Exotic Tree Species as an Adaptation Option to Climate Change in ...

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Introduction<br />

Under conditions of climate ch<strong>an</strong>ge, ma<strong>in</strong>ta<strong>in</strong><strong>in</strong>g species <strong>an</strong>d<br />

ecosystem diversity <strong>in</strong> the western boreal forest may require<br />

<strong>in</strong>cre<strong>as</strong><strong>in</strong>gly <strong>in</strong>tensive m<strong>an</strong>agement policies. The purpose of<br />

this summary is <strong>to</strong> <strong>as</strong>sess the possibility of <strong>in</strong>troduc<strong>in</strong>g new<br />

tree species <strong>in</strong><strong>to</strong> the western boreal forest <strong>as</strong> <strong>an</strong> adaptation<br />

<strong>to</strong> climate ch<strong>an</strong>ge, <strong>an</strong>d discuss government policies <strong>to</strong><br />

address this issue. The regional focus is on the Boreal Pla<strong>in</strong><br />

Ecozone of M<strong>an</strong>i<strong>to</strong>ba, S<strong>as</strong>katchew<strong>an</strong>, <strong>an</strong>d Alberta. This<br />

region encomp<strong>as</strong>ses the ma<strong>in</strong> are<strong>as</strong> of production forestry <strong>in</strong><br />

these prov<strong>in</strong>ces, but also <strong>in</strong>cludes parks <strong>an</strong>d other protected<br />

are<strong>as</strong>, <strong>as</strong> well <strong>as</strong> are<strong>as</strong> along the southern fr<strong>in</strong>ge of the region<br />

where forest h<strong>as</strong> been cleared for agriculture.<br />

The study looks beyond the Prairie region <strong>to</strong> ga<strong>in</strong> a global<br />

perspective on the benefits of exotic tree species, the threats<br />

posed by these exotics, <strong>an</strong>d methods for <strong>as</strong>sess<strong>in</strong>g their<br />

<strong>in</strong>v<strong>as</strong>iveness. Next is <strong>an</strong> <strong>as</strong>sessment of present <strong>an</strong>d future<br />

climatic suitability for a number of native <strong>an</strong>d non-native<br />

tree species <strong>to</strong> the region under study. Seven non-native<br />

species are exam<strong>in</strong>ed <strong>in</strong> greater detail <strong>to</strong> determ<strong>in</strong>e their<br />

suitability for <strong>in</strong>troduction. F<strong>in</strong>ally, <strong>an</strong> exam<strong>in</strong>ation of<br />

global, federal, <strong>an</strong>d prov<strong>in</strong>cial policies on exotic tree species<br />

provides further context for the development of a new policy<br />

perspective on the issue <strong>an</strong>d policy recommendations.<br />

Rationale for Introduc<strong>in</strong>g <strong>Exotic</strong> <strong>Species</strong><br />

M<strong>an</strong>y re<strong>as</strong>ons exist for <strong>in</strong>troduc<strong>in</strong>g exotic tree species<br />

throughout the world. <strong>Exotic</strong> species provide a number<br />

of benefits <strong>to</strong> forestry <strong>in</strong> particular. In m<strong>an</strong>y c<strong>as</strong>es, exotic<br />

species grow f<strong>as</strong>ter th<strong>an</strong><br />

native species, have greater<br />

seed availability, are more<br />

e<strong>as</strong>ily m<strong>an</strong>aged, <strong>an</strong>d are better<br />

unders<strong>to</strong>od by foresters.<br />

Introduction of exotic trees<br />

c<strong>an</strong> also provide benefits <strong>to</strong><br />

the l<strong>an</strong>d <strong>an</strong>d ecosystems. Their<br />

<strong>in</strong>troduction h<strong>as</strong> frequently<br />

been justified by their value <strong>in</strong><br />

reclamation of disturbed are<strong>as</strong>,<br />

such <strong>as</strong> eroded l<strong>an</strong>ds (Zobel<br />

et al. 1987). F<strong>as</strong>t-grow<strong>in</strong>g<br />

exotic pl<strong>an</strong> tations also tend <strong>to</strong><br />

reduce the need for <strong>in</strong>tensive<br />

m<strong>an</strong>agement of the rema<strong>in</strong><strong>in</strong>g<br />

natural forest (Zobel et al.<br />

1987). It h<strong>as</strong> even been argued<br />

that exotic species c<strong>an</strong> have<br />

positive ecological value by<br />

contribut<strong>in</strong>g <strong>to</strong> the structure<br />

or function of a particular<br />

ecosystem (Williams 1997).<br />

A new rationale for <strong>in</strong>troduction<br />

of exotic trees is their<br />

possible role <strong>in</strong> adaptation <strong>to</strong><br />

climate ch<strong>an</strong>ge. Recent climate<br />

ch<strong>an</strong>ge <strong>as</strong>sessments <strong>in</strong> the Figure 1: Carag<strong>an</strong>a bushes<br />

3<br />

Prairie Prov<strong>in</strong>ces have made the po<strong>in</strong>t that the climate may<br />

become less suitable for native trees <strong>in</strong> some are<strong>as</strong>, lead<strong>in</strong>g<br />

<strong>to</strong> reduced growth, regeneration failure, <strong>an</strong>d gradual loss of<br />

forest cover. Retention of the economic <strong>an</strong>d environmental<br />

values <strong>as</strong>sociated with forest may require <strong>in</strong>troduction of<br />

exotic varieties or species that are adapted <strong>to</strong> the warmer <strong>an</strong>d<br />

drier climate (Thorpe et al. 2001, Henderson et al. 2002).<br />

Williams (1997) argued that exotic pl<strong>an</strong>ts now considered<br />

problematic may turn out <strong>to</strong> have ecological value <strong>in</strong> the<br />

future because of climate ch<strong>an</strong>ge, by fill<strong>in</strong>g the ecological<br />

roles played by native species that have been elim<strong>in</strong>ated.<br />

Threats from Introduc<strong>in</strong>g <strong>Exotic</strong> <strong>Tree</strong> <strong>Species</strong><br />

<strong>Exotic</strong> species c<strong>an</strong> pose a number of threats <strong>to</strong> regions <strong>an</strong>d<br />

ecosystems. Threats of dise<strong>as</strong>e tr<strong>an</strong>smission, genetic crosshybridization,<br />

site degradation, <strong>an</strong>d biodiversity loss have<br />

been documented <strong>in</strong> various regions of the world. Globally<br />

the most import<strong>an</strong>t threat attached <strong>to</strong> the <strong>in</strong>troduction<br />

of exotic pl<strong>an</strong>ts is the potential for <strong>in</strong>v<strong>as</strong>ion of adjacent<br />

ecosystems. While most successful <strong>in</strong>v<strong>as</strong>ions do not alter<br />

large-scale ecosystem processes, some <strong>in</strong>v<strong>as</strong>ions do have<br />

major impacts (Vi<strong>to</strong>usek 1990). This happens <strong>in</strong> situations<br />

<strong>in</strong> which <strong>in</strong>vaders:<br />

• Differ subst<strong>an</strong>tially from natives <strong>in</strong> resource<br />

acquisition or utilization<br />

• Alter the trophic structure of the <strong>in</strong>vaded area<br />

• Alter disturb<strong>an</strong>ce frequency <strong>an</strong>d/or <strong>in</strong>tensity<br />

Depend<strong>in</strong>g on the situation, certa<strong>in</strong> exotics are deemed<br />

<strong>to</strong> be more <strong>in</strong>v<strong>as</strong>ive th<strong>an</strong> others. In C<strong>an</strong>ada, the follow<strong>in</strong>g

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