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Invasiveness Ranking System for Non-Native Plants of Alaska

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Role <strong>of</strong> anthropogenic and natural disturbance in3establishment (0–5)Narrowleaf hawksbeard readily colonizes disturbed sites andopen areas (Densmore et al. 2001, I. Lapina pers obs). However,it has established on river bars in southeast <strong>Alaska</strong> (M. Shephardpers. obs.) and following <strong>for</strong>est fires (Villano 2007).Current global distribution (0–5) 5The present world distribution <strong>of</strong> narrowleaf hawksbeard includesmost <strong>of</strong> Europe, Asia, and North America to the subarctic–arcticzone (Hultén. 1968).Extent <strong>of</strong> the species U.S. range and/or occurrence <strong>of</strong>5<strong>for</strong>mal state or provincial listing (0–5)Narrowleaf hawksbeard is widespread in the northeastern UnitedStates and Canada (Royer and Dickinson 1999, USDA 2002). It islisted as noxious in Minnesota, Alberta, and Manitoba (InvadersDatabase <strong>System</strong> 2003).Total <strong>for</strong> Ecological Amplitude and Distribution 18/25Feasibility <strong>of</strong> ControlScoreSeed banks (0–3)ULongevity <strong>of</strong> seed bank is not documented. Densmore (2001)suggested seed viability <strong>of</strong> 1 year or less.Vegetative regeneration (0–3) 0Narrowleaf hawksbeard does not resprout after abovegroundgrowth is removed (Densmore et al. 2001).Level <strong>of</strong> ef<strong>for</strong>t required (0–4) 3Narrowleaf hawksbeard does not persist without repeatedanthropogenic disturbance in <strong>Alaska</strong>. It is likely that controlcan be accomplished with repeated mechanical or chemicaltreatments. Future monitoring after site eradication is importantas this plant is likely to be reintroduced after it is eradicated(Densmore et al. 2001).Total <strong>for</strong> Feasibility <strong>of</strong> Control 3/7Total score <strong>for</strong> 4 sections 47/87§Crupina vulgaris Cass.<strong>Ranking</strong> SummaryEcoregion known or expected to occur inSouth CoastalInterior BorealArctic AlpinePotential Max.Ecological ImpactBiological Characteristics and DispersalAmplitude and DistributionFeasibility <strong>of</strong> ControlRelative MaximumRejected from considerationClimatic ComparisonCollected in<strong>Alaska</strong> regions?common names: common crupina, bearded creeperNoNoNoScoreCLIMEXsimilarity?South CoastalInterior BorealArctic AlpineCrupina vulgaris has not been collected in <strong>Alaska</strong> (Hultén 1968,Welsh 1974, AKEPIC 2004, UAM 2004). The native population<strong>of</strong> Crupina vulgaris is distributed around the Mediterraneanregion. Western limits are the Iberian Peninsula and Morocco.Northern limits include southern Europe, northern Greece, andTurkey. The range extends south to northern Iran and Iraq andeast to the Caucasus region, Uzbekistan, Turkmenistan, andnortheastern Afghanistan. This species has been introducedin Idaho, Cali<strong>for</strong>nia, Washington, and Oregon (Garnatje et al.2002, USDA 2002, USDA, ARS 2005). The CLIMEX climatematching program indicates the climatic similarity betweenJuneau, Fairbanks, and Nome and areas where the species isdocumented is low. Similarity between Juneau, Fairbanks, andNome and Soria and Cuenca, Spain and Braganca, Portugal is25% to 30%. Similarity between <strong>Alaska</strong> climate with areas <strong>of</strong>Crupina introduced range in Oregon and Idaho is 21% to 40%.Thus establishment <strong>of</strong> Crupina vulgaris in <strong>Alaska</strong> is unlikely. Thisspecies is rejected from consideration <strong>for</strong> ranking.Ecological ImpactScoreImpact on Ecosystem Processes (0–10)Impact on Natural Community Structure (0–10)Impact on Natural Community Composition (0–10)Impact on Higher Trophic Levels (0–10)Total <strong>for</strong> Ecological Impact /Biological Characteristics and Dispersal ScoreMode <strong>of</strong> Reproduction (0–3)Long-distance dispersal (0–3)Spread by humans (0–3)Allelopathic (0–2)Competitive Ability (0–3)Thicket-<strong>for</strong>ming/Smothering growth <strong>for</strong>m (0–2)Germination requirements (0–3)Other invasive species in the genus (0–3)Aquatic, wetland or riparian species (0–3)Total <strong>for</strong> Biological Characteristics and Dispersal /Ecological Amplitude and Distribution ScoreHighly domesticated or a weed <strong>of</strong> agriculture (0–4)Known level <strong>of</strong> impact in natural areas (0–6)Role <strong>of</strong> anthropogenic and natural disturbance inestablishment (0–5)Current global distribution (0–5)Extent <strong>of</strong> the species U.S. range and/or occurrence <strong>of</strong><strong>for</strong>mal state or provincial listing (0–5)Total <strong>for</strong> Ecological Amplitude and Distribution /Feasibility <strong>of</strong> ControlScoreSeed banks (0–3)Vegetative regeneration (0–3)Level <strong>of</strong> ef<strong>for</strong>t required (0–4)Total <strong>for</strong> Feasibility <strong>of</strong> Control /Total score <strong>for</strong> 4 sections /§B-29

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