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Invasiveness Ranking System for Non-Native Plants of Alaska

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Current global distribution (0–5) 3Scotch broom is native to the British Isles as well as Central andSouthern Europe to the Canary Islands (USDA, ARS 2004). Ithas become widely naturalized in North America (Hoshovsky1986) as well as India, Iran, New Zealand, Australia, and SouthAfrica (Prasad 2002).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)In western North America, scotch broom has now becomeestablished along the inland valleys <strong>of</strong> the Pacific Northwest,from British Columbia to central Cali<strong>for</strong>nia (Hitchcock andCronquist 1990). It is found in 25 states (USDA 2002) and islisted as noxious in Cali<strong>for</strong>nia, Hawaii, Idaho, Oregon, andWashington (Invaders Database <strong>System</strong> 2003).Total <strong>for</strong> Ecological Amplitude and Distribution 18/25Feasibility <strong>of</strong> ControlScoreSeed banks (0–3) 3Seeds remain viable <strong>for</strong> over 80 years (Bossard et al. 2000,Coombs and Turner 1995, Hoshovsky 1986, Prasad 2002).Vegetative regeneration (0–3) 2<strong>Plants</strong> can resprout after burning or cutting, particularly duringthe rainy season (Bossard et al. 2000, Hoshovsky 1986).Level <strong>of</strong> ef<strong>for</strong>t required (0–4) 3Hand pulling, cutting, or mowing can be effective. However,broom easily resprouts and seeds are long-lived. There<strong>for</strong>e, longtermmonitoring is needed (Hoshovsky 1986).Total <strong>for</strong> Feasibility <strong>of</strong> Control 8/10Total score <strong>for</strong> 4 sections 69/100§Dactylis glomerata L.<strong>Ranking</strong> SummaryEcoregion known or expected to occur inSouth CoastalInterior BorealArctic AlpineYesYesYesPotential Max. ScoreEcological Impact 40 16Biological Characteristics and Dispersal 25 10Amplitude and Distribution 25 22Feasibility <strong>of</strong> Control 10 5Relative Maximum 53Climatic ComparisonCollected in<strong>Alaska</strong> regions?CLIMEXsimilarity?South Coastal Yes –Interior Boreal No YesArctic Alpine No YesDactylis glomerata has been collected in the south coastalecogeographic region <strong>of</strong> <strong>Alaska</strong> (Hultén 1968, Welsh 1974,AKEPIC 2005,UAM 2004). Dactylis glomerata is known to occurthroughout Europe and has been documented as far north as thenorthern province in Norway (Finnmark) at 70°N (Lid and Lid1994). The range <strong>of</strong> this species also includes Røros and Dombås,Norway, which have 76% and 63% climatic matches with Nome,and 55% and 52% climatic matches with Fairbanks, respectively.Thus, it may be possible <strong>for</strong> Dactylis glomerata to becomeestablished in the interior boreal and arctic alpine ecogeographicregions.Ecological ImpactScoreImpact on Ecosystem Processes (0–10) 5Dense stands <strong>of</strong> orchardgrass may suppress the growth <strong>of</strong>native shrubs (Anderson and Brooks 1975) and trees (Powellet al. 1994). Lodgepole pine seedling survival and growth ratedecreased as the density <strong>of</strong> orchardgrass increased in a field studyconducted in British Columbia (Powell et al. 1994).Impact on Natural Community Structure (0–10) 3Orchardgrass alone usually does not <strong>for</strong>m a dense layer, but whenit grows with another perennial European grass such as Festucaarundinacea, Holcus lanatus, or Phalaris aquatica, it is capable <strong>of</strong>developing a dense stand that excludes native perennial grasses(Cobrin et al. 2004, Cal-IPC 2005).common names: orchardgrassImpact on Natural Community Composition (0–10) 3As a codominant with other exotic perennial grasses,orchardgrass is capable <strong>of</strong> causing reduction and extirpation <strong>of</strong>native perennial grasses (Cobrin et al. 2004, Cal-IPC 2005).Impact on Higher Trophic Levels (0–10) 5Orchardgrass is moderately nutritious and highly palatable tograzing animals. Orchardgrass also provides food and cover <strong>for</strong>a number <strong>of</strong> small mammals, birds, and insects (Sullivan 1992).However, suppressed development <strong>of</strong> native shrubs might bedetrimental to native wildlife habitat (Anderson and Brooks1975).Total <strong>for</strong> Ecological Impact 16/40Biological Characteristics and Dispersal ScoreMode <strong>of</strong> Reproduction (0–3) 1Orchardgrass reproduces by seeds (Beddows 1957). Becauseorchardgrass breeders have traditionally focused on <strong>for</strong>age traits,most cultivars are not necessarily good seed producers (Casler etal. 2003).Long-distance dispersal (0–3) 2Most seeds fall directly to the soil below the parent plant. Someseeds attach to animals and travel long distances (Beddows 1957).Spread by humans (0–3) 3Orchardgrass is widely used as a <strong>for</strong>age crop and is recommendedas part <strong>of</strong> a mix <strong>for</strong> erosion control and pasture rehabilitation(Anderson and Brooks 1975, McLean and Clark 1980). It is acommon commercial seed contaminant (Bush et al. 2005).Allelopathic (0–2) 0Orchardgrass is not listed as an allelopathic (USDA, NRCS2006). In experimental studies orchardgrass did not showsignificant inhibition <strong>of</strong> germination, root, and shoot growth(Grant and Sallens 1964, Larson et al. 1995).Competitive Ability (0–3) 1Orchardgrass is able to compete with native perennials andannual species (Corbin et al. 2004).Thicket-<strong>for</strong>ming/Smothering growth <strong>for</strong>m (0–2) 0Orchardgrass rarely <strong>for</strong>ms dense layers, but it is capable <strong>of</strong>creating a dense stand when grown with other perennialEuropean grasses (Corbin et al. 2004, Cal-IPC 2005).B-31

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