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Invasiveness Ranking System for Non-Native Plants of Alaska

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Germination requirements (0–3) 0Seedlings are rare and only established in disturbed areas,including molehills (Turkington et al. 1979). Soil temperatures<strong>of</strong> at least 50 °F are required <strong>for</strong> germination (Royer andDickinson 1999). The seeds do not germinate until the seed coatis sufficiently broken down (by decay or abrasion) to admit water(Densmore et al. 2001).Other invasive species in the genus (0–3) 3Trifolium angustifolium L., T. arvense L., T. aureum L., T. campestreSchreb., T. dubium Sibth., T. hirtum All., T. hybridum L.,T. incarnatum L., T. pratense L., and T. subterraneum L.Aquatic, wetland or riparian species (0–3) 1White clover is a serious weed <strong>of</strong> lawns, roadsides, and disturbedareas (Hultén 1968; Royer and Dickinson 1999).Total <strong>for</strong> Biological Characteristics and Dispersal 15/25Ecological Amplitude and Distribution ScoreHighly domesticated or a weed <strong>of</strong> agriculture (0–4) 4White clover was common as a <strong>for</strong>age crop in Canada (Royerand Dickinson 1999) It has been widely planted <strong>for</strong> lawns andrevegetation on roadsides and other disturbed areas in <strong>Alaska</strong>(Densmore et al. 2001).Known level <strong>of</strong> impact in natural areas (0–6) 1White clover invades prairies in Wisconsin (WDNR 2004).Role <strong>of</strong> anthropogenic and natural disturbance inestablishment (0–5)In <strong>Alaska</strong> white clover is found in sites disturbed in recent yearsand readily invades open habitats (Densmore et al. 2001). Itis relatively shade intolerant (USDA 2002). Frequent, intensegrazing encourages growth <strong>of</strong> white clover (Rutledge andMcLendon 1996).0Current global distribution (0–5) 5White clover is native to Europe and Asia. It has been introducedto North and southern Africa, North and South America, NewZealand, Australia, Tasmania, and India (Hultén 1968). It is <strong>of</strong>tenfound north <strong>of</strong> the Arctic Circle (Royer and Dickinson 1999).Extent <strong>of</strong> the species U.S. range and/or occurrence <strong>of</strong>4<strong>for</strong>mal state or provincial listing (0–5)White clover occurs in nearly all states <strong>of</strong> the United States. It islisted as a weed in Kentucky (USDA 2002).Total <strong>for</strong> Ecological Amplitude and Distribution 14/25Feasibility <strong>of</strong> ControlScoreSeed banks (0–3) 3Seeds <strong>of</strong> white clover remain viable in the soil over 30 years(Rutledge and McLendon 1996).Vegetative regeneration (0–3) 2Grazing promotes resprouting <strong>of</strong> white clover (Rutledge andMcLendon 1996).Level <strong>of</strong> ef<strong>for</strong>t required (0–4) 3It is virtually impossible to eradicate white clover from invadedsites (Densmore et al. 2001). Herbicides can be used to controlwhite clover (Rutledge and McLendon 1996).Total <strong>for</strong> Feasibility <strong>of</strong> Control 8/10Total score <strong>for</strong> 4 sections 59/100§Tripleurospermum per<strong>for</strong>ata(Merat) M. Lainz<strong>Ranking</strong> SummaryEcoregion known or expected to occur inSouth CoastalInterior BorealArctic AlpineYesYesYesPotential Max. ScoreEcological Impact 40 13Biological Characteristics and Dispersal 23 13Amplitude and Distribution 25 15Feasibility <strong>of</strong> Control 10 6Relative Maximum 48Climatic ComparisonCollected in<strong>Alaska</strong> regions?common names: scentless false mayweed,scentless chamomileCLIMEXsimilarity?South Coastal Yes –Interior Boreal Yes –Arctic Alpine Yes –Scentless false mayweed has been collected in the south coastal,interior boreal, and arctic alpine ecogeographic regions <strong>of</strong> <strong>Alaska</strong>(AKEPIC 2004, UAM 2004).Ecological ImpactScoreImpact on Ecosystem Processes (0–10) 3Scentless false mayweed reduces soil moisture and nutrients<strong>for</strong> other species. It likely causes retardation <strong>of</strong> successionalestablishment <strong>of</strong> native species (NAPPO 2003).B-135Impact on Natural Community Structure (0–10) 3Dense stands <strong>of</strong> scentless false mayweed in prairies have beenreported (CWMA 2000, NAPPO 2003, Parchoma 2004). Thisplant has not been observed in dense stands in <strong>Alaska</strong>, but it doesincrease the density <strong>of</strong> the early successional herbaceous layer(I. Lapina pers. obs.).Impact on Natural Community Composition (0–10) 3Spring-emergent seedlings can <strong>for</strong>m very dense stands, reducingthe growth <strong>of</strong> seedlings <strong>of</strong> other species (NAPPO 2003).Impact on Higher Trophic Levels (0–10) 4Scentless false mayweed is unpalatable to animals and can <strong>for</strong>mdense stands in pastures and hayfields, thus altering the quantity<strong>of</strong> <strong>for</strong>aging sites (CWMA 2000, Parchoma 2004). The flowersattract bees and flies (Harris and McClay 2003) and may alter thepollination ecology <strong>of</strong> native communities.Total <strong>for</strong> Ecological Impact 13/40Biological Characteristics and Dispersal ScoreMode <strong>of</strong> Reproduction (0–3) 3Scentless false mayweed reproduces entirely by copious amounts<strong>of</strong> seed. A single plant can produce up to a million seeds, withdense stands capable <strong>of</strong> producing 1,800,000 seeds per squaremeter (Harris and McClay 2003, Juras et al. 2004, NAPPO 2003,Parchoma 2004).

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