Centaurea solstitialis L.<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?South CoastalNoInterior BorealNoNoNoNoScoreCLIMEXsimilarity?Arctic AlpineNoCentaurea solstitialis has not been documented in <strong>Alaska</strong> (Hultén1968, AKEPIC 2004,UAM 2004). Yellow starthistle is believedto be native <strong>of</strong> the Mediterranean region. Today, it can be foundin most temperate areas <strong>of</strong> Europe, North and South America,but not in the Arctic (Lid and Lid 1994, Maddox et al. 1985,Elven Reidar pers. com., USDA 2002). This weed occurs innearly every American state, with the most severe infestations inCali<strong>for</strong>nia, Idaho, Oregon, and Washington. It has also expandedinto Canada from British Columbia to Ontario. The CLIMEXclimate matching program indicates the climatic similaritybetween Juneau, Fairbanks, and Nome and areas where thespecies is documented is low. Thus establishment <strong>of</strong> Centaureasolstitialis in <strong>Alaska</strong> is unlikely. The species is rejected fromconsideration <strong>for</strong> ranking.common names: yellow starthistleEcological 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-20
Chenopodium album L.<strong>Ranking</strong> SummaryEcoregion known or expected to occur inSouth CoastalInterior BorealArctic AlpineYesYesYesPotential Max. ScoreEcological Impact 40 5Biological Characteristics and Dispersal 25 12Amplitude and Distribution 25 15Feasibility <strong>of</strong> Control 10 5Relative Maximum 37Climatic ComparisonCollected in<strong>Alaska</strong> regions?common names: lambsquarters, white goosefootCLIMEXsimilarity?South Coastal Yes –Interior Boreal Yes –Arctic Alpine Yes –Chenopodium album has been collected from all <strong>Alaska</strong>necoregions: south coastal (Afognak, Kodiak, Middleton Island,and Skagway), interior boreal (Anchorage, Bettles, Big Delta,Circle, Fairbanks, Gulkana, and Ophir), and arctic alpine(Nulato) (Hultén 1968, Welsh 1974, Densmore et al. 2001, UAM2003).Ecological ImpactScoreImpact on Ecosystem Processes (0–10) 1Chenopodium album has not been observed in undisturbed areasin <strong>Alaska</strong> (Densmore et al. 2001, Hultén 1968, Welsh 1974). It isunlikely that measurable impacts to ecosystem processes occurdue to its presence.Impact on Natural Community Structure (0–10) 1Lambsquarters establishes in a sparsely vegetated herbaceouslayer, increasing the density <strong>of</strong> the layer in south-central <strong>Alaska</strong>(I. Lapina and M.L. Carlson pers obs.).Impact on Natural Community Composition (0–10) 0Lambsquarters has not been observed in undisturbed areas in<strong>Alaska</strong>, no perceived impact on native populations has beendocumented (Densmore et al. 2001).Impact on Higher Trophic Levels (0–10) 3<strong>Plants</strong> are reported to be poisonous to sheep and pigs, but no datais present regarding its toxicity to native herbivores (CU-PPID2004). It is an alternate host <strong>for</strong> a number <strong>of</strong> viral diseases <strong>of</strong>barley, beet, potato, turnip, and tobacco—some <strong>of</strong> these crops aregrown commercially in <strong>Alaska</strong> (Royer and Dickinson 1999). Allparts <strong>of</strong> the plants contain nitrate.Total <strong>for</strong> Ecological Impact 5/40Biological Characteristics and Dispersal ScoreMode <strong>of</strong> Reproduction (0–3) 3Lambsquarters reproduces entirely by seed. Each plant canproduce over 500,000 seeds (Royer and Dickinson 1999).Long-distance dispersal (0–3) 2Chenopodium album lacks any seed dispersal adaptations andmost seeds are deposited near the parental plant. Seeds may bewashed into ditches and can be moved long distances despitelacking buoyancy. Also, seeds remain viable after passing throughthe digestive tract <strong>of</strong> animals (Rutledge and McLendon 1996).Spread by humans (0–3) 2The seeds can be a contaminant in grass and cereal seed. It hasbeen reported to spread as a contaminant <strong>of</strong> the topsoil andhorticultural stock. It appears to spread along <strong>of</strong>f-road vehicletrails and road edges in <strong>Alaska</strong> (M.L. Carlson pers. obs.)Allelopathic (0–2) 2Leachates from Chenopodium album significantly reducetomato shoot biomass and accumulation <strong>of</strong> N, P, K, Ca, and Mg(Qasem et al. 1989). The allelopathic effects were separated fromcompetitive effectsCompetitive Ability (0–3) 0Lambsquarters is moderately competitive <strong>for</strong> moisture andnutrient in cultivated fields. However, it competes poorly withnative species (Densmore et al. 2001, Royer and Dickinson 1999,Rutledge and McLendon 1996).Thicket-<strong>for</strong>ming/Smothering growth <strong>for</strong>m (0–2) 0Lambsquarters can grow up to 3.5 feet tall (Royer and Dickinson1999), but usually does not <strong>for</strong>m dense stands in <strong>Alaska</strong> (I.Lapina pers. obs.).Germination requirements (0–3) 0Seeds must be in the top 3 cm <strong>of</strong> soil to germinate. Light has beenreported as necessary <strong>for</strong> germination. Germination is inhibitedin areas shaded by other plants (Densmore et al. 2001, Royer andDickinson 1999, Rutledge and McLendon 1996).Other invasive species in the genus (0–3) 3Chenopodium murale L. is considered invasive (USDA, NRCS2002).Aquatic, wetland or riparian species (0–3) 0Lambsquarters is found in cultivated fields, roadsides, and wasteareas (Densmore et al. 2001, Gubanov et al. 2003).Total <strong>for</strong> Biological Characteristics and Dispersal 12/25Ecological Amplitude and Distribution ScoreHighly domesticated or a weed <strong>of</strong> agriculture (0–4) 4Lambsquarters is a cosmopolitan weed <strong>of</strong> cultivated areas (Royerand Dickinson 1999).Known level <strong>of</strong> impact in natural areas (0–6) 1Chenopodium album is found in river bottoms and eroded areasassociated with overgrazing, burns, or logging in the desertor desert grassland, pinyon juniper, and yellow pine <strong>for</strong>ests inArizona (Parker 1990).Role <strong>of</strong> anthropogenic and natural disturbance inestablishment (0–5)Lambsquarters is a short-lived colonizer <strong>of</strong> disturbed areas andwill be present <strong>for</strong> only 1–3 years unless the site is repeatedlydisturbed (Densmore et al. 2001, Royer and Dickinson 1999).Current global distribution (0–5) 5Introduced from Europe, its current distribution is worldwide,including Africa, North and South America, Australia, Hawaii,Greenland, and New Zealand (Hultén 1968).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)Chenopodium album is listed as “noxious” in Minnesota and as a“weed” in Kentucky, Nebraska, Florida, Manitoba, and Quebec(Invaders Database <strong>System</strong> 2003, Royer and Dickinson 1999,USDA, NRCS 2002).Total <strong>for</strong> Ecological Amplitude and Distribution 15/2505B-21
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United StatesDepartment ofAgricultu
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Lonicera tatarica L. common names:
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Other invasive species in the genus
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Known level of impact in natural ar
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Biological Characteristics and Disp
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Ecological Amplitude and Distributi
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Melilotus alba MedikusRanking Summa
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Melilotus officinalis (L.) Lam.Rank
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Allelopathic (0-2)UThere is no data
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Ecological Amplitude and Distributi
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Biological Characteristics and Disp
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Other invasive species in the genus
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Role of anthropogenic and natural d
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Plantago major L.Ranking SummaryEco
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Competitive Ability (0-3) 1Annual b
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Poa pratensis ssp. pratensis L.comm
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Polygonum aviculare L. common names
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Competitive Ability (0-3) 2Black bi
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Other invasive species in the genus
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Known level of impact in natural ar
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Rumex acetosella L.Ranking SummaryE
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Long-distance dispersal (0-3) 3The
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Long-distance dispersal (0-3) 3Ragw
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Feasibility of ControlScoreSeed ban
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Sonchus arvensis L. common names: f
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Spread by humans (0-3) 3European mo
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Ecological Amplitude and Distributi
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Stellaria media (L.) Vill.Ranking S
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Taraxacum officinale ssp. officinal
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Aquatic, wetland or riparian specie
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Trifolium hybridum L.Ranking Summar
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Current global distribution (0-5) 3
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Long-distance dispersal (0-3) 2The
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Role of anthropogenic and natural d
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Vicia villosa RothRanking SummaryEc
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Current global distribution (0-5) 0
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Anderson, D. Phalaris. In J. C. Hic
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Best, K.F., G.G. Bowes, A.G. Thomas
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Cameron, E. 1935. A study of the na
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Corbin, J.D., M. Thomsen, J. Alexan
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Douglas, G.W. and A. MacKinnon. 199
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Frankton, C. and G.A. Mulligan. 197
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Haggar, R.J. 1979. Competition betw
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Howard, J.L. 2002. Descurainia soph
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Klinkhamer, P.G. and T.J. De Jong.
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MAFF - Ministry of Agriculture, Foo
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Miki, S. 1933. On the sea-grasses i
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Paddock, Raymond, E. III. Environme
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Proctor, V.W. 1968. Long-distance d
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Saner, M.A., D.R. Clements, M.R. Ha
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Stebbins, L.G. 1993. Tragopogon: Go
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Townshend, J.L. and T.R. Davidson.
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Washington State Department of Ecol
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Wolfe-Bellin, K.S. and K.A. Moloney
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B. Invasiveness Ranking1. Ecologica
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2.5. Competitive abilityA. Poor com
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4. Feasibility of Control4.1. Seed