Allelopathic (0–2)UThere is no data concerning allelopathy. The small volume <strong>of</strong>literature on this species suggests that it has not been tested.Competitive Ability (0–3) 1Wall lettuce almost always occurs as a component <strong>of</strong> sparsevegetation and is rarely found in closed swards. It may competewith co-occurring species in closed woodland vegetation (Clabbyand Osborn 1999).Thicket-<strong>for</strong>ming/Smothering growth <strong>for</strong>m (0–2) 0Wall lettuce does not <strong>for</strong>m thickets or patches. It usually occursin small groups or as scattered individuals (Clabby and Osborne1999).Germination requirements (0–3) 2Wall lettuce germinates mainly on barren or sparsely vegetatedsites (Clabby and Osborn 1999).Other invasive species in the genus (0–3) 0The genus Mycelis is monotypic (USDA 2002).Aquatic, wetland or riparian species (0–3) 0Wall lettuce is a species <strong>of</strong> moist to mesic <strong>for</strong>ests in the lowlandand montane zones. It is commonly found in open woods, woodmargins, and woodland clearings, but also occurs in scrub and onwalls and rock outcrops (Clabby and Osborne 1999, Cronquist1955, Douglas et al. 1998, Gubanov et al. 1995).Total <strong>for</strong> Biological Characteristics and Dispersal 11/23Ecological Amplitude and Distribution ScoreHighly domesticated or a weed <strong>of</strong> agriculture (0–4) 0The species is not known as an agricultural weed.Known level <strong>of</strong> impact in natural areas (0–6) 1Though wall lettuce occurs mainly on disturbed sites (Clabby andOsborn 1999), it has been observed to invade <strong>for</strong>est communitiesin Oregon (M.L. Carlson pers. obs.). Wall lettuce has been foundalong old logging roads in southeast <strong>Alaska</strong> (AKEPIC 2004).Role <strong>of</strong> anthropogenic and natural disturbance in0establishment (0–5)Wall lettuce habitats are <strong>of</strong>ten associated with natural oranthropogenic disturbances such as storms, fires, and clearcuts(Clabby and Osborne 1999).Current global distribution (0–5) 5Wall lettuce is native to most <strong>of</strong> temperate continental Europe.Its distribution extends eastward to Turkey and the CaucasusMountains and north in Norway at 68.5°N. Wall lettuce alsooccurs in North Africa, North America, and New Zealand(Clabby and Osborn 1999).Extent <strong>of</strong> the species U.S. range and/or occurrence <strong>of</strong>2<strong>for</strong>mal state or provincial listing (0–5)Wall lettuce has been found in Maine, Massachusetts, Michigan,Minnesota, New Hampshire, New York, Oregon, Vermont, andWashington (USDA 2002). Mycelis muralis is exotic to NorthAmerica but is not listed as noxious (Invaders Database <strong>System</strong>2003, USDA 2002).Total <strong>for</strong> Ecological Amplitude and Distribution 8/25Feasibility <strong>of</strong> ControlScoreSeed banks (0–3) 2In laboratory experiments, dry seeds stored in a refrigeratorremained viable <strong>for</strong> at least 3 years. Seeds stored at roomtemperature lost viability after 2 years (Clabby and Osborne1999). In Kellman’s (1974) study the number <strong>of</strong> viable seedsdeclined during the 3 years <strong>of</strong> monitoring, suggesting a shortperiod <strong>of</strong> seed viability.Vegetative regeneration (0–3) 0Wall lettuce does not regenerate vegetatively (Clabby and Osborn1999).Level <strong>of</strong> ef<strong>for</strong>t required (0–4) 2Control options have not been investigated. Kellman (1974)suggested that wall lettuce will not persist on sites withestablished perennials.Total <strong>for</strong> Feasibility <strong>of</strong> Control 4/10Total score <strong>for</strong> 4 sections 30/98§B-84
Myriophyllum spicatum L.<strong>Ranking</strong> SummaryEcoregion known or expected to occur inSouth CoastalInterior BorealArctic AlpineYesYesYesPotential Max. ScoreEcological Impact 40 38Biological Characteristics and Dispersal 22 20Amplitude and Distribution 25 20Feasibility <strong>of</strong> Control 10 9Relative Maximum 90Climatic ComparisonCollected in<strong>Alaska</strong> regions?CLIMEXsimilarity?South Coastal No YesInterior Boreal No YesArctic Alpine No YesSpecial Note: This taxonomy and identification <strong>of</strong> Eurasianwatermilfoil is problematic. It is <strong>of</strong>ten synonymized with M.sibiricum Komarov, which is native to <strong>Alaska</strong> (ITIS Database2004) and the two taxa are known to hybridize (Moody and Les2007). Hultén (1968) and the UAM database treat the nativetaxon in <strong>Alaska</strong> broadly and as M. spicatum; however, it appearsthat Eurasian watermilfoil in the strict sense is not known fromany locations in <strong>Alaska</strong>.The very closely related Myriophyllum sibiricum (synonymizedby many authors) has been collected in the south coastal, interiorboreal, and arctic alpine ecoregions in <strong>Alaska</strong> (Hultén 1968). Thespecies’ range includes the Norland province in Norway, whereit is only occasionally found (Lid and Lid 1994), the climaticsimilarity <strong>of</strong> this region is similar to the interior boreal and arcticalpine ecoregions <strong>of</strong> <strong>Alaska</strong> (CLIMEX 1999). It is known fromsouthwestern Norway which tends to have a strong climaticsimilarity with the <strong>Alaska</strong>n south coastal ecoregion (Bergen hasa 73% climatic match with Juneau). Last, the closely related M.sibiricum has similar range in Europe and is widespread in <strong>Alaska</strong>.We suggests that establishment <strong>of</strong> M. subspicatum in the southcoastal, interior boreal, and arctic alpine ecogeographic regions ispossible.Ecological ImpactScoreImpact on Ecosystem Processes (0–10) 8Dense Eurasian watermilfoil mats alter water quality by raisingpH, decreasing dissolved oxygen under the mats, and increasingtemperature. The dense mats <strong>of</strong> vegetation can increase thesedimentation rate by trapping sediments (Jacono and Richerson2003, Washington State Department <strong>of</strong> Ecology 2003).Impact on Natural Community Structure (0–10) 10Eurasian watermilfoil <strong>for</strong>ms dense floating mats <strong>of</strong> vegetation,preventing light penetration <strong>for</strong> native aquatic plants (Jacono andRicherson 2003, Remaley 1998, Washington State Department <strong>of</strong>Ecology 2003).Impact on Natural Community Composition (0–10) 10This aquatic plant is able to displace and reduce natural diversity(Bossard 2004, Jacono and Richerson 2003, Washington StateDepartment <strong>of</strong> Ecology 2003).common names: Eurasian watermilfoil,myriophylle en epi, spike watermilfoilImpact on Higher Trophic Levels (0–10) 10Monospecific stands <strong>of</strong> Eurasian watermilfoil provide poorhabitat <strong>for</strong> waterfowl, fish, and other wildlife (Jacono andRicherson 2003). Loss <strong>of</strong> nutrient-rich native plants reduces foodsources <strong>for</strong> waterfowl; it impacts fish spawning; and it disruptspredator-prey relationships by fencing out larger fish. Stagnantwater created by Eurasian watermilfoil mats provides goodbreeding grounds <strong>for</strong> mosquitoes (Bossard 2004).Total <strong>for</strong> Ecological Impact 38/40Biological Characteristics and Dispersal ScoreMode <strong>of</strong> Reproduction (0–3) 3Reproduction is by seeds, rhizomes, fragmentation, and winterbuds. Young populations <strong>of</strong> Eurasian watermilfoil averaged a seedset <strong>of</strong> 112 seeds per stalk. Despite the high seed production, it ispropagated predominantly by vegetative fragments (Aiken 1981,Bossard 2004, Remaley 1998, Washington State Department <strong>of</strong>Ecology 2003).Long-distance dispersal (0–3) 3Fragments can be spread by floating downstream, waterfowl,and other wildlife. Fruits are buoyant <strong>for</strong> short period and can bedispersed by water (Bossard 2004).Spread by humans (0–3) 3It is spread from lake to lake on boat trailers and fishing gear.A number <strong>of</strong> populations found in Oklahoma were introducedby earthworm farmers who packed their product in Eurasianwatermilfoil (Jacono and Richerson 2003, Washington StateDepartment <strong>of</strong> Ecology 2003). It could very likely be moved byfloatplanes and small boats used in <strong>Alaska</strong>.Allelopathic (0–2) 0No records <strong>of</strong> allelopathy.Competitive Ability (0–3) 3Eurasian watermilfoil competes aggressively with native aquaticplants (Bossard 2004, Jacono and Richerson 2003). Eurasianwatermilfoil is an extremely adaptable plant, able to tolerate andeven thrive in a variety <strong>of</strong> environmental conditions. It grows instill to flowing waters, survives under ice, tolerates pH from 5.4to 11, and can grow over a broad temperature range. This plantbegins spring growth earlier than other aquatic plants, quicklygrows to the surface and <strong>for</strong>ming dense canopies (Jacono andRicherson 2003).Thicket-<strong>for</strong>ming/mothering growth <strong>for</strong>m (0–2) 2This aquatic plant <strong>for</strong>ms a large, dense canopy <strong>of</strong> vegetation(Jacono and Richerson 2003, Remaley 1998).Germination requirements (0–3)N/AGermination <strong>of</strong> seed is not a significant factor in reproduction.(Remaley 1998, Washington State Department <strong>of</strong> Ecology 2003).Other invasive species in the genus (0–3) 3Myriophyllum exalbescens Fern. (Royer and Dickinson 1999).M. aquaticum (Vell.) Verdc. (Anderson and Spencer 1999, USDA2002).Aquatic, wetland or riparian species (0–3) 3The typical habitat <strong>for</strong> Eurasian watermilfoil includes freshto brackish water <strong>of</strong> fishponds, lakes, slow-moving streams,reservoirs, estuaries, and canals (Bossard 2004, Jacono andRicherson 2003).Total <strong>for</strong> Biological Characteristics and Dispersal 20/22B-85
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United StatesDepartment ofAgricultu
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IntroductionThe control of invasive
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Overview and aimsThe authors, repre
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The scoring from each system is ver
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While the relative ranks of species
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Figure 4. Ranks for Polygonum cuspi
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Biological Characteristics and Disp
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2.3. Potential to be spread by huma
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3.4. Current global distribution.A
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obs.), suggesting that establishmen
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DiscussionThe existing weed risk as
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AcknowledgementsThe U.S. Forest Ser
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Prather, T., S. Robins, L. Lake, an
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Appendices
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EcologicalimpactBiologicalcharacter
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Appendix A.2.Summary Scores Of Inva
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EcologicalImpactBiologicalCharacter
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Alliaria petiolata (Bieb.) Cavara &
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Biological Characteristics and Disp
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Ecological Amplitude and Distributi
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Feasibility of ControlScoreSeed ban
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Germination requirements (0-3) 2See
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Capsella bursa-pastoris (L.) Medik.
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Spread by humans (0-3) 3The Siberia
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Known level of impact in natural ar
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Extent of the species U.S. range an
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Centaurea solstitialis L.Ranking Su
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Cirsium vulgare (Savi) TenRanking S
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Competitive Ability (0-3) 3Due to i
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Cytisus scoparius (L.) LinkRanking
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Germination requirements (0-3) 3Orc
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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