Poa pratensis ssp. pratensis L.common names: Kentucky bluegrassPoa pratensis ssp. irrigata (Lindm.) Lindb. f.spreading bluegrassPoa trivialis L.rough bluegrass<strong>Ranking</strong> SummaryEcoregion known or expected to occur inSouth CoastalInterior BorealArctic AlpinePotentialYesYesYesScoreMax.Ecological Impact 40 12Biological Characteristics and Dispersal 25 14Amplitude and Distribution 25 19Feasibility <strong>of</strong> Control 10 7Relative Maximum 52Climatic ComparisonPoapratensis ssp.PratensisCollectedPoapratensisssp. IrrigateCollectedPoa trivialisCollectedCLIMEXsimilarity?South Coastal Yes Yes Yes –Interior Boreal Yes Yes No YesArctic Alpine Yes Yes No YesRough bluegrass (Poa trivialis): The CLIMEX matching programindicates the climatic similarity between Fairbanks and areaswhere rough bluegrass is documented is high. Rough bluegrassis well established in Omsk, Tobolsk, and Tomsk, Russia(Malyschev and Peschkova 1990), which has 77%, 70% and68% climatic matches with Fairbanks, respectively. Poa trivialisis documented in arctic areas <strong>of</strong> Ust-Tsilma and Arkhangelsk,Russia (Tolmachev et al. 1995), which have 78% and 76% <strong>of</strong>climate similarity with Nome, respectively. The establishment <strong>of</strong>rough bluegrass in interior boreal and arctic alpine ecogeographicregions <strong>of</strong> <strong>Alaska</strong> may be possible.Ecological ImpactScoreImpact on Ecosystem Processes (0–10) 3Kentucky, spreading, and rough bluegrasses have the potential <strong>for</strong>long-term modification or retardation <strong>of</strong> succession (Butterfieldet al. 1996). In <strong>Alaska</strong> these grasses are restricted to non-nativecommunities (J. Conn pers. com.). Rough bluegrass likelyincreases soil–water content in sod (Glenn and Welker 1996).Impact on Natural Community Structure (0–10) 3Poa pratensis is capable <strong>of</strong> creating uni<strong>for</strong>m, dense mats, greatlyincreasing the density <strong>of</strong> lower herbaceous layers (Weaver andDarland 1948). Poa trivialis rarely occurs in pure stands, but iscapable <strong>of</strong> changing the density <strong>of</strong> the layer (Uchytil 1993).Impact on Natural Community Composition (0–10) 3Kentucky and rough bluegrass have the ability to dominatecommunities, replace prairie plant species, reducing speciesdiversity, and altering the natural floristic composition (Marriottet al. 2003, Wisconsin DNR 2003, Rutledge and McLendon1996, Sather 1996). However, these species are not observedin undisturbed areas in <strong>Alaska</strong>, and negative effects are likelyminimal (J. Conn pers. com.).Impact on Higher Trophic Levels (0–10) 3Bluegrasses can be an important part <strong>of</strong> the diets <strong>of</strong> elk, deer,and sheep (Rutledge and McLendon 1996). The leaves and seedsare eaten by numerous species <strong>of</strong> small mammals and birds.Kentucky-bluegrass-dominated grassland provide habitat <strong>for</strong>species <strong>of</strong> small mammals and birds. It naturally hybridizes withseveral other native and exotic bluegrasses (Uchytil 1993, Daleet al. 1975). It is a host <strong>for</strong> number <strong>of</strong> pest insects and diseases(Butterfield et al. 1996, Uchytil 1993).Total <strong>for</strong> Ecological Impact 12/40Biological Characteristics and Dispersal ScoreMode <strong>of</strong> Reproduction (0–3) 3Kentucky and spreading bluegrass reproduce from both seed andrhizomes. Kentucky bluegrass can produce 100–200 seeds perpanicle in the first year, and as many as 800,000 seeds per squaremeter. Production <strong>of</strong> 1,000 seeds per plant <strong>of</strong> rough bluegrass hasbeen documented (Froud-Williams and Ferris 1985). Rhizomesexpand horizontal growth as much as 2 square meters in 2 years(Rutledge and McLendon 1996, Sather 1996).Long-distance dispersal (0–3) 1The seeds can spread short distances in clumps (Froud-Williamsand Ferris 1986), but they lack specific adaptations <strong>for</strong> longdistancedispersal.Spread by humans (0–3) 3Kentucky, spreading, and rough bluegrasses are commonlyplanted as lawn and pastures grasses (Butterfield et. al. 1996,Liskey 1999). They are used in <strong>Alaska</strong>, Colorado, and Wisconsin<strong>for</strong> soil stabilization along highway roadbanks (Uchytil 1993).They also contaminate commercial seeds (Liskey 1999).Hodkinson and Thompson (1997) found seeds <strong>of</strong> rough andspreading bluegrass on vehicles and with topsoil and horticulturalstock.Allelopathic (0–2) 0These species are not listed as allelophathic (USDA 2002).Competitive Ability (0–3) 1Bluegrass can outcompete native grasses and <strong>for</strong>bs and dominateon high nitrogen soils (Wisconsin DNR 2003). These grasses donot appear to be competing with native species in <strong>Alaska</strong> (J. Connpers. com.). Bluegrass is adapted to a wide range <strong>of</strong> environmentalconditions, and is marginally flood tolerant (Lenssen et al. 2004,Rutledge and McLendon 1996). It grows early in the season, whenmost other species are still dormant. However, because it has ashallow root system it is susceptible to high soil temperaturesand low soil moisture (Wisconsin DNR 2003). In experimentalconditions rough bluegrass appeared to compete strongly withryegrass (Lolium perenne) during first weeks <strong>of</strong> establishment(Haggar 1979).Thicket-<strong>for</strong>ming/Smothering growth <strong>for</strong>m (0–2) 0Bluegrass is capable <strong>of</strong> <strong>for</strong>ming dense sod in highly fertile soils(Sather 1996, Uchytil 1993). In <strong>Alaska</strong>, naturalized populations <strong>of</strong>bluegrass do not <strong>for</strong>m dense stands (J. Conn pers. com.).B-98
Germination requirements (0–3) 2Generally, Kentucky and rough bluegrass requires light and opensoil <strong>for</strong> germination and establishment (Butterfield et al. 1996,Sather 1996). However, some rough bluegrass cultivars do notrequire open surface and are recommended <strong>for</strong> overseeding inestablished lawns (Liskey 1999).Other invasive species in the genus (0–3) 3Poa annua L. and P. compressa L. (Hultén 1968, Royer andDickinson 1999, Whitson et al. 2000).Aquatic, wetland or riparian species (0–3) 1These grasses <strong>of</strong>ten invade wetland and riparian habitatsin addition to gardens, pastures, roadways, meadows, openwoodlands, and prairies (Rutledge and McLendon 1996). In itsnative range Kentucky and rough bluegrass inhabits swamps andmarshes, wet meadows, and streambanks (Gubanov et al. 2003,Tolmachev et al. 1995, Malyschev and Peschkova 1990).Total <strong>for</strong> Biological Characteristics and Dispersal 14/25Ecological Amplitude and Distribution ScoreHighly domesticated or a weed <strong>of</strong> agriculture (0–4) 4Kentucky bluegrass and spreading bluegrass were introducedas cultivars and have since undergone selective breeding. Over100 cultivars <strong>of</strong> Kentucky bluegrass have been developed. It iscommonly planted as a lawn and pastures grass (Butterfield et. al.1996, Wisconsin DNR 2003).Known level <strong>of</strong> impact in natural areas (0–6) 3Bluegrass has successfully invaded prairies and savannas inWisconsin and Nebraska (Weaver and Darland 1948, WisconsinDNR 2003). It is naturalized in dry to moist meadows in Oregonand Washington, and it is a major problem species in aspencommunities in central Colorado and South Dakota (Uchytil1993).Role <strong>of</strong> anthropogenic and natural disturbance in2establishment (0–5)Bluegrasses readily establish by seeds on disturbed sites.Kentucky bluegrass increases with grazing and burning (Sather1996, Weaver and Darland 1948).Current global distribution (0–5) 5These taxa are native to Europe. They have been introduced intoNorth and South America, New Zealand, and Australia (Gubanovet al. 2003, 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)Kentucky, spreading, and rough bluegrasses are found naturalizedin nearly all American states and in Canada from Labrador to thewest coast. Poa pratensis is listed as an invasive weed in Nebraskaand Wisconsin. Poa trivialis is a restricted weed seed in NewJersey and Virginia (Invaders Database <strong>System</strong> 2003, USDA2002).Total <strong>for</strong> Ecological Amplitude and Distribution 19/25Feasibility <strong>of</strong> ControlScoreSeed banks (0–3) 3A maximum <strong>of</strong> 560 Poa pratensis seed/m2 in soil samples from aNetherlands pastures was reported. Seeds germinate within thefirst 4-years after burial (Sather 1996); however, other studiesindicate that the seed is no longer dormant 6 months after harvest(Butterfield et al. 1996). Chippindale and Milton (1934) stated intheir study that seeds <strong>of</strong> Poa trivialis may remain dormant in thesoil <strong>for</strong> 24, 40 and even 68 years.Vegetative regeneration (0–3) 1These grasses can resprout rapidly (Rutledge and McLendon1996).Level <strong>of</strong> ef<strong>for</strong>t required (0–4) 3Chemical methods and burning might be useful. Practices thatwill damage bluegrass may <strong>of</strong>ten harm the native species more(Butterfield et al. 1996, Sather 1996).Total <strong>for</strong> Feasibility <strong>of</strong> Control 7/10Total score <strong>for</strong> 4 sections 52/100§B-99
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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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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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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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Cytisus scoparius (L.) LinkRanking
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Germination requirements (0-3) 3Orc
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Digitalis purpurea L.Ranking Summar
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Extent of the species U.S. range an
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Galeopsis bifida Boenn. and G. tetr
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Extent of the species U.S. range an
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Heracleum mantegazzianumSommier & L
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Hesperis matronalis L.Ranking Summa
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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