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Invasiveness Ranking System for Non-Native Plants of Alaska

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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)The range <strong>of</strong> ground ivy extends throughout the United States;it is naturalized in Canada and ranges from Newfoundland toBritish Columbia. This species is listed as a weed in Kentucky,Nebraska, and Wisconsin, though the species is not declarednoxious (Invaders Database <strong>System</strong> 2003, USDA 2002). Groundivy is on the Invasive Garden Perennials Not to Plant StatewideList <strong>of</strong> <strong>Alaska</strong> (Integrated Pest Management Program 2004).Total <strong>for</strong> Ecological Amplitude and Distribution 14/25Feasibility <strong>of</strong> ControlScoreSeed banks (0–3) 3Seeds <strong>of</strong> ground ivy remain viable in the soil more than 4 years(Chancellor 1985). Small numbers <strong>of</strong> viable seeds were foundin soil samples <strong>of</strong> nearly 20 to over 40 years old (Hutchings andPrice 1999).Vegetative regeneration (0–3) 2Pieces <strong>of</strong> stem can root at the nodes (Hutchings and Price 1999).Level <strong>of</strong> ef<strong>for</strong>t required (0–4) 3Once it is establishes ground ivy is difficult to control. Groundivy is nearly impossible to dig up and remove all roots and stolonfragments (Mitich 1994).Total <strong>for</strong> Feasibility <strong>of</strong> Control 8/10Total score <strong>for</strong> 4 sections 48/100§Gypsophila paniculata L.<strong>Ranking</strong> SummaryEcoregion known or expected to occur inSouth CoastalInterior BorealArctic AlpineYesYesYesPotential Max. ScoreEcological Impact 40 25Biological Characteristics and Dispersal 25 14Amplitude and Distribution 25 18Feasibility <strong>of</strong> Control 7 3Relative Maximum 57Climatic ComparisonCollected in<strong>Alaska</strong> regions?CLIMEXsimilarity?South Coastal No YesInterior Boreal Yes –Arctic Alpine No YesGypsophila paniculata has been collected in Anchorage andMatanuska–Susitna Valley in <strong>Alaska</strong> (I. Lapina pers. obs.,J. Snyder pers. com.). Using CLIMEX matching program,climatic similarity between Nome and areas where the species isdocumented is high. Range <strong>of</strong> the species includes Banff, Alberta,Canada and Regina, Saskatchewan, Canada (Darwemt 1975),which has a 61% and 54% climatic match with Nome respectively.Gypsophila paniculata can withstand considerable variationin temperature and moisture. It is one <strong>of</strong> the few perennialornamentals recommended <strong>for</strong> gardens located on permafrost(Darwent 1975). This suggests that establishment <strong>of</strong> Gypsophylapaniculata in lower part <strong>of</strong> arctic alpine <strong>Alaska</strong> may be possible.Establishment is also likely in drier portions <strong>of</strong> the south coastalregion, such as upper Lynn Canal.Ecological ImpactScoreImpact on Ecosystem Processes (0–10) 3Baby’s-breath appears to reduce available nutrients <strong>for</strong> cooccurringgrass species (Robson 2004, Wisconsin DNR 2004).Protein content <strong>of</strong> desirable grasses declines with the presence <strong>of</strong>Gypsophila paniculata (Wisconsin DNR 2005).Impact on Natural Community Structure (0–10) 7Baby’s-breath can <strong>for</strong>m dense stands and outcompete nativeperennial species (Darwent 1975, Rutledge and McLendon 1996,Wisconsin DNR 2005).common names: baby’s-breathImpact on Natural Community Composition (0–10) 5Baby’s-breath likely displaces native species (Robson 2004,Rutledge and McLendon 1996, Wisconsin DNR 2005).Impact on Higher Trophic Levels (0–10) 5Though baby’s-breath is not used by native mammals or birds,it has the ability to degrade wildlife habitat (Robson 2004).Baby’s-breath contains high levels <strong>of</strong> saponins that could resultin animal toxicity (<strong>Plants</strong> <strong>for</strong> a future 2002). Flowers <strong>of</strong> thisplant are attractive to numerous species <strong>of</strong> pollinating bees andflies (Darwent 1975, Darwent and Coupland 1966), potentiallyimpacting pollination ecology <strong>of</strong> co-occurring plant species.Baby’s-breath is also reported to be an alternate host <strong>for</strong> number<strong>of</strong> viruses (Royer and Dickinson 1999).Total <strong>for</strong> Ecological Impact 20/40Biological Characteristics and Dispersal ScoreMode <strong>of</strong> Reproduction (0–3) 3Baby’s-breath reproduces entirely by seed. <strong>Plants</strong> are capable<strong>of</strong> producing up to 14,000 seeds (Royer and Dickinson 1999,Rutledge and McLendon 1996).Long-distance dispersal (0–3) 3Most capsules drop <strong>of</strong>f near the parent plant. However, windis capable <strong>of</strong> carrying seeds distances <strong>of</strong> 1 km (Rutledge andMcLendon 1996). At maturity, the plant <strong>of</strong>ten breaks <strong>of</strong>f at baseand tumbles in the wind, spreading seeds widely (Royer andDickinson 1999).Spread by humans (0–3) 3Baby’s-breath is cultivated in gardens and flower beds; it is readilyavailable <strong>for</strong> sale at nurseries. It has escaped cultivation intopastures and rangelands (Robson 2004, Rutledge and McLendon1996, Whitson et al. 2000). Its fairly wide distribution in thenorthwestern U.S. may be a result <strong>of</strong> it invading transportationcorridors (Robson 2004).It also is a potential seed contaminant(USDA, ARS 2004).Allelopathic (0–2) 0No considerable allelopathic effects were found in experiments(Robson 2004).B-42

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