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Invasiveness Ranking System for Non-Native Plants of Alaska

Invasiveness Ranking System for Non-Native Plants of Alaska

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DiscussionThe existing weed risk assessment systems that we evaluated have useful approaches to predicting invasion anddamage in particular contexts. The systems are largely driven by specific values <strong>of</strong> the authors (e.g., impacts toa specific area or to agriculture), many <strong>of</strong> which are not universal, and most require more in<strong>for</strong>mation than istypically available (Williams and Newfield 2002), which is a severe drawback to a state such as <strong>Alaska</strong> that is onlybeginning to face large-scale introductions. For most non-native species, little to no research has been conductedin the state and the paucity <strong>of</strong> in<strong>for</strong>mation curtails confidence in ranks. We emphasize the need <strong>for</strong> more researchon invasive species ecology, distribution, and trends in <strong>Alaska</strong>.The system presented here differs from the existing systems by including a climate filtering stage, handling specieswith a range <strong>of</strong> known in<strong>for</strong>mation, and focusing on impacts to natural systems in <strong>Alaska</strong>. Despite thosedifferences, the <strong>Alaska</strong> system produced ranks that were very similar to the Southwest system. We borrowedmany components <strong>of</strong> the “innate ability to become a pest (i.e., biology)” and “ease <strong>of</strong> control sections” from theSouthwest system, but did not include a similar “level <strong>of</strong> impact” section and the systems differed in the relativeweight <strong>of</strong> the remaining sections.Scores <strong>for</strong> the four sections <strong>of</strong> the <strong>Alaska</strong> system are generally strongly positively related to one another (i.e., specieswith large ecosystem impacts also have a more invasive biology, broad distributions, and are more difficultto control). However, the feasibility <strong>of</strong> control section was not as strongly correlated with the other sections andthis is likely due to this section having only three questions, leading to greater variation in scores than the othersections. A number <strong>of</strong> species scored high values in the biological characteristics and distribution sections, butrelatively low scores in the ecology section. These species represent a group <strong>of</strong> ruderal specialists (e.g., Persicarialapathifolium, Poa annua, and Plantago major) that are good dispersers, highly dependent on soil disturbance, butpoor competitors (see Baker 1974). While invasions and their impacts are very difficult to predict, our systemstresses the importance <strong>of</strong> whether the species is invasive in other areas. This trait is most strongly correlated withthe probability <strong>of</strong> invasion into new areas (Forcella and Wood 1984, Rejmanek and Richardson 1996, Rejmanek2001).Species that are regarded as particularly threatening to <strong>Alaska</strong>n ecosystems such as Melilotus alba, Polygonum cuspidatum,and Vicia cracca consistently ranked high in the <strong>Alaska</strong> system among reviewers, while more ruderal speciessuch as Chenopodium album and Matricaria discoidea were consistently ranked with low scores, as expected.The Australian system, on the other hand, ranked species that are not considered problematic in <strong>Alaska</strong> with veryhigh scores. This system gives more weight than the others to agricultural pests and to species linked to specificecological concerns in Australia. <strong>System</strong>s such as the Australian, Southwest, and <strong>Alaska</strong>n that produced continuousnumeric invasiveness ranks resulted in less variation among assessors.The distribution <strong>of</strong> scores in the <strong>Alaska</strong> system currently ranges from 27 (Lepidium densiflorum, the least invasivespecies) to 90 (Myriophyllum spicatum, the most invasive species, which is not yet recorded <strong>for</strong> <strong>Alaska</strong>). The averageis 58. While different users will have different concepts <strong>of</strong> what constitutes various levels <strong>of</strong> invasiveness (e.g.,what is “highly invasive” vs. “moderately invasive” may differ among management agencies), we divided the ranksinto six blocks in Appendix A. We consider species with scores ≥80 as “Extremely Invasive” and species withscores 70–79 as “Highly Invasive;” both <strong>of</strong> these groups are composed <strong>of</strong> species estimated to be very threateningto <strong>Alaska</strong>. Species with scores <strong>of</strong> 60–69 as “Moderately Invasive” and scores <strong>of</strong> 50–59 represent “ModestlyInvasive” species; both <strong>of</strong> these groups still pose significant risks to ecosystems. Species with scores <strong>of</strong> 40–49are “Weakly Invasive”, and

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