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Current Extent and Potential Distribution of Yellow Flag Iris in

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3.3 Ecological impactsThe ability <strong>of</strong> yellow flag iris to tolerate a wide range <strong>of</strong> conditions makes it a threatto many natural habitats that are periodically wet. These <strong>in</strong>clude riparian floodpla<strong>in</strong>s,lake shorel<strong>in</strong>es, swamps, marshes, fens, <strong>and</strong> brackish wetl<strong>and</strong>s.In North America, yellow flag iris has <strong>in</strong>vaded <strong>and</strong> dom<strong>in</strong>ated a range <strong>of</strong> vegetationtypes (Tu 2003). Along the Mercer River <strong>in</strong> California, it completely displaced Typha<strong>and</strong> other <strong>in</strong>digenous marsh plants with<strong>in</strong> 20 years <strong>of</strong> establishment (Raven <strong>and</strong>Thomas 1970), although it is possible that other factors also contributed (Thomas1980). Along the riparian floodpla<strong>in</strong>s associated with the Lower Waikato River,yellow flag iris appears to displace some <strong>of</strong> the few <strong>in</strong>digenous plant communitiesthat still exist, <strong>in</strong>clud<strong>in</strong>g raupo (Typha orientalis) <strong>and</strong> Carex sedgel<strong>and</strong> (author’s pers.obs.).Once established, yellow flag iris develops a thick rhizome mat that can suppressgerm<strong>in</strong>ation <strong>of</strong> other plant seedl<strong>in</strong>gs <strong>and</strong> also elevate local topography by trapp<strong>in</strong>gsediment <strong>and</strong> thereby creat<strong>in</strong>g a drier habitat (Thomas 1980). This can allow it tospread <strong>in</strong>to previously unsuitable habitat but also enable other species to <strong>in</strong>vade,alter<strong>in</strong>g successional trajectories. Along the Potomac River near Wash<strong>in</strong>gton D.C.,yellow flag iris has contributed to the conversion <strong>of</strong> riparian marshes to less wetforests dom<strong>in</strong>ated by ashes (Frax<strong>in</strong>us spp.) rather than willows (Salix spp.) (Thomas1980).While a reasonable range <strong>of</strong> <strong>in</strong>vertebrates feed on the stems, roots, leaves, fruits <strong>and</strong>seeds <strong>of</strong> the plant it has not been recorded <strong>in</strong> the diet <strong>of</strong> any bird species (Sutherl<strong>and</strong>1980). In North America wildlife has decl<strong>in</strong>ed <strong>in</strong> areas where yellow flag iris hasdisplaced key food species such as Pelt<strong>and</strong>ra virg<strong>in</strong>ica (Thomas 1980; Cox 1999). Noresearch has been conducted <strong>in</strong> New Zeal<strong>and</strong> to determ<strong>in</strong>e whether it provides anyhabitat value for <strong>in</strong>digenous fauna.4. CURRENT EXTENT AND POTENTIAL DISTRIBUTION4.1 MethodsThe current extent <strong>and</strong> potential distribution <strong>of</strong> yellow flag iris along the LowerWaikato River was mapped dur<strong>in</strong>g a 2.5 hour helicopter survey from Ngaruawahia toTuakau on 6 April 2011. Aerial photographs at a scale <strong>of</strong> 1:2,500 were used dur<strong>in</strong>gthe low-fly<strong>in</strong>g survey, to del<strong>in</strong>eate the extent <strong>and</strong> density <strong>of</strong> yellow flag iris <strong>and</strong> toidentify potential habitat. Density <strong>of</strong> yellow flag iris was assigned to one <strong>of</strong> fourcategories, as listed <strong>in</strong> Table 1.Approximately 500 photographs were taken dur<strong>in</strong>g the helicopter survey. These wereused, along with Google Map <strong>and</strong> a report from a ground-based survey conductedbetween Huntly <strong>and</strong> Te Onetea Stream (Department <strong>of</strong> Conservation 2010), to ref<strong>in</strong>emaps <strong>of</strong> yellow flag iris extent <strong>and</strong> potential distribution.© 20115Contract Report No. 2714

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