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SBCT Final EIS - Govsupport.us

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Chapter 3 ⎯ Affected EnvironmentAdjacent to the northwest corner of PTA is the 22,675-acre WPAA (Keamuku Parcel). The plantcommunities are similar to those within PTA and include native and nonnative dominated shrublandsand drainages of varying density and composition. Fountain grass is the dominant member of severalgrassland communities that can include a proportion of native shrubs, herbs, and trees. The highlydisturbed communities are identified as Eucalypt<strong>us</strong> woodlots, nonnative forb lands, and pastureland,all of which contain native plants scattered throughout the area.WetlandsNo wetlands have been identified at PTA.Noxio<strong>us</strong> WeedsPTA has federal and state listed noxio<strong>us</strong> weeds. Though kikuyu grass (Pennisetum clandestinum) isincluded in this category, it is exceptional at PTA and is not invasive at high-elevation dry ecosystems(USAG-HI 2004; Shaw and Castillo 1997). Invasive and noxio<strong>us</strong> weeds that are targeted for controlon PTA include banana poka (Passiflora mollissima), fountain grass, fireweed (Senecio madagascarensis),and R<strong>us</strong>sian thistle (Salsola kali). Other widespread weed species are controlled where theythreaten native plants and communities.WildlifeZoological field surveys that have been conducted on PTA include those by Shallenberger (1977),David (1995), and Freed (1991). More recent surveys targeting native rare invertebrates, mammals,and birds were also conducted (Gon et al. 1993; HINHP 1998; USARHAW and 25th ID [L] 2001b),as were entomology surveys of the PTA lava tubes (Garcia and Associates 2003). There have been nospecific reptile surveys on PTA beca<strong>us</strong>e there are no native terrestrial reptiles and amphibians on theHawaiian Islands. Surveys of PTA were conducted by the University of Hawaii, the Bishop M<strong>us</strong>eumHawaiian Heritage Program, and the HINHP, which are cited in the following section. These naturalresource surveys have been <strong>us</strong>ed for the resource assessments in the Biological Inventory and ManagementAssessment on the PTA for USARHAW (HINHP 1994a), as well as the PTA INRMP(USARHAW and 25th ID [L] 2001b). The following section describes the general presence of invertebrate,mammal, bird, and fish species.Invertebrates. Native and endemic invertebrates on PTA include the Hawaiian helicoverpa moth(Helicoverpa conf<strong>us</strong>a) and the Giffards rhyncogon<strong>us</strong> weevil (Rhyncogon<strong>us</strong> giffardi). Snails documentedat PTA are Letachatina spp., Euconul<strong>us</strong> gaetanoi, Nesopupa subcentralis, Nesovitrea hawaiiensis,Striatura spp., and Vitrina tenella. The helicarionid land snail (Philonesia spp.) and succineidland snail (Succinea konaensis) were also observed on PTA (HINHP 1994b; R. M. TowillCorp. 1997a; USARHAW and 25th ID [L] 2001b). Three endemic caterpillar species, Schrankia sp.,were noted during recent surveys for native invertebrates at PTA lava tubes (Garcia and Associates2003). Surveys of PTA by HINHP in 1993 detected the following nonnative snails: giant Africansnail, bradybaenid land snail, cannibal snail, and the zonitid land snail. Humans have purposely or accidentallyintroduced these species to the Island of Hawaii. They now threaten the native snail speciesthrough competition for resources, predation, and the spread of disease (PCSU 1999).Amphibians. There are no native terrestrial amphibians on the Hawaiian Islands. Nonnative amphibiansfound on the Island of Hawaii include bullfrog, wrinkled frog, coqui frog, giant toad, and Cubantree frog. These species were introduced into Hawaii from other countries and have inhabited areas ofadequate aquatic habitat and surrounding vegetation. While these species have not been documentedin PTA, they could occur in the general PTA ROI, which includes the proposed PTA Trail.February 2008 3–74 2/25th <strong>SBCT</strong> <strong>Final</strong> <strong>EIS</strong>

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