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Final Comprehensive Conservation Plan - U.S. Fish and Wildlife ...

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Hakalau Forest National <strong>Wildlife</strong> Refuge<br />

<strong>Comprehensive</strong> <strong>Conservation</strong> <strong>Plan</strong><br />

contract for labor <strong>and</strong> equipment <strong>and</strong> to purchase herbicide to spray blackberry <strong>and</strong> other invasive<br />

species. Backpack sprayers will be used to spray patches of blackberry scattered throughout the<br />

forest. The contractor will also be asked to provide a tractor-mounted spray rig (with two spray<br />

w<strong>and</strong>s) for use on larger patches located in more accessible areas within the grassl<strong>and</strong>s <strong>and</strong> upper<br />

edge of the forest. The Refuge will direct the contractor where to spray, provide herbicide, provide<br />

water at minimal distance to the operational area, <strong>and</strong> do everything possible to maximize efficiency.<br />

Concurrently, Refuge staff will continue their blackberry control efforts (spray application of<br />

herbicide, pig control <strong>and</strong> reforestation) at similar levels to those of the past few years. Outlying<br />

blackberry colonies will receive highest priority for eradication. As the periphery is controlled, the<br />

effort will constrict inward toward the core infestation, where blackberry patches reach their greatest<br />

size <strong>and</strong> density.<br />

Monitoring will consist of continuing annual weed <strong>and</strong> ungulate surveys on established transect lines.<br />

Every fifth year a more intensive survey methodology will be applied to assess control efforts <strong>and</strong><br />

make adaptive adjustments to the control approach. Progress of the blackberry eradication effort will<br />

be monitored though annual weed <strong>and</strong> ungulate surveys using established transect methods. Gross<br />

changes in distribution <strong>and</strong> abundance will be monitored through collection of presence/absence <strong>and</strong><br />

density data within a contiguous series of 5 x 10 meter plots along the 17 transects. This will<br />

maintain the continuous series of data collected annually since 1995 <strong>and</strong> sporadically before that<br />

date. Continued funding for weed <strong>and</strong> ungulate surveys will be essential through the planning period,<br />

beginning in FY2010 <strong>and</strong> beyond.<br />

Six endangered bird species (‘akiapōlā’au, Hawai‘i ‘ākepa, Hawai‘i creeper, ‘io, nēnē, <strong>and</strong> koloa<br />

maoli) the endangered ‘ōpe‘ape‘a, six endangered plant species, <strong>and</strong> the diverse assemblage of other<br />

native plants <strong>and</strong> animals that inhabit the Refuge will all benefit from blackberry <strong>and</strong> other invasive<br />

weed species control efforts. Endangered <strong>and</strong> native plants will experience reduced competition for<br />

space, light <strong>and</strong> nutrients. Areas currently occupied by blackberry <strong>and</strong> other invasives will be<br />

recolonized by native plants that provide food <strong>and</strong> habitat for the native animals <strong>and</strong> plants the<br />

Refuge is m<strong>and</strong>ated to protect. The absence of thorny blackberry thickets will facilitate fence<br />

maintenance, tree planting efforts, <strong>and</strong> the ability of staff <strong>and</strong> visitors to walk <strong>and</strong> work in the forest.<br />

The biodiversity <strong>and</strong> health of the native forest community will increase.<br />

A weed control program will be established on the Kona Forest Unit to promote restoration of the<br />

forest understory to benefit native wildlife species. Intensive weed monitoring <strong>and</strong> control efforts at<br />

the Kona Forest Unit will require resources that are not currently available. It is hoped that during the<br />

plan period resources can be obtained that will make the program viable on the Kona Unit modeled<br />

loosely on what has been done at the Hakalau Unit (i.e., use of staff, partner <strong>and</strong> contractor resources<br />

as available).<br />

Cost Estimate: $150K annually, $200,000 every 5th year<br />

H) Predator exclusionary fence for nēnē nesting at Hakalau Forest NWR<br />

Nēnē at Hakalau Forest NWR thrive well, except during breeding when predation on nēnē goslings<br />

by cats, mongooses, <strong>and</strong> possibly ‘io has been a problem. The current fences in the area are not<br />

working well. The fences are outdated, too small, <strong>and</strong> do not prevent predation. A 15-acre fenced<br />

exclosure will be built using predator proof fencing materials to reduce predation by terrestrial<br />

predators. Reproductive success is measured each year at Hakalau Forest NWR, <strong>and</strong> comparisons<br />

C-20 Appendix C. <strong>Plan</strong> Implementation

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