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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 />

Appendix L. Summary of Past <strong>and</strong> Current Management<br />

When Hakalau Forest National <strong>Wildlife</strong> Refuge was created in 1985 to protect native forest habitat<br />

for endangered animals <strong>and</strong> plants, the initial l<strong>and</strong>s acquired with the help of the Nature Conservancy<br />

had been used for cattle ranching, some of which had also been logged. As such, the condition of the<br />

native forest had been degraded by 100 years of cattle grazing, with about 5,000 acres of upper<br />

elevation forest (mostly above 6,000 ft) converted into open woodl<strong>and</strong> <strong>and</strong> pasture dominated by<br />

introduced grasses (though most of the Refuge still had closed canopy forest, with the most intact<br />

areas in the lower elevations). Under the closed canopy forest, certain sections of the understory had<br />

been disturbed by cattle, pigs, <strong>and</strong> rats. The mesic koa/‘ōhi‘a <strong>and</strong> koa/māmane forests were the most<br />

severely degraded. Listed species that were found at the time included Phyllostegia racemosa <strong>and</strong><br />

Clermontia lindseyana. The first initial management actions implemented by the Refuge included<br />

surveys (forest bird, native plant, weed, ungulate), construction of ungulate proof fences, ungulate<br />

removal, weed control, <strong>and</strong> reforestation (outplanting of koa) <strong>and</strong> reforestation research focused on<br />

techniques (mainly with assistance of the USFS-Institute of Pacific Isl<strong>and</strong>s Forestry (IPIF)). Due to<br />

the remote location of the Refuge, a cabin <strong>and</strong> storage building as well as water catchment systems<br />

had to be constructed to support Refuge operations. The last cattle permitted to graze at the Refuge<br />

were removed in 1996. Over the years, other parcels of the Refuge (Pua ‘Ākala, Middle Papaikou,<br />

Middle Hakalau, <strong>and</strong> units B-F) were acquired so that today, HFU is 32,730 acres.<br />

In 1997, an additional 5,300 acres was purchased from the Les Marks Estate in South Kona, bringing<br />

the total Refuge acreage up to 38,030 acres. This unit was established specifically for the endangered<br />

‘alalā, as well as other listed species. Vegetation at the lower portions, around the 2,000-foot<br />

elevation, was dominated by a mixture of introduced <strong>and</strong> native trees, shrubs, <strong>and</strong> grasses. These<br />

included guava (Psidium guajava), strawberry guava (Psidium cattleianum), silky oak (Grevillea<br />

robusta), <strong>and</strong> Christmas berry (Schinus terebinthifolius), <strong>and</strong> ‘ōhi‘a (Metrosideros polymorpha) was<br />

the most common native tree. Above the 2,500-foot elevation, introduced trees <strong>and</strong> shrubs become<br />

less prevalent, <strong>and</strong> the forest community was dominated by an overstory of ‘ōhi‘a trees <strong>and</strong> an<br />

understory of native trees, shrubs, <strong>and</strong> hapu‘u tree ferns (Cibotium spp.). Between the 3,000-<br />

6,000 foot elevations, a diverse native forest community was found. This forest type is characterized<br />

by an overstory comprised of a mixture of koa (Acacia koa) <strong>and</strong> ‘ōhi‘a trees <strong>and</strong> an understory of<br />

native shrubs <strong>and</strong> hapu‘u. Cattle grazing had created pastures in some of these upper elevations.<br />

Above the 6,000-foot elevation, the native forest was characterized by a mixed māmane-s<strong>and</strong>alwood<br />

(Sophora chrysophylla-Santalum ellipticum) <strong>and</strong> koa or ‘ōhi‘a dryl<strong>and</strong> natural communities with<br />

ground cover of nonnative grasses <strong>and</strong> native shrubs. Listed species found included the ‘ōpe‘ape‘a,<br />

Hawai‘i ‘ākepa, the Hawai‘i creeper, the ‘akiapōlā‘au, <strong>and</strong> the ‘io. Initial refuge management of this<br />

unit included securing road access, surveys (forest bird, native plant, weed, ungulate), <strong>and</strong><br />

establishing a field camp.<br />

Current Refuge management for both units (Hakalau Forest Unit <strong>and</strong> Kona Forest Unit) revolves<br />

around maintaining <strong>and</strong> constructing new fencing, controlling pest species (plants <strong>and</strong> animals),<br />

native forest restoration, reforestation, <strong>and</strong> threatened <strong>and</strong> endangered species management. In<br />

addition, the Refuge contains structures <strong>and</strong> facilities that existed before the original acquisition. The<br />

Refuge has built its own facilities to support management. All require maintenance, including a<br />

c<strong>and</strong>idate historic structure (Pua ‘Ākala Cabin). Chapter 5 provides additional information on Refuge<br />

facilities.<br />

Appendix L. Summary of Past <strong>and</strong> Current Management L-1

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