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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 />

to drier conditions <strong>and</strong> changes in the microclimate. One natural pond, known as Frog Pond, occurs<br />

between the Honohina <strong>and</strong> Hakalau Tracts at about 5,600 ft (Tomonari-Tuggle 1996).<br />

A baseline water resource assessment <strong>and</strong> stream fauna assessment has not been conducted at the<br />

HFU (USFWS 2007). However, numerous surveys have been conducted at the lower elevations of<br />

streams that pass through the Refuge. The lower reaches of these streams support native fishes <strong>and</strong><br />

invertebrates (Tate 1996, Nishimoto <strong>and</strong> Kuamo‘o 1997). Although unstudied, stream fauna at higher<br />

elevations within the HFU are believed to be exclusively invertebrate.<br />

According to the Water Resources Protection <strong>Plan</strong> (USFWS 2005), the HFU is located in the<br />

Pa‘auilo, Hakalau, <strong>and</strong> Onomea hydrological units. These aquifers have a sustainable yield of 60,<br />

150, <strong>and</strong> 147 mgd, respectively. The size of these systems shows that a large amount of potable basal<br />

groundwater can be developed in the area (Yuen <strong>and</strong> Associates 1990).<br />

3.3.2 Kona Forest Unit Hydrology<br />

Due to the extremely permeable lava <strong>and</strong> well-drained soils, there are no perennial surface waters or<br />

drainages on the KFU. As a result, no st<strong>and</strong>ard water resource assessments have been performed<br />

(USFWS 2007). The closest permanent surface water is the Lumiawai waterhole, located about<br />

0.5 mi south of the southeast corner (Rayond <strong>and</strong> Valentine 2007). Ki‘ilae Stream, which is south of<br />

Hōnaunau, is the closest stream (Yuen <strong>and</strong> Associates 1990).<br />

The Water Resources Protection <strong>Plan</strong> (USFWS 2005) depicts the KFU within the Ka‘apuna<br />

hydrological unit. Groundwater in this region is primarily composed of a thin basal lens that is not<br />

protected by caprock. The aquifer in the Ka‘apuna hydrological unit has a sustainable yield of<br />

50 mgd (Yuen <strong>and</strong> Associates 1990). The Refuge area functions as an important groundwater<br />

recharge area for Kona as a result of the porous substrate <strong>and</strong> high moisture conditions (USFWS<br />

2008a).<br />

South Kona is vulnerable to flooding due to the combination of intense storms, lack of drainages,<br />

steep terrain, permeable soils, <strong>and</strong> urban l<strong>and</strong> uses (County of Hawai‘i 2006, TMA 2007). No records<br />

of flooding on the unit have been found.<br />

3.4 Topography<br />

The Isl<strong>and</strong> of Hawai‘i is considered the highest oceanic isl<strong>and</strong> in the world. However, similar to<br />

other volcanic isl<strong>and</strong>s, summit heights are constantly changing due to erosion, lava deposition, <strong>and</strong><br />

isostatic compensation (Jordan et al. 2003). Hawai‘i Isl<strong>and</strong> is characterized by high elevation areas<br />

<strong>and</strong> gentle slopes. The majority of Hawai‘i Isl<strong>and</strong> (88 percent) is above 500 ft (HDBEDT 2007).<br />

Furthermore, almost 70 percent is above 2,000 ft (Mitchell et al. 2005, HDBEDT 2007). The highest<br />

point on the isl<strong>and</strong>, Mauna Kea, reaches 13,796 ft. Although Hawai‘i Isl<strong>and</strong> has some of the highest<br />

peaks in the State, the inclines are relatively mild. Approximately 70 percent of Hawai‘i Isl<strong>and</strong> has a<br />

slope of less than 10 percent (HDBEDT 2007).<br />

Chapter 3. Physical Environment 3-11

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