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COR-17-110296
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2024-05-22 Leeward
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Item #2 Waikoloa Lutheran Church/Erick Jacobson (PL-USE-2023-000018)
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PL-USE-2023-000018
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6-8-002:056
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PL-USE-2024-000024
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6-8-002:031
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COR-17-110296
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Last modified
3/8/2019 9:52:38 PM
Creation date
3/9/2017 3:59:59 PM
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Plan Doc Template
Document Date
3/9/2017
Permit Number
COR-17-110296
Parcel Number
680020310000
Description
680020310000, COMMENTS FROM US DEPT OF INTERIOR, FISH AND WILDLIFE, REVIEW OF PROPOSED 60 FT MONOPALM
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Mr. Michael Yee 2 <br /> roosting are cleared during the pupping season, there is a risk that young bats could inadvertently <br /> be harmed or killed. To minimize impacts to the endangered Hawaiian hoary bat, woody plants <br /> greater than 15 feet (4.6 meters)tall should not be disturbed, removed, or trimmed during the bat <br /> birthing and pup rearing season (June 1 through September 15). Additionally, Hawaiian hoary <br /> bats forage for insects from as low as three feet to higher than 500 feet(152 meters) above the <br /> ground. When barbed wire is used in fencing, Hawaiian hoary bats can become entangled. <br /> Therefore, the Service recommends barbed wire not be used for fencing. <br /> Hawaiian hawk <br /> The Hawaiian hawk is known to occur across a broad range of forest habitats throughout the <br /> Island of Hawaii. Loud, irregular and unpredictable activities, such as using heavy equipment or <br /> building a structure, near an endangered Hawaiian hawk nest may cause nest failure. <br /> Harassment of Hawaiian hawk nesting sites can alter feeding and breeding patterns or result in <br /> nest or chick abandonment. Nest disturbance can also increase exposure of chicks and juveniles <br /> to inclement weather or predators. Ground clearing or construction should not occur within <br /> 1,600 feet of any Hawaiian hawk nest during the Hawaiian hawk breeding season (March <br /> through September). If work must be conducted during the March through September Hawaiian <br /> hawk breeding season, a qualified ornithologist should conduct a nest search of the project <br /> footprint and surrounding areas immediately prior to the start of construction activities. Pre- <br /> disturbance surveys for Hawaiian hawks are only valid for 14 days. If disturbance for the <br /> specific location does not occur within 14 days of the survey, another survey will be conducted. <br /> Hawaiian petrel,Newell's shearwater, and band-rumped storm petrel <br /> Hawaiian seabirds may traverse the project area at night during the breeding season. Outdoor <br /> lighting could result in seabird disorientation, fallout, and injury or mortality. Seabirds are <br /> attracted to lights and after circling the lights they may collide with nearby wires, buildings, or <br /> other structures or they may land on the ground due to exhaustion. Downed seabirds are subject <br /> to increased mortality due to collision with automobiles, starvation, and predation by dogs, cats, <br /> and other predators. Young birds (fledglings) traversing the project area between September 15 <br /> and December 1.5, in their first flights from their mountain nests to the sea, are particularly <br /> vulnerable. To minimize potential project impacts to seabirds during their breeding season, all <br /> outdoor lights should be fully shielded so the bulb can only be seen from below bulb height and <br /> only used when necessary. Automatic motion sensor switches and controls should be installed <br /> on all outdoor lights or lights should be turned off when human activity is not occurring in the <br /> lighted area. Any increase in night-time lighting, particularly during each year's peak fallout <br /> period (September 15 through December 15), could result in seabird injury or mortality. <br /> Nighttime construction should be avoided during the seabird fledging period, September 15 <br /> through December 15. <br /> Yellow-faced Bees <br /> Habitat destruction and modification and land use conversion leads to fragmentation of foraging <br /> and nesting areas of these yellow-faced bee species. Habitat destruction and modification by <br /> nonnative plants adversely impact native Hawaiian plant species by modifying the availability of <br /> light, altering soil-water regimes, modifying nutrient cycling, altering the fire characteristics <br /> (increasing the fire cycle), and ultimately converting native dominated plant communities to <br /> nonnative plant communities; such habitat destruction and modification result in removal of food <br /> sources and nesting sites for the listed yellow-faced bee. To minimize potential adverse effects <br />
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