ARTICLES ON HAWAIIAN
BIRDS AND BIRDWATCHING AND OTHER
PACIFIC WILDLIFE
The Hawaiian Hoary Bat (Lasiurus cinereus semotus)
Known locally as the 'ope'ape'a, the Hawaiian Hoary bat is the only existing
native terrestrial mammal known to occur in the Hawaiian archipelago, although other bat species have been found
in subfossil remains. The Hoary Bat is today found on Hawai'i Maui, O'ahu, Kaua'i and Moloka'i with unconfirmed
observations from Kaho'olawe. The largest concentrations of bats are considered to occur on Hawai'i and Kaua'i.
On the Big Island most observations have been from between sea level and 7,500 feet elevation, although individuals
have been recorded at elevations as high as 13,200 feet.
It is suspected that the number of bats has decreased in the past 100 years or so due to habitat loss, although
population numbers are not known. Other threats which affect the bats are the availability of roosting sites, pesticides
(directly and indirectly), predation, changes in the composition and availability of food, and roost disturbance.
The Hawaiian Hoary Bat was listed as endangered by the U.S. Fish and Wildlife Service on 13th October 1970 and
assigned a recovery plan which indicates a subspecies with moderate degree of threat and a high potential for recovery.
The Hawaiian Hoary Bat is a medium-sized nocturnal, insectivorous species, which averages 14-22 grams in weight.
The species is heavily furred and they possess a brown-grey hair colouration, which is tinged with white, producing
a "hoary" appearance. The bat has short, thick, rounded ears which are edged black. The Hawaiian species
may be somewhat more red in colour than the North American Hoary Bat. The Hawaiian species is about 45 % smaller
in mass than the American counterpart and females are larger than males (females average 17.9 grams, males average
14.2 grams). Both sexes have a wingspan of about 26.9 - 34.6 centimetres.
The Hawaiian Hoary Bat belongs to the suborder Michrochiroptera, which includes all bats except Old World
fruit bats. The taxonomic treatment of the genus Lasiurus varies from authority to authority. Koopman (1993)
recognised seven species, including five in North America alone; Jones et al (1992) recognised seven species in
North America north of Mexico; and Nowak (1994) recognised thirteen species. The Hawaiian Hoary Bat is one of three
recognised Hoary Bat subspecies; Lasiurus cinereus cinereus occurs throughout North America, and L.c.
vilosissimus occurs in South America.
The Hawaiian species is endemic to the Hawaiian Islands and is thought to have derived from the North American
Hoary Bat. Jacobs (1993) has presented morphological evidence suggesting that significant divergence of the Hawaiian
species from the mainland form has occurred, and Tomich (1986) has suggested classification as a full species may
be appropriate. However, Morales and Bickham (1995) found that a relatively low genetic divergence had occurred
between the Hawaiian and mainland forms, and thus argue that sub-specific status for the Hawaiian form is more
appropriate.
Only a small amount of research has been conducted on the Hawaiian Hoary Bat, but diet and echolocation practices
have been studied, as well as numerous surveys. The species is a solitary bat that roosts among the foliage of
trees. During a 2-week period Jacobs (1993) found that two radio-tagged bats returned to the same roosting area
each night, and possibly used the same roosting tree. However it has been suggested that roost site fidelity may
vary seasonally and with reproductive condition; fidelity to a home area may be more prevalent than fidelity to
a specific roost among foliage roosting bats. Jacobs (1993) also found that bats typically departed the roost shortly
before sunset and returned before midnight, although this is based on a small number of observations.
The Hawaiian Hoary Bat has been observed foraging in a variety of habitats, both open areas and more vegetatively
cluttered habitats, including open fields near native and non-native woodland, over open ocean (in bays near shore),
over lava flows and at streams and ponds. The North American Hoary Bat forages almost exclusively in open areas
away from vegetation. The Hawaiian form has been observed feeding from 1 metre to over 150 metres above the ground
or water.
The North American Hoary Bat feeds primarily on moths (Black, 1972) and Bellwood and Fullard (1984) found similar
food stuffs were important for the Hawaiian form on Kaua'i. Having said this, other researchers have found no particular
food selection more common in bats studied in both Canada and Hawai'i. Jacobs (1993) has suggested that the Hawaiian
form has a more varied diet compared to mainland bats, possibly due to morphological differences between the two
subspecies, including the fact that the Hawaiian form has a smaller body size and relatively larger skull size.
Pregnant bats have been documented on both Hawai'i and Kaua'i. It may be that males in Hawai'i are fertile all
year-round, although breeding probably occurs mostly between September and December, with birth of the young occurring
in May or June. One female was reported to have been possibly pregnant in April, and large fetuses were found in
females collected in May and June (Baldwin, 1950). Lactating females have been recorded between late June and early
August, and females examined between September and December were post-lactating (Tomich, 1986).
Most temperate insectivorous bats exhibit sperm storage and delayed fertilisation in which adults breed in the
fall and sperm is stored in the females reproductive tract until spring, when ovulation and fertilisation occurs.
This has not been confirmed in Hawaiian Hoary Bats, but is presumed to occur in the mainland form.
Hawaiian Hoary Bats are non-migratory, although seasonal elevation movements and island-wide migrations may occur.
The North American form is migratory with Canadian and northern States individuals travelling south to central
and southern States, and even further south. The activity of Hawaiian bats apparently varies seasonally, although
the exact nature of these movements is unclear. Kepler and Scott (1990) found that most observations of bats was
between August and December. On the Big Island 82 percent of the observations occurred during this period, although
the greatest sampling effort was between May and August. Other researchers found fewer bats in November and December.
On Kaua'i Telfer (1992) found that there was a decrease in observations between May and September in some areas.
Kepler and Scott (1990) suggested that reduced activity may be due to bats entering torpor (a dormant state with
reduced metabolic rates) during the winter months as well as the possible appearance of newly fledged young.
It has not yet been established whether native vegetation is required or is important to the Hawaiian form, although
loss of native vegetation may account for the reported decrease in numbers in the Islands. Kepler and Scott (!990)
found that they were more frequently observed in association with non-native vegetation, with only a few occurring
in native vegetation. However, with the marked increase in non-native species in the last century or so, the numbers
of bats recorded would undoubtedly increase. Fullard (1989) found on Kaua'i that bats frequented areas near native
forest though, rather than near towns or open fields. Fullard (1989) also found bats commonly foraging over ocean
outlets of forested rivers on Kaua'i.
Roosting bats have been recorded from a variety of species including hala (Pandanus tectorius), Kukui (Aleurites
moluccana), Pukiawe (Styphelia tameiameiae) and Java Plum (Syzygium cumini). They have also been
frequently recorded roosting in Eucalyptus trees.
Current and Historic Range and Population Status
The Hawaiian Hoary Bat is known from the islands of Hawai'i, Maui, O'ahu, Kaua'i and Moloka'i, although may only
be resident on Hawai'i, Maui and Kaua'i. There are no records for Lana'i and just one unconfirmed sighting for
Kaho'olawe. The population may have been quite large on O'ahu prior to the early 19th century, but this is based
on a single observation of an unknown number of bats at an unknown location (Tomich 1986). The largest populations
are currently considered to exist on Kaua'i and Hawai'i.
Actual numbers or even estimated population size are not known. Estimates have put the population at thousands,
but this is based solely on individual observations, rather than any sort of quantified survey methods. Observations
were apparently widespread on Hawai'i and Kaua'i between 1939 and 1986 (Tomich 1986). Bats occur in both dry and
wet areas, but appear to be more common on the drier leeward side (Jacobs 1994). Fullard (1989) reported that on
Kaua'i the bat was "not common" and is apparently limited to the northern forested zones of the island,
but more recent anecdotal evidence suggests that bats are common there (A.Asquith, U.S. Fish and Wildlife Service,
pers.comm. 1997). It is certainly true that bats are quite commonly seen along the northern edge of the island,
from sea level to high elevation forest and individuals have been recorded quite frequently on the south-east (Lihue
area) and south (Koloa) areas (C.W. Melgar, unpublished field notes. 1998, 1999, 2000, 2001). Kepler and Scott
(1990) suggested that bats found on O'ahu, Maui and Moloka'i may be migrants or vagrant individuals , although
more recent data suggests that bats are resident on Maui. Two bats have been documented on Moloka'i, where one
was seen over open ocean. At present the seasonal bias, distribution and numbers of bats recorded may be an effect
of research effort and location of observation and so any information must be treated with a certain amount of
caution.
Reasons for decline and current threats and conservation
As there is very little overall data and as historical information regarding its past distribution is scant, the
decline of the bat has largely been inferred. Observations and specimen records appear to show that bats are now
absent from historically occupied ranges, although numbers of individuals in these areas is lacking. The population
of the Hawaiian Hoary Bat could be threatened by habitat loss, pesticides, predation and roost disturbance. Fenton
and Barclay (1980) and others, suggest that in general, the availability of roosting sites rather than food availability,
predation or other factors is believed to be the primary limitation in distribution and abundance of many bat species
(Fenton 1970, Humphrey 1975).
It would seem however that in the Hawaiian islands there is still a large enough amount of forest (native and non-native)
to support a large population of bats. Predation in Hawai'i is probably limited to the indigenous Hawaiian Short-eared
Owl (Asio flammeus sandwichensis) and introduced Barn Owl (Tyto alba), although several other species
of Owl were present in the Islands before the first Polynesians arrived and so it is unlikely that predation by
Owls has increased very much. On Hawai'i the endemic Hawaiian Hawk or I'o (Buteo solitarius) is present,
but is a diurnal hunter and the two species probably do not meet very often.
Pesticide use has increased markedly in the last century, especially with the rise in the amount of area taken
up by sugar cane and this may have a marked effect on the amount of available food for bats. Now that the sugar
cane industry in Hawai'i is on the way out, perhaps we will see a rise in the number of bats.
Disturbance of roost sites could easily occur in human-inhabited areas, but in the more remote forested areas (even
near towns etc), disturbance is likely only from introduced rats and cats, and possibly foraging ungulates, such
as pigs and goats.
The Hawaiian Hoary Bat was listed as endangered on 13th October 1970, which means that it is considered likely
that the species is in danger of extinction throughout all or part of its range. The Bat is fully protected by
law and this prohibits the taking, harassing, pursuance, wounding, killing, trapping, capturing or collection of
any individuals.
Where to see Hawaiian Hoary Bats in Hawai'i
Clearly by reading the above account it is not a species which can be predicted with any ease where a sighting
may be best achieved. The following maps show locations of observations in recent times, as shown in the Hawaiian
Hoary Bat Recovery Plan.





On Kaua'i, where bats were observed by Melgar between 1998 and 2001, the following locations provided sightings:
| Location | Habitat | Time of Year | Number of Bats | No. of Observations | Notes |
| Nawiliwili Harbor/ Kalapaki Bay near Lihue. | Around street lights over park and near beach. | Jan - March | Singles | Three | Close views of bats as they fed along park edge near street lights. |
| Tunnel of Trees, near Koloa. | Open land and over reservoir edge. | Summer | Singles | Two | Flying near Eucalyptus trees and reservoir edge, as well as grassland. |
| Hanalei NWR | Over ponds and taro lo'i. | All year, but especially late Fall | Singles, but up to 3 seen at once (no interaction). | More than 10 | Flying fairly low over and beside water. |
Bats have been reported on numerous occasions from Kilauea Point in the past, but almost nightly observations
by Melgar during 1998 - 2001 failed to observe any bats.
References
BALDWIN, P.H. 1950. Occurrence and behavior of the Hawaiian Bat. J. Mamm. 31.
BELLWOOD, J.J. and J.H. FULLARD. 1984. Echolocation and foraging behavior in the Hawaain
hoary bat, Lasiurus cinereus smotus. Canadian J. Zool. 62.
BLACK, H. 1972. Differential exploitation of moths by the bat Eptesicus fuscus and Lasiurus
cinereus. J. Mamm. 53.
FENTON, M.B. and R.M.R BARCLAY. 1980. Myotis lucifugus. Mamm.
Species. No. 142.
FENTON, M.B. 1970. Population studies of Myotis lucifugus (Chiroptera vespertillionidae)
in Ontorio. Life Sci. Contrib. R. Ont. Mus. 77.
FULLARD, J.H. 1989. Echolocation survey of the distribution of the Hawaiian hoary bat
(L.c.semotus) on the island of Kauai. J. Mamm. 70.
HUMPHREY, S.R. 1975. Nursery roosts and community diversity of Nearctic bats. J. Mamm. 56.
JACOBS, D.S. 1993. Character release in the endangered Hawaiian hoary bat, (L.c. semotus).
Ph.D. Dissertation, Univ. of Hawaii, Honolulu. 136pp.
JACOBS, D.S. 1993. Foraging behavior of the endangered Hawaiian hoary bat, L.c. semotus.
Final report to the U.S. Fish and Wildlife Service. 6pp.
JACOBS, D.S. 1994. Distribution and abundance of the endangered Hawaiian hoary bat, L.c.
semotus. Pacific Sci. 48.
JONES, J.K. Jr., R.S. HOFFMAN, D.W. RICE, C. JONES, R.J. BAKER and M.D. ENGSTROM. 1992. Revised
checklist of North American mammals north of Mexico. Occ. Pap. Mus. Texas Tech Univ.
146.
KEPLER, C.B. and J.M. SCOTT. 1990. Notes on distribution and behavior of the endangered
Hawaiian hoary bat (L.c. semotus), 1964-1983. 'Elepaio 50.
KOOPMAN, K. 1993. Order Chiroptera in D.E. Wilson and D.M. Reeder, eds. Mammal species
of the world: a taxonomic and geographic reference. Smithsonian Institution Press, Washington
D.C. 634pp.
MELGAR, C.W. 1998. Unpublished filed notes from Hawai'i.
MELGAR, C.W. 1999. Unpublished filed notes from Hawai'i.
MELGAR, C.W. 2000. Unpublished filed notes from Hawai'i.
MELGAR, C.W. 2001. Unpublished filed notes from Hawai'i.
MORALES, J.C. and J.W. BICKHAM. 1995. Molecular systematics of the genus Lasiurus (Chiroptera:
Vespertilionidae) based on restriction-site maps of the mitrochondrial ribosomal genes.
J. Mamm. 76.
NOWAK, R.M. 1994. Walker's bats of the World. The Johns Hopkins
University Press. 287pp.
TELFER, T.C. 1992. Survey of the Hawaiian bat on the island of Kauai and selected areas
statewide. Unpublished report, Hawaii Division of Forestry and Wildlife.
TOMICH, P.Q. 1974. The Hawaiian hoary bat, daredevil of the volcanoes. National Parks and Conservation Magazine. 48.
TOMICH, P.Q. 1986. Mammals in Hawaii. Bishop Museum Press, Honolulu.
375 pp.
U.S. FISH AND WILDLIFE SERVICE. 1998. Recovery Plan for the Hawaiian Hoary Bat. U.S. Fish and Wildlife Service, Portland, OR. 50pp.
Christian Melgar. Worthing, West Sussex, UK. 2002.