Geology topics

Michelle H. Reynolds

Publications and source records attributed to Michelle H. Reynolds.

25 records · Page 2Linked to original sources

USGS2003

Evidence of change in a low-elevation forest bird community of Hawai'i since 1979

We evaluated the abundance and distribution of low-elevation forest birds on windward Hawai'i Island during August 1993-February 1994, and present evidence of changes in the species composition of the forest bird community since 1979. Endemic Hawaiian birds occurred in native-dominated forests as low as 120 m elevation. Non-native species were detected at all survey locations. We observed non-native Saffron Finch Sicalis flaveola , previously unrecorded in Puna. Variable circular plot surveys of Kahauale'a Natural Area Reserve indicated the disappearance of two native species ('I'iwi Vestiaria coccinea and 'O'u Psittitostra psittacea ), and two non-native additions (Red-billed Leiothrix Leiothrix lutea and Kalij Pheasant Lophura leucomelana ) to the study area since the Hawai'i Forest Bird Survey conducted in 1979. We present evidence that native 'Elepaio Chasiempsis sandwichensis has experienced a decrease in population density and an elevational range contraction since 1979. Surveys indicate Puna's forest bird community has had increasing aliens and declining native species since 1979. The persistence of some native bird species within the range of avian disease vectors such as Culex quinquefasciatus in forests below 1,000 m elevation presents an important enigma that requires additional study.

Hawai'i↗

USGS2001

Drepanidine movements in relation to food availability in subalpine woodland on Mauna Kea, Hawai'i

Flowers of the mamane tree ( Sophoru chrysophylla ) are the primary nectar source for Hawaiian honeycreepers in subalpine woodland on Mauna Kea Volcano on the island of Hawai‘i. Mamane seeds are the primary food resource of the endangered Palila ( Loxioides bailleui ), which is now restricted to subalpine woodland on Mauna Kea. The objectives of this study were to determine the patterns and relative scales of movements of the drepanidine community in relationship to food availability and tree density on leeward Mauna Kea. ‘I‘iwi ( Vestiaria coccinea ) and ‘Apapane ( Himatione sanguinea ) densities were related to mamane flower abundance. Palila densities were related to mamane pod abundance. These species also had higher densities in mamane woodland than in naiomamane woodland, unlike the more insectivorous Hawai‘i ‘Amakihi ( Hemignathus virens ) whose densities did not differ between woodland types. Palila and Hawai’i ‘Amakihi do not make movements on the same scale as ‘I‘iwi and ‘Apapane, whose densities changed by more than an order of magnitude. Ungulate eradication, grass reduction, tire management, and restored corridors of mamane woodland would benefit all drepanidines on Mauna Kea, particularly the Palila.

Hawai'i↗

USGS2001

The Hawai'i rare bird search 1994-1996

We compiled the recent history of sightings and searched for 13 rare and missing Hawaiian forest birds to update status and distribution information. We made 23 expeditions between August 1994 and April 1996 on the islands of Hawai‘i, Maui, Moloka‘i, and Kaua‘i totaling 1,685 search hours, 146 field days, and 553 person days. During our surveys we found four critically endangered birds: the Po‘ouli ( Melamprusops phaeosoma , five to six individuals), Maui Nukupu‘u ( Hemignathus lucidus affinis , one individual), ‘I‘iwi ( Vestiaria coccinea ) on Moloka‘i (one individual), and the Puaiohi ( Myadestes palmeri , 55-70 individuals). Detection rates for each species were 0.013, 0.002, 0.012, and 0.318 detections/hr, respectively. Although not visually confirmed during our surveys, auditory detections, unconfirmed sightings, and other reports suggest the possible existence of ‘O‘u ( Psittirostra psittacea ) on Hawai‘i, Kaua‘i Nukupu‘u ( Hemignathus lucidus hanapepe ), and Maui ‘Akepa ( Loxops coccineus ochraceus ) in perilously low numbers. Six undetected forest bird populations, Kama‘o ( Myadestes myudestinus ), Kaua‘i ‘O‘o ( Moho braccatus ), Bishop’s ‘O‘o ( Moho bishopi ), ‘O‘o on Kaua‘i, Greater ‘Akialoa ( Hemignafhus ellisianus ), and Kakawahie ( Paroveomyza flammea ) have high probabilities of being extinct. Oloma‘o ( Myadestes lanaiensis ) from Moloka‘i are probably extirpated from the areas searched on that island but may persist on the unsurveyed Oloku‘i Plateau.

Hawai'i↗

USGS2000

Population status of the Tinian Monarch ( Monarcha takatsukasae ) on Tinian, Commonwealth of the Northern Mariana Islands

We conducted surveys to evaluate the current population status of the Tinian Monarch ( Monarcha takatsukasae ), an insectivorous forest bird restricted to the island of Tinian, Commonwealth of the Northern Mariana Islands. In 1996, we recounted transects surveyed in 1982 and used the same analysis procedure to compare 1982 and 1996 population estimates. The 1996 population estimate was 55,721 ± 3,846 SE (48,345–63,495 95% CI), which is 57% higher than our estimate of 35,846 ± 2,211 SE (31,668–40,337 95% CI) for 1982. Vegetation density, measured by canopy cover and lateral visibility at each station, has also increased since 1982. Our data suggest that the Tinian Monarch population has increased possibly due to increased habitat availability, but remains at risk both from an accidental introduction of brown tree snakes ( Boiga irregularis ) to the island and stochastic processes.

Tinian↗

USGS1998

Ou ( Psittirostra psittacea )

The ‘Ö‘ü and the Läna‘i Hookbill are plump, predominantly olive green, thick-billed Hawaiian honeycreepers. The ‘Ö‘ü is now very rare and restricted to remote, high-elevation native forest, and the Läna‘i Hookbill is extinct. They are closely related species, belonging to a specialized tribe, Psittirostrini, consisting of nine historically known Hawaiian species with heavy, finchlike to parrotlike bills. Because of their taxonomic affinity and the paucity of information on the Läna‘i Hookbill, we are treating the two species in a single account.

Birds of North America↗

USGS1997

Evidence of Newell's Shearwater breeding in Puna District, Hawaii

Nocturnal surveys using auditory cues and night-vision equipment were conducted during the seabird breeding season in 1993 to determine use of inland areas in the Puna District, Hawaii by Newell's Shearwater ( Puffinus auricularus newelli ). Two hundred sixty Newell's Shearwater auditory or visual detections were made during 275 survey hours from 23 Jul. 1993 - 20 Sep. 1993. Mean detection rates were 1.26 birds/h at Puulena Crater ( n = 160 Newell's Shearwater detections), 1.05 birds/h at Heiheiahulu ( n = 99) and 0.04 birds/ h at Puu Kaliu ( n = 2). Vocalizing peaked between 50 and 90 min after sunset and 4 h before sunrise. Although night-vision equipment was used on most of the seabird surveys, only 4% of seabirds were detected visually. Two road-killed birds collected in Puna in June 1993, and four burrows located in Puulena Crater after the 1994 breeding season, provided additional evidence of breeding.

Hawaii↗

USGS1997

Kauai's endangered solitaires: Update on population status and distribution 1996

The puaioihi ( Myadestes palmeri ) and the kamao ( M. myadestinus ) are endangered solitaires endemic to Kauai in the Hawaiian Islands and now restricted to the Alakai Swamp. The puaiohi has been rare historically with population estimates declining since the first population surveys 1968-73. Puaiohi were believed to be on the verge of extinction with population estimates less than 35 birds since 1981. In 1995 intensive studies of the breeding biology and population status of the puaiohi began using mist netting, color banding, spot mapping, and surveys. Fifty active nests were discovered and 63-75 birds monitored at the Koaie study site. Seven survey expeditions in 1996 detected 55-70 more puaiohi from 6 of 8 main river drainages of four survey areas explored. Although still rare and vulnerable to extinction (145±19 individuals known), puaiohi are more widely distributed within the Alakai Swamp than previously believed. Our data from 1996 suggest previous surveys methods have underestimated the population size or that the population has increased since 1981. The kamao has not been confirmed since 1985, but unconfirmed reports were made from 1989-1996. We have not sighted kamao to date despite intensive search efforts. We infer from detection probabilities that the species in highly likely to be extinct.

Hawaii↗