Browsing by Author "Laut, Megan"

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    Hawaiian forest bird conservation strategies for minimizing the risk of extinction: biological and biocultural considerations
    (2022-04-14) Paxton, Eben H.; Laut, Megan; Enomoto, Stanton; Bogardus, Michelle
    The iconic forest birds of Hawai‘i are facing a conservation crisis. Across the Hawaiian Islands, native forest birds have been experiencing population declines that have accelerated in the last one to two decades. While habitat loss, invasive species, and non-native predators have negatively affected forest bird species for hundreds of years, and continue to do so, introduced diseases, particularly avian malaria, are the greatest threat to forest birds today. Further, climate change has increased temperatures in the high-elevation forests, facilitating the spread of disease into areas that were once largely disease-free. Rapid population declines have now (2022) pushed four Hawaiian honeycreeper species to the brink of extinction: the endangered ‘akikiki (Oreomystis bairdi) and ‘akeke‘e (Loxops caeruleirostris) on Kaua‘i Island, and kiwikiu (Pseudonestor xanthophrys) and ‘ākohekohe (Palmeria dolei) on Maui Island. The biologists that study these birds strongly agree that without a rapid conservation response to the threat of increasing disease mortality there is a high probability these species will go extinct in the coming decade. To help evaluate alternative conservation strategies for minimizing the risk of extinction, we convened diverse groups of experts with broad experience in Hawai‘i forest birds and ecosystems, as well as the management approaches being considered, to assess the probability of success of alternative management actions. In addition to assessing this crisis from a biological perspective, we convened a group of Native Hawaiian participants that have a strong connection to the forest birds, forests, and the integration of their culture in natural and biocultural resource management. They give voice to the significance of forest birds to Native Hawaiians and provide their perspectives on alternative management actions. Broadly, the three alternative management actions being considered to prevent the extinction of forest birds from the increasing threat of disease are (1) landscape-level mosquito control through the Wolbachia incompatible insect technique, (2) captive care, and (3) conservation translocations. The two key components of the problem of preventing extinction in these four bird species is time and risk. For each species, very few individuals remain, and they are all in danger of imminent extinction. Each management action takes time to implement, which might exceed the actual time to extinction. Additionally, each of these conservation actions has potential benefits and inherent risks, as well as substantial uncertainty in terms of being successful. Native Hawaiian perspectives and considerations also vary across the conservation actions. The expert evaluations summarized in this report provide a broad assessment of conservation strategies that could be undertaken to prevent the extinction of ‘akikiki, ‘akeke‘e, kiwikiu, and ‘ākohekohe. While this report does not recommend specific actions, the information is intended to support decision-makers as they assess which, if any, conservation strategies to pursue. // Ke hālāwai nei nā manu o ka nahele o Hawai‘i me ka pōpilikia maluō. Ma ka pae ‘āina ‘o Hawai‘i, ke emi mai nei nō ka nui manu a keu aku ma nā makahiki he 10 a 20 i hala aku nei. I loko nō o ka pā hewa o ka manu no nā makahiki he lō‘ihi a he mau haneli i ka nele o kahi e noho ai, ka lāhulu komo hailapu, a me ka po‘ii‘a malihini, ‘o ka ma‘i malihini, ‘o ia ho‘i ka avian malaria, ka mea nui e pau nei ka manu ‘ānō. Ua pi‘i pū ho‘i ka mehana o ka nahele o nā wao ki‘eki‘e a‘e i ka mehana honua e laha ai ua ma‘i nei i nā wahi loa‘a mua ‘ole o ua ma‘i nei. Ua lilo ka pau ‘emo ‘ole ‘ana o ka manu he kumu e pau nei ka ‘ehā lāhulu manu mūkīkī i ka make loa: ‘o ka ‘akikiki (Oreomystis bairdi) lāua me ka ‘akeke‘e (Loxops caeruleirostris) ma ka mokupuni ‘o Kaua‘i a me ke kiwikiu (Pseudonestor xanthophrys) lāua me ka ‘ākohekohe (Palmeria dolei) ma ka mokupuni ‘o Maui. Ua lōkahi ka mana‘o o nā akeakamai kālaimeaola nāna e noi‘i ana i kēia po‘e manu, he nui loa ka papaha o ka pau o ua mau lāhulu nei i ka make loa i loko o nā makahiki he ‘umi e hiki mai auane‘i ke pa‘a ‘ole ke ki‘ina ho‘omaluō e lapa‘au ai. I mea e kālailai ‘ia ai nā ka‘akālai ho‘omaluō e emi ai ka pau loa ‘ana o ka manu i ka make loa, ua ho‘ohui ‘ia nā mea mākaukau o nā ‘ano like ‘ole nona ka ‘ike laulā i ka manu o ka nahele a kaiaola o Hawai‘i a me nā ala ho‘omalu e no‘ono‘o ‘ia ana e noi‘i ai i ka papaha o ka puka o ua mau ki‘ina ho‘omalu nei. Ma waho o ka noi‘i i ka pōpilikia ma ke kuana‘ike kālaimeaola, ua ho‘ohui pū ‘ia he hui o nā kānaka Hawai‘i nona ka pilina ikaika i ka manu o ka nahele, ka nahele, a me ka ‘āwili ‘ia o ka mo‘omeheu Hawai‘i ma ka ho‘omalu kumuwaiwai ao kūlohelohe e komo ai ka mana‘o i ka mea nui o ka manu i ke kānaka Hawai‘i me ka hāpai pū ‘ia o ka mana‘o no nā ki‘ina ho‘omalu pū kekahi. Ma ka laulā, he ‘ekolu ki‘ina ho‘omalu e no‘ono‘o ‘ia nei he ala e pau ‘ole ai ka manu o ka nahele i ka make loa, 1) ke kāohi makika ma o ka Wolbachia incompatible insect technique, 2) ka hānai ka‘awale, a me 3) ka ho‘omaluō ka‘awale. ‘O ka manawa a me ka ‘a‘a i ka hana nā kumuloli nui ‘elua o ke pani i ka pau ‘ana o kēia mau lāhulu manu ‘ehā i ka make loa. No kēlā me kēia lāhulu, kāka‘ikahi nō ke koe ‘ana mai o kona mau manu a ke hālāwai maoli nei nō me ka pōpilikia o pau i ka make loa. He wā ka mea e pono ai kēlā me kēia ki‘ina ho‘omalu e hele ana paha a ma ‘ō aku o ka manawa e pau ai ua mau manu nei i ka make loa. He hopena maika‘i a maika‘i ‘ole nō paha ko kēia mau ki‘ina ho‘omalu, a pēlā pū ke kānalua nui i ka puka a me ka puka ‘ole nō paha. ‘Oko‘a pū ke kuana‘ike o ke kānaka Hawai‘i no kēlā me kēia ki‘ina ho‘omalu. Hō‘ike nā mana‘o o nā mea mākaukau i hō‘ulu‘ulu ‘ia ma kēia mo‘olelo he ‘ike laulā no nā ki‘ina ho‘omaluō e lawelawe ‘ia e pani ‘ia ai ka pau ‘ana o ka ‘akikiki, ka ‘akeke‘e, ke kiwikiu, a me ka ‘ākohekoke i ka make loa. I loko nō o ka hāpai ‘ole ‘ia o nā ki‘ina pono‘ī, i mea ho‘i ka ‘ike o loko e kāko‘o ‘ia ai nā mea nona ka mana ho‘oholo ma ke koho paha i ke ki‘ina ho‘omaluō e ‘imi ‘ia aku.
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    Status and trends of the land bird avifauna on Tinian and Aguiguan, Mariana Islands.
    (2016-01-26) Camp, Richard; Pratt, Thane; Amidon, Fred; Marshall, Ann; Kremer, Shelly; Laut, Megan
    Avian surveys were conducted on the islands of Tinian and Aguiguan, Marianas Islands, in 2008 by the U.S. Fish and Wildlife Service to provide current baseline densities and abundances and assess population trends using data collected from previous surveys. On Tinian, during the three surveys (1982, 1996, and 2008), 18 species were detected, and abundances and trends were assessed for 12 species. Half of the 10 native species—Yellow Bittern (Ixobrychus sinensis), White-throated Ground-Dove (Gallicolumba xanthonura), Collared Kingfisher (Todiramphus chloris), Rufous Fantail (Rhipidura rufifrons), and Micronesian Starling (Aplonis opaca)—and one alien bird—Island Collared-Dove (Streptopelia bitorquata)—have increased since 1982. Three native birds—Mariana Fruit-Dove (Ptilinopus roseicapilla), Micronesian Honeyeater (Myzomela rubratra), and Tinian Monarch (Monarcha takatsukasae)—have decreased since 1982. Trends for the remaining two native birds—White Tern (Gygis alba) and Bridled White-eye (Zosterops saypani)—and one alien bird—Eurasian Tree Sparrow (Passer montanus)—were considered relatively stable. Only five birds—White-throated Ground-Dove, Mariana Fruit-Dove, Tinian Monarch, Rufous Fantail, and Bridled White-eye—showed significant differences among regions of Tinian by year. Tinian Monarch was found in all habitat types, with the greatest monarch densities observed in limestone forest, secondary forest, and tangantangan (Leucaena leucocephala) thicket and the smallest densities found in open fields and urban/residential habitats. On Aguiguan, 19 species were detected on one or both of the surveys (1982 and 2008), and abundance estimates were produced for nine native and one alien species. Densities for seven of the nine native birds—White-throated Ground-Dove, Mariana Fruit-Dove, Collared Kingfisher, Rufous Fantail, Bridled White-eye, Golden White-eye (Cleptornis marchei), and Micronesian Starling—and the alien bird—Island Collared-Dove—were significantly greater in 2008 than 1982. No differences in densities were detected between the two surveys for White Tern and Micronesian Honeyeater. Three native land birds—Micronesian Megapode (Megapodius laperouse), Guam Swiftlet (Collocalia bartschi), and Nightingale Reed-Warbler (Acrocephalus luscinia)—were either not detected during the point-transect counts or the numbers of birds detected were too small to estimate densities for either island. Increased military operations on Tinian may result in increases in habitat clearings and the human population, which would expand human-dominated habitats, and declines in some bird populations would be likely to continue or be exacerbated with these actions. Expanded military activities on Tinian would also mean increased movement between Guam and Tinian, elevating the probability of transporting the brown tree snake (Boiga irregularis) to Tinian.