Parasites of Wild and Captive Nene Branta Sandvicensis in Hawaii

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Parasites of Wild and Captive Nene Branta Sandvicensis in Hawaii Parasites of wild and captive Nene Branta sandvicensis in Hawaii TOM BAILEYand JEFFREYBLACK The risk of introducing disease or parasites into the wild has long concerned managers involved in the Nene recovery programme. In this initial survey helminth eggs were found in samples from 17 of 77free-ranging Nene and eight of 28 captive Nene, giving an overall prevalence of 22%. Percent prevalence, estimated for each of the nine collection sites, was not correlated with bird density. No haemoparasites were detected on micro- scopic examination of the blood smears. A longer term study to determine the dynamics of the Nene-parasite relationship is needed to confirm the initial suggestion that the birds' recovery probably is not limited by heavy parasite infection. Keywords: Nene, Hawaiian Goose, Parasites, Threatened Species The Hawaiian Goose or Nene Branta the risk of disease in threatened popula· sandvicensis is the only endemic goose tions, especially where captive animals surviving on the Hawaiian archipelago are involved through reintroduction pro- and, in 1951,there were just 30 Nene left grammes (Scott et al; 1986, Seal 1991). in the wild (Smith 1952). An intensive Endemic Hawaiian avifauna evolved in international captive breeding and the absence of many diseases common release programme has succeeded in in continental areas and it is believed reintroducing many Nene to the wild. that a reduction in the effectiveness of Restocking began in 1960 and there are immunogenic mechanisms has occurred 500 Nene currently living in the wild on (van Riper & van Riper 1985). Thus, three of the larger Hawaiian islands when native birds encounter introduced (Black et al. 1991). The release pro- pathogens they may be affected more gramme has prolonged effectively the severely than introduced birds. Malaria extinction process, but potent limiting has played a significant role in reducing factors in Hawaii are still active and native Hawaiian birds' populations (van inhibiting recovery (Black & Banko 1994, Riper et al. 1982, Warner 1986, Cooper Black 1995). Managers and researchers 1989). Current studies on the impact of concerned with the management of wild disease on Hawaiian avifauna on Big Nene have suggested that parasitic Island are finding that 75% of native infections and/or other diseases may be passerines dying in National Parks are factors responsible for the Nene's poor infected with both avian pox and productivity (Kear & Berger 1980, Stone malaria (C. Atkinson, pers. comm.). et al. 1983). The risk of infecting a susceptible wild Disease has long been recognised as a population with a disease originating in potent selective factor in the evolution captive stock is a serious concern. In of all organisms (Loye & Zuk 1992). 1987, an outbreak of gapeworm Hudson (1986) has shown that the Cyathostoma bronchialis caused mortal- nematode parasite Trichostrongylus ity in a Nene flock at the Hawaiian tenuis can reduce the productivity of Breeding Centre (Gassman-Duvall 1987). wild populations of Red Grouse Lagopus It was considered that this parasite, pre- scoticus. Conservationists are also viously unreported from the Hawaiian becoming increasingly concerned about Islands, was introduced by migratory 59 Wildfowl 46 (1995): 59-65 60 Parasites and Hawaiian Geese geese or via the introduction of Rio behavioural observations. When birds Grande Turkeys Meieagridis gallopauo were observed defecating, the faecal near to the Centre (although there was samples were collected and, where pos- no evidence in the literature that turkeys sible, the bird's identity was recorded. are infected by gapeworms). Fresh faecal samples were collected from Introductions of native species bred else- 113different geese and preserved in 10% where must be examined carefully and formal saline. They were examined for this applies especially to the Nene rein- helminth eggs and coccidian oocysts troduction programme because several using the standard methods of coverslip potentially serious diseases, that have flotation and McMaster's technique not yet been reported on the Hawaiian (Bailey 1989). The coverslip flotation Islands, have been found in the captive method detected those samples infected Hawaiian Geese in England (van Riper & with helminth eggs and McMaster's tech- van Riper 1985,Kear & Berger 1980). nique was performed on all helminth This project was one of 13 studies positive samples to estimate the number aimed at assessing the causes of the of eggs per gramme of faeces. low productivity and survival of Birds that were handled were given a Hawaiian Geese that have been clinical examination and checked for released into the wild (see Nene ectoparasites. Blood samples were col- Recovery Initiative - Black 1990, Black lected in EDTApaediatric tubes from the et ai. 1991, Black 1995). The initiative, brachial vein. Blood smears were pre- launched in November 1990, is a collab- pared, stained and examined microscop- orative project between The Wildfowl & ically for blood parasites according to Wetlands Trust, four organisations in the method of Gulland & Hawkey (1990). Hawaii (Division of Forestry & Wildlife, Packed cell volumes (pCV) were mea- National Park Service, National sured using a field centrifuge (Ames, Biological Survey and US Fish & Wildlife Microspin, Bayer Diagnostics). Service) and the National Zoological Accounts of other diseases, including Park, Smithsonian Institute. parasitic infections, were gathered from Managers and scientists have sug- meetings with avian veterinarians who gested several, potential biological fac- have examined wild and captive Nene tors that may be limiting the growth of over the years. the Hawaiian Goose population (see Black 1995). The aim of this study was to begin to assess the distribution of Results parasites in free-living and captive Hawaiian Geese in Hawaii. This base- Helminth eggs and/or cestode eggs line information provides a foundation were detected by coverslip flotation in for future health monitoring and 22% of the 113 samples (Table 1). Eggs screening programmes for the Nene were found in samples from 17 of 77 restoration programme. free-ranging Nene and eight of 28 cap- tive Nene; the difference between sam- ples was not significant statistically Materials and methods (X'=O.OO, df=l, NS). Few eggs were found in infected samples by coverslip flota- This study was carried out from 18 tion and all coverslip flotation positive November to 7 December 1992 on the samples were McMaster's negative, Hawaiian islands of Oahu, Maui and which indicated that the birds were not Hawaii. Wild birds (many of which were burdened heavily with helminth para- marked individually with colour leg sites. Between one and 15 eggs were bands) were sampled in a variety of counted per faecal sample (mean=2.8, habitats, notably release sites, supple- SD=3.4)and in most cases only one egg mentary feeding sites, areas with the was found using the coverslip flotation largest flocks and at a variety of captive technique; single eggs were found in 16 flocks in Hawaii. Galliforms occurred in of the 27 positive samples where the egg all of the wild areas. number was quantified. Six nematodes Faecal samples were collected from were identified using parasite identifica- Nene in the field during the course of tion guides (Janssen Pharmaceuticals Parasites and Hawaiian Geese 61 Table 1. Frequency of Hawaiian Goose faecal samples that contained helminth eggs from various locations In Hawaii. Site Samples Samples (birds (bird containing in region) density) helminth n (ha) eggs n Prevalence % Hawaii Kipuka Ainahou b 3 2 67 Pu'u 6677 b 2 0 o Pu'u Lani Ranch I 0 o Keauhou '" 6 I 17 Ainapo Corral 6 1 17 Kaaua bd 6 3 50 Volcanoes National Park 27 5 19 'Ainahou Pens' 5 3 60 Kahuku Pens' 5 I 20 Maul Haleakala National Park 20 3 15 Haleakala Pens'b 2 0 o Headquarters Area d 6 2 33 Olinda ESF' 15 2 13 Qillru Honolulu Zoo' 7 2 29 Waimea Falls' 2 0 o Total JJ:J 25 22 , = Nene housed in a captive situation. b = collected near feeder where other birds visit '= recent release from Olinda d = not strictly a wild area Note: Sites visited in Volcanoes Park included Kipuka Nene Campsite, 'Ainahou free-ranging birds, golf course, observatory nest, Keanakakoi Crater. Sites visited in Haleakala National Park included Kapalaoa cabin, Paliku cabin, Lau'ulu trail, Holua cabin. Note: Three indices of bird density estimated as 1) number of droppings per 10m2, 2) number of birds found in collection areas at anyone time and 3) flock size in the area: Kipuka Ainahou (3.5 droppings, 2 birds, 10 birds), Pu'u 6677 (1.5, 5, ]5), Pu'u Lani Ranch (0.5, 2,15), Keauhou (0.5, 4,10), Ainapo Corral (2, 4, 15), Kaaua (3, 10,30), Volcanoes Nationall'ark (0.4, 2.5, 130), Haleakala National Park (I, 3.3, 130), Headquarters Area (0.5, 0.8, 130). Table 2. Packed cell volume (pCV) results, clinical examination findings and blood smear readings for haemoparasites from five Hawaiian Geese at the Kahuku Ranch pens. Bird ID PCV/% Clinical examination Haemoparasite result VP 56 no abnormality detected negative VS 54 no abnormality detected negative J8 46 no abnormality detected negative ZX 58 no abnormality detected negative JA 48 no abnormality detected negative 62 Parasites and Hawaiian Geese Diagnosing Helminthiasis): Ascaridia reported as 46%+/-2% (Fowler 1986). spp., Heterakis spp., Amidostomum The average PCV for the five Nene was anseris, Trichostrongylus tenuis, 52.4%+/-5.2%. Echinuria uncinata and Capillaria spp. Echinuria uncinata which had not been identified previously on the Hawaiian Discussion Islands (van Riper & van Riper 1985). The presence of cestode eggs and coc- The health of the 150strong flock of cap- cidian oocysts was also recorded, but tive Nene at The Wildfowl & Wetlands these were not counted or identified; Trust Centres has been monitored coccidia were recorded in 18 of 113 fae- closely since 1960 by M.J.
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