Research Article |
Corresponding author: Stefano Taiti ( stefano.taiti@cnr.it ) Academic editor: Didier Bouchon
© 2015 Stefano Taiti, J. Judson Wynne.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Taiti S, Wynne JJ (2015) The terrestrial Isopoda (Crustacea, Oniscidea) of Rapa Nui (Easter Island), with descriptions of two new species. In: Taiti S, Hornung E, Štrus J, Bouchon D (Eds) Trends in Terrestrial Isopod Biology. ZooKeys 515: 27–49. https://doi.org/10.3897/zookeys.515.9477
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Nine species of terrestrial isopods are reported for the Polynesian island of Rapa Nui (Easter Island) based upon museum materials and recent collections from field sampling. Most of these animals are non-native species, but two are new to science: Styloniscus manuvaka sp. n. and Hawaiioscia rapui sp. n. Of these, the former is believed to be a Polynesian endemic as it has been recorded from Rapa Iti, Austral Islands, while the latter is identified as a Rapa Nui island endemic. Both of these new species are considered ‘disturbance relicts’ and appear restricted to the cave environment on Rapa Nui. A short key to all the oniscidean species presently recorded from Rapa Nui is provided. We also offered conservation and management recommendations for the two new isopod species.
Crustacea, Isopoda, Oniscidea, new species, Rapa Nui, Easter Island, disturbance relicts, caves
Rapa Nui (Easter Island) is one of the most ecologically degraded islands in Polynesia. A number of factors including geographic isolation, island size and low topographic relief (
Contemporarily, few native plant species remain and all terrestrial vertebrates have gone extinct (
Through fieldwork led by the second author, at least eight island endemic and two Polynesian endemic arthropod species have been recently identified (
With the exception of the Hawaiian islands (
Fieldwork was conducted on the Roiho lava flow, ~5 km north of the village of Hanga Roa during three research trips in 2008, 2009 and 2011. The study area is characterized by gently rolling hills (i.e., extinct scoria cones) with coastal cliff faces flanking the western-most boundary. Vegetation was grassland and invasive guava (Psidium guajava) shrub. Within the collapse pit and skylight entrances of most caves, several non-native tree species occurred, including fig (Ficus sp.), avocado (Persea americana), apple banana (Musa × paradisiaca), roseapple (Syzygium jambos), guava (Psidium guajava) and Eucalyptus spp.
Caves are zonal environments often consisting of four principle zones: (1) an entrance (or light) zone representing a combination of both surface and cave climatic conditions; (2) a twilight zone where light is diminished and surface climate conditions are progressively dampened; (3) a transition zone characterized by complete darkness with a further diminished influence of surface climate conditions; and, (4) a deep zone (usually the deepest portion of the cave) where environmental conditions (e.g., complete darkness, temperature, and air flow) remain relatively stable over time and the evaporation rate is negligible (
Cave and surface sampling was conducted. Research teams (led by the second author) systematically sampled 10 caves during three research trips (16–21 August 2008; 28 June–17 July 2009; and 01–07 August 2011). Four methodologies (pitfall traps, time-constrained searches, opportunistic collecting, and timed direct intuitive searches) were applied to sample 10 caves during the first two trips. Pitfall trap construction consisted of two 946-ml stacked plastic containers (13.5 cm high, 10.8-cm-diameter rim and 8.9-cm base). A teaspoon of peanut butter placed in the bottom of the exterior container was used as bait. The bottom of the interior container had several dozen holes to allow the bait to “breathe” to attract arthropods. Traps were deployed for three to four days.
Time-constrained searches involved estimating a one-meter radius around each pitfall trap sampling station and then conducting a timed search. Searches were conducted for one to three minutes (one minute if no arthropods were observed, three if arthropods were detected) before pitfall trap deployment and prior to trap removal.
Opportunistic collection involved collecting arthropods as encountered – while deploying and removing pitfall traps, and between timed searches. During these intervals, personnel searched the ground, walls and ceilings as they walked the length of each cave. In five caves (where all the collecting methodologies were applied), we also conducted timed direct intuitive searches (DIS) of fern-moss gardens by gently combing through the fern and moss and looking beneath rocks for 40 search-minutes per garden (two observers × 20 minutes per observer). In four additional caves, we limited sampling to DIS within fern-moss gardens only (two observers × 20 minutes per observer).
During the last research trip to the island, the deep zones of four of the caves were sampled via bait sampling and DIS. Three types of baits were placed directly on the ground and within cracks and fissures on cave walls, ceilings and floors: sweet potato (Ipomoea batatas), chicken and fish entrails, and small branches from local hibiscus (Hibiscus rosa-sinensis) and Gaoho (Caesalpinia major) shrubs. Two to three stations of each bait type were deployed, for four to five days, within the deep zone(s) of each cave. At proximity to bait sampling arrays, we also conducted one DIS by searching the cave floor for 10 minutes within a 1-m2 area.
From 28 June through 08 July 2009 (total of 10 days), we deployed two 15 x 20 meter surface pitfall trapping grids. Surface Grid 1 (with trap numbers 1 - 20) was established inland at the approximate center of our study area. Surface Grid 2 (with trap numbers 21 - 40) was deployed at the western extent of the study area (~250 m from the coastal cliff face). All pitfall traps were countersunk to ground surface with trap spacing at 5 m between each trap.
For additional information on sampling refer to
We recognize standard practice for locality information is to provide geographical coordinates to facilitate future collecting and interpretation. However, Chilean park officials have requested that neither cave names nor coordinates be included due to cultural and natural resource sensitivities of caves. In place of cave names, we used cave codes supplied by CONAF – Parque Nacional Rapa Nui. A copy of this paper, which includes a table of cave names with associated cave codes, is on file with CONAF – Parque Nacional Rapa Nui headquarters Hanga Roa, Easter Island, and CONAF, Jefe Departamento, Diversidad Biológica, Gerencia de Areas Protegidas y Medio Ambiente, Santiago, Chile.
All material was preserved in 95% ethanol. Identifications were based on morphological characters with the use of micropreparations. Line drawings were made with the aid of a camera lucida mounted on Wild M5 and M20 microscopes. Whole-specimen images were captured using a 1.1 MP Canon 5D Mark II (with a 65 mm zoom lens) mounted on a Visionary Digital BK Lab Plus camera mounting system. We used the program Zerene Stacker to merge images into a composite image. Photoshop CS5 was used for image post-processing.
AMNH American Museum of Natural History, New York, USA;
BPBM Bernice P. Bishop Museum, Honolulu, Hawai‘i, USA;
MNHN Museo Nacional de Historia Natural, Santiago, Chile;
MZUF Museo di Storia Naturale, sezione di Zoologia, dell’Università di Firenze, Florence, Italy;
YPM Peabody Museum of Natural History, Yale University, New Haven, Connecticut, USA.
Ligyda exotica;
The record of this species by
Pantropical.
Styloniscus sp.;
Chile, Rapa Nui: 1 ♂ holotype, 2 ♂♂, 2 ♀♀, 1 juv. paratypes (MNHN), Mahunga Hiva Hiva, Cave Q15-070, fern-moss garden (entrance zone), direct intuitive search, 10.VII.2009, leg. J.J. Wynne; 2 ♂♂, 1 ♀, 2 juvs. paratypes (MZUF), same location, 50 m from entrance, direct intuitive search (on decomposing tree branches; twilight zone), 6.VIII.2011, leg. J.J. Wynne; 1 ♀ paratype (MNHN), same data; 1 ♂, 1 ♀ paratypes (BPBM), Mahunga Hiva Hiva, Cave Q15-074, skylight entrance (1st entrance NE of main entrance; entrance zone), 3.VII.2009, leg. J.J. Wynne; 1 ♀ paratype (BPBM), Mahunga Hiva Hiva, Cave Q15-119, timed search at trap 4A, 5.VII.2009, leg. J.J. Wynne; 1 ♂ paratype (BPBM), same location, Zone 2 (approx. cave deep zone), trap, fish entrails 1, 6.VIII.2011, leg. J.J. Wynne; 1 ♀ paratype (BPBM), Mahunga Hiva Hiva, Cave Q15-071, Zone 2 (approx. cave deep zone), bait trap, fish entrails 1, 7.VIII.2011, leg. J.J. Wynne; 1 ♀ paratype (BPBM), Cave Q15-067, fern-moss garden (entrance zone), direct intuitive search, 4.XII.2008, leg J.J. Wynne.
French Polynesia, Bass Islands (Austral Islands), Rapa Iti Island: 4 ♂♂ (YPM), Pumarua-Maurua Ridge, Pumarua and some west, 500-620 m, from dead leaves of the bird’s nest fern, Asplenium nidus, 9.I.1980, leg. G. Paulay.
Maximum length: ♂ 4 mm, ♀ 4.2 mm. Dorsum brown with the usual yellow muscle spots (Fig.
Male. Pereopod 1 (Fig.
The species name is a combination of two Rapanui terms, manu and vaka. Manu is “bug” and vaka is “canoe” or “boat”; when combined this translates to “canoe bug.” Based upon the identification of this species, and a collembolan (Lepidocyrtus olena Christiansen & Bellinger, 1992) previously known from the Hawaiian Islands only,
At present the genus Styloniscus includes about 45 species distributed in the tropics and the southern hemisphere (
On Rapa Nui, Styloniscus manuvaka sp. n. is presently restricted to the cave environment, but is not troglomorphic (cave-adapted). This animal was detected within the fern-moss gardens (entrance zone) of three caves, but also occurred within the twilight and cave deep zones. This species was not detected during the surface sampling work conducted in 2009, nor has it been identified during previous invertebrate inventory work (e.g.,
Presently known from Rapa Nui and Rapa Iti.
Hawaiioscia sp.;
Chile, Rapa Nui: 1 ♂ holotype, 2 ♀♀ paratypes (MNHN), Mahunga Hiva Hiva, Cave Q15-034, pitfall trap 5A (twilight zone) 12.VII.2009, leg. J.J. Wynne; 1 ♀ paratype (MZUF), 1 ♀ paratype (BPBM), same data, pitfall trap 7A (approx. deep zone); 1 ♂ Paratype (MZUF), Mahunga Hiva Hiva, Cave Q15-076/078, pitfall trap 2C (light zone), 4.VII.2009, leg. J.J. Wynne.
Maximum length: ♂ and ♀ 7.5 mm. Dorsum light brown with the usual muscle spots (Fig.
Hawaiioscia rapui sp. n., ♂ holotype: A adult specimen in dorsal view. ♀ paratype: B dorsal scale-seta C co-ordinates of noduli laterales D cephalon in dorsal view E cephalon in frontal view F cephalon in lateral view G pereonites with noduli laterales H pleonite 5, telson and uropods I antennula.
Male. Pereopod 1 carpus with a brush of trifid spines on sternal margin (Fig.
The new species is named after Sergio Rapu Haoa, a humanitarian who has furthered cultural and archeological knowledge of Rapa Nui. Sergio was Rapa Nui’s first governor of Rapanui descent and the first director and curator of Museo Antropológico P. Sebastián Englert on Rapa Nui. He is also a world-renowned Rapa Nui archaeologist and purveyor of Rapa Nui culture. He graciously provided logistical support to the second author and his research teams while on Rapa Nui.
Prior to discovering this new species, the genus Hawaiioscia consisted of four troglomorphic species restricted to lava tube caves on the Hawaiian Islands (Schultz 1973;
Specimens from this new species were collected from both within the entrance zone of one cave and the twilight zone of another cave. It is important to note, this species does not have troglomorphic characteristics, such as body depigmentation or eye reduction as do other congeners within Hawaiioscia. However, as with Styloniscus manuvaka sp. n., this new species was not detected during the surface sampling effort, nor has it been previously identified by earlier entomological surveys of the island. Thus, we believe this animal to be restricted to cave environment on Rapa Nui.
Presently endemic to Rapa Nui.
Chile, Rapa Nui: 1 ♀ (BPBM), Mahunga Hiva, Cave Q15-074, pitfall trap 1B (light zone), 30.VI.2009, leg. J.J. Wynne.
Pantropical. Introduced to greenhouses worldwide.
Chile, Rapa Nui: 2 ♂♂, 3 ♀♀ (AMNH 18360), Cannibal Cave, 21.VIII.1999, leg. C. Boyko, J. Tanacredi, S. Reanier, H. Tonnemacher and S. Lopez; 1 ♀ (BPBM), Mahunga Hiva Hiva, Cave, Q15-074, time search at 1A (light zone), 30.VI.2009, leg. J.J. Wynne; 1 ♂, 3 ♀♀ (BPBM), same location, leaf litter beneath skylight, (3rd entrance NW of main entrance; entrance zone), direct intuitive search, 2.VIII.2011, leg. J.J. Wynne; 1 ♀ (BPBM), Mahunga Hiva Hiva, Cave Q15-067, fern-moss garden (entrance zone), direct intuitive search, 10.VII.2009, leg. J.J. Wynne; 1 ♂ (BPBM), Mahunga Hiva Hiva, Cave Q15-070, fern-moss garden (entrance zone), direct intuitive search, 10.VII.2009, leg. J.J. Wynne.
Cosmopolitan species of Mediterranean origin.
Porcellio scaber;
Chile, Rapa Nui: 1 ♀ (AMNH 18362), VIII.1999, leg. C. Boyko, J. Tanacredi, S. Reanier, H. Tonnemacher and S. Lopez; 2 ♂♂, 1 ♀ (AMNH 18363), Maunga Tangaroa, 20.VIII.1999, leg. C. Boyko, J. Tanacredi, S. Reanier, H. Tonnemacher and S. Lopez; 2 ♂♂, 3 ♀♀ (AMNH 18365), Ana te Pahu, 21.VIII.1999, leg. C. Boyko, J. Tanacredi, S. Reanier, H. Tonnemacher and S. Lopez; 2 ♂♂, 13 ♀♀ (AMNH 18364), Poike region, 25.VIII.1999, leg. C. Boyko, J. Tanacredi, S. Reanier, H. Tonnemacher and S. Lopez; 1 ♂ (BPBM), Mahunga Hiva Hiva, surface in front of Cave Q15-038, opportunistic collection (eastern-most collapse pit, southern extent near cave entrance), 18.VIII.2008, J.J. Wynne; 1 ♂ (BPBM), Mahunga Hiva Hiva, surface grid 2, 27°06'41.3"S, 109°25'09.2"W, pitfall trap 21, 10.VII.2009, leg. J.J. Wynne; 1 juv. (BPBM), Mahunga Hiva Hiva, surface in front of Cave Q15-038, timed search at 1C (eastern-most collapse pit on southern extent near cave entrance), 20.VIII.2008, leg. J.J. Wynne; 3 ♂♂ (BPBM), Cave Q15-038, fern-moss garden (entrance zone), direct intuitive search, 4.XII.2008, leg. J.J. Wynne; 1 ♂, 2 ♀♀ (BPBM), Mahunga Hiva Hiva, Cave Q15-076/078, opportunistic collection, 4.VII.2009, leg. J.J. Wynne; 1 ♂, 2 ♀♀ (BPBM), Mahunga Hiva Hiva, Cave Q15-070, fern-moss garden (entrance zone), direct intuitive search, 13.VII.2009, leg. J.J. Wynne; 2 ♂♂, 1 ♀ (BPBM), Mahunga Hiva Hiva, Cave Q15-074, skylight entrance (1st entrance NW of main entrance; entrance zone), opportunistic collection, 3.VII.2009, leg. J.J. Wynne; 1 juv. (BPBM), Mahunga Hiva Hiva, Cave Q15-067, fern-moss garden (entrance zone), direct intuitive search, 10.VII.2009, leg. J.J. Wynne; 1 ♀ (BPBM), Mahunga Hiva Hiva, Cave Q15-127, entrance zone, pitfall trap 1A, 5.VII.2009, leg. J.J. Wynne; 1 ♂ (BPBM), same data, pitfall traps 1B; 1 ♂, 1 ♀ (BPBM), Mahunga Hiva Hiva, surface grid 1, 27°06'53.1"S, 109°24'20.3"W, pitfall trap 3, 10.VII.2009, leg. J.J. Wynne; 1 ♂, 1 ♀ (BPBM), same location, pitfall trap 10, 10.VII.2009, leg. J.J. Wynne; 2 ♂♂, 5 ♀♀ (BPBM), same location, pitfall trap 12, 10.VII.2009, leg. J.J. Wynne.
Cosmopolitan species of western European origin.
Chile, Rapa Nui: 2 ♂♂ (AMNH 18362), VIII.1999, leg. C. Boyko, J. Tanacredi, S. Reanier, H. Tonnemacher and S. Lopez; 2 ♂♂, 1 juv. (AMNH 18363), Maunga Tangaroa, 20.VIII.1999, leg. C. Boyko, J. Tanacredi, S. Reanier, H. Tonnemacher and S. Lopez; 1 ♂, 1 ♀ (AMNH 18365), Cave Q15-074, location within cave not reported, 21.VIII.1999, leg. C. Boyko, J. Tanacredi, S. Reanier, H. Tonnemacher and S. Lopez; 2 ♂♂, 7 ♀♀ (AMNH 18361), La Pérouse Bay, 21.VIII.1999, leg. C. Boyko, J. Tanacredi, S. Reanier, H. Tonnemacher and S. Lopez.
Cosmopolitan species of Mediterranean origin.
Armadillidium vulgare; Fuentes, 1914: 315.
Chile, Rapa Nui: 1 ♂ (AMNH 18362), VIII.1999, leg. C. Boyko, J. Tanacredi, S. Reanier, H. Tonnemacher and S. Lopez; 6 ♂♂, 5 ♀♀ (AMNH 18365), Cave Q15-074, location within cave not reported, 21.VIII.1999, leg. C. Boyko, J. Tanacredi, S. Reanier, H. Tonnemacher and S. Lopez; 3 ♂♂, 9 ♀♀ (AMNH 18366), Hotel Hanga Roa, Hanga Roa, 21.VIII.1999, leg. C. Boyko, J. Tanacredi, S. Reanier, H. Tonnemacher and S. Lopez; 2 ♂♂, 2 ♀♀ (AMNH 18364), Poike region, 25.VIII.1999, leg. C. Boyko, J. Tanacredi, S. Reanier, H. Tonnemacher and S. Lopez; 1 ♂, 1 ♀ (BPBM), Mahunga Hiva Hiva, surface in front of Cave Q15-038, timed search at 1B (eastern-most collapse pit, southern extent near cave entrance), 20.VIII.2008, leg. J.J. Wynne; 1 ♀ (BPBM), Cave Q15-038, fern-moss garden (entrance zone), direct intuitive search, 21.XIII.2008, leg. J.J. Wynne; 2 ♀♀ (BPBM), Mahunga Hiva Hiva, surface grid 2, 27°06'41.3"S, 109°25'09.2"W, pitfall trap 23, 10.VII.2009, leg. J.J. Wynne; 1 ♂ (BPBM), surface grid 1, 27°06'53.1"S, 109°24'20.3"W, pitfall trap 17, 10.VII.2009, leg. J.J. Wynne; 3 ♀♀ (BPBM), same location, pitfall trap 19, 10.VII.2009, leg. J.J. Wynne; 1 ♂, 3 ♀♀ (BPBM), same location, pitfall trap 4, 10.VII.2009, leg. J.J. Wynne.
Cosmopolitan species of Mediterranean origin.
Chile, Rapa Nui: 2 ♂♂ (BPBM), Mahunga Hiva Hiva, surface grid 2, 27°06'41.3"S, 109°25'09.2"W, pitfall trap 39, 10.VII.2009, leg. J.J. Wynne; 1 ♂ (BPBM), same location, pitfall trap 32, 10.VII.2009, leg. J.J. Wynne.
Widespread in tropical and subtropical regions. It has been introduced to European greenhouses. For diagnostic figures of this species see
1 | Antennal flagellum with >10 articles; eye with >100 ommatidia | Ligia exotica |
– | Antennal flagellum with <6 articles, eye with <30 ommatidia | 2 |
2 | Antennal flagellum of 5 articles | Styloniscus manuvaka |
– | Antennal flagellum of 3 or 2 articles | 3 |
3 | Antennal flagellum of 3 articles | Hawaiioscia rapui |
– | Antennal flagellum of 2 articles | 4 |
4 | Body depigmented; eye consisting of a single ommatidium | Trichorhina tomentosa |
– | Body pigmented; eye consisting of several ommatidia | 5 |
5 | Body slightly convex, unable to roll up into a ball | 6 |
– | Body strongly convex, able to roll up into a perfect ball | 8 |
6 | Cephalon with a V-shaped suprantennal line; pereonite 1 with posterior margin straight and posterior corners rounded | Porcellionides pruinosus |
– | Cephalon without suprantennal line; pereonite 1 with posterior margin more or less concave at sides and posterior corners right-angled or acute | 7 |
7 | Dorsal body surface smooth | Porcellio laevis |
– | Dorsal body surface distinctly granulated | Porcellio scaber |
8 | Cephalon with a triangular frontal scutellum; telson trapezoidal; uropod exopodite flattened, filling the gap between telson and pleonite 5 | Armadillidium vulgare |
– | Cephalon with no frontal scutellum; telson hour-glass shaped; uropod protopodite flattened, filling the gap between telson and pleonite 5 | Venezillo parvus |
Nine species of terrestrial isopods are known from Rapa Nui: Ligia exotica, Styloniscus manuvaka sp. n., Hawaiioscia rapui sp. n., Trichorhina tomentosa, Porcellionides pruinosus, Porcellio laevis, P. scaber, Armadillidium vulgare, and Venezillo parvus.
Only one species (Ligia exotica) is littoral, halophilic, and widely distributed along coastal habitats in the tropics. We have not examined any specimens belonging to this species and its identification needs to be confirmed. Littoral habitats have not been adequately sampled on Rapa Nui and other littoral species may also be present on the island. Two species (Trichorhina tomentosa and Venezillo parvus) have a wide distribution in the tropics, and four species of European or Mediterranean origin (Porcellionides pruinosus, Porcellio laevis, P. scaber, and Armadillidium vulgare) are now cosmopolitan. All of these species were introduced to Rapa Nui due to human activities. Styloniscus manuvaka sp. n. and Hawaiioscia rapui sp. n. are Polynesian and Rapa Nui endemics, respectively.
Given that few native arthropod species remain on Rapa Nui (
Despite their persistence, these endemic species are considered imperiled (
Further, the combined effects of global climate change and interactions with non-native species may further threaten the persistence of these endemic isopods. Competition with non-native species has been identified as threatening the persistence of surface-dwelling endemic arthropods on other island ecosystems (see
Conservation and management of these endemic terrestrial isopods (as well as the other endemic species) and their habitats should be a high priority for the Rapanui community, policy makers and resource managers. Given the concerns associated with global climate change and non-native invasive species, a captive breeding program of these new species is recommended. Captive breeding of isopods is relatively easy and inexpensive (
Finally, we know little concerning the distributions of these endemic isopods. We recommend additional surveys be conducted in other caves on the island, as well as in other habitats likely to support terrestrial isopods (and endemic arthropods, in general). This final step will provide resource managers with the ability to better characterize endemic isopod habitat, and to further improve our understanding of the distribution of these animals on Rapa Nui.
JJW wishes to thank Ninoska Cuadros Hucke, Susana Nahoe, and Enrique Tucky of CONAF-Parque Nacíonal Rapa Nui and Consejo de Monumentos, Rapa Nui, for administrative and logistical support. Cristian Tambley of Campo Alto Operaciones and Sergio Rapu provided additional logistical assistance. Javier Les of the Sociedad de Ciencias Espeleológicas and Andrzej Ciszewski of the Polish Expedition team provided cave maps. Kyle Voyles co-developed the cave-dwelling arthropod sampling protocol. Christina Colpitts, Lynn Hicks, Bruce Higgins, Alicia Ika, Talina Konotchick, Scott Nicolay, Knutt Petersen, Lázero Pakarati, Victoria Pakarati Hotus, Pete Polsgrove, Dan Ruby, and Liz Ruther were invaluable in the field. The Explorers Club and the National Speleological Society partially funded the field research. Color images of S. manuvaka sp. n. and H. rapui sp. n. were provided by Caitlin Chapman and Neil Cobb, Colorado Plateau Museum of Arthropod Biodiversity (CPMAB), Northern Arizona University. Jacob Higgins formerly of CPMAB assisted with identifications of known isopod species. Julianna Rapu provided suggestions on etymology and confirmations of Rapa Nui place names. We are also grateful to Dr. Christopher Boyko and Dr. Eric A. Lazo-Wasem for the loan of the material deposited in AMNH and YPM, respectively.