(Odonata: Zygoptera: Coenagrionidae)
Megalagrion oceanicum is endemic to the Hawaiian island of Oahu. M. oceanicum was found historically in the mountain ranges of Koolau and Waianae, and is currently restricted to about seven populations in the Koolau Range. Its limited habitat and small scattered populations may affect long-term stability. The species is susceptible to the effects of habitat loss and introduced species. Research should focus on habitat management and protection, and control of invasive species.
Megalagrion oceanicum is in the family Coenagrionidae (pond damsels), and is one of the larger Hawaiian damselflies. Adults are 47-50 mm (1.9-2.0 in.) in length, with a wingspan of 51 to 55 mm (2.0-2.2 in.). Both sexes have prominent striped patterns; males are predominantly red with dark markings on the thorax and the tops of the last several abdominal segments, while females are pale green. Nymphs are also large, reaching up to 30 mm (1.2 in.) and have long grasping legs and three slender, elongated, pointed (lanceolate) gills at the tip of the abdomen (Polhemus & Asquith 1996).
Megalagrion oceanicum (McLachlan, 1883). The taxonomic status of this species is accepted as valid.
The predaceous aquatic nymphs inhabit rocks and gravel in swiftly flowing sections of perennial mountain streams or the waterfall faces of small cascades. Older nymphs have been observed crawling out of the stream channel and foraging on moss pads on rocks and on wet rock walls (Williams 1936). Adults are strong fliers and fly upward into the overhanging canopy when disturbed.
This species is endemic to Oahu and was historically present in both the Waianae Mountains, where it was first described, and the Koolau Mountain range (Haleauau Stream, Hering Spring stream, Honolulu, Kahamainui Gulch, Kalihi Valley, Kawailoa Stream, Manoa Stream, Moanalua Valley, Palolo Stream, Poamoho Trail, Punaluu, Pupukea, Waiahole Stream, and Waimanalo). It has apparently been extirpated from the Waianae Mountains and is now found only at seven sites in the upper reaches (above 100 meters/300 ft.) of perennial streams on the windward side of the Koolau Range. Individuals are currently collected at higher elevations than was seen historically.
Nymphs inhabit rocks and gravel in swiftly flowing sections of perennial mountain streams or the waterfall faces of small cascades. Older nymphs have been observed crawling out of the stream channel and foraging on moss pads on rocks and on wet rock walls.
Canada – Species at Risk Act: N/A
Canada – provincial status: N/A
USA – Endangered Species Act: Candidate
USA – state status: S2 Imperiled
NatureServe: G2 Imperiled
IUCN Red List: VU Vulnerable
M. oceanicum is a candidate for listing under the Endangered Species Act, and the USFWS is currently developing a proposed listing rule (Federal Register 2007). Published observations and museum collections indicate that this species was well-represented in collections in the early 1900s, and was also collected at lower elevations. It has declined sharply since the 1970s, and is currently restricted to seven populations in the upper drainages of the Koolau mountain range on the windward side. Existing state regulatory mechanisms do not provide sufficient protection.
M. oceanicum is threatened by habitat loss, including water diversion for agricultural purposes, and the effects of introduced species. Hawaiian damselflies evolved in the presence of few predatory fish, and nymphs exhibit exposed swimming and feeding behaviors that make them vulnerable to predation by poeciliid fish introduced for mosquito control (McPeek 1990). It is possible that populations are negatively impacted by predation from introduced backswimmers (Hemiptera: Notonectidae) and resource competition from introduced caddisflies (Trichoptera). Habitat may also be threatened by the invasive plant California grass (Brachiaria mutica), which forms dense stands that can eliminate standing water. Small scattered populations are vulnerable to the effects of inbreeding and decreased genetic diversity, and the impacts of natural events such as drought or hurricanes.
Necessary actions include monitoring known populations and searching for new ones, and protecting habitat in regions where the species is known to occur.
Research into habitat management and the interactions and potential competition between the endemic M. oceanicum and introduced invertebrate species would be valuable.
Englund R. A. 1999. The impacts of introduced poeciliid fish and Odonata on the endemic Megalagrion (Odonata) damselflies of Oahu Island, Hawaii. Journal of Insect Conservation 3:225-243.
Federal Register Environmental Documents. 2007. Endangered and Threatened Wildlife and Plants; Review of Native Species That Are Candidates for Listing as Endangered or Threatened; Annual Notice of Findings on Resubmitted Petitions; Annual Description of Progress on Listing Actions. Vol. 72:234.
Hawaiian Terrestrial Arthropoda Checklist. 2nd Edition. 1994. Nishida, G.M. (ed.) Hawaii Biological Survey, Contribution No. 94-04. Bishop Museum. Honolulu, Hawaii. 287 pp.
McLachlan, R. 1883. Neuroptera of the Hawaiian Islands. Part I. pseudo-Neuroptera. Ann. Mag. Nat. Hist., (V) 12:226-240.
McPeek, M.A. 1990. Behavioral differences between Enallagma species (Odonata) influencing differential vulnerability to predators. Ecology 71:1714-1726.
Polhemus, D.A. and Asquith, A. 1996. Hawaiian Damselflies. A field identification guide. Bishop Museum Press, Honolulu.
U. S. Fish and Wildlife Service. 2007. Species assessment for the Oceanic Hawaiian damselfly. Available online.
Williams, F.X. 1936. Biological studies in Hawaiian water-loving insects. Part 1. Coleoptera or beetles. Part 2. Odonata or dragonflies. Proceedings of the Hawaiian Entomological Society 9:235-345.
NatureServe Explorer (Accessed September 2008)
Profile prepared by Celeste Mazzacano, The Xerces Society for Invertebrate Conservation.