Epibionts on a nesting female loggerhead sea turtle Caretta caretta (Linnaeus, 1758; 92.1 cm straight carapace length and 70.7 cm straight carapace length) were examined on the island of Yakushima, Kagoshima, Japan (30.4156°N, 130.4394°S) on 16 June 2009 (Fig. 1a). Specimens were photographed, counted and identified at the lowest taxonomic level, and four species of barnacles were found: Chelonibia testudinaria (Linnaeus, 1758), Platylepas hexastylos (Fabricius, 1798), Stephanolepas muricata Fischer, 1886, and Fistulobalanus albicostatus (Pilsbry, 1916). The turtle barnacles C. testudinaria (n = 6), P. hexastylos (n = 42) and S. muricata (n = 1) are common on Japanese turtles (Hayashi 2012), while this is the first record of F. albicostatus (n = 4) on sea turtles. The acorn barnacle F. albicostatus is a common species in estuaries and mangroves and as a biofouling species on ships, and occurs in the waters of Japan, China, Taiwan and Korea (Newman and Ross 1976; Chan 2007). The barnacle has also been recorded in California waters as an invasive species (Bonnot 1935; Henry and McLaughlin 1975). Japanese loggerhead turtles migrate over the Pacific Ocean as developmental migration in their ontogenetic stages (Bowen et al. 1995); sea turtle migration allows F. albicostatus and possibly other organisms biofouling sea turtles to invade new habitats, as seen in a case of rapa whelk Rapana venosa (Valenciennes, 1846) recorded in Harding et al. (2011). In one example for F. albicostatus, a new geographic expansion into Norway by biofouling plastic tags on migrating birds was reported (Tottrup et al. 2010). Further studies are needed to examine the potential role of migratory animals such as sea turtles and birds as dispersal vectors of these hitchhikers.