Antarctic necrophagous lysianassoids from a stranded fur seal carcass

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vol. 30, no. 1, pp. 29 36, 2009 Antarctic necrophagous lysianassoids from a stranded fur seal carcass Anna JAŻDŻEWSKA Zakład Biologii Polarnej i Oceanobiologii, Uniwersytet Łódzki, Banacha 12/16, 90 237 Łódź, Poland <jazdz@wp.pl> Abstract: A large sample of more than 1500 individuals of scavenging Amphipoda from fur seal carcass was studied. Six species have been identified. The two most abundant spe cies, Abyssorchomene plebs and Waldeckia obesa, are sublittoral, necrophagous amphi pods that could attack the carcass when submerged in the sea. After stranding on the beach they became an attractive food source for birds eating not only the seal tissues but also the scavenging amphipods. The species composition of the present sample as well as earlier data on Antarctic tern stomach content and baited traps taken in the same area and at the same time agreed quite well. These observations confirm the expectation that Antarctic tern feeds on necrophagous amphipods picked out from carcasses stranding on the sea shore. Key words: Antarctica, King George Island, Amphipoda, scavengers. Introduction Amphipod crustaceans belong to the most diverse groups of invertebrates in the Southern Ocean. More than 800 species have been recorded south of the Sub tropical Front (De Broyer et al. 2007). Most of the species are benthic dwellers but there are also some pelagic ones. Amphipods comprise different trophic groups herbivores, predators, omnivores as well as scavengers (Dauby et al. 2001). On the other hand, amphipods constitute a food source for many other invertebrates as well as vertebrate animals fishes, birds and mammals (Dauby et al. 2003). Am phipod crustaceans were reported from the diet of different penguin species (Aptenodytes forsteri, Eudyptes chrysolophus, Pygoscelis adeliae, Pygoscelis antarctica, Pygoscelis papua), blue petrel (Halobaena caerulea), Antarctic and Arctic tern (Sterna vittata, Sterna macrura), Antarctic prion (Pachyptila crassi rostris), fulmar prion (Pachyptila desolata) and diving petrels (Pelecanoides georgica, P. urinatrix) (Ealey 1954; Payne and Prince 1979; Croxall and Furse Pol. Polar Res. 30 (1): 29 36, 2009

30 Anna Jażdżewska 1980; Croxall and Prince 1980; Prince 1980; Jażdżewski 1981; Hindell 1988; Cherel and Kooyman 1998; Jażdżewski and Konopacka 1999; Lescroël et al. 2004; Lynnes et al. 2004; Rombolá et al. 2006; Casaux et al. 2008). In most cases preyed crustaceans were pelagic species and were caught during shallow diving of birds. However, among food items, some benthic amphipods were also observed. While studying the diet of Antarctic tern (Sterna vittata) it appeared that all Amphipoda found in its stomach content were benthic scavengers (Jabłoński 1995; Jażdżewski and Konopacka 1999). These authors were of the opinion that this was a result of birds feeding on amphipods eating tissues of dead seals or other animals stranded on the shore. However, no sample of these crustaceans collected directly from the carcass was available to prove this expectation. The aim of the present study was to examine the species composition of necrophagous amphipods found on a fur seal carcass. Study area, material, methods The material was collected by Dr B. Jabłoński, member of the IVth Polish Antarctic Expedition, on 6th January1980 from a fur seal carcass (Arctocephalus gazella). The animal was lying at the water line at Turret Point (62 04'59 S 57 57'00 W), King George Island, South Shetland Islands. Turret Point is lo cated at the eastern limit of King George Bay, west of Three Sisters Point. It is a cobble beach on the southern coast and melt pools inland. The beach opens to the Bransfield Strait waters and inlandward gently slopes to an extensive, heavily crevassed glacier. The amphipods were preserved in 4% formaldehyde and later transferred to 75% ethyl alcohol. Nearly all specimens were identified to species level and sexed. Results Among 1562 individuals 6 species were found, all belonging to the superfamily Lysianassoidea: Lysianassidae s.s and Uristidae. Two species: Abyssorchomene plebs and Waldeckia obesa constituted more than 90% of all individuals in the sam ple. 1.3% of the sample were juveniles, that were too small to be identified with cer tainty. Details of the identified material is given in Table 1. Sex ratio in the two most abundant species is shown in Fig. 1. In Abyssorchomene plebs a relatively high share of juveniles (ca. 40%) was observed; males and females constituted respectively ca. 30% and ca. 25% of all individuals. Some ovigerous females were also found but their share was comparatively low. In Waldeckia obesa males and females each con stituted ca. 45% of all animals, whereas the share of juveniles was only 10%. No ovigerous females have been found.

Antarctic amphipods from a fur seal carcass 31 100% 90% 80% 70% 60% 50% 40% 30% 20% 10% 0% Abyssorchomene plebs Waldeckia obesa juveniles non-ovigerous females ovigerous females males Fig 1. Sex frequency in two most abundant species. Amphipods found in the sample Table 1 Discussion Species Abundance [N of ind.] % Abyssorchomene plebs 1323 85 Waldeckia obesa 118 7.3 Cheirimedon femoratus 60 4 Pseudorchomene coatsi 16 1 Hippomedon kergueleni 15 0.9 Orchomenella rotundifrons 9 0.5 Lysianassidae indet. 21 1.3 total 1562 100 The composition of amphipod species is almost the same as observed by Jażdżewski and Konopacka (1999) in the stomach content of Sterna vittata caught at King George Island, on shores of Admiralty Bay. The proportions of different amphipods differed but the dominance of Abyssorchomene plebs in both cases could be seen (see Fig. 2). All the species found in the present sample are known for their scavenging habits (Walker 1907; Bregazzi 1972, 1973; Arnaud 1974; Rakusa Suszczewski

32 Anna Jażdżewska Abyssorchomene plebs Waldeckia obesa Cheirimedon femoratus Pseudorchomene coatsi Hippomedon kergueleni Orchomenella rotundifrons others Fig. 2. The share of different species in the abundance in the present material (a) and Antarctic tern stomach content (b). Fig. 2b according to Jażdżewski and Konopacka 1999. 1982; Arnaud et al. 1986; Presler 1986; Slattery and Oliver 1986; Dauby et al. 2001). Necrophagous amphipods are able to locate the food source from a distance of up to 200 m and may appear at the bait even 5 20 minutes after setting down (Hessler et al. 1978; Sainte Marie and Hargrave 1987). Abyssorchomene plebs is a circumantarctic and infrequently sub Antarctic species that has been reported from a wide range of depths, namely from 7 to 1000 m (De Broyer et al. 2004; De Broyer et al. 2007). Detailed studies on this species in Admiralty Bay (Presler 1986) showed its preference to mid sublittoral waters, with the highest abundance in baited traps observed at the depths of 30 60 m. This species is a very active scavenger (Slattery and Oliver 1986), however Dauby et al. (2001) treated it as an opportunistic feeder, taking into account its predatory habit in the water column. The sex ratio of this species was similar in the currently analyzed sample, in bird stomach (Jażdżewski and Konopacka 1999) and in baited traps set by Presler (1986) in Admiralty Bay (Fig. 3). Comparatively low proportion of ovigerous females (5% of all individuals) in the material agrees with the observations of Slattery and Oliver (1986). The second most abundant species in the present collection was Waldeckia obesa. It is also a circumantarctic species, occurring down to the depth of 1030 m (De Broyer et al. 2007). It prefers deep waters; records in shallow places are rare. Presler (1986) reported its highest abundance in baited traps in Admiralty Bay from the depths of 60 90 m and it was observed in numbers at depths of ca. 100 m when taking pictures of the Admiralty Bay bottoms in 2007 (own observation).

Antarctic amphipods from a fur seal carcass 33 100% 90% 80% 70% 60% 50% 40% 30% 20% 10% 0% juveniles non-ovigerous females ovigerous females males Fig 3. Comparison of sex frequency of Abyssorchomene plebs in present material (a), samples from Sterna vittata stomach (b) and baited traps (c) all collected in 1980 (b, according to Jażdżewski and Konopacka 1999; c, according to Presler 1986). Cheirimedon femoratus is a circumantarctic and sub Antarctic species found from 0 to 310 m with preferred depth of 5 30 m in Admiralty Bay (Presler 1986; Jażdżewski et al. 1991a, b; De Broyer et al. 2007). Smale et al. (2007) noticed in Adelaide Island that this species occurs at the bait only in winter season and sup posed that it is an opportunistic feeder in that area. The next three species constituted less than 10% of the sample. Pseud orchomene coatsi is a circumantarctic and sub Antarctic, deep sub littoral species found in baited traps at depths over 150 m (De Broyer et al. 2004, 2007). The last two species, Hippomedon kergueleni and Orchomenella rotundifrons, are shallow water dwellers. Their highest abundance in Admiralty Bay was recorded at depths less than 20 m (Presler 1986; Jażdżewski et al. 1991a, b). More than 90% of amphipods found on the fur seal carcass are sub littoral spe cies. Obviously they attacked the carcass when it was lying on the bottom of the sea. When reaching the food they do not stop eating even when taken out of the wa ter (Jażdżewski pers. comm.). Apparently, the carcass of the seal was thrown away from the sea by the waves but amphipods still persisted in its body. Jabłoński (1995) and Konopacka and Jażdżewski (1999), who have studied the stomach con tent of S. vittata collected at the same island, during three consecutive Antarctic summers, were of the opinion that the necrophagous amphipods found in tern

34 Anna Jażdżewska stomachs were preyed on by birds on the seal bodies. According to those authors that would explain the presence of the comparatively deep sea amphipods in bird stomachs. It is worth noting that Sterna vittata is only a contact dipping and plunge diving bird, unable to dive even to 1 m depth (Sagar 1991). The share of particular species in the present collection matches comparatively well the results of the analysis of Antarctic tern stomach content and samples taken from baited traps at the same time in Admiralty Bay (Presler 1986; Jażdżewski and Konopacka 1999). The differences may be related to the locality where the seal carcass was found. Turret Point is influenced by open waters of Bransfield Strait so the composition of benthic amphipod fauna may differ from the communities in fjord like Admiralty Bay. It is also possible that the results are influenced by the sampling method. The two most abundant species in the present material are larger species than the rest ones so they may be easier to collect. Nevertheless, the proportions of the species occurring in the sample studied are similar to those observed in baited traps set by Presler (1986) in Admiralty Bay at the depth 30 m and more. This suggests that this very carcass could lie in com paratively deep sublittoral (say >20 m). On the other hand one cannot exclude the possibility that scavenging lyssianassoids arrived to the shallower place since their chemoreceptory abilities to locate the prey are very good. The present note confirms the suggestions by Jażdżewski and Konopacka (1999), that Antarctic birds, including Antarctic tern, Sterna vittata, feed on the necrophagous lysianassoids, pecking them up from the stranding carcasses. It is an interesting food chain link between amphipods and birds. Simultaneously it is dif ficult to say that lysianassoids are constant element of Antarctic tern diet; only am phipods studied by Jażdżewski and Konopacka (1999) were completely identified to the species level. Casaux et al. (2008) also reported gammarids in the diet of Sterna vittata gaini, but only two species (Eurymera monticulosa and Bovallia gigantea) were identified, the majority of the amphipod material was defined as unidentified gammarid amphipods. Acknowledgments. I would like to thank Dr B. Jabłoński, the collector of the sample. By his courtesy I have received recently this interesting material. Thanks are due also to Prof. M. Grabowski for his comments and language corrections.this work was supported by a research grant 51/N IPY/2007/0 from the Ministry of Science and Higher Education. References ARNAUD P.M. 1974. Contribution à la bionomie marine benthique des régions antarctiques et subantarctiques. Téthys 6: 465 656. ARNAUD P., JAŻDŻEWSKI K., PRESLER P. and SICIŃSKI J. 1986. Preliminary survey of benthic inver tebrates collected by Polish Antarctic Expeditions in Admiralty Bay (King George Island, South Shetland Islands, Antarctica). Polish Polar Research 7: 7 24.

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36 Anna Jażdżewska PAYNE M.R. and PRINCE P.A. 1979. Identification and breeding biology of the diving petrels Pelecanoides georgicus and P. urinatrix exsul at South Georgia. New Zealand Journal of Zool ogy 6: 299 318. PRESLER P. 1986. Necrophagous invertebrates of the Admiralty Bay of King George Island (South Shetland Islands, Antarctica). Polish Polar Research 7: 25 61. PRINCE P.A. 1980. The food and feeding ecology of Blue petrel (Halobaena caerulea) and Dove prion (Pachyptila desolata). Journal of Zoology, London 190: 59 76. RAKUSA SUSZCZEWSKI S. 1982. The biology and metabolism of Orchomene plebs (Hurley 1965) (Amphipoda: Gammaridea) from McMurdo Sound, Ross Sea, Antarctic. Polar Biology 1: 47 54. ROMBOLÁ E., MARSCHOFF E. and CORIA N. 2006. Interannual study of Chinstrap penguin s diet and reproductive success at Laurie Island, South Orkney Islands, Antarctica. Polar Biology 29: 502 509. SAGAR P.M. 1991. Aspects of the breeding and feeding of Kerguelen and Antarctic terns at the Kerguelen Islands. Notornis 38: 191 198. SAINTE MARIE B. and HARGRAVE B.T. 1987. Estimation of scavenger abundance and distance of at traction to bait. Marine Biology 94: 431 443. SLATTERY P.N. and OLIVER J.S. 1986. Scavenging and other feeding habits of lysianassid amphi pods (Orchomene spp.) from McMurdo Sound, Antarctica. Polar Biology 6: 171 177. SMALE D.A., BARNES D.K.A., FRASER K.P.P., MANN P.J. and BROWN M.P. 2007. Scavenging in Antarctica: intense variation between sites and seasons in shallow benthic necrophagy. Journal of Experimental Marine Biology and Ecology 349: 405 417. Received 29 October 2008 Accepted 27 January 2009