- Research article
- Open Access
Diet of the sea anemone Anthopleura nigrescens: composition and variation between daytime and nighttime high tides
Zoological Studies volume 53, Article number: 26 (2014)
The diverse feeding habits of sea anemones have led them to be classified as opportunistic polyphagous predators. However, most studies have focused on the diet of temperate sea anemones, and little is known about the trophic ecology of tropical species and their role in tropical ecosystems. We studied the diet of the intertidal sea anemone Anthopleura nigrescens by examining the gut contents of specimens collected at two sites on Costa Rica’s Pacific coast, testing for differences in prey items captured between daytime and nighttime high tides.
We found 25 prey items including: mollusks, crustaceans, annelids, insects and eggs. Juvenile bivalves, barnacle cyprids, and copepods were the main prey items. The anemones at Playa Dominical captured significantly more juvenile bivalves during nighttime high tides, and those at Mata de Limón captured more cyprids during daytime high tides.
This study shows that A. nigrescens is an opportunistic polyphagous predator, like most of its temperate counterparts.
Anthopleura nigrescens (Verrill ) is a common, azooxanthellate sea anemone in the rocky intertidal habitats of Costa Rica’s Pacific coast. It is most abundant in the lower intertidal zone, but can occur in the middle and upper zones, usually in crevices or pools (Acuña et al. ). This species forms large aggregations of individuals that during low tide retract their tentacles to reduce desiccation. Aggregating behavior and adhesive verrucae that attach gravel to the column also diminish desiccation (Hart and Crowe ; Bingham et al. ), and presumably allow A. nigrescens to colonize hot, tropical intertidal zones. This species was redescribed in detail using specimens from Hawaii (Dunn ) and was only recently recorded for Costa Rica, indicating that it is distributed across the Indo-Pacific (Acuña et al. ). Its abundance and ease of identification and collection in the field make it an ideal species for trophic ecology studies.
The diet of sea anemones is an interesting aspect of their ecology and diet studies provide insight into their role in trophic webs. Several authors have characterized sea anemones as opportunistic polyphagous predators that feed on the available prey, usually benthic organisms, in their surrounding environment (Chintiroglou and Koukouras ; Acuña and Zamponi ; Acuña et al. ). For example, Acuña and Zamponi () studied the diet of three temperate species and found that their main prey was the bivalve Brachidontes rodriguezi, which was also the most abundant organism in the sampled areas. Other studies on temperate anemones have found that diet changes seasonally (Chintiroglou and Koukouras ; Acuña and Zamponi ). For example, Acuña et al. () observed that Anthothoe chilensis feeds mainly on gammarid crustaceans that are abundant during the summer, but feeds on pycnogonids, cirratulid polychaetes and caprellid crustaceans during the other seasons. Studies have also shown that the diet of one species may vary between different locations (Kruger and Griffiths ; Tsurpalo and Kostina ; Davenport et al. ), or even between different depths at a same site (Chintiroglou and Koukouras ). These findings have led authors to suggest that the diet of sea anemones reflects the prey availability in the communities they inhabit (Chintiroglou and Koukouras ; Tsurpalo and Kostina ).
Although the diets of many temperate sea anemone species have been well documented, there is a considerable gap in our knowledge of the trophic ecology of tropical species. In this study we describe the diet of A. nigrescens and compare the composition of the diet between locations. We also tested the hypothesis that the diet would change between daytime and nighttime high tides, presumably due to temporal differences in prey availability.
Collection and sampling
A total of 158 specimens were collected from two sites on Costa Rica’s Pacific coast: a rocky promontory that extends towards the sandy beach in Playa Dominical (9°15′00″ N, 83°51′36″ W) and an artificial breakwater in Mata de Limón (9°55′15″ N, 84°42′53″ W). These sites were selected because they are easily accessible and have large aggregations of A. nigrescens that are exposed during low tide.
On 3 and 4 April 2012, 88 specimens were collected from Playa Dominical, 44 specimens after a daytime high tide near noon and another 44 specimens after a nighttime high tide near midnight. Then, on 22 and 23 April 2013, 70 specimens were collected from Mata de Limón, 35 specimens again after a noon high tide and 35 specimens after a midnight high tide. In both cases, the collection dates were within 4 days of spring tides (and full moons) because the low tides allowed for a longer collecting period. The sea anemones were collected as soon as possible after they were exposed by the falling tide to reduce the digestion time and allow the extraction of fresh prey from the sea anemone coelenterons. Specimens were placed in seawater and were narcotized with small additions of a 7.5% magnesium chloride solution (Moore ), which reduced regurgitation of the food bolus upon addition of the preservative. Finally, specimens were fixed by adding concentrated formalin to reach a 6% formalin in seawater solution.
In the laboratory the specimens were washed with tap water to remove the formalin and placed in 70% ethanol until processing, which was carried out within three months of the collection date. Before dissection, attached gravel was removed with forceps from each specimen and detritus was washed off. Specimens were dissected on a petri dish by carefully cutting them longitudinally and removing the food bolus and large prey items with forceps. Then, a scalpel was used to scrape the mesenteric filaments from the mesenteries and the coelenteron was flushed several times. The petri dish was examined under a stereoscope and prey items were identified to the lowest possible taxonomic level and counted. Whether the items were undigested, partially digested, or completely digested was also noted. For example, empty crustacean exoskeletons were noted as completely digested, whereas exoskeletons with some tissue were noted as partially digested. This distinction was also applied to mollusk shells.
The methods described by Deniel () with the modified terminology by Acuña and Zamponi () were used to calculate the following parameters: percentage of empty gastric cavities or vacuity index (V), frequency index of each prey item (f), and percentage of each prey item (P).
To obtain the composition of the diet of A. nigrescens populations at Playa Dominical and Mata de Limón, the data from all individuals collected after both high tides at each site were combined. All prey items were taken into account, including completely digested, partially digested and undigested items. Preliminary analyses showed that there were no statistically significant differences in prey item composition between sites.
To compare between the composition of prey items captured during daytime and nighttime high tides, the same methodology as above was applied, but only partially digested and undigested prey items were included in the analyses. Sea anemone coelenterons may contain a mix of freshly captured and old prey items (Davenport et al. ). Thus, fully digested prey items were excluded to ensure that all prey items included in the analyses had been captured exclusively during the previous high tide. We assumed that old prey items were completely digested during the previous tidal cycle (approximately 12 hours). Sea anemone digestion rates depend on the type of prey, the size of the prey items and the anemone species. However, the average digestion time of the temperate species Anthopleura elegantissima is 8 to 9 hours (Hiebert and Bingham ) and previous studies show that digestion rates are faster at higher temperatures and with exposure to sunlight (Kruger and Griffiths ; Rossi et al. ; Purcell ; Hiebert and Bingham ).
Data were analyzed with the statistical software PAST v.2.15 (Hammer et al. ). A one-way Analysis of Similarity (ANOSIM) test was used to find differences in the composition of prey items captured during daytime and nighttime high tides. To determine which prey items contribute most to the differences between the tides, a Similarity Percentage (SIMPER) test was used. The abundances of all prey items were square root transformed prior to analyses, to prevent the most abundant prey from dominating the analyses.
A total of 158 sea anemone coelenterons were analyzed. These contained 25 different prey items, distributed in five groups: mollusks, crustaceans, insects, annelids, and eggs (Figures 1 and 2). Prey items were found in all coelenterons examined, resulting in a vacuity index of 0%. However, when only semidigested or undigested prey items were included, the vacuity index was 3%. Most prey items found were highly digested. Mollusk shells were usually found whole, occasionally with mesenteric filaments still inside the shell, indicating that digestion was ongoing at the time of fixation. Brachidontes sp. bivalves were always found with their shells open, on rare occasions with some remaining tissue. Unidentified juvenile bivalves were mostly found intact. Crustaceans were difficult to identify because they were almost always highly digested and fragmented. In most cases, only parts of the exoskeleton remained. Corycaeid copepods were rarely found whole and usually only the exoskeleton of the cephalosome remained. Barnacle larvae (cyprids) were often found intact, but in most cases only the exoskeleton was observed. Insects were also very fragmented, although more easily identifiable due to their dark exoskeleton. Our findings suggest that A. nigrescens is unable to the digest the exoskeletons of planktonic crustaceans and insects.
At both sites, the most common prey were juvenile bivalves, cypris larvae, and corycaeid copepods. Juvenile bivalves and cyprids were found in almost all examined coelenterons, whereas corycaeid copepods were found in about half. There were also differences in the percentage of each type of prey between sites. At Mata de Limón, cyprids were the primary prey item (58%), while juvenile bivalves were secondary prey (26%) and copepods were occasional prey (8%) (Table 1). In the population at Dominical, cyprids (47%) and juvenile bivalves (44%) were primary prey, while copepods were again occasional prey items (7%) (Table 1). When data for both populations were combined, it is clear that A. nigrescens diet is composed mainly by cyprids and juvenile bivalves, complemented by occasional prey items such as copepods, gastropods, insects, and eggs.
The sea anemones at Playa Dominical captured considerably more juvenile bivalves during the nighttime high tide than during the daytime high tide, and captured slightly more cyprids during the night (Figure 3). The composition of prey items between tides was significantly different at this site (ANOSIM: r = 0.06; p < 0.01). Bivalves contributed substantially to the dissimilarity in the diet between tides (52.28%), while cyprids contributed 26.25%. The sea anemones at Mata de Limón captured more cyprids during daytime high tides than during nighttime high tides, and captured slightly more bivalves during the night that during the day (Figure 4). However, no significant differences were found in the composition of prey between tides (ANOSIM: r = 0.01; p = 0.2). The prey items that contributed most to the dissimilarity in the diet between daytime high tides and nighttime high tides were cyprids (42.51%) and bivalves (41.11%).
A. nigrescens in our study preyed mainly on cypris larvae, juvenile bivalves and copepods. The predominance of cyprids may be explained by reproductive cycles in the local barnacle population and patterns in the larval settlement. Working in Punta Mala, on Costa Rica’s Pacific coast, Sutherland () found that the reproductive activity of Chthamalus fissus was high during the dry season (December-April), and that there was a recruitment peak in the middle of the year. It is possible that the abundance of cyprids in our samples reveals a recruitment peak or simply reflects a large abundance of these larvae in the water column. Cyprids may be captured while swimming in the water column during their pelagic phase. Planktonic larvae may be carried towards the shore by a number of hydrodynamic processes (see Pineda et al. ) and currents in the intertidal zone can force the larvae into the tentacles of a sea anemone. Cyprids may also be captured if they wander onto the tentacles of a sea anemone during their settlement stage, when they walk on the substrate searching for a suitable place to cement themselves (Lagersson and Høeg ).
Bivalves were also an important component of A. nigrescens diet. Juvenile bivalves, which were too small to be identified, were presumably captured during the settlement process. Brachidontes are found attached to the rocky intertidal zone and may be caught by the sea anemones if they become detached from the substrate. Mytilid bivalves form aggregations and are subject to intraspecific competition that generates high levels of mortality in the population (Guiñez ). Moreover, bivalves in the intertidal zone are subjected to strong waves that can detach them from the substrate, depending on the size of the bivalve and how firmly it is adhered (Hunt and Scheibling ).
Site to site differences in diet
This study found few differences in A. nigrescens diet between sites. More mytilid bivalves were captured by the anemones in Mata de Limón than those in Playa Dominical and polychaetes were only found in sea anemones collected from Playa Dominical. These findings reflect the differences in the communities of potential prey items that colonize each site. The artificial breakwater in Mata de Limón receives low-energy waves that allow sessile organisms such as mytilid bivalves and barnacles to thrive, whereas the site at Playa Dominical receives high-energy waves and is only colonized by sea anemones and sabellid polychaetes. High wave energy results in slower bivalve growth rates and higher bivalve mortality (McQuaid and Lindsay ), and may hinder bivalve colonization of rocky sites in Playa Dominical.
The presence of insects in the specimens collected at Playa Dominical is noteworthy and reinforces the opportunistic feeding of these sea anemones. Several other studies have found insects in the coelenterons of sea anemones. For example, Acuña and Zamponi () found coleopterans in Oulactis muscosa and Möller () found six kinds of insects in Anemonia sulcata. Davenport et al. () suggest that the presence of insects is determined by the direction of the wind, the location of the anemones on the coast, and the presence of abundant coastal vegetation. Our findings support this hypothesis, because Playa Dominical has abundant vegetation close to the intertidal zone, whereas the artificial breakwater at Mata de Limón lacks vegetation.
Day to night differences in diet
The main differences in diet between daytime and nighttime high tides are attributable to cyprids and juvenile bivalves, which comprise the bulk of A. nigrescens diet. Cyprids seem to be captured mostly during daytime high tides. Cruz () found that settlement of Chthamalus spp. in the low intertidal zone during daytime high tides was significantly higher than during the night, with densities of up to 74 cyprids and metamorphs per 25 cm2 quadrat. In another study, settlement of C. montagui was ten times higher during the day than during the night, which led the authors to hypothesize that cyprids use light as a cue to settle (Cruz et al. ). Conversely, in our study juvenile bivalves were captured predominantly during nighttime high tides. However, due to the difficulty of identifying the bivalves, it is not possible to know about their natural history, although data from this study suggest that they settle mainly at night.
We were unable to observe any patterns in copepod time of capture because they were rarely found undigested. However, it is likely that corycaeid copepods, which were an abundant prey item, are captured mainly during nighttime high tides. Many copepod species are part of the demersal plankton, organisms with vision and motility that hide in the benthos during the day and migrate into the water column at night (Alldredge and King ). Studies on zooplankton in coral reefs and subtidal sand flats have found that the abundance of corycaeid copepods increases during the night (Alldredge and King ; Ohlhorst ; Alldredge and King ; Nakajima et al. ). Heidelberg et al. () propose that pelagic species that have a daily vertical migration offshore conserve such behavior in shallow environments. Also, demersal plankton such as copepods may migrate higher into the water column during full moon (Alldredge and King ), which may promote dispersal towards the shore.
We acknowledge that due to the lack of temporal replication in the present study it is difficult draw strong conclusions about the diurnal and nocturnal abundance patterns of the prey items in A. nigrescens diet.
The intertidal sea anemone A. nigrescens feeds mainly on juvenile bivalves and zooplankton such as cyprids and copepods. Insects are an occasional prey item that reflect the opportunistic character of this species. Moreover, the time of the high tides seems to have an effect on the types of prey that become available to the sea anemones. Our research shows that the diet may change not only between sites and depths, as other studies have revealed, but may also vary according to the time of day. We suggest that future trophic ecology studies should mention the time of day that specimens are collected, as results may be affected by temporal differences in prey availability. Finally, our findings show that A. nigrescens is an opportunistic polyphagous predators, like most of its temperate counterparts.
Acuña FH, Zamponi MO: Feeding ecology of intertidal sea anemones (Cnidaria, Actiniaria): food sources and trophic parameters. Biociencias 1995, 3: 73–84.
Acuña FH, Zamponi MO: Ecología trófica de las anémonas intermareales Phymactis clematis Dana, 1849; Aulactinia marplatensis (Zamponi, 1977) and A. reynaudi (Milne-Edwards, 1857) (Actiniaria: Actiniidae): relaciones entre las anémonas y sus presas. Ciencias Mar 1996, 22: 397–413.
Acuña FH, Zamponi MO: Estructura poblacional y ecología trófica de Oulactis muscosa Dana, 1849 (Actiniaria, Actiniidae) del litoral Bonaerense (Argentina). Physis 1999, A57: 11–16.
Acuña FH, Excoffon AC, Genzano G: Feeding of Anthothoe chilensis (Actiniaria, Sagartiidae) in Mar del Plata Port (Buenos Aires, Argentina). Biociencias 2001, 9: 111–120.
Acuña FH, Alvarado J, Garese A, Cortés J: First record of the sea anemone Anthopleura nigrescens (Cnidaria: Actiniaria: Actiniidae) on the Pacific coast of Central America. Mar Biodivers Rec 2012, 5: e24. 10.1017/S175526721200022X
Alldredge AL, King JM: Distribution, abundance, and substrate preferences of demersal reef zooplankton at Lizard Island Lagoon, great barrier reef. Mar Biol 1977, 41: 317–333. 10.1007/BF00389098
Alldredge AL, King JM: Effects of moonlight on the vertical migration patterns of demersal zooplankton. J Exp Mar Bio Ecol 1980, 44: 133–156. 10.1016/0022-0981(80)90150-1
Alldredge AL, King JM: The distance demersal zooplankton migrate above the benthos: implications for predation. Mar Biol 1985, 84: 253–260. 10.1007/BF00392494
Bingham BL, Freytes I, Emery M, Dimond J, Muller-Parker G: Aerial exposure and body temperature of the intertidal sea anemone Anthopleura elegantissima . Invertebr Biol 2011, 130: 291–301. 10.1111/j.1744-7410.2011.00241.x
Chintiroglou C, Koukouras A: Observations on the feeding habits of Calliactis parasitica (Couch, 1842), Anthozoa, Cnidaria. Oceanol Acta 1991, 14: 389–396.
Chintiroglou C, Koukouras A: The feeding habits of three Mediterranean sea anemone species, Anemonia viridis (Forskål), Actinia equina (Linnaeus) and Cereus pedunculatus (Pennant). Helgoländer Meeresuntersuchungen 1992, 46: 53–68. 10.1007/BF02366212
Cruz T: Settlement patterns of Chthamalus spp. at Praia da Oliveirinha (SW Portugal). Acta Oecol 1999, 20: 285–287. 10.1016/S1146-609X(99)00138-1
Cruz T, Castro JJ, Delany J, McGrath D, Meyers AA, O´Riordan RM, Power A-M, Rabaça J, Hawkins SJ: Tidal rates of settlement of the intertidal barnacles Chthamalus stellatus and Chthamalus montagui in western Europe: the influence of the night/day cycle. J Exp Mar Bio Ecol 2005, 318: 51–60. 10.1016/j.jembe.2004.12.005
Davenport J, Moloney T, Kelly J: Common sea anemones Actinia equina are predominantly sessile intertidal scavengers. Mar Ecol Prog Ser 2011, 430: 147–155. 10.3354/meps08861
Deniel C: Régimes alimentaires d’ Amoglossus thori Kyle et d’ Amoglossus imperialis Rafinisque (Teleosteens, Bothidae) en baie de Douarmenez. Rev des Trav l’Institut des Pêches Marit 1975, 39: 105–116.
Dunn DF: Redescription of Anthopleura nigrescens from Hawaii. Pacific Sci 1974, 28: 377–382.
Guiñez R: A review on self-thinning in mussels. Rev Biol Mar Oceanogr 2005, 40: 1–6. 10.4067/S0718-19572005000100001
Hammer Ø, Harper DAT, Ryan PD: PAST: paleontological statistics software package for education and data analysis. Palaeontol Electron 2001, 4: 9.
Hart CE, Crowe JH: The effect of attached gravel on survival of intertidal anemones. Trans Am Microsc Soc 1977, 96: 28–41. 10.2307/3225960
Heidelberg KB, Sebens KP, Purcell JE: Composition and sources of near reef zooplankton on a Jamaican forereef along with implications for coral feeding. Coral Reefs 2004, 23: 263–276. 10.1007/s00338-004-0375-0
Hiebert TC, Bingham BL: The effects of symbiotic state on heterotrophic feeding in the temperate sea anemone Anthopleura elegantissima . Mar Biol 2012, 159: 939–950. 10.1007/s00227-011-1871-8
Hunt H, Scheibling R: Predicting wave dislodgment of mussels: variation in attachment strength with body size, habitat, and season. Mar Ecol Prog Ser 2001, 213: 157–164. 10.3354/meps213157
Kruger LM, Griffiths CL: Digestion rates of prey eaten by intertidal sea anemones from the south-western Cape, South Africa. South African J Zool 1997, 32: 101–105.
Kruger LM, Griffiths CL: Sea anemones as secondary consumers on rocky shores in the south-western Cape, South Africa. J Nat Hist 1998, 32: 629–644. 10.1080/00222939800770331
Lagersson NC, Høeg JT: Settlement behavior and antennulary biomechanics in cypris larvae of Balanus amphitrite (Crustacea: thecostraca: cirripedia). Mar Biol 2002, 141: 513–526. 10.1007/s00227-002-0854-1
McQuaid C, Lindsay T: Effect of wave exposure on growth and mortality rates of the mussel Perna perna : bottom-up regulation of intertidal populations. Mar Ecol Prog Ser 2000, 206: 147–154. 10.3354/meps206147
Möller H: Investigations on the feeding ecology of Anemonia sulcata . Zool Anz 1978, 200: 369–373.
Moore SJ: Narcotising sea anemones. J Mar Biol Assoc United Kingdom 1989, 69: 803–811. 10.1017/S0025315400032173
Nakajima R, Yoshida T, Othman BHR, Toda T: Diel variation in abundance, biomass and size composition of zooplankton community over a coral-reef in Redang Island, Malaysia. Plankt Benthos Res 2008, 3: 216–226. 10.3800/pbr.3.216
Ohlhorst SL: Diel migration patterns of demersal reef zooplankton. J Exp Mar Bio Ecol 1982, 60: 1–15. 10.1016/0022-0981(81)90176-3
Pineda J, Porri F, Starczak V, Blythe J: Causes of decoupling between larval supply and settlement and consequences for understanding recruitment and population connectivity. J Exp Mar Bio Ecol 2010, 392: 9–21. 10.1016/j.jembe.2010.04.008
Purcell JE: Extension of methods for jellyfish and ctenophore trophic ecology to large-scale research. Hydrobiologia 2009, 616: 23–50. 10.1007/s10750-008-9585-8
Rossi S, Ribes M, Coma R, Gili JM: Temporal variability in zooplankton prey capture rate of the passive suspension feeder Leptogorgia sarmentosa (Cnidaria: octocorallia), a case study. Mar Biol 2004, 144: 89–99. 10.1007/s00227-003-1168-7
Sutherland JP: Recruitment regulates demographic variation in a tropical intertidal barnacle. Ecology 1990, 71: 955–972. 10.2307/1937365
Tsurpalo A, Kostina E: Feeding characteristics of three species of intertidal sea anemones of the South Kuril Islands. Russ J Mar Biol 2003, 29: 31–40. 10.1023/A:1022823819872
Verrill A: Hawaiian shallow water anthozoa. Bernice P Bish Museum Bull 1928, 49: 1–30.
We are grateful for the support provided by the Centro de Investigación en Ciencias del Mar y Limnología (CIMAR) of the Universidad de Costa Rica. Marco Corrales, Victoria Bogantes, Allan Carrillo, Steven Zamora, Jeffrey Sibaja, Kimberly García and Rita Vargas contributed to the identification of many prey items. We are very grateful for the financial support provided by the Quesada-Satterthwaite family. We would also like to thank Brian Bingham and two anonymous reviewers for their valuable comments that greatly improved this manuscript.
Authors declare they have no competing interests.
AJQ, FHA, and JC designed the study. AJQ collected, analyzed and interpreted the data, and drafted the manuscript. FHA and JC made intellectual contributions to the final draft of the manuscript and revised it critically. All authors read and approved the final manuscript.