Temporal patterns in the post-larval supply of two crustacean taxa in Rangiroa Atoll, French Polynesia

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Fish Sci (2012) 78:75 80 DOI 10.1007/s12562-011-0430-z ORIGINAL ARTICLE Biology Temporal patterns in the post-larval supply of two crustacean taxa in Rangiroa Atoll, French Polynesia Raphael Santos Craig A. Radford Joseph Poupin Christophe Brié Suzanne C. Mills René Galzin David Lecchini Received: 7 August 2011 / Accepted: 18 October 2011 / Published online: 5 November 2011 Ó The Japanese Society of Fisheries Science 2011 Abstract The post-larval supply of two crustacean taxa (Brachyura and Stomatopoda) was monitored using one crest net over three lunar months at Rangiroa Atoll, French Polynesia. We captured a total of 37,068 brachyuran and 12,697 stomatopod post-larvae during the study. Post-larval supply was higher during the warm season (February April) than during the cold season (June July) for both Brachyura (warm season: 85% of total post-larval supply) and Stomatopoda (warm season: 92%). Moreover, the pulse of the brachyuran post-larval supply occurred predominantly around the last, while the pulse of stomatopods occurred predominantly around the new moon. However, for both taxa, the post-larval supply was lowest around the full moon and the first. Overall, our monitoring highlighted that the post-larval supply of Brachyura and Stomatopoda was modulated by seasons and lunar phases at Rangiroa. R. Santos S. C. Mills R. Galzin D. Lecchini (&) Laboratoire d Excellence CORAIL, USR 3278 CNRS-EPHE, CRIOBE, BP 1013, Papetoai 98729, Moorea, French Polynesia e-mail: lecchini@univ-perp.fr C. A. Radford Leigh Marine Laboratory, University of Auckland, PO Box 349, Warkworth 0941, New Zealand J. Poupin Institut de Recherche de l Ecole Navale, BP 600, 29240 BrestArmées, France C. Brié Tropical Fish Tahiti, Avatoru 98729, Rangiroa, French Polynesia D. Lecchini Institut de Recherche pour le Développement, UR 227, 101 Promenade Roger Laroque, 98848 Nouméa, New Caledonia Keywords Brachyura Stomatopoda Reef colonization Lunar cycle Crest net Introduction Most marine species (molluscs, crustaceans, and fish) have a life cycle that includes a dispersive planktonic larval phase (in the open ocean), which usually lasts from a few days to six weeks, followed by a sedentary site-associated juvenile and adult reef phase [1]. A potentially critical period in the development of these marine larvae is the migration from continental shelf waters back to shore (i.e., usually more than 80% of the larval population dies during this period) [2, 3]. Thus, one of the first steps in building predictive models of population dynamics that will aid in the future management of marine systems under climatic or human changes is identifying the environmental attributes that influence the patterns of larval supply [4]. In coral reefs, marine larvae at the end of their pelagic phase have to return to a reef habitat to continue their ontogenetic development [5]. It has been shown that fish larval supply in French Polynesia [6, 7] and in the Solomon Islands [8] occurs in the highest densities over the reef crest during the new moon. However, little information is available on the spatio-temporal variations in larval supply of other coral reef taxa [9 11]. Indeed, the majority of studies on the patterns and processes of connectivity of reef-dwelling populations have concentrated on coral reef fish [5]. The present study is one of the first to explore the temporal variation of Stomatopoda larval supply to coral reefs and to enhance previous studies concerning Brachyuran species in tropical areas [12]. Among the different methods that can be utilized to study marine larval supply (e.g., light traps and nets either

76 Fish Sci (2012) 78:75 80 towed or dropped in the water column), crest nets have a number of advantages over other methods [13]: (1) marine larvae are caught just before settlement, which would give a suitable measure of larval supply; (2) the high energy and turbulence of the reef crest minimizes net avoidance by larvae; and (3) since the net is deployed at night, the net is cryptic, and thus it is passive gear for easy larval capture. Crest nets sample late-stage larvae of marine species in the process of, or immediately prior to, settlement in the reef. For this reason, they provide an accurate estimate of larval supply to reef habitats [14, 15]. Specifically, our aims were to assess the arrival of postlarval crustaceans at the reef (with crest net sampling) and to monitor how post-larval supply varied over the lunar phases (new moon, first, full moon vs. last ) and seasons (warm vs. cold season). The term post-larvae was used in the study, as crustaceans captured with the crest net were ready for settlement in the coral lagoon, but they colonized at different developmental stages (e.g., megalopa, alima, erichtus) [11, 12, 15]. Materials and methods Crustacean post-larval supply was monitored daily on the north coast of Rangiroa Atoll, French Polynesia (14 57 0 48S; 147 38 0 79W) during three lunar months (warm season: 29 February to 28 March 2008 and 29 March to 26 April 2008; cold season: 29 June to 27 July 2008) using a crest net. At Rangiroa Atoll, seawater temperature ranges from 26 to 28 C during the warm season (September May) and from 23 to 25 C during the cold season (June to August data from Meteo-France: http://www.meteo-france.fr). There is a prevailing wind that changes direction with the season: east/northeast direction during the warm season, and east/southeast direction during the cold season (data from the Service Hydrographique et Oceanographique de la Marine; http://www.shom.fr). The crest net used was similar to the one used by Lo-Yat at Rangiroa [4]. The net (5.0 m long) had a rectangular mouth (2.0 m wide, 1.5 m high), and was made of a 1 mm mesh, which was fine enough to retain most of the incoming crustacean post-larvae before settlement and the subsequent molting process. The mouth of the net was open to the offshore. Four hinged panels (2.0 m long, 1.5 m high) of 0.7 mm mesh enlarged the mouth area of the net to 6 m. Thus, the crest net was divided into two chambers: the mouth where post-larvae entered, and the cod end where the post-larvae were captured. The whole structure was fastened and secured by steel cables that were bolted firmly onto the reef rock to prevent the net from being swept away during periods of strong current. The cod end was attached to the net at dusk (6 pm) to minimize the accumulation of debris in the net during the day, when few marine post-larvae are usually captured [6, 11, 12], and was cleared of catches at dawn (6 am). Catches were transported into laboratory tanks (60 9 50 9 50 cm) supplied with air pumps. Once at the laboratory, catches were sorted in a large aquarium (100 9 50 9 10 cm), and crustaceans (alive or dead larvae) were identified and counted. Post-larval identification was undertaken under a dissecting microscope (Wild M3B, Wild Heerbrugg, Heerbrugg, Switzerland) using meristic and morphologic characters of crustaceans [16]. Some post-larvae were kept alive in aquaria for several weeks (fed with nauplii of Artemia salina) to confirm their identification (allowing metamorphosis into the juvenile phase). Thus, all brachyuran and stomatopod post-larvae were counted, and six species were identified: two species of Brachyura (Pachygrapsus planifrons de Man, 1888; Calappa calappa Linnaeus, 1758) and four species of Stomatopoda (Lysiosquillina maculata Fabricius, 1793; Lysiosquillina sulcata Manning, 1978; Raoulserenea sp., Pseudosquilla sp.). The other unidentifiable brachyuran and stomatopod post-larvae were placed into another category (Brachyura spp. or Stomatopoda spp.). To highlight a potential seasonal effect on larval supply, a Kruskal Wallis test was conducted with month as the variable (29 February 28 March 2008, 29 March 26 April 2008, and 29 June 27 July 2008; days were repeat observations). To highlight a potential lunar effect on larval supply, a Kruskal Wallis test was conducted with lunar s as the variable (new moon : week centered on new moon, first, full moon, and last ; days were repeat observations). This last analysis was conducted separately for each month. ly, the correlation of catches with tide height was investigated separately for each month using a Spearman test. Tidal data were provided daily by the Service Hydrographique et Oceanographique de la Marine. Results A total of 37,068 brachyuran post-larvae and 12,697 stomatopod post-larvae were collected during the three months of the study (Fig. 1). A significant temporal variation in post-larval supply with lunar month was found (Kruskal Wallis test: df = 2, F = 2.34, P = 0.012 for Brachyura, df = 2, F = 6.92, P = 0.001 for Stomatopoda). The highest post-larval supply occurred in March/April (54 and 81% of the total post-larval supply for Brachyura and Stomatopoda, respectively) during the warm season. The lowest post-larval supply occurred in June/July (15 and 8% of the

Fish Sci (2012) 78:75 80 77 total post-larval supply for Brachyura and Stomatopoda, respectively) during the cold season. No significant relationship was observed between the post-larval supply of Brachyura or Stomatopoda and tidal height for any month (Spearman correlation: for Brachyura: n = 30, r \ 0.21, P [ 0.19 for each month; for Stomatopoda, n = 30, r \ 0.08, P [ 0.71 for each month). ly, a significant temporal variation in post-larval supply with lunar phase was noted (Kruskal Wallis test: df = 3, P \ 0.05 for both Brachyura and Stomatopoda). For both Brachyura and Stomatopoda, the post-larval supply was highest in the last in February/March (Fig. 1). In March/April and June/July, the post-larval supply was highest in the last for Brachyura and around the new moon for Stomatopoda (Fig. 1). At the species level, the same temporal patterns were observed with the lunar month and phase (Fig. 2a, b). Among the post-larvae of Brachyura, Calappa calappa arrived mainly during the last of March (27 29 March), while Pachygrapsus planifrons post-larvae arrived daily from the last of March (23 March) to a few days after the new moon (12 April). For Stomatopoda, Lysiosquillina maculata and L. sulcata post-larvae arrived on one night only (both on 30 March, last ). For Raoulserenea sp., post-larval supply occurred mainly in the last (27 March 02 April), while Pseudosquilla sp. post-larvae arrived around the new moon (3 9 April). ly, the post-larval supply of these six species was weak in June/July (less than 5% of the total post-larval supply), except for P. planifrons (1,612 larvae on 23 July, last Fig. 1 Temporal variations in the post-larval abundances of Brachyura and Stomatopoda per night during three lunar months: a 29 February 28 March, b 29 March 26 April, c 29 June 27 July 2008. Each month was separated into four lunar s: new moon, first, full moon, and last. The dashed line represents the flood tide sea level (m) in Rangiroa. Black and white circles represent the new moon and full moon, respectively (a) (b) Post-larval supply 1 0.8 0.6 0.4 0.2 0 1 Flood tide sea level (m) Post-larval supply 0.8 0.6 0.4 0.2 0 Flood tide sea level (m) (c) 1 Post-larval supply 0.8 0.6 0.4 0.2 Flood tide sea level (m) 0 Brachyura Stomatopoda

78 Fish Sci (2012) 78:75 80 (a) Post-larval supply of Brachuyra 4000 C. calapa P. planifrons (b) Post-larval supply of Stomatopoda L. maculata L. sulcata Pseudosquilla sp. Raoulserenea sp. Fig. 2 a Temporal variation in post-larval abundance per night for two species of Brachyura from 23 March to 26 April 2008: Calappa calappa (3% of total post-larval supply) and Pachygrapsus planifrons (69%); b temporal variation in post-larval abundance per night for four species of Stomatopoda from 27 March to 12 April 2008: Lysiosquillina maculata (2% of total post-larval supply), L. sulcata (1%), Raoulserenea sp. (44%) and Pseudosquilla sp. (45%). Outside of these periods, the post-larval supply of the six species was weak (less than 5% of the total post-larval supply), except for P. planifrons (1,612 post-larvae on 23 July) and Pseudosquilla sp. (415 post-larvae on 30 June) ) and Pseudosquilla sp. (415 post-larvae on 30 June, around the new moon). Discussion The recruitment of marine invertebrates is highly variable, causing temporal and spatial fluctuations in adult populations and community dynamics, but the processes creating this variability are poorly understood, especially for Brachyura and Stomatopoda taxa in coral reefs [11, 12]. Our monitoring highlighted that the post-larval supply of Brachyura and Stomatopoda was modulated by seasons and lunar phases at Rangiroa. The post-larval supply of Brachyura and Stomatopoda in the present study was higher during the warm season than the cold season for both Brachyura (February/March 31% of total larval supply, March/April 54%, and June/July 15%) and Stomatopoda (February/March 11%, March/ April 81%, and June/July 8%). The same temporal variation was highlighted for coral reef fish post-larvae, with the highest post-larval supply during the warm season [4, 6]. Three main factors might explain these differences in post-larval supply between warm and cold seasons: (1) spawning periodicity, (2) seawater temperature, and (3) prevailing wind [9]. (1) Although there are no data on the seasonal reproduction of brachyurans and stomatopods in French Polynesia, Eggleston [17] showed that differences in spawning periodicity explained the temporal variation of spiny lobster post-larval supply in the central Bahamas. (2) Shanks [3] highlighted that the temporal variation of crab post-larvae with season was correlated with oceanographic

Fish Sci (2012) 78:75 80 79 processes that can transport post-larvae to shore, as well as with seawater temperature (lowest post-larval supply in the cold season). At Rangiroa Atoll, seawater temperature was higher during the warm season (27.5 C from 29 February to 28 March 2008 and 27.4 C from 29 March to 26 April 2008) than during the cold season (24.3 C from 29 June to 27 July 2008 data from Meteo-France). (3) Robertson [18] showed that strong prevailing winds have major effects on the temporal variation of post-larval supply by reducing the survivorship of eggs and larvae in ocean, whereas weak winds may enable post-larvae to more actively determine their settlement destination compared with when water currents are stronger. In agreement, the wind at Rangiroa was very strong during the cold season ( Maraamuu east/southeast direction, intensity range: 15 25 knots). In contrast, the wind was relatively weak during the warm season (east/northeast direction, intensity range: 5 15 knots data from Service Hydrographique et Oceanographique de la Marine). Thus, the strong prevailing wind (Maraamuu) during the cold season might have reduced post-larval survival at Rangiroa Atoll [4]. Nevertheless, the crest net was only located on the north coast (lack of spatial replication in our study). For coral reef fish, the spatial variation is characterized by a post-larval distribution that occurred simultaneously at sites separated by 200 m (on the same coast) [7, 19] or by 10 km (on different coasts) [20]. As crustacean post-larvae had reduced swimming abilities compared to fish post-larvae [1], a stronger spatial variability in the post-larval supply of crustaceans could be expected, based on prevailing wind direction. Overall, even though additional data should be recorded for a whole year and several crest nets should be set up on the different coasts of Rangiroa, our monitoring highlighted significant differences in post-larval supply for both Brachyura and Stomatopoda with the season (warm vs. cold season) that could be explained by seasonal reproduction, seawater temperature, and/or the prevailing wind. Our monitoring highlighted some temporal variation with lunar phase (Figs. 1, 2). For each sampling month, the pulse of the brachyuran post-larval supply occurred predominantly around the last. In contrast, the pulse of stomatopod post-larvae occurred predominantly around the new moon in March/April and June/July, and around the last in February/March. However, for both taxa, the post-larval supply was lowest around the full moon and the first. Reyns [12] analyzed the temporal patterns of megalopal brachyuran crab in the Caribbean with respect to daily wind and ambient current regime. The results showed that Xanthidae and Grapsidae post-larvae colonized predominately during the last moon and intermediate to minimum amplitude tides. The same lunar variation was highlighted for coral reef fish post-larvae, with the highest post-larval supply occurring from the last to the new moon period [6, 7]. To explain the pulse of crustaceans around the last, we suggest an effect of tide (as in Reyns study [12]), even though no significant relationship was found between post-larval supply and tidal height. Indeed, the third period at Rangiroa was often associated with high tides during the middle of the night (data from Service Hydrographique et Oceanographique de la Marine). This could potentially result in crest nets being exposed to greater quantities of water-containing nocturnal animals than during other lunar phases (in comparison with the first ) when the high tides are closer to dawn and dusk. Yet, post-larval supply is often low at dawn and dusk [4, 6]. To explain the pulse of crustaceans around the new moon, we suggest an effect of light intensity. This temporal pattern might take advantage of these incoming darker nighttime tides for predator avoidance [10]. Indeed, the new moon period is a lunar phase when visual predation is likely reduced due to low light levels [17, 21]. Predation is so intense that all marine post-larvae arriving on reefs have been said to make a suicide drop onto the reef and to face a wall of mouths [2]. In conclusion, even over a short sampling period, our monitoring of Brachyura and Stomatopoda highlighted some temporal variations in post-larval supply according to season (higher post-larval supply in the warm than the cold season) and lunar phase (higher post-larval supply from the last to the new moon period than around the full moon and the first ). These temporal variations in post-larval supply significantly influence on the dynamics of marine populations [2], and have therefore been the subject of much scientific scrutiny [4, 5, 14]. Examining how biological and physical factors contribute to fluctuations in post-larval supply is important when attempting to understand how populations are maintained over time [12]. Acknowledgments We thank Tropical Fish Tahiti and Services de la Pêche et de la Perliculture of French Polynesia (G. Remoissenet, C. Lo, M. Bellais) for kindly agreeing to house this study in their facilities. This research was supported by grants from ANR (ANR-06- JCJC-0012-01), MOM (06 PF 15), the CRISP (Coral Reef Initiatives in the South Pacific) program, and the French Polynesian Ministry of Fisheries. References 1. Kingsford MJ, Leis JM, Shanks A, Lindeman K, Morgan S, Pineda J (2002) Sensory environments, larval abilities and local self-recruitment. Bull Mar Sci 70:309 340 2. Doherty PJ (2002) Variable replenishment and the dynamics of reef fish populations. In: Sale PF (ed) Coral reef fishes: dynamics and diversity in a complex ecosystem. Academic, San Diego, pp 327 358

80 Fish Sci (2012) 78:75 80 3. Shanks AL (2006) Mechanisms of cross-shelf transport of crab megalopae inferred from a time series of daily abundance. Mar Biol 148:1383 1398 4. Lo-Yat A, Simpson SD, Meekan M, Martinez E, Lecchini D, Galzin R (2011) Extreme climatic events reduce ocean productivity and larval supply in a tropical reef ecosystem. Glob Chang Biol 17:1695 1702 5. Leis JM, McCormick MI (2002) The biology, behavior, and ecology of the pelagic, larval stage of coral reef fishes. In: Sale PF (ed) Coral reef fishes: dynamics and diversity in a complex ecosystem. Academic, San Diego, pp 171 199 6. Dufour V, Galzin R (1993) Colonization patterns of reef fish larvae to the lagoon at Moorea Island, French Polynesia. Mar Ecol Prog Ser 102:143 152 7. Lecchini D, Dufour V, Carleton J, Strand S, Galzin R (2004) Study of the fish larval flux at Moorea Island: is the spatial scale significant? J Fish Biol 65:1142 1146 8. Hair CA, Bell JD, Doherty PJ (2002) The use of wild-caught juveniles in coastal aquaculture and its application to coral reef fishes. In: Stickney RR, McVey JP (eds) Responsible marine aquaculture. CAB International, New York, pp 327 353 9. Shanks AL, Eckert GL (2005) Population persistence of California current fishes and benthic crustaceans: a marine drift paradox. Ecol Monog 75:505 524 10. Ogburn MB, Diaz H, Forward RB (2009) Mechanisms regulating estuarine ingress of blue crab Callinectes sapidus megalopae. Mar Ecol Prog Ser 389:181 192 11. Acosta CA, Matthews TR, Butler MJ (1997) Temporal patterns and transport processes in recruitment of spiny lobster (Panulirus argus) postlarvae to South Florida. Mar Biol 129:79 85 12. Reyns N, Sponaugle S (1999) Patterns and processes of brachyuran crab settlement to Caribbean coral reefs. Mar Ecol Prog Ser 185:155 170 13. Lecchini D, Polti S, Nakamura Y, Mosconi P, Tsuchiya M, Remoissenet G, Planes S (2006) New perspectives on aquarium fish trade. Fish Sci 72:40 47 14. Lecchini D, Galzin R (2003) Influence of pelagic and benthic, biotic and abiotic, stochastic and deterministic processes on the dynamics of auto-recruitment of coral reef fish. Cybium 27:167 184 15. Bell JD, Clua E, Hair CA (2009) The capture and culture of postlarval fish and invertebrates for the marine ornamental trade. Rev Fish Sci 17:223 240 16. Poupin J (2007) Database of crustacea (Decapoda and Stomatopoda) from central Pacific Islands. http://decapoda.free.fr, http://decapoda.ecole-navale.fr) 17. Eggleston DB, Lipcius RN, Marshall LS, Ratchford SG (1998) Spatio-temporal variation in postlarval recruitment of the Caribbean spiny lobster in the central Bahamas. Mar Ecol Prog Ser 174:33 49 18. Robertson DR, Swearer SE, Kaufmann K, Brothers EB (1999) Settlement vs. environmental dynamics in a pelagic-spawning reef fish at Caribbean Panama. Ecol Monog 69:195 218 19. Doherty PJ, McIlwain J (1996) Monitoring larval fluxes through the surf zones of Australian coral reefs. Mar Freshw Res 47:383 390 20. Dufour V, Riclet E, Lo-Yat A (1996) Colonization of reef fishes at Moorea Island, French Polynesia: temporal and spatial variation of the larval flux. Mar Freshw Res 47:413 422 21. Acosta CA, Butler MJ (1999) Adaptive strategies that reduce predation on Caribbean spiny lobster postlarvae during onshore transport. Limnol Oceanog 44:494 501