Santa Cruz de Tenerife, octubre 2007 lSSN 0210-945X Biological information aod comments 00 Ha/ophi/a decipiens meadows of tbe Canary Islands (Hydrocbaritaceae, Magnoliophyta) M" CANDELARIA GIL-RooRlGVEZ " MARCELlNO DEL ARCO WILDPRET DE LA CA RLOS 1, WOLFREDO TORRE' L. HERNÁNDEZ-GONZÁLE.Z' y RICARDO J. HAROUN 2 / Departamento de Biología Vegetal, Area de Botánica. Facultad de Farmacia. Univ. de La Laguna. 3807/ La Laguna, Tenerife. Islas Canarias. España. mcgí[email protected] 1 Departamento de Biología. Facultad de Ciencias del Mar. Univ. de Las Palmas de Gran Canaria. 35017 Las Palmas, Gran Canaria, España. M" C"'''llHAR1A G'L-RoDRIGUél, MARCE.L1NO DF.L ARCO, WOLFREDO W,LDPRET DE LA TORRE'. L. ¡'¡ERN~NDF.2-GONzALEZ y RICARDO J. HAROUN (2007). Comentarios e información biológica sobre las praderas de Halophila decipiens amenazas en las islas Canarias (Hydrocharilaceae, Magnoliophyla). V/ERAE. 35: 77·85. CARLOS RESUMEN: Halophila Thouars es un género pantropical de plantas de pequeño porte que fOnTIan poblaciones en el sublitoral. H. decipiens Ostenfeld foona praderas que se localizan entre los 15-40 m en las costas canari as, y que constituyen la asoc iación Halophiletum decipienlis W i Idpret & M .C. Gil. H. decipiens es una especie protegida y ha sido considerada como planta de "interés especial" en el catálogo de las especies en peligro de plantas Canarias (BOC 2001 /097). De similar fOnTIa Halophiletum decipielltis ha sido considerado por la Comisión de las Comunidades Europeas, DG Environment, 1999. "Habitat del Inlerés Comunitario" (nO 111022). Comparte hábitat con Cymodoeea nodosa (Ueria) Ascherson, también bajo protección, como "planta sensible a la destrucción de su hábitat", BOC 200 I /097. Y Cymodocetum nodosae es considerado hábitat "de interés Comunitario" (nO 111021). En el presente trabajo se pone en evidencia la evolución y la posible amenaza del hábitat Halophiletum decipientis por la intromisión de Caulerpa racemosa varo cyhndracea (Sonder) Verlaque, Huisman et Boudouresque, una clorofita invasora de origen australiano. Palabras claves: Especies protegidas; especies invasoras; conservación; Halophila decipiens; Caulerpa racemosa var. cilindracea. 78 ABSTRACT: HalopMla Thouan isa pantropical genusofsmall size seagrasses. flalophila decipiens Oslenfcld fOlTllS deep-water seagrass beds e¡(lending from 15-40 m in the Canarian coasts which constitute Ihe associalion Haloplliletum decipientis Wildpret & M.C. Gil. H. decipiens is a protecled specics ¡ha! was considered as a planl of "special ínterest" by ¡he Canary Islands Endangered $pecies Catalogue, BQC 2001/097, and Halophilefum decipienfis was considered by Ihe European Commission, DG Environment, 1999. "Habital ofCommunity (nlerest" (No 111022). It shares habita! with Cymodocea "odosa (Ucria) Ascherson, also considered under protection. as "sensilive lO habita! disturbanec", BOC 2001 1097. and the communiry Cymodocetumnodosaeisalso"HabitalofCommunitarian interest"(No 111021). In [his paper the evolution of Halophilerum decipienlis in rC(:ent years is shown, and the possible threat of the habita! because of the intromission Caulerpa racemosa 'lar. cylilldracea (Sonder) Verlaque, Huisman et Boudouresque, an invasive Australian ehlorophyte, is eonsidered. Keywords: Endangered speeies; invasive species; conservation; Halophila decipiens; Caulerpa racemosa 'lar. cy/illdracea. INTRODUCTION Seagrass meadows are charaeteristicalty found growing ón uneonsolida[ed substtata of marine environments in tropical and temperate regions. These nowering plant communities are eonsidered among Ihe mosl producllve in the biosphere (MeRoy & Me Millan, 1977; Young, 1978; Bell & Westoby. 1989: Larkum el al.. 1989; Duarte & Chiseano, 1999; Hemminga & Duarte, 2000; Pavon-Salas el al., 2000). Besides, their meadows serve as nursery and breeding grounds for diverse marine organisms (Young, 1978; Bell eta!', 1989). Three marine phanerogams, Cymodocea nodosa (Ueria) Aseherson, Zas lera ncltii Homemann and Ha/ophi/a decipjens Ostenfeld are reported mainly from leeward subtidal sites ofthe Canary Arehipelago (Haroun el al., 2002, 2003). One ofthem, H. decjpiens, was designated among the spennatophytes of "speeial interest" in the Canary Islands Endangered Species Calalogue, BOC 2001 1097, Deeret 151nOOl. Furthcnnore, the eommunity of H. decipiens (Ha/ophiletum decipientis) is included as "Habitat of Corrununity Interest" (No. J 1102) (European Commission, DG Environment, 1999). H. decipjens, with type localilY at Gulf ofThailand off Koh Kahdat (Womersley, 1984; Guiry & Nie Dhonncha 2004), is the sccond most abundant vascular marine speeies in [he Canary Arehipetago, after Cymodocea nodosa (Pavón-Salas el al., 2000). It has a pantTopieal distribulion (www.algaebase.com.): Australasia (Womersley, 1984; Huisman, 2000); Paeifie Ocean (payri el al., 2000); Brazil (Oliveira el al., J 983); Caribbean Sea (linIer & Litter, 2000); N AtlanticOeean, ineluding Canary Islands (Haroun el al.. 2002,2003). The firsl rcport of H. decipiens from the Central-East Atlanlie Ocean was done by Gil~Rodriguez & Cruz (1982) and Gil-Rodriguez el o/.. (1982) from collections in few localities along the southeaslem eoasl ofTenerife. and sinee Ihen several new localilies nave been addcd. Later it was reeorded for La Patma, in the harbour of Santa Cruz de La Palma between 6·9 ro depth (Hemández-González & Gil-Rodriguez. 199:3), and also in Gran Cana- 79 Tia, in one locality oflhe SW coas! (Puerto Rico. 19 m depth) (Bctancon el al., 1995; Pavón-Salas er al., 2000). Moreira et al. (2004) found il growing Iocal1y from 20 to 40 m depttl in two localilies oflne SE ofTenerife. Recen! surveys along the Canary coasts have rcsulted in a mueh extended knowledge of this interesting species. This study provides sorne ecological and chorological knowledge of H. decipiens meadows in ¡he Canary Islands regarding lO environmenlal status and habital Ihreatens. MATERIAL AND METHOOS Sludy area: The Canary Archipelago is located in the Central Easl Allantic Ocean, ntar lo the Nonhwcstem African Coasl; [he mínimum distance wilh (he continent is about 110 km. This volcanic archipelago is composed ofseven maio islands and several islets. Exccpt in the case of Lanzarole and Fuertevenlura, which share Ihe same subtidal shelf, Ihe sea-bonom may reach more than 2000 m deplh among lhe íslands. The older islands have wide insular shelves mainly localed al lhe Soulhem and Soulhweslem CoaSIS. EXlensive sandy bonoms, Sllilable for seagrass meadows development. may appear in such areas. Methods: Several rransecls were sampled between 20-30 m deplh along rhe coasl of Tenerife and Gran Canaria islands lO characlerize Ihe community srrucrure. The sampling was performed using 20 x 20 cm quadrals divided inro subquadrars of IOx IOem side (Fig. 1a, b). Phytosociological relevés chosen randomly were eompiled following Ihe prolocol ofthe Zürich-Montpellier School (Sraun Blanquel, 1979) (Table 1). Numbers in lhal rabie refers lO Ihe abundance/dominanee indexo The phytosociologieal nomenc1ature is aceording ro Rivas-Martínez el al. (2oo 1) for hígh level sintaxa. The association name and descriplion is aceording lO Rivas-Martinez el al. (2002). Al rhe same time. Ihe frequency, abundanee and densiry of Halophi/a planrs in lhe sampled area was delermined. in Tenerife Island (Table 2) following lhe quadral melhod proposed by Dawes(1986, 1998), wilh quadrats of 18 x 18 cm divided iOlo subquadratsof 2 x 2 cm (Fig. le, d), by using Ihe following equalions (Dawes. 1986: 400; 1998: ]69): Ftequency= Number 01 occupiedquadralSI unils Totalnumber 01 QUadrats I units Abundance = Tolal number of individual p1ants (:!erial sprouts) Number 01 oc:cupíed quadrats 1units · = cNc",="be~'o::r::;'''''o'::'·:';C"'='"'''''''';c:,;·0'::1:,",:"'c"=rec De nSlty Totalnumber of unir areas '=- Voucher specirnens are kept in the TFC Herbarium al University ofla laguna (TFC no 43.298; 4].614-43.623; 43.800). Furthermore, underwater pictures oflhe cornmunily wefe laken on lransecls along lhe sourheasrem coast ofTenerife. 80 Fig. l.- la: Halophiletum decipienlis, with Coulerpa racemosa llar cylindracea.- lb: 20 x lOcro quadrat and 10 x subquadrats. le: Ha{ophilelum decipientis general view.1d: 18 x 18 cm quadral ano 2 x 2 subquadrats. RESULTS The Canarian specimens of H. dee/pien! ti! into ¡he general description of [he species, pravided among olhers by den Hanog (1970, 1971) and Gil-Rodríguez & Cruz Sirnó (1982). H. decipiens (Hydrocharitaceae) i5 a monoecious small plant, with a slendcr rhizome nol exceeding 1 mm in diameler, and intemodes 0.5-4.5 cm long. Roots are 2·5 cm long and 0.2-0.5 mm thick. Both, solitary roots and leaves paired, bom from sprouts at each node. Leaves elliptic-oblong, wilh a rounded apex, somelimes cuneate al ¡he base, S10 mm in length and nol more Ihan 5 mm in widlh. The dislribulion panem ofthis species is enlarged lO include a new 10calilY in the E coas! ofTenerife Island (at 20-25 m deph in Igueste de San Andrés) (More ira el 01.,2004); in the SE coas! ofGran Canaria (at 25 m deplh in Playa del Cabrón, Arinaga; F. Espino and R. Herrera, pers. com.) below Cymodocea nadose meadows and iI is now firsl recorded for Gomera (Punta de la Herradura, al19 m dCplh, TFC Phyc43.S00 )and La Caleta (El Hierro, recorded by C.L. Hemández-González) where it is presenl only in srnall and isolaled palches. In lhe Halophj{etum decipienlis of San Andrés (E ofTcncrifc) stand (L1C "sebadales de San Andrés" ES 7020120) has been recenlly discovered Avrainvillea conariensis A_ Gepps el E.S. Gepps an endemic chlorophyte speeies under proteetion, "sensilive lO habitat disturbance" (BOC 200 11 097). SI The expansion of ¡he cornmunity has becn observed recently in ¡he E and S of Tenerife ( Moreira, com. pers.) as well as an important change in jls compositioo, which now ¡neludes Caulerpa racemasa varo cylindracea (Sonder) Verlaque, Huisman el Boudouresque an invasive chlorophyta species of Australian origin, recorded as such in the Medirerranean basin from Port Menton, near Italy, 10 Marsei1le and now in ¡he Canary Islands (Verlaque elal., 2000, 2003, 20(4). Davis el al, (2001) reported a competitían for nilrogen between the neorropical seagrass Thalossia tesludinum Banks ex Kiinig, and ¡he rhizophytic green macroalga Halimeda incrassala Larnouroux in the Florida Keys. 1$ a similarproccss operating between H. decipicns and Caulerpa racemosa vaL cylindracea in the Canary waters? funher researeh is needed. Ha/ophiletum decipienlis eonstitutes along the Canarian eoast an oligospecifie (somelimes monospeeifie) meadow eommunity, in deep water, dominated by H. decipiens. The macroalgae Gaulerpa racemosa var. cylindracea is frequenl in the community, al leas! in subtidal areas of Tenerire Island. Somelimes Cymodocea nadosa as well as Dictyola dicholama (Hudson) J. V_Lamouroul\ grow in the eommunity (Pavon-Salas el al., 2000). Apan from these planls, only sorne few epiphytes have been recorded. Using two different eomplementary approaehes we have tried lO evaluale Ihe floristic composition and olher quantitative paramelers of Ha{oph¡letum decipienlis in Canary Islands. Table 1 shows details of this composition and Ihe phytosociological adscriplion oflhe communiry. Tabl.l. HakJphiIeIum decipfenlis Wldpel & M.C. Gi 2002, StTingodio-Thalasion lestucfnum Bomidi 1996. TIlaJassiaS¡fflgodietafia fikIonris Bothidí. Muñil & Del Risro ¡., Bor!Hd; 1996. HaIodvio wrighli-Thalassietea Ies/ue/ioom Den Hartog el; Rivas-Martínez. Fei'OOndez·GonzáIez & L.oicli 1999. "'" "' Oeplh (m} Area (Qn2} "'" "'101 lau N\I'I1ber Cllarilcl.er taXiI: HaIopIliIa dedpiens Oster1feld , 21 '00 60 5 • " " "'" "'" " "'" "" "'" "'"" " " "'" " , " • • • 2 25 3 2J • 21 5 21 6 7 21 9 30 26.5 25,5 '00 400 400 15 25 3 25 '00 40 2 1 1 3 2 3 15 1 1 15 '00 60 1 1 • 2 Comf)jnion laxa: CatJerpa fllUmosa Y<Jl, cylindracea (Sonderj Veriaque.HlJisman ellloudouresque 2 , C~ nodosa (Veria) Ascherson DidyoIa dic/loloma (li.Idson) Lamouroux Epipltytes U/oUltU /lacea (Oilhoiyn) Thurel in le JoIis CyanopIlyO?la , , loulities - Tel\llrife: l.· Cueva ele los Camarones; 2. 5. 9 ~ 10.- El Palm-t.la.I; 3lJOd T.-la Afenila: 4 and 6.' BocinegIO: 8,· Cueva de La Rasca, locali\íes - Griln c..nariil: 11.· Playa B Cabr6n: 12.· Puerto Rico. Note: Epiphytes are in6cated Itvough presente I absence DI&. (jej , 2 P~. 82 The strucrure of ¡he meadows is in evenly dislribulCd homogeneous parches. The vertical distribUlion pattem Oflhis species is between 6 and 40 m depth. 15-25 m dcplh being the mosl common. H. decipicns has becn found growing on sandy and muddy hollams. Table 2, bascd in Tenerife populations. showing frequency, abundance and density data, refers ro the dominanl role played by H. decipiens in the community. 1I is slill early lO relate density of H. decipiens and presence of Caulerpa racemosa 'lar. cy/indracea, and moniloring tasks are required in the Canary ArchipeJago in ¡he future. Table 2. Halophilefllm dedpientis Wiklpret & M.C. Gil 2002 . Plol nO 1 2 3 4 5 6 ¡ 8 9 Dep!ll{m) 22 25 23 22 20 22 30 26.5 25.5 324 324 21 324 324 324 324 53 74 32' 24 324 76 " Ama (cm2) 32' 324 Frequen<;y ("lo) 88 54 ""''''~ 3.13 3.84 2.19 6.79 5.46 5.96 3.75 " 37 5.33 " 70 2.37 2.33 4.70 1.70 2.02 1.54 5.19 2.90 4.91 0.92 1.17 0.66 Densily Loulities - Tenerife. 1.- Cueva de los Camarooes; 2, 5, 9 aod 10.- El Palm-Mar; 3 and 7.-la Arellita; 4 and 6.- Punta de! Boo'negro: 8.· ClJeva de la Rasca. DISCUSSION Halophiletum decipientis constitutes an important submergcd comrllunity in the Canary Islands, which is probably spread on the sea bottom ofall islands. This expansion seerns lO be related to Ihe combined efTect of sorne environrnental faclors, among them seawater temperatute and substrate characteristics. In Tenerife, we have noticed an increase ofthe populations in [he vicinity offish cages for aquaculture farming. In the CaDary !slands as in olher placcs [Ceccherelli el al., 2000; Ceccherelli & Campos, 2002; Fama el al.. 2000; Modena el al.. 2000; Piazzi el al., 2001; Verlaque el al.. 2000,2003,2004)] we have noticed an importantchange in the noristic composition ofthe cornmunity because ofthe progressive expansion oflhe invasive chlorophyta Caulerpa racemosa varo cylindraceae. Because ofthe importance ofthis particular habitat, nowadays endangered because disturbance and íntroduction of an invasive algae, we call the attention in order lO control the fish cages expansion and lts possible relation lO nutrients increase. ACKNOWLEDGEMENTS The authors wish 10 than.k a D. G. González; A. Sancho; R. Linares, R. Herrera, F. Espino and Julio Afonso-Canillo. 83 REFERENCES BELL, 1.0. & WESTÜBY, M. (1989). Abundance ofmacrofauna in denseseagrass is due lO habita! preference, nol predation. Oeeo/agia. 68: 205-209. BETANCORT VlLLALBA, M.J., GONZÁLEZ HENRÍQUEZ, M.N., HAROVNTABRAUE, R., HERRERA PÉREZ, R., SOLER ÜNÍS, E. & V(ERA ROOR.lGUEZ, M.A. (1995). Adiciones coro lógicas a la flora marina de Canarias. Bol. Mocoronésica, 22: 75-89. 80C2OO1/097. Boletín Oficial de Canarias n~97 del1.0S.2QOI.Decre!o 151/2001 de23 de Julio por el que se crea el "Catálogo de especies amenazadas de Canarias". BRAUN I:'ILANQUET, J. (1979). Fitosocio!ogia. Basespara el estudio de las comunidades vegeta/es. H. Blume. Ed. Madrid. (Traducción al español). CECHERELLI, C., PlAZZI, L & CINELLI, F. (2000). Response oCnon-indigenous Caulerpa racemaso (Forsskal) J.Agardh to the native seagrass Posidonia oceanico (L.) Delile: effecl of density of shoots and orientation of edges of meadows. J. Exp. Mar. Biol. &01.,243: 227-240. CECHERELLI, C. & CAMPOS, D. (2002). Different efTeetsofCaulerpa racemosaon two eo-oecuring seagrasses in the Mediterranean. Bol. Marino, 45: 71-76. DAV¡S, B.e. & FOURQUREAN, J.W. (2001). Competition between Ihe tropical alga, Halimeda incrassata. and the seagrass, Thalassia lestudinum. Aquat. Bol.. 71: 2 I7- 232. DA WES, CJ. (1986). Bottinica Marina. Ed. Limusa. Mexieo.673 pp. DAWES, C.J. (1998). Marine Botany. John Wiley& Sons, Ine. New York. - 2a.! ed. Unidet States of America. 480 pp. den HARTOG. C. (1970). The seagrassesofthe world. North-HolJand Pub., Amsterdam. 275pp. den HARTOG, C. (1971). The dynamic aspect in the ecology ofseagrass communities. ThalassiaJugosl.• 7: 101-112. DUARTE, C.M. & CHISCANO. C.L. (1999). Seagrass biomass and produclion: a reassessment. Aquat. BOl., 65: 159·174. EUROPEAN COMMISSION, DO ENVIRONMENT (1999). Na/uro 2000. Interpreta/ion manual ofEuropean Union habitats. Eur. 15n. I 19 pp. FAMA, P., OLSEN,J-L., STAM, W.T. & PROCACCfNl, G. (2000).I~igh levelsofrntra-and ¡n ter-individual polyrnorphism in the rONA ITS 1 of Cauferpa racemosa (Ghlorophyta). Eur. J. Phycol., 35: 349-356. GIL-ROOIUGUEZ, M.C. & CRUZ SIMÓ, T. (1982). Halophifa decipiens Ostenfeld (Hidrocharitaeeae) una fanerógama marina nueva para el Atlántico Oriental. Vieraea, 11:207-216. GIL-RODRÍGUEZ, M.C., AfONSO-CARRll..LO,J. & Wll..DPRET DELA TORRE, W_( 1982). Occurrenee of Halophilo decipiens Ostenfeld on Tenerife, Canary Islands. Aquat. &t., 12: 205-207. GUIRY, M.D. & NlC OHONNCHA, E. (2004). AlgaeBase version 2.1. World-Wide eleco-onic publicalion, National University oflreland. Galway. hnp:llwww.algabase.org " HARüUN, R., GIL·RODRioUEZ,M.C., OrAZ DECASTRO,J. & PRUD' HOMME VAN REINE, W.F. (2002). A Checklistoflhe marine plants from IheCanary Islands, Cen[(al Easlem Atlan!ic Ocean). Bot. Marina, 45: 139-169. HAROUN. R., GIL~RODRÍGUEZ, M.C. & WILDPRET DE LA TORRE, W .(2003). Plan/as Marinas de las Islas Canarias. Ed. Canseeo. 319 pp. HEMMINGA M.A. & DUARTE, C.M. (2000). Seagrass Eco/agy. Cambridge Univ. Press, Cambridge. 298 pp. HERNÁNDEZ-GONZÁLEZ, CL. & GIL-ROORiGUEZ, M.C. (1993). Nuevas citas para la flora marina de la isla de La Palma, Islas Canarias). XSimposio Nacional de Bolánica Criptogómica. Universidad de La Laguna. Tenerife, Islas Canarias. 44 pp. HUISMAN, J.M. (2000). Marine Pfants 01 Australia. University of Westem Australia Press, Nedlands, Westem Australia. 300 pp. LARKUM, A W.D., MCCüMB, A.l.& SHEPERD. S.A. (1989). BioJogyofSeagrasses. A treatise on Ihe biology of seagrasses wilh refrences to rhe Australian region. Amsterdam, Elsevier. 841 pp. L1lTLER, D. S. & L1nER, M. M. (2000). Caribbean ReefPlants. AII identificolionguide lO the reefplalllsaflhe Caribbean. Bahamas, Florida alld GulfofMexico. Offshore Graphics, Ine. Washinglon DC. 542 pp. MeROY c.P. & MeMILLAN, C. (1977). Produelion eeofogyand physiology 01seagrasses. Seagrass eeosystems: a scielllific perspecti"lle. New York C..P. Mc Roy and C. Helffeerieh, pp. 53-87. MODENA, M., MATRICARDI, a., VACCHI, M. & GUIDETII, P. (2000). Spreadingof Caulerpa racemosa (Forsskal) J. Agradh (Bryopsidaceae, Chlorophyta) along the coast ofthe Lígurian Sea. Cryptogamie. Algol., 21: 301-304. MORElRA-REYES. A., MONTERRüSO, O., AGUIRRE, H., CRUZ-REYES, A., GIL· RODRiGUEZ, M.C. & NÚÑEZ, J. (2004). Diversidad y estruerui-a de Ha/ophiJetum decipientis en el L1C sebadales de San Andrés (ES 7020 I20), Tenerife, islas Canarias. Rev. Acad. Can. de Ciencias.. XV, 3-4: 143-158. QLlVElRA DE, E.C., PIRANI J.R. &GIUl.JETTI, A.M. (1983). The BraziJian seagrasses. Aqual. BOL" 16: 251-267. PAYRI, C., N'YEURT, A.D.R. & OREMPULLER, J. (2000). Algae ofFrench Polynesia. Algues de Polynésie Franr;aise. Au Vent des l1es Editions-Tahili. 187 pp. PAVüN-SALAS, N., HERRERA, R., HERNÁNDEZ-GUERRA, A. & HAROUN, R. (2000). Distnbutíonal pattem of seagrasses in the Canary Islands, Central-East Atlantic Oeean).J. CoastaJ Research. 16: 329·335. PlAZZl, L., CECCHERELLI, a. & CINELLl, F. (200 1). Threat 10 macroalgal diversiry: effccts oflhe introduced green alga Caulerpa racemosa in the Medíterranean. Mar. Eco/. Prog. Ser., 210: 149·159. RlVAS-MARTÍNEZ, S., FERNÁNDEZ GONZÁLEZ, F., WIDI, J., LOUSA, M. & PENAS, A. (200 1). Sintaxonomical eheeklist ofvascular plam conununílies ofSpaín and Portugal to association leve!. ltínera Geobotánica, ¡ 4: 5-341. " RIV AS-MARTlNEZ, S., DIAz, T.E., FERNÁNDEZ-GONZÁLEZ. F., rzco, J., lüIDI, l, LousA, M. & PENAS, A, (2002). Vascular. Plan! communiries ofSpain and Portugal. Addenda to the synl3xonomica[ Checklist of2001. [linera GeobOlánica, 15: 115-116. VERLAQUE, M., BOUDOURESQUE, C.F., MEINESZ. A & ORA VEZ, V. (2000). The Cal.llerpo. racemosa Complex, Caulerpales, Ulvophyceae) in the Mediterranean Sea, Bol. Mor¡na,4): 49-68. VERLAQUE. M., DURAND, c., mnSMAN J.M., BOUDOURESQUE. C.F. & LE PARCO Y. (2003).00 ¡he identiry and origín ofthe Mediterranean invasive Cau/erpa racemosa (CaulerpaJes, Chlorophyta). Eur.J. Phycol., 38: 325-339. VERLAQUE, M., AFüNSO-CARRILLO, 1., GlL-ROORÍGUEZ M.C., DURAND, e., BüUOüURESQUE.CH.F. &LE PARCO, Y..(2004). Blitzkrieg ¡na marine invasion: Caulerpa racemosa varo cylindracea (Bryopsidales, Chlorophyta) reaches the Caoary Islands, (nonh-east Atlanlic). Biological /nvasions, 6: 269-281. WOMERSLEY, H.B.S. (1984). The marine benrhicjlora o[soulhern Australia_ Pan!. Government Printer, Soulh Australia, Adelaide. 329 pp. YOUNG, P.C. (1978). Moreton Bay, Queensland: A nurseyarea forjuvenilepenaeid prawns. Ausl. J Mar. Freshw. Res., 29: 55-75. Fecha de recepción: 2geDero 2007 Fecha de aceptación: 15 febrero 2007