Abstract
Bioeroding sponges play a central role in carbonate cycling on corals reefs. They may respond differently to habitat deterioration than many other benthic invertebrates, because at some locations, their abundances increased after disturbance. We reviewed literature on these sponges in context of environmental change and provide meta-analyses at global level. A difficult taxonomy and scarce scientific expertise leave them inadequately studied, even though they are the best-known internal bioeroders. They are sheltered within the substrate they erode, appear to be comparatively resilient against environmental change and can have heat-resistant photosymbionts and ‘weedy’ traits, including multiple pathways to reproduce or disperse and fast growth and healing abilities. Especially temperature stress appears to disable calcifiers stronger than bioeroding sponges. Moreover, increases in bioeroding sponge abundances have been related to eutrophication and disturbances that led to coral mortality. Chemical sponge bioerosion is forecast to double with doubled partial pressure of carbon dioxide, but reduced substrate density may counteract this effect, as dominant sponges erode more in denser substrates. Case examples portray shifting impacts of bioeroding sponges with environmental change, with some reefs already being erosional. Most available data and the largest known species record are from the Caribbean. Data from the Coral Triangle and India are largely restricted to faunistic records. Red Sea, Japanese and cold-water reef bioeroding sponges are the least studied. We need more quality research on functions and interaction effects, about which we are still insufficiently informed. With many calcifiers increasingly failing and bioeroding sponges still doing well, at least at intermediate levels of local and global change, these sponges may continue to significantly affect coral reef carbonate budgets. This may transform them from valuable and necessary recyclers of calcium carbonate to problem organisms.
Access this chapter
Tax calculation will be finalised at checkout
Purchases are for personal use only
References
Achlatis M, van der Zande RM, Schönberg CHL, Fang JKH, Hoegh-Guldberg O, Dove S (in press) Sponge bioerosion on changing reefs: ocean warming poses physiological constraints to the success of a photosymbiotic excavating sponge. Sci Rep
Acker KL, Risk MJ (1985) Substrate destruction and sediment production by the boring sponge Cliona caribbaea on Grand Cayman Island. J Sediment Petrol 55:705–711
Aerts LA, van Soest RW (1997) Quantification of sponge/coral interactions in a physically stressed reef community, NE Colombia. Mar Ecol Prog Ser 148:125–134
Ainsworth TD, Heron SF, Ortiz JC, Mumby PJ, Grech A, Ogawa D, Eakin CM, Leggat W (2016) Climate change disables coral bleaching protection on the Great Barrier Reef. Science 352:338–342
Alander H (1935) Additions to the Swedish sponge fauna. Ark Zool 28:1–6
Alander H (1942) Sponges from the Swedish west-coast and adjacent waters. PhD thesis, University Gothenburg, Gothenburg, 95 pp, 16 pls
Al-Sofyani AA, Floos YAM (2013) Effect of temperature on two reef-building corals Pocillopora damicornis and P. verrucosa in the Red Sea. Oceanologia 55:917–935
Althaus F, Hill N, Ferrari R, Edwards L, Przeslawski R, Schönberg CHL, Stuart-Smith R, Barrett N, Edgar G, Colquhoun J, Trn M, Jordan A, Rees T, Gowlett-Holmes K (2015) A standardised vocabulary for identifying benthic biota and substrata from underwater imagery: the CATAMI Classification Scheme. PLoS One 10:e0141039
Alvarado JJ, Cortés J, Guzman H, Reyes-Bonilla H (2016) Bioerosion by the sea urchin Diadema mexicanum along Eastern Tropical Pacific coral reefs. Mar Ecol 37:1088–1102
Alvarado JJ, Grassian B, Cantera-Kintz JR, Carballo JL, Londoño-Cruz E (2017) Coral reef bioerosion in the Eastern Tropical Pacific. In: Glynn PW, Manzello PD, Enochs IC (eds) Coral reefs of the Eastern Tropical Pacific. Springer, Netherlands, pp 369–403
Amaro M, Ramírez I (2011) Nuevos registros de esponjas (Porifera) para el Golfo de Cariaco, Venezuela. Bol Inst Oceanogr Venezuela 50:133–147
Andersson AJ, Mackenzie FT (2011) Ocean acidification: setting the record straight. Biogeosci Discuss 8:6161–6190
Andréa BR, Batista D, Sampaio CLS, Muricy G (2007) Spongivory by juvenile angelfish (Pomacanthidae) in Salvador, Bahia State, Brazil. In: Custódio MR, Lôbo-Hajdu G, Hajdu E, Muricy G (eds) Porifera research. Biodiversity, innovation and sustainability. National Museum, Rio de Janeiro, pp 131–137
Angermeier H, Kamke J, Abdelmohsen UR, Krohne G, Pawlik JR, Lindquist NL, Hentschel U (2011) The pathology of sponge orange band disease affecting the Caribbean barrel sponge Xestospongia muta. FEMS Microbiol Ecol 75:218–230
Angermeier H, Glöckner V, Pawlik JR, Lindquist NL, Hentschel U (2012) Sponge white patch disease affecting the Caribbean sponge Amphimedon compressa. Diseases Aquat Org 99:95
Annandale N (1907) Notes on freshwater sponges. VI. The midday siesta of Spongilla in the tropics. Rec Indian Mus 1:387
Annandale N (1915a) Some sponges parasitic on Clionidae with further notes on that family. Rec Indian Mus 11:457–478, pl XXXIV
Annandale N (1915b) Indian boring sponges of the family Clionidae. Rec Indian Mus 11:1–24, pl I
Annandale N (1915c) Fauna of the Chilka Lake sponges. Mem Indian Mus Calcutta 5:21–55, pls III-V
Annandale N (1920) Description of a clionid sponge parasitic in the shells of Bullinus prinsepii. Rec Geol Surv India 51:62–64
Arndt W (1927) Kalk-und Kieselschwämme von Curaçao. Bijdr Dierk 25:133–158
Australian National Coral Reef Task Force (2016) Only 7% of the Great Barrier Reef has avoided coral bleaching. Media release of the Australian National Coral Reef Task Force issued by the ARC Centre of Excellence for Coral Reef Studies. https://www.coralcoe.org.au/media-releases/only-7-of-the-great-barrier-reef-has-avoided-coral-bleaching. [6 June 2016]
Ávila E, Riosmena-Rodríguez R, Hinojosa-Arango G (2012) Sponge–rhodolith interactions in a subtropical estuarine system. Helgol Mar Res 67:349–357
Azzini F, Calcinai B, Iwasaki N, Bavestrello G (2007a) A new species of Thoosa (Demospongiae, Hadromerida) excavating precious coral Corallium sp. from Midway. Ital J Zool 74:405–408
Azzini F, Calcinai B, Cerrano C; Bavestrello G & Pansini M (2007b) Sponges of the marine karst lakes and of the coast of the islands of Ha Long Bay (north Vietnam). In: Custódio MR, Lôbo-Hajdu G, Hajdu E, Muricy G (eds) Porifera research. Biodiversity, innovation and sustainability. National Museum, Rio de Janeiro, pp 157–164
Baba T, Mleczko R, Burbidge D, Cummins PR, Thio HK (2008) The effect of the Great Barrier Reef on the propagation of the 2007 Solomon Islands tsunami recorded in northeastern Australia. Pure Appl Geophys 165:2003–2018
Bak RPM (1976) The growth of coral colonies and the importance of crustose coralline algae and burrowing sponges in relation with carbonate accumulation. Neth J Sea Res 10:285–337
Baker AC, Starger CJ, McClanahan TR, Glynn PW (2004) Coral reefs: corals’ adaptive response to climate change. Nature 430:741
Ball FW (1975) A survey of the marine organisms at Halape, Hawaii Valocanoes National Park. Halape Marine Survey Technical Report 10. University of Hawaii and Manoa, Honolulu, pp 1–51
Baquero DR (2010) Caracterisacion estructural de la comunidad bentonica en el arrecife de Mahahual, Mexico. PhD thesis, Instituto Politecnico Nacional, La Paz, 117 pp
Barbieri M, Bavestrello G, Sarà M (1995) Morphological and ecological differences in two electrophoretically detected species of Cliona (Porifera, Demospongiae). Biol J Linnean Soc 54:193–200
Barletta G, Vighi M (1968) Ricerche sul corallo rosso. V. Poriferi perforanti lo sclerasse di Corallium rubrum Lamarck. Rend Ist Lombardo Sci Lett Milano B 102:145–159
Barnes DKA, Bell JJ (2002) Coastal sponge communities of the West Indian Ocean: taxonomic affinities, richness and diversity. Afr J Ecol 40:37–349
Barthelmy D (1997–2014) Webmineral. Mineralogy database. http://www.webmineral.com. [6 June 2016]
Barucca M, Azzini F, Bavestrello G, Biscotti MA, Calcinai B, Canapa A, Cerrano C, Olmo E (2007) The systematic position of some boring sponges (Demospongiae, Hadromerida) studied by molecular analysis. Mar Biol 151:529–535
Bass D (1993) First report of Suberites undulatus (Demospongiae) from coastal waters of the Gulf of Maxico. Bull Mar Sci 52:843
Batista D, Muricy GR, Andréa BR, Villaça RC (2012) High intraspecific variation in the diet of the french angelfish Pomacanthus paru in the south-western Atlantic. Braz J Oceanogr 60:449–454
Bautista-Guerrero E, Carballo JL, Cruz-Barraza JA, Nava HH (2006) New coral reef boring sponges (Hadromerida: Clionaidae) from the Mexican Pacific Ocean. J Mar Biol Assoc UK 86:963–970
Bautista-Guerrero E, Carballo JL, Maldonado M (2010) Reproductive cycle of the coral-excavating sponge Thoosa mismalolli (Clionaidae) from Mexican Pacific coral reefs. Invertebr Biol 129:285–296
Bautista-Guerrero E, Carballo JL, Maldonado M (2014) Abundance and reproductive patterns of the excavating sponge Cliona vermifera: a threat to Pacific coral reefs? Coral Reefs 33:259–266
Bautista-Guerrero E, Carballo JL, Aguilar-Camacho JM, Sifuentes-Romero I (2016) Molecular and morphological differentiation of sympatric larvae of coral excavating sponges of genus Thoosa. Zoomorphology 135:159–165
Bavestrello G, Arillo A, Benati U, Cerrano C, Cattaneovietti R, Cortesogno L, Gaggero L, Giovine M, Tonetti M, Sarà M (1995) Quartz dissolution by the sponge Chondrosia reniformis (Porifera, Demospongiae). Nature 378:374–376
Bavestrello G, Calcinai B, Cerrano C, Pansini M, Sarà M (1996) The taxonomic status of some Mediterranean clionids (Porifera: Demospongiae) according to morphological and genetic characters. Bull Inst Royal Sci Nat Belgique Biol suppl 66:185–195
Bavestrello G, Calcinai B, Cerrano C, Sarà M (1998) Alectona species from north-western Pacific (Demospongiae: Clionidae). J Mar Biol Assoc UK 78:59–73
Bavestrello G, Bo M, Canese S, Sandulli R, Cattaneo-Vietti R (2014) The red coral populations of the gulfs of Naples and Salerno: human impact and deep mass mortalities. Ital J Zool 81:552–563
Becker LC, Reaka-Kudla ML (1997) The use of tomography in assessing bioerosion in corals. In: Proceedings of the 8th international coral reef symposium, vol 2, Panama City, pp 1819–1824
Becking LE, Cleary DFR, de Voogd NJ (2013) Sponge species composition, abundance, and cover in marine lakes and coastal mangroves in Berau, Indonesia. Mar Ecol Prog Ser 481:105–120
Beckley LE, Lombard AT (2012) A systematic evaluation of the incremental protection of broad-scale habitats at Ningaloo Reef, Western Australia. Mar Freshw Res 63:17–22
Beer S, Ilan M (1998) In situ measurements of photosynthetic irradiance responses of two Red Sea sponges growing under dim light conditions. Mar Biol 131:613–617
Bell JJ (2002) Regeneration rates of a sublittoral demosponge. J Mar Biol Assoc UK 82:169–170
Bell JJ, Davy SK, Jones T, Taylor MW, Webster N (2013) Could some coral reefs become sponge reefs as our climate changes? Glob Change Biol 19:613–2624
Bellwood DR (1985) Direct estimate of bioerosion by two parrotfish species, Chlorurus gibbus and C. sordidus, on the Great Barrier Reef, Australia. Mar Biol 121:419–429
Bengtson P (1988) Open nomenclature. Palaeontology 31:223–227
Benzoni F, Calcinai B, Eisinger M, Klaus R (2008) Coral disease mimic: sponge attacks Porites lutea in Yemen. Coral Reefs 27:695
Bergman KM (1983) The distribution and ecological significance if the boring sponge Cliona viridis on the Great Barrier Reef, Australia. MSc thesis, McMaster University, Hamilton, 69 pp
Bergquist PR (1961) A collection of Porifera from northern New Zealand, with descriptions of seventeen new species. Pac Sci 15:33–48
Bergquist PR (1965) The sponges of Micronesia, Part I. The Palau Archipelago. Pac Sci 19:123–204
Bergquist PR (1967) Additions to the sponge fauna of the Hawaiian Islands. Micronesica 3:159–174
Bergquist PR (1977) Porifera. In: Devaney DM, Eldredge LG (eds) Reef and shore fauna of Hawaii. Section 1: Protozoa through Ctenophora. Bishop Museum Press, Honolulu, pp 53–69
Bergquist PR, Tizard CA (1967) Australian intertidal sponges from the Darwin area. Micronesica 3:175–202
Bergquist PR, Morton JE, Tizard CA (1971) Some Demospongiae from the Solomon Islands with descriptive notes on the major sponge habitats. Micronesica 7:99–121
Berkelmans R, De’ath G, Kininmonth S, Skirving WJ (2004) A comparison of the 1998 and 2002 coral bleaching events on the Great Barrier Reef: spatial correlation, patterns, and predictions. Coral Reefs 23:74–83
Berman T, Paldor N, Brenner S (2003) Annual SST cycle in the Eastern Mediterranean, Red Sea and Gulf of Elat. Geophys Res Lett 30:1261
Bertolino M, Pica D, Bavestrello G, Iwasaki N, Calcinai B (2011) A new species of Triptolemma (Porifera: Pachastrellidae) from the Pacific Ocean with a revision of the genus. J Mar Biol Assoc UK 91:329–338
Bertolino M, Cerrano C, Bavestrello G, Carella M, Pansini M, Calcinai B (2013) Diversity of Porifera in the Mediterranean coralligenous accretions, with description of a new species. ZooKeys 336:1–37
Bertram GC (1936) Some aspects of the breakdown of coral at Ghardaqa, Red Sea. Proc Zool Soc Lond 106:1011–1026
Berumen ML, Hoey AS, Bass WH, Bouwmeester J, Catania D, Cochran JE, Khalil MT, Miyake S, Mughal MR, Spaet JL, Saenz-Agudelo P (2013) The status of coral reef ecology research in the Red Sea. Coral Reefs 32:737–748
Beuck L, Freiwald A (2005) Bioerosion patterns in a deep-water Lophelia pertusa (Scleractinia) thicket (Propeller Mound, northern Porcupine Seabight). In: Freiwald A, Roberts JM (eds) Cold-water corals and ecosystems. Springer, Berlin, pp 915–936
Beuck L, Vertino A, Stepina E, Karolczak M, Pfannkuche O (2007) Skeletal response of Lophelia pertusa (Scleractinia) to bioeroding sponge infestation visualised with micro-computed tomography. Facies 53:157–176
Beuck L, Freiwald A, Taviani M (2010) Spatiotemporal bioerosion patterns in deep-water scleractinians from off Santa Maria di Leuca (Apulia, Ionian Sea). Deep Sea Res II Topical Stud Oceanogr 57:458–470
Bhagirathan U, Panda SK, Madhu VR, Meenakumari B (2008) Occurrence of live octocorals in the trawling grounds of Veraval Coast of Gujarat, Arabian Sea. Turkish J Fish Aquat Sci 8:369–372
Bloom SA (1976) Morphological correlations between dorid nudibranch predators and sponge prey. Veliger 18:289–301
Bo M, Bava S, Canese S, Angiolillo M, Cattaneo-Vietti R, Bavestrello G (2014) Fishing impact on deep Mediterranean rocky habitats as revealed by ROV investigation. Biol Conserv 171:167–176
Borchiellini C, Alivon EL, Vacelet J (2004) The systematic position of Alectona (Porifera, Demospongiae): a tetractinellid sponge. Boll Mus Ist Biol Univ Genova 68:209–217
Bosc LAG (1802) Histoire naturelle des éponges. Éponge pezize, Spongia peziza. Hist Nat Vers 3:147–148
Boury-Esnault N (1971) Spongiaires de la zone rocheuse de Banyuls-sur-Mer. II. Systématique. Vie Milieu B 22:287–350
Boury-Esnault N (1973) Résultats Scientifiques des Campagnes de la ‘Calypso’. Campagne de la ‘Calypso’ au large des côtes atlantiques de l’Amérique du Sud (1961-1962). I. 29. Spongiaires. Ann Institut Océanogr 49(Suppl 10):263–295
Boury-Esnault N, Pansini M, Uriz MJ (1994) Spongiaires bathyaux de la mer d’Alboran et du golfe ibéro-marocain. Mém Mus Natl Hist Nat 160:1–174
Boury-Esnault N, Klautau M, Bézac C, Wulff J, Solé-Cava AM (1999) Comparative study of putative conspecific sponge populations from both sides of the Isthmus of Panama. J Mar Biol Assoc UK 79:39–50
Bramanti L, Movilla J, Guron M, Calvo E, Gori A, Dominguez-Carrió C, Grinyó J, Lopez-Sanz A, Martinez-Quintana A, Pelejero C, Ziveri P (2013) Detrimental effects of ocean acidification on the economically important Mediterranean red coral (Corallium rubrum). Glob Change Biol 19:1897–1908
Bramanti L, Vielmini I, Rossi S, Tsounis G, Iannelli M, Cattaneo-Vietti R, Priori C, Santangelo G (2014) Demographic parameters of two populations of red coral (Corallium rubrum L. 1758) in the North Western Mediterranean. Mar Biol 161:1015–1026
Brodie J, Waterhouse J (2016) Great Barrier Reef (Australia): a multi-ecosystem wetland with a multiple use management regime. In: Finlayson CM, Milton GR, Prentice RC, Davidson NC (eds) The wetland book II: distribution, description and conservation. Springer, Dordrecht, pp 915–936
Bromley RG (1978) Bioerosion of Bermuda reefs. Palaeogeogr Palaeoclimatol Palaeoecol 23:169–197
Bromley RG (2004) A stratigraphy of marine bioerosion. In: McIlroy D (ed) The application of ichnology to palaeoenvironmental and stratigraphic analysis. Geol Soc Special Pub 228, London, pp 455–479
Bromley RG, D’Alessandro A (1984) The ichnogenus Entobia from the Miocene, Pliocene and Pleistocene of southern Italy. Riv It Paleont Strat 90:227–296
Brooke S, Ross SW, Bane JM, Seim HE, Young CM (2013) Temperature tolerance of the deep-sea coral Lophelia pertusa from the southeastern United States. Deep Sea Res II Topical Stud Oceanogr 92:240–248
Bruckner AW (2009) Rate and extent of decline in Corallium (pink and red coral) populations: existing data meet the requirements for a CITES Appendix II listing. Mar Ecol Prog Ser 397:319–332
Bruckner AW, Dempsey AC (2015) The status, threats, and resilience of reef-building corals of the Saudi Arabian Red Sea. In: Rasul NMA, Stewart ICF (eds) The Red Sea. Springer, Berlin, pp 471–486
Bruggemann JH, van Oppen MJH, Breeman AM (1994) Foraging by the stoplight parrotfish Sparisoma viride. I. Food selection in different, socially determined habitats. Mar Ecol Prog Ser 106:41–55
Burton M (1934) Sponges. Great Barrier Reef Expedition (1928–1929). Rep Br Mus Nat Hist 4:513–614
Büttner E, Siebler F (2013) The impact of simulated dredging on sponges of the East Australian coastal line. University of Stuttgart, Stuttgart, 70
Caballero H, Rosales D, Alcalá A (2005) Estudio diagnóstico del arrecife coralino del Rincón de Guanabo, Ciudad de la Habana, Cuba. 1. Corales, gorgonáceos y esponjas. Rev Invest Mar 26:207–217 (same article in Rev Invest Mar 27:49–59 in 2006)
Calcinai B, Cerrano C, Bavestrello G, Sarà M (1999) Biology of the massive symbiotic sponge Cliona nigricans (Porifera: Demospongiae) in the Ligurian Sea. Mem Queensl Mus 44:77–83
Calcinai B, Cerrano C, Sarà M, Bavestrello G (2000) Boring sponges (Porifera, Demospongiae) from the Indian Ocean. Ital J Zool 67:203–219
Calcinai B, Bavestrello G, Cerrano C, Sarà M (2001) Boring sponges living into precious corals from the Pacific Ocean. Ital J Zool 68:153–160
Calcinai B, Cerrano C, Bavestrello G, Milanese M, Sarà M (2002) Il popolamento di spugne perforatrici di Corallium rubrum e die alcuni madreporari del Promontorio die Portofino. Boll Mus Ist Biol Univ Genova 64-65:53–59
Calcinai B, Bavestrello G, Cerrano C (2004a) Bioerosion micro-patterns as diagnostic characteristics in boring sponges. Boll Mus Ist Biol Univ Genova 68:229–238
Calcinai B, Azzini F, Bavestrello G, Iwasaki N, Cerrano C (2004b) Redescription of Alectona verticillata (Johnson) (Porifera, Alectonidae) boring into Japanese precious coral. Ital J Zool 71:337–339
Calcinai B, Bavestrello G, Cerrano C (2005) Excavating sponge species from the Indo-Pacific Ocean. Zool Stud 44:5–18
Calcinai B, Azzini F, Bavestrello G, Cerrano C, Pansini M, Thung DC (2006) Boring sponges from the Ha Long Bay, Tonkin Gulf, Vietnam. Zool Stud 45:201–212
Calcinai B, Azzini F, Bavestrello G, Gaggero L, Cerrano C (2007a) Excavating rates and boring pattern of Cliona albimarginata (Porifera: Clionaidae) in different substrata. In: Custódio MR, Lôbo-Hajdu G, Hajdu E, Muricy G (eds) Porifera research. Biodiversity, innovation and sustainability. National Museum, Rio de Janeiro, pp 203–210
Calcinai B, Cerrano C, Bavestrello G (2007b) Three new species and one re-description of Aka. J Mar Biol Assoc UK 87:1355–1365
Calcinai B, Cerrano C, Iwasaki N, Bavestrello G (2008a) Sponges boring into precious corals: an overview with description of a new species of Alectona (Demospongiae, Alectonidae) and a world-wide identification key for the genus. Mar Ecol 29:273–279
Calcinai B, Bavestrello G, Cerrano C, Gaggero L (2008b) Substratum microtexture affects the boring pattern of Cliona albimarginata (Clionaidae, Demospongiae). In: Wisshak M, Tapanila L (eds) Current developments in bioerosion. Springer, Berlin, pp 204–211
Calcinai B, Cerrano C, Iwasaki N, Bavestrello G (2010) Biodiversity and ecology of sponge boring into precious corals: a worldwide overview. In Bussoletti E, Cottingham D, Bruckner A, Roberts G, Sandulli R (eds) Proceedings of the International Workshop on Red Coral Science, Management, and Trade: Lessons from the Mediterranean, Naples. NOAA Technical Memorandum CRCP-13, Silver Spring, pp 165–171
Calcinai B, Bertolino M, Bavestrello G, Montori S, Mori M, Pica D, Valisano L, Cerrano C (2015) Comparison between the sponge fauna living outside and inside the coralligenous bioconstruction. A quantitative approach. Medit Mar Sci 16:413–418
Callahan MK (2005) Distribution of clionid sponges in the Florida Keys National Marine Sanctuary (FKNMS), 2001–2003. PhD thesis, University of South Florida, 79 pp
Cantera K, Jaime R, Orozco C, Londoño-Cruz E, Toro-Farmer G (2003) Abundance and distribution patterns of infaunal associates and macroborers of the branched coral (Pocillopora damicornis) in Gorgona Island (Eastern Tropical Pacific). Bull Mar Sci 72:207–219
Carballo JL, Cruz-Barraza JA (2005) Cliona microstrongylata, a new species of boring sponge from the Sea of Cortés (Pacific Ocean, México). Cah Biol Mar 46:379–387
Carballo JL, Nava H (2007) A comparison of sponge assemblage patterns in two adjacent rocky habitats (tropical Pacific Ocean, Mexico). Ecoscience 14:92–102
Carballo JL, Sanchez-Moyano JE, García-Gómez JC (1994) Taxonomic and ecological remarks on boring sponges (Clionidae) from the Straits of Gibraltar (southern Spain): tentative bioindicators? Zool J Linnean Soc 112:407–424
Carballo JL, Naranjo SA, García-Gómez JC (1996) Use of marine sponges as stress indicators in marine ecosystems at Algeciras Bay (Southern Iberian Peninsula). Mar Ecol Prog Ser 135:109–122
Carballo JL, Cruz-Barraza JA, Gomez P (2004) Taxonomy and description of clionaid sponges (Hadromerida, Clionaidae) from the Pacific Ocean of Mexico. Zool J Linnean Soc Lond 141:353–397
Carballo JL, Hepburn L, Nava HH, Cruz-Barraza JA, Bautista-Guerrero E (2007) Coral boring Aka-species (Porifera: Phloeodictyidae) from Mexico with description of Aka cryptica sp. nov. J Mar Biol Assoc UK 87:1477–1484
Carballo JL, Cruz-Barraza JA, Nava H, Bautista E (2008a) Esponjas perforadoras de sustratos calcáreos: importancia en los ecosistemas arrecifales del Pacifico este. CONABIO, México City, 187 pp
Carballo JL, Bautista-Guerrero E, Leyte-Morales GE (2008b) Boring sponges and the modeling of coral reefs in the east Pacific Ocean. Mar Ecol Prog Ser 356:113–122
Carballo JL, Bautista E, Nava H, Cruz-Barraza JA, Chávez JA (2013) Boring sponges, an increasing threat for coral reefs affected by bleaching events. Ecol Evol 3:872–886
Carballo JL, Ovalle-Beltrán H, Yáñez B, Bautista-Guerrero E, Nava-Bravo H (2016) Assessment of the distribution of sponge chips in the sediment of East Pacific Ocean reefs. Mar Ecol 38:e12390
Carpenter RC (1988) Mass mortality of a Caribbean sea urchin: immediate effects on community metabolism and other herbivores. PNAS 85:511–514
Carreiro-Silva M, McClanahan TR (2012) Macrobioerosion of dead branching Porites, 4 and 6 years after coral mass mortality. Mar Ecol Prog Ser 458:103–122
Carricart-Ganivet JP, Vásquez-Bedoya LF, Cabanillas-Terán N, Blanchon P (2013) Gender-related differences in the apparent timing of skeletal density bands in the reef-building coral Siderastrea siderea. Coral Reefs 32:769–777
Carter HJ (1874) Descriptions and figures of deep-sea sponges and their spicules from the Atlantic Ocean, dredged up on board H.M.S. ‘Porcupine’, chiefly in 1869; with figures and descriptions of some remarkable spicules from the Agulhas Shoal and Colon, Panama. Ann Mag Nat Hist 14:207–221, 245–257, pls XIII–XV
Carter HJ (1879) Contributions to our knowledge of the Spongida. Ann Mag Nat Hist 3:284–304, 343–360, pls XXV–XXVII
Carter HJ (1880) Report on specimens dredged up from the Gulf of Manaar and presented to the Liverpool Free Museum by Capt. W.H. Cawne Warren. Ann Mag Nat Hist 6:35–61, pls IV–VI; 129–156, pls VII, VIII
Carter HJ (1881) Supplementary report on specimens dredged up from the Gulf of Manaar, together with others from the sea in the vicinity of the Basse Rocks and from Bass’s Straits respectively, presented to the Liverpool Free Museum by Capt. H. Cawne Warren. Ann Mag Nat Hist 7:361–385, pl XVIII
Carter HJ (1882) Some sponges from the West Indies and Acapulco in the Liverpool Free Museum described, with general and classificatory remarks. J Nat Hist 9:266–301, 346–368, pls XI–XII
Carter HJ (1887) Report on the marine sponges, chiefly from King Island, in the Mergui Archipelago, collected for the trustees of the Indian Museum, Calcutta, by Dr. John Anderson, F.R.S., superintendent of the museum. J Linnean Soc Zool 21:61–84, pls 5–7
Carvalho MD, Hajdu E, Mothes B, van Soest RW (2004) Amorphinopsis (Halichondrida: Demospongiae) from the Atlantic Ocean, with the description of a new species. J Mar Biol Assoc 84:925–930
Carver CE, Thériault I, Mallet AL (2010) Infection of cultured eastern oysters Crassostrea virginica by the boring sponge Cliona celata, with emphasis on sponge life history and mitigation strategies. J Shellfish Res 29:905–915
Cavalcanti HGB (2013) Taxonomia de esponjas marinhas do litoral norte de Pernambuco. MSc thesis, Federal University of Pernambuco, Recife, p 70
Cebrian E (2010) Grazing on coral reefs facilitates growth of the excavating sponge Cliona orientalis (Clionaidae, Hadromerida). Mar Ecol 31:533–538
Cebrian E, Uriz MJ (2006) Grazing on fleshy seaweeds by sea urchins facilitates sponge Cliona viridis growth. Mar Ecol Prog Ser 323:83–89
Cerrano C, Bavestrello G, Bianchi CN, Cattaneo-Vietti R, Bava S, Morganti C, Morri C, Picco P, Sarà G, Schiaparelli S, Siccardi A (2000) A catastrophic mass-mortality episode of gorgonians and other organisms in the Ligurian Sea (North-western Mediterranean), summer 1999. Ecol Lett 3:284–293
Cerrano C, Bavestrello G, Bianchi CN, Calcinai B, Cattaneo-Vietti BR, Morri C, Sarà M (2001) The role of sponge bioerosion in Mediterranean coralligeneous accretions. In: Faranda FM, Letterio G, Spezie G (eds) Mediterranean ecosystems. Structures and processes. Springer, Italy, pp 235–240
Cerrano C, Bavestrello G, Boyer M, Calcinai B, Lalamentik LTX, Pansini M (2002) Psammobiontic sponges from the Bunaken Marine Park (North Sulawesi, Indonesia): interactions with sediments. In: Proceedings of the 9th international coral reef symposium, vol 1, Bali, pp 279–282
Cerrano C, Sambolino P, Azzini F, Calcinai B, Bavestrello G (2007) Growth of the massive morph of Cliona nigricans (Schmidt 1862) (Porifera, Clionaidae) on different mineral substrata. Ital J Zool 74:13–19
Cerrano C, Cardini U, Bianchelli S, Corinaldesi C, Pusceddu A, Danovaro R (2013) Red coral extinction risk enhanced by ocean acidification. Sci Rep 3:srep01457
Chaves-Fonnegra A, Zea S (2007) Observations on reef coral undermining by the Caribbean excavating sponge Cliona delitrix (Demospongiae, Hadromerida). Porifera research: biodiversity, innovation and sustainability. In: Custódio MR, Lôbo-Hajdu G, Hajdu E, Muricy G (eds) Porifera research. Biodiversity, innovation and sustainability. National Museum, Rio de Janeiro, pp 247–264
Chaves-Fonnegra A, Zea S (2011) Coral colonization by the encrusting excavating Caribbean sponge Cliona delitrix. Mar Ecol 32:162–173
Chaves-Fonnegra A, Castellanos L, Zea S, Duque C, Rodríguez J, Jiménez C (2008) Clionapyrrolidine A – a metabolite from the encrusting and excavating sponge Cliona tenuis that kills coral tissue upon contact. J Chem Ecol 34:1565–1574
Chaves-Fonnegra A, Feldheim KA, Secord J, Lopez JV (2015) Population structure and dispersal of the coral-excavating sponge Cliona delitrix. Mol Ecol 24:1447–1466
Chavez-Fonnegra A, López-Victoria M, Parra-Velandia F, Zea S (2005) Ecología química de las esponjas excavadoras Cliona aprica, C. caribbaea, C. delitrix y C. tenuis. Bol Invest Mar Cost 34:43–67
Chavez-Fonnegra A, Zea S, Gómez ML (2007) Abundance of the excavating sponge Cliona delitrix in relation to sewage discharge at San Andres Island, sw Caribbean, Colombia. Bol Invest Mar Cost 36:63–78
Chavez-Fonnegra A, Maldonado M, Blackwelder P, Lopez JV (2016) Asynchronous reproduction and multi-spawning in the coral-excavating sponge Cliona delitrix. J Mar Biol Assoc UK 96:515–528
Chazottes V, Le Campion-Alsumard T, Peyrot-Clausade M (1995) Bioerosion rates on coral reefs: interactions between macroborers, microborers and grazers (Moorea, French Polynesia). Palaeogeogr Palaeoclimatol Palaeoecol 113:189–198
Chen T, Li S, Yu K (2013) Macrobioerosion in Porites corals in subtropical northern South China Sea: a limiting factor for high-latitude reef framework development. Coral Reefs 32:101–108
Chervyakova NA (2007) Porifera (Demospongia) of the Nhatrang bay. In: Britayev TA, Pavlov DS (eds) Benthic fauna of the Bay of Nhatrang, Southern Vietnam. KMK Scientific Press, Moscow, pp 235–249
Chiappone M, Rutten LM, Miller SL, Swanson DW (2007) Large-scale distributional patterns of the encrusting and excavating sponge Cliona delitrix Pang on Florida Keys coral substrates. In: Custódio MR, Lôbo-Hajdu G, Hajdu E, Muricy G (eds) Porifera research. Biodiversity, innovation and sustainability. National Museum, Rio de Janeiro, pp 255–263
Clark T, Morton B (1999) Relative roles of bioerosion and typhoon-induced disturbance on the dynamics of a high latitude scleractinian coral community. J Mar Biol Assoc UK 79:803–820
Cobb WR (1969) Penetration of calcium carbonate substrates by the boring sponge, Cliona. Am Zool 9:783–790
Cobb WR (1975) Fine structural features of destruction of calcareous substrata by the burrowing sponge Cliona celata. Trans Am Micros Soc 94:197–202
Coles SL, Bolick H (2007) Invasive introduced sponge Mycale grandis overgrows reef corals in Kāne‘ohe Bay, O‘ahu, Hawai‘i. Coral Reefs 26:911
Colgan M (1990) El Niño and the history of Eastern Pacific reef building. In: Glynn PW (ed) Global ecological consequences of the 1982–83 El Niño-Southern Oscillation. Elsevier, Amsterdam, pp 183–232
Collin C, Díaz MC, Norenburg J, Rocha RM, Sánchez JA, Schulze A, Schwartz M, Valdés A (2005) Photographic identification guide to some common marine invertebrates of Bocas del Toro, Panama. Carib J Sci 41:638–707
Coraltraits (2016) Coral trait databace. Available from: https://coraltraits.org. [6 June 2016]
Corredor JE, Wilkinson CR, Vicente VP, More JM, Otero E (1988) Nitrate release by Caribbean reef sponges. Limnol Oceanogr 33:114–122
Corriero G, Abbiati M, Santangelo G (1997) Sponges inhabiting a Mediterranean red coral population. Mar Ecol 18:147–155
Cortés J (1992) Los arrecifes coralinos de Golfo Dulce, Costa Rica: aspectos ecológicos. Rev Biol Trop 40:19–26
Cortés J (1993) Comparison between Caribbean and eastern Pacific coral reefs. Rev Biol Trop 41:19–21
Cortés J (1997) Biology and geology of eastern Pacific coral reefs. Coral Reefs 16:39–46
Cortés J, Reyes-Bonilla H (2017) Human influences on Eastern Tropical Pacific coral communities and coral reefs. In: Glynn PW, Manzello PD, Enochs IC (eds) Coral reefs of the Eastern Tropical Pacific. Springer, Netherlands, pp 549–563
Cortés J, Enochs IC, Sibaja-Cordero J, Hernández L, Alvarado JJ, Breedy O, Cruz-Barrazza JA, Esquivel-Garrote O, Fernández-García C, Hermosillo A, Kaiser KL, Medina-Rosas P, Morales-Ramírez A, Pacheco C, Pérez-Matus A, Reyes-Bonilla H, Riosmena-Rodríguez R, Sánchez-Noguea C, Wieters EA, Zapata FA (2017) Marine biodiversity of Eastern Tropical Pacific reefs. In: Glynn PW, Manzello PD, Enochs IC (eds) Coral reefs of the Eastern Tropical Pacific. Springer, Netherlands, pp 203–250
Cramer KL, Jackson JB, Angioletti CV, Leonard-Pingel J, Guilderson TP (2012) Anthropogenic mortality on coral reefs in Caribbean Panama predates coral disease and bleaching. Ecol Lett 15:561–567
Cruz Simó T (2002) Esponjas marinas de Canarias. Consejeria de Politica Territorial y Medio Ambiente, Canary Islands, 260 p
Cruz T, Bacallado JJ (1983) Esponjas perforantes (Porifera, Clionidae) de Tenerife, Islas Canarias. Vierea 12:37–48
Cruz-Barraza JA, Carballo JL, Bautista-Guerrero E, Nava H (2011) New species of excavating sponges (Porifera: Demospongiae) on coral reefs from the Mexican Pacific Ocean. J Mar Biol Assoc UK 91:999–1013
Cuevas E, de los Ángeles Liceaga-Correa M, Garduño-Andrade M (2007) Spatial characterization of a foraging area for immature hawksbill turtles (Eretmochelys imbricata) in Yucatan, Mexico. Amphib Rept 28:337–346
Daume S, Fromont J, Parker F, Davidson M, Murphy D, Hart A (2010) Quantifying sponge erosions in Western Australian pearl oyster shells. Aquac Res 41:e260–e267
Davies AJ, Wisshak M, Orr JC, Roberts JM (2008) Predicting suitable habitat for the cold-water coral Lophelia pertusa (Scleractinia). Deep Sea Res I Oceanogr Res Papers 55:1048–1062
Davis KA, Lentz SJ, Pineda J, Farrar JT, Starczak VR, Churchill JH (2011) Observations of the thermal environment on Red Sea platform reefs: a heat budget analysis. Coral Reefs 30:25–36
Dawydoff C (1952) Contribution à l’Étude des Invertébrés de la faune marine benthique de Indochine. Suppl Bull Biol France Belg 37:1–155
De Goeij JM, Moodley L, Houtekamer M, Carballeira NM, van Duyl FC (2008) Tracing 13C-enriched dissolved and particulate organic carbon in the bacteria- containing coral reef sponge Halisarca caerulea: evidence for DOM feeding. Limnol Oceanogr 53:1376–1386
De Goeij JM, van Oevelen D, Vermeij MJA, Osinga R, Middelburg JJ, de Goeij AF, Admiraal W (2013) Surviving in a marine desert: the sponge loop retains resources within coral reefs. Science 342:108–110
De Lamarck JBPA de Monet (1815) Sur les polypiers empâtés. Mém Mus Nat Hist Nat Paris 1:69–80, 162–168, 331–340
De Laubenfels MW (1932) The marine and fresh-water sponges of California. Proc US Natl Mus 81:1–140
De Laubenfels MW (1934) New sponges from the Puerto Rican deep. Smithsonian Misc Coll 91:1–28
De Laubenfels MW (1935) A collection of sponges from Puerto Galera, Mindoro, Philippine Islands. Philipp J Sci 56:327–337, 1 pl
De Laubenfels MW (1936a) A comparison of the shallow-water sponges near the Pacific end of the Panama Canal with those at the Caribbean end. Proc US Natl Mus 83:441–466
De Laubenfels MW (1936b) A discussion of the sponge fauna of the Dry Tortugas in particular and the West Indies in general, with material for a revision of the families and orders of the Porifera. Carnegie Inst Washington Publ 467 (Tortugas Lab Paper 30):1–225, pls 1–22
De Laubenfels MW (1939) Sponges collected on the presidential cruise of 1938. Smithsonian Misc Coll 98:1–7
De Laubenfels MW (1949) Sponges of the western Bahamas. Am Mus Novit 1431:1–25
De Laubenfels MW (1950a) The Porifera of the Bermuda Archipelago. Trans Zool Soc Lond 27:1–153
De Laubenfels MW (1950b) The Sponges of Kaneohe Bay, Oahu. Pac Sci 4:3–36
De Laubenfels MW (1951) The sponges of the Island of Hawaii. Pac Sci 5:256–271
De Laubenfels MW (1953) Sponges from the Gulf of Mexico. Bull Mar Sci Gulf Caribb 2:511–557
De Laubenfels MW (1954) The sponges of the West-Central Pacific. Oregon State Monogr Stud Zool 7:1–320
De Laubenfels MW (1956) Preliminary discussion of the sponges of Brasil. Contrib Avul Inst Oceanogr São Paulo 1:1–4
De Paula TS, Zilberberg C, Hajdu E, Lôbo-Hajdu G (2012) Morphology and molecules on opposite sides of the diversity gradient: four cryptic species of the Cliona celata (Porifera, Demospongiae) complex in South America revealed by mitochondrial and nuclear markers. Mol Phyl Evol 62:529–541
De Voogd NJ, Cleary DFR (2009) Variation in sponge composition among Singapore reefs. Raffles Bull Zool Suppl 22:59–67
De’ath G, Fabricius KE, Sweatman H, Puotinen M (2012) The 27-year decline of coral cover on the Great Barrier Reef and its causes. PNAS 109:17995–17999
De'ath G, Lough JM, Fabricius KE (2009) Declining coral calcification on the Great Barrier Reef. Science 323:116–119
DeCarlo TM, Cohen AL, Barkley HC, Cobban Q, Young C, Shamberger KE, Brainard RE, Golbuu Y (2015) Coral macrobioerosion is accelerated by ocean acidification and nutrients. Geology 43:7–10
Dendy A (1887) The Sponge-fauna of Madras. A report on a collection of sponges obtained in the neighbourhood of Madras by Edgar Thurston, Esq. Ann Mag Nat Hist 20:153–165. pls IX–XII
Dendy A (1897) Catalogue of Non-Calcareous Sponges collected by J. Bracebridge Wilson, Esq., M.A., in the neighbourhood of Port Phillip Heads. Part III. Proc R Soc Vict New Ser 9:230–259
Dendy A (1905) Report on the sponges collected by Professor Herdman, at Ceylon, in 1902. In: Herdman WA (ed), Report to the government of Ceylon on the pearl oyster fisheries of the Gulf of Manaar. Royal Soc Suppl Report 3, suppl 18:57–246, pls I–XVI
Dendy A (1916) Report on the non-calcareous sponges collected by Mr. James Hornell at Okhamandal in Kattiawar in 1905–6. Report to the Government of Baroda on the Marine Zoology of Okhamandal in Kattiawar. 2:93–146, pls I–IV
Dendy A (1922) Report on the Sigmatotetraxonida collected by H.M.S. ‘Sealark’ in the Indian Ocean. Reports of the Percy Sladen Trust Expedition to the Indian Ocean in 1905. Volume 7. Trans Linn Soc London Zool 18:1–164, pls 1–18
Dendy A, Frederick LM (1924) On a collection of sponges from the Abrolhos Islands, Western Australia. Zool J Linnean Soc London 35:477–519
Desqueyroux-Faúndez R (1981) Révision de la collection d’éponges d’Amboine (Moluques, Indonésie) constituée par Bedot et Pictet et conserve au Muséum d’histoire naturelle de Genève. Rev Suisse Zool 88:723–764
Desqueyroux-Faúndez R (1990) Spongiaires (Demospongiae) de l’Île de Pâques (Isla de Pascua). Rev Suisse Zool 97:373–409
Desqueyroux-Faúndez R, Valentine C (2002) Family Phloeodictyidae Carter, 1882. In: Hooper JNA, van Soest RWM (eds) Systema Porifera. A guide to the classification of sponges, vol 1. Kluwer Academic/Plenum Publishers, New York, pp 893–905
Desqueyroux-Faúndez R, van Soest RWM (1997) Shallow water demosponges of the Galápagos Islands. Rev Suisse Zool 104:379–467
Díaz MC (2005) Common sponges from shallow marine habitats from Bocas del Toro region, Panama. Caribb J Sci 41:465–475
Díaz MC, Rützler K (2007) Biodiversity and abundance of sponges in Caribbean mangrove: indicators of environmental quality. Smithsonian Contrib Mar Sci 38:151–172
Díaz MC, Zea S (2008) Distribución de esponjas sobre la plataforma continental de La Guajira, Caribe Colombiano. Bol Invest Mar Cost 37:27–43
Díaz MC, Alvarez B, Laughlin RA (1990) The sponge fauna on a fringing coral reef in Venezuela II: community structure. In: Rützler K (ed) New perspectives in sponge biology. Smithsonian Institution Press, Washington, pp 367–375
Díaz MC, Thacker RW, Rützler K, Piantoni C (2007) Two new haplosclerid sponges from Caribbean Panama with symbiotic filamentous cyanobacteria, and an overview of sponge-cyanobacteria associations. In: Custódio MR, Lôbo-Hajdu G, Hajdu E, Muricy G (eds) Porifera research. Biodiversity, innovation and sustainability. National Museum, Rio de Janeiro, pp 31–39
DiBattista JD, Roberts MB, Bouwmeester J, Bowen BW, Coker DJ, Lozano-Cortés DF, Howard Choat J, Gaither MR, Hobbs JP, Khalil MT, Kochzius M, Myers RF, Paulay G, Robitzch VSN, Seanz-Agudelo P, Salas E, Sinclair-Taylor TH, Toonen RJ, Westneat MW, Williams ST, Berumen ML (2016) A review of contemporary patterns of endemism for shallow water reef fauna in the Red Sea. J Biogeogr 43:423–439
Dickinson MG (1945) Sponges of the Gulf of California. Reports on the collections obtained by Alan Hancock Pacific Expeditions of Velero III off the coast of Mexico, Central America, South America, and Galapagos Islands in 1932, in 1933, in 1934, in 1935, in 1936, in 1937, in 1939, and 1940. The University of Southern California Press, Los Angeles, pp 1–55, pls 1–97
Diez ME, Vázquez N, Urteaga D, Cremonte F (2014) Species associations and environmental factors influence activity of borers on Ostrea puelchana in northern Patagonia. J Moll Stud:eyu035
Doroudi MS (1996) Infestation of pearl oysters by boring and fouling organisms in the northern Persian Gulf. Indian J Mar Sci 25:168–169
Dragnewitsch P (1906) Spongien von Singapore. Zool Jahrb 23:440–448
Duchassaing de Fonbressin P, Michelotti G (1864) Spongiaires de la mer Caraibe. Nat Verhand Holl Maatsch Wetensch Haarlem 21:1–124, pls I–XXV
Duckworth AR, Peterson BJ (2013) Effects of seawater temperature and pH on the boring rates of the sponge Cliona celata in scallop shells. Mar Biol 160:27–35
Dunn JG, Sammarco PW, LaFleur G (2012) Effects of phosphate on growth and skeletal density in the scleractinian coral Acropora muricata: a controlled experimental approach. J Exp Mar Biol Ecol 411:34–44
Dunstan P (1975) Growth and form in the reef-building coral Montastrea annularis. Mar Biol 33:101–107
Eakin CM (1992) Post-El Niño Panamanian reefs: less accretion, more erosion and damselfish protection. In: Proceedings of the 7th international coral reef symposium, vol 1, Guam, pp 387–396
Eakin CM (2001) A tale of two ENSO events: carbonate budgets and the influence of two warming disturbances and intervening variability, Uva Island, Panama. Bull Mar Sci 69:171–186
Edinger EN, Risk MJ (1997) Sponge borehole size as a relative measure of bioerosion and paleoproductivity. Lethaia 29:275–286
Edinger EN, Jompa J, Limmon GV, Widjatmoko W, Risk MJ (1998) Reef degradation and coral biodiversity in Indonesia: effects of land-based pollution, destructive fishing practices and changes over time. Mar Poll Bull 36:617–630
Edinger EN, Limmon GV, Jompa J, Widjatmoko W, Heikoop JM, Risk MJ (2000) Normal coral growth rates on dying reefs: are coral growth rates good indicators of reef health? Mar Poll Bull 40:404–425
Educypedia (2015) The educational encyclopedia. Free atlas, outline maps, globes and maps of the world. Outline map of the world – blank world map. http://educypedia.karadimov.info/library/BlankMap-World.png. [4 September 2015]
Eisapor S, Safaeian S (2013) Identification of sponges of intertidal zone in North of Hengam Island, Persian Gulf. J Mar Sci Eng 3:141–148
Eisapor S, Safaeian S, Esmaeili A, Vakili AH, Bavandi R (2012) Identification of sponges of the offshore zone in the northwest of Hengam Island, Persian Gulf. J Mar Sci Tech Res 6:79–90
Emson RH (1966) The reactions of the sponge Cliona celata to applied stimuli. Comp Biochem Physiol 18:805–827
Enochs IC, Manzello DP (2012) Species richness of motile cryptofauna across a gradient of reef framework erosion. Coral Reefs 31:653–661
Enochs IC, Manzello DP, Calton RD, Graham DM, Ruzicka R, Colella MA (2015) Ocean acidification enhances the bioerosion of a common coral reef sponge: implications for the persistence of the Florida Reef Tract. Bull Mar Sci 91:271–290
EOL Rapid Response Team (2017) Encyclopedia of life: Cassis tuberosa. http://eol.org/pages/461034/overview. [26 January 2017]
Erdman MV (2000) Destructive fishing practices in Indonesian seas. In: Sheppard C (ed) Seas at the millenium: an environmental evaluation. Pergamon, Amsterdam, pp 392–393
Erpenbeck D, van Soest RWM (2002) Family Halichondriidae Gray, 1867. In: Hooper JNA, van Soest RWM (eds) Systema Porifera. A guide to the classification of sponges, vol 1. Kluwer Academic/Plenum Publishers, New York, pp 787–815
Erpenbeck D, Voigt O, Al-Aidaroos AM, Berumen ML, Büttner G, Catania D, Guirguis AN, Paulay G, Schätzle S, Wörheide G (2016) Molecular biodiversity of Red Sea demosponges. Mar Poll Bull 105:507–514
Erwin PM, Thacker RW (2007) Incidence and identity of photosynthetic symbionts in Caribbean coral reef sponge assemblages. J Mar Biol Assoc UK 87:1683–1692
Escobar D, Zea S, Sánchez JA (2012) Phylogenetic relationships among the Caribbean members of the Cliona viridis complex (Porifera, Demospongiae, Hadromerida) using nuclear and mitochondrial DNA sequences. Mol Phyl Evol 64:271–284
Eyster LS, Stancyk SE (1981) Reproduction, growth and trophic interactions of Doriopsilla pharpa Marcus in South Carolina. Bull Mar Sci 31:72–82
Fabricius KE (2005) Effects of terrestrial runoff on the ecology of corals and coral reefs: review and synthesis. Mar Poll Bull 50:125–146
Fahmy M (2003) Water quality in the Red Sea coastal waters (Egypt): analysis of spatial and temporal variability. Chem Ecol 19:67–77
Fang JKH, Schönberg CHL (2015) Carbonate budgets of coral reefs: recent developments in excavating sponge research. Reef Encounter 30:43–46
Fang JKH, Schönberg CHL, Kline DI, Hoegh-Guldberg O, Dove S (2013a) Methods to quantify components of the excavating sponge Cliona orientalis Thiele, 1900. Mar Ecol 34:193–206
Fang JKH, Mello-Athayde MA, Schönberg CHL, Kline DI, Hoegh-Guldberg O, Dove S (2013b) Sponge biomass and bioerosion rates increase under ocean warming and acidification. Glob Change Biol 19:3581–3591
Fang JKH, Schönberg CHL, Mello-Athayde MA, Hoegh-Guldberg O, Dove S (2014) Effects of ocean warming and acidification on the energy budget of an excavating sponge. Glob Change Biol 20:1043-1m054
Fang JKH, Mason RAB, Schönberg CHL, Hoegh-Guldberg O, Dove S (2017a) Studying interactions between excavating sponges and massive corals by the use of hybrid cores. Mar Ecol 38:e12393
Fang JKH, Schönberg CHL, Hoegh-Guldberg O, Dove S (2017b) Symbiotic plasticity of Symbiodinium in a common excavating sponge. Mar Biol 164:104
Fang JKH, Schönberg CHL, Hoegh-Guldberg O, Dove S (2016) Day-night ecophysiology of the photosymbiotic bioeroding sponge Cliona orientalis Thiele, 1900. Mar Biol 163:1–12
Färber C, Titschack J, Schönberg CHL, Ehrig K, Boos K, Baum D, Illerhaus B, Asgaard U, Bromley RG, Freiwald A, Wisshak M (2016) Long-term macrobioerosion in the Mediterranean Sea assessed by micro-computed tomography. Biogeosciences 13:3461–3474
Fell PE, Parry EH, Balsamo AM (1984) The life histories of sponges in the Mystic and Thames Estuaries (Connecticut), with emphasis on larval settlement and postlarval reproduction. J Exp Mar Biol Ecol 78:127–141
Feng M, Hendon HH, Xie SP, Marshall AG, Schiller A, Kosaka Y, Caputi N, Pearce A (2015) Decadal increase in Ningaloo Niño since the late 1990s. Geophys Res Lett 42:104–112
Fernandes L, Day JO, Lewis A, Slegers S, Kerrigan B, Breen DA, Cameron D, Jago B, Hall J, Lowe D, Innes J, Tanzer J, Cahdwick V, Thompson L, Gorman K, Simmons M, Barnett B, Sampson K, De’ath G, Mapstone B, Marsh H, Possingham H, Ball I, Ward T, Doobs K, Aumend J, Slater D, Stapleton K (2005) Establishing representative no-take areas in the Great Barrier Reef: large-scale implementation of theory on marine protected areas. Conserv Biol 19:1733–1744
Ferrario F, Calcinai C, Erpenbeck D, Galli P, Wörheide G (2010) Two Pione species (Hadromerida, Clionaidae) from the Red Sea: a taxonomical challenge. Org Divers Evol 10:275–285
Fishelson L (1971) Ecology and distribution of the benthic fauna in the shallow waters of the Red Sea. Mar Biol 10:113–133
Fisher R, Radford BT, Knowlton N, Brainard RE, Michaelis FB, Caley MJ (2011) Global mismatch between research effort and conservation needs of tropical coral reefs. Conserv Lett 4:64–72
Form AU, Riebesell U (2012) Acclimation to ocean acidification during long-term CO2 exposure in the cold-water coral Lophelia pertusa. Glob Change Biol 18:843–853
Försterra G, Beuck L, Häussermann V, Freiwald A (2005) Shallow-water Desmophyllum dianthus (Scleractinia) from Chile: characteristics of the biocoenoses, the bioeroding community, heterotrophic interactions and (paleo)-bathymetric implications. In: Freiwald A, Roberts JM (eds) Cold-water corals and ecosystems. Springer, Berlin, pp 937–977
Freiwald A, Roberts JM (2005) Cold-water corals and ecosystems. Springer, Berlin, 1243 pp
Freiwald A, Wilson JB (1998) Taphonomy of modern deep, cold-temperate water coral reefs. Hist Biol 13:37–52
Fromont J (1993) Descriptions of species of the Haplosclerida (Porifera: Demospongiae) occurring in tropical waters of the Great Barrier Reef. Beagle Rec North Territory Mus Arts Sci 10:7–40
Fromont J, Sampey A (2014) Kimberley marine biota. Historical data: sponges (Porifera). Rec West Aust Mus Suppl 84:69–100
Fromont J, Craig R, Rawlinson L, Alder J (2005) Excavating sponges that are destructive to farmed pearl oysters in Western and Northern Australia. Aquac Res 36:150–162
Furby KA, Bouwmeester J, Berumen ML (2003) Susceptibility of central Red Sea corals during a major bleaching event. Coral Reefs 32:505–513
Fütterer DK (1974) Significance of the boring sponge Cliona for the origin of fine grained material of carbonate sediments. J Sed Res 44:79–84
Gallmetzer I, Haselmair A, Velimirov B (2010) Slow growth and early sexual maturity: bane and boon for the red coral Corallium rubrum. Estuar Coastal Shelf Sci 90:1–10
Galtsoff PA, Pertzoff V (1926) Some physiochemical properties of dissociated sponge cells. J Gen Physiol 10:239–255
Gammill ER (1997) Identification of coral reef sponges. Providence Marine Publishing, Tampa. 117 pp
Gammill ER, Fenner D (2005) Disease threatens Caribbean sponges: report and identification guide. http://www.reefbase.org/resource_center/publication/main.aspx?refid=24912. [29 April 2016]
Gappa JJ, Landoni N (2005) Biodiversity of Porifera in the Southwest Atlantic between 35° S and 56° S. Rev Mus Argentino Cienc Nat Nueva Ser 7:191–219
Garrabou J, Perez T, Sartoretto S, Harmelin JG (2001) Mass mortality event in red coral Corallium rubrum populations in the Provence region (France, NW Mediterranean). Mar Ecol Prog Ser 217:263–272
Garrone R (1974) Ultrastructure d’une ‘gemmule armee’ planctonique d’eponge clionidae. Arch Anat Micros Morph Exp 63:163–182
Gass SE, Roberts JM (2006) The occurrence of the cold-water coral Lophelia pertusa (Scleractinia) on oil and gas platforms in the North Sea: colony growth, recruitment and environmental controls on distribution. Mar Poll Bull 52:549–559
Gilliam DS (2012) Southeast Florida coral reef evaluation and monitoring project 2011 year 9 final report. Nova Southeastern University, Dania Beach, p 42. http://nsuworks.nova.edu/occ_facreports/72. [23 April 2016]
Glynn PW (1982) Coral communities and their modifications relative to past and prospective Central American seaways. Adv Mar Biol 19:91–132
Glynn PW (1990) Coral mortality and disturbances to coral reefs in the Tropical Eastern Pacific. In: Glynn PW (ed) Global ecological consequences of the 1982–83 El Niño-Southern oscillation. Elsevier, Amsterdam, pp 55–126
Glynn PW (1997) Bioerosion and coral reef growth: a dynamic balance. In: Birkeland C (ed) Life and death of coral reefs. Chapman and Hall, New York, pp 69–98. 536 pp
Glynn PW, Colgan MW (1992) Sporadic disturbances in fluctuating coral reef environments: El Niño and coral reef development in the eastern Pacific. Am Zool 32:707–718
Glynn PW, Maté JL, Baker AC, Calderón MO (2001) Coral bleaching and mortality in Panama and Ecuador during the 1997–1998 El Niño-Southern Oscillation event: spatial/temporal patterns and comparisons with the 1982–1983 event. Bull Mar Sci 69:79–109
Glynn PW, Mones AB, Podestá GP, Colbert A, Colgan MW (2017) El-Niño Southern oscillations: effects on Eatsrn Pacific coral reefs and associated biota. In: Glynn PW, Manzello PD, Enochs IC (eds) Coral reefs of the Eastern Tropical Pacific. Springer, Netherlands, pp 252–290
Gomez ED, Alino PM, Yap HT, Licuanan WY (1994) A review of the status of Philippine reefs. Mar Poll Bull 29:62–68
González-Gándara C, Patiño-García A, Asís-Anastasio U, Serrano A, Gómez P (2009) Lista de esponjas marinas asociadas al arrecife Tuxpan, Veracruz, México. Rev Mex Biodiv 80:1–5
González-Rivero M, Yakob L, Mumby PJ (2011) The role of sponge competition on coral reef alternative steady states. Ecol Model 222:1847–1853
González-Rivero M, Ferrari R, Schönberg CHL, Mumby PJ (2012) Impacts of macroalgal competition and parrotfish predation on the growth of a common bioeroding sponge. Mar Ecol Prog Ser 444:133–142
González-Rivero M, Ereskovsky AV, Schönberg CHL, Ferrari R, Fromont J, Mumby JP (2013) Life-history traits of a common Caribbean coral-excavating sponge, Cliona tenuis (Porifera: Hadromerida). J Nat Hist 47:2815–2834
Google Scholar (2016) Google Scholar. Stand on the shoulders of giants. http://scholar.google.com.au/schhp?hl=en&as_sdt=1,5. [26 April 2015]
Goreau T, McClanahan T, Hayes R, Strong AL (2000) Conservation of coral reefs after the 1998 global bleaching event. Conserv Biol 14:5–15
Goreau TF, Hartman WD (1963) Boring sponges as controlling factors in the formation and maintenance of coral reefs. In: Sognnaes RF (ed) Mechanisms of hard tissue destruction. Publication American Association Advance of Science, Washington 75:25–54
Gori A, Ferrier-Pagès C, Hennige SJ, Murray F, Rottier C, Wicks LC, Roberts JM (2016) Physiological response of the cold-water coral Desmophyllum dianthus to thermal stress and ocean acidification. PeerJ 4:e1606
Granados C, Camargo C, Zea S, Sánchez JA (2008) Phylogenetic relationships among zooxanthellae (Symbiodinium) associated to excavating sponges (Cliona spp.) reveal an unexpected lineage in the Caribbean. Mol Phyl Evol 49: 554–560
Grant RE (1826) Notice of a new zoophyte (Cliona celata, Gr.) from the Firth of Forth. Edinburgh New Phil J 1:78–81
GRBMPA (2003) Great Barrier Reef Marine Park Zoning Plan 2003. Great Barrier Reef Marine Park Authority, Townsville. 211 pp
Grech A, Pressey RL, Day JC (2016) Coal, cumulative impacts, and the Great Barrier Reef. Conserv Lett 9:200–207
Guida VG (1976) Sponge predation in the oyster reef community as demonstrated with Cliona celata Grant. J Exp Mar Biol Ecol 25:109–122
Guzmán HM (1988) Distribución y abundancia de organismos coralívoros en los arrecifes coralinos de la Isla del Caño, Costa Rica. Rev Biol Trop 36:191–207
Guzmán HM, Cortés J (1993) Arrecifes coralinos del Pacífico oriental tropical: revisión y perspectivas. Rev Biol Trop 41:535–557
Hadi TA, Budiyanto A, Wentao N (2016) The morphological and species diversity of sponges on coral reef ecosystems in the Lembeh Strait, Bitung. Mar Res Indones 40:61–72
Hain S, Corcoran E (2004) The status of the cold-water coral reefs of the world. In: Wilkinson CR (ed) Status of coral reefs of the world: 2004. Volume 1. Australian Institute of Marine Science, Townsville, pp 115–135
Hall KA, Hooper JNA (2016) SpongeMaps - an online community for sponge taxonomy. www.spongemaps.org. [23 April 2016]
Hallmann EF (1920) New genera of monaxonid sponges related to the genus Clathria. Proc Linn Soc New South Wales 44:767–792, pls XXXVI–XL
Halperin AA, Chaves-Fonnegra A, Gilliam DS (2016) Effects of excavating-sponge removal on coral growth. J Mar Biol Assoc UK 96:473–479
Hamner WM, Jones MS (1976) Distribution, burrowing, and growth rates of the clam Tridacna crocea on interior reef flats. Oecologia 24:207–227
Hancock A (1849) On the excavating powers of certain sponges belonging to the genus Cliona; with descriptions of several new species, and an allied generic form. Ann Mag Nat Hist 17:321–348, pls XII–XV
Hansson HG (1999) NEAT (North East Atlantic Taxa): Scandinavian marine Porifera (Spongiaria) check-list. http://www.tmbl.gu.se/libdb/taxon/neat_pdf/NEAT*Porifera.pdf. [30 April 2016]
Harper MK (2014) UU1027 Zyzzya fuliginosa (Carter, 1879). In: Hall KA, Hooper JNA (eds) SpongeMaps: an online community for taxonomy and identification of sponges. http://www.spongemaps.org. [15 January 2017]
Hartman WD (1958) Natural history of the marine sponges of southern New England. Bull Peabody Mus Nat Hist 12:1–155
Hatch WI (1980) The implication of carbonic anhydrase in the physiological mechanism of penetration of carbonate substrata by the marine burrowing sponge Cliona celata (Demospongiae). Biol Bull 159:135–147
Hechtel GJ (1965) A systematic study of the Demospongiae of Port Royal, Jamaica. Bull Peabody Mus Nat Hist 20:1–103
Hein FJ, Risk MJ (1975) Bioerosion of coral heads: inner patch reefs, Florida reef tract. Bull Mar Sci 25:133–138
Hentschel E (1909) Die Fauna Südwest-Australiens. Ergebnisse ther Hamburger südwest-australischen Forschungsreise 1905. Tetraxonida. 1. Teil. Gustav Fischer, Jena, pp 347-, pls XXII–XXIII
Hentschel E (1912) Kiesel- und Hornschwämme der Aru- und Kei-Inseln. Abh Senckenb Naturf Ges 34:293–448, pls 13–21
Hepburn LJ, Perry CT, Blanchon P (2006) Distribution of macroborers in reef rubble, Puerto Morelos, Mexican Caribbean. In: Proceedings of the 10th international coral reef symposium, Okinawa, pp 327–334
Hernández-Ballesteros LM, Elizalde-Rendón EM, Carballo JL, Carricart-Ganivet JP (2013) Sponge bioerosion on reef-building corals: dependent on the environment or on skeletal density? J Exp Mar Biol Ecol 441:23–27
Herrera-Moreno A, Betancourt L, Alcolado PM (2012) Espicies de esponjas marinas conocidas para la Isla Hispaniola. Novitates Carib 5:81–94
Highsmith RC (1981a) Coral bioerosion at Enewetak: agents and dynamics. Int Rev Ges Hydrobiol 66:335–375
Highsmith RC (1981b) Coral bioerosion: damage relative to skeletal density. Am Nat 117:193–198
Highsmith RC, Lueptow RL, Schonberg SC (1983) Growth and bioerosion of three massive corals on the Belize barrier reef. Mar Ecol Prog Ser 13:261–271
Hill M (1996) Symbiotic zooxanthellae enhance boring and growth rates of the tropical sponge Anthosigmella varians forma varians. Mar Biol 125:649–654
Hill M (1998) Spongivory on Caribbean reefs releases corals from competition with sponges. Oecologia 117:143–150
Hill M (1999) Morphological and genetic examination of phenotypic variability in the tropical sponge Anthosigmella varians. Mem Queensl Mus 44:239–247
Hill M, Wilcox T (1998) Unusual mode of symbiont repopulation after bleaching in Anthosigmella varians: acquisition of different zooxanthellae strains. Symbiosis 25:279–289
Hill M, Allenby A, Ramsby B, Schönberg CHL, Hill A (2011) Symbiodinium diversity among host clionaid sponges from Caribbean and Pacific reefs: evidence of heteroplasmy and putative host-specific symbiont lineages. Mol Phylogenet Evol 59:81–88
Hill M, Walter C, Bartels E (2016) A mass bleaching event involving clionaid sponges. Coral Reefs 35:153
Hill MS, Hill AL (2002) Morphological plasticity in the tropical sponge Anthosigmella varians: responses to predators and wave energy. Biol Bull 202:86–95
Hodgson G (1999) A global assessment of human effects on coral reefs. Mar Poll Bull 38:345–355
Hoegh-Guldberg O (2011) Coral reef ecosystems and anthropogenic climate change. Reg Environ Chang 11:215–227
Hoegh-Guldberg O, Ridgway T (2016) Coral bleaching hits Great Barrier Reef as global temperatures soar. Green Left Weekly 1090:10
Hoegh-Guldberg O, Mumby PJ, Hooten AJ, Steneck RS, Greenfield P, Gomez E, Harvell CD, Sale PF, Edwards AJ, Caldeira K, Knowlton N (2007) Coral reefs under rapid climate change and ocean acidification. Science 318:1737–1742
Hoeksema BW (2007) Delineation of the Indo-Malayan centre of maximum marine biodiversity: the coral triangle. In: Renema W (ed) Biogeography, time, and place: distributions, barriers, and islands. Springer, Dordrecht, pp 117–178
Hofman CC, Kielman M (1992) The excavating sponges of the Santa Marta area, Colombia, with description of new species. Bijdr Dierk 61:205–217
Holmes KE (1997) Eutrophication and its effect on bioeroding sponge communities. In: Proceedings of the 8th international coral reef symposium, Panama City, pp 1411–1415
Holmes KE (1997) Eutrophication and its effect on bioeroding sponge communities. Proc 8th Int Coral Reef Symp, Panama City, pp 1411–1415
Holmes KE (2000) Effects of eutrophication on bioeroding sponge communities with the description of new West Indian sponges, Cliona spp. (Porifera: Hadromerida: Clionidae). Invertebr Biol 119:125–138
Holmes KE, Edinger EN, Hariyadi H, Limmon GV, Risk MJ (2000) Bioerosion of live massive corals and branching coral rubble on Indonesian coral reefs. Mar Poll Bull 40:606–661
Hooper JN, Krasochin V (1989) Redescription of the burrowing sponge Zyzzya massalis (Dendy) from the Seychelles and Houtman-Abrolhos Islands. Beagle Rec Mus Art Galler North Territory 6:133–140
Hooper JN, Kennedy JA, Soest RWM (2000) Annotated checklist of sponges (Porifera) of the South China Sea region. Raffles Bull Zool 8:125–207
Hooper JN, Hall KA, Ekins M, Erpenbeck D, Wörheide G, Jolley-Rogers G (2013) Managing and sharing the escalating number of sponge ‘unknowns’: the SpongeMaps Project. Integr Comp Biol. doi:10.1093/icb/ict038
Hooper JNA (2002) Family Acarnidae Dendy, 1922. In: Hooper JNA, van Soest RWM (eds) Systema Porifera. A guide to the classification of sponges 1. Kluwer Academic/Plenum Publishers, New York, pp 412–431
Hooper JNA, Wiedenmayer F (1994) Porifera. In: Wells A, Houston WWK (eds) Zoological Catalogue of Australia 12. CSIRO Australia, Melbourne, 620 pp
Hoshino T (1976) Demosponges from the western coast of Kii Peninsula, Japan. Zool Mag 85:248–261
Hoshino T (1977) Demosponges from the Kii channel and its environs, western Japan. Proc Jap Soc Syst Zool 13:5–15
Hoshino T (1981) Shallow-water demosponges of western Japan, II. J Sci Hiroshima Univ 29:207–289
Hoshino T (1982) Descriptions of the dominant species of the class Demospongia dredged from the coastal area of the Izu Peninsula of sagami Bay. Mem Natn Sci Mus Tokyo 15:139–148, pls 7–8
Hoshino T (1987) A preliminary catalogue of the marine species of the class Demospongia (Porifera) from Japanese waters. Mukaishima Marine Biological Station, Faculty of Science, Hiroshima University, Hiroshima, 48 pp
Hourigan TF, Stanton FG, Motta PJ, Kelley CD, Carlson B (1989) The feeding ecology of three species of Caribbean angelfishes (family Pomacanthidae). Environ Biol Fish 24:105–116
Hudson JH (1977) Long-term bioerosion rates on a Florida reef: a new method. In: Proceedings of the 3rd international coral reef symposium, Miami, pp 491–497
Hughes TP (1994) Catastrophes, phase shifts, and large-scale degradation of a Caribbean coral reef. Science 265:1547–1551
Hume BC, Voolstra CR, Arif C, D’Angelo C, Burt JA, Eyal G, Loya Y, Wiedenmann J (2016) Ancestral genetic diversity associated with the rapid spread of stress-tolerant coral symbionts in response to Holocene climate change. PNAS 113:4416–4421
Hutchings PA (1986) Biological destruction of coral reefs. Coral Reefs 4:239–252
Hutchings PA, Peyrot-Clausade M, Osorno A (2005) Influence of land runoff on rates and agents of bioerosion of coral substrates. Mar Poll Bull 51:438–447
Immanuel T, Krishnan P, Raghunathan C (2015) An updated report on the diversity of marine sponges of the Andaman and Nicobar Islands. In: Venkataraman K, Sivaperuman C (eds) Marine faunal diversity in India. Taxonomy, ecology and conservation. Academic Press, Amsterdam, pp 3–13
Ise Y, Tekeda M, Watanabe Y (2004) Psammobiontic Clionaidae (Demospongiae: Hadromerida) in lagoons of the Ryukyu Islands, southwestern Japan. Boll Mus Isl Biol Univ Genova 68:381–389
Ise Y (2010) Floating dispersal through asexual reproduction of a psammobiontic sponge in coral reefs of the Ryukyu Islands, Southern Japan. Abstract 8th world sponge conference, Girona, suppl 1:70
Jafari MA, Seyfabadi J, Shokri MR (2016) Internal bioerosion in dead and live hard corals in intertidal zone of Hormuz Island (Persian Gulf). Mar Poll Bull 105:586–592
Jameson SC, Ammar MS, Saadalla E, Mostafa HM, Riegl B (1999) A coral damage index and its application to diving sites in the Egyptian Red Sea. Coral Reefs 18:333–339
Järnegren J, Kutti T (2014) Lophelia pertusa in Norwegian waters. What have we learned since 2008? NINA Report 1028. Norwegian Institute for Nature Research, Trondheim, 35 pp
Jennings AV (1891) On a variety of Alectona millari (Carter). Linn Soc J Zool 23:531–539, pl. 13
Jensen A, Frederiksen R (1992) The fauna associated with the bank-forming deepwater coral Lophelia pertusa (Scleractinaria) on the Faroe shelf. Sarsia 77:53–69
Jones T, Glasson J, Wood D, Fulton EA (2011) Regional planning and resilient futures: destination modelling and tourism development – the case of the Ningaloo coastal region in Western Australia. Plan Pract Res 26:393–415
Karako-Lampert S, Katcoff DJ, Achituv Y, Dubinsky Z, Stambler N (2004) Do clades of symbiotic dinoflagellates in scleractinian corals of the Gulf of Eilat (Red Sea) differ from those of other coral reefs? J Exp Mar Biol Ecol 311:301–314
Keller C (1891) Die Spongienfauna des Rothen Meeres (II. Hälfte). Z wiss Zool 52:294–368, pls XVI–XX
Kelly M (1986) Systematics and ecology of the sponges of Motupore Island, Papua New Guinea. MSc thesis, University of Auckland, Auckland, p 101, 6 apps, 15 pls. https://researchspace.auckland.ac.nz/handle/2292/5966. [27 April 2016]
Kelly M, Hooper JNA, Paul VA, Paulay GU, van Soest RWM, de Weerdt WA (2003) Taxonomic inventory of the sponges (Porifera) of the Mariana Islands. Micronesica 35:100–120
Kelly-Borges M, Bergquist PR (1988) Sponges from Matupore Island, Papua New Guinea. Indo-Malayan Zool 5:121–159
Kelly-Borges M, Vacelet J (1998) Sponges of the New Caledonian Lagoon: class Demospongiae, order Hadromerida. In: Lévi C, Laboute P, Bargibant G, Menou J-L (eds) Sponges of the New Caledonian Lagoon. Orstom Editions, Paris, pp 87–93
Kelmo F, Bell JJ, Attrill MJ (2013) Tolerance of sponge assemblages to temperature anomalies: resilience and proliferation of sponges following the 1997–1998 El-Niño Southern Oscillation. PLoS One 8:e76441
Kennedy EV, Perry CT, Halloran PR, Iglesias-Prieto R, Schönberg CHL, Wisshak M, Form AU, Carricart-Ganivet JP, Fine M, Eakin CM, Mumby PJ (2013) Avoiding coral structural collapse requires local and global action. Curr Biol 23:912–918
Kiene WE, Hutchings PA (1994) Bioerosion experiments at Lizard Island, Great Barrier Reef. Coral Reefs 13:91–98
Kieschnick O (1896) Silicispongiae von Ternate nach den Sammlungen von Herrn Prof. Dr. W. Kükenthal. Zool Anz 19:526–534
Kieschnick O (1900) Kieselschwämme von Amboina. In: Semon R (ed) Zoologische Forschungsreisen in Australien und dem Malayischen Archipel ausgesführt in den Jahren 1891–1893. Denkschr Med Nat Ges 8. Gustav Fischer, Jena, pp 547–582
Kirkpatrick R (1900a) Description of sponges from Funafuti. Ann Mag Nat Hist (7)6:345–362, pls XIII–XV
Kirkpatrick R (1900b) On the sponges of Christmas Island. Proc Zool Soc London 1900:127–141, pls XII–XIII
Kiruba-Sankar R, Chadha NK, Dam-Roy S, Sawant PB, Saharan N, Krishnan P (2016) Marine sponges as biological indicator of oligotrophic Andaman waters. Indian J Geo Mar Sci 45:338–341
Klein R, Mokady O, Loya Y (1991) Bioerosion in ancient and contemporary corals of the genus Porites: patterns and palaeoenvironmental implications. Mar Ecol Prog Ser 77:245–251
Kobluk DR, van Soest RWM (1989) Cavity-dwelling sponges in a southern Caribbean coral reef and their paleontological implications. Bull Mar Sci 44:1207–1035
Kotb M, Abdulaziz M, Al-Agwan Z, Al-Shaikh K, Al-Yami H, Banajah A, DeVantier L, Eisinger M, Eltayeb M, Hassan M, Heiss, G, Howe S, Kemp J, Klaus R, Krupp F, Mohamed N, Rouphael A, Turner J, Zajonz U (2004) Status of coral reefs in the Red Sea and Gulf of Aden in 2004. In: Wilkinson CR (ed) Status of coral reefs of the world: 2004. Volume 1. Australian Institute of Marine Science, Townsville, pp 137–154
Kumar A (1925) Report on some tetraxonid sponges in the collection of the Indian Museum. Rec Indian Mus 27:211–229
Kumar M, Jogani S (2014) Primary characterization of sponge associated bacteria of marine sponges-Halichondria glabrata, Cliona lobata, Spirastrella pachyspira and their antimicrobial properties. J Microbiol Biotechnol Food Sci 4:117–121
Kumar MS, Shah B (2014) Comparative structural morphometry and elemental composition of three marine sponges from Western Coast of India. Microsc Res Tech 77:296–304
Lafratta A, Fromont J, Speare P, Schönberg CHL (2016) Coral bleaching in turbid waters of North-Western Australia. Mar Freshw Res 68:65–75
Lang JC, Marks KW, Kramer PA, Richards Kramer P, Ginsburg RN (2010) Atlantic and gulf rapid reef assessment protocols, Ver. 5.4. http://www.agrra.org/. [23 April 2016]
Leal CV, de Paula TS, Lôbo-Hajdu G, Schönberg CHL, Esteves EL (2016) Morphological and molecular systematics of the ‘Cliona viridis complex’ from south-eastern Brazil. J Mar Biol Assoc UK 96:313–322
Lehnert H (1993) Die Schwämme von Cozumel. Bestandsaufnahme, kritischer Vergleich taxonomischer Merkmale und Beschreibung einer neuen Art. Acta Biol Benrodis 5:35–127
Lehnert H, van Soest RWM (1998) Shallow water sponges of Jamaica. Beaufortia 48:71–103
Lehnert H, van Soest RWM (1999) More north Jamaican deep fore-reef sponges. Beaufortia 49:141–169
León YM, Bjorndal KA (2002) Selective feeding in the hawksbill turtle, an important predator in coral reef ecosystems. Mar Ecol Prog Ser 245:249–258
León-Pech MG, Cruz-Barraza JA, Carballo JL, Calderon-Aguilera LE, Rocha-Olivares A (2015) Pervasive genetic structure at different geographic scales in the coral-excavating sponge Cliona vermifera (Hancock, 1867) in the Mexican Pacific. Coral Reefs 34:887–897
Lescinsky HL, Edinger E, Risk MJ (2002) Mollusc shell encrustation and bioerosion rates in a modern epeiric sea: taphonomy experiments in the Java Sea, Indonesia. Palaios 17:171–191
Lévi C (1956) Spongiaires des côtes de Madagascar. Mém Inst Sci Madagascar A 10:1–23, figs 1–14
Lévi C (1958) Résultats scientifiques des Campagnes de la ‘Calypso’.Campagne 1951–1952 en Mer Rouge (suite). 11. Spongiaires de Mer Rouge recueillis par la ‘Calypso’ (1951–1952). Ann Inst Océanogr 34:3–46
Lévi C (1959a) Campagnes de la ‘Calypso’: Golfe de Guinée. Spongiaires. Ann Inst Océanogr 37:115–140, pls 5–6
Lévi C (1959b) Spongiaires des Iles Philippines, principalement récoltées au voisinage de Zamboanga. Philipp J Sci 88:509–533
Lévi C (1961) Résultats scientifiques des Campagnes de la ‘Calypso’. Campagne 1954 dans l’Océan Indien (suite). 2. Les spongiaires de l’Ile Aldabra. Ann Inst Océanogr 39:1–32, pls 1–2
Lévi C (1965a) Spongiaires récoltés par l’expédition israélienne dans le sud de la Mer Rouge en 1962. Israel South Red Sea Expedition1962, Report 13. Bull Sea Fish Res Stat Israel 39:3–27
Lévi C (1965b) Spongiaires des côtes de Madagascar. Mém Inst Sci Madagascar A 10:1–23
Li TH (2013) Preliminary survey on the biodiversity of marine sponges (Porifera: Demonspongiae) in the southern water off the Penghu Archipelago. MSc thesis, National Sun Yat-sen University, Kaohsiung, p 152. http://etd.lib.nsysu.edu.tw/ETD-db/ETDsearch/view_etd?URN=etd-0201113-151352. [24 January 2017]
Lim SC, de Voogd NJ, Tan KS (2008) A guide to sponges of Singapore. Science Centre Singapore, Singapore, 173 p
Lim SC, de Voogd NJ, Tan KS (2009) Fouling sponges (Porifera) on navigation buoys from Singapore waters. Raffles Bull Zool 22:41–58
Lim SC, de Voogd NJ, Tan KS (2012a) Biodiversity of shallow-water sponges (Porifera) in Singapore and description of a new species of Forcepia (Poecilosclerida: Coelosphaeridae). Contrib Zool 81:55–71
Lim SC, Tun K, Goh E (2012b) Rediscovery of the Neptune’s cup sponge in Singapore: Cliona or Poterion? Contrib Mar Sci Natl Univ Singapore 2012:49–56
Lim SC, Putchakarn S, Thai MQ, Wang D, Huang YM (2016) Inventory of sponge fauna from the Singapore Strait to Taiwan Strait along the western coastline of the South China Sea. Raffles Bull Zool Suppl 34:104–129
Lindberg B, Mienert J (2005) Postglacial carbonate production by cold-water corals on the Norwegian Shelf and their role in the global carbonate budget. Geology 33:537–540
Lindgren NG (1898) Beitrag zur Kenntniss der Spongienfauna des Malayischen Archipels und der chinesischen Meere. Zool Jahrb Jena, 11:283–378, pls 17–20
Lirman D, Glynn PW, Baker AC, Leyte Morales GE (2001) Combined effects of three sequential storms on the Huatulco coral reef tract, Mexico. Bull Mar Sci 69:267–278
Little FJ Jr (1963) The sponge fauna of the St. George’s Sound, Apalache Bay, and Panama City Regions of the Florida Gulf Coast. Tulane Stud Zool 11:31–71
Little FJ (1968) An experimental or tentative revision of the genus Cliona utilizing the principles of numerical taxonomy. Proc Pa Acad Sci 42:38–48
Longakit MBA, Sotto FB, Kelly M (2005) The shallow water marine sponges (Porifera) of Cebu, Philippines. Sci Diliman 17:52–74
Longo C, Mastrototaro F, Corriero G (2005) Sponge fauna associated with a Mediterranean deep-sea coral bank. J Mar Biol Assoc UK 85:1341–1352
López-Victoria M, Zea S (2004) Storm-mediated coral colonization by an excavating Caribbean sponge. Clim Res 26:251–256
López-Victoria M, Zea S (2005) Current trends of space occupation by encrusting excavating sponges on Colombian coral reefs. Mar Ecol 26:33–41
López-Victoria M, Zea S, Weil E (2006) Competition for space between encrusting excavating Caribbean sponges and other coral reef organisms. Mar Ecol Prog Ser 312:113–121
López-Victoria MA, Zea SV, Weil ER (2004) New aspects on the biology of the encrusting excavating sponges Cliona aprica, Cliona caribbaea and Cliona sp. Boll Mus Ist Biol Univ Genova 68:425–432
Low MEY (2012) The date of publication of Cliona patera (Hardwicke), the ‘sponge plant from the shores of Singapore’ (Porifera: Hadromerida: Clionaidae). Nat Singapore 5:223–227
Loya Y, Lubinevsky H, Rosenfeld M, Kramarsky-Winter E (2004) Nutrient enrichment caused by in situ fish farms at Eilat, Red Sea is detrimental to coral reproduction. Mar Poll Bull 49:344–453
Lucas SG (1986) Proper syntax when using aff. and cf. in taxonomic statements. J Vertebr Paleont 6:202
Luke SR (1998) Catalog of the benthic invertebrate collections of the Scripps Institution of Oceanography. Porifera. SIO Reference Series 98–06. Scripps Institution of Oceanography, San Diego, 31 pp
Lunden JJ, McNicholl CG, Sears CR, Morrison CL, Cordes EE (2014) Acute survivorship of the deep-sea coral Lophelia pertusa from the Gulf of Mexico under acidification, warming, and deoxygenation. Front Mar Sci 1:78/1–78/12
Lynch TC, Phlips EJ (2000) Filtration of the bloom-forming cyanobacteria Synechococcus by three sponge species from Florida Bay, USA. Bull Mar Sci 67:923–936
Macdonald IA, Perry CT (2003) Biological degradation of coral framework in a turbid lagoon environment, Discovery Bay, North Jamaica. Coral Reefs 22:523–535
MacGeachy JK (1977) Factors controlling sponge boring in Barbados reef corals. In: Proceedings of the 3rd international coral reef symposium, vol 2, Miami, pp 477–483
MacGeachy JK, Stearn CW (1976) Boring by macro-organisms in the coral Montastrea annularis on Barbados Reefs. Int Rev ges Hydrobiol Hydrogr 61:715–745
Madin EMP (2015) Halt reef destruction in South China Sea. Nature 524:291
Maier C (1997) Distribution and abundance of internal bioeroders in coral reefs. A field survey in the northern Red Sea. MSc thesis at the Bremen University, Bremen, 94 pp
Makowski C, Keyes P (2011) Using the benthic ecological assessment for marginal reefs (BEAMR) method to quantify nearshore reef conditions in the Southeast Gulf of Mexico. J Coast Res 27:428–440
Maldonado M (1992) Demosponges of the red coral bottoms from the Alboran Sea. J Nat Hist 26:1131–1161
Mallela J, Perry CT (2007) Calcium carbonate budgets for two coral reefs affected by different terrestrial runoff regimes, Rio Bueno, Jamaica. Coral Reefs 26:129–145
Mallela JA (2004) Coral reef communities and carbonate production in a fluvially-influenced embayment, Rio Bueno, Jamaica. PhD thesis, Manchester Metropolitan University, Manchester, 222 pp
Manasrah R, Raheed M, Badran MI (2006) Relationships between water temperature, nutrients and dissolved oxygen in the northern Gulf of Aqaba, Red Sea. Oceanologia 48:237–253
Manzello DP (2010) Ocean acidification hotspots: spatiotemporal dynamics of the seawater CO2 system of eastern Pacific coral reefs. Limnol Oceanogr 55:239–248
Manzello DP, Kleypas JA, Budd DA, Eakin CM, Glynn PW, Langdon C (2008) Poorly cemented coral reefs of the eastern tropical Pacific: possible insights into reef development in a high-CO2 world. PNAS 105:10450–10455
Manzello DP, Eakin CM, Glynn PW (2017) Effects of global warming and ocean acidification on carbonate budgets of Eastern Pacific coral reefs. In: Glynn PW, Manzello PD, Enochs IC (eds) Coral reefs of the Eastern Tropical Pacific. Springer, Netherlands, pp 517–533
Mariani S, Uriz MJ (2001) Copepods of the genus Asterocheres (Copepoda: Siphonostomatoida) feeding on sponges: behavioral and ecological traits. Invertebr Biol 120:269–277
Mariani S, Uriz MJ, Turon X (2000) Larval bloom of the oviparous sponge Cliona viridis: coupling of larval abundance and adult distribution. Mar Biol 137:783–790
Mariani S, Piscitelli MP, Uriz MJ (2001) Temporal and spatial co-occurrence in spawning and larval release of Cliona viridis (Porifera: Hadromerida). J Mar Biol Assoc UK 81:565–567
Mariani S, Uriz MJ, Turon X (2005) The dynamics of sponge larvae assemblages from northwestern Mediterranean nearshore bottoms. J Plankton Res 27:249–262
Mariani S, Uriz MJ, Turon X, Alcoverro T (2006) Dispersal strategies in sponge larvae: integrating the life history of larvae and the hydrologic component. Oecologia 149:174–184
Márquez JC, Zea S (2012) Parrotfish mediation in coral mortality and bioerosion by the encrusting, excavating sponge Cliona tenuis. Mar Ecol 33:417–426
Márquez JC, Zea S, López-Victoria M (2006) Is competition for space between the encrusting excavating sponge Cliona tenuis and corals influenced by higher-than-normal temperatures? Bol Invest Mar Cost 35:256–265
Martin D (1996) A new species of Polydora (Polychaeta, Spionidae) associated with the excavating sponge Cliona viridis (Porifera, Hadromerida) in the North Western Mediterranean sea. Ophelia 45:159–174
Marulanda-Gómez Á, López-Victoria M, Zea S (2017) Current status of coral takeover by an encrusting excavating sponge in a Caribbean reef. Mar Ecol 38:e12379
Massaro AJ, Weisz JB, Hill MS, Webster NS (2012) Behavioral and morphological changes caused by thermal stress in the Great Barrier Reef sponge Rhopaloeides odorabile. J Exp Mar Biol Ecol 416-417:55–60
Mastrototaro F, d’Onghia G, Corriero G, Matarrese A, Maiorano P, Panetta P, Gherardi M, Longo C, Rosso A, Sciuto F, Sanfilippo R (2010) Biodiversity of the white coral bank off Cape Santa Maria di Leuca (Mediterranean Sea): an update. Deep Sea Res II 57:412–430
McCoy SJ (2013) Morphology of the crustose coralline alga Pseudolithophyllum muricatum (Corallinales, Rhodophyta) responds to 30 years of ocean acidification in the northeast Pacific. J Phycol 49:830–837
McKenna SA (1997) Interactions between the boring sponge Cliona lampa and two hermatypic corals from Bermuda. In: Proceedings of the 8th international coral reef symposium, vol 2, Panama City, pp 1369–1374
McKenna SA, Ritter J (1999) Cliona lampa and disturbance on the coral reefs of Castle Harbour, Bermuda. Mem Queensl Mus 44:360
McMurray SE, Finelli CM, Pawlik JR (2015) Population dynamics of giant barrel sponges on Florida coral reefs. J Exp Mar Biol Ecol 473:73–80
Megina C, Carballo JL, Cervera JL, García-Gómez JC (2002) The diet of Platydoris argo (Gastropoda: Nudibranchia) and the dietary specialization of sponge eating dorids. J Molluscan Stud 68:173–179
Melone N (1965) I poriferi associati a Corallium rubrum (L.) della Sardegna. Ann Mus Civ Storia Nat Giacomo Doria 75:344–358
Miller AN, Strychar KB, Shirley TC, Rützler K (2010) Effects of heat and salinity stress on the sponge Cliona celata. Int J Biol 2:3–16
Miller I, Sweatman H (2004) Status of coral reefs in Australia and Papua New Guinea in 2004. In: Wilkinson CR (ed) Status of coral reefs of the world: 2004, vol 1. Australian Institute of Marine Science, Townsville, pp 303–335
Millero FJ (2007) The marine inorganic carbon cycle. Chem Rev 107:308–341
Moore Jr CH, Shedd WW (1977) Effective rates of sponge bioerosion as a function of carbonate production. In: Proceedings of the 3rd international coral reef symposium, Miami, pp 499–505
Moraes FC (2011) Esponjas das Ilhas Oceânicas Brasileiras. Museu Nacional, Série Livros 44, Rio de Janeiro, 252 pp
Morgan K (2014) A calcium carbonate budget of a Maldivian reef platform. PhD thesis, University of Auckland, 204 pp, 6 appendices
Morgan KM, Kench PS (2012) Skeletal extension and calcification of reef-building corals in the central Indian Ocean. Mar Environ Res 81:78–82
Morrow C, Cárdenas P (2015) Proposal for a revised classification of the Demospongiae (Porifera). Front Zool 12:1–27
Morton B (1996) Protecting Hong Kong’s marine biodiversity: present proposals, future challenges. Environ Conserv 23:55–65
Mueller B, de Goeij JM, Vermeij MJ, Mulders Y, van der Ent E, Ribes M, van Duyl FC (2014) Natural diet of coral-excavating sponges consists mainly of dissolved organic carbon (DOC). PLoS One 9:e90152
Mumby PJ, Dahlgren CP, Harborne AR, Kappel CV, Micheli F, Brumbaugh DR, Holmes KE, Mendes JM, Broad K, Sanchirico JN, Buch K, Box S, Stoffle RW, Gill AB (2006a) Fishing, trophic cascades, and the process of grazing on coral reefs. Science 311:98–101
Mumby PJ, Hedley JD, Zychaluk K, Harborne AR, Blackwell PG (2006b) Revisiting the catastrophic die-off of the urchin Diadema antillarum on Caribbean coral reefs: fresh insights on resilience from a simulation model. Ecol Model 196:131–148
Muricy G (1991) Structure des peuplements de spongiaires autour de l'égout de Cortiou (Marseille, France). Vie Milieu 41:205–221
Muricy G, Hajdu E (2006) Porifera Brasilis: guia de identificação das esponjas marinhas mais comuns do sudeste do Brasil. Museu Nacional Série Livros 17, Rio de Janeiro, 214 pp
Muricy G, Moraes FC (1998) Marine sponges of Pernambuco state, NE Brazil. Rev Bras Oceanogr 46:213–217
Muricy G, Esteves EL, Moraes FC, Santos JP, da Silva SM, Klautau M, Lanna E (2008) Biodiversidade marinha da Bacia Potiguar. Museu Nacional, Série Livros 29, Rio de Janeiro, 156 pp
Muricy G, Lopes DA, Hajdu E Carvalho MS, Moraes FC, Klautau M, Menegola C, Pinheiro U (2011) Catalogue of Brazilian Porifera. Museu Nacional, Série Livros 46, Rio de Janeiro, 300 pp
Muricy G, Esteves EL, Monteiro LC, Rodrigues BR, Albano RM (2015) A new species of Haliclona (Demospongiae: Haplosclerida: Chalinidae) from southeastern Brazil and the first record of Haliclona vansoesti from the Brazilian coast. Zootaxa 3925:536–550
Murphy GN, Perry CT, Chin P, McCoy C (2016) New approaches to quantifying bioerosion by endolithic sponge populations: applications to the coral reefs of Grand Cayman. Coral Reefs 35:1109–1121
Nakano Y (2004) Global environmental change and coral bleaching. In: Tsuchiya M, Nadaoka K, Kayanne H, Yamano H (eds) Coral Reefs of Japan. Ministry of the environment and Japanese Coral Reef Society, Tokyo, pp 42–48
Namboothri N, Fernando SA (2012) Coral-boring fauna of the Great Nicobar Island. In: Venkataraman K, Raghunathan C, Sivaperuman C (eds) Ecology of faunal communities on the Andaman and Nicobar Islands. Springer, Berlin, pp 59–70
Nardo GD (1840) Sopra un nuovo genere di spongiali silicei intitolato Vioa il quale vive nell’interno delle pietre e de gusci marini perforandoli in mille guise. Medaglie d’Oro, Venice, pp 1–8
Nava H, Carballo JL (2008) Chemical and mechanical bioerosion of boring sponges from Mexican Pacific coral reefs. J Exp Biol 211:2827–2831
Nava H, Carballo JL (2013) Environmental factors shaping boring sponge assemblages at Mexican Pacific coral reefs. Mar Ecol 34:269–279
Nava H, Carballo JL (2016) Assessment of the effectiveness of natural coral fragmentation as a dispersal mechanism for coral reef boring sponges. Mar Ecol 37:1008–1018
Nazemi M, Gilkolai FR, Lakzaei F, Pishvarzad F, Ahmadzadeh O (2015) First record on the distribution and abundance of three sponge species from Hormoz Island, Persian Gulf – Iran. Biol Forum Int J 7:72–78
Neumann AC (1966) Observations on coastal erosion in Bermuda and measurements of the boring rate of the sponge Cliona lampa. Limnol Oceanogr 11:92–108
Nichols SA (2005) An evaluation of support for order-level monophyly and interrelationships within the class Demospongiae using partial data from the large subunit rDNA and cytochrome oxidase subunit I. Mol Phyl Evol 34:81–96
Nicol WL, Reisman HM (1976) Ecology of the boring sponge Cliona celata at Gardiner’s Island, New York. Chesap Sci 17:1–7
NOAA Oceanservice (2014) Map of major stony coral reefs of the world. http://oceanservice.noaa.gov/education/kits/corals/media/supp_coral05a.html. [16 January 2017]
Odum HT, Odum EP (1955) Trophic structure and productivity of a windward coral reef community on Eniwetok Atoll. Ecol Monogr 25:291–320
Old MC (1941) The taxonomy and distribution of the boring sponges (Clionidae) along the Atlantic coast of North America. Chesapeake Biol Lab Publ 44:1–30
Olson JB, Thacker RW, Gochfeld DJ (2014) Molecular community profiling reveals impacts of time, space, and disease status on the bacterial community associated with the Caribbean sponge Aplysina cauliformis. FEMS Microbiol Ecol 87:268–279
Omori M (2011) Degradation and restoration of coral reefs: experience in Okinawa, Japan. Mar Biol Res 7:3–12
Orejas C, Gori A, Lo Iacono C, Puig P, Gili JM, Dale MRT (2009) Cold-water corals in the Cap de Creus canyon, northwestern Mediterranean: spatial distribution, density and anthropogenic impact. Mar Ecol Prog Ser 397:37–51
Orejas C, Ferrier-Pagès C, Reynaud S, Tsounis G, Allemand D, Gili JM (2011) Experimental comparison of skeletal growth rates in the cold-water coral Madrepora oculata Linnaeus, 1758 and three tropical scleractinian corals. J Exp Mar Biol Ecol 405:1–5
Osorno A, Peyrot-Clausade M, Hutchings PA (2005) Patterns and rates of erosion in dead Porites across the Great Barrier Reef (Australia) after 2 years and 4 years of exposure. Coral Reefs 24:292–303
Otter GW (1937) Rock-destroying organisms in relation to coral reefs. Sci Rep Great Barrier Reef Exped 1:323–352
Pacheco Solano C (2012) Estudio taxonómico de las esponjas perforadoras (Porifera, Demospongiae) de arrecifes de coral del Pacífico de Costa Rica. Licentiate thesis, University of Costa Rica, San José, 73 pp
Pacheco Solano C (2015) Taxonomía des esponjas perforadoras (Demospongiae, Porifera) asociadas a arrecifes coralinos del Pacífico oriental tropical Centroamericano y filogeografía de Cliona mucronata. MSc thesis, Universidad Autónoma de México, Sinaloa, 121 pp
Padovan A, Munksgaard N, Alvarez B, McGuinness K, Parry D, Gibb K (2012) Trace metal concentrations in the tropical sponge Spheciospongia vagabunda at a sewage outfall: synchrotron X-ray imaging reveals the micron-scale distribution of accumulated metals. Hydrobiologia 687:275–288
Pang RK (1973) The systematics of some Jamaican excavating sponges (Porifera). Postilla 161:1–75
Pansini M, Sará M (1999) Taxonomical and biogeographical notes on the sponges of the Strait of Magellan. Sci Mar 63(Suppl 1):203–208
Pari N, Peyrot-Clausade M, Hutchings PA (2002) Bioerosion of experimental substrates on high islands and atoll lagoons (French Polynesia) during 5 years of exposure. J Exp Mar Biol Ecol 276:109–127
Pattanayak JG (2006) Marine sponges of Andaman and Nicobar Islands, India. Rec Zool Survey India Occas Paper 255:1–152, 12 pls
Pattanayak JG (2009) Catalogue of extant Porifera type specimens in the Zoological Survey of India. Zool Surv India Occas Paper 307:1–79
Pawlik JR (1983) A sponge-eating worm from Bermuda: Branchiosyllis oculata (Polychaeta, Syllidae). PSZNI Mar Ecol 4:65–79
Pawlik JR (2011) The chemical ecology of sponges on Caribbean reefs: natural products shape natural systems. Bioscience 61:888–898
Pérez TH, Garrabou J, Sartoretto S, Harmelin JG, Francour P, Vacelet J (2000) Mortalité massive d’invertébrés marins: un événement sans précédent en Méditerranée nord-occidentale. C R Acad Sci III Sci Vie 323:853–865
Pérez TH, Vacelet JE, Rebouillon PI (2004) In situ comparative study of several Mediterranean sponges as potential biomonitors of heavy metals. Boll Mus Ist Biol Univ Genova 68:517–525
Perry CT (1998) Macroborers within coral framework at Discovery Bay, north Jamaica: species distribution and abundance, and effects on coral preservation. Coral Reefs 17:277–287
Perry CT, Harborne AR (2016) Bioerosion on modern reefs: impacts and responses under changing ecological and environmental conditions. In: Hubbard DK, Rogers CS, Lipps JH, Stanley Jr JD (eds) Coral Reefs at the crossroads. Springer, Netherlands, pp 69–101
Perry CT, Spencer T, Kench PS (2008) Carbonate budgets and reef production states: a geomorphic perspective on the ecological phase-shift concept. Coral Reefs 27:853–866
Perry CT, Edinger EN, Kench PS, Murphy GN, Smithers SG, Steneck RS, Mumby PJ (2012) Estimating rates of biologically driven coral reef framework production and erosion: a new census-based carbonate budget methodology and applications to the reefs of Bonaire. Coral Reefs 31:853–868
Pica D, Bertolino M, Calcinai B, Puce S, Bavestrello G (2012) Boring and cryptic sponges in stylasterids. Ital J Zool 79:266–272
Pineda MC, Duckworth A, Webster N (2016a) Appearance matters: sedimentation effects on different sponge morphologies. J Mar Biol Assoc UK 96:481–492
Pineda MC, Strehlow B, Duckworth A, Doyle J, Jones R, Webster NS (2016b) Effects of light attenuation on the sponge holobiont-implications for dredging management. Sci Rep 6:39038
Pineda MC, Strehlow B, Kamp J, Duckworth A, Jones R, Webster NS (2017a) Effects of combined dredging-related stressors on sponges: a laboratory approach using realistic scenarios. Sci Rep 7:5155
Pineda MC, Strehlow B, Sternel M, Duckworth A, den Haan J, Jones R, Webster NS (2017b) Effects of sediment smothering on the sponge holobiont with implications for dredging management. Sci Rep 7:5156
Pineda MC, Strehlow B, Sternel M, Duckworth A, Jones R, Webster NS (2017c) Effects of suspended sediments on the sponge holobiont with implications for dredging management. Sci Rep 7:4925
Piscitelli MP, Corriero G, Gaino E, Uriz MJ (2011) Reproductive cycles of the sympatric excavating sponges Cliona celata and Cliona viridis in the Mediterranean Sea. Invertebr Biol 130:1–10
Pomponi SA (1979) Cytochemical studies of acid phosphatase in etching cells of boring sponges. J Mar Biol Ass UK 59:785–789
Pomponi SA (1980) Cytological mechanisms of calcium carbonate excavation by boring sponges. Int Rev Cytol 65:301–319
Pomponi SA, Meritt DW (1990) Distribution and life history of the boring sponge Cliona truitti in the Upper Chesapeake Bay. In: Rützler K (ed) New perspectives in sponge biology. Smithsonian Institution Press, Washington, pp 384–390
Ponti M, Fava F, Abbiati M (2011) Spatial-temporal variability of epibenthic assemblages on subtidal biogenic reefs in the northern Adriatic Sea. Mar Biol 158:1447–1459
Powell A, Jones T, Smith DJ, Jompa J, Bell JJ (2015) Spongivory in the Wakatobi Marine National Park, Southeast Sulawesi, Indonesia. Pac Sci 69:487–508
Priori C, Mastascusa V, Erra F, Angiolillo M, Canese S, Santangelo G (2013) Demography of deep-dwelling red coral populations: age and reproductive structure of a highly valued marine species. Estuar Coast Shelf Sci 118:43–49
Pulitzer-Finali G (1982) Some new or little-known sponges from the Great Barrier Reef of Australia. Boll Mus Inst Biol Univ Genova 48-49:87–141
Pulitzer-Finali G (1986) A collection of West Indian Demospongiae (Porifera). In appendix, a list of the Demospongiae hitherto recorded from the West Indies. Ann Mus Civ Storia Nat Giacomo Doria 86:65–216
Pulitzer-Finali G (1993) A collection of marine sponges from East Africa. Ann Mus Civ Storia Nat Giacomo Doria 89:247–350
Putchakarn S (2007) Species diversity of marine sponges dwelling in coral reefs in Had Khanom-Mo Ko Thale Tai National Park, Nakhon Si Thammarat Province, Thailand. J Mar Biol Assoc UK 87:1635–1642
Putchakarn S (2011) Species diversity of marine sponges along Chanthaburi and Trat Provinces, the eastern coast of the Gulf of Thailand. Publ Seto Mar Biol Lab 41:17–23
Radford B, Ridgway T (2011) The Ningaloo Atlas. Ningaloo Coast world heritage status. http://ningaloo-atlas.org.au/node/200. [23 April 2016]
Raghunathan C (2015) Diversity of reef associated macrofauna of Rutland Island, Andaman and Nicobar Islands. Rec Zool Surv India Occas Paper 370:1–52
Ramsby BD, Hoogenboom MO, Whalan S, Webster NS, Thompson A (2017) A decadal analysis of bioeroding sponge cover on the inshore Great Barrier Reef. Sci Rep 7:2706
Randall JE, Hartman WD (1968) Sponge-feeding fishes of the West Indies. Mar Biol 1:216–225
Reaka-Kudla ML, Feingold JS, Glynn W (1996) Experimental studies of rapid bioerosion of coral reefs in the Galapagos Islands. Coral Reefs 15:101–107
Reimer JD, Mizuyama M, Nakano M, Fujii T, Hirose E (2011) Current status of the distribution of the coral-encrusting cyanobacteriosponge Terpios hoshinota in southern Japan. Galaxea 13:35–44
Reis MAC, Leão ZMAN (2000) Bioerosion rate of the sponge Cliona celata (Grant 1826) from reefs in turbid waters, north Bahía, Brazil. In: Proceedings of the 9th international coral reef symposium, vol 1, Bali, pp 273–278
Ridley SO (1884) Spongiida. Report on the coological collections made in the Indo-Pacific Ocean during the Voyage of H.M.S. ‘Alert’, 1881–2. British Museum of Natural History, London, pp 366–482, pls 39–43; 582–630, pls 53–54
Riegl B, Luke KE (1998) Ecological parameters of dynamited reefs in the northern Red Sea and their relevance to reef rehabilitation. Mar Poll Bull 37:488–498
Riegl B, Piller WE (1999) Coral frameworks revisited–reefs and coral carpets in the northern Red Sea. Coral Reefs 18:241–253
Riegl BM, Bruckner AW, Rowlands GP, Purkis SJ, Renaud P (2012) Red Sea coral reef trajectories over 2 decades suggest increasing community homogenization and decline in coral size. PLoS One 7:e38396
Riesgo A, Peterson K, Richardson C, Heist T, Strehlow B, McCauley M, Cotman C, Hill M, Hill A (2014) Transcriptomic analysis of differential host gene expression upon uptake of symbionts: a case study with Symbiodinium and the major bioeroding sponge Cliona varians. BMC Genomics 15:376
Risk MJ, Sammarco PW (1982) Bioerosion of corals and the influence of damselfish territoriality: a preliminary study. Oecologia 52:376–380
Risk MJ, Sammarco PW (1991) Cross-shelf trends in skeletal density of the massive coral Porites lobata from the Great Barrier Reef. Mar Ecol Prog Ser 69:196–200
Risk MJ, Sammarco PW, Edinger EN (1995) Bioerosion in Acropora across the continental shelf of the Great Barrier Reef. Coral Reefs 14:79–86
Risk MJ, Heikoop JM, Edinger EN, Erdmann MV (2001) The assessment ‘toolbox’: community-based reef evaluation methods coupled with geochemical techniques to identify sources of stress. Bull Mar Sci 69:443–458
Roberts CM, McClean CJ, Veron JE, Hawkins JP, Allen GR, McAllister DE, Mittermeier CG, Schueler FW, Spalding M, Wells F, Vynne C (2002) Marine biodiversity hotspots and conservation priorities for tropical reefs. Science 295:1280–1284
Roberts JM, Cairns SD (2014) Cold-water corals in a changing ocean. Curr Opin Environ Sustain 7:118–216
Roberts JM, Wheeler AJ, Freiwald A, Cairns SD (2009) Cold-water corals: the biology and geology of deep-sea coral habitats. Cambridge University Press, Cambridge. 334 pp
Rogers AD (1999) The biology of Lophelia pertusa (Linnaeus, 1758) and other deep-water reef-forming corals and impacts from human activities. Int Rev Hydrobiol 84:315–406
Romero MA, Villamizar E, Malaver N (2013) Estructura de la comunidad de esponjas (Porifera) en tres arrecifes del Parque Nacional Morrocoy, Venezuela y su relación con algunas variables ambientales. Rev Biol Trop 61:1229–1241
Rose CS, Risk MJ (1985) Increase in Cliona delitrix infestation of Montastrea cavernosa heads on the organically polluted portion of the Grand Cayman fringing reef. PSZN Mar Ecol 6:345–363
Rosell D (1993) Effects of reproduction in Cliona viridis (Hadromerida) on zooxanthellae. Sci Mar 57:405–413
Rosell D (1994) Morphological and ecological relationships of two clionid sponges. Ophelia 40:37–50
Rosell D, Uriz MJ (1991) Cliona viridis (Schmidt, 1862) and Cliona nigricans (Schmidt, 1862) (Porifera, Hadromerida): evidence which shows they are the same species. Ophelia 33:45–53
Rosell D, Uriz MJ (1992) Do associated zooxanthellae and the nature of the substratum affect survival, attachment and growth of Cliona viridis (Porifera: Hadromerida)? An experimental approach. Mar Biol 114:503–507
Rosell D, Uriz MJ (1997) Phylogenetic relationships within the excavating Hadromerida (Porifera), with a systematic revision. Cladistics 13:349–366
Rosell D, Uriz MJ (2002a) Excavating and endolithic sponge species (Porifera) from the Mediterranean: species descriptions and identification key. Org Divers Evol 2:55–86
Rosell D, Uriz MJ (2002b) Phylogenetic relationships within the excavating Hadromerida (Porifera), with a systematic revision. Cladistics 13:349–366
Row RWH (1911) Reports on the marine biology of the Sudanese Red Sea, from collections made by Cyril Crossland, M.A., B.Sc., F.Z.S. XIX. Report on the sponges collected by Mr. Cyril Crossland in 1904–5. Part II. Non-Calcarea. J Linnean Soc Zool 31:287–400, pls 35–41
Rudi E, Campbell SJ, Hoey AS, Fadli N, Linkie M, Baird AH (2012) The coral triangle initiative: what are we missing? A case study from Aceh. Oryx 46:482–485
Rützler K (1971) Bredin-Archbold-Smithsonian biological survey of Dominica: burrowing sponges, genus Siphonodictyon Bergquist, from the Caribbean. Smithsonian Contrib Zool 77:1–37
Rützler K (1973) Clionid sponges from the coast of Tunisia. Bull Inst Océanogr Pêche Salammbô 2:623–637
Rützler K (1974) The burrowing sponges of Bermuda. Smithsonian Contrib Zool 165:1–32
Rützler K (1975) The role of burrowing sponges in bioerosion. Oecologia 19:203–216
Rützler K (1990) Associations between Caribbean sponges and photosynthetic organisms. In: Rützler K (ed) New perspectives in sponge biology. Smithsonian Institution Press, Washington, pp 455–466
Rützler K (1997) The role of psammobiontic sponges in the reef community. In: Proceedings of the 8th international coral reef symposium, vol 2, Panama City, pp 1393–1398
Rützler K (2002a) Impact of crustose clionid sponges on Caribbean reef corals. Acta Geol Hisp 37:61–72
Rützler K (2002b) Family Clionaidae Ridley & Dendy, 1886. In: Hooper JNA, van Soest RWM (eds) Systema Porifera. A guide to the classification of sponges 1. Kluwer Academic/Plenum Publishers, New York, pp 173–185
Rützler K (2002c) Family Spirastrellidae Ridley & Dendy, 1886. In: Hooper JNA, van Soest RWM (eds) Systema Porifera. A guide to the classification of sponges 1. Kluwer Academic/Plenum Publishers, New York, pp 220–223
Rützler K (2002d) Family Alectonidae Rosell, 1996. In: Hooper JNA, van Soest RWM (eds) Systema Porifera. A guide to the classification of sponges 1. Kluwer Academic/Plenum Publishers, New York, pp 281–290
Rützler K, Hooper JNA (2000) Two new genera of hadromerid sponges (Porifera, Demospongiae). Zoosystema 22:337–344
Rützler K, Rieger G (1973) Sponge burrowing: fine structure of Cliona lampa penetrating calcareous substrata. Mar Biol 21:144–162
Rützler K, Stone SM (1986) Discovery and significance of Albany Hancock’s microscope preparations of excavating sponges (Porifera: Hadromerida: Clionidae). Proc Biol Soc Wash 99:658–675
Rützler K, van Soest RWM, Piantoni C (2009) Sponges (Porifera) of the Gulf of Mexico. In: Felder DL, Camp DK (eds) Gulf of Mexico – origins, waters, and biota. Biodiversity. Texas A&M Press, College Station, pp 285–313
Rützler K, Piantoni C, van Soest RWM, Díaz MC (2014) Diversity of sponges (Porifera) from cryptic habitats on the Belize barrier reef near Carrie Bow Cay. Zootaxa 3805:1–29
Sammarco PW, Risk MJ (1990) Large-scale patterns in internal bioerosion of Porites: cross-continental shelf trends in the Great Barrier Reef. Mar Ecol Prog Ser 59:145–156
Sammarco PW, Carleton JH, Risk MJ (1986) Effects of grazing and damselfish territoriality on bioerosion of dead corals: direct effects. J Exp Mar Biol Ecol 98:1–9
Sammarco PW, Risk MJ, Rose C (1987) Effects of grazing and damselfish territoriality on internal bioerosion of dead corals: indirect effects. J Exp Mar Biol Ecol 112:185–199
Santangelo G, Carletti E, Maggi E, Bramanti L (2003) Reproduction and population sexual structure of the overexploited Mediterranean red coral Corallium rubrum. Mar Ecol Prog Ser 248:99–108
Santangelo G, Cupido R, Cocito S, Bramanti L, Tsounis G, Iannelli M (2012) Demography of long-lived octocorals: survival and local extinction. In: Proceedings of the 12th international coral reef symposium, Cairns, pp 9–13
Santos CP, Coutinho AB, Hajdu E (2002) Spongivory by Eucidaris tribuloides from Salvador, Bahia (Echinodermata: Echinoidea). J Mar Biol Assoc UK 82:295–297
Sarà M, Pansini R, Pronzato M (1979) Zonation of photophilous sponges related to water movement in reef biotopes of Obhor Creek (Red Sea). In: Lévi C, Boury-Esnault N (eds) Biologie des spongiaires. Coll Int CNRS Paris 291:283–288
Sardiñas ZM, Alcolado PM (2004) Esponjas marinas del Archipiélago de Sabana-Camagüey, Cuba. Cocuyo 14:5–7
Sawall Y, Al-Sofyani A, Banguera-Hinestroza E, Voolstra CR (2014) Spatio-temporal analyses of Symbiodinium physiology of the coral Pocillopora verrucosa along large-scale nutrient and temperature gradients in the Red Sea. PLoS One 9:e103179
Scaps P, Denis V (2008) Can organisms associated with live scleractinian corals be used as indicators of coral reef status? Atoll Res Bull 566:1–18
Scheffers A, Scheffers S (2007) Tsunami deposits on the coastline of west Crete (Greece). Earth Planet Sci Lett 259:613–624
Schellinger J (2013) Hardbottom sessile macroinvertebrate communities of the Apalachee Bay Region of Florida's northeastern Gulf of Mexico. MSc thesis, Florida State University, Tallahassee, 50 pp
Schlegel H (1857) Handleiding tot beoefening der dierkunde. Volume 20, second part. Nys, Breda, pp 1–628
Schleyer MH, Heikoop JM, Risk MJ (2006) A benthic survey of Aliwal Shoal and assessment of the effects of a wood pulp effluent on the reef. Mar Poll Bull 52:503–514
Schmidt O (1870) Grundzüge einer Spongien-Fauna des atlantischen Gebietes. Wilhelm Engelmann, Leipzig, 88 pp, 6 pls
Schofield CH (2015) Why the world is wary of China’s ‘great wall of sand’ in the sea. Conversation RIS 101436
Schönberg CHL, Loh WKW (2005) Molecular identity of the unique symbiotic dinoflagellates found in the bioeroding demosponge Cliona orientalis. Mar Ecol Prog Ser 299:157–166
Schönberg CHL, Ortiz JC (2009) Is sponge bioerosion increasing? In: Proceedings of the 11th international coral reef symposium, Ft Lauderdale, pp 520–523
Schönberg CHL (1999) An improved method of tissue digestion for spicule mounts in sponge taxonomy. Mem Queensl Mus 44:524–533
Schönberg CHL (2000) Bioeroding sponges common to the Central Australian Great Barrier Reef: descriptions of three new species, two new records, and additions to two previously described species. Senckenberg Marit 30:161–221
Schönberg CHL (2001a) Estimating the extent of endolithic tissue of a clionid Great Barrier Reef sponge. Senckenberg Marit 31:29–39
Schönberg CHL (2001b) Small-scale distribution of Australian bioeroding sponges in shallow water. Ophelia 55:39–54
Schönberg CHL (2002a) Sponges of the ‘Cliona viridis complex’ – a key for species identification. Proc 9th Int Coral Reef Symp, Bali,1, pp 295–299
Schönberg CHL (2002b) Substrate effects on the bioeroding demosponge Cliona orientalis. 1. Bioerosion rates. PSZN I Mar Ecol 23:313–326
Schönberg CHL (2002c) Pione lampa, a bioeroding sponge in a worm reef. Hydrobiologia 482:49–68
Schönberg CHL (2003) Substrate effects on the bioeroding demosponge Cliona orientalis. 2. Substrate colonization and tissue growth. PSZN I Mar Ecol 24:59–74
Schönberg CHL (2006) Growth and erosion of the zooxanthellate Australian bioeroding sponge Cliona orientalis are enhanced in light. Proc 10th Int Coral Reef Symp, Okinawa, pp 168–174
Schönberg CHL (2008) A history of sponge erosion: from past myths and hypotheses to recent approaches. In: Wisshak M, Tapanila L (eds) Current developments in bioerosion. Springer, Berlin, Heidelberg, pp 165–202
Schönberg CHL (2013) Siphonodictyon type material: lost in history. In: Poster at the 9th World Sponge Conference, Fremantle 2013. http://f1000research.com/posters/1094687. [23 April 2016]
Schönberg CHL (2015a) Self-cleaning surfaces in sponges. Mar Biodiv 45:623–624
Schönberg CHL (2015b) Monitoring bioeroding sponges: using rubble, quadrat, or intercept surveys? Biol Bull 228:137–155
Schönberg CHL (2016a) Who is who in sponge science 2016. In: Van Soest RWM, Boury-Esnault N, Hooper JNA, Rützler K, de Voogd NJ, Alvarez de Glasby B, Hajdu E, Pisera AB, Manconi R, Schönberg CHL, Janussen D, Tabachnick KR, Klautau M, Picton B, Kelly M, Vacelet J, Dohrmann M, Díaz MC, Cárdenas P, Carballo JL (eds) World porifera database. http://www.marinespecies.org/porifera. [22 April 2016]
Schönberg CHL (2016b) Happy relationships of marine sponges with sediments – a review and some observations from Australia. J Mar Biol Assoc UK 96:493–514
Schönberg CHL (2017) Culture, demography and biogeography of sponge science: from past conferences to strategic research? Mar Ecol 38:e12416
Schönberg CHL, Beuck L (2007) Where Topsent went wrong: Aka infesta a.k.a. Aka labyrinthica (Demospongiae: Hadromerida) and implications for other Aka spp. J Mar Biol Assoc UK 87:1459–1476
Schönberg CHL, Burgess H (2013) Storm damage after cyclone Yasi: bioeroding sponges survived. Poster at the 9th World Sponge Conference, Fremantle 2013. Available from: http://f1000.com/posters/browse/summary/1094699. 12 Dec 2013
Schönberg CHL, Fromont J (2012) Sponge gardens of Ningaloo Reef (Carnarvon Shelf, Western Australia) are biodiversity hotspots. Hydrobiologia 687:143–161
Schönberg CHL, Shields G (2008) Micro-computed tomography for studies on Entobia: transparent substrate versus modern technology. In: Wisshak M, Tapanila L (eds) Current developments in bioerosion. Springer, Berlin, pp 147–164
Schönberg CHL, Suwa R (2007) Why bioeroding sponges may be better hosts for symbiotic dinoflagellates than many corals. In: Custódio MR, Lôbo-Hajdu G, Hajdu E, Muricy G (eds) Porifera research. Biodiversity, innovation and sustainability. National Museum, Rio de Janeiro, pp 569–580
Schönberg CHL, Tapanila L (2006a) Bioerosion research before and after 1996 – a discussion of what has changed since the first international bioerosion workshop. Ichnos 13:99–102
Schönberg CHL, Tapanila L (2006b) The bioeroding sponge Aka paratypica, a modern tracemaking analogue for the Paleozoic ichnogenus Entobia devonica. Ichnos 13:147–157
Schönberg CHL, Wilkinson CR (2001) Induced colonization of corals by a clionid bioeroding sponge. Coral Reefs 20:69–76
Schönberg CHL, Wisshak M (2012) The perks of being endolithic. Aquatic Biol 17:1–5
Schönberg CHL, Wisshak M (2014) Marine bioerosion. In: Goffredo S, Dubinsky Z (eds) The Mediterranean Sea: its history and present challenges. Springer, Dordrecht, pp 449–461
Schönberg CHL, Wilkinson CR, Hoppe KN (1997) Coral skeletal destruction – boring sponges on the Great Barrier Reef. In: Proceedings of Great Barrier Reef Science Use Management Nat Conference 2, Great Barrier Reef Marine Park Authority, Townsville, pp 67–71
Schönberg CHL, de Beer D, Lawton A (2005) Oxygen microsensor studies on zooxanthellate clionaid sponges from the Costa Brava, Mediterranean Sea. J Phycol 41:774–779
Schönberg CHL, Grass S, Heiermann AS (2006) Cliona minuscula, sp. nov. (Hadromerida: Clionaidae) and other bioeroding sponges that only contain tylostyles. Zootaxa 1312:1–24
Schönberg CHL, Suwa R, Hidaka M (2008) Sponge and coral zooxanthellae in heat and light: preliminary results of photochemical efficiency monitored with pulse amplitude modulated fluorometry. Mar Ecol 29:247–258
Schönberg CHL (2015a) Self-cleaning surfaces in sponges. Mar Biodiv 45:623-624
Schönberg CHL, Fang JKH, Carreiro-Silva M, Tribollet A, Wisshak M (2017) Bioerosion: the other ocean acidification problem. ICES J Mar Sci 74:895–925
Schönberg CHL, Tribollet A, Fang JKH, Carreiro-Silva M, Wisshak M (in press) Viewpoints in bioerosion research – are we really disagreeing? A reply to the comment by Silbiger and de Carlo. ICES J Mar Sci
Schuhmacher H, Plewka M (1981) The adaptive significance of mechanical properties versus morphological adjustments in skeletons of Acropora palmata and Acropora cervicornis (Cnidaria, Scleractinia). In: Gomez ED, Birkeland CE, Buddemeier RW, Johannes RE, Marsh Jr. JA, Tsuda RT (eds) Proceedings of the 4th International Coral Reef Symposium 2, Manila 1981, pp 121–128
Scoffin TP, Stearn CW, Boucher D, Frydl P, Hawkins CM, Hunter IG, MacGeachy JK (1980) Calcium carbonate budget of a fringing reef on the west coast of Barbados. II. Erosion, sediments and internal structure. Bull Mar Sci 30:475–508
Scott PJ (1987) Associations between corals and macro-infaunal invertebrates in Jamaica, with a list of Caribbean and Atlantic coral associates. Bull Mar Sci 40:271–286
Silbiger NJ, Guadayol Ò, Thomas FI, Donahue MJ (2014) Reefs shift from net accretion to net erosion along a natural environmental gradient. Mar Ecol Prog Ser 515:33–44
Sitjà C, Maldonado M (2014) New and rare sponges from the deep shelf of the Alboran Island (Alboran Sea, Western Mediterranean). Zootaxa 3760:141–179
Sivaleela G (2014) Marine sponges of Gulf of Mannar and Palk Bay. Rec Zool Surv India 114:607–622
Smyth MJ (1990) Incidence of boring organisms in gastropod shells on reefs around Guam. Bull Mar Sci 46:432–449
Sollas IBJ (1902) On the Sponges collected during the ‘Skeat Expedition’ to the Malay Peninsula, 1899–1900. Proc Zool Soc Lond 2:210–221, pls 14–15
Sollas WJ (1878) On two new and remarkable species of Cliona. Ann Mag Nat Hist 1:54–66
Sollas WJ (1888a) Voyage of H.M.S. Challenger. Zoology. Report on the Tetractinelida collected by H.M.S. Challenger during the years 1873–76. Zoology 25:1–458, pls I–XLIV, 1 map
Sollas WJ (1888b) Report on the Tetractinellida collected by H.M.S. Challenger during the years 1873–1876. The voyage of the H.M.S. Challenger. Zoology 25:1–458, pls I-XLIV, 1 map
Souter D, Obura D, Lindén O (2000) Coral reef degradation in the Indian Ocean. Status reports and project presentations 2000. CORDIO, Stockholm, 206 pp
Southerland M (2016) China’s island building in the South China Sea: damage to the marine environment, implications, and international law. Report of the United States–China economic and security review commission, Washington, p 11. http://origin.www.uscc.gov/sites/default/files/Research/China’s%20Island%20Building%20in%20the%20South%20China%20Sea_0.pdf. [14 June 2016]
Sowa K, Watanabe T, Kan H, Yamano H (2014) Influence of land development on Holocene Porites coral calcification at Nagura Bay, Ishigaki Island, Japan. PLoS One 9:e88790
Stearn CW, Scoffin TP (1977) Carbonate budget of a fringing reef, Barbados. In: Taylor DL (ed) Procedings of the 3rd International Coral Reef Symposium, Miami, 1977, pp 471–476
Stearn CW, Scoffin TP, Martindale W (1977) Calcium carbonate budget of a fringing reef on the west coast of Barbados. Part I – Zonation and productivity. Bull Mar Sci 27:479–510
Steindler L, Beer S, Peretzman-Shemer A, Nyberg C, Ilan M (2001) Photoadaptation of zooxanthellae in the sponge Cliona vastifica from the Red Sea, as measured in situ. Mar Biol 138:511–515
Stella J, Pears R, Wachenfeld D (2016) Interim report: 2016 coral bleaching event on the Great Barrier Reef. Great Barrier Reef Marine Park Authority, Townsville, 28 pp
Stevely JM, Sweat DE, Bert TM, Sim-Smith CA, Kelly MI (2011) Sponge mortality at Marathon and Long Key, Florida: patterns of species response and population recovery. In: Proceedings of the 63rd Gulf and Caribben Fisheries Institute, San Juan, 2010, pp 384–400
StoneContact (2016) International builders marketplace. http://www.stonecontact.com. [6 June 2016]
Strehlow B, Friday S, McCauley M, Hill M (2016a) The potential of azooxanthellate poriferan hosts to assess the fundamental and realized Symbiodinium niche: evaluating a novel method to initiate Symbiodinium associations. Coral Reefs 35:1201–1212
Strehlow BW, Jorgensen D, Webster NS, Pineda MC, Duckworth A (2016b) Using a thermistor flowmeter with attached video camera for monitoring sponge excurrent speed and oscular behaviour. PeerJ 4:e2761
Stubler AD, Peterson BJ (2016) Ocean acidification accelerates net calcium carbonate loss in a coral rubble community. Coral Reefs 35:795–803
Stubler AD, Furman BT, Peterson BJ (2014) Effects of pCO2 on the interaction between an excavating sponge, Cliona varians, and a hermatypic coral, Porites furcata. Mar Biol 161:1851–1859
Stubler AD, Furman BT, Peterson BJ (2015) Sponge erosion under acidification and warming scenarios: differential impacts on living and dead coral. Glob Change Biol 21:4006–4020
Sullivan B, Faulkner DJ, Webb L (1983) Siphonodictidine, a metabolite of the burrowing sponge Siphonodictyon sp. that inhibits coral growth. Science 221:1175–1176
Sunil Kumar P, Thomas PA (2011) Sponge infestation on Perna indica Kuriakose and Nair, 1976 in experimental culture systems. Indian J Geo-Mar Sci 40:731–733
Sunil Kumar P, Thomas PA (2012) Discovery of Alectona wallichii (Carter, 1874) from the Indian seas as a pest of brown mussel with notes on the zoogeography and substratum preference in Alectona spp. (Demospongiae: Alectonidae). J Mar Biol Assoc India 54:80–84
Sunil Kumar P, Thomas PA (2015) Systematics, zoogeography and affinity of boring sponges infesting the brown mussel, Perna indica Kuriakose and Nair from the southwest coast of India. J Mar Biol Assoc India 57:37–45
Sutcliffe PR, Hooper JNA, Pitcher CR (2010) The most common sponges on the Great Barrer Reef seabed, Australia, include species new to science (phylum Porifera). Zootaxa 2616:1–30
Swain TD, Wulff JL (2007) Diversity and specificity of Caribbean sponge–zoanthid symbioses: a foundation for understanding the adaptive significance of symbioses and generating hypotheses about higher-order systematics. Biol J Linnean Soc 92:695–711
Sweatman H, Delean S, Syms C (2011) Assessing loss of coral cover on Australia’s Great Barrier Reef over two decades, with implications for longer-term trends. Coral Reefs 30:521–531
Tabudravu JN, Eijsink VGH, Gooday GW, Jaspars M, Komander D, Legg M, Synstad B, van Aalten DMF (2002) Psammaplin A, a chitinase inhibitor isolated from the Fijian marine sponge Aplysinella rhax. Bioorg Med Chem 10:1123–1128
Tanita S (1961) Report on the sponges collected from the Kurushima Strait, Seto Inland Sea. Mem Ehime Univ Sect II B 4:335–354
Tanita S (1965) Report on the sponges obtained from the adjacent waters of the Sado Island, Japan Sea. Bull Jap Sci Reg Fish Res Lab 14:43–66
Tanita S (1967) Report on the sponges obtained from the Tajima District, southwestern region of the Japan Sea. Bull Jap Sci Reg Fish Res Lab 17:111–126
Tanita S (1968) Sponge-fauna of the Ariake Sea. Bull Seikai Reg Fish Res Lab 36:39–63
Tanita S (1969) Further studies on the sponges obtained from the Sado Inland and its adjacent waters. Bull Jap Sea Reg Fish Res Lab 21:67–88
Tanita S, Hoshino T (1989) The Demospongiae of Sagami Bay. Biological Laboratory, Imperial Household, Japan, pp 1–197, pls 1–19, 1 map
Tapanila L (2006) Devonian Entobia borings from Nevada, with a revision of Topsentopsis. J Paleontol 80:760–767
Templado J, García-Carrascosa M, Baratech L, Capaccioni R, Juan A, López-Ibor A, Silvestre R, Massó C (1986) Estudio preliminar de la fauna asociada a los fondos coralíferos del mar de Alborán (SE de España). Bol Inst Esp Oceanogr 3:93–104
Tendal OS (1969) Demospongiae from the Fiji Islands. Vidensk Meddr Dansk naturh Foren 132:31–44
Thiele J (1898) Studien über pazifische Spongien. I. Japanische Demospongien. Zoologica. Original-Abhandlungen aus dem Gesamtgebiete der Zoologie. Stuttgart 24(1):1–72, pls I–VIII
Thiele J (1899) Studien über pazifische Spongien. II. Ueber einige Spongien von Celebes. Zoologica. Original-Abhandlungen aus dem Gesamtgebiete der Zoologie. Stuttgart 24(2):1–33, pls I–V
Thiele J (1900) Kieselschwämme von Ternate I. Abh Senckenb naturf Gesellsch Frankf 25:19–80
Thomas MLH (1996) Origin and community structure of the Harrington Sound Notch, Bermuda. Bull Mar Sci 58:753–763
Thomas MLH, Logan A, Eakins KE, Mathers SM (1992) Biotic characteristics of the anchialine ponds of Bermuda. Bull Mar Sci 50:133–157
Thomas PA (1968) Studies on indian sponges – V. Two new records of silicious sponges belonging to the families Myxillidae Hentschel and Spirastrellidae Hentschel from the Indian Region. J Mar Biol Assoc India 10:264–268
Thomas PA (1972) Boring sponges of the reefs of Gulf of Mannar and Palk Bay. In: Mukundan C, Gopinadha Pillai CS (eds) Proceedings of the 1st Int Coral Reef Symposium on Corals and Coral Reefs, Mandapam Camp, 1969, pp 333–362
Thomas PA (1973) Marine Demospongiae of Mahe Island in the Seychelles Bank (Indian Ocean). Ann Mus Royal Afr Centrale. Sci Zool 203:1–96, pls I–VIII
Thomas PA (1979a) Sponges destructive to economically important molluscan beds and coral reefs in Indian Seas. Indian J Fish 26:163–200
Thomas PA (1979b) Studies on Sponges of the Mozambique Channel. I. – Sponges of Inhaca Island: II. – Sponges of Mambone and Paradise Islands. Ann Mus Royal Afr Centrale. Sci Zool 227:1–73, pls I–III
Thomas PA (1981) A second collection of marine Demospongiae from Mahe Island in the Seychelles Bank (Indian Ocean). Ann Mus Royal Afr Centrale. Sci Zool 233:1–54, pls I–IV
Thomas PA (1988) Sponge-generated bioerosion in Lakshadweep. Tech Ext Ser CFMRI Cochin, India 86:20–26
Thomas PA (1989) Sponge fauna of Lakshadweep. Bull Central Mar Fish Res Inst 43:150–161
Topsent E (1888) Contribution à l’étude des Clionides. Arch Zool Exp Gén 5:1–165, pls I–VII
Topsent E (1889) Quelques spongiaires du Banc de Campêche et de la Pointe-à-Pître. Mém Soc Zool Fr 2:30–52
Topsent E (1897) Spongiaires de la Baie d’Amboine. Voyage de MM. M. Bedot et C. Pictet dans l’Archipel Malais. Rev Suisse Zool 4:421–487, pls 18–21
Topsent E (1918) Éponges de San Thome. Essai sur les genres Spirastrella, Donatia et Chondrilla. Arch Zool Exp Gén 57:535–618
Topsent E (1920) Caractères et affinités des Thoosa Hanc. et des Alectona Cart. Considérations sur leurs germes à armure. Bull Soc Zool Fr 45:89–97
Topsent E (1932) Notes sur des clionides. Arch Zool Exp Gén 74:549–579
Topsent E (1933) Éponges de Lamarck conservées au Muséum de Paris. Arch Mus Paris (6)10:1–58, pls I–III
Topsent E (1900) Étude monographique des spongiaires de France. III. Monaxonida (Hadromerina). Arch Zool Exp Gén 8:1–331. pls I–VIII
Topsent E (1904) Spongiaires des Açores. Rés Camp Sci Monaco 25:109–111
Topsent E (1907) Cliona purpurea Hck. n’est pas une Clionide. Arch Zool Exp Gén 7:16–20
Torrents O, Tambutté E, Caminiti N, Garrabou J (2008) Upper thermal thresholds of shallow vs. deep populations of the precious Mediterranean red coral Corallium rubrum (L.): assessing the potential effects of warming in the NW Mediterranean. J Exp Mar Biol Ecol 357:7–19
Toth LT, Aronson RB, Vollmer SV, Hobbs JW, Urrego DH, Cheng H, Enochs IC, Combosch DJ, van Woesik R, Macintyre IG (2012) ENSO drove 2500-year collapse of eastern Pacific coral reefs. Science 337:81–84
Trégouboff G (1939) Sur les larves planctoniques d’éponges. C R Acad Sci Paris 208:1245–1246
Trégouboff G (1942) Contribution à la connaissance des larves planctoniques d’éponges. Arch Zool Exp Gen 82:357–399
Tribollet A, Golubic S (2005) Cross-shelf differences in the pattern and pace of bioerosion of experimental carbonate substrates exposed for 3 years on the northern Great Barrier Reef, Australia. Coral Reefs 24:422–434
Tun K, Chou LM, Cabanban A, Tuan VS, Philreefs YT, Suharsono SK, Lane D (2004) Status of coral reefs, coral reef monitoring and management in Southeast Asia, 2004. In: Wilkinson CR (ed) Status of coral reefs of the world: 2004, vol 1. Australian Institute of Marine Science, Townsville, pp 235–275
Tunnicliffe V (1979) The role of boring sponges in coral fracture. In: Lévi C, Boury-Esnault N (eds) Biologie des spongiaires. Coll Int CNRS Paris 291:309–315
Tunnicliffe V (1981) Breakage and propagation of the stony coral Acropora cervicornis. Proc Nat Acad Sci 78:2427–2431
Turner HM (1985) Parasites of eastern oysters from subtidal reefs in a Louisiana estuary with a note on their use as indicators of water quality. Estuaries 8:323–325
Tyler JC, Böhlke JE (1972) Records of sponge-dwelling fishes, primarily of the Caribbean. Bull Mar Sci 22:601–642
Ugalde D, Gomez P, Simoes N (2015) Marine sponges (Porifera: Demospongiae) from the Gulf of México, new records and redescription of Erylus trisphaerus (de Laubenfels, 1953). Zootaxa 3911:151–183
UNESCO (2016a) Great Barrier Reef. http://whc.unesco.org/en/list/154. [6 June 2016]
UNESCO (2016b) Damage to Great Barrier Reef assessed; stricter shipping surveillance proposed. http://whc.unesco.org/en/news/606. [21 December 2016]
UNESCO (2016c) Director-general meets with experts responsible for health or Great Barrier Reef. http://whc.unesco.org/en/news/1199. [21 December 2016]
UNESCO (2016d) Ningaloo Coast. http://whc.unesco.org/en/list/136. [23 April 2016]
UNESCO (2016e) World heritage list. http://whc.unesco.org/en/list. [21 December 2016]
UNESCO (2016f) Tentative lists. http://whc.unesco.org/en/tentativelists. [21 December 2016]
Vacelet J (1969) Éponges de la roche du large et de l’étage bathyal de Méditerranée (récoltes de la soucoupe plongeante Coustaeu et dragages). Mém Mus Natl Hist Nat Sér A 59:145–219, pls. I–III
Vacelet J (1981) Algal-sponge symbioses in coral refs of New Caledonia: a morphological study. In: Gomez ED, Birkeland CE, Buddemeier RW, Johannes RE, Marsh Jr. JA, Tsuda RT (eds) Proceedings of the 4th international Coral Reef Symposium 2, Manila 1981, pp 713–719
Vacelet J (1999) Planktonic armoured propagules of the excavating sponge Alectona (Porifera: Demospongiae) are larvae: evidence from Alectona wallichii and A. mesatlantica sp. nov. Mem Queensl Mus 44:627–642
Vacelet J, Vasseur P (1971) Éponges des récifs coralliens de Tuléar (Madagascar). Thetys 1:51–126
Vacelet J, Vasseur P, Lévi C (1976) Spongiaires de la pente externe des récifs coralliens de Tuléar (sud-ouest de Madagascar). Mém Mus Natl Hist Nat Sér A Zool 99:1–107, 9 pls
Vacelet J, Bitar G, Dailianis T, Zibrowius H, Pérez T (2008) A large encrusting clionaid sponge in the Eastern Mediterranean Sea. Mar Ecol 29:237–246
Valderrama D, Zea S (2003) Esquemas de distribución de esponjas arrecifales (Porifera) del noroccidente del golfo de Urabá, Caribe sur, Colombia. Bol Invest Mar Cost 32:37–56
Valderrama D, Zea S (2013) Annotated checklist of sponges (Porifera) from the southernmost Caribbean reefs (north-west Gulf of Urabá), with description of new records for the Colombian Caribbean. Rev Acad Colomb Cienc 37:353–378
Van Keulen M, Langdon MW (2011) Ningaloo collaboration cluster: biodiversity and ecology of the Ningaloo Reef lagoon. Ningaloo Collaboration Cluster Final Report 1c. CSIRO, Clayton, 71 pp
Van Soest RWM, Beglinger E, de Voogd N (2010) Skeletons in confusion: a review of astrophorid sponges with (dicho?) calthrops as structural megascleres (Porifera, Demospongiae, Astrophorida). ZooKeys 68:1–88
Van Soest RWM, Stone SM, Boury-Esnault N, Rützler K (1983) Catalogue of the Duchassaing & Michelotti (1864) collection of West Indian sponges (Porifera). Bull Zool Mus Univ Amsterdam 9:189–205
Van Soest RWM, Meesters EH, Becking LE (2014) Deep-water sponges (Porifera) from Bonaire and Klein Curaçao, Southern Caribbean. Zootaxa 3878:401–443
Van Soest RWM (1981) A checklist of the Curaçao sponges (Porifera Demospongiae) including a pictorial key to the more common reef-forms. Verslagen en Technische Gegevens Instituut voor Taxonomische Zoölogie (Zoölogisch Museum) Universiteit van Amsterdam 31:1–39
Van Soest RWM (1989) The Indonesian sponge fauna: a status report. Neth J Sea Res 23:223–230
Van Soest RWM (1990) Shallow-water reef sponges of eastern Indonesia. In: Rützler K (ed) New perspectives in sponge biology. Smithsonian Institution Press, Washington, pp 302–308
Van Soest RWM (2009) New sciophilous sponges from the Caribbean (Porifera: Demospongiae). Zootaxa 2107:1–40
Van Soest RWM (2017) Sponges of the Guyana Shelf. Zootaxa 4217:1–225
Van Soest RWM, Beglinger EJ (2008) Tetractinellid and hadromerid sponges of the Sultanate of Oman. Zool Med Leiden 82:749–790
Van Soest RWM, Beglinger EJ (2009) New bioeroding sponges from Mingulay coldwater reefs, north-west Scotland. J Mar Biol Assoc UK 89:329–335
Van Soest RWM, Zea S, Kielman M (1994) New species of Zyzzya, Cornulella, Damiria, and Acheliderma (Porifera: Poecilosclerida), with a review of fistular genera of Iophonidae. Bijdr Dierk 64:163–192
Van Soest RWM, Boury-Esnault N, Hooper JNA, Rützler K, de Voogd NJ, Alvarez de Glasby B, Hajdu E, Pisera AB, Manconi R, Schönberg CHL, Janussen D, Tabachnick KR, Klautau M, Picton B, Kelly M, Vacelet J, Dohrmann M, Díaz MC, Cárdenas P, Carballo JL (2017) World Porifera Database. Available from: http://www.marinespecies.org/porifera. 20 Jan 2017
Venkataraman K, Krishnamoorty P, Satyanarayana C, Sivaleela G (2007) Studies on faunal diversity and coral reef ecosystems of Palk Bay. Rec Zool Surv India Occas Paper 279:1–47
Verdín Padilla CJ, Carballo JL, Camacho ML (2010) A qualitative assessment of sponge-feeding organisms from the Mexican Pacific coast. Open Mar Biol J 4:39–46
Vermeij MJ, van der Heijden RA, Olthuis JG, Marhaver KL, Smith JE, Visser PM (2013) Survival and dispersal of turf algae and macroalgae consumed by herbivorous coral reef fishes. Oecologia 171:417–425
Veron JE, Devantier LM, Turak E, Green AL, Kininmonth S, Stafford-Smith M, Peterson N (2009) Delineating the coral triangle. Galaxea 11:91–100
Vicente VP (1978) An ecological evaluation of the West Indian demosponge Anthosigmella varians (Hadromerida: Spirastrellidae). Bull Mar Sci 28:771–777
Vicente VP (1990) Response of sponges with autotrophic endosymbionts during the coral-bleaching episode in Puerto Rico. Coral Reefs 8:199–202
Villamizar E, Díaz MC, Rützler K, Nóbrega R (2014) Biodiversity, ecological structure, and change in the sponge community of different geomorphological zones of the barrier fore reef at Carrie Bow Cay, Belize. Mar Ecol 35:425–435
Von Brandis RG, Mortimer JA, Reilly BK, van Soest RWM, Branch GM (2014) Diet composition of hawksbill turtles (Eretmochelys imbricata) in the Republic of Seychelles. West Indian Ocean J Mar Sci 13:81–91
Wall CC, Rodgers BS, Gobler CJ, Peterson BJ (2012) Responses of loggerhead sponges Spechiospongia vesparium during harmful cyanobacterial blooms in a sub-tropical lagoon. Mar Ecol Prog Ser 451:31–43
Warburton FE (1958a) Reproduction of fused larvae in the boring sponge Cliona celata. Nature 181:493–494
Warburton FE (1958b) The manner in which the sponge Cliona bores in calcareous objects. Can J Zool 36:555–562
Warburton FE (1966) The behaviour of sponge larvae. Ecology 47:672–674
Ward-Paige CA, Risk MJ, Sherwood OA, Jaap WC (2005) Clionid sponge surveys on the Florida Reef Tract suggest land-based nutrient inputs. Mar Poll Bull 51:570–579
Weil E, Hernández-Delgado EA, Bruckner AW, Ortiz AL, Nemeth M, Ruiz H (2003) Distribution and status of acroporid coral (Scleractinia) populations in Puerto Rico. In: Bruckner A (ed) Proceedings of the Caribbean Acropora Workshop: potential application of the US Endangered Species Act as a conservation strategy, Miami. NOAA Technical Memorandum NMFS-OPR-24, Silver Spring, pp 71–98
Weil E, Hernández-Delgado EA, Bruckner AW, Ortiz AL, Nemeth M, Ruiz H (2003) Distribution and status of acroporid coral (Scleractinia) populations in Puerto Rico. In: Bruckner A (ed) Proc Caribb Acropora Workshop: potential application of the US Endangered Species Act as a conservation strategy, Miami. NOAA Technical Memorandum NMFS-OPR-24, Silver Spring, pp 71–98
Weinstein DK, Smith TB, Klaus JS (2014) Mesophotic bioerosion: variability and structural impact on US Virgin Island deep reefs. Geomorphology 222:14–24
Weisz JB, Massaro AJ, Ramsby BD, Hill MS (2010) Zooxanthellar symbionts shape host sponge trophic status through translocation of carbon. Biol Bull 219:189–197
Wells HW (1959) Boring sponges (Clionidae) of Newport River, North Carolina. J Elisha Mitchell Sci Soc 75:168–173
Wells HW (1961) The fauna of oyster beds, with special reference to the salinity factor. Ecol Monogr 31:239–266
Westinga E, Hoetjes PC (1981) The intrasponge fauna of Spheciospongia vesparia (Porifera, Demospongiae) at Curaçao and Bonaire. Mar Biol 62:139–150
Wheeler AJ, Beyer A, Freiwald A, De Haas H, Huvenne VA, Kozachenko M, Olu-Le Roy K, Opderbecke J (2007) Morphology and environment of cold-water coral carbonate mounds on the NW European margin. Int J Earth Sci 96:37–56
Wiedenmayer F (1977) Shallow-water sponges of the Western Bahamas. Experient Suppl 28:281 pp
Wikipedia (2016a) List of historical tsunamis. https://en.wikipedia.org/wiki/List_of_historical_tsunamis. [2 June 2016]
Wikipedia (2016b) Calcite. Avialable from: https://en.wikipedia.org/wiki/Calcite. [6 June 2016]
Willenz P, Avezedo F, Carvalho de Souza M, Desqueroux-Faúndez R, Hajdu E, Klautau M, Lôbo-Hajdu G (2009) Porifera – sponges. In: Häussermann V, Försterra G (eds) Marine benthic fauna of Chilean Patagonia. Nature in Focus, Chile, pp 93–170
Williams EH Jr, Clavijo I, Kimmel JJ, Colin PL, Díaz Carela C, Bardales AT, Armstrong RA, Bunkley Williams L, Boulon RH, García JR (1983) A checklist of marine plants and animals of the Dominican Republic. Carib J Sci 19:39–53
Wilson HV (1925) Silicious and horny sponges collected by the U.S. Fisheries Steamer ‘Albatross’ during the Philippine Expedition, 1907-10. Contributions to the biology of the Philippine Archipelago and adjacent regions. Bull US Natl Mus 100:273–532
Wisshak M (2008) Two new dwarf Entobia ichnospecies in a diverse aphotic ichnocoenosis (Pleistocene/Rhodes, Greece). In: Wisshak M, Tapanila L (eds) Current developments in bioerosion. Springer, Berlin, pp 213–233
Wisshak M (in press) Taming an ichnotaxonomical Pandora’s box: revision of dendritic and rosetted microborings (ichnofamily: Dendrinidae). Eur J Taxon
Wisshak M, Freiwald A, Lundälv T, Gektidis M (2005) The physical niche of the bathyal Lophelia pertusa in a non-bathyal setting: environmental controls and palaeoecological implications. In: Freiwald A, Roberts JM (eds) Cold-water corals and ecosystems. Springer, Berlin, pp 979–1001
Wisshak M, Schönberg CHL, Form AU, Freiwald A (2012) Ocean acidification accelerates reef bioerosion. PLoS One 7:e45124
Wisshak M, Schönberg CHL, Form AU, Freiwald A (2013) Effects of ocean acidification and global warming on bioerosion – lessons from a clionaid sponge. Aquatic Biol 19:111–127
Wisshak M, Schönberg CHL, Form AU, Freiwald A (2014) Sponge bioerosion accelerated by ocean acidification across species and latitudes? Helgoland Mar Res 68:253–263
WoRMS Editorial Board (2017) World register of marine species. https://en.wikipedia.org/wiki/List_of_historical_tsunamis. [3 February 2017]
Wulff JL (1994) Sponge feeding by Caribbean angelfishes, trunkfishes, and filefishes. In: Van Soest RWM, van Kempen TMG, Braekman JC (eds) Sponges in time and space. Balkema, Rotterdam, pp 265–271
Wulff JL (1995) Sponge-feeding by the Caribbean starfish Oreaster reticulatus. Mar Biol 123:313–325
Wulff JL (2006) Rapid diversity and abundance decline in a Caribbean coral reef sponge community. Biol Conserv 127:167–176
Xavier JR, Rachello-Dolmen PG, Parra-Velandia FJ, Schönberg CHL, Breeuwer JAJ, van Soest RWM (2010) Molecular evidence of cryptic speciation in the ‘cosmopolitan’ excavating sponge Cliona celata (Porifera, Clionaidae). Mol Phyl Evol 56:13–20
Yokochi H (2004) Predation damage to corals. In: Tsuchiya M, Nadaoka K, Kayanne H, Yamano H (eds) Coral reefs of Japan. Ministry of the environment and Japanese Coral Reef Society, Tokyo, pp 49–55
Young HR, Nelson CS (1985) Biodegradation of temperate-water skeletal carbonates by boring sponges on Scott Shelf, British Columbia, Canada. Mar Geol 65:33–45
Zahir H (2002) Assessing bioerosion and its effect on reef structure following a bleaching event in the Maldives. In: Lindén O, Souter D, Wilhelmsson D, Obura D (eds) Coral reef degradation in the Indian Ocean. Status report 2002. CORDIO, Kalmar, pp 135–138
Zalmon IR, Krohling W, Ferreira CE (2011) Abundance and diversity patterns of the sessile macrobenthic community associated with environmental gradients in Vitória Harbor, southeastern Brazil. Zool Curitiba 28:641–652
Zea S (1987) Esponjas del Caribe Colombiano. Catálogo Científico, Bogota, pp 1–286
Zea S (1993) Cover of sponges and other sessile organisms in rocky and coral reef habitats of Santa Marta, Colombian Caribbean Sea. Caribb J Sci 29:75–88
Zea S, López-Victoria M (2016) Cliona acephala (Porifera: Demospongiae: Clionaida), a new encrusting excavating reef sponge from the Colombian Caribbean belonging to the Cliona viridis species complex. Zootaxa 4178:583–592
Zea S, Weil E (2003) Taxonomy of the Caribbean excavating sponge species complex Cliona caribbaea – C. aprica – C. langae (Porifera, Hadromerida, Clionaidae). Caribb J Sci 39:348–370
Zea S, Henkel TP, Pawlik JR (2016) The Sponge Guide: a picture guide to Caribbean sponges. 3rd Edition. Available from: http://www.spongeguide.org/index.php. 23 Apr 2016
Zilberberg C, Maldonado M, Solé-Cava AM (2006) Assessment of the relative contribution of asexual propagation in a population of the coral-excavating sponge Cliona delitrix from the Bahamas. Coral Reefs 25:297–301
Zundelevich A, Lazar B, Ilan M (2007) Chemical versus mechanical bioerosion of coral reefs by boring sponges – lessons from Pione cf. vastifica. J Exp Biol 210:91–96
Acknowledgements
I. Kötter supplied samples of the Red Sea Pione. M. Achlatis (University of Queensland), G. Heiss (Freie University Berlin), M. Jaini (Dakshin Foundation), J. Marlow (Victoria University), and M. Wisshak (Senckenberg Institute) contributed a photograph each of reef environments. R. van Soest provided advice on nomenclatural procedures. A. Chaves-Fonnegra, M. Hill, Y. Ise, J. Marlow and F. Moraes shared or discussed some of their recent observations. Data that were used in the faunistic record as ‘pers. obs.’ of CS were obtained during a visit at the Paris Natural History Museum funded by a Synthesis stipend and hosted by I. Domart-Coulon, a stay on the Ryukyu Islands funded by the Japan Society for the Promotion of Science hosted by M. Hidaka and R. Suwa, fieldwork conducted at the Australian Institute of Marine Science and observations of samples from the Western Australian Museum made accessible by J. Fromont and O. Gómez. Wound healing data of Mexican Cliona californiana were generated during fieldwork for the MSc thesis of L. Camacho. G. Moore assisted with radiographic imagery at the Western Australian Museum. D. Bellwood at James Cook University provided insights into parrotfish bioerosion. We thank E. Hajdu, F. Moraes, M. Ilan and J. Marlow to cross check our faunistic lists with their local species records and for giving us their permission the use of further unpublished data for Brazil, the Red Sea and Indonesia. A. Ereskovsky, I. Guibert, E. Hajdu, S. Morrison, D. Nacimento, M. Thollesson and P. Willenz sent literature that was difficult to obtain.
Author information
Authors and Affiliations
Corresponding author
Editor information
Editors and Affiliations
Appendices
Appendix A
Annotated faunistic list of sponge species confirmed or assumed to contribute to bioerosion in corals of selected bioregions. Based on Table 7.1, van Soest et al. (2017) and explanations given below, we accepted 260 valid sponges globally as separate species of confirmed or likely coral bioeroders, including all known morphologies. From this we generated a global analysis of bioeroding sponge biogeographies (Fig. 7.4). If available, additional OTUs (operational taxonomy units) were entered in the analysis if we could be reasonably sure not to duplicate existing records. For some decisions, we used NOAA Oceanservice (2014) and Wheeler et al. (2007) to judge which areas should be considered as supporting dense coral communities and chose bioregions as indicated and grouped below. As long as sponges occurred in known coral habitats, we assumed that they at least occasionally eroded coral materials, regardless of their morphology. While we examined details of many records, we took most publications at face value and caution the readers that difficult genera and groups such as Pione, Spheciospongia and the Cliona viridis complex will likely contain the largest rates of inaccuracies and that we are unable to provide an error value within the scope of this study. A few taxonomic decisions were nevertheless made if we considered the reasons as obvious, and these are explained below. Pending new results, we treated unresolved species complexes as one species, unless we could distinguish species within them based on the literature. An effort was made to include mostly original accounts on primary observations and to avoid secondary records compiled from the literature, as well as to divide records by habitats that were often defined by depth (shallow warm-water reefs versus corals being eroded in cold waters, deep or shallow—anything between 0 and 50 m was immediately scored as ‘shallow’). Publications on sponge biochemistry were avoided due to their often unreliable species identifications. For reasons given below, species names presented in brackets were not used for the biogeographic analysis. Abbreviations: Unconf. possible, but unconfirmed species record; ? author respective record by this author here needing confirmation, possibly erroneous identification or a tentative interpretation by us that this author may have meant this species; CS comments by Christine Schönberg; JLC comments by José Luis Carballo; AM Atlanto-Mediterranean sponges eroding cold-water corals; IP Indo-Pacific sponges eroding cold-water corals. Taxon validities and authorities were confirmed in van Soest et al. (2017), where full citations of original descriptions can also be found.
Species | Taxon authority | Type locality | References for reports in bioregion since original description (e.g.) |
---|---|---|---|
Caribbean, Gulf of Mexico, Florida and Bermuda (62 spp. of coral-eroding sponges in warm water) | |||
Alectona jamaicensis | Pang, 1973 | Jamaica, from 14 m | MacGeachy (1977), Scoffin et al. (1980), Pulitzer-Finali (1986), Lehnert and van Soest (1998); CS: The type sample was eroding Porites furcata in 14 m and was thus used for the warm-water analysis |
Amorphinopsis sp. | Not formally described | Reported from Belize | Rützler et al. (2014); CS: As the authors describe evidence that this sponge was actively excavating, we counted it for the biogeography data |
Cervicornia cuspidifera | (De Lamarck, 1815) | Caribbean Sea | Topsent (1933, as Spirastrella), Pulitzer-Finali (1986, as Spheciospongia), Vicente (1990, as Spheciospongia), Rützler (1997), Rützler and Hooper (2000), Díaz (2005), Rützler et al. (2009), Hill et al. (2011), Herrera-Moreno et al. (2012), Rützler et al. (2014) |
Cliona acephala | Zea and López-Victoria, 2016 | Caribbean Colombia | Very recent description, no other reports known |
Cliona amplicavata | Rützler, 1974 | Bermuda | Rützler (1974), MacGeachy (1977), Bromley (1978), Scoffin et al. (1980), ? van Soest (1981, as Cliona cf. amplicavata), Pulitzer-Finali (1986), Kobluk and van Soest (1989), Hofman and Kielman (1992), Holmes (2000), Rützler et al. (2014), Ugalde et al. (2015); CS: Cliona amplicavata may be a species complex and should be studied with molecular means |
Cliona aprica | Pang, 1973 | Jamaica | Rützler (1975), MacGeachy (1977), Pulitzer-Finali (1986), Vicente (1990), ? Gammill (1997), Lehnert and van Soest (1998), Perry (1998), Macdonald and Perry (2003), Valderrama and Zea (2003, as Cliona aprica-langae-caribbaea), Zea and Weil (2003), Díaz (2005), Granados et al. (2008), Rützler et al. (2009), Herrera-Moreno et al. (2012), Romero et al. (2013), Valderrama and Zea (2013), Rützler et al. (2014) |
(Cliona arenosa) taxon inquirendum | (Schmidt, 1870) | Florida Keys | Rützler et al. (2009); CS: According to van Soest et al. (2017), this species is a taxon inquirendum. Based on the original description, Cliona arenosa appears to be different from other local Cliona spp. but is very similar to Cliona tumula from Florida. As the two species could not adequately be compared during the present approach, only the species with the more comprehensive description was included into our biogeographic analysis |
Cliona barbadensis | Holmes, 2000 | Barbados | No other primary records found |
Cliona caribbaea | Carter, 1882 | St. Vincent | Topsent (1889), ? Topsent (1900, as Cliona viridis), de Laubenfels (1936a, 1953), Pang (1973, partly as Cliona langae), Rützler (1974), MacGeachy (1977), Bromley (1978), Pomponi (1979, partly as Cliona langae), Scoffin et al. (1980), van Soest (1981, as Cliona caribboea), Highsmith et al. (1983), Pulitzer-Finali (1986, partly as Cliona langae), Scott (1987, as Cliona langae), Rützler (1990), Vicente (1990), Hofman and Kielman (1992), Thomas (1996), Gammill (1997), Lehnert and van Soest (1998, partly as C. langae), Perry (1998, partly as Cliona langae), Holmes (2000), Rützler (2002a, includes Cliona aprica), Weil et al. (2002, as Cliona langae), Macdonald and Perry (2003, partly as Cliona langae), Valderrama and Zea (2003, as Cliona aprica-langae-caribbaea), Zea and Weil (2003), Callahan (2005), Collin et al. (2005), Díaz (2005), Díaz and Rützler (2007), Granados et al. (2008), González-Gándara et al. (2009), Rützler et al. (2009), Baquero (2010), Hill et al. (2011), Herrera-Moreno et al. (2012), Schellinger (2013), Villamizar et al. (2014); CS: Most reports for this species need to be confirmed and may not have relied on an accurate identification. Accounts for Cliona caribbaea from 2003 and before may relate to different species, likely including Cliona aprica and Cliona tenuis |
Cliona cf. celata | Unresolved species complex | Sensu stricto: Scotland | Topsent (1888, 1889), Arndt (1927), Hartman (1958), Little (1963), Pulitzer-Finali (1986), Rützler et al. (2009), Schellinger (2013); CS: Cliona celata was described from Scotland and represents a taxonomically difficult species complex (Xavier et al. 2010, de Paula et al. 2012). All faunistic accounts are unreliable, unless including molecular data. This report may or may not represent Cliona celata sensu stricto |
Cliona delitrix | Pang, 1973 | Jamaica | MacGeachy (1977), Pomponi (1979), Scoffin et al. (1980), van Soest (1981), Highsmith et al. (1983, as Cliona laticavicola), Pulitzer-Finali (1986, partly as Cliona laticavicola), Scott (1987, partly as Cliona laticavicola), Kobluk and van Soest (1989), Díaz et al. (1990), Hofman and Kielman (1992, as Cliona laticavicola), Lehnert (1993), Gammill (1997), Lehnert and van Soest (1998, partly as Cliona laticavicola), Perry (1998, partly as Cliona laticavicola), Holmes (2000), Rützler (2002b), Macdonald and Perry (2003, partly as Cliona laticavicola), Sardiñas and Alcolado (2004), Caballero et al. (2005), Callahan (2005), Collin et al. (2005), Díaz (2005), Ward-Paige et al. (2005), Zilberberg et al. (2006), Erwin and Thacker (2007), Mallela and Perry (2007, as Cliona laticavicola), Granados et al. (2008, as Cliona laticavicola), Baquero (2010, partly as Cliona laticavicola), González-Gándara et al. (2009), Rützler et al. (2009), Herrera-Moreno et al. (2012), Schellinger (2013), Valderrama and Zea (2013, as Cliona laticavicola), Mueller et al. (2014), Villamizar et al. (2014), Chaves-Fonnegra et al. (2015), Halperin et al. (2016); CS: Chaves-Fonnegra et al. (2017) recently showed that Cliona laticavicola is an ecophenotype of and conspecific with Cliona delitrix, with the latter being the senior synonym by a few pages in Pang (1973) |
Cliona dioryssa | (De Laubenfels, 1950a) | Bermuda | Pulitzer-Finali (1986), Hofman and Kielman (1992), Lehnert (1993), Thomas (1996) |
(Cliona? dubbia) taxon inquirendum | (Duchassaing de Fonbressin and Michelotti, 1864) | Caribbean | No other primary records found. CS: The World Porifera Database lists this species as taxon inquirendum (van Soest et al. 2017). The original description is insufficient, and apparently there is no type material for this species (van Soest et al. 1983). We disregarded this species entirely |
(Cliona? Pione? duvernoysii): genus transfer to Entobia duvernoysii new comb. | (Duchassaing de Fonbressin, 1850) | Caribbean | No other primary records found. CS: Taxon inquirendum (van Soest et al. 2017). According to the description by Duchassaing de Fonbressin and Michelotti (1864) this is not a biotaxon and a sponge, but a description of the ichnotaxon (Entobia duvernoysii new comb.). It is here not accepted as a record that can conclusively be matched with a bioeroding sponge and was ignored |
Cliona ensifera | Sollas, 1878 | Unknown, found in an octocoral (Isis sp.), which does not provide further information about the sample site. Assumed to be from the Indo-Pacific | MacGeachy (1977), Scoffin et al. (1980), Highsmith et al. (1983), Holmes (2000); CS: Cliona ensifera is frequently found in the Indo-Pacific (see below) and has not formally been redescribed for the Caribbean. This record should be checked. Being different from the other local species, it was still counted |
Cliona euryphylle | Topsent, 1888 | Campeche, Gulf of Mexico | Topsent (1889, 1900), Pulitzer-Finali (1986, as Cliona euryphilla), Rützler et al. (2009) |
Cliona flavifodina | Rützler, 1974 | Bermuda | Hechtel (1965, as Cliona viridis; see explanation given by Rützler 1974), MacGeachy (1977), Bromley (1978), Scoffin et al. (1980), Pulitzer-Finali (1986), Hofman and Kielman (1992, also as Cliona aff. flavifodina), Thomas et al. (1992), Thomas (1996), Holmes (2000), Rützler et al. (2014), Ugalde et al. (2015) |
Cliona janitrix | Topsent, 1932 | Strait of Bonifacio, Mediterranean | Pang (1973), Pulitzer-Finali (1986), Scott (1987, as Cliona janatrix), Kobluk and van Soest (1989), Lehnert and van Soest (1998), Perry (1998) |
(Cliona latens) taxon inquirendum | (Duchassaing de Fonbressin and Michelotti, 1864) | Caribbean | No other primary records found. CS: The World Porifera Database lists this species as taxon inquirendum (van Soest et al. 2017). While the original description suggests that this species may belong to the Cliona celata species complex, it is insufficient. Moreover, apparently there is no type material for this species (van Soest et al. 1983). We disregarded this species entirely |
Cliona laticavicola | Pang, 1973 | Jamaica | Highsmith et al. (1983), Pulitzer-Finali (1986), Scott (1987), Hofman and Kielman (1992), Lehnert and van Soest (1998), Perry (1998), Macdonald and Perry (2003), Mallela and Perry (2007), Granados et al. (2008), Baquero (2010), Valderrama and Zea (2013) |
Cliona lobata | Hancock, 1849 | English Channel | Hartman (1958) |
Cliona macgeachii | Holmes, 2000 | Barbados | Scoffin et al. (1980, as Cliona sp. 2), Holmes (2000) |
Unconf.: Cliona millepunctata | Hancock, 1849 | Unknown. Was found in the king helmet, Cassis tuberosa, which occurs in the W Atlantic (N Carolina to Brazil), Caribbean and at the Cape Verde Islands | Pulitzer-Finali (1986), Rützler and Stone (1986); CS: These records are based on the original description by Hancock, who provided no information about the sample site. However, as the king helmet is rare in Florida and northwards but common in the West Indies (EOL Rapid Response Team 2017), we tentatively counted Cliona millepunctata for the Atlantic, but only for the Caribbean. Topsent (1900) reported another specimen from the Indian Ocean, but this is presently regarded as an erroneous account |
(Cliona mucronata) | Sollas, 1878 | Unknown, found in an octocoral (Isis sp.), which does not provide further information about the sample site. Assumed to be from the Indo-Pacific | MacGeachy (1977), Scoffin et al. (1980), Scott (1987), Holmes (2000); CS: Cliona mucronata sensu stricto is frequently found in the Indo-Pacific (see below) and has not formally been redescribed for the Caribbean. This record should be checked and may represent Cliona cf. mucronata sensu Rützler et al. (2014; see below). Not being able to compare these two records and to avoid duplication, this one was excluded from the biogeography |
Cliona aff. mucronata | Unresolved species complex | Sensu stricto: unknown, likely Indo-Pacific | Rützler et al. (2014, as Cliona cf. mucronata); CS: Cliona mucronata is frequently found in the Indo-Pacific (see below) and has not formally been redescribed for the Caribbean. The spicules depicted in this publication are not typical for Cliona mucronata sensu Sollas. But as this species is different from the other Caribbean species, it was used for the biogeography |
Cliona paucispina | Rützler, 1974 | Bermuda | MacGeachy (1977), Bromley (1978), Scoffin et al. (1980), Pulitzer-Finali (1986), Thomas et al. (1992) |
Cliona peponaca | Pang, 1973 | Jamaica | Bak (1976), MacGeachy (1977), Highsmith et al. (1983), Pulitzer-Finali (1986), Lehnert and van Soest (1998), Macdonald and Perry (2003) |
(Cliona phallica) taxon inquirendum | Leidy, 1889 | Florida, Gulf of Mexico | No other primary records found. CS: Cliona phallica was described as one of the most common sponges in the area, to be yellowish and to have a single osculum per column. As we did not access type material, the description makes it likely that this is a synonym of Cliona varians. Therefore, we did not consider Cliona phallica in our biogeography |
(Unconf.: Cliona radiata) | Hancock, 1849 | Unknown. Was found in the Atlantic triton, Charonia variegata, which occurs in the Mediterranean, Atlantic and Caribbean | See also Rützler and Stone (1986). CS: We do not know the exact origin of this sample. However, as confirmed sample locations for the Atlantic triton are in the western Atlantic (WoRMS Editorial Board 2017b), we ignored Cliona radiata for the Caribbean and Brazil but tentatively counted it for the Gulf of Guinea. It also may be a senior synonym of Cliona amplicavata |
Cliona raphida | Boury-Esnault, 1973 | Brazil | Díaz and Rützler (2007) |
(Cliona saxicava) taxon inquirendum | (Duchassaing de Fonbressin and Michelotti, 1864) | Caribbean | No other primary records found. CS: The World Porifera Database lists this species as a valid species, but as incertae sedis (van Soest et al. 2017). However, while the original description suggests that this species may belong to the Cliona viridis species complex, it is insufficient. Apparently there is also no type material (van Soest et al. 1983), i.e. this should also be a taxon inquirendum. We disregarded this species entirely |
Cliona cf. schmidtii | (Ridley, 1881); based on an erroneous record of a ‘variety’ of Vioa johnstonii in Schmidt, 1870 p. 5 | Adriatic Sea, Mediterranean | Topsent (1889, as Cliona johnstonii), Pang (1973), MacGeachy (1977), Pomponi (1979), Scoffin et al. (1980), Pulitzer-Finali (1986), Kobluk and van Soest (1989, Lehnert and van Soest (1998), Perry (1998), Macdonald and Perry (2003), Mallela and Perry (2007), Rützler et al. (2009, 2014); JLC: Mediterranean and Caribbean Cliona schmidtii may be different species. CS: See van Soest et al. (2017) for a comment on this record. Spicules from sponges that were identified as Cliona schmidtii can be quite different, here leading to the assumption that the Caribbean material may not be conspecific with the type material (e.g. compare spicules pictured in Pang (1973) with those in Rosell and Uriz (2002a). However, there is at least one purple clionaid in the Caribbean; thus, it was used for the biogeographic analysis |
(Cliona? Pione? strombi): genus transfer to Entobia strombi new comb. | (Duchassaing de Fonbressin and Michelotti, 1864) | Caribbean | No other primary records found. CS: Taxon inquirendum (van Soest et al. 2017). According to Duchassaing de Fonbressin and Michelotti (1864) this is not a biotaxon and a sponge, but a description of the ichnotaxon and the bioerosion trace (Entobia strombi new comb.). It is here not accepted as a record that can conclusively be matched with a bioeroding sponge and was ignored |
(Cliona subulata) | Sollas, 1878 | Unknown but sympatric with Cliona ensifera and Cliona mucronata, thus assumed as Indo-Pacific | Topsent (1889), Rützler et al. (2009); CS: Cliona subulata is assumed to be an Indo-Pacific species. It has tylostyles and spirasters with long, discrete spines. Sollas’ drawings of the spicules strongly resemble those of Pang (1973) for Cliona caribbaea, and pending new results, we did not use this species in the biogeography for this bioregion to avoid duplication by using possibly synonymous species. Sollas’ type material needs to be re-examined |
Cliona tenuis | Zea and Weil, 2003 | Caribbean Colombia | ? Vicente (1990, as Anthosigmella sp.),? Gammill (1997, as Cliona langae), ? Valderrama and Zea (2003, as Cliona aprica-langae-caribbaea), Collin et al. (2005), Díaz (2005), Granados et al. (2008), Baquero (2010), González-Rivero et al. (2012, 2013), Valderrama and Zea (2013), Murphy et al. (2016) |
(Unconf.: Cliona topsenti) | (Von Lendenfeld, 1898) | Adriatic Sea, Mediterranean | Highsmith et al. (1983); CS: This might be a doubtful report as Cliona topsenti has not otherwise been rerecorded from outside of the Mediterranean and is a Cliona viridis complex species similar to other Caribbean species with a difficult taxonomy. We conservatively disregarded this report for the biogeographic analysis |
Cliona tumula | Friday et al., 2013 | Florida Keys | Hill et al. (2011, as ‘unidentified Cliona’), Schönberg pers. obs. (2008, as ‘unidentified Cliona’, Florida Keys); CS: Shares a significant number of characters with Schmidt’s Cliona arenosa (see above), which is also from Florida. Not having type material at our disposal, we only used Cliona tumula for our biogeography in order to avoid duplication of possibly synonymous species |
Cliona undulata | (George and Wilson, 1919) | South Carolina | ? Little (1963, as Cliona viridis), Bass (1993), Rützler et al. (2009) |
Cliona varians | (Duchassaing de Fonbressin and Michelotti, 1864) | Caribbean | ? Carter (1882, as Suberites coronarius), Topsent (1889, as Papillina arcuata), de Laubenfels (1949, 1953, as Anthosigmella), Little (1963, as Anthosigmella), Hechtel (1965, as Anthosigmella), Pang (1973, as Anthosigmella), Wiedenmayer (1977, as Anthosigmella), Vicente (1978, as Anthosigmella), ? van Soest (1981, as Cliona (Anthosigmella) sp.), van Soest et al. (1983, as Anthosigmella), Williams et al. (1983, as Anthosigmella), Pulitzer-Finali (1986, as Anthosigmella), Corredor et al. (1988, as Anthosigmella), Kobluk and van Soest (1989, as Anthosigmella), Díaz et al. (1990, as Anthosigmella), Vicente (1990, as Anthosigmella), Hofman and Kielman (1992, as Anthosigmella), Zea (1993, as Anthosigmella), Hill (1996, as Anthosigmella), Aerts and van Soest (1997, as Anthosigmella), Gammill (1997, as Anthosigmella), Lehnert and van Soest (1998, as Anthosigmella), Hill (1999, as Anthosigmella), Hill and Hill (2002, as Anthosigmella), Rützler (2002b), Valderrama and Zea (2003, as Anthosigmella), Sardiñas and Alcolado (2004), Caballero et al. (2005), Collin et al. (2005), Díaz (2005), Díaz and Rützler (2007), Erwin and Thacker (2007), Díaz and Zea (2008), Rützler et al. (2009), Baquero (2010), Amaro and Ramírez (2011), Hill et al. (2011), Stevely et al. (2011), Herrera-Moreno et al. (2012), Schellinger (2013), Valderrama and Zea (2013), Rützler et al. (2014), Stubler et al. (2014), Villamizar et al. (2014) |
Cliona vermifera | Hancock, 1867 | Unknown. In Chama sp., information which does not provide further clues | Topsent (1888, 1889), Hechtel (1965), Pang (1973), MacGeachy (1977), Bromley (1978), Scoffin et al. (1980), van Soest (1981), Highsmith et al. (1983), Pulitzer-Finali (1986), Rützler and Stone (1986), Scott (1987), Kobluk and van Soest (1989), Hofman and Kielman (1992), Lehnert and van Soest (1998), Perry (1998), Holmes (2000), Macdonald and Perry (2003), Mallela and Perry (2007), Rützler et al. (2009); CS: Cliona vermifera is thought to be a species complex (see, e.g. León-Pech et al. 2015), but pending new results is here treated as a single species |
Cliona viridis | (Schmidt, 1862) | Adriatic Sea, Mediterranean | Schmidt (1870, as Papillina suberea), Pulitzer-Finali (1986), Rützler et al. (2009) |
(Cliothosa hancocki) | (Topsent, 1888) | French Polynesia | Pulitzer-Finali (1986); CS: Pulitzer-Finali based this report on Topsent (1888, as Thoosa hancocci, for the Indo-Pacific) and Rützler (1973, for Tunisia). Neither of these two authors lists the species for the W Atlantic. We ignored this record for the wider Caribbean. CS regards this name as a species complex that needs to be resolved per respective bioregion |
Cornulella santamartae | (Van Soest et al., 1994) | Caribbean Colombia | Díaz and Zea (2008) |
Cornulum johnsoni | (De Laubenfels, 1934) | Greater Antilles | Pulitzer-Finali (1986), van Soest et al. (1994), Rützler et al. (2014) |
Dercitus (Stoeba) plicatus | (Schmidt, 1868) | Algeria, Mediterranean | ? Van Soest (1981, as Dercitus cf. plicatus), ? Kobluk and van Soest (1989, as Dercitus sp.; the authors state that this may be a new species) |
Diplastrella bistellata | (Schmidt, 1862) | Adriatic Sea, Mediterranean | |
Diplastrella megastellata | Hechtel, 1965 | Jamaica | Kobluk and van Soest (1989), Lehnert and van Soest (1998), Díaz (2005), Díaz and Rützler (2007), van Soest (2009), Herrera-Moreno et al. (2012) |
(Diplastrella ministrella) taxon inquirendum | Gammill, 1997 | Florida | No other primary records found. CS: Van Soest (2017) discussed the status of this species. It was here ignored |
Haliclona (Halichoclona) vansoesti | De Weerdt et al., 1999 | Curaçao | Erwin and Thacker (2007), Valderrama and Zea (2013), Rützler et al. (2014) |
Pione carpenteri | (Hancock, 1867) | Mazatlán | Topsent (1888, 1889, as Cliona), Rützler et al. (2009); CS: Species of the genus Pione are taxonomically difficult, and this record is based on very old publications on a Pacific species. Nevertheless, Pione carpenteri has rather robust tylostyles, and this record may thus be distinct from the other Pione species in the bioregion. This species was tentatively counted |
(Pione? dissociata): genus transfer to Entobia dissociata new comb. | (Duchassaing de Fonbressin, 1850) | Caribbean | No other primary records found. CS: According to Duchassaing de Fonbressin and Michelotti (1864) this is not a biotaxon and a sponge, but a description of a ichnotaxon and bioerosion trace (Entobia dissociata new comb.). It is here not accepted as a record that can conclusively be matched with a bioeroding sponge and was ignored |
(Unlikely record: Pione fryeri) | (Hancock, 1849) | Unknown. Was found in window pane oyster, Placuna placenta, which occurs between the Gulf of Aden and the Philippines | No other reports known for the wider Caribbean. CS: Van Soest et al. (2017) list the Caribbean Vioa/Pione dissociata as a synonym for Pione fryeri. However, as the description for Vioa dissociata appears to be for a bioerosion trace, it cannot conclusively be matched to a single sponge species (see comments for Pione dissociata). Moreover, as the type of Pione fryeri inhabited a windowpane oyster, its occurrence in the Caribbean is rather unlikely. Placuna placenta is commercially very important in the Philippines, and we tentatively assumed that the sample was from there and counted Pione fryeri only for the Coral Triangle |
Pione lampa | (De Laubenfels, 1950b) | Bermuda | De Laubenfels (1953, as Cliona), Little (1963, as Cliona), Neumann (1966, as Cliona), Pang (1973, as Cliona), Rützler and Rieger (1973, as Cliona), Rützler (1975, as Cliona), MacGeachy (1977, as Cliona), Bromley (1978, as Cliona), Scoffin et al. (1980, as Cliona), van Soest (1981, as Cliona), Pulitzer-Finali (1986, as Cliona), Hofman and Kielman (1992, as Cliona), Thomas et al. (1992, as Cliona), Lehnert and van Soest (1998, as Cliona), Perry (1998, as Cliona), Holmes (2000, as Cliona cf. vastifica), Schönberg (2002b), Rützler 2002c, as Cliona), Macdonald and Perry (2003, as Cliona), Callahan (2005, as Cliona), Ward-Paige et al. (2005, as Cliona), Mallela and Perry (2007, as Cliona), Rützler et al. (2009), Herrera-Moreno et al. (2012), Enochs et al. (2015) |
Pione truitti | (Old, 1941) | Chesapeake Bay | Hartman (1958, as Cliona), Little (1963, as Cliona), Turner (1985, as Cliona), Pulitzer-Finali (1986, as Cliona), Rützler et al. (2009); CS: The genus Pione is taxonomically difficult and confused, and the alpha-morphology Pione spp. of the Caribbean have not convincingly been redescribed or distinguished. At present, we follow Old (1941) and assume that the records for Pione truitti and Pione vastifica refer to different species |
Pione cf. vastifica | (Hancock, 1849) | Scotland | Topsent (1888, 1889, as Cliona), de Laubenfels (1949, as Cliona), Hartman (1958, as Cliona), Little (1963, as Cliona), Bromley (1978, as Cliona), Pulitzer-Finali (1986, as Cliona), Holmes (2000, as Cliona), Rützler et al. (2009); CS: The genus Pione is taxonomically difficult and confused, and the alpha-morphology Pione spp. of the Caribbean have not convincingly been redescribed or distinguished. At present, we follow Old (1941) and assume that the records for Pione truitti and Pione vastifica refer to different species |
Clionaid undetermined aff. Pione enigmatica sensu Moraes (2011) | Not formally described but reported in Rützler et al. (2014, as Cliona sp.) | Reported from Belize | No other reports known. CS: This sponge has unusual, complicated spirasters or spined rhabds not unlike those in, e.g. some Thoosidae. These microrhabds strongly resemble those in Pione enigmatica from Brazil, which is different from this species. It is presently not possible to conclusively allocate this material to a known genus, but it differs from all other known species and was counted |
Samus anonymus | Gray, 1867 | Brazil | Carter (1879), de Laubenfels (1950a), Rützler et al. (2009, 2014) |
Scolopes megastra | De Laubenfels, 1953 | Florida, Gulf of Mexico | |
Siphonodictyon brevitubulatum | Pang, 1973 | Jamaica | ? Topsent (1889, as Cliona labyrinthica), Rützler (1971), MacGeachy (1977), Pulitzer-Finali (1986), Zea (1987), Hofman and Kielman (1992, as Aka aff. brevitubulata), Lehnert and van Soest (1998, as Aka), Perry (1998, as Aka), Macdonald and Perry (2003, as Aka), Valderrama and Zea (2003, as Aka), Caballero et al. (2005, as Aka), Díaz (2005, as Aka cf. brevitubulatum), Carballo et al. (2007, as Aka), Mallela and Perry (2007, as Aka), Schönberg and Beuck (2007, as Aka), Murphy et al. (2016) |
Siphonodictyon cachacrouense | Rützler, 1971 | Dominica | MacGeachy (1977), Scoffin et al. (1980), Pulitzer-Finali (1986), Zea (1993, as Aka), Aerts and van Soest (1997, as Aka), Gammill (1997), Schönberg and Beuck (2007, as Aka) |
Siphonodictyon coralliphagum | Rützler, 1971 | Jamaica | Rützler (1971), MacGeachy (1977), Scoffin et al. (1980), van Soest (1981), Pulitzer-Finali (1986), Scott (1987), Zea (1987), Kobluk and van Soest (1989, as Aka), Hofman and Kielman (1992, as Aka), Lehnert (1993), Gammill (1997), Lehnert and van Soest (1998, 1999, as Aka), Luke (1998, as Aka), Caballero et al. (2005, as Aka), Collin et al. (2005, as Aka), Díaz (2005, as Aka coralliphagon), Díaz and Rützler (2007, as Aka), Schönberg and Beuck (2007, as Aka), Rützler et al. (2009, as Aka), Baquero (2010), Herrera-Moreno et al. (2012, as Aka), ? Mueller et al. (2014, as Siphonodictyon sp.), Rützler et al. (2014), Villamizar et al. (2014) |
(Siphonodictyon densum) | (Schmidt, 1868) | Gulf of Mexico | Van Soest et al. (2014, as Siphonodictyon viridescens); CS: The recent redescription for Siphonodictyon viridescens provides spicule dimensions that very well match those of Siphonodictyon densum, which has characteristic, unusually large oxeas for the genus. However, the sponge was reported from depths significantly deeper than 100 m, and it was not included in the biogeographic analysis for warm-water habitats in the Caribbean |
Siphonodictyon occultum | Rützler et al., 2014 | Belize | To date, no other primary records available |
Siphonodictyon ruetzleri | Calcinai et al., 2007a | Belize | |
Siphonodictyon siphonum | (De Laubenfels, 1949) | Bahamas | Rützler (1971), Wiedenmayer (1977), Williams et al. (1983), Pulitzer-Finali (1986), Hofman and Kielman (1992, as Aka), Lehnert and van Soest (1998, as Aka), Díaz and Rützler (2007, as Aka), Rützler et al. (2009, as Aka), Herrera-Moreno et al. (2012, as Aka) |
Siphonodictyon terebrans | (Schmidt, 1870) | St. Thomas | ? Carballo et al. (2007, as Aka coralliphagum); CS: After assessing a slide of the type material (2006), CS tentatively recognises this species as different from the other Siphonodictyon spp., and we counted it separately. Carballo et al.’s (2007) material resembles it but was not formally compared |
(Siphonodictyon viridescens) | (Schmidt, 1880) | Barbados | No other primary records found. CS: The record by van Soest (2017, as Siphonodictyon viridescens) is here regarded as Siphonodictyon densum. Both species occur well below 100 m water depth and have not yet been observed to erode coral materials. Both were excluded from the biogeographic analysis for warm-water habitats in the wider Caribbean |
Siphonodictyon xamaycaense | Pulitzer-Finali, 1986 | Jamaica | Hofman and Kielman (1992, as Aka aff. xamaycaensis), Lehnert and van Soest (1998, 1999, as Aka), Rützler et al. (2014) |
(Unlikely record: Spheciospongia papillosa) | (Ridley and Dendy, 1886) | Sydney Harbour, Australia | Rützler et al. (2009); CS: Unlikely report for a taxonomically comparatively difficult species that was originally found in the Pacific. As this record cannot conclusively be compared with Spheciospongia vesparium, it was ignored for the biogeography to avoid possible duplication |
Spheciospongia vesparium | (De Lamarck, 1815) | Caribbean | Arndt (1927, as Spirastrella pulvinata), Topsent (1933), Schmidt (1870, as Papillina cribrosa), de Laubenfels (1934, as Pseudosuberites melanos, 1936b, 1949, 1950a, as Spheciospongia othella, 1953, partly as Prianos tierney), Little (1963), Hechtel (1965), Wiedenmayer (1977), Bromley (1978, as Spheciospongia othella), van Soest (1981), Westinga and Hoetjes (1981), Pulitzer-Finali (1986), Díaz et al. (1990), Vicente (1990), Hofman and Kielman (1992), Thomas et al. (1992, as Spheciospongia othella), Lehnert (1993), Lehnert and van Soest (1998), Macdonald and Perry (2003, as Spheciospongia othella), Sardiñas and Alcolado (2004, as Cliona), Caballero et al. (2005), Collin et al. (2005), Díaz (2005), Rützler et al. (2009, partly as Spheciospongia cribosa), Stevely et al. (2011), Herrera-Moreno et al. (2012), Schellinger (2013), Rützler et al. (2014) |
Spirastrella coccinea | (Duchassaing de Fonbressin and Michelotti, 1864) | Caribbean | De Laubenfels (1936b), Dickinson (1945), de Laubenfels (1949, 1950a), Little (1963), Hechtel (1965), Wiedenmayer (1977), van Soest (1981), Pulitzer-Finali (1986), Kobluk and van Soest (1989), Aerts and van Soest (1997), Lehnert and van Soest (1998, 1999), Valderrama and Zea (2003), Caballero et al. (2005, as Spitastrella), Collin et al. (2005), Díaz (2005), Díaz and Rützler (2007), Erwin and Thacker (2007), Díaz and Zea (2008), Rützler et al. (2009), Herrera-Moreno et al. (2012), Schellinger (2013), Valderrama and Zea (2013) |
Spirastrella coccinopsis | (De Laubenfels, 1953) | Gulf of Mexico | Little (1963), Pulitzer-Finali (1986), Zea (1993), Rützler et al. (2009, 2014) |
Spirastrella hartmani | Boury-Esnault et al., 1999 | Caribbean Panama | Arndt (1927, as Spirastrella cunctatrix), de Laubenfels (1936a, as Spirastrella cunctatrix), Wiedenmayer (1977, as Spirastrella cunctatrix), Pulitzer-Finali (1986, as Spirastrella cunctatrix), Boury-Esnault et al. (1999), Collin et al. (2005), Díaz (2005), Díaz and Rützler (2007), Amaro and Ramírez (2011), Valderrama and Zea (2013) |
Spirastrella mollis | Verrill, 1907 | Bermuda | Thomas et al. (1992), Thomas (1996), Collin et al. (2005), Díaz (2005, as Spirastrella cf. mollis), Díaz and Rützler (2007), Rützler et al. (2014), ? Ugalde et al. (2015, as Spirastrella aff. mollis) |
(Spirastrella phyllodes) taxon inquirendum | (Schmidt, 1870) | Antilles | Rützler et al. (2009); CS: Taxon inquirendum (van Soest et al. 2017). Pending new results and confirmation of this species, it was not included into the biogeography to avoid possible duplication with other species |
Spiroxya spiralis | (Johnson, 1899) | Azores | Rützler et al. (2014) |
Cf. Suberea flavolivescens | (Hofman and Kielman, 1992) | Caribbean Colombia | ? Kobluk and van Soest (1989, as ‘keratose?excavating sponge’), Valderrama and Zea (2013), Rützler et al. (2014) |
Thoosa armata | Topsent, 1888 | Gulf of Guinea | |
Timea oxyasterina | Rützler et al., 2014 | Belize | Recent description. To date, no other reports known for the wider Caribbean |
Triptolemma endolithicum | Van Soest, 2009 | Caribbean Colombia | No other reports known for the wider Caribbean |
(Volzia cf. albicans) | (Volz, 1939) | Adriatic Sea, Mediterranean | Highsmith et al. (1983, as Cliona cf. albicans); CS: Possibly same species as below? Conservatively, only one was included in the biogeography |
Volzia cf. rovignensis | (Volz, 1939) | Adriatic Sea, Mediterranean | MacGeachy (1977, as Cliona ?rovignensis), Scoffin et al. (1980, as Cliona ?rovignensis), Holmes (2000, as Cliona rovignensis); CS: Possibly same species as above? Conservatively, only one was included in the biogeography, and we took the one more commonly mentioned |
Zyzzya invemar | (Van Soest et al., 1994) | Caribbean Colombia | No other primary records found |
Brazil and NE coast of South America, including Guyana (25 spp. of coral-eroding sponges in warm water) | |||
Cervicornia cuspidifera | (De Lamarck, 1815) | Caribbean Sea | Muricy et al. (2011), Cavalcanti (2013), van Soest (2017), F. Moraes et al. unpubl. data (2017) |
Cliona carteri | (Ridley, 1881) | Victoria Bank, 20°42′S, 37°27′W | Muricy et al. (2011, as mere record), Moraes et al. unpubl. data (2017); CS: This species may have largely been misunderstood, which depends on its colour. Ridley described it as ‘vivid crimson’ (red) in alcohol, but red colours in clionaids normally dull over time. He also stated that the colour was identical with that of Cliona schmidtii (Vioa johnstonii sensu Schmidt 1870) and very similar to that of Spheciospongia purpurea, which would make the colour a bright purple, not red. Purple pigments in some clionaids are remarkably stable after sampling, and we presently consider Cliona carteri to be a purple sponge. The question of the colour had already been raised by Topsent (1900). Regardless of the colour, Cliona carteri has significantly longer tylostyles than Cliona schmidtii sensu Boury-Esnault (1973) reported from Brazil. For Brazil, we considered Cliona carteri as a separate species for our biogeographic analysis |
Cliona cf. celata – clade C sensu de Paula et al. (2012) | Grant, 1826 | Sensu stricto: Scotland | ? Boury-Esnault (1973), ? Muricy and Moraes (1998), ? Reis and Leão (2002), ? Muricy and Hajdu (2006), ? Muricy et al. (2011), ? Cavalcanti (2013, as Cliona celata complex sp.); CS: Cliona celata is a morphologically difficult and unresolved species complex (Xavier et al. 2010). At least one of the two reported Brazilian records differs from Cliona celata sensu stricto; they were distinguished from each other with molecular means (de Paula et al. 2012) and are used in our analysis as two different species |
Cliona aff. celata – clade D sensu de Paula et al. (2012) | Not formally described | Reported from Brazil | ? Boury-Esnault (1973), ? Muricy and Moraes (1998), ? Reis and Leão (2002), ? Muricy and Hajdu (2006), ? Muricy et al. (2011), ? Cavalcanti (2013, as Cliona celata complex sp.); CS: Cliona celata is a morphologically difficult and partially unresolved species complex (Xavier et al. 2010). At least one of the two reported Brazilian records differs from Cliona celata sensu stricto; they were distinguished from each other with molecular means (de Paula et al. 2012) and are used in our analysis as two different species |
Cliona delitrix | Pang, 1973 | Jamaica | Muricy et al. (2011), F. Moraes et al. unpubl. data |
Cliona dioryssa | (De Laubenfels, 1950) | Bermuda | Muricy and Hajdu (2006), F. Muricy et al. (2011), Zalmon et al. (2011), Moraes et al. unpubl. data (2017) |
(Unconf.: Cliona millepunctata) | Hancock, 1849 | Unknown. Was found in the king helmet, Cassis tuberosa, which occurs in the W Atlantic (N Carolina to Brazil), Caribbean and at the Cape Verde Islands | No other reports known. CS: We do not know the exact origin of this sample. However, as the king helmet ‘is rare in Florida and northwards but common in the West Indies’ (EOL Rapid Response Team 2017), we tentatively counted Cliona millepunctata within the Atlantic, but only for the Caribbean. Topsent (1900) reported another specimen from the Indian Ocean, but this is presently regarded as an erroneous account |
(Unconf.: Cliona radiata) | Hancock, 1849 | Unknown. Was found in the Atlantic triton, Charonia variegata, which occurs in the Mediterranean, Atlantic and Caribbean | No other reports known. CS: We do not know the exact origin of this sample. However, as confirmed sample locations for the Atlantic triton are in the western Atlantic (WoRMS Editorial Board 2017c), we ignored Cliona radiata for the Caribbean and Brazil but tentatively counted it for the Gulf of Guinea. It also may be a senior synonym of Cliona ampliclavata |
Cliona raphida | Boury-Esnault, 1973 | Brazil | Boury-Esnault (1973) |
Cliona cf. schmidtii | (Ridley, 1881); based on an erroneous record of a ‘variety’ of Vioa johnstonii in Schmidt, 1870 p. 5 | Adriatic Sea, Mediterranean | Boury-Esnault (1973), ? Cavalcanti (2013); CS: Spicules from sponges that were identified as Cliona schmidtii can be quite different, and reports require confirmation (see spicules pictured in Pang 1973, Rosell and Uriz 2002) |
Cliona varians | (Duchassaing de Fonbressin and Michelotti, 1864) | Caribbean Sea | Muricy and Moraes (1998, as Anthosigmella), Moraes (2011), Muricy et al. (2011), Cavalcanti (2013), F. Moraes et al. unpubl. data (2017) |
Cliona viridis | (Schmidt, 1862) | Adriatic Sea, Mediterranean | Leal et al. (2016; with molecular support) |
Cliona sp. undetermined, red (aff. flavifodina?) | Awaiting assessment | From Bahía, Brazil | ? Topsent (1900, as Cliona viridis var. carteri, described as ‘scarlet red’), F. Moraes et al. unpubl. data (2017) |
Diplastrella megastellata | Hechtel, 1965 | Jamaica | Moraes (2011) |
(Diplastrella spirastrelloides) | Van Soest, 2017 | French Guiana | Very recent description, no other records known. CS: Diplastrella spirastrelloides encrusted coarse sediments in 94 m depth and was presently not counted as a coral bioeroder |
Haliclona (Halichoclona) vansoesti | De Weerdt et al., 1999 | Curaçao | Muricy et al. (2015) |
Pione aff. carpenteri | Unresolved species complex | Sensu stricto: Mazatlán | Boury-Esnault (1973, as Cliona), Cavalcanti (2013); CS: The genus Pione is taxonomically difficult, and this record is based on very old publications on a Pacific species. While the species may not be Pione carpenteri, no other typical Pione sp. has been recorded from Brazil, and it was here counted |
Pione enigmatica: recommendation to reassess genus allocation | Moraes, 2011 | Brazil | No other reports known. CS: This species has tylostyles, smooth oxeas and microrhabds with unusual, complicated spines not unlike, e.g. in some Thoosidae. The microrhabds strongly resemble those in Cliona sp. sensu Rützler et al. (2014) from Belize. We cannot conclusively allocate this material to a known genus, but it differs from all the other known species |
Samus anonymus | Gray, 1867 | Brazil | Sollas (1888b) |
Scolopes moseleyi | Sollas, 1888 | Brazil | Cavalcanti (2013) |
Siphonodictyon brevitubulatum | Pang, 1973 | Jamaica | Moraes (2011, as Siphonodictyon coralliphagum) |
Siphonodictyon coralliphagum | Rützler, 1971 | Jamaica | F. Moraes et al. unpubl. data (2017) |
Siphonodictyon sp. | Not yet formally described | From Bahía, Brazil | F. Moraes et al. unpubl. data 2017; CS: This Siphonodictyon sp. is different from the other species known from Brazil |
(Siphonodictyon aff. densum) | (Schmidt, 1870) | Gulf of Mexico | Van Soest (2017); CS: Schmidt’s species was described with small fistules (‘barely the width of a quill’), while Van Soest (2017) reported fistules of 1 cm thickness. This may not be a strong, distinctive character, but the holotype has sharply pointed oxeas on average 240 μm long (C. Schönberg unpubl. data 2005), i.e. significantly longer oxeas than recorded by van Soest (2017). The latter material may not be Siphonodictyon densum. It was also sampled from 130 m depth and may thus not be a typical coral reef sponge. It was presently not counted in our biogeographic analysis |
Spheciospongia symbioticum | Hechtel, 1983 | Brazil | Cavalcanti (2013) |
Spheciospongia vesparium | (De Lamarck, 1815) | Caribbean Sea | Muricy et al. (2008), Cavalcanti (2013), F. Moraes et al. unpubl. data (2017) |
Spirastrella coccinea | (Duchassaing de Fonbressin and Michelotti, 1864) | Caribbean Sea | |
Spirastrella erylicola | Van Soest, 2017 | French Guiana | Very recent description, no other records known |
Spirastrella hartmani | Boury-Esnault et al., 1999 | Caribbean Panama | ? De Laubenfels (1956, as Spirastrella cunctatrix), Moraes (2011), Muricy et al. (2011), Cavalcanti (2013) |
Gulf of Guinea (8 spp. of coral-eroding sponges in warm water) | |||
Cliona aethiopica | Burton, 1932 | Gulf of Guinea | No other primary records found |
Cliona lobata | Hancock, 1849 | English Channel | Topsent (1918) |
Unconf.: Cliona radiata | Hancock, 1849 | Unknown. Was found in the Atlantic triton, Charonia variegata, which occurs in the Mediterranean, Atlantic and Caribbean | No other reports known. CS: We do not know the exact origin of this sample. However, as confirmed sample locations for the Atlantic triton are in the western Atlantic (WoRMS Editorial Board 2017b), we ignored Cliona radiata for the Caribbean and Brazil but tentatively counted it for the Gulf of Guinea. It also may be a senior synonym of Cliona ampliclavata |
Pione carpenteri | (Hancock, 1867) | Mazatlán | Topsent (1918, as Cliona); CS: The genus Pione is taxonomically difficult, and this record is based on very old publications on a Pacific species. As ‘carpenteri’ and ‘vastifica’ were reported by the same author, we assume that they represent two different Pione spp. Therefore, two Pione spp. were counted for the biogeography analysis of this bioregion |
Pione vastifica | (Hancock, 1849) | Scotland | Topsent (1918, as Cliona) |
Samus anonymus | Gray, 1867 | Brazil | Lévi (1959a) |
Spirastrella cunctatrix | Schmidt, 1868 | Algeria, Mediterranean | |
Thoosa armata | Topsent, 1888 | Gulf of Guinea | |
Red Sea, Persian Gulf and W Arabian Sea (19 spp. of coral-eroding sponges in warm water) | |||
Cliona aff. celata | Unresolved species complex | Sensu stricto: Scotland | ? Row (1911), ? Nazemi et al. (2015); CS: The authors’ species identifications should be reassessed. For the time being, this record is counted as a separate species for the bioregion |
Cliona aff. dioryssa | Sensu stricto: (De Laubenfels, 1950) | Sensu stricto: Bermuda | Eisapor et al. (2012), Eisapor and Safaeian (2013); CS: The papillae figured by the authors strongly resemble those of Cliothosa aurivillii. Regardless of the exact species identification, this is a different species than other species known from the area and was counted in our analysis |
Cliona jullieni | Topsent, 1891 | La Réunion | Ferrario et al. (2010) |
(Clionaid sp. undetermined 1, aff. Cliona jullieni or Cliona rhodensis) | Not morphologically identified | Reported from the Red Sea | Erpenbeck et al. (2016, as Cliona sp. OTU#04); CS: See their 28S and COI reconstruction. Here not counted for biogeographic analysis to avoid possible duplication with either Cliona jullieni above or other Cliona viridis complex species as below |
(Clionaid sp. undetermined 2, aff. Cliona jullieni or Cliona rhodensis) | Not morphologically identified | Reported from the Red Sea | Erpenbeck et al. (2016, as Cliona sp. GW3452); CS: See their 28S and COI reconstruction. Here not counted to avoid possible duplication with either Cliona jullieni above or other Cliona viridis complex species as below |
(Cliona subulata) | Sollas, 1878 | Unknown, but sympatric with Cliona ensifera and Cliona mucronata, thus assumed as Indo-Pacific | No other primary records found for this bioregion. CS: Cliona subulata has tylostyles and spirasters with long, discrete spines. Sollas’ drawings of the spicules suggest that the species belongs to the Cliona viridis complex, of which there are other species in the area that cannot adequately be compared with Cliona subulata. Pending new results, we did not use Cliona subulata in the biogeography to avoid possible duplication. Sollas’ type material needs to be re-examined |
Cliona viridis complex sp. or spp. | Unresolved species complex | Cliona orientalis sensu stricto: Molucca Sea, Indonesia | Lévi (1958, as Cliona orientalis), Fishelson (1971, as Cliona orientalis), ? Erpenbeck et al. (2016, as Cliona sp. OTU#03); CS: This record needs to be confirmed. New, similar species were described that may occur in the area, and there may be more than one Cliona viridis complex species. |
Cliothosa aff. hancocki | Unresolved species complex | Sensu stricto: French Polynesia | Lévi (1965a); CS regards this name as a species complex that needs to be resolved per respective bioregion, and Lévi’s spicules look odd. It is here still counted as a species distinct from the others occurring in this region |
(Unconf.: Cornulella purpurea) | (Hancock, 1849) | Unknown, sample found in Tridacna gigas, which has an Indo-Pacific distribution | Referring to Hancock’s sample and thus not reporting a confirmed sample site: Kirkpatrick (1900a, as Dyscliona), Topsent (1907, as undetermined genus), Hallmann (1920, as Paracornulum), Rützler and Stone (1986, as Cliona), van Soest et al. (1994); CS: It is possible that Cornulella purpurea occurs in this bioregion, but as the sample site is unknown and cannot be conclusively matched to our bioregions, this species did not become part of our analysis |
Diplastrella gardineri | Topsent, 1918 | Maldives | Lévi (1958) |
Pione carpenteri | (Hancock, 1867) | Mazatlán | Doroudi (1996, as Cliona), Ferrario et al. (2010); CS: The genus Pione is taxonomically difficult, and this record is based on a very old publication of an E Pacific species. However, while the exact species identification may need to be reconfirmed, the latter authors distinguished three species of Pione by molecular means, so it can here be counted for the biogeography |
Cf. Pione cervina | (Hancock, 1849) | Unknown. Found in a pearl shell, Pinctada cf. albina, which occurs in the Red Sea | No other primary records found. CS: Taxon inquirendum (van Soest et al. 2017). Has tuberculate diactines unusual for Pione (Rützler and Stone 1986). But as it differs from the other species, it is here tentatively counted (based on the vague identification of the host shell) |
Pione margaritiferae | (Dendy, 1905) | Gulf of Mannar | Doroudi (1996, as Cliona), Ferrario et al. (2010); CS: The genus Pione is taxonomically difficult, and this record is based on a comparatively old publication of an Indian species. However, while the exact species identification may need to be reconfirmed, the authors distinguished three species of Pione by molecular means, so it can here be counted for the biogeographic analysis |
Pione mussae | (Keller, 1891) | Central Red Sea, Sudan | Bertram (1936, as Cliona), Lévi (1958, as Cliona vastifica), ? Doroudi (1996, as Cliona vastifica), Beer and Ilan (1998, as Cliona vastifica), Steindler et al. (2001, as Cliona vastifica), Ferrario et al. (2010, as Pione cf. vastifica and Pione cf. lampa), Bruckner and Dempsey (2015, as ‘bioeroding sponge’), Nazemi et al. (2015, as Cliona vastifica), Erpenbeck et al. (2016, as Pione cf. vastifica OTU#07); CS: This refers to the bright orange-red, papillate or encrusting-endolithic species that is most commonly reported in beta morphology, and the authors separated this species from the other two Pione spp. in the Red Sea by molecular analysis. Three species were counted |
Siphonodictyon sp. | Not formally described, noticed by C. Schönberg pers. obs. (2006) | Gulf of Aden | No other primary records found. CS thinks this is an undescribed Siphonodictyon sp. (working name ‘zipallapiz’) |
Spheciospongia inconstans | (Dendy, 1887) | Madras | Lévi (1965a, as Spirastrella), Fishelson (1971, as Spirastrella), ? Van Soest and Beglinger (2008, as Spheciospongia tentorioides) |
Spheciospongia mastoidea | (Keller, 1891) | Southern Red Sea, Eritrea | No other primary records found |
Spheciospongia cf. vagabunda | (Ridley, 1884) | Torres Straits | Erpenbeck et al. (2016, as Spirastrella OTU#05); CS: Gamma morphology. See their 28S reconstruction |
Spirastrella decumbens | Ridley, 1884 | Torres Straits | Keller (1891), Lévi (1958), Lévi (1965a, as Spirastrella cunctatrix), Fishelson (1971, as Spirastrella cunctatrix), ? Erpenbeck et al. (2016, as OTU #06), CS: See their 28S and COI reconstructions. Van Soest et al. (2017) consider records of Spirastrella cunctatrix as incorrect for the Red Sea. As this species is very similar to Spirastrella decumbens, we tentatively listed respective reports as Spirastrella decumbens |
Spirastrella cf. hartmani | Boury-Esnault et al., 1999 | Caribbean Panama | Erpenbeck et al. (2016, as GW5949), CS: See their 28S and COI reconstructions |
Spirastrella pachyspira | Lévi, 1958 | E Red Sea, Saudi Arabia | No other records known from the Red Sea |
(Unconf.: Thoosa cactoides) | Hancock, 1849 | Unknown. In the pearl oyster, Pinctada margaritifera, which has an Indo-Pacific distribution | No other primary records found. CS: As we do not know the exact type location of this species, we did not count it for any specific bioregion |
Unconf.: Thoosa circumflexa | Topsent, 1891 | Unknown, sample found in Caen, on Tridacna sp., a genus which has an Indo-Pacific distribution | ? Lévi (1965a, as Thoosa armata), ? Fishelson (1971, as Thoosa armata); CS: According to van Soest et al. (2017), Thoosa circumflexa is a taxon inquirendum, but after viewing Topsent’s samples in Paris (2006–2007), CS finds this to be a good species. The Red Sea records are for Thoosa armata, which is an Atlantic species, and according to van Soest et al. (2017) it does not occur in the Red Sea. Lévi’s drawings appeared to be most similar to drawings CS made of spicules of Thoosa circumflexa, which is an Indo-Pacific sponge and may possibly occur in the Red Sea. The present decision is very tentative, but the species counted for our biogeographic analysis |
Unconf.: Thoosa letellieri | Topsent, 1891 | Unknown, sample found in Caen, on Tridacna sp., a genus which has an Indo-Pacific distribution | No other primary records found. CS: It is an Indo-Pacific sponge and may possibly occur in the Red Sea. According to van Soest et al. (2017), this is a taxon inquirendum, but after viewing Topsent’s samples in Paris (2006–2007), CS finds this to be a good species. As we decided that Thoosa circumflexa might occur in the Red Sea (see above) and the type of Thoosa letellieri was found in the same shell, we tentatively counted the latter as well |
E Africa, Madagascar, Seychelles, Reunion and Mauritius (38 spp. of coral-eroding sponges in warm water) | |||
Alectona primitiva | Topsent, 1932 | Kangaroo Island, S Australia, in the whirling abalone Haliotis cyclobates (as Haliotis excavata) | Vacelet and Vasseur (1971, from shallow water) |
Alectona wallichii | (Carter, 1874) | Agulhas Bank, S of Africa (Carter: also from the ‘South Sea’ and Seychelles), first reported as spicules in sediment | Vacelet (1999, from shallow water) |
Amorphinopsis excavans | Carter, 1887 | W Andaman Sea | Thomas (1973); CS: Amorphinopsis excavans is seen as an Indo-Pacific species, but characters described in older accounts vary. The species (complex?) needs to be re-examined and revised (Carvalho et al. 2004) |
Aff. Cervicornia cuspidifera | Unresolved species complex | Sensu stricto: Caribbean Sea | Thomas (1973, 1981, as Spirastrella cuspidifera); CS: Cervicornia cuspidifera is a Caribbean species. Other endopsammic clionaids exist in the Indo-Pacific, and this account needs to be re-examined. It was still counted as a species different from the others in the area |
Cliona albimarginata | Calcinai et al., 2005 | N Sulawesi | ? Thomas (1981, as Cliona viridis), ? Pulitzer-Finali (1993, as Cliona viridis), ? Calcinai et al. (2000, as Spheciospongia varians), ? Schleyer et al. (2006, as Anthosigmella orientalis), Azzini in Calcinai et al. (2008a) |
Cliona aff. celata | Unresolved species complex | Sensu stricto: Scotland | Dendy (1922), Vacelet and Vasseur (1971), Thomas (1973, 1979a), Calcinai et al. (2000); CS: Cliona celata was described from Scotland and represents a taxonomically difficult species complex (Xavier et al. 2010, de Paula et al. 2012). All faunistic accounts are unreliable unless including molecular data. This report is unlikely to be Cliona celata sensu stricto but was still counted as a clionaid different from others in the bioregion |
Cliona ensifera | Sollas, 1878 | Unknown, found in an octocoral (Isis sp.), which does not provide useful information. Assumed from Indo-Pacific | Vacelet et al. (1976) |
Cliona johnstonii | (Carter, 1886) | Bass Strait | Ridley (1884, as Vioa schmidti), Topsent (1900, as Cliona schmidti), Vacelet et al. (1976, as Cliona schmidtii); CS: We tentatively listed all ‘Cliona schmidtii’ reported from the Indo-Pacific as Cliona johnstonii to imply that the two species are different. See van Soest et al. (2017) for comments on the distribution of Cliona schmidtii |
Cliona jullieni | Topsent, 1891 | La Réunion | Vacelet et al. (1976) |
Cliona aff. lobata | Unresolved species complex | Sensu stricto: English Channel | Vacelet et al. (1976); CS: The Atlantic species Cliona lobata has been widely reported, but maybe not always accurately. These accounts have to be re-examined. The present record is possibly misidentified but is here counted as a morphologically different clionaid for the bioregion |
(Unconf.: Cliona michelini) | Topsent, 1888 | Indian Ocean, in shell of rock snail | No other primary records found for this bioregion. CS: This species may occur in the bioregion, but as the exact sample origin is unknown, it was not included here. Based on notes on a slide preparation, Cliona michelini was listed for India, however |
Cliona mucronata | Sollas, 1878 | Unknown, found in an octocoral (Isis sp.), which does not provide further information about the sample site. Assumed to be from the Indo-Pacific | Vacelet et al. (1976), Thomas (1979a), Calcinai et al. (2000) |
Cliona aff. mucronata sensu Vacelet and Vasseur (1971) | Unresolved species complex | Sensu stricto: Unknown, likely Indo-Pacific | Vacelet and Vasseur (1971); CS: Their figure of the short tylostyle is not typical for Cliona mucronata sensu stricto. As Cliona aff. mucronata and sensu stricto can both be found on the Great Barrier Reef (C. Schönberg unpubl. data 2010–2011), the species were here considered separately |
(Cliona subulata) | Sollas, 1878 | Unknown, but sympatric with Cliona ensifera and Cliona mucronata, thus assumed as Indo-Pacific | No other primary records found for this bioregion. CS: Cliona subulata has tylostyles and spirasters with long, discrete spines. Sollas’ drawings of the spicules suggest that the species belongs to the Cliona viridis complex, of which there are others in the area that cannot adequately be compared with Cliona subulata. Pending new results, we did not use this species in the biogeography to avoid possible duplication. Sollas’ type material needs to be re-examined |
(Unconf.: Cliona thoosina) | Topsent, 1888 | Unknown, in Tucetona shell (as Pedunculus), which does not provide helpful information. However, a tissue preparation of the type DT2538 at the Paris Museum was marked ‘Indian Ocean’ (C. Schönberg pers. obs. 2006–2007) | No other primary records found for this bioregion. CS: The species could possibly occur in this bioregion, but we were unable to confirm the exact type location and could not consider this species in our biogeographic analysis. Other records were from the Mediterranean (e.g. Pulitzer-Finali 1983, as Cliona cretensis, in calcareous rock; Rosell and Uriz 2002b, Ponti et al. 2011) |
Cliothosa hancocki | (Topsent, 1888) | French Polynesia | Topsent (1888, also as Cliona quadrata, does not state exact sample site, in Tridacna sp.), Vacelet et al. (1976), Thomas (1979a), Pulitzer-Finali (1993); CS regards this name as a species complex that needs to be resolved per respective bioregion. It is here still counted as a species distinct from others occurring in this region |
(Unconf.: Cliothosa quadrata) | (Hancock, 1849) | In the giant clam, Tridacna gigas, which occurs in the Indo-Pacific | CS: After accessing Topsent’s samples at the Paris Museum (2006–2007), CS regards Cliothosa hancocki as a species complex. Cliothosa hancocki and Cliothosa quadrata are very similar (e.g. Calcinai et al. 2005) but have not yet been formally compared. To avoid possible duplication only Cliothosa hancocki was counted for our biogeographic analysis (more commonly used name), despite records from the area under the name Cliothosa quadrata (see entries above) |
Cornulella amirantensis | Van Soest et al., 1994 | Seychelles | No other primary records found |
Cornulella lundbecki | Dendy, 1922 | Seychelles | Van Soest et al. (1994) |
Cornulella minima | (Vacelet et al., 1976) | Madagascar | Van Soest et al. (1994) |
(Unconf.: Cornulella purpurea) | (Hancock, 1849) | Unknown, sample found in Tridacna gigas, which has an Indo-Pacific distribution | Referring to Hancock’s sample and thus not reporting a confirmed sample site: Kirkpatrick (1900a, as Dyscliona), Topsent (1907, as undetermined genus), Hallmann (1920, as Paracornulum), Rützler and Stone (1986, as Cliona), van Soest et al. (1994); CS: It is possible that Cornulella purpurea occurs in this bioregion, but as the sample site is unknown and cannot be conclusively matched to our bioregions, this species did not become part of our analysis |
Cornulella tyro | Van Soest et al., 1994 | Seychelles | No other primary records found |
Diplastrella gardineri | Topsent, 1918 | Maldives | |
Pione carpenteri | (Hancock, 1867) | Mazatlán | Thomas (1979a, 1981), Calcinai et al. (2000); CS: Pione species are difficult to identify, but as the three species reported for this bioregion have different spicule dimensions, they were all counted |
Pione margaritiferae | (Dendy, 1905) | Gulf of Mannar | ? Vacelet and Vasseur (1971); CS: But no tylostyles were recovered, and the displayed microscleres represent a mix of Pione microrhabds and non-Pione spirasters); Thomas (1979a, 1981) |
Pione aff. vastifica | Unresolved species complex | Sensu stricto: Scotland | Thomas (1973, 1979a, 1981, as Pione vastifica), Calcinai et al. (2000, as Pione vastifica); CS: Pione vastifica was originally reported from the Atlantic, and this may be a different species, but it is here counted as a third Pione species different from the other two in this bioregion |
Samus anonymus | Gray, 1867 | Brazil | Thomas (1973) |
Siphonodictyon minutum | (Thomas, 1972) | Sri Lanka | |
(Spheciospongia capensis) | (Carter, 1882) | Agulhas Bank | No other primary records found. CS: May not occur far enough north to be a coral reef sponge, was not counted for the biogeography |
Spheciospongia excentrica | (Burton, 1931) | Natal | Vacelet et al. (1976, as Spirastrella), Schleyer et al. (2006) |
Spheciospongia florida | (Von Lendenfeld, 1897) | Tanzania | |
Spheciospongia globularis | (Dendy, 1922) | Chagos | |
Spheciospongia inconstans | (Dendy, 1887) | Madras | Lévi (1961, as Spirastrella), Vacelet and Vasseur (1971, as Spirastrella), Thomas (1973, as Spirastrella), Vacelet et al. (1976, as Spirastrella), Thomas (1979a, 1981, as Spirastrella), Pulitzer-Finali (1993, as Spirastrella) |
Spheciospongia poterionides | (Vacelet and Vasseur, 1971) | Madagascar | No other primary records found |
Spheciospongia solida | (Ridley and Dendy, 1886) | Philippines | Barnes and Bell (2002, as Spirastrella) |
Spheciospongia transitoria: reversed comb. to Spirastrella transitoria | Ridley, 1884 | Seychelles | No other primary records found. CS: The original description places this species into the genus Spirastrella and clearly mentions the encrusting habit. The sponge has tylostyles and large, robust, conically spined spirasters and derivates. Based on these characters, the species is here returned to Spirastrella |
Spheciospongia vagabunda | (Ridley, 1884) | Torres Straits | Dendy (1922 as Spirastrella, including the varieties tubulodigitata and gelatinosa, the former being accepted as Spheciospongia vagabunda—van Soest et al. 2017), Lévi (1965a, as Spirastrella), Thomas (1973), Pulitzer-Finali (1993), Barnes and Bell (2002, as Spirastrella), Schleyer et al. (2006) |
Spirastrella cunctatrix | Schmidt, 1868 | Algeria, Mediterranean | ? Carter (1882, described either with purple colour or as ‘variety’ on a crab’s back), Vacelet and Vasseur (1971), Vacelet et al. (1976), Calcinai et al. (2000) |
Spirastrella decumbens | Ridley, 1884 | Torres Straits | |
Spirastrella pachyspira | Lévi, 1958 | E Red Sea, Saudi Arabia | Lévi (1961), Vacelet and Vasseur (1971), Vacelet et al. (1976), Thomas (1973), Barnes and Bell (2002) |
Spirastrella punctulata | Ridley, 1884 | Mozambique | No other primary records found |
(Unconf.: Thoosa cactoides) | Hancock, 1849 | In the pearl oyster, Pinctada margaritifera, which has an Indo-Pacific distribution | No other primary records found. CS: As we do not know the exact type location of this species, we did not count it for any specific bioregion |
(Unconf.: Thoosa circumflexa) | Topsent, 1891 | Unknown, sample found in Caen, on Tridacna sp., a genus which has an Indo-Pacific distribution | No other primary records found. CS: It is an Indo-Pacific sponge and may possibly occur in the Indian Ocean. According to van Soest et al. (2017), this is a taxon inquirendum, but after viewing Topsent’s samples in Paris (2006–2007), CS finds this to be a good species. As we cannot confirm the exact origin of Topsent’s sample, we did not include this species in our biogeographic analysis for the W Indian Ocean |
Thoosa cf. fischeri | Topsent, 1891 | Sri Lanka | ? Thomas (1973, as Thoosa armata); CS: Thoosa armata is an Atlantic species, and unlike the material of Thomas (1973), it does not have tylostyles. Given the spicule complement and the sampling area, Thomas’ material is likely Thoosa fischeri. It differs from Thoosa radiata (below) and was counted |
(Unconf.: Thoosa letellieri) | Topsent, 1891 | Unknown, sample found in Caen, on Tridacna sp., a genus which has an Indo-Pacific distribution | No other primary records found. CS: It is an Indo-Pacific sponge and may possibly occur in the Indian Ocean. According to van Soest et al. (2017), this is a taxon inquirendum, but after viewing Topsent’s samples in Paris (2006–2007), CS finds this to be a good species. As we cannot confirm the exact origin of Topsent’s sample, we did not include this species in our biogeographic analysis for the W Indian Ocean |
Thoosa radiata | Topsent, 1888 | Unknown, in Tridacna sp., a genus which has an Indo-Pacific distribution | Thomas (1981) |
Zyzzya fuliginosa | (Carter, 1879) | Torres Straits | Dendy (1922), Vacelet et al. (1976, as Paracornulum atoxa), Hooper and Krasochin (1989, as Zyzzya massalis), van Soest et al. (1994) |
India, Maldives, Laccadives, British Ocean T erritory and Andaman Islands (47 spp. of coral-eroding sponges in warm water) | |||
Alectona wallichii | (Carter, 1874) | Agulhas Bank, S of Africa (Carter: also from the ‘South Sea’ and Seychelles), first reported as spicules in sediment | ? Namboothri and Fernando (2012, as Alectona sp.), Sunil Kumar and Thomas (2012, 2015) |
Amorphinopsis excavans | Carter, 1887 | W Andaman Sea | Carter (1887), Annandale (1915a), Kumar (1925), Thomas (1972, 1979b, 1989), Venkataraman et al. (2007), Pattanayak (2009); CS: Amorphinopsis excavans is seen as an Indo-Pacific species, but characters described in different accounts vary, and the species (complex?) needs to be revised (Carvalho et al. 2004). Pattanayak lists three forms or varieties. This material needs to be re-examined to see whether they all belong to the same species. It was still counted as a separate species for the bioregion |
Aff. Cervicornia cuspidifera | Unresolved species complex | Sensu stricto: Caribbean Sea | Thomas (1972, 1979b, 1989, as Spirastrella), Venkataraman et al. (2007 as Spirastrella); CS: Cervicornia cuspidifera is a Caribbean species. Other endopsammic clionaids exist in the Indo-Pacific, and this account needs to be re-examined. It was still counted as a different species in the bioregion |
Cliona annulifera | Annandale, 1915a | Sri Lanka | |
Cliona aff. celata | Unresolved species complex | Sensu stricto: Scotland | Carter (1881, as Cliona warreni), Annandale (1915b, partly as Cliona warreni), Thomas (1972, 1979b, 1989), Venkataraman et al. (2007), Sunil Kumar and Thomas (2011), Namboothri and Fernando (2012), Sunil Kumar and Thomas (2015); CS: Cliona celata was described from Scotland and represents a taxonomically difficult species complex (Xavier et al. 2010, de Paula et al. 2012). All faunistic accounts are unreliable unless including molecular data. This report is unlikely to be Cliona celata sensu stricto but was still counted as a clionaid different from other species in the bioregion |
Cliona ensifera | Sollas, 1878 | Unknown, found in an octocoral (Isis sp.), which does not provide further information about the sample site. Assumed to be from the Indo-Pacific | Sollas (1878), Annandale (1915b), Thomas (1972, 1979b, 1989), Calcinai et al. (2000), Pattanayak (2006), Immanuel et al. (2015), Raghunathan (2015), Kiruba-Sankar et al. (2016) |
(Unconf.: Cliona insidiosa) | Hancock, 1849 | In the giant clam, Tridacna gigas, occurs in the Indo-Pacific | No other primary records found. CS: The sponge could possibly occur in this bioregion but was not observed since its description. As the exact type location is unknown, it was not included in the biogeographic analysis |
Cliona johnstonii | (Carter, 1886) | Bass Strait | Calcinai et al. (2000, as Cliona schmidti); CS: We tentatively listed all ‘Cliona schmidtii’ reported from the Indo-Pacific as Cliona johnstonii to imply that the two species are different. See van Soest et al. (2017) for comments on the distribution of Cliona schmidtii |
Cliona kempi | Annandale, 1915a | Andaman Islands | Thomas (1979b), Pattanayak (2006, 2009), Namboothri and Fernando (2012), Immanuel et al. (2015) |
Cliona aff. lobata | Unresolved species complex | Sensu stricto: English Channel | Thomas (1979b), Pattanayak (2006), Sunil Kumar and Thomas (2011), Namboothri and Fernando (2012), ? Sivaleela (2014), ? Kumar and Jogani (2014), ? Kumar and Shah (2014), Immanuel et al. (2015); CS: The Atlantic species Cliona lobata has been widely reported, but maybe not always accurately. These accounts have to be re-examined. The present record is possibly misidentified but is here counted as a morphologically different clionaid for the bioregion |
Cliona michelini | Topsent, 1888 | Indian Ocean, in shell of rock snail | Annandale (1915b); CS: The listing by Annandale is based on Topsent’s description. However, slide DX425 of Cliona michelini at the Paris Museum was marked ‘Bombay’ (C. Schönberg pers. obs. 2006–2007), suggesting that the species was found at least once in Indian waters |
Cliona mucronata | Sollas, 1878 | Unknown, found in an octocoral (Isis sp.), which does not provide further information about the sample site. Assumed to be from the Indo-Pacific | Annandale (1915a, b), Thomas (1972, 1979b, 1989), Calcinai et al. (2000), Pattanayak (2006), Bhagirathan et al. (2008), Namboothri and Fernando (2012), Immanuel et al. (2015) |
Cliona nodulosa | Calcinai et al., 2000 | Maldives | No other primary records found |
Cliona patera | (Hardwicke, 1820) | Singapore | Annandale (1915b) |
(Cliona subulata) | Sollas, 1878 | Unknown, but sympatric with Cliona ensifera and Cliona mucronata, thus assumed as Indo-Pacific | No other primary records found for this bioregion. CS: Cliona subulata has tylostyles and spirasters with long, discrete spines. Sollas’ drawings of the spicules suggest that the species belongs to the Cliona viridis complex, of which there are others in the area that cannot adequately be compared with Cliona subulata. Pending new results, we did not use this species in the biogeography to avoid possible duplication. Sollas’ type material needs to be re-examined |
(Unconf.: Cliona thoosina) | Topsent, 1888 | Unknown, in Tucetona shell (as Pedunculus), which does not provide helpful information. However, a tissue preparation of the type DT2538 at the Paris Museum was marked ‘Indian Ocean’ (C. Schönberg pers. obs. 2006–2007) | No other primary records found for this bioregion. CS: The species could possibly occur in this bioregion, but we were unable to confirm the exact type location and could not consider this species in our biogeographic analysis. Other records were from the Mediterranean (e.g. Pulitzer-Finali 1983, as Cliona cretensis, in calcareous rock; Rosell and Uriz 2002a; Ponti et al. 2011) |
Cliona aff. viridis sp. 1 (aff. cuspidifera?) Cliona aff. viridis sp. 2 (aff. orientalis?) | Unresolved species complex | Sensu stricto: Adriatic Sea, Mediterranean | Carter (1887, as Suberites coronarius), Dendy (1916, as Cliona coronaria), Annandale (1915b, as Cliona viridis and Cliona orientalis), Kumar (1925, as Cliona viridis), Thomas (1972, 1979b, 1989, as Cliona viridis and Cliona orientalis), Calcinai et al. (2000, as Cliona orientalis and Spheciospongia varians?), Namboothri and Fernando (2012), Immanuel et al. (2015, as Cliona varians), Raghunathan (2015, as Cliona varians), Kiruba-Sankar et al. (2016, as Cliona varians); CS: The group is taxonomically difficult, and there are several species that may possibly occur (e.g. Cliona albimarginata, Cliona orientalis as common ones). As some of the authors listed two separate species in their publications, two species were counted, but local material will need to be investigated with molecular means |
Cliothosa aurivillii | (Lindgren, 1897) | Java Sea | Thomas (1972, 1989, as Spirastrella), Venkataraman et al. (2007, as Spirastrella), Namboothri and Fernando (2012) |
Cliothosa dichotoma | (Calcinai et al., 2000) | Maldives | Calcinai et al. (2000) |
Cliothosa hancocki | (Topsent, 1888) | French Polynesia | Topsent (1888, as Cliona quadrata), Annandale (1915a, as Thoosa hancocci and Cliona quadrata, 1915b, as Thoosa), Thomas (1972, as Cliona quadrata, 1979b, as Thoosa), Pattanayak (2006, partly as Cliona quadrata), Sivaleela (2014, as Cliothosa quadrata), Sunil Kumar and Thomas (2015), Immanuel et al. (2015, partly as Cliothosa quadrata); CS regards this name as a species complex that needs to be resolved per respective bioregion. It is here counted as one species distinct from the others occurring in this region |
(Cliothosa quadrata) | (Hancock, 1849) | In the giant clam, Tridacna gigas, occurs in the Indo-Pacific | CS: After accessing Topsent’s samples at the Paris Museum (2006–2007), CS regards Cliothosa hancocki as a species complex. Cliothosa hancocki and Cliothosa quadrata are very similar (e.g. Calcinai et al. 2005) but have not yet been formally compared. To avoid possible duplication, only Cliothosa hancocki was counted for our biogeographic analysis, despite records from India under the name Cliothosa quadrata (see entries above) |
(Unconf.: Cornulella purpurea) | (Hancock, 1849) | Unknown, sample found in Tridacna gigas, which has an Indo-Pacific distribution | Referring to Hancock’s sample and thus not reporting a confirmed sample site: Kirkpatrick (1900a, as Dyscliona), Topsent (1907, as undetermined genus), Hallmann (1920, as Paracornulum), Rützler and Stone (1986, as Cliona), van Soest et al. (1994); CS: It is possible that Cornulella purpurea occurs in this bioregion, but as the sample site is unknown and cannot be conclusively matched to our bioregions, this species did not become part of our analysis. |
(Delectona higgini) | (Carter, 1880) | Sri Lanka | Thomas (1972, 1979b); CS: But Thomas apparently referred to Carter’s account or sample, did not state a sampling depth either and reported coralline algae as substrate. The three other Delectona spp. occur in deep water. As this sponge may not occur in shallow water, it was not included in the biogeographic analysis related to warm-water corals |
Dercitus (Stoeba) simplex | (Carter, 1880) | Sri Lanka | Sollas (1888a), ? Annandale (1915a, as Stoeba plicata), ? Calcinai et al. (2000 as Dercitus plicatus), van Soest et al. (2010), Immanuel et al. (2015); CS: Reports outside the Mediterranean are unlikely to be Dercitus (Stoeba) plicatus (see e.g. van Soest et al. 2010). The species was tentatively included here as one species of Dercitus |
(Dotona pulchella) | Carter, 1880 | Sri Lanka | Thomas (1972, 1979b); CS: But Thomas’ account seems to rely on other people’s samples, which were largely from deep water (see below). The present record was not included into the warm-water analysis |
Pione carpenteri | (Hancock, 1867) | Mazatlán | Carter (1887, as Cliona bacillifera), Topsent (1888, as Cliona), Annandale (1915a, b, as Cliona), Thomas (1979b, 1989, as Cliona), Calcinai et al. (2000), Immanuel et al. (2015), Sunil Kumar and Thomas (2015); CS: This may not be Pione carpenteri, but it represents the local Pione species with straight, spindle-shaped microrhabds |
(Unconf.: Pione fryeri) | (Hancock, 1849) | Unknown. Was found in window pane oyster, Placuna placenta, which occurs between the Gulf of Aden and the Philippines | No other primary records found. CS: This species could potentially occur in the bioregion, but as we do not know the exact sample site, we could not conclusively assign it to any one of our bioregions. Placuna placenta is commercially very important in the Philippines, and we tentatively assumed that the sample was from there and counted Pione fryeri only for the Coral Triangle |
Pione indica: recommendation to reassess genus allocation | (Topsent, 1891) | Sri Lanka | Annandale (1915b, as Cliona), (Thomas 1979b, as Cliona); CS saw a slide of the type material in Paris (2006–2007). The species shares Pione and Cliona characters: Pro-Pione characters are that the tylostyles are always very straight and that the sponge contains acanthose microrhabds (spirasters?). Pro-Cliona characters are that the tylostyles are always robust, the tyles contain occasional vesicles, and there are no oxeas. This species may be close to the Cliona lobata group? The species was found in a pearl oyster shell and was thus assumed to be from shallow water |
Pione margaritiferae | (Dendy, 1905) | Sri Lanka | Annandale (1915b, as Cliona), Thomas (1972, 1979b, as Cliona), Venkataraman et al. (2007 as Cliona), Sunil Kumar and Thomas (2011, 2015); CS: This has been described from the bioregion and represents the local Pione with helical microrhabds |
Pione aff. vastifica | Unresolved species complex | Sensu stricto: Scotland | Annandale (1915b, c, as Cliona), Thomas (1972, 1979b, 1989, as Cliona), Pattanayak (2006 as Cliona), Venkataraman et al. (2007 as Cliona), Sunil Kumar and Thomas (2011), Namboothri and Fernando (2012), Immanuel et al. (2015), Sunil Kumar and Thomas (2015) |
Samus anonymus | Gray, 1867 | Brazil | |
Siphonodictyon diagonoxeum | (Thomas, 1968a) | Sri Lanka | |
Siphonodictyon maldiviense | Calcinai et al., 2000 | Maldives | Calcinai et al. (2007b) |
Siphonodictyon minutum | (Thomas, 1972) | Sri Lanka | Thomas (1972, 1979b, 1989, as Aka), Pattanayak (2009, as Aka), Sunil Kumar and Thomas (2015) |
Siphonodictyon mucosum | Bergquist, 1965 | Palau | Namboothri and Fernando (2012, as Aka) |
(Siphonodictyon laccadiviense) taxon inquirendum | (Thomas, 1989) | Laccadives | No other primary records found. CS: This name has been synonymised with Zyzzya fuliginosa (van Soest et al. 2017), but it is here assumed that Thomas really meant a Siphonodictyon species. However, we were unable to find a formal description or to locate any type material (which is supposed to exist at the Calcutta Museum, P. Thomas pers. comm. 2012). At this stage we cannot adequately avoid possible species duplication and ignored this name |
Spheciospongia florida | (Von Lendenfeld, 1897) | Zanzibar | Kumar (1925, as Spirastrella) |
Spheciospongia globularis | (Dendy, 1922) | Chagos | Dendy (1922, as Spirastrella) |
Spheciospongia inconstans | (Dendy, 1887) | Madras | Dendy (1887, as Suberites, 1922), Thomas (1972, 1979b, 1989, as Spirastrella), Calcinai et al. (2000), Pattanayak (2006), Venkataraman et al. (2007, as Spirastrella), Sivaleela (2014), Immanuel et al. (2015) |
Spheciospongia tentorioides | (Dendy, 1905) | Sri Lanka | No other primary records found |
Spheciospongia vagabunda | (Ridley, 1884) | Torres Straits | Carter (1887, as Spirastrella trincomaliensis), Dendy (1905, as Spirastrella), Dendy (1916, as Spirastrella vagabunda var. tubulodigitata), Dendy (1922, as Spirastrella and the varieties tubulodigitata and gelatinosa), Immanuel et al. (2015), Raghunathan (2015), Kiruba-Sankar et al. (2016, as Spirastrella) |
Spirastrella andamanensis | Pattanayak, 2006 | Andaman Islands | |
(Spirastrella aff. coccinea) | Unresolved species complex | Sensu stricto: Caribbean | Thomas (1989), Venkataraman et al. (2007); CS: See comments for Spirastrella aff. cunctatrix |
Spirastrella aff. cunctatrix (sabogae?) | Unresolved species complex | Sensu stricto: Algeria, Mediterranean | Carter (1887), Immanuel et al. (2015), Raghunathan (2015), Kiruba-Sankar et al. (2016); CS: Related records require confirmation. See Boury-Esnault et al. (1999) for the distribution of similar Spirastrella spp. Spirastrella coccinea and Spirastrella cunctatrix are morphologically very similar. To avoid possible duplication, we excluded one of the locally unexpected species from our analyses. We assumed that the more likely species to occur might be Spirastrella cunctatrix, possibly introduced to the Indo-Pacific via the Suez Canal. Alternatively, this could be Spirastrella sabogae |
Timea curvistellifera: genus transfer to Spirastrella curvistellifera new comb. | (Dendy, 1905) | Sri Lanka | No other primary records found. CS: Timea curvistellifera is transferred into Spirastrella, because according to the original description, it is a thinly encrusting sponge that has no asters as typical for Timea but an ectosomal crust of spirasters with robust, conical spines either terminally arranged or following the convex sides of the axis, which is congruent with Spirastrella |
Spirastrella pachyspira | Lévi, 1958 | E Red Sea, Saudi Arabia | Thomas (1968), ? Kumar and Jogani (2014), ? Kumar and Shah (2014) |
Spirastrella punctulata | Ridley, 1884 | Mozambique | Kumar (1925) |
Spiroxya acustella | (Annandale, 1915b) | Bay of Bengal | Thomas (1979b, as Donotella), Pattanayak (2009, as Cliona); CS: Reported from shallow water |
Spiroxya levispira | (Topsent, 1898) | Acores | Calcinai et al. (2000); CS: Reported from shallow water |
Thoosa armata | Topsent, 1888 | Gulf of Guinea | Annandale (1915b), Thomas (1979b, 1989), Sunil Kumar and Thomas (2015) |
Thoosa bulbosa | Hancock, 1849 | In the giant clam, Tridacna gigas, occurs in the Indo-Pacific | |
(Unconf.: Thoosa cactoides) | Hancock, 1849 | In the pearl oyster, Pinctada margaritifera, which has an Indo-Pacific distribution | No other primary records found. CS: As we do not know the exact type location of this species, we did not count it for any specific bioregion |
(Unconf.: Thoosa circumflexa) | Topsent, 1891 | Unknown, sample found in Caen, on Tridacna sp., a genus which has an Indo-Pacific distribution | No other primary records found. CS: It is an Indo-Pacific sponge and may possibly occur in the Indian Ocean. According to van Soest et al. (2017), this is a taxon inquirendum, but after viewing Topsent’s samples in Paris (2006–2007), CS finds this to be a good species. As we cannot confirm the exact origin of Topsent’s sample, we did not include this species in our biogeographic analysis for Indian sites |
Thoosa fischeri | Topsent, 1891 | Sri Lanka | Thomas (1979b) |
Thoosa laeviaster | Annandale, 1915b | Myanmar | Thomas (1979b, as Annandalea) |
(Unconf.: Thoosa letellieri) | Topsent, 1891 | Unknown, sample found in Caen, on Tridacna sp., a genus which has an Indo-Pacific distribution | No other primary records found. CS: It is an Indo-Pacific sponge and may possibly occur in the Indian Ocean. According to van Soest et al. (2017), this is a taxon inquirendum, but after viewing Topsent’s samples in Paris (2006–2007), CS finds this to be a good species. As we cannot confirm the exact origin of Topsent’s sample, we did not include this species in our biogeographic analysis for Indian sites |
(Unconf.: Thoosa radiata) | Topsent, 1888 | Unknown, in Tridacna sp., a genus which has an Indo-Pacific distribution | No other primary records found. CS: This Indo-Pacific sponge might occur in the Indian Ocean. However, as we cannot confirm the exact type location, we did not include this species in our biogeographic analysis for Indian sites |
Thoosa socialis | Carter, 1880 | Gulf of Mannar | |
Zyzzya fuliginosa | (Carter, 1879) | Torres Straits | Dendy (1922, as Lissodendoryx massalis), Thomas (1981, 1989, partly as Damirina laccadiviensis), van Soest et al. (1994), Calcinai et al. (2000) |
Zyzzya papillata | (Thomas, 1968a) | Sri Lanka | Van Soest et al. (1994) |
NW Australia, Cocos and Christmas Islands (3 5 spp. of coral-eroding sponges in warm water) | |||
Cliona caesia | (Schönberg, 2000) | Central Great Barrier Reef | C. Schönberg pers. obs. (2012, Ningaloo) |
Cliona aff. celata | Unresolved species complex | Sensu stricto: Scotland | Hentschel (1909), Schönberg and Fromont (2012), Fromont and Sampey (2014); CS: Cliona celata was described from Scotland and represents a taxonomically difficult species complex (Xavier et al. 2010, de Paula et al. 2012). All faunistic accounts are unreliable unless including molecular data. This report is unlikely to be Cliona celata sensu stricto but was still counted as a clionaid different from others in the bioregion |
Cliona dissimilis | Ridley and Dendy, 1886 | Arafura Sea | |
Cliona ensifera | Sollas, 1878 | Unknown, found in an octocoral (Isis sp.), which does not provide further information about the sample site. Assumed to be from the Indo-Pacific | C. Schönberg pers. obs. (2012, Ningaloo) |
(Unconf.: Cliona insidiosa) | Hancock, 1849 | In the giant clam, Tridacna gigas, occurs in the Indo-Pacific | No other primary records found. CS: The sponge could possibly occur in this bioregion but was not noted since its description. As the exact type location is unknown, it was not included in the biogeographic analysis |
Unconf.: Cliona johannae | Topsent, 1932 | W Australia. But reported from the red abalone, Haliotis rufescens, which occurs in the E Pacific, Oregon to Baja California | No other primary records found. CS: This species has been published as being from Western Australia (sometimes: Shark Bay). However, in that case, the host material must have been misidentified, as it has an E Pacific distribution. We presently rely on the published statement for the type location. W Australian abalone spp. do not extend into Shark Bay, and it may even be a sample from further south than always assumed |
(Unconf.: Cliona michelini) | Topsent, 1888 | Indian Ocean, in shell of rock snail | No other primary records found for this bioregion. CS: This species may occur in the bioregion, but as the exact sample origin is unknown, it was not included here. Based on notes on a slide preparation, Cliona michelini was listed for India, however |
Cliona minuscula | Schönberg et al., 2006 | Central Great Barrier Reef | C. Schönberg pers. obs. (2012, Ningaloo) |
Cliona mucronata | Sollas, 1878 | Unknown, found in an octocoral (Isis sp.), which does not provide further information about the sample site. Assumed to be from the Indo-Pacific | C. Schönberg pers. obs. (2012, Ningaloo) |
Cliona orientalis | Thiele, 1900 | Molucca Sea, Indonesia | C. Schönberg pers. obs. (2012, Kimberley, Ningaloo); ? Schönberg and Fromont (2012), Fromont and Sampey (2014) |
(Cliona subulata) | Sollas, 1878 | Unknown, but sympatric with Cliona ensifera and Cliona mucronata, thus assumed as Indo-Pacific | No other primary records found for this bioregion. CS: Cliona subulata has tylostyles and spirasters with long, discrete spines. Sollas’ drawings of the spicules suggest that the species belongs to the Cliona viridis complex, of which there are others in the area that cannot adequately be compared with Cliona subulata. Pending new results, we did not use this species in the biogeography to avoid possible duplication. Sollas’ type material needs to be re-examined |
(Unconf.: Cliona thoosina) | Topsent, 1888 | Unknown, in Tucetona shell (as Pedunculus), which is not helpful information. A tissue preparation of the type DT2538 at the Paris Museum was marked ‘Indian Ocean’ (C. Schönberg pers. obs. 2006) | No other primary records found for this bioregion. CS: The species could possibly occur in this bioregion, but we were unable to confirm the exact type location and could not consider this species in our biogeographic analysis. Other records were from the Mediterranean (e.g. Pulitzer-Finali 1993, as Cliona cretensis, in calcareous rock; Rosell and Uriz 2002b; Ponti et al. 2011) |
Cliona cf. tinctoria | Schönberg, 2000 | Central Great Barrier Reef | |
Cliona vermifera | Hancock, 1867 | Unknown. In Chama sp., information which does not provide further clues | C. Schönberg pers. obs. (2012, Ningaloo); CS: Cliona vermifera is thought to be a species complex (see e.g. León-Pech et al. 2015), but pending new results is here treated as a single species |
(Cliona spp. undetermined) | Not formally described | Reported from NW Australia | Fromont and Sampey (2014, as Cliona sp. 8, sp. 17, sp. K1, sp. NW1); CS: Apart from Cliona celata, Cliona dissimilis, Cliona orientalis and Cliona tinctoria, the authors reported four other Cliona spp. as OTUs. As we cannot presently match these against the other listed Cliona spp., we did not count them for the biogeographic analysis |
(Unconf.: Cornulella purpurea) | (Hancock, 1849) | Unknown, sample found in Tridacna gigas, which has an Indo-Pacific distribution | Referring to Hancock’s sample and thus not reporting a confirmed sample site: Kirkpatrick (1900a, as Dyscliona), Topsent (1907, as undetermined genus), Hallmann (1920, as Paracornulum), Rützler and Stone (1986, as Cliona), van Soest et al. (1994); CS: It is possible that Cornulella purpurea occurs in this bioregion, but as the sample site is unknown and cannot be conclusively matched to our bioregions, this species did not become part of our analysis |
Dercitus (Stoeba) occultus | Hentschel, 1909 | Shark Bay | Van Soest et al. (2010) |
Pione carpenteri | (Hancock, 1867) | Mazatlán | Hentschel (1909, as Cliona carpenteri var. gracilis), Hooper and Wiedenmayer (1994, as Cliona); CS: The genus Pione is taxonomically difficult. However, as Hentschel distinguished four Pione spp. in the same publication, we accept that they were different from each other |
(Unconf.: Pione fryeri) | (Hancock, 1849) | Unknown. Was found in window pane oyster, Placuna placenta, which occurs between the Gulf of Aden and the Philippines | No other primary records found. CS: This species could potentially occur in the bioregion, but as we do not know the exact sample site, we could not conclusively assign it to any one of our bioregions. Placuna placenta is commercially very important in the Philippines, and we tentatively assumed that the sample was from there and counted Pione fryeri only for the Coral Triangle |
Pione aff. lampa | Unresolved species complex | Sensu stricto: Bermuda | Fromont and Sampey (2014, as Pione lampa); CS: This record needs to be revisited; Pione lampa has not yet been recorded from anywhere apart from the Caribbean. As another species known to grow in encrusting morphology—Pione velans—was listed in the same publication, this one was accepted as different and different from the papillate Pione spp. listed by Hentschel (1909) |
Pione margaritiferae | (Dendy, 1905) | Gulf of Mannar | Hentschel (1909, as Cliona), Hooper and Wiedenmayer (1994, as Cliona) |
Pione aff. vastifica | Unresolved species complex | Sensu stricto: Scotland | Hentschel (1909, as Cliona vastifica) |
Pione velans | (Hentschel, 1909) | Shark Bay | Hooper and Wiedenmayer (1994, as Cliona), Fromont et al. (2005), Fromont and Sampey (2014) |
(Pione spp. undetermined) | Not formally described | Reported from NW Australia | Fromont and Sampey (2014, as Pione sp. 2781, sp. 2782); CS: Apart from Pione lampa and Pione velans, the authors reported two other Pione spp. as OTUs. As we cannot presently match these against the other listed Pione spp., we did not count them for the biogeographic analysis |
Siphonodictyon minutum | (Thomas, 1972) | Sri Lanka | C. Schönberg pers. obs. (2012, Ningaloo) |
Siphonodictyon mucosum | Bergquist, 1965 | Palau | Fromont and Sampey (2014) |
Siphonodictyon paratypicum | (Fromont, 1993) | Central Great Barrier Reef | Fromont and Sampey (2014); CS: This species is similar to Siphonodictyon maldiviense, and this record needs reassessment. However, it represents a different species from the other ones in the bioregion and was counted |
7 Siphonodictyon spp. undetermined | Not formally described | Reported from NW Australia | Schönberg and Fromont (2012, as 10 Siphonodictyon spp.), Fromont and Sampey (2014, as 6 Siphonodictyon spp.); CS: We counted seven of these species in addition to the identified species, because without reassessing the material, we could not rule out species duplication |
Spheciospongia digitata | (Hentschel, 1909) | Shark Bay | Hooper and Wiedenmayer (1994, as Spirastrella) |
Spheciospongia papillosa | (Ridley and Dendy, 1886) | Sydney Harbour, Australia | Schönberg and Fromont (2012, as ‘cf.’), Fromont and Sampey (2014); CS: This species is better known from colder water (e.g. Dendy 1897), but according to the authors, it occurred on northwestern Australian reefs and was counted for the NW Australian biogeography |
Spheciospongia purpurea | (De Lamarck, 1815) | Bass Strait | Carter (1882, as Alcyonium purpureum), Topsent (1933, as Spirastrella), Hooper and Wiedenmayer (1994, as Spirastrella); CS: The sponge is best known from southwestern Australia, but it has been sampled as far north as the Abrolhos Islands and was counted (C. Schönberg pers. obs. 2015, accessing samples of the Western Australian Museum) |
Spheciospongia tentorioides | (Dendy, 1905) | Sri Lanka | Hentschel (1909, as Spirastrella tentorioides var. australis), Hooper and Wiedenmayer (1994, as Spirastrella) |
Spheciospongia vagabunda | (Ridley, 1884) | Torres Straits | Dendy and Frederick (1924, as Spirastrella), Hooper and Wiedenmayer (1994, as Spirastrella), Schönberg and Fromont (2012, as ‘cf.’), Fromont and Sampey (2014) |
(Spheciospongia spp. undetermined) | Not formally described | Reported from NW Australia | Schönberg and Fromont (2012), Fromont and Sampey (2014); CS: Not fully identified Spheciospongia spp. could not be adequately be compared to other Spheciospongia spp. in our data table. We did not count them for the biogeographic analysis |
(Spirastrella sp. undetermined) | Not formally described | Reported from the Kimberley | Fromont and Sampey (2014, as Spirastrella WA1); CS: As this species could not adequately be compared with the record of Spirastrella decumbens, it was here ignored to avoid duplication |
Spirastrella decumbens | Ridley, 1884 | Torres Straits | Kirkpatrick (1900b), ? Hentschel (1909, as Spirastrella cunctatrix), Hooper and Wiedenmayer (1994) |
(Unconf.: Thoosa cactoides) | Hancock, 1849 | In the pearl oyster, Pinctada margaritifera, which has an Indo-Pacific distribution | No other primary records found. CS: As we do not know the exact type location of this species, we did not count it for any specific bioregion |
(Unconf.: Thoosa circumflexa) | Topsent, 1891 | Unknown, sample found in Caen, on Tridacna sp., a genus which has an Indo-Pacific distribution | No other primary records found. CS: This Indo-Pacific sponge might occur in the Indian Ocean. According to van Soest et al. (2017), this is a taxon inquirendum, but after viewing Topsent’s samples in Paris (2006–2007), CS finds this to be a good species. Without the exact type location, we did not include this species in our biogeographic analysis for the NW Australia |
(Unconf.: Thoosa letellieri) | Topsent, 1891 | Unknown, sample found in Caen, on Tridacna sp., a genus which has an Indo-Pacific distribution | No other primary records found. CS: This Indo-Pacific sponge might occur in the Indian Ocean. Taxon inquirendum (van Soest et al. 2017), but after viewing Topsent’s samples in Paris (2006–2007), CS finds this to be a good species. Without the exact type location, we did not use this species here |
(Unconf.: Thoosa radiata) | Topsent, 1888 | Unknown, in Tridacna sp., a genus which has an Indo-Pacific distribution | No other primary records found. CS: It is an Indo-Pacific sponge and may possibly occur in the Indian Ocean. However, as we cannot confirm the exact origin of Topsent’s sample, we did not include this species here |
Zyzzya cf. criceta | Schönberg, 2000 | Central GBR | Fromont and Sampey (2014) |
Zyzzya fuliginosa | (Carter, 1879) | Torres Straits | Hooper and Krasochin (1989, as Zyzzya massalis), Schönberg and Fromont (2012 as ‘aff.’), Fromont and Sampey (2014, as ‘cf.’), van Soest et al. (1994) |
Zyzzya sp. undetermined | Not formally described | From Carnarvon Shelf | Schönberg and Fromont (2012, as Zyzzya sp. 1) |
Coral Sea, including Great Barrier Reef (GBR), Arafura Sea, Papua New Guinea and New Caledonia (3 3 spp. of coral-eroding sponges in warm water) | |||
Aff. Cervicornia sp. | Not formally described | Observed on the central and southern GBR | C. Schönberg pers. obs. (2010–2014, endopsammic, zooxanthellate, with tylostyles and spirasters, agglutinating and incorporating particles); CS: This is at least one species, different from the other ones here listed |
Cliona caesia | (Schönberg, 2000) | Central GBR | Schönberg (2000, 2001a, as Pione), Schönberg et al. (2006), Hill et al. (2011), C. Schönberg pers. obs. (2014, southern GBR) |
Cliona aff. celata | Unresolved species complex | Sensu stricto: Scotland | ? Kelly-Borges and Vacelet (1998, as Cliona sp.), Schönberg (2000, 2001a), Schönberg et al. (2006), C. Schönberg pers. obs. (2014, southern GBR); CS: Cliona celata was described from Scotland and represents a taxonomically difficult species complex (Xavier et al. 2010, de Paula et al. 2012). All faunistic accounts are unreliable unless including molecular data. This report is unlikely Cliona celata sensu stricto but was still counted as a clionaid different from others. It may represent more than one species; some samples had raphides as well as tylostyles. Bioerosion traces differed with sample |
Cliona dissimilis | Ridley and Dendy, 1886 | Arafura Sea | Hooper and Wiedenmayer (1994) |
Cliona ensifera | Sollas, 1878 | Unknown, found in an octocoral (Isis sp.), which does not provide further information about the sample site. Assumed to be from the Indo-Pacific | Schönberg et al. (2006), Pica et al. (2012, depth unknown), C. Schönberg pers. obs. (2010–2014, central and southern GBR) |
(Unconf.: Cliona insidiosa) | Hancock, 1849 | In the giant clam, Tridacna gigas, occurs in the Indo-Pacific | No other primary records found. CS: The sponge could possibly occur in this bioregion but was not noted since its description. As the exact type location is unknown, it was not included in the biogeographic analysis |
Cliona johnstonii | (Carter, 1886) | Bass Strait | Schönberg et al. (2006, as Cliona cf. schmidti); CS: We tentatively listed all ‘Cliona schmidtii’ reported from the Indo-Pacific as Cliona johnstonii to imply that the two species are different. See van Soest et al. (2017) for comments on the distribution of Cliona schmidtii |
Cliona cf. jullieni | Topsent, 1891 | La Réunion | Kelly-Borges and Vacelet (1998), Hill et al. (2011), C. Schönberg pers. obs. (2010–2011, central GBR) |
Cliona minuscula | Schönberg et al., 2006 | Central GBR | Schönberg et al. (2006), C. Schönberg pers. obs. (2014, southern GBR) |
Cliona mucronata | Sollas, 1878 | Unknown, found in an octocoral (Isis sp.), which does not provide further information about the sample site. Assumed to be from the Indo-Pacific | Schönberg et al. (2006), C. Schönberg pers. obs. (2010–2014, central and southern GBR) |
Cliona aff. mucronata sensu Vacelet and Vasseur (1971) | Unresolved species complex | Sensu stricto: Unknown, likely Indo-Pacific | C. Schönberg pers. obs. (2011, central GBR) |
Cliona orientalis | Thiele, 1900 | Molucca Sea, Indonesia | Vacelet (1981), Kelly-Borges and Vacelet (1998), Schönberg (2000, 2001), Schönberg et al. (2006), Hill et al. (2011), Ramsby et al. (2017) |
Cliona tinctoria | Schönberg, 2000 | Central GBR | ? Carter (1882, as purple-coloured Spirastrella cunctatrix, for ‘Australia’), ? Pulitzer-Finali (1982, as Cliona carteri from Heron Island; CS observed Cliona tinctoria at Heron Island 2002–2004, a similar, but more likely species), Schönberg (2000), Schönberg et al. (2006) |
Cliona vermifera | Hancock, 1867 | Unknown. In Chama sp., information which does not provide further clues | Schönberg (2001a, as Bernatia), Schönberg et al. (2006), C. Schönberg pers. obs. (2010–2014, central and southern GBR); CS: Cliona vermifera is thought to be a species complex (see e.g. León-Pech et al. 2015), but pending new results is here treated as a single species |
Cliothosa aurivillii | (Lindgren, 1897) | Java Sea | Burton (1934, as Spirastrella), Hooper and Wiedenmayer (1994, as Spirastrella), Schönberg and Wisshak (2012) |
Cliothosa hancocki | (Topsent, 1888) | French Polynesia | Risk et al. (1995), Schönberg (2000, 2001a), C. Schönberg pers. obs. (2014, southern GBR); CS regards this name as a species complex that needs to be resolved per respective bioregion. It is here still counted as a species distinct from the others occurring in this region |
(Unconf.: Cliothosa quadrata) | Hancock, 1849 | In the giant clam, Tridacna gigas occurs in the Indo-Pacific | No record found for this bioregion. CS: After accessing Topsent’s samples at the Paris Museum (2006–2007), CS regards Cliothosa hancocki as a species complex. Cliothosa hancocki and Cliothosa quadrata are very similar (e.g. Calcinai et al. 2005). To avoid possible duplication, only Cliothosa hancocki was counted for our biogeographic analysis (more commonly used name) |
(Unconf.: Cornulella purpurea) | (Hancock, 1849) | Unknown, sample found in Tridacna gigas, which has an Indo-Pacific distribution | Referring to Hancock’s sample and thus not reporting a confirmed sample site: Kirkpatrick (1900a, as Dyscliona), Topsent (1907, as undetermined genus), Hallmann (1920, as Paracornulum), Rützler and Stone (1986, as Cliona), van Soest et al. (1994); CS: Cornulella purpurea might occur in the bioregion, but as the sample site is unknown and cannot be conclusively matched to our bioregions, this species did not become part of our analysis |
Cornulum virguliferum | (Lévi and Lévi, 1983) | New Caledonia | Van Soest et al. (1994) |
Pione aff. vastifica | Unresolved species complex | Sensu stricto: Scotland | Schönberg (2001); CS: Unlikely to be Pione vastifica sensu stricto, but counted as the only Pione species recorded in the bioregion |
Neamphius huxleyi | (Sollas, 1888) | Vanuatu | Díaz et al. (2007) |
(Unconf.: Siphonodictyon labyrinthicum) | (Hancock, 1849) | Unknown type location, but found in the giant clam, Tridacna gigas, which occurs in the Indo-Pacific | Pica et al. (2012, as Aka, likely New Caledonia, in Distichopora sp., but depth unknown); CS: Presently not counted |
Siphonodictyon minutum | (Thomas, 1972) | Sri Lanka | Schönberg et al. (2006) |
Siphonodictyon mucosum | Bergquist, 1965 | Micronesia | Kelly (1986), Kelly-Borges and Bergquist (1988), Fromont (1993, as Aka), Hooper and Wiedenmayer (1994, as Aka), Schönberg (2000, 2001, as Aka), Schönberg and Wisshak (2012, as Aka) |
Siphonodictyon paratypicum | (Fromont, 1993) | Central GBR | Hooper and Wiedenmayer (1994, as Aka), Schönberg and Tapanila (2006, as Aka) |
Siphonodictyon sp. yellow | Not formally described | Central GBR | C. Schönberg pers. obs. (2011, endopsammic, may or may not be conspecific with the species observed at the Marianas; see Kelly et al. 2003); CS: This record is different from the species known from the bioregion and was counted for the biogeography analysis |
Spheciospongia congenera | (Ridley, 1884) | Torres Straits | Hooper and Wiedenmayer (1994, as Spirastrella) |
Spheciospongia inconstans | (Dendy, 1887) | Madras | Burton (1934, as Spirastrella), Vacelet (1981, as Spirastrella), Hooper and Wiedenmayer (1994, as Spirastrella), Kelly-Borges and Vacelet (1998) |
Spheciospongia lacunosa | (Kieschnick, 1898) | Torres Straits | Hooper and Wiedenmayer (1994, as Spirastrella) |
(Spheciospongia purpurea) | (De Lamarck, 1815) | Bass Strait | ? Hentschel (1912); CS: Hentschel approached this species using a wide scope. It may not be Spheciospongia purpurea and likely represents more than one species. As we could not rule out duplication, we did not count it |
Spheciospongia ramulosa | (Von Lendenfeld, 1888) | Sydney Harbour | No other primary records found |
Spheciospongia semilunaris | (Lindgren, 1897) | Java Sea | Burton (1934, as Spirastrella), Hooper and Wiedenmayer (1994, as Spirastrella) |
Spheciospongia spiculifera | (Kieschnick, 1898) | Torres Straits | Hooper and Wiedenmayer (1994, as Spirastrella) |
Spheciospongia vagabunda | (Ridley, 1884) | Torres Straits | Bergquist and Tizard (1967, as Spirastrella), Kelly (1986, partly as Spheciospongia fungoides or Spheciospongia gallensis or Spheciospongia trincomaliensis), Kelly-Borges and Bergquist (1988), Kelly-Borges and Vacelet (1998), Sutcliffe et al. (2010) |
Spirastrella decumbens | Ridley, 1884 | Torres Straits | Hooper and Wiedenmayer (1994) |
(Unconf.: Thoosa cactoides) | Hancock, 1849 | In the pearl oyster, Pinctada margaritifera, which has an Indo-Pacific distribution | No other primary records found. CS: It is an Indo-Pacific sponge and may possibly occur in the Coral Sea. As we cannot confirm the exact origin of Hancock’s sample, however, we did not use it for this bioregion |
(Unconf.: Thoosa circumflexa) | Topsent, 1891 | Unknown, sample found in Caen, on Tridacna sp., a genus which has an Indo-Pacific distribution | No other primary records found. CS: It is an Indo-Pacific sponge and may possibly occur in the Coral Sea. As we cannot confirm the exact origin of Topsent’s sample, however, we did not use it for this bioregion |
(Unconf.: Thoosa letellieri) | Topsent, 1891 | Unknown, sample found in Caen, on Tridacna sp., a genus which has an Indo-Pacific distribution | No other primary records found. CS: It is an Indo-Pacific sponge and may possibly occur in the Coral Sea. As we cannot confirm the exact origin of Topsent’s sample, however, we did not use it for this bioregion |
(Unconf.: Thoosa radiata) | Topsent, 1888 | Unknown, in Tridacna sp., a genus which has an Indo-Pacific distribution | No other primary records found. CS: It is an Indo-Pacific sponge and may possibly occur in the Coral Sea. As we cannot confirm the exact origin of Topsent’s sample, however, we did not use it for this bioregion |
Thoosa sp. | Not yet formally described | Reported from the central GBR (C. Schönberg pers. obs. 2012) | No other primary records found. CS: At this stage, the material has only been identified to genus |
Zyzzya criceta | Schönberg, 2000 | Central Great Barrier Reef | Schönberg (2000, 2001a), ? Harper (2014, as Zyzzya fuliginosa), C. Schönberg pers. obs. (2014, on the southern GBR) |
Zyzzya fuliginosa | (Carter, 1879) | Torres Straits | Van Soest et al. (1994) |
Coral Triangle, including Indonesia, South China Sea, Taiwan, Gulf of Thailand, Singapore, Malaysia, Vietnam, the Philippines and Palau (4 3 spp. of coral-eroding sponges in warm water) | |||
Amorphinopsis excavans | Carter, 1887 | W Andaman Sea | Hooper et al. (2000), Azzini et al. (2007b), Lim et al. (2009, 2016); CS: Amorphinopsis excavans is seen as an Indo-Pacific species, but characters described in older accounts vary, and the species (complex?) needs to be re-examined and revised (Carvalho et al. 2004) |
Aff. Cervicornia cuspidifera | Unresolved species complex | Sensu stricto: Caribbean Sea | Hooper et al. (2000), Putchakarn (2007); CS: Cervicornia cuspidifera is a Caribbean species. Other endopsammic clionaids exist in the Indo-Pacific, and this account needs to be re-examined. It was still counted as different |
Cliona albimarginata | Calcinai et al., 2005 | N Sulawesi | ? Hooper et al. (2000, as Cliona cf. caroboea), Calcinai et al. (2005), Putchakarn (2007), Lim et al. (2016); CS: Cliona albimarginata and Cliona orientalis have both been recorded from this bioregion and are very similar |
Cliona aff. celata | Unresolved species complex | Sensu stricto: Scotland | Dawydoff (1952), ? van Soest (1990, as Cliona sp. orange), Hooper et al. (2000, as Cliona cf. celata), Calcinai et al. (2006), Azzini et al. (2007b), Chervyakova (2007), Lim et al. (2009, 2012, 2016); CS: Cliona celata was described from Scotland and represents a taxonomically difficult species complex (Xavier et al. 2010, de Paula et al. 2012a). All faunistic accounts are unreliable unless including molecular data. This report is unlikely to be Cliona celata sensu stricto but was still counted as a clionaid different from others in the bioregion |
(Cliona dissimilis) | Ridley and Dendy, 1886 | Arafura Sea | ? Lim et al. (2012a, as Cliona sp. ‘orange encrusting’); CS: This is not a confirmed record. To avoid possible duplication, we did not count it |
Cliona ensifera | Sollas, 1878 | Unknown, found in an octocoral (Isis sp.), which does not provide further information about the sample site. Assumed to be from the Indo-Pacific | Hooper et al. (2000) |
Cliona favus | Calcinai et al., 2005 | N Sulawesi | No other primary records found |
(Unconf.: Cliona insidiosa) | Hancock, 1849 | In the giant clam, Tridacna gigas, occurs in the Indo-Pacific | No other primary records found. CS: The sponge could possibly occur in this bioregion but was not noted since its description. As the exact type location is unknown, it was not included in the biogeographic analysis |
Cliona johnstonii | (Carter, 1886) | Bass Strait | De Laubenfels (1954), Hooper et al. (2000, as Cliona cf. schmidtii); CS: We tentatively listed all ‘Cliona schmidtii’ reported from the Indo-Pacific as Cliona johnstonii to imply that the two species are different. See van Soest et al. (2017) for comments on the distribution of Cliona schmidtii |
Cliona kempi | Annandale, 1915a | Andaman Islands | Hooper et al. (2000) |
Cliona liangae | Calcinai et al., 2005 | N Sulawesi | No other primary records found |
Cliona aff. lobata | Hancock, 1849 | English Channel | Hooper et al. (2000); CS: The Atlantic species Cliona lobata has been widely reported but maybe not always accurately. These accounts have to be re-examined. The present record is possibly misidentified but is here counted as a morphologically different clionaid for the bioregion |
Cliona mucronata | Sollas, 1878 | Unknown, found in an octocoral (Isis sp.), which does not provide further information about the sample site. Assumed to be from the Indo-Pacific | Dawydoff (1952), Desqueyroux-Faúndez (1981), Hooper et al. (2000), Calcinai et al. (2005), Lim et al. (2016) |
Cliona orientalis | Thiele, 1900 | Molucca Sea, Indonesia | Hooper et al. (2000), Calcinai et al. (2006), Azzini et al. (2007b), Lim et al. (2012a), Lim et al. (2016); CS: Cliona albimarginata and Cliona orientalis have both been recorded from this bioregion and are very similar |
Cliona patera | (Hardwicke, 1820) | Singapore | Schlegel (1857, as Spongia (Poterion) neptuni), Dawydoff (1952, as Poterion), Hooper et al. (2000, as Poterion neptuni), Lim et al. (2009, 2012a, 2012b), Low (2012), Lim et al. (2016) |
Cliona utricularis | (Calcinai et al., 2005) | N Sulawesi | |
(Cliona aff. viridis) | Unresolved species complex | Sensu stricto: Adriatic Sea, Mediterranean | Hooper et al. (2000, as Cliona cf. viridis); CS: Cliona viridis complex species are taxonomically difficult. This account is a tentative identification and would have incurred the risk of duplication. We did not count it |
Cliothosa aurivillii | (Lindgren, 1897) | Java Sea | Dawydoff (1952, as Spirastrella), Bergquist (1965), Hooper et al. (2000, as Spirastrella), ? Calcinai et al. (2006, as Cliona), ? Azzini et al. (2007b, as Cliona), Putchakarn (2011), Lim et al. (2016, listed as Cliona and Cliothosa), J. Marlow pers. comm. (2015, Celebes Sea); CS: The tylostyles in Calcinai et al. (2006) very much resemble those of Spheciospongia peleia. Azzini et al. (2007b) followed Calcinai et al.’s decision |
Cliothosa dichotoma | (Calcinai et al., 2000) | Maldives | Calcinai et al. (2005) |
Cliothosa hancocki | (Topsent, 1888) | French Polynesia | Lindgren (1898, as Thoosa), Dawydoff (1952, as Thoosa), Hooper et al. (2000, as Thoosa (Cliothosa) hancocki and Cliona quadrata), Calcinai et al. (2006), Azzini et al. (2007b), Chervyakova (2007, as Thoosa), Lim et al. (2016), J. Marlow pers. comm. (2016, Celebes Sea); CS regards this name as a species complex that needs to be resolved per respective bioregion. It is here still counted as a species distinct from the others occurring in this region |
(Cliothosa quadrata) | (Hancock, 1849) | In the giant clam, Tridacna gigas, occurs in the Indo-Pacific | CS: After accessing Topsent’s samples at the Paris Museum (2006–2007), CS regards Cliothosa hancocki as a species complex. Cliothosa hancocki and Cliothosa quadrata are very similar (e.g. Calcinai et al. 2005). To avoid possible duplication, only Cliothosa hancocki was counted (more commonly used name), even though Cliothosa quadrata was also recorded (see above) |
(Unconf.: Cornulella purpurea) | (Hancock, 1849) | Unknown, sample found in Tridacna gigas, which has an Indo-Pacific distribution | Referring to Hancock’s sample and thus not reporting a confirmed sample site: Kirkpatrick (1900a, as Dyscliona), Topsent (1907, as undetermined genus), Hallmann (1920, as Paracornulum), Rützler and Stone (1986, as Cliona), van Soest et al. (1994); CS: It is possible that Cornulella purpurea occurs in this bioregion, but as the sample site is unknown and cannot be conclusively matched to our bioregions, this species did not become part of our analysis |
(Dercitus (Stoeba) plicatus) | (Schmidt, 1868) | Algeria, Mediterranean | Sollas (1902, as Dercitus plicata), Hooper et al. (2000, as Dercitus plicatus); CS: Doubtful record. Was not counted for the biogeographic analysis |
Dercitus (Stoeba) simplex | (Carter, 1880) | Gulf of Mannar | |
(Diplastrella spiniglobata): recommendation to reassess genus allocation | (Carter, 1879) | ‘South Sea’ | Hooper et al. (2000); CS: The spicules depicted by Carter suggest that it is not a bioeroding sponge but it may be closer to a Placospongia. The species needs to be reassessed and was not counted |
Holoxea excavans | Calcinai et al., 2001 | Taiwan | Lim et al. (2016) |
Neamphius huxleyi | (Sollas, 1888) | Vanuatu | |
Pione carpenteri | (Hancock, 1867) | Mazatlán | Hooper et al. (2000, as Cliona and partly as Cliona bacillifera), Calcinai et al. (2006), Azzini et al. (2007b) |
Unconf.: Pione fryeri | (Hancock, 1849) | Unknown. Was found in window pane oyster, Placuna placenta, which occurs between the Gulf of Aden and the Philippines | No other primary records found. CS: This species might occur in the bioregion, but as we do not know the exact sample site, we could not assign it to any one of our bioregions. Placuna placenta is commercially very important in the Philippines, and we tentatively assumed that the sample was from there and counted Pione fryeri only for the Coral Triangle |
(Pione aff. vastifica) | Unresolved species complex | Sensu stricto: Scotland | Hooper et al. (2000, as Cliona); CS: This record could not adequately be verified and was not used for the biogeographic analysis |
Samus anonymus | Gray, 1867 | Brazil | |
Siphonodictyon maldiviense | Calcinai et al., 2000 | Maldives | Calcinai et al. (2007b), ? Putchakarn (2007, as Aka sp.), Lim et al. (2012a, 2016, as Aka) |
Siphonodictyon microterebrans | Calcinai et al., 2007b | N Sulawesi | No other primary records found |
Siphonodictyon mucosum | Bergquist, 1965 | Palau | Rützler (1971), Cerrano et al. (2002, as Aka), Hooper et al. (2000, as Aka), Calcinai et al. (2005, 2006, as Aka), Azzini et al. (2007b, as Aka), Putchakarn (2007, as Aka), de Voogd and Cleary (2009, as Aka), Lim et al. (2012a, as Aka), Becking et al. (2013), Lim et al. (2016) |
(Siphonodictyon sp. undetermined) | Not formally described | Reported from Singapore | Lim et al. (2012a, as Siphonodictyon sp. ‘white fistules soft’); CS: Conservatively, we treat this as a doubtful record and did not count it |
(Siphonodictyon sp. undetermined) | Not formally described | Reported from Vietnam | Chervyakova (2007, as Aka sp. – ‘yellow soft sponge’); CS: Possibly doubtful genus allocation? Conservatively not counted |
Spheciospongia areolata | (Dendy, 1897) | Port Phillip Bay, South Australia | Dawydoff (1952, as Spirastrella), Hooper et al. (2000, as Spirastrella), Lim et al. (2016) |
Spheciospongia carnosa | (Topsent, 1897) | Ambon, Banda Sea | Desqueyroux-Faúndez (1981, as Spirastrella), Hooper et al. (2000, as Spirastrella) |
Spheciospongia congenera | (Ridley, 1884) | Torres Straits | Putchakarn (2011) |
Spheciospongia inconstans | (Dendy, 1887) | Madras | Thiele (1899, as Spirastrella); Sollas (1902, as Spirastrella); Hooper et al. (2000, as Spirastrella); Lévi (1959b, as Spirastrella); Chervyakova (2007), Lim et al. (2016) |
Spheciospongia lacunosa | (Kieschnick, 1898) | Ternate | Kieschnick (1900, as Spirastrella), Dragnewitsch (1906, as Spirastrella), Hooper et al. (2000, as Spirastrella), Lim et al. (2016) |
Spheciospongia peleia | (De Laubenfels, 1954) | Palau | ? Calcinai et al. (2006, as Cliona aurivillii), ? Azzini et al. (2007b, as Cliona aurivillii), Becking et al. (2013) |
Spheciospongia purpurea | (De Lamarck, 1815) | Bass Strait | Hooper et al. (2000, as Spirastrella, including the taxon inquirendum Spirastrella purpurea glaebosa), Lim et al. (2016); CS: The sponge is best known from southwestern Australia, but it has been sampled as far north as the Abrolhos Islands and was tentatively counted (C. Schönberg pers. obs. 2015, accessing samples of the Western Australian Museum) |
Spheciospongia semilunaris | (Lindgren, 1897) | Java Sea | Hooper et al. (2000, as Spirastrella) |
Spheciospongia solida | (Ridley and Dendy, 1886) | Philippines | Topsent (1897, as Spirastrella), Lindgren (1898, as Spirastrella), Desqueyroux-Faúndez (1981, as Spirastrella), van Soest (1989, 1990, as Spirastrella), Hooper et al. (2000, as Spirastrella), Cerrano et al. (2002, as Spirastrella), Calcinai et al. (2006, as Spirastrella), Azzini et al. (2007b), Putchakarn (2007, 2011, as Spirastrella), Pica et al. (2012, as Spheciospongia cf. solida, enveloping and eroding basal parts of Stylaster sp.), Becking et al. (2013), Lim et al. (2016) |
Spheciospongia spiculifera | (Kieschnick, 1898) | Ambon | Kieschnick (1900, as Spirastrella), Hooper et al. (2000, as Spirastrella spiculifer) |
Spheciospongia tentorioides | (Dendy, 1905) | Sri Lanka | Calcinai et al. (2006, as Spirastrella), Azzini et al. (2007b), ? Li (2013, as Spheciospongia sp.), Lim et al. (2016) |
Spheciospongia vagabunda | (Ridley, 1884) | Torres Straits | Kieschnick (1896, as Spirastrella cylindrica), Thiele (1900, as Spirastrella cylindrica), Wilson (1925, as Spirastrella), de Laubenfels (1935, as Spirastrella), Bergquist (1965, as Spirastrella), van Soest (1989, 1990, as Spirastrella), Hooper et al. (2000, as Spirastrella, also as ‘cf.’ and Suberites trincomaliensis), Longakit et al. (2005), Chervyakova (2007), de Voogd and Cleary (2009), Lim et al. (2012a, as Spheciospongia cf. vagabunda), Becking et al. (2013), Hadi et al. (2016), Lim et al. (2016) |
(Spirastrella aff. coccinea) | Unresolved species complex | Sensu stricto: Caribbean | Hooper et al. (2000); CS: See comments for Spirastrella aff. cunctatrix |
Spirastrella aff. cunctatrix (sabogae?) | Unresolved species complex | Sensu stricto: Algeria, Mediterranean | Desqueyroux-Faúndez (1981), Hooper et al. (2000), Azzini et al. (2007b); CS: This record requires confirmation. See Boury-Esnault et al. (1999) about the distribution of similar Spirastrella spp. Spirastrella coccinea and Spirastrella cunctatrix are morphologically very similar. To avoid possible duplication, we excluded one of the locally unexpected species from our biogeographic analysis. We assumed that the more likely species to occur might be Spirastrella cunctatrix, which might have been introduced to the Indo-Pacific via the Suez Canal. Alternatively, this could be Spirastrella sabogae |
Spirastrella decumbens | Ridley, 1884 | Torres Straits | Topsent (1897), van Soest (1990), Hooper et al. (2000), Calcinai et al. (2006; sensu Kirkpatrick 1900a), Azzini et al. (2007b), Lim et al. (2012a, as Spirastrella decumbens var. robusta), Becking et al. (2013), Lim et al. (2016) |
Spirastrella pachyspira | Lévi, 1958 | E Red Sea, Saudi Arabia | Hooper et al. (2000) |
Spirastrella tristellata | Topsent, 1897 | Ambon | |
(Unconf.: Thoosa cactoides) | Hancock, 1849 | In the pearl oyster, Pinctada margaritifera, which has an Indo-Pacific distribution | No other primary records found. CS: As we do not know the exact type location of this species, we did not count it for any specific bioregion |
(Unconf.: Thoosa circumflexa) | Topsent, 1891 | Unknown, sample found in Caen, on Tridacna sp., a genus which has an Indo-Pacific distribution | No other primary records found. CS: It is an Indo-Pacific sponge and may possibly occur in the Coral Triangle. According to van Soest et al. (2017), this is a taxon inquirendum, but after viewing Topsent’s samples in Paris (2006–2007), CS finds this to be a good species. As we cannot confirm the exact origin of Topsent’s sample, we did not include this species here in our biogeographic analysis |
(Unconf.: Thoosa letellieri) | Topsent, 1891 | Unknown, sample found in Caen, on Tridacna sp., a genus which has an Indo-Pacific distribution | No other primary records found. CS: It is an Indo-Pacific sponge and may possibly occur in the Coral Triangle. According to van Soest et al. (2017), this is a taxon inquirendum, but after viewing Topsent’s samples in Paris (2006–2007), CS finds this to be a good species. As we cannot confirm the exact origin of Topsent’s sample, we did not include this species here |
(Unconf.: Thoosa radiata) | Topsent, 1888 | Unknown, in Tridacna sp., a genus which has an Indo-Pacific distribution | No other primary records found. CS: It is an Indo-Pacific sponge and may possibly occur in the Coral Triangle. However, as we cannot confirm the exact origin of Topsent’s sample, we did not include this species here |
Zyzzya criceta | Schönberg, 2000 | Central GBR | J. Marlow, pers. comm. (2016, Celebes Sea); CS: See also http://www.kudalaut.eu/en/dph/5483/Photos-Sale/Boring-sponge; http://www.kudalaut.eu/en/dph/4793/Photos-Sale/Sponge |
Japan , especially the Ryukyu Islands , Korea (18 spp. of coral-eroding sponges in warm water) – Y. Ise pers. comm. (2017) : Species identifications partly unconfirmed, need re-assessment | |||
Cliona cf. amplicavata | Rützler, 1974 | Bermuda | C. Schönberg pers. obs. (2004, Ryukyu Islands, preliminary identification only) |
(Cliona argus) (Cliona argus var. laevicollis) | Thiele, 1898 | Hakodate, Tsugaru Strait, in mollusc and brachiopod shells | No other primary records found. CS: The type location is cold temperate, and in addition, the variety was sampled from 140 m. Cliona argus was thus not included in the biogeographic analysis |
Cliona caesia | (Schönberg, 2000) | Central Great Barrier Reef | C. Schönberg pers. obs. (2004, Ryukyu Islands); Hill et al. (2011) |
Cliona aff. celata | Unresolved species complex | Sensu stricto: Scotland | Hoshino (1981), Hoshino (1987), C. Schönberg pers. obs. (2004, Ryukyu Islands); CS: Cliona celata was described from Scotland and represents a taxonomically difficult species complex (Xavier et al. 2010, de Paula et al. 2012). All faunistic accounts are unreliable unless including molecular data. This report is unlikely to be Cliona celata sensu stricto but was still counted as a clionaid different from others in the bioregion |
Cliona infrafoliata | (Thiele, 1898) | Hakodate, Tsugaru Strait, in mollusc and brachiopod shells | Hoshino (1981, as Suberites infrafoliatus), Tanita and Hoshino (1989, as Suberites infrafoliata); CS: The type location is cold temperate, but the sponge has later been recorded from Bingonada Sea, which has a mild, warm climate. Japanese waters are influenced by the Kuroshio Current, which supports corals further north than at some other places. The sponge was tentatively counted into the biogeographic analysis |
Cliona cf. minuscula | Schönberg et al., 2006 | Central Great Barrier Reef | C. Schönberg pers. obs. (2004, Ryukyu Islands) |
(Unconf.: Cliona orientalis) | Thiele, 1900 | Molucca Sea, Indonesia | C. Schönberg pers. obs. (2004, Ryukyu Islands), Schönberg et al. (2008); CS: Several characters of Cliona raromicrosclera, Cliona reticulata and Cliona orientalis are very similar. Cliona orientalis and Cliona reticulata have almost identical spicule dimensions, but in both, tylostyles are about 100 μm shorter than those of Cliona raromicrosclera. Pending a direct comparison, we avoided possible duplication of the same species; only Cliona raromicrosclera and Cliona reticulata were counted into the biogeography |
Cliona aff. raromicrosclera | Unresolved species complex | Sensu stricto: Gulf of California | Hoshino (1981, as Anthosigmella), Hoshino (1987), Tanita and Hoshino (1989, as Anthosigmella); CS & JLC: This might be an unlikely record for Japan and belongs to the taxonomically difficult Cliona viridis complex. For example, several characters of Cliona raromicrosclera and Cliona reticulata are very similar. However, as Cliona reticulata tylostyles are about 100 μm shorter than those of Cliona raromicrosclera, both species were tentatively counted |
Cliona reticulata | Ise and Fujita, 2005 | Ryukyu Islands | No other primary records found |
Cliothosa hancocki | (Topsent, 1888) | French Polynesia | C. Schönberg pers. obs. (2004, Ryukyu Islands); CS regards this name as a species complex that needs to be resolved per respective bioregion. It is here still counted as a species distinct from the others occurring in this region |
(Unconf.: Cornulella purpurea) | (Hancock, 1849) | Unknown, sample found in Tridacna gigas, which has an Indo-Pacific distribution | Referring to Hancock’s sample and thus not reporting a confirmed sample site: Kirkpatrick (1900a, as Dyscliona), Topsent (1907, as undetermined genus), Hallmann (1920, as Paracornulum), Rützler and Stone (1986, as Cliona), van Soest et al. (1994); CS: It is possible that Cornulella purpurea occurs in this bioregion, but as the sample site is unknown and cannot be conclusively matched to our bioregions, this species did not become part of our analysis |
(Pione concharum) | (Thiele, 1898) | Hakodate, Tsugaru Strait (maybe also Sagami Bay), in mollusc and brachiopod shells | No other primary records found. CS: The confirmed sampling area is cold temperate, and Pione concharum was thus conservatively excluded from the biogeographic analysis |
Pione aff. vastifica | Unresolved species complex | Sensu stricto: Scotland | Hoshino (1981, 1987, as Cliona); Schönberg pers. obs. (2004, Ryukyu Islands) |
Spheciospongia panis | (Thiele, 1898) | Sagami Bay | Hoshino (1976, 1977, 1982, 1987, as Spirastrella), Tanita and Hoshino (1989, as Spirastrella); CS: This is a massive species that was sampled from 51–80 m but was found as far south as subtropical Amami Oshima |
Spheciospongia peleia | (De Laubenfels, 1954) | Palau | Hoshino (1981, as Ridleya); CS: Recorded from Ishigaki Island that is described as semi-tropical and counted. Ise et al. (2004) synonymised Spheciospongia peleia with Spheciospongia vagabunda (or inconstans), a decision that is not here followed |
(Spheciospongia rotunda) | (Tanita and Hoshino, 1989) | Sagami Bay | Tanita and Hoshino (1989, as Spirastrella); CS: This is a massive species that was sampled from 80–90 m and was conservatively excluded from the biogeographic analysis |
Unconf.: Spheciospongia cf. vagabunda | (Ridley, 1884) | Torres Straits | ? Ise et al. (2004, as Spheciospongia inconstans) |
Spheciospongia sp. undetermined | Presently not adequately resolved | Reported from various sites in Japan | Hoshino (1977, 1981, 1987 as Cliona lobata); CS: Reported from Kii Channel, but apparently inconsistent with the original description for Cliona lobata. This is a massive sponge with exceptionally fine spirasters that does not match any of the other Japanese Spheciospongia species and was counted for the biogeographic analysis as an undetermined clionaid |
Spirastrella abata | Tanita, 1961 | Kurushima Strait | Tanita (1967, 1968, 1969), Hoshino (1981, 1987), Tanita and Hoshino (1989); CS: Was recorded from the Ariake Sea and tentatively counted |
Spirastrella aff. coccinea (cunctatrix?, sabogae?) | Unresolved species complex | Sensu stricto: Caribbean | Hoshino (1981, 1987); CS: See Boury-Esnault et al. (1999) on the distribution of similar Spirastrella spp. Spirastrella coccinea and Spirastrella cunctatrix are morphologically very similar |
Spirastrella insignis | Thiele, 1898 | Sagami Bay | Thiele (1898), Tanita (1961, 1965, 1967, 1968, 1969), Hoshino (1977, 1987), Tanita and Hoshino (1989); CS: Was recorded from the Ariake Sea |
Spirastrella yongmeoriensis | Kim and Sim, 2009 | East China Sea | No other primary records found |
Thoosa sp. | Not formally described | Reported from Okinawa | C. Schönberg pers. obs. (2004, Ryukyu Islands, only identified to genus) |
Central Pacific Islands (Fiji, Hawaii, French Polynesia, Funafuti, Vanuatu, Marshall Islands, Marianas, Easter Islands) ( 29 spp. of coral-eroding sponges in warm water) | |||
Alectona wallichii | (Carter, 1874) | Agulhas Bank, S of Africa (Carter: also from the ‘South Sea’ and Seychelles), first reported as spicules in sediment | ? Smyth (1990, as Alectona sp.?), Vacelet (1999, in calcareous rock, but also from Tuléar in intertidal scleractinians) |
Aplysinella rhax | (De Laubenfels, 1954) | Marshall Islands | Tabudravu et al. (2002) |
Cliona aff. celata | Grant, 1826 | Scotland | Topsent (1932); CS: Cliona celata was described from Scotland and represents a taxonomically difficult species complex (Xavier et al. 2010, de Paula et al. 2012). All faunistic accounts are unreliable unless including molecular data. This report is unlikely to be Cliona celata sensu stricto but was still counted as a clionaid different from others in the bioregion |
Cliona ecaudis | Topsent, 1932 | Society Islands | Topsent (1932), S. Pohler pers. comm. (2009, Fiji); CS: Spicules of Cliona ecaudis could easily be interpreted as immature spicules of Cliona mucronata. After viewing Cliona ecaudis type material (C. Schönberg pers. obs. 2006–2007), it is here accepted as separate species |
Cliona ensifera | Sollas, 1878 | Unknown, found in an octocoral (Isis sp.), which does not provide further information about the sample site. Assumed to be from the Indo-Pacific | |
Cliona euryphylle | Topsent, 1888 | Campeche, Gulf of Mexico | De Laubenfels (1954, as Cliona euryphylla) |
(Unconf.: Cliona insidiosa) | Hancock, 1849 | In the giant clam, Tridacna gigas, occurs in the Indo-Pacific | No other primary records found. CS: The sponge could possibly occur in this bioregion but was not noted since its description. As the exact type location is unknown, it was not included in the biogeographic analysis |
Cliona johnstonii | (Carter, 1886) | Bass Strait | Kirkpatrick (1900a, as Cliona schmidti); CS: We tentatively list all ‘Cliona schmidtii’ reported from the Indo-Pacific as Cliona johnstonii to imply that the two species are different. See van Soest et al. (2017) for comments on the distribution of Cliona schmidtii |
Cliona mucronata | Sollas, 1878 | Unknown, found in an octocoral (Isis sp.), which is not useful information. Assumed to be from the Indo-Pacific | Kirkpatrick (1900a) |
Cliona aff. orientalis | Unresolved species complex | Sensu stricto: Molucca Sea, Indonesia | ? Topsent (1932, as Cliona viridis and a variety of Cliona caribbaea), ? de Laubenfels (1954, as Cliona lobata), Smyth (1990, as Cliona viridis), Kelly et al. (2003, as Cliona viridis) |
Cliona raromicrosclera | (Dickinson, 1945) | Gulf of California | No other primary records found |
Cliona aff. topsenti | Unresolved species complex | Sensu stricto: Adriatic Sea | Topsent (1932) |
Cliona valentis | (De Laubenfels, 1957) | Hawaii | Bergquist (1977, as Anthosigmella or Spirastrella) |
Cliona vermifera | Hancock, 1867 | Unknown. In Chama sp., information which does not provide further clues | Topsent (1932); CS: Cliona vermifera is thought to be a species complex (see e.g. León-Pech et al. 2015), but pending new results is here treated as a single species |
Cliothosa hancocki | (Topsent, 1888) | French Polynesia | Topsent (1932), Highsmith (1981a, as Cliona cf. quadrata); CS regards this as a species complex that needs to be resolved per bioregion. It is here still counted as a species distinct from the others occurring in this region |
(Cliothosa quadrata) | Hancock, 1849 | In the giant clam, Tridacna gigas, occurs in the Indo-Pacific | CS: After accessing Topsent’s samples at the Paris Museum (2006–2007), CS regards Cliothosa hancocki as a species complex. Cliothosa hancocki and Cliothosa quadrata are very similar (e.g. Calcinai et al. 2005). To avoid possible duplication, only Cliothosa hancocki was counted for our biogeographic analysis (more commonly used name), even though Cliothosa quadrata has been reported in the area (see above) |
(Unconf.: Cornulella purpurea) | (Hancock, 1849) | Unknown, sample found in Tridacna gigas, which has an Indo-Pacific distribution | Referring to Hancock’s sample and thus not reporting a confirmed sample site: Kirkpatrick (1900a, as Dyscliona), Topsent (1907, as undetermined genus), Hallmann (1920, as Paracornulum), Rützler and Stone (1986, as Cliona), van Soest et al. (1994); CS: It is possible that Cornulella purpurea occurs in this bioregion, but as the sample site is unknown and cannot be conclusively matched to our bioregions, this species did not become part of our analysis |
(Diplastrella spiniglobata): recommendation to reassess genus allocation | (Carter, 1879) | ‘South Sea’ | Bergquist (1967, 1977); CS: The spicules depicted by Carter suggest that it is not a bioeroding sponge but it may be closer to a Placospongia. The spicules in the figure in Bergquist (1967) may suggest a tethyid? The species needs to be reassessed and was not counted |
Dotona davidi: recommendation to reassess genus allocation | (Kirkpatrick, 1900a) | Tuvalu | No other primary records found. CS: The species is described to have microacanthose subtylotes and may be an acarnid. Without examining the type material, we were unable to make a clear decision on a genus allocation, but we presently counted this record into the Poecilosclerida for the biogeographic analysis |
Pione carpenteri | (Hancock, 1867) | Mazatlán | Topsent (1932, as Cliona); CS: The material was reported to have two colours and may represent two different species but was counted as one |
Pione aff. vastifica | Unresolved species complex | Sensu stricto: Scotland | Topsent (1932, as Cliona), de Laubenfels (1950b, 1954, as Cliona), Bergquist (1977, as Cliona), Desqueyroux-Faúndez (1990, as Cliona), Smyth (1990), Kelly et al. (2003); CS: The Pione species complex is taxonomically difficult and confused. However, this species was counted as different to Pione carpenteri |
Siphonodictyon cf. diagonoxeum | (Thomas, 1968) | Sri Lanka | Highsmith (1981, as Aka cf. diagonoxeum); CS: This record needs to be checked against Siphonodictyon maldiviense but was counted as a separate Siphonodictyon sp. |
Siphonodictyon sp. yellow | Not formally described | Reported from the Mariana Islands | Kelly et al. (2003); CS: May or may not be conspecific with the yellow Siphonodictyon sp. from the central Great Barrier Reef |
Spheciospongia globularis | (Dendy, 1922) | Chagos | Kelly et al. (2003) |
Spheciospongia potamophera: reversed comb. to Spirastrella potamophera | De Laubenfels, 1954 | Marshall Islands | Kelly et al. (2003, as Spheciospongia); CS: The original description characterises this species as encrusting; having tylostyles and large, robust, conically spined spirasters and derivates; and inflated surface canals in branching-radiate, raylike arrangement typical for Spirastrella. The sponge is thus presently returned to Spirastrella |
Spheciospongia solida | (Ridley and Dendy, 1886) | Philippines | Tendal (1969, as Spirastrella) |
Spheciospongia vagabunda | (Ridley, 1884) | Torres Straits | ? De Laubenfels (1954, as Anthosigmella), Bergquist (1967, as Spirastrella), Bergquist et al. (1971, as Spirastrella), Bergquist (1977, as Spirastrella), Tendal (1969, as Spirastrella), Kelly et al. (2003) |
(Spirastrella aff. coccinea) | Unresolved species complex | Sensu stricto: Caribbean | Bergquist (1967), Bergquist et al. (1971), Bergquist (1977); CS: See comments for Spirastrella aff. cunctatrix |
Spirastrella aff. cunctatrix (sabogae?) | Unresolved species complex | Sensu stricto: Algeria, Mediterranean | Desqueyroux-Faúndez (1990); CS: This record requires confirmation. See Boury-Esnault et al. (1999) about the distribution of similar Spirastrella spp. Spirastrella coccinea and Spirastrella cunctatrix are morphologically very similar. To avoid possible duplication, we excluded one of the locally unexpected species from our biogeographic analysis. We assumed that the more likely species to occur might be Spirastrella cunctatrix, which might have been introduced to the Indo-Pacific via the Suez Canal. Alternatively, this could be Spirastrella sabogae |
Spirastrella decumbens | Ridley, 1884 | Torres Straits | De Laubenfels (1954) |
Spirastrella keaukaha | De Laubenfels, 1951 | Hawaii | De Laubenfels (1951), Ball (1975, as Spirastrella keaukaha (coccinea?)) |
Thoosa amphiasterina | Topsent, 1920 | French Polynesia, presumably in shallow water, because of Tridacna sp. | |
Thoosa bulbosa | Hancock, 1849 | In the giant clam, Tridacna gigas, occurs in the Indo-Pacific | |
Zyzzya fuliginosa | (Carter, 1879) | Torres Straits | Luke (1998, partly as Zyzzya massalis), Van Soest et al. (1994) |
Eastern Tropical Pacific (ETP) between S California and Galápagos Islands (27 spp. of coral-eroding sponges in warm water) | |||
Cliona amplicavata | Rützler, 1974 | Bermuda | Carballo et al. (2004, 2008a), Verdín Padilla et al. (2010), Pacheco Solano (2012, 2015), Alvarado et al. (2017) |
Cliona californiana | De Laubenfels, 1932 | N California | ? De Laubenfels (1939, as Cliona celata), ? Luke (1998, partly as Cliona celata, partly as Cliona celata var. californica), Carballo et al. (2004), Carballo et al. (2008a), Verdín Padilla et al. (2010), Pacheco Solano (2012, 2015), Ávila et al. (2012), Alvarado et al. (2017) |
Cliona cf. chilensis | Thiele, 1905 | Chilean Patagonia | Desqueyroux-Faúndez and van Soest (1997); CS: The name Cliona chilensis apparently comprises two species, with one of them extending at least as far north as N Chile (de Paula et al. 2012) |
Cliona ensifera | Sollea, 1878 | Unknown, found in an octocoral (Isis sp.), which does not provide further information about the sample site. Assumed to be from the Indo-Pacific | |
Cliona euryphylle | Topsent, 1888 | Campeche, Gulf of Mexico | Carballo et al. (2004, as Cliona euryphylla), Carballo et al. (2008a, as Cliona euryphylla), Verdín Padilla et al. (2010, as euryphylla), Ávila et al. (2012, as Cliona euryphylla), Pacheco Solano (2012, 2015, both as Cliona euryphylla), Alvarado et al. (2017, as Cliona euryphylla) |
Cliona flavifodina | Rützler, 1974 | Bermuda | Carballo et al. (2004), Carballo et al. (2008a), Verdín Padilla et al. (2010), Alvarado et al. (2017) |
(Unconf.: Cliona johannae) | Topsent, 1932 | Unknown. In the red abalone, Haliotis rufescens, which occurs in the E Pacific, Oregon to Baja California, but published for Western Australia | No other primary records found. CS: This species was previously published to be from Western Australia. However, the host material suggests an E Pacific distribution, but the sponge was not reported since its description. We more strongly relied on the stated type location and counted this sponge for W Australia, not here |
Cliona medinae | Cruz-Barraza et al., 2011 | Isla Clarion, Mexican Pacific | Carballo et al. (2008a, as Cliona sp. 2), Cruz-Barraza et al. (2011), Alvarado et al. (2017) |
Cliona microstrongylata | Carballo and Cruz-Barraza, 2005 | Gulf of California | Carballo and Cruz-Barraza (2005), Carballo et al. (2008a), Pacheco Solano (2015) |
Cliona aff. mucronata | Unresolved species complex | Sensu stricto: Unknown, likely Indo-Pacific | Bautista-Guerrero et al. (2006), Carballo et al. (2008a, 2008b), Pacheco Solano (2012, 2015, as Cliona cf. mucronata), Alvarado et al. (2017); JLC: Cliona mucronata is a species complex (see Pacheco Solano 2015); CS: Local spicule shapes strongly resemble those displayed by Rützler et al. (2014), but their spicules are longer (see also Pacheco Solano 2015). Neither of the authors described spirasters, as occur in C. mucronata sensu stricto |
Cliona papillae | Carballo et al., 2004 | Mazatlán | Carballo et al. (2004), Carballo et al. (2008a), Verdín Padilla et al. (2010) |
Cliona pocillopora | Bautista-Guerrero et al., 2006 | Nayarit | Bautista-Guerrero et al. (2006), Carballo et al. (2008a), Pacheco Solano (2012, 2015), Alvarado et al. (2017) |
Cliona raromicrosclera | (Dickinson, 1945) | Gulf of California | Carballo et al. (2004), Carballo et al. (2008a), Alvarado et al. (2017) |
Cliona tropicalis | Cruz-Barraza et al., 2011 | Nayarit | Carballo et al. (2008a, as Cliona sp. 1), Cruz-Barraza et al. (2011), Pacheco Solano (2015), Alvarado et al. (2017) |
Cliona vallartense | Carballo et al., 2004 | Jalisco | Carballo et al. (2004), Carballo et al. (2008a), Alvarado et al. (2017) |
Cliona vermifera | Hancock, 1867 | Unknown. In Chama sp., information which does not provide further clues | Carballo et al. (2004, 2008a, b), Pacheco Solano (2012), Bautista-Guerrero et al. (2014), León-Pech et al. (2015), Pacheco Solano (2015), Alvarado et al. (2017); CS: Cliona vermifera is thought to be a species complex (see e.g. León-Pech et al. 2015), but pending new results is here treated as a single species |
Cliothosa tylostrongylata | Cruz-Barraza et al., 2011 | Oaxaca | Carballo et al. (2008a, b, as Cliothosa hancocki), Cruz-Barraza et al. (2011), Pacheco Solano (2015), Alvarado et al. (2017) |
(Unconf.: Cornulella purpurea) | (Hancock, 1849) | Unknown, sample found in Tridacna gigas, which has an Indo-Pacific distribution | Only referring to Hancock’s sample: Kirkpatrick (1900a, as Dyscliona), Topsent (1907, as undetermined genus), Hallmann (1920, as Paracornulum), Rützler and Stone (1986, as Cliona), van Soest et al. (1994); CS: Cornulella purpurea might occur in this bioregion, but as the type location is unknown, this species did not become part of our analysis |
Pione carpenteri | (Hancock, 1867) | Mazatlán | Carballo et al. (2004, 2008a, 2008b), Verdín Padilla et al. (2010), Pacheco Solano (2012, 2015, both as ‘cf.’), Alvarado et al. (2017) |
Pione mazatlanensis | (Hancock, 1867) | Mazatlán | Carballo et al. (2004), Carballo et al. (2008a), Verdín Padilla et al. (2010), Pacheco Solano (2015, as ‘cf.’), Alvarado et al. (2017) |
Siphonodictyon crypticum | (Carballo et al., 2007) | Oaxaca | Carballo et al. (2007, 2008a, 2008b, as Aka), Alvarado et al. (2017) |
Spheciospongia confoederata | De Laubenfels, 1930 | California | |
Spheciospongia incrustans | Carballo et al., 2004 | Jalisco | Carballo et al. (2004), Carballo et al. (2008a), Alvarado et al. (2017) |
Spheciospongia ruetzleri | Carballo et al., 2004 | Nayarit | |
Spirastrella decumbens | Ridley, 1884 | Torres Straits | Carballo and Nava (2007), Verdín Padilla et al. (2010, as Spiastrella decubens) |
Spirastrella sabogae | Boury-Esnault et al., 1999 | Pacific Panama | ? Dickinson (1945, as Spirastrella coccinea), Boury-Esnault et al. (1999) |
Thoosa calpulli | Carballo et al., 2004 | Nayarit | Carballo et al. (2004, 2008a, 2008b), Pacheco Solano (2015, as ‘cf.’), Bautista-Guerrero et al. (2016), Alvarado et al. (2017) |
Thoosa mismalolli | Carballo et al., 2004 | Jalisco | Carballo et al. (2008a), Bautista-Guerrero et al. (2010), Verdín Padilla et al. (2010), Pacheco Solano (2012, 2015), Bautista-Guerrero et al. (2016), Alvarado et al. (2017) |
Thoosa purpurea | Cruz-Barraza et al., 2011 | Revillagigedo Archipelago | Alvarado et al. (2017) |
Corals in cold-water habitats of the Atlant o -Mediterranean (AM) or Indo-Pacific (IP) (e.g. Lophelia/ Madrepora/hydrozoan communities or precious corals such as Corallium, Paracorallium; most samples from deeper than 100 m but also partly from diving depths if in colder water) (49 spp. of coral-eroding sponges in cold water) | |||
(Alectona mesatlantica) | Vacelet, 1999 | Mid-Atlantic Ridge, in 2030 m, in calcareous rock | AM: No other primary record known from cold-water reefs. CS: According to Wheeler et al. (2007), the sponge’s type location is not known for coral carbonate mounds with, e.g. Lophelia. This species has not yet been recorded from corals and was not counted for the cold-water coral eroders |
Alectona microspiculata | Bavestrello et al., 1998 | Philippines, depth not stated, in Distichopora sp. | IP: No other primary record known. CS: No depth stated, but samples from commercial fisheries. We counted it assuming it was from some depth |
Alectona millari | Carter, 1879 | N Atlantic between N Scotland and Faroe Islands, 653 m, in Madrepora oculata (latter as Amphihelia) | AM: Jennings (1891, Denmark, from shallow depths?, in mollusc shells), Topsent (1900, at the Faroes, Norway, Azores, French Mediterranean, in corals), Topsent (1904, Azores, 880 m, in a coral, 1920, Gulf of Lion, Mediterranean, 500–600 m, substrate not described), Alander (1935, 1942, Norway and Sweden, 85–1190 m, in Lophelia), Barletta and Vighi (1968, Strait of Bonifacio, 100 m, in Corallium rubrum), Vacelet (1969, Ligurian Sea, 146–170 m, in Dendrophyllia cornigera), Templado et al. (1986, Alboran Sea, 100–200 m, from Corallium rubrum community, but maybe not in the coral), Jensen and Frederiksen (1992, Faroe Islands, 252–260 m, in dead Lophelia pertusa), Maldonado (1992, Alboran Sea, 70–120 m, in Corallium rubrum), Freiwald and Wilson (1998, as Alectona millaris, Norway, 200–400 m, in Lophelia pertusa), Hansson (1999, Scandinavia, depth and substrate not specified), Borchiellini et al. (2004, NW Atlantic off Ireland, 590–880 m, in corals), Beuck and Freiwald (2005, Porcupine Bight, 780 m, in Lophelia pertusa), Beuck et al. (2007, Porcupine Bight, 1039 m, in Lophelia pertusa), Roberts et al. (2009, Porcupine Bight, in Lophelia pertusa), van Soest and Beglinger (2009, Mingulay Reefs, in Lophelia and Madrepora spp.), Calcinai et al. (2010, Mediterranean, depth not stated, in precious coral); CS: The species can also occur in shallow depths |
Alectona sarai | Calcinai et al., 2008a | Japan, 120 m, in Paracorallium japonicum | IP: Calcinai et al. (2010, Pacific, depth not stated, in precious coral) |
Alectona sorrentini | Bavestrello et al., 1998 | Japan Sea, depth not stated, in Corallium elatius | IP: Calcinai et al. (2010, Pacific, depth not stated, in precious coral); CS: Sample obtained through commercial fisheries and assumed to be from some depth. It was counted into the cold-water category of the analysis |
Alectona triradiata | Lévi and Lévi, 1983 | New Caledonia, 290–350 m, in calcareous substrate | IP: Bavestrello et al. (1998, Japan Sea, depth not stated, in Corallium elatius), Calcinai et al. (2010, Pacific, depth not stated, in precious coral) |
Alectona verticillata | (Johnson, 1899) | Madeira, ‘from deep water’, in Corallium johnsoni (as Pleurocorallium) and Dendrophyllia ramea | AM, IP: Calcinai et al. (2004b, Ryukyu Islands, 195–300 m, in Corallium elatius), Calcinai et al. (2010, Mediterranean and Pacific, depth not stated, in precious coral) |
Alectona wallichii | (Carter, 1874) | Agulhas Bank, S of Africa (Carter: also from the ‘South Sea’ and Seychelles), 144–180 m, first reported as spicules in sediment | IP, AM?: Carter (1879, as Corticium, in the ‘South Seas’ in Stylaster sanguineus), Bavestrello et al. (1998, Japan Sea, depth not stated, in Corallium elatius), Hansson (1999, Scandinavia, depth and substrate not specified), Calcinai et al. (2010, Pacific, depth not stated, in precious coral); CS: Hansson’s record requires reassessment and is presently not accepted as correct |
Alectona sp. | Not formally described, but reported by Bavestrello et al. (1998) | Japan Sea, depth not stated, in Corallium elatius | IP: No other original report known from cold-water reefs. CS: The species appears to be different to all other known Alectona spp. and was counted |
(Cliona annulifera) | Annandale, 1915b | Sri Lanka, 1265 m, in mollusc shells | Thomas (1979b), Pattanayak (2009); CS: This species was not included in the cold-water analysis, because it was only found in mollusc shells and it was not clear whether it was sampled from a coral habitat |
Cliona caledoniae | Van Soest and Beglinger, 2009 | Scotland, Mingulay Reefs in Lophelia and Madrepora spp., 127 m (paratypes 82–131 m) | AM: No other original report known from cold-water reefs |
Cliona cf. celata | Grant, 1826 | Scotland, from shore, in Ostrea edulis shells | AM: Alander (1942, Sweden, to 200 m, in thick-shelled bivalves), Hansson (1999, Scandinavia, depth and substrate not specified), Cruz Simó (2002, depth not stated, in Dendrophyllia ramea); CS: These accounts of Cliona celata may refer to different species. It was described from Scotland and represents a taxonomically difficult species complex (Xavier et al. 2010, de Paula et al. 2012). All faunistic accounts are unreliable unless including molecular data. These reports are unlikely to represent Cliona celata sensu stricto but were still counted as a clionaid different from others in the bioregion |
Cliona chilensis | Thiele, 1905 | Chilean Patagonia, 18 m, massive or on shells | IP, AM: Försterra et al. (2005, Chilean Patagonia, shallow water, in Desmophyllum dianthus), Willenz et al. (2009, Chilean Patagonia, 1–30 m, in ‘stony corals’); CS: It also occurs in the Atlantic (e.g. de Paula et al. 2012) |
Cliona desimoni | (Bavestrello et al., 1995) | W Pacific, off Taiwan, 150–200 m, in Corallium elatius | IP: Calcinai et al. (2010, Pacific, depth not stated, in precious coral) |
(Unconf.: Cliona ensifera) | Sollas, 1878 | Unknown, found in an octocoral (Isis sp.), which does not provide further information about the sample site. Assumed to be from the Indo-Pacific | IP?: Pica et al. (2012, likely New Caledonia, in Distichopora sp., but depth unknown); CS: This record was not counted, because it might have been for a shallow, warm-water environment |
Cliona janitrix | Topsent, 1932 | Strait of Bonifacio, Mediterranean, depth not stated, in oyster shell | AM: Melone (1965, Strait of Bonifacio, 60 m, in Corallium rubrum), Barletta and Vighi (1968, different sites in the Mediterranean, 25–100 m, in Corallium rubrum), Corriero et al. (1997, Ligurian Sea, 20–45 m, in Corallium rubrum), Calcinai et al. (2002, Ligurian Sea, 15–35 m, in Corallium rubrum and Leptopsammia pruvoti), Rosell and Uriz (2002, Balearic Sea, Mediterranean, 30 m, in Corallium rubrum), Calcinai et al. (2010, Mediterranean, depth not stated, in precious coral) |
Cliona lobata | Hancock, 1849 | English Channel | AM: Alander (1942, Sweden, down to 1265 m, in thin-shelled bivalves), Topsent (1900, in England, Denmark, Belgium and France, but the substrate mentioned referred to mollusc shells), Hansson (1999, Norway, depth and substrate not specified), Calcinai et al. (2010, Mediterranean, depth not stated, in precious coral) |
Cliona cf. schmidtii | (Ridley, 1881); based on an erroneous record of a ‘variety’ of Vioa johnstonii in Schmidt, 1870 p. 5 | Adriatic Sea, Mediterranean, depth not stated, substrate not specified | AM: Cruz-Simó (2002, Canary Islands, depth not stated, in Dendrophyllia ramea) |
Cliona vermifera | Hancock, 1867 | Unknown. In Chama sp., information which does not provide further clues | AM, IP?: Corriero et al. (1997, Ligurian Sea, 20–45 m, in Corallium rubrum); CS: Cliona vermifera is thought to be a species complex (see e.g. León-Pech et al. 2015). Pending new results, it is treated as a single species |
Cliona viridis | (Schmidt, 1862) | Adriatic Sea, Mediterranean, depth not stated, as massive sponge and in Cladocora caespitosa (as Caryophyllaea) | AM: ? Templado et al. (1986, as Cliona copiosa, Alboran Sea, 100–200 m, from Corallium rubrum community, but maybe not in the coral), Corriero et al. (1997, Ligurian Sea, 20–45 m, in Corallium rubrum community but not in the coral itself), Hansson (1999, Norway, depth and substrate not specified), Sitjà and Maldonado (2014, Alboran Sea, 52–92 m, substrate not specified); CS: Only tentatively counted, because it has access to corals |
(Cornulum virguliferum) | (Lévi and Lévi, 1983) | New Caledonia, 175–430 m, in foraminiferan | IP: No other primary record known from cold-water reefs. CS: As the sponge was reported at depth from a foraminiferan, it was only included in the warm-water coral-related biogeographic analysis |
Delectona alboransis | Rosell, 1996 | Alboran Sea, W Mediterranean, 70–120 m, in Corallium rubrum | AM: No other primary record known from cold-water reefs |
Delectona ciconiae | Bavestrello et al., 1996 | Alboran Sea, W Mediterranean (but also found at Elba Island, Bosa Marina, 80–120 m, in Corallium rubrum) | AM: ? Barletta and Vighi (1968, as Thoosa sp., different sites in the Mediterranean, 25–100 m, in Corallium rubrum), Calcinai et al. (2002, Ligurian Sea, 25 m, in Corallium rubrum, 2010, Mediterranean, depth not stated, in precious coral) |
Delectona higgini | (Carter, 1880) | Sri Lanka, depth not stated, in coralline algae | IP: No other primary record known from cold-water reefs. CS: Carter did not state a sampling depth and reported coralline algae as substrate. The sample may have originated in shallow, warm water. However, as the three other Delectona spp. occur in deep water, Delectona higgini was tentatively included in the cold-water count as well |
Delectona madreporica | Bavestrello et al., 1997 | Ligurian Sea, 22 m, in Leptopsammia pruvoti and Madracis pharensis | AM: ? Barletta and Vighi (1968, as Thoosa sp., different sites in the Mediterranean, 25–100 m, in Corallium rubrum), Calcinai et al. (2002, Ligurian Sea, 15 m, in Leptopsammia pruvoti) |
Dercitus (Stoeba) plicatus | (Schmidt, 1868) | Algeria, Mediterranean, depth not stated, in coralline algae | AM: Templado et al. (1986, Alboran Sea, 80–120 m, from Corallium rubrum community, but maybe not in the coral), ? Calcinai et al. (2002, as Dercitus sp., Ligurian Sea, 25 m, in Corallium rubrum, 2010, as Stoeba spp., Mediterranean and Pacific, depth not stated, in precious coral), Mastrototaro et al. (2010, as Stoeba plicata, Ionian Sea, 513–747 m, in Madrepora oculata and Lophelia pertusa), Sitjà and Maldonado (2014, Alboran Sea, 52–112 m, substrate not specified) |
Diplastrella bistellata | (Schmidt, 1862) | Adriatic sea, Mediterranean, depth or substrate not stated | AM: Vacelet (1969, Gulf of Lion, substrate not described), Maldonado (1992, Alboran Sea, 70–120 m, on Corallium rubrum), Sitjà and Maldonado (2014, Alboran Sea, 87–92 m, substrate not specified) |
Dotona pulchella | Carter, 1880 | Sri Lanka, depth not stated, in coralline algae | AM, IP: Topsent (1904, Azores, 880 m, in corals), Calcinai et al. (2001, Taiwan, between 250 and 400 m, in Corallium elatius), Rosell and Uriz (2002, as Dotona pulchella subsp. mediterranea, Alboran Sea, Mediterranean, 70–120 m, in Corallium rubrum), Calcinai et al. (2010, Mediterranean and Pacific, depth not stated, in precious coral); CS: As all the reports from the Atlanto-Mediterranean region are from deeper waters, the Sri Lankan sample was also counted for deep water |
Holoxea excavans | Calcinai et al., 2001 | Taiwan, between 250 and 400 m, in Corallium elatius | IP: Calcinai et al. (2008b Japan, depth not stated, in Paracorallium japonicum, 2010, Pacific, depth not stated, in precious coral) |
Holoxea furtiva | Topsent, 1892 | Gulf of Lion, Mediterranean, depth not stated, in coralline algae | AM: Templado et al. (1986, Alboran Sea, 100–200 m, from Corallium rubrum community, but maybe not in the coral), Calcinai et al. (2001, Cape Verde Islands, depth not stated, in Corallium rubrum, 2010, as Holoxea furtive, Mediterranean, depth not stated, in precious coral) |
(Neamphius huxleyi) | (Sollas, 1888) | Vanuatu, 108–126 m, massive sponge | IP: No other primary record known from cold-water reefs. CS: But numerous (here ignored) publications on the biochemistry of this species are available that suggest that the species is widely distributed in the Pacific. As we have no knowledge whether this sponge erodes corals, we did not use this record |
Pione vastifica | (Hancock, 1849) | Scotland, depth not stated, from mollusc shells | AM: Alander (1942, as Cliona, Sweden, 65–600 m, in Lophelia), Templado et al. (1986, as Cliona, Alboran Sea, 100–200 m, from Corallium rubrum community, but maybe not in the coral), Maldonado (1992, as Cliona, Alboran Sea, 70–120 m, in Corallium rubrum), Cruz-Simó (2002, as Cliona, Canary Islands, depth not stated, in Dendrophyllia ramea), Hansson (1999, Scandinavia, depth and substrate not specified) |
Siphonodictyon corallirubri | (Calcinai et al., 2007b) | Tyrrhenian Sea, depth unknown, in Corallium rubrum | AM: Calcinai et al. (2010, Mediterranean, depth not stated, in precious coral) |
Siphonodictyon infestum | (Johnson, 1899) | Madeira, depth not stated, in bivalve shells | AM: ? Topsent (1904, as Cliona labyrinthica), ? Alander (1942, as Aka labyrinthica, W Norway and Sweden, 85–300 m, in Lophelia), ? Melone (1965, as Cliona labyrinthica, 60–75 m, Strait of Bonifacio in Corallium rubrum), ? Jensen and Frederiksen (1992, as Siphonodictyon labyrinthicum, Faroe Islands, 252–260 m, in dead Lophelia pertusa), ? Corriero et al. (1997, as Aka labyrinthica, Ligurian Sea, 20–45 m, in Corallium rubrum), ? Freiwald and Wilson (1998, as Aka labyrinthica, Norway in Lophelia pertusa), ? Hansson (1999, as Siphonodictyon labyrinthica, Scandinavia, substrate or depth not described), ? Calcinai et al. (2002, as Aka labitinthyca, Ligurian Sea, 25 m, in Corallium rubrum), ? Rosell and Uriz (2002a, as Aka labyrinthica, Balearic Sea, Mediterranean, 30 m, in Corallium rubrum), Beuck et al. (2007, as Aka infesta, Porcupine Bight, 1030 m, in Lophelia pertusa), Schönberg and Beuck (2007, Ionian Sea, 671–679 m, in Madrepora oculata), Beuck et al. (2010, Ionian Sea, 671–679 m, in Madrepora oculata), Calcinai et al. (2010, Mediterranean, depth not stated, in precious coral) |
Siphonodictyon insidiosum | (Johnson, 1899) | Madeira, depth not stated, in bivalve shells | AM: ? Barletta and Vighi (1968, as Cliona labyrinthica, different sites in the Mediterranean, 25–100 m, in Corallium rubrum), Calcinai et al. (2008b, Mediterranean, depth not stated, in Corallium rubrum, 2010, Mediterranean and Pacific, depth not stated, in precious coral) |
Siphonodictyon labyrinthicum | (Hancock, 1849) | Unknown type location, but found in the giant clam, Tridacna gigas, which occurs in the Indo-Pacific in shallow water | IP: Pica et al. (2012, as Aka, likely New Caledonia, in Distichopora sp., but depth unknown), Calcinai et al. (2008b, 2010, Pacific, depth not stated, in precious coral); CS: This species has been widely—and erroneously—reported from the Atlanto-Mediterranean region (see Schönberg and Beuck 2007 for details). None of the presently available accounts can be considered as reliable, but the species was tentatively counted for cold-water reefs, because its spicule shape was more congruent with deep-water species |
Siphonodictyon rodens | (Johnson, 1899) | Madeira, ‘from deep water’ in Dendrophyllia ramea | AM: ? Vacelet (1969, as Cliona labyrinthica, Gulf of Lion, 175–235 m, in rock debris); CS: The spicules of Vacelet’s material may be too thin to match this species (his oxea dimensions given as 130–170 × 2.5–5 μm). Van Soest et al. (2017) synonymised it with Siphonodictyon insidiosum. It is here listed, tentatively recognised as a valid species and counted, because a morphometric study on the spicules revealed differences between the Johnson species (Schönberg and Beuck 2007; although this was based on hand drawings of the spicules) |
(Siphonodictyon spp.) | Not formally described, reported by Cruz in a few publications | Canary Islands, depth not stated, in corals, calcareous algae and mollusc shells | AM: Cruz and Bacallado (1983) and Cruz Simó (2002, Canary Islands, depth not stated, e.g. in Dendrophyllia ramea and Cladocora debilis); CS: After observing some of Cruz’s vouchers, it became clear that he had misidentified and combined more than one species under the same name. At least one species very much resembled Siphonodictyon brevitubulatum and is thus different from the other species listed here. However, as we cannot exactly allocate which record belongs to which substrate, we did not include this record in our biogeographic analysis |
Spirastrella cunctatrix | Schmidt, 1868 | Algeria, Mediterranean, depth and substrate not stated | AM: Templado et al. (1986, Alboran Sea, 100–200 m, from Corallium rubrum community, but maybe not in the coral); CS: The sponge erodes coral materials in shallow depths and was not excluded from the biogeographic analysis for cold-water habitats |
Pione abyssorum: genus transfer to Spiroxya abyssorum new comb. | (Carter, 1874) | English Channel, 900 m, in Lophelia pertusa (as Lophohelia prolifera) | AM: Hansson (1999, as Cliona abyssorum, Scandinavia, depth and substrate not specified); CS: The species was listed as a Pione on the World Porifera Database (van Soest et al. 2017). However, based on the spicule combination of subtylostyles, smooth oxeas and helical microstrongyles, the species is here transferred to Spiroxya. Carter (1974) and Topsent (1904) already stated that the present species resembles other Spiroxya spp. |
Spiroxya acus | (Bavestrello et al., 1995) | W Pacific, 150–200 m, in Corallium elatius | IP: Calcinai et al. (2010, Pacific, depth not stated, in precious coral) |
Spiroxya corallophila | (Calcinai et al., 2002b) | Ligurian Sea, Mediterranean, 30–35 m (but also other sites in the Mediterranean), in Corallium rubrum | AM: Calcinai et al. (2010, Mediterranean, depth not stated, in precious coral) |
Spiroxya heteroclita | Topsent, 1896 | Gulf of Lion, Mediterranean, depth not stated, in stones | AM: Corriero et al. (1997, Ligurian Sea, 20–45 m, in Corallium rubrum), Beuck and Freiwald (2005, also as Entobia laquea, Porcupine Bight, 780 m, in Lophelia pertusa), Longo et al. (2005, Ionian Sea, 640–662 m, substrate not specified), Beuck et al. (2007, Porcupine Bight, 1030 m, in Lophelia pertusa), Calcinai et al. (2010, Mediterranean, depth not stated, in precious coral), Mastrototaro et al. (2010, Ionian Sea, 640–662 m, in Madrepora oculata and Lophelia pertusa) |
Spiroxya levispira | (Topsent, 1898) | Azores, 880 m, in coral | AM: Topsent (1904, Azores, as Cliona levispira, 1165–1360 m, in coral), Boury-Esnault et al. (1994, as Cliona, Maroccan Atlantic, 1378 m, in pebbles or madrepores), Hansson (1999, as Cliona, Scandinavia, depth and substrate not specified), Rosell and Uriz (2002a, as Scantiletta, Balearic and Alboran Sea, Mediterranean, 30–120 m, in Corallium rubrum, 100 m, in Lophelia pertusa), Borchiellini et al. (2004, NW Atlantic off Ireland, 590–880 m, in corals), Longo et al. (2005, Ionian Sea, 634–809 m, substrate not specified), van Soest and Beglinger (2009, Mingulay Reefs and Rockall Bank, 82–762 m, in Lophelia and Madrepora spp.), Beuck et al. (2010, Ionian Sea, 300–1100 m, in Desmophyllum dianthus, Lophelia pertusa, Madrepora oculata, Pseudamussium peslutrae), ? Calcinai et al. (2010, Pacific, depth not stated, in precious coral), Mastrototaro et al. (2010, Ionian Sea, 642–809 m, in Madrepora oculata and Lophelia pertusa), Bavestrello et al. (2014, Tyrrhenian Sea, Mediterranean, 45–280 m, in Corallium rubrum); CS: The record for the Pacific by Calcinai et al. (2010) is here regarded as a possible mistake |
Spiroxya macroxeata | (Calcinai et al., 2001) | Taiwan, between 250 and 400 m, in Corallium elatius | IP: No other original report known from cold-water reefs |
Spiroxya pruvoti | (Topsent, 1900) | Gulf of Lion, 5–600 m, in coral | AM: Hansson (1999, Scandinavia, depth and substrate not specified) |
Spiroxya sarai | (Melone, 1965) | Strait of Bonifacio, 68 m, in Corallium rubrum | AM: Barletta and Vighi (1968, different sites in the Mediterranean, 25–100 m, in Corallium rubrum), Corriero et al. (1997, as Cliona, Ligurian Sea, 20–45 m, in Corallium rubrum), Calcinai et al. (2002, as Cliona, Ligurian Sea, 30–35 m, in Corallium rubrum, 2010, Mediterranean, depth not stated, in precious coral) |
Thoosa armata | Topsent, 1888 | Gulf of Guinea, depth and substrate not specified | AM: Topsent (1904, Azores, 599 m, in a coral), Barletta and Vighi (1968, Tyrrhenian Sea, 50–65 m, in Corallium rubrum), Templado et al. (1986, Alboran Sea, 100–200 m, from Corallium rubrum community, but maybe not in the coral), Calcinai et al. (2010, Mediterranean, depth not stated, in precious coral) |
Thoosa bulbosa | Hancock, 1849 | In the giant clam, Tridacna gigas, occurs in shallow waters of the Indo-Pacific | IP: Calcinai et al. (2001, Taiwan, between 250 and 400 m, in Corallium elatius, 2010, Pacific, depth not stated, in precious coral) |
(Cliothosa investigatoris): recommendation to reassess genus allocation and to consider Thoosa, the genus used in the original description, or alternatively a sample including Cliothosa and Thoosa spicules | (Annandale, 1915b) | Sri Lanka, 1265 m, in gastropod shell | IP: Pattanayak (2009, as Thoosa); CS: The original description of Cliothosa investigatoris shares taxonomic characters that make it difficult to decide whether this species is a Cliothosa or a Thoosa (or both?). The species is presently listed as a Cliothosa (van Soest et al. 2017), which would however be a very unusual genus in deep water. Based on the occurrence of microacanthose, bulbous amphiasters, the species is more likely Thoosa. Nevertheless, lacking access to the type material, we have not made a firm decision. As this species has not yet been reported to erode coral materials, it was not counted |
Thoosa midwayi | Azzini et al., 2007a | Midway Atoll, central N Pacific, between 100 and 1500 m, in Corallium sp. | IP: Calcinai et al. (2001, as Thoosa amphiasterina, Midway Atoll, central N Pacific, between 100 and 1500 m, in Corallium sp., 2010, Pacific, depth not stated, in precious coral) |
Thoosa mollis | Volz, 1939 | Adriatic Sea, Mediterranean, 2–8 m, in calcareous stones | AM: Calcinai et al. (2010, Mediterranean, depth not stated, in precious coral) |
(Thoosa sp.) | Not fully identified | Reported for bathyal depths at New Caledonia, in Vaceletia crypta Borchiellini et al. (2004) | CS: No further information provided. As we could not decide which species this could be and wanted to avoid duplication, we did not use this account |
Triptolemma simplex | (Sarà, 1959) | Tyrrhenian Sea, Mediterranean, 0–1 m in calcareous rock wall of cave | AM: Templado et al. (1986, Alboran Sea, 100–200 m, from Corallium rubrum community, but maybe not in the coral), ? Corriero et al. (1997, as Triptolemus sp., Ligurian Sea, 20–45 m, in Corallium rubrum), Bertolino et al. (2011, Ligurian and Tyrrhenian Sea, 30–40 m, in calcareous rock and Corallium rubrum) |
Triptolemma strongylata | Bertolino et al., 2011 | Japan, ca. 200 m, in Paracorallium japonicum | IP: No other original report known from cold-water reefs |
Zyzzya coriacea | (Lundbeck, 1910) | N Atlantic, Mid-Atlantic Ridge, 1438 m, massive sponge | AM: No other original report known. CS: The species’ distribution overlaps that of Lophelia reefs (van Soest et al. (2017), enabling us to count it |
Valid species of bioeroding sponges that to date have neither been found in coral reef environments nor are known for eroding coral material (31 spp.) | |||
Cliona adriatica | Calcinai et al., 2011 | Adriatic Sea, Mediterranean, in calcareous rock | No other primary records found. Not yet reported for eroding coral materials or for occurring on coral reefs |
Cliona burtoni | Topsent, 1932 | Bonifacio, W Mediterranean, in oyster shell | To date only known from the Mediterranean (e.g. Bertolino et al. 2013, Calcinai et al. 2015). Not yet reported for eroding coral materials or for occurring on coral reefs |
Cliona diversityla | Sarà, 1978, in serpulid tubes and mollusc shells | Tierra del Fuego | To date, only known from the Tierra del Fuego (e.g. Gappa and Landoni 2005). Not yet reported for eroding coral materials or for occurring on coral reefs |
Cliona labiata | (Keller, 1880) | Capri, Tyrrhenian Sea, Mediterranean, massive sponge | No other primary records found. Not yet reported for eroding coral materials or for occurring on coral reefs, not described to embed or agglutinate calcareous materials. JLC and CS: It may well be that this is a synonym for the massive form of Cliona viridis, but we did not access type material |
Cliona lesueuri | Topsent, 1888 | Kangaroo Island, S Australia, in the whirling abalone Haliotis cyclobates (as Haliotis excavata) | No other primary records found. Reported to erode in mollusc shells, not yet for eroding coral materials or for occurring on coral reefs |
Cliona lisa | Cuartas, 1991 | Patagonia, in pebble | Only known from Argentina (e.g. Gappa and Landoni 2005). Not yet reported for eroding coral materials or for occurring on coral reefs |
Cliona parenzani | Corriero and Scalera-Liaci, 1997 | Ionian Sea, Mediterranean, massive, eroding calcareous rock | Only known from the Mediterranean (e.g. Vacelet et al. 2008). Not yet reported for eroding coral materials or for occurring on coral reefs. CS: Vacelet et al. (2008) may in part include Cliona burtoni, which, however, presents the same situation (see above) |
Cliona rhodensis | Rützler and Bromley, 1981 | Rhodes, E Mediterranean, 0.5–8 m, in Mesozoic limestone, coralline algae and pebbles | No other primary records found. Not yet reported for eroding coral materials or for occurring on coral reefs |
Cliona spissaspira | Corriero and Nonnis Marzano, 2007 | Ionian Sea, Mediterranean, in calcareous rock | No other primary records found. Reported to erode in calcareous rock, not yet for eroding coral materials or for occurring on coral reefs |
Clionaopsis platei | Thiele, 1905 | Patagonia, massive sponge | Only known from Patagonia (e.g. Willenz et al. 2009, referring to massive sponge, Diez et al. 2014, in oyster shell). Not yet reported for eroding coral materials or for occurring on coral reefs |
Diplastrella ornata | Rützler and Sarà, 1962 | Adriatic Sea, Mediterranean | Only known from the Mediterranean. The sponge was found on the lower surface of a stone. Not yet reported for eroding coral materials or for occurring on coral reefs |
Pione angelae | Urteaga and Pastorino, 2007 | Mar del Plata, Argentina, in gastropod shells | Only known from Patagonia and the Chilean fjords (e.g. Diez et al. 2014, in oyster shell). Not yet reported for eroding coral materials or for occurring on coral reefs. CS: Pione muscoides and Pione angelae need to be compared, they may be synonymous |
Pione gibraltarensis | Austin et al., 2014 | W Canada, Gulf of Alaska, in bivalve shells | No other primary records found. Not yet reported for eroding coral materials or for occurring on coral reefs |
Pione hancocki taxon inquirendum | (Schmidt, 1862) | Adriatic Sea, Mediterranean | No other primary records found. CS: The species type has a very unusual spicule combination that seems to include Pione-like tylostyles and spined or nodulose rhabdostyles as they may occur in poecilosclerids. This species requires reassessment, and we have ignored it entirely |
Pione hixoni | (Von Lendenfeld, 1886) | Sydney Harbour, Australia, massive sponge | No other primary records found. CS: The massive sponge was reported from 40 m depth and ‘attached to the sand’ of a subtropical habitat. It was thus not included in our biogeographic analysis |
Pione muscoides | (Hancock, 1849) | Unknown. Reported from the gastropod Chorus giganteus (as Monoceros fusoides), which occurs along the Chilean coastline | No other primary records found. Not yet reported for eroding coral materials or for occurring on coral reefs. CS: The only other record under this name is likely erroneous, as the spicule dimensions differ (Bergquist 1961, as Cliona muscoides, from New Zealand). Pione muscoides and Pione angelae need to be compared; they have very similar spicule dimensions and may be synonymous |
Pione rhabdophora | (Hentschel, 1914) | Cape Verde Islands, in Strombus shell | No other primary records found. Not yet reported for eroding coral materials or for occurring on coral reefs |
Pione robusta | (Old, 1941) | Chesapeake Bay, in oysters | No other primary records found. Not yet reported for eroding coral materials or for occurring on coral reefs |
Pione spirilla | (Old, 1941) | Chesapeake Bay, in oysters | Only known from the east of the USA and from oysters (e.g. Wells 1959, 1961). Not yet reported for eroding coral materials or for occurring on coral reefs |
Pione stationis | (Nassonow, 1883) | Black Sea, in bivalve shells | No other primary records found. Not yet reported for eroding coral materials or for occurring on coral reefs. CS: The original description is insufficient for comparisons; the type material needs to be re-examined |
Scolopes lignea | (Hallmann, 1912) | New South Wales coast, Australia, massive sponge | No other primary records found. Not yet reported for eroding coral materials or for occurring on coral reefs |
Siphonodictyon nodosum | (Hancock, 1849) | Unknown type location, but found in the giant clam, Tridacna gigas, which occurs in the Indo-Pacific | No other primary records found. Not yet reported for eroding coral materials or for occurring on coral reefs |
Spheciospongia albida | (Carter, 1886) | Port Phillip Bay, massive sponge that incorporates sediments | No other primary records found. Not yet reported for eroding coral materials or for occurring on coral reefs |
Spheciospongia alcyonoides | (Hallmann, 1912) | S Queensland, massive sponge | Hooper and Wiedenmayer (1994); CS: This species is known from the subtropics but has not yet been reported to occur on coral reefs of erode corals and was not counted for the biogeographic analysis |
Spheciospongia australis | (Von Lendenfeld, 1888) | Sydney Harbour, Australia, massive sponge | No other primary records found. Not yet reported for eroding coral materials or for occurring on coral reefs |
Spheciospongia massa | (Ridley and Dendy, 1886) | Bass Straits, Australia, massive sponge | No other primary records found. Not yet reported for eroding coral materials or for occurring on coral reefs |
Spheciospongia montiformis | (Hallmann, 1912) | S Queensland, massive sponge | Hooper and Wiedenmayer (1994, as Spirastrella); CS: This species is known from the subtropics but has not yet been reported to occur on coral reefs of erode corals and was not counted for the biogeographic analysis |
Spheciospongia poculoides | (Hallmann, 1912) | New South Wales coast, Australia, massive sponge | No other primary records found. Not yet reported for eroding coral materials or for occurring on coral reefs |
Spheciospongia robusta | (Carter, 1886) | Port Phillip Bay, South Australia, massive sponge | Only known from South Australia (e.g. Dendy 1897). Not yet reported for eroding coral materials or for occurring on coral reefs |
Thoosa tortonesei | (Sarà, 1958) | Ligurian Sea, Mediterranean | No other primary records found. Reported to erode in calcareous rock, not yet for eroding coral materials or for occurring on coral reefs. CS: The spicules pictured by Sarà may suggest that at least part of the sample was contributed by a Cliona viridis-like sponge. They may represent more than one species, and the material needs to be re-examined |
Volzia azzaroliae | (Sarà, 1978) | Patagonia, in rock material made of coralline algae | Only known from Patagonia (e.g. Pansini and Sarà 1999, Gappa and Landino 2005). Not yet reported for eroding coral materials or for occurring on coral reefs |
Appendix B
Taxonomic list of non-sponge species mentioned in the publication (with the exception of Vaceletia crypta, a hypercalcified sponge that was used by bioeroding sponges as substate). Taxon validities and authorities were verified in the World Register of Marine Species (WoRMS Editorial Board).
Context: Bioerosion rates and host organisms (background information for main text and Appendices C and D) | |||||
---|---|---|---|---|---|
Phylum | Class | Family | Species | Taxon authority | Common name |
Mollusca | Bivalvia (Heterodonta) | (Cardioidea) Cardiidae (Tridacninae) | Tridacna gigas | (Linnaeus, 1758) | Giant clam |
Tridacna squamosa | (De Lamarck, 1819) | Fluted giant clam | |||
Bivalvia (Pteriomorphia) | (Anomioidea) Placunidae | Placuna placenta | (Linnaeus, 1758) | Windowpane oyster | |
(Arcoidea) (Glycimerididae) | Tucetona sp. | Iredale, 1931 | Bittersweet clam | ||
(Chamoidea) Chamidae | Chama macerophylla | Gmelin, 1791 | Leafy jewelbox | ||
(Ostreoidea) Ostreidae (Ostreinae) | Ostrea edulis | Linnaeus, 1758 | Edible oyster | ||
(Pectinoidea) Pectinidae (Palliolinae) | Pseudamussium peslutrae | (Linnaeus, 1771) | Seven-rayed scallop | ||
(Pterioidea) Pteriidae | Pinctada margaritifera | (Linnaeus, 1758) | Black-lip pearl oyster | ||
Gastropoda (Caenogastropoda) | (Muricoidea) Muricidae (Ocenebrinae) | Chorus giganteus | (Lesson, 1831) | Giant unicorn snail | |
(Stromboidea) Strombidae | Lobatus gigas | (Linnaeus, 1758) | Queen conch | ||
(Tonnoidea) Cassidae | Cassis tuberosa | (Linnaeus, 1758) | King helmet | ||
(Tonnoidea) Ranellidae (Cymatiinae) | Charonia variegata | (De Lamarck, 1816) | Atlantic triton | ||
Gastropoda (Vetigastropoda) | (Haliotoidea) Haliotidae | Haliotis cyclobates | Péron and Lesueur, 1816 | Whirling abalone | |
Haliotis rufescens | Swainson, 1822 | Red abalone | |||
Cnidaria | Anthozoa (Hexacorallia) | Acroporidae | Acropora muricata | (Linnaeus, 1758) | Spiny coral |
Acropora palmata | (De Lamarck, 1816) | Elkhorn coral | |||
Astreopora listeri | Bernard, 1896 | Starflower coral | |||
Montipora digitata | (Dana, 1846) | Pore coral | |||
Agariciidae | Agaricia agaricites | (Linnaeus, 1758) | Lettuce coral |
Cnidaria ctnd. | Anthozoa (Hexacorallia) | Astrocoeniidae | Madracis myriaster | (Milne Edwards and Haime, 185) | Striate finger coral |
Madracis pharensis | (Heller, 1868) | Encrusting star coral | |||
Caryophylliidae | Desmophyllum dianthus | (Esper, 1794) | Cockscomb cup coral | ||
Lophelia pertusa | (Linnaeus, 1758) | Spider hazard, cold-water coral, deep-sea coral | |||
Dendrophylliidae | Dendrophyllia cornigera | (De Lamarck, 1816) | Doe cup coral | ||
Dendrophyllia ramea | (Linnaeus, 1758) | Branching cup coral | |||
Leptopsammia pruvoti | Lacaze-Duthiers, 1897 | Sunset cup coral | |||
Meandrinidae | Dichocoenia stokesii | Milne Edwards and Haime, 1848 | Pineapple coral | ||
Meandrina meandrites | (Linnaeus, 1758) | Meander coral | |||
Merulinidae | Cyphastrea serailia | (Forskål, 1775) | Lesser knob coral | ||
Dipsastraea pallida | (Dana, 1846) | Knob coral | |||
Favites halicora | (Ehrenberg, 1834) | Larger star coral | |||
Goniastrea retiformis | (De Lamarck, 1816) | Lesser star coral | |||
Orbicella annularis | (Ellis and Solander, 1786) | Caribbean or boulder star coral | |||
Montastraeidae | Montastraea cavernosa | (Linnaeus, 1767) | Great star coral, false knob coral | ||
Mussidae | Manicina areolata | (Linnaeus, 1758) | Porous coral | ||
Pseudodiploria clivosa | (Ellis and Solander, 1786) | Knobby brain coral | |||
Pseudodiploria strigosa | (Dana, 1846) | Symmetrical brain coral | |||
Oculinidae | Madrepora oculata | Linnaeus, 1758 | Zigzag coral | ||
Pocilloporidae | Pocillopora verrucosa | (Ellis and Solander, 1786) | Cauliflower coral |
Phylum | Class | Family | Species | Taxon authority | Common name |
Cnidaria ctnd. | Anthozoa (Hexacorallia) | Poritidae | Goniopora tenuidens | (Quelch, 1886) | Anemone coral |
Porites astreoides | De Lamarck, 1816 | Yellow Porites, mustard hill coral | |||
Porites cylindrica | Dana, 1846 | Cylindrical hump coral | |||
Porites furcata | De Lamarck, 1816 | Split hump coral | |||
Porites lobata | Dana, 1846 | Lobate hump coral | |||
Porites lutea | Milne Edwards and Haime, 1851 | Mound coral | |||
Porites porites | (Pallas, 1766) | Hump coral | |||
Porites rus | (Forskål, 1775) | Knobbly hump coral | |||
Siderastreidae | Siderastrea radians | (Pallas, 1766) | Lesser starlet coral | ||
Siderastrea siderea | (Ellis and Solander, 1768) | Massive starlet coral | |||
Siderastrea stellata | Verrill, 1868 | Starry starlet coral | |||
Cladocora caespitosa | (Linnaeus, 1767) | Pillow coral | |||
Scleractinia incertae sedis | Cladocora debilis | Milne Edwards and Haime, 1849 | Thin tube coral | ||
Anthozoa (Octocorallia) | Coralliidae | Corallium elatius | Ridley, 1882 | Japanese pink coral | |
Corallium johnsoni | Gray, 1860 | Johnson’s precious coral | |||
Corallium rubrum | (Linnaeus, 1758) | Red coral, precious coral | |||
Paracorallium japonicum | (Kishinouyi, 1903) | Japanese red coral | |||
Idididae | Isis sp. | Linnaeus, 1758 | Bamboo coral | ||
Hydrozoa | Stylasteridae | Distichopora sp. | De Lamarck, 1816 | Lace stick coral | |
Porifera | Demospongiae (Keratosa) | Verticillitidae | Vaceletia crypta | (Vacelet, 1977) | Cryptic hypercalcified sponge |
Context: Spongivory (background information for Appendix E) | |||||
---|---|---|---|---|---|
Chordata (Vertebrata) | (Tetrapoda) Reptilia | Cheloniidae | Eretmochelys imbricata | (Linnaeus, 1766) | Hawksbill turtle |
(Pisces) Actinopterygii | Acanthuridae | Acanthurus coeruleus | Bloch and Schneider, 1801 | Blue tang surgeonfish | |
Acanthurus pyroferus | Kittlitz, 1834 | Chocolate surgeonfish | |||
Chaetodontidae | Chaetodon kleinii | Bloch, 1790 | Sunburst butterflyfish | ||
Chaetodon vagabundus | Linnaeus, 1758 | Vagabond butterflyfish | |||
Zanclidae | Zanclus cornutus | (Linnaeus, 1758) | Moorish idol | ||
Pomacentridae | Stegastes partitus | (Poey, 1868) | Bicolour damselfish | ||
Stegastes planifrons | (Cuvier, 1830) | Threespot damselfish | |||
Scaridae | Chlorurus microrhinos | (Bleeker, 1854) | Blunt-head parrotfish | ||
Scarus coelestinus | Valenciennes, 1840 | Midnight parrotfish | |||
Scarus iseri | (Bloch, 1789) | Striped parrotfish | |||
Sparisoma viride | (Bonnaterre, 1788) | Stoplight parrotfish | |||
(Pisces) Coelacanthi | Pomacanthidae | Holacanthus ciliaris | (Linnaeus, 1758) | Queen angelfish | |
Holacanthus passer | Valenciennes, 1846 | King angelfish | |||
Holacanthus tricolor | (Bloch, 1795) | Rock beauty | |||
Pomacanthus arcuatus | (Linnaeus, 1758) | Gray angelfish | |||
Pomacanthus paru | (Bloch, 1787) | French angelfish | |||
Pomacanthus zonipectus | (Gill, 1862) | Cortez angelfish | |||
Echinodermata (Asterozoa) | Asteroidea | Oreasteridae | Oreaster reticulatus | (Linnaeus, 1758) | Red cushion sea star, West Indian sea star |
Ophiuroidea | Ophiotrichidae | Ophiothrix (Ophiothrix) angulata | (Say, 1825) | Angular brittle star | |
Echinodermata (Echinozoa) | Echinoidea (Cidaroidea) | (Cidaroidea) Cidaridae | Eucidaris tribuloide | (De Lamarck, 1816) | Slate pencil urchin |
Echinoidea (Euechinoidea) | Arbaciidae | Arbacia punctulata | (De Lamarck, 1816) | Purple-spined sea urchin | |
Toxopneustidae | Lytechinus variegatus | (De Lamarck, 1816) | Variegated sea urchin, green urchin | ||
Arthropoda (Crustacea) | (Multicrustacea) (Copepoda) | Asterocheridae | Asterocheres suberitis | Giesbrecht, 1879 | Suberites copepod |
Arthropoda (Crustacea) ctnd. | (Multicrustacea) Malacostraca (Eumalacostraca) | (Alpheoidea) Alpheidae | Alpheus heterochaelis | Say, 1818 | Bigclaw snapping shrimp |
(Eriphioidea) Menippidae | Menippe mercenaria | (Say, 1818) | Southern or Florida stone crab | ||
(Palaemonoidea) Palaemonidae (Palaemoninae) | Palaemonetes vulgaris | (Say, 1818) | Marsh grass shrimp | ||
(Pilumnoidea) Pilumnidae (Pilumninae) | Pilumnus sayi | Rathbun, 1897 | Spineback hairy crab | ||
(Sphaeromatoidea) Sphaeromatidae | Paracerceis caudata | (Richardson, 1899) | Tailed isopod | ||
(Xanthoidea) Panopeidae (Panopeninae) | Dyspanopeus sayi | (Smith, 1869) | Say’s mud crab | ||
Panopeus herbstii | Milne Edwards, 1834 | Atlantic mud crab | |||
Annelida | Polychaeta | Syllidae | Branchiosyllis oculata | Ehlers, 1887 | Eyed gillworm |
Mollusca | Gastropoda (Caenogastropoda) | (Triphoroidea) Cerithiopsidae | Seila adamsi | (Lea, 1845) | Adam’s cerith snail |
Gastropoda (Heterobranchia) | (Doridoidea) Chromodorididae | Doriprismatica sedna | (Marcus and Marcus, 1967) | Sedna prism nudibranch | |
Felimare agassizii | (Bergh, 1894) | Agassizi’s coloured nudibranch | |||
(Doridoidea) Discodorididae | Platydoris argo | (Linnaeus, 1767) | Doris argo nudibranch | ||
(Phyllidioidea) Dendrodorididae | Doriopsilla albopunctata | (Cooper, 1863) | Whitespot Doris nudibranch | ||
Doriopsilla pharpa | Marcus, 1961 | Lemon drop nudibranch | |||
Gastropoda (Vetigastropoda) | (Fissurelloidea) Fissurellidae (Diodorinae) | Diodora cayenensis | (De Lamarck, 1822) | Cayenne keyhole limpet |
Appendix C
Published sponge bioerosion rates with reference to substrate types. For separate sponge species, we aimed to use data that had the same units or could be converted to match other published data (e.g. we looked for rates over time with reference to sponge tissue area or to reef area). Values for all sponges together may not be as easily related to each other, and caution is advisable when comparing these data. Data from settlement block experiments were not included, because in this context, they are not as meaningful and incur a high risk of variation or bias due to attachment mode and duration of exposure. Some means were hierarchically calculated to weigh data according to the subgrouping in the respective study (see Appendix D). Specific gravity of bulk densities refers to water at 4 °C, and references for material densities are referenced by highset numbers and citations at the bottom of the table. Part of the data displayed below were used for Fig. 7.7 (used only for zooxanthellate β-morphology sponges eroding biological skeleton or pure calcite, but excluding building materials such as limestone). GBR Great Barrier Reef. Bioeroding sponge morphologies are α papillate-endolithic, β encrusting-endolithic, γ free-living, δ endopsammic (for explanations, see main text or Schönberg et al. 2017). Further taxon information can be found in Appendix A (for bioeroding sponges) and in Appendix B (for non-sponge taxa).
Species, morphology | Location | Substrate material | Specific gravity | % substrate removed | Annual bioerosion [kg] per m2 sponge tissue | Annual bioerosion per m2 reef area | References |
---|---|---|---|---|---|---|---|
Photosymbiotic spp. (Percentages refer to the area of full sponge penetration only.) | |||||||
Cliona albimarginata, β | N Sulawesi | Prun limestone | 2.61, 19 | 2.9 | Calcinai et al. (2007a) | ||
Vicenza limestone | 21, 1.919 | 11.0 | |||||
Conero majolica | 2.81 | 12.6 | |||||
Coral: Acropora sp. | 2.31, 2.97 | 15.6 | |||||
Clam shell: Hippopus sp. | 2.71, 2.917 | 24.0 | |||||
Finale calcarenite | 2.01, 19 | 24.2 | |||||
Carrara marble | 2.71, 19 | 29.5 | |||||
Mean across substrates | 1.9–2.9 | 17.1 | |||||
Cliona aprica, α | Caribbean | Conch shells: Lobatus gigas | Ca. 50 | 7.0 | Rützler (1975, snail as Strombus) | ||
Cliona caribbaea, β | Grand Cayman | Coral (unspecified) | 1.71 | 20.0 | 8.0* | 0.4 | Acker and Risk (1985) |
Cliona flavifodina, α | Mexican Pacific | Coral: Pocillopora verrucosa | 2.82 | 0.5 | Nava and Carballo (2008) | ||
Cliona orientalis, β | Central GBR | Mollusc shell: bivalve? | 2.61 | 71.9 | Bergman (1983) | ||
Coral: coral rubble | 2.61 | 53.5 | |||||
Mollusc shell: cockscomb oyster | 2.61 | 55.0 | |||||
Coral (unspecified) | 1.21 | 47.0 | |||||
Mollusc shell: cockscomb oyster | 1.91 | 24.6 | |||||
Coral (unspecified) | 2.41 | 49.2 | |||||
Coral (unspecified) | 2.31 | 49.1 | |||||
Coral (unspecified) | 2.21 | 48.2 | |||||
Coral (unspecified) | 1.21 | 7.4 | |||||
Coral (unspecified) | 1.71 | 39.7 | |||||
Coral (unspecified) | 1.21 | 15.8 | |||||
Coral (unspecified) | 1.61 | 23.4 | |||||
Coral (unspecified) | 2.01 | 42.2 | |||||
Coral (unspecified) | 1.71 | 28.8 | |||||
Coral (unspecified) | 2.11 | 36.1 | |||||
Coral (unspecified) | 1.91 | 39.8 | |||||
Coral (unspecified) | 1.61 | 29.9 | |||||
Coral (unspecified) | 1.61 | 34.1 | |||||
Mean across all substrates | 1.2–2.6 | 38.6 | |||||
Cliona orientalis, β | Central GBR | Coral: Astreopora listeri | 1.31 | 3.4 | Schönberg (2002c, Dipsastrea as Favia) | ||
Coral: Goniopora tenuidens | 1.21 | 6.7 | |||||
Coral: Favites halicora | 1.41 | 6.8 | |||||
Coral: Cyphastrea serailia | 1.51 | 7.1 | |||||
Coral: Dipsastraea pallida | 1.61, 1.46 | 9.6 | |||||
Coral: massive Porites | 1.61, 1.214 | 9.7 | |||||
Coral: Goniastrea retiformis | 2.01, 1.76 | 10.3 | |||||
Clam shell: Tridacna squamosa | 2.81 | 17.6 | |||||
Mean across substrates | 1.2–2.0 | 8.9 | |||||
Cliona orientalis, β | Central GBR | Mineral: Iceland spar | 2.719 | 51.6 (central) 57.7 (marginal) | Schönberg and Shields (2008) | ||
Cliona orientalis, β | Central GBR | Coral: massive Porites | 1.61, 1.214 | 2.2 | Wisshak et al. (2012) | ||
Cliona orientalis, β | Southern GBR | Coral: massive Porites | 1.61, 1.214 | 2.5 | Fang et al. (2013b) | ||
Cliona orientalis, β | S Queensland | Coral: Goniastraea sp. | 2.01, 1.76 (for G. retiformis) | 6.1 | Holmes et al. (2009) | ||
Cliona varians, γ | Florida Keys | Calcite material | NA, ca. 2.5 | 22.8 | Hill (1996, as Anthosigmella) | ||
?Pione mussae, β | Aqaba | Reef rock | NA | 0.3 (2.6?)*** | Zundelevich et al. (2007) | ||
? – The predominant Red Sea Pione species has occasionally been reported to be photosynthetic (Beer and Ilan 1998; Steindler et al. 2001, both as Cliona vastifica), but it is not a typical species to contain dinoflagellate zooxanthellae | |||||||
Heterotrophic spp. (Percentages refer to the area of full sponge penetration only.) | |||||||
Cliona cf. celata, α | Bahía, Brazil | Coral: Siderastrea stellata | 1.81, 1.3–1.55 | 1.0 | Reis and Leão (2000) | ||
Cliona aff. celata, α | Central GBR | Mineral: Iceland spar | 2.719 | 90.7 (central) 79.1 (marginal) | Schönberg and Shields (2008) | ||
Cliona delitrix, α-β | Grand Cayman | Coral: Montastraea cavernosa | 1.71 | 53.0 | Rose and Risk (1985) | ||
Coral: Porites astreoides | 1.31, 1.418 | 47.0 | |||||
Mean across substrates | 1.3–1.7 | 50.0 | |||||
Cliona peponaca, α | Curaçao | Coral: Orbicella annularis | 1.7–2.16, 1.89, 1.418 | 2.5–3.3** | Bak (1976, Orbicella as Montastrea) | ||
Cliona vermifera, α | Mexican Pacific | Coral: Pocillopora verrucosa | 2.82 | 1.2 | Bautista-Guerrero et al. (2014) | ||
Clionaid sp. undet. (Pione lampa?) | Belize | Bivalve shells: Chama macerophylla | NA, >2.5 | Ca. 50 | 1.7–4.4 | Rützler (1975) | |
Pione lampa, β | Bermuda | Porous dolomite | 2.83 or < | 2.9 | Neumann (1966) | ||
Bermuda | Dense aragonite | 2.93 | 4.0–15.0 | ||||
Pione lampa, β | Bermuda | Iceland spar | 2.720 | 6.6–14.2 | Rützler (1975) | ||
Bermuda | Dense calcite | 2.73 | 18.9–23.8 | ||||
Entire guild of bioeroding sponges (Please note! Values below refer to the entire coral or to reef area studied and are thus these are different values than the above percentages, even if in the same column.) | |||||||
All sponge bioerosion | Bermuda | Different materials, mostly reef framework | NA | 0.26, or 3.0 where sponges dense | Rützler (1975) | ||
All sponge bioerosion | Florida Keys | Coral: Dichocoenia stokesii | 2.09 | 8.5 | Hein and Risk (1975, Pseudodiploria as Dodiploria, Orbicella as Montastrea)**** | ||
Coral: Pseudodiploria strigosa | 1.210 | 7.3 | |||||
Coral: Orbicella annularis | 1.7–2.16, 1.89, 1.418 | 3.5, 11.6 | |||||
Coral: Manicina areolata | NA | 2.8 | |||||
Coral: Siderastrea radians | 1.81, 1.3–1.55 (for S. stellata) | 33.4, 31.7 | |||||
Coral: all massive corals | 12.3 | ||||||
All sponge bioerosion | Veracruz | Coral: Orbicella annularis | 1.31 | 1.3 | Hernández-Ballesteros et al. (2013, Orbicella as Montastraea) | ||
Coral: Porites astreoides | 1.41 | 2.7 | |||||
Mean across all substrates | 1.3–1.4 | 2.0 | |||||
All sponge bioerosion | Yucatán | Coral: Orbicella annularis | 1.41 | 3.6 | Hernández-Ballesteros et al. (2013, Orbicella as Montastraea) | ||
Coral: Porites astreoides | 1.61 | 6.7 | |||||
Mean across all substrates | 1.4–1.6 | 5.2 | |||||
All sponge bioerosion | Yucatán | Coral: different species | NA | 16.4 per reef area | Hepburn et al. (2006) | ||
All sponge bioerosion | Belize | Coral: Orbicella annularis | 1.88 | 7.4 | Highsmith et al. (1983) | ||
Coral: Montastraea cavernosa | 1.61 | 4.6 | |||||
Coral: Porites astreoides | 1.51 | 4.1 | |||||
Mean across substrates | 1.5–1.8 | 5.4 | |||||
All sponge bioerosion | St. Thomas | Rubble, unspecified | NA | 47.0–88.5 | Weinstein et al. (2014) | ||
All sponge bioerosion | St. Croix | Coral cores: Acropora palmata | 1.916 | 41.3 (41.1–41.4) | 0.22 (0.21–0.23) | Moore and Shedd (1977) | |
Coral cores: Millepora sp. | 2.313 | 31.5 (31.0–32.0) | 5.23 (1.2–3.5) | ||||
Mean across all substrates | 1.9–2.3 | 36.4 | 0.37 | ||||
All sponge bioerosion | Barbados | Coral: Orbicella annularis | 1.7–2.16, 1.89, 1.418 | 9.4–11.6 | MacGeachy (1977, Orbicella as Montastrea) | ||
Coral: Porites astreoides | 1.418 | 3.3–6.2 | |||||
Coral Siderastrea siderea | 1.618 | 1.3–7.8 | |||||
Mean across all substrates | 1.4–1.8 | 0.28 | |||||
All sponge bioerosion | Barbados | Rubble, unspecified | NA | 24.0–41.0 | Holmes (2000) | ||
All sponge bioerosion | Barbados | Coral: Agaricia agaricites | 1.918 | 0.35 | Stearn and Scoffin (1977, Orbicella as Montastraea)***** | ||
Coral: Orbicella annularis | 1.7–2.16, 1.89, 1.418 | 0.35 | |||||
Coral: Porites astreoides | 1.418 | 0.14 | |||||
Coral Siderastrea siderea | 1.618 | 0.07 | |||||
Mean across all substrates | 1.4–1.9 | 0.23 | |||||
All sponge bioerosion | Barbados | Coralline algae | 0.5–0.711 | 0.47 | Scoffin et al. 1980, Orbicella as Montastraea)***** | ||
Coral: Agaricia agaricites | 1.917 | 0.29 | |||||
Coral: Orbicella annularis | 1.7–2.16, 1.89, 1.418 | 0.44 | |||||
Coral: Porites astreoides | 1.418 | 0.19 | |||||
Coral: Porites porites | 1.218 | 0.18 | |||||
Coral Siderastrea siderea | 1.617 | 0.09 | |||||
Mean across all substrates | 0.5–1.9 | 0.28 | |||||
All sponge bioerosion | Curaçao | Coral: Orbicella annularis | 1.7–2.16, 1.89, 1.418 | 2.4 | Bak (1976, Orbicella as Montastrea) | ||
Coral: Meandrina meandrites | 1.910 | 1.7 | |||||
Mean across substrates | 1.4–2.1 | 2.1 | |||||
All sponge bioerosion | Bonaire | Different coral spp. dominating | NA | 0.04 | Perry et al. (2012, Orbicella as Montastraea, Madracis myriaster as Madracis mirabilis; sponge bioerosion rates were estimated by using values from other oceans and species, partly not congeneric; development of the algorithm remains unclear as some of the cited works did not provide data for sponge tissue area—Scoffin et al. 1980—or did not separate sponge bioerosion from macroboring—Chazottes et al. 1995.) | ||
Mean across all substrates at non-diving sites, dominated by Orbicella annularis and Madracis myriaster | O. a nnularis: 1.7–2.16, 1.88, 1.418 M. m yriaster: 1.64 | 0.02 | |||||
Mean across all substrates | 0.03 | ||||||
All sponge bioerosion | Red Sea | Coral: Porites sp. | NA | 1.0 | Klein et al. (1991) | ||
All sponge bioerosion | Kenya | Branching coral: Porites cylindrica, Porites rus, Montipora digitata | 0.10–0.15 (fished and unfished) | Carreiro-Silva and McClanahan (2012, Montipora digitata as Porites palmata) | |||
All sponge bioerosion | Maldives | Coral rubble | NA | 0.03 | Morgan (2014) | ||
All sponge bioerosion | South China Sea | Coral: Porites lutea | 1.66 | 3.7 | Chen et al. (2013) | ||
All sponge bioerosion | Indonesia | Coral: Porites lobata | 1.412 | 2.8 | Holmes et al. (2000) | ||
All sponge bioerosion | Central GBR | Coral: Porites lobata | 1.412 | 1.8 | Sammarco and Risk (1990) | ||
All sponge bioerosion | Central GBR | Coral: Acropora muricata | 2.66 | Ca. 0.5–3.0 | Risk et al. (1995, as Acropora formosa) | ||
All sponge bioerosion | Central GBR | Massive Porites sp. | Likely 1.4–1.6, see above | 2.2 | Schönberg et al. (1997) | ||
All sponge bioerosion | Enewetak | Coral: Goniastraea retiformis | 1.71, 2.015 | 6.0 | Highsmith (1981a, Dipsastraea as Favia, Orbicella as Montastrea) | ||
Coral: Porites lutea | 1.41 | 2.0 | |||||
Coral: Dipsastraea pallida | 1.41, 1.615 | 0.9 | |||||
Rubble | NA | 3.8 |
References for material densities: 1Same reference as listed on the right. 2Al-Sofyani and Floos (2013), 3Barthelmy (1997–2014), 4Bruggemann et al. (1994), 5Carricart-Ganivet et al. (2013), 6Coraltraits (2016), 7Dunn et al. (2012), 8Dunstan (1975), 9Highsmith (1981b), 10Mallela (2004), 11McCoy (2013) for Pseudolithophyllum, 12Morgan and Kench (2012). 13Odum and Odum (1955), 14Risk and Sammarco (1991), 15Schönberg (2002b), 16Schuhmacher and Plewka (1981), 17Sowa et al. (2014), 18Stearn et al. (1977), 19StoneContact (2016), 20Wikipedia (2016b). *Acker and Risk (1985) calculated their value by using average growth rates and average sponge areas, and while the value was obtained by a different method than used by the other authors, the value aligns well (Fig. 7.7). **Bak (1976) did not state whether the areal reference for his bioerosion rates was sponge surface area or block area. In the latter case, the values would be meaningless, and it is here assumed that the reference is the sponge surface area. ***Zundelevich et al.’s (2007) total bioerosion rate was calculated by adding together their measures for chemical and mechanical bioerosion. However, they estimated mechanical bioerosion by quantifying the resulting sediment, which is likely an inaccurate method (see Discussion in Fang et al. 2013a; Schönberg et al. 2017). Chemical sponge bioerosion has previously been determined as being closer to 10% (Wisshak et al. 2013; Schönberg et al. 2017), which would mean that Zundelevich’s total bioerosion rates for P. mussae may have been around 2.6 kg m−2 yr.−1 instead of 0.3, a value which would be more similar to other published bioerosion rates for this genus. ****Hein and Risk’s (1975) values per coral species are all based on only one or two specimens. Their bioerosion rates were given as mm3 yr.−1, without reference to area. Therefore, the values could not be recalculated as standardised data. *****The sponge bioerosion rates from Stearn and Scoffin (1977) and Scoffin et al. (1980) were calculated by using their average contribution of sponges to total macroboring of 92%.
Appendix D
Proportional contributions of sponge, worm, mollusc and other bioerosion to total macroboring. Means were calculated hierarchical, e.g. first within a given study, then across studies, then across ocean, as outlined below. Where the published total did not exactly match the sum of the partial bioerosion, we set the sum of the partial bioerosion values to 100%. Taxonomic information for non-sponge taxa that form the substrate for bioeroding sponges can be found in Appendix B. Data were used for Figs. 7.5 and 7.8. A selection of data of block settlement experiments was here included, because by calculating values into %, they were all relative and thus comparable. However, block data were only used after a minimum of 1 year of exposure.
Ocean | Location | Substrate | Proportion of macrobioerosion [mean % of total] | References | |||
---|---|---|---|---|---|---|---|
Sponges | ‘Worms’ | Molluscs | Others | ||||
W Atlantic 1 | Florida Keys | Dichocoenia stokesii | 70.7 | 19.6 | 9.7 | NA | Hein and Risk (1975, Orbicella as Montastrea, Pseudodiploria as Diploria). Data were calculated from their Table 1 |
Orbicella annularis | 36.0 | 62.5 | 1.5 | NA | |||
Pseudodiploria strigosa | 31.5 | 34.0 | 34.5 | NA | |||
Pseudodiploria clivosa | 0.0 | 12.9 | 87.1 | NA | |||
Manicina areolata | 18.4 | 81.6 | 0.0 | NA | |||
Siderastrea radians | 66.7 | 29.7 | 3.6 | NA | |||
Means Florida Keys across substrates | 37.2 | 40.1 | 22.7 | NA | |||
W Atlantic 2 | Bahamas | Orbicella annularis | X-ray: 79.3 | X-ray: 16.0 | X-ray: 3.6 | X-ray: 1.1 | Becker and Reaka-Kudla (1997, Orbicella as Montastrea). Calculated from their Table 1. The paper compared X-ray and CAT scan |
CAT: 75.1 | CAT: 19.9 | CAT: 5.0 | CAT: 0.0 | ||||
Means Bahamas across different methods | Mean: 77.2 | Mean: 17.9 | Mean: 4.3 | Mean: 0.6 | |||
Jamaica 1, 1–30 m | Dead corals and rubble | 81.5 | 15.9 | 2.5 | 0.1 | Perry (1998). Calculated from his Table 3 | |
W Atlantic 3 | Jamaica 2, 0–8 m | Different coral spp. | 84.4 | 11.8 | 2.4 | 1.4 | Macdonald and Perry (2003). Calculated from their Table 3 |
8–16 m | 77.3 | 8.0 | 14.4 | 0.3 | |||
16–25 m | 71.1 | 6.4 | 20.4 | 2.1 | |||
Means Jamaica 2, across depths | 77.6 | 8.7 | 12.4 | 1.3 | |||
Means across Jamaica 1–2 | 79.6 | 12.3 | 7.4 | 0.7 | |||
W Atlantic 4 | St. Thomas (mesophotic) | Coral rubble | 73.4 | 7.9 | 14.5 | 4.2 | Weinstein et al. (2014). Data were read off their Fig. 4, lowest part |
Barbados | Orbicella annularis, 0–15 m | 95.7* | 1.8* | 0.3 | 2.2 | MacGeachy and Stearn (1976, Orbicella as Montastrea). Data were calculated from their Table 7.2. *The value for sponges includes bioerosion from spionids and should be smaller; the one for worms should be larger | |
W Atlantic 5 | Barbados | Orbicella annularis, 0–15 m | 92.0 | 1.4 | 0.0 | 6.6 | Scoffin et al. 1980, Orbicella as Montastrea). Data were calculated from their p. 486. Data are part of the above study. These values are only for the part of the study in which worms were common. As they accounted for <3% of macroboring, they were ignored at the other sites, which were part of the studies for MacGeachy and Stearn (1976) |
Means Barbados across studies | 93.9 | 1.6 | 0.1 | 4.4 | |||
W Atlantic 6 | Veracruz Reefs | Orbicella annularis | 79.3 | 5.3 | 12.4 | 3.0 | Hernández-Ballesteros et al. (2013, Orbicella as Montastrea). Data were calculated from their Table 1 |
Porites astreoides | 73.7 | 20.7 | 5.6 | 0.0 | |||
Means Veracruz across different substrates | 76.5 | 13.0 | 9.0 | 1.5 | |||
W Atlantic 7 | Puerto Morelos, N Yucatán | Coral rubble | 76.2 | 4.9 | 18.2 | 0.7 | Hepburn et al. (2006). Data were read off their Fig. 3 |
S Yucatán | Orbicella annularis | 94.5 | 0.5 | 4.2 | 0.8 | Hernández-Ballesteros et al. (2013, Orbicella as Montastrea). Data were calculated from their Table 1 | |
Porites astreoides | 89.8 | 6.2 | 4.0 | 0.0 | |||
Means S Yucatán across different substrates | 92.1 | 3.4 | 4.1 | 0.4 | |||
Means Yucatán across N and S | 84.1 | 4.2 | 11.2 | 0.5 | |||
W Atlantic 8 | Belize, 2–7 m | Orbicella annularis | 93.8 | 2.3 | 2.2 | 1.7 | Highsmith et al. (1983, Orbicella as Montastrea). Data were calculated from their Table 2. Where the sum of their percentages did not reach 100%, values were recalculated so that it did |
Montastrea cavernosa | 91.0 | 3.0 | 3.5 | 2.5 | |||
Porites astreoides | 84.0 | 16.0 | 0.0 | 0.0 | |||
Means Belize across different substrates | 89.6 | 7.1 | 1.9 | 1.4 | |||
W Atlantic 9 | Bahía, Brazil | Siderastrea stellata | 35.0 | 15.0 | 50.0 | 0.0 | Reis and Leão (2000). Data were read off their Fig. 2 |
Means W Atlantic 1–9 | 71.8 | 13.2 | 13.5 | 1.5 | |||
Indian Ocean 1 | Red Sea | Porites spp. | 23.9 | 41.3 | 19.2 | 15.6 | Klein et al. (1991). Data were calculated from their Table 1. Only their recent material was considered, not the fossil substrate |
(Indian Ocean) | Persian Gulf | Dead corals | (2.2) | (27.4) | (46.9) | (23.5) | Jafari et al. (2016). It seems that the authors included embedding barnacles as bioeroders (?), and perhaps sponge bioerosion is underestimated? The values are here displayed, but not used in the overall calculations |
Without barnacles: | |||||||
(2.8) | (35.8) | (61.3) | (NA) | ||||
Indian Ocean 2 | Kenya fished | Branching coral: Porites cylindrica, Porites rus, Montipora digitata – 6 years after coral death | 47.4 | 44.3 | 8.4 | NA | Carreiro-Silva and McClanahan (2012, Montipora digitata as Porites palmata). Data were calculated from their App. 1 |
Kenya unfished | 58.4 | 33.4 | 8.1 | NA | |||
Means Kenya | 52.9 | 38.9 | 8.2 | NA | |||
Maldives 1 at 5 m | Porites sp. (blocks – 14-month exposure) | 62.4 | 28.5 | 9.1 | NA | Zahir (2002) Data were read off his Fig. 3 | |
Maldives 1 at 10 m | 23.6 | 48.7 | 27.7 | NA | |||
Means Maldives 1 | 43.0 | 38.6 | 18.4 | NA | |||
Indian Ocean 3 | Maldives 2 lagoon | Acropora rubble | 74.1 | 22.2 | 3.7 | NA | Morgan (2014). Data were read off his Fig. 4.5. |
Maldives 2 inner reef | 51.2 | 29.1 | 19.7 | NA | |||
Maldives 2 outer reef | 32.0 | 37.7 | 30.3 | NA | |||
Means Maldives 2 | 52.4 | 29.7 | 17.9 | NA | |||
Means Maldives across 1–2 | 47.7 | 34.2 | 18.1 | NA | |||
Means Indian Ocean 1–3 | 41.5 | 38.1 | 15.2 | 5.2 | |||
W Pacific 1 | Daya Bay, South China Sea | Porites lutea | 38.3 | 5.7 | 48.0 | 8.0 | Chen et al. (2013). Data were calculated from their Fig. 3 |
W Pacific 2 | Lizard Island, northern GBR 1, windward | Porites lutea (blocks – 5-year exposure, at 1–20 m) | 33.3 | 39.4 | 27.3 | NA | Kiene and Hutchings (1994). Data were read off their Fig. 3. The eight sites were grouped by us, so that leeward sites included the channel and leeward slope and deep sites |
Flat and lagoon | 10.2 | 86.2 | 3.6 | NA | |||
Leeward sites | 66.1 | 26.5 | 7.4 | NA | |||
Means northern GBR 1 | 36.5 | 50.7 | 12.8 | NA | |||
Northern GBR 2, two inshore sites | Massive Porites (blocks – 4-year exposure, at 7–10 m) | 35.8 | 34.6 | 29.6 | NA | Hutchings et al. (2005). Data were read off their Fig. 7.3. The sites for this and the following two studies were inshore sites, Snapper Island and Low Isles; midshelf site, Lizard Island; reef edge sites, Harrier Reef and Ribbon Reef 3; and an oceanic site, Osprey Reef | |
One midshelf site | 11.7 | 71.6 | 16.7 | NA | |||
Two reef edge sites | 18.1 | 44.7 | 37.2 | NA | |||
One oceanic site | 18.4 | 75.8 | 5.8 | NA | |||
Means northern GBR 2 | 21.0 | 56.7 | 22.3 | NA | |||
Northern GBR 3, two inshore sites | Massive Porites (blocks – 4-year exposure, at 7–10 m) | 41.7 | 26.7 | 31.6 | NA | Osorno et al. (2005). Data were calculated from their Table 1 | |
One midshelf site | 21.9 | 63.3 | 14.9 | NA | |||
Two reef edge sites | 17.2 | 45.9 | 36.9 | NA | |||
One oceanic site | 18.8 | 72.4 | 8.8 | NA | |||
Means northern GBR 3 | 24.9 | 52.1 | 23.0 | NA | |||
Northern GBR 4, two inshore sites | Massive Porites (blocks – 3-year exposure) | 35.6 | 32.0 | 32.4 | NA | Tribollet and Golubic (2005). Data were calculated from their Table 3 | |
One midshelf site | 20.1 | 74.8 | 5.1 | NA | |||
Two offshore sites | 15.8 | 58.2 | 26.0 | NA | |||
One oceanic site | 18.0 | 69.1 | 12.9 | NA | |||
Means northern GBR 4 | 22.4 | 58.5 | 19.1 | NA | |||
Means northern GBR across studies 1–4 | 23.9 | 53.2 | 22.9 | NA | Averaged by distance from shore first, then across studies | ||
Central GBR, One inshore site | Porites lobata, from 7–9 m | 22.6 | 24.8 | 52.6 | NA | Sammarco and Risk (1990). Data were calculated from their Table 3. The sites were inshore, Orpheus Island; midshelf, Britomart, Rib and Davies Reef; and offshore, Myrmidon Reef | |
Three midshelf sites | 58.3 | 26.7 | 15.0 | NA | |||
One offshore site | 38.7 | 54.6 | 6.7 | NA | |||
Means central GBR for Porites 1 | 39.9 | 35.4 | 24.7 | NA | |||
Central GBR, one inshore site | Massive Porites | 20.4 | 4.1 | 75.5 | NA | Schönberg et al. (1997). Data were read off their Fig. 1. ‘Worms’ included ‘other’ bioerosion. The sites were inshore, Pandora Reef; midshelf, Rib Reef; and offshore, Myrmidon Reef | |
One midshelf site | 68.5 | 14.8 | 16.7 | NA | |||
One offshore site | 57.7 | 19.2 | 23.1 | NA | |||
Means central GBR for Porites 2 | 48.9 | 12.7 | 38.4 | NA | |||
Means central GBR for Porites across studies 1–2 | 44.4 | 24.0 | 31.6 | NA | |||
Central GBR, Two inshore sites | Acropora muricata, at 6–8 m | 77.8 | 12.0 | 6.2 | 4.0 | Risk et al. (1995, as Acropora formosa). Data were calculated from their Table 3 | |
Three midshelf sites | 69.7 | 15.5 | 11.5 | 3.3 | |||
One offshore site | 48.0 | 42.5 | 7.5 | 2.0 | |||
Means central GBR for Acropora | 65.2 | 23.3 | 8.4 | 3.1 | |||
Means central GBR across substrates | 54.8 | 23.7 | 20.0 | 1.5 | |||
Means across GBR | 39.5 | 38.5 | 21.4 | 0.7 | |||
Western Pacific 3 | Java Sea, low resuspension | Coral: Porites lobata | 54.1 | 27.4 | 8.1 | 10.4 | Holmes et al. (2000). Data were read off their Figs. 1 and 4. Data were grouped by us with respect to resuspension levels |
Ambon, low resuspension | 57.0 | 24.9 | 15.1 | 3.0 | |||
Means low resuspension | 55.6 | 26.1 | 11.6 | 6.7 | |||
Java Sea, high resuspension | Coral: Porites lobata | 46.6 | 18.6 | 12.1 | 22.7 | ||
Means Indonesia across suspension levels | 51.1 | 22.3 | 11.9 | 14.7 | |||
Means Western Pacific 1–3 | 43.0 | 22.1 | 27.1 | 7.8 | |||
Central Pacific 1 | Enewetak, 0–30 m | Goniastrea retiformis | 76.1 | 1.3 | 4.0 | 18.6 | Highsmith (1981b). Data were calculated from his Table 5 |
Porites lutea | 82.3 | 10.9 | 1.5 | 5.3 | |||
Dipsastraea pallida | 75.0 | 25.0 | 0.0 | 0.0 | |||
Rubble | 69.8 | 15.4 | 3.7 | 11.1 | |||
Means Enewetak across substrates | 75.8 | 13.2 | 2.3 | 8.7 | |||
Central Pacific 2 | Moorea and Tahiti | Porites lutea (blocks – 5-year exposure) | 42.9 | 36.3 | 20.8 | NA | Pari et al. (2002). Data were read off their Fig. 3 |
Polynesia atolls | 72.8 | 26.7 | 0.5 | NA | |||
Means French Polynesia across sites | 57.9 | 31.5 | 10.6 | NA | |||
Means Central Pacific 1–2 | 66.9 | 22.4 | 6.4 | 4.3 | |||
Eastern Tropical Pacific (ETP) | Porites lobata | 11.9 | 0.0 | 88.1 | 0.0 | Carballo unpubl. data (2017) | |
Means Pacific | 40.6 | 14.8 | 40.5 | 4.1 | |||
Means World | 51.3 | 22.0 | 23.1 | 3.6 |
Appendix E
Spongivorous organisms feeding on bioeroding sponges (see also Fig. 7.6). Only examples of feeding directly on the sponges are here reported; experiments using sponge-extract infused artificial pellets are not listed. Taxonomic information can be found in Appendix A (for bioeroding sponges) and in Appendix B (for non-sponge taxa).
Sponge species | Predator species | Location | Observation | Reference |
---|---|---|---|---|
Cervicornia cuspidifera | Sea star, Oreaster reticulatus | San Blas, Caribbean | The sea star fed on the sponge in a feeding choice experiment | Wulff (1995) |
Cliona albimarginata | Parrotfish, Bolbometopon sp. | N Sulawesi | The fish feeding on the sponge | Calcinai et al. (2005) |
Cliona ampliclavata | Nudibranch, Doriprismatica sedna | Mexican Pacific | The nudibranch consumed C. ampliclavata | Verdín Padilla et al. (2010, as Glossodoris sedna) |
Cliona californiana | Nudibranchs, Doriprismatica sedna and Felimare agassizii | Mexican Pacific | The nudibranchs consumed C. californiana | Verdín Padilla et al. (2010, as Glossodoris sedna and Hypselodoris agassizii) |
Cliona caribbaea | Parrotfishes, wrasses, surgeonfishes | Caribbean | Evidenced by occasional bite marks | Acker and Risk (1985) |
Cliona cf. celata | Nudibranch, Doriopsilla albopunctata | California? | From the literature | Bloom (1976) |
Cliona cf. celata | Keyhole limpet, Diodora cayenensis, cerithid snail, Seila adamsi, isopod, Paracerceis caudata, snapping shrimp, Alpheus heterochaelis, grass shrimp, Palaemonetes vulgaris, brachyurid crabs, Menippe mercenaria, and Pilumnus sayi, xanthid crabs, Panopeus herbstii, and Dyspanopeus sayi, urchins, Arbacia punctulata and Lytechinus variegatus, and possibly the brittle star Ophiothrix (Ophiothrix) angulata | N Carolina | Feeding experiments with starved potential predators using undisturbed C. cf. celata specimens and specimens of which the endosome was exposed revealed that many organisms will feed on that sponge, depending on access | Guida (1976, as Cilicaea cordata and Neopanope sayi) |
Cliona cf. celata | Nudibranch, Doriopsilla pharpa | S Carolina | Faeces and laboratory observations confirmed that the nudibranch fed on C. cf. celata but less during winter when C. celata cf. retracted | Eyster and Stancyk (1981) |
Snapping shrimp, Alpheus heterochaelis | S Carolina | The shrimp consumed the nudibranch and C. cf. celata papillae | ||
Cliona euryphylle | Angelfishes, Holacanthus passer and Pomacanthus zonipectus | Mexican Pacific | The fishes consumed C. euryphylle | Verdín Padilla et al. (2010) |
Cliona flavifodina | Nudibranch, Doriprismatica sedna | Mexican Pacific | The nudibranch consumed C. flavifodina | Verdín Padilla et al. (2010, as Glossodoris sedna) |
Cliona orientalis | Parrotfish, Chlorurus microrhinos | Central Great Barrier Reef | C. orientalis was observed with occasional parrotfish bite marks | Schönberg et al. (2017) |
Cliona papillae | Angelfishes, Holacanthus passer, Pomacanthus zonipectus and the nudibranchs, Doriprismatica sedna and Felimare agassizii | Mexican Pacific | The fishes and the nudibranchs consumed C. papillae | Verdín Padilla et al. (2010, as Glossodoris sedna and Hypselodoris agassizii) |
Cliona tenuis | Parrotfishes, Scarus iseri, Scarus coelestinus and Sparisoma viride; damselfishes, Stegastes planifrons and Stegastes partitus and the surgeonfish Acanthurus coeruleus | Belize, Caribbean | The fishes were observed to feed on C. tenuis, and bite frequency decreased in listed sequence | González-Rivero et al. (2012) |
Cliona varians | Sea star, Oreaster reticulatus | San Blas, Caribbean | The sea star fed on the sponge in the field and in a feeding choice experiment | Wulff (1995, as Anthosigmella varians) |
Cliona varians | Angelfish, Pomacanthus paru | Caribbean | Gut content analysis confirmed that the fishes ate C. varians | Randall and Hartman (1968, as Anthosigmella varians) |
Cliona varians | Angelfishes, Pomacanthus arcuatus and Pomacanthus paru | US Virgin Islands, Caribbean | The fishes consumed C. varians | Hourigan et al. (1989) |
Cliona varians | Angelfish, Pomacanthus arcuatus | Florida Keys | Uncaged C. varians exhibited bite marks | Hill (1998) |
Cliona varians | Angelfishes, Holacanthus ciliaris, Pomacanthus arcuatus and Pomacanthus paru, hawksbill turtle Eretmochelys imbricate (It is not clear, however, which of these, or all, targeted the sponge.) | Florida Keys | Uncaged branching C. varians morphs were eaten and lost their branches | Hill and Hill (2002, as Anthosigmella varians) |
Cliona varians | Angelfish, Pomacanthus paru | Brazil | C. varians was consumed by the angelfish, as evidenced by gut content | Batista et al. (2012) |
Cliona viridis | Copepod, Asterocheres suberitis | W Mediterranean | Copepod behaviour was studied with videography | Mariani and Uriz (2001) |
Cliothosa aurivillii | Copepod, Tisbe sp. | Central Great Barrier Reef | C. aurivillii became infested with copepods that produced faeces in the colour of the sponge | Schönberg and Wisshak (2012) |
Cliona sp. | Angelfishes, Holacanthus tricolor, Pomacanthus arcuatus and Pomacanthus paru | US Virgin Islands, Caribbean | The fishes consumed Cliona sp. | Hourigan et al. (1989) |
Cliona sp. or spp. | Sea star, Oreaster reticulatus | San Blas, Caribbean | The sea star fed on Cliona sp. in the field and in a feeding choice experiment | Wulff (1995) |
Cliona spp. | Sea urchin, Eucidaris tribuloides | Bahía, Brazil | Spicules found in the urchin guts showed that it fed on clionaid sponges | Santos et al. (2002) |
Cliona sp. | Angelfishes, Holacanthus passer and Pomacanthus zonipectus | Mexican Pacific | The fishes consumed Cliona sp. | Verdín Padilla et al. (2010) |
Unidentified clionaid | Angelfish, Pomacanthus paru | Brazil | The clionaid was consumed by the angelfish, as evidenced by gut content | Batista et al. (2012) |
Pione carpenteri | Angelfish, Holacanthus passer, and the nudibranch, Doriprismatica sedna | Mexican Pacific | The fish and the nudibranch consumed P. carpenteri | Verdín Padilla et al. (2010, as Cliona mazatlanensis) |
Pione mazatlanensis | Angelfish, Holacanthus passer, and the nudibranchs, Doriprismatica sedna and Felimare agassizii | Mexican Pacific | The fish and the nudibranch consumed P. mazatlanensis | Verdín Padilla et al. (2010, as Cliona mazatlanensis, Glossodoris sedna and Hypselodoris agassizii) |
Pione vastifica | Nudibranch, Platydoris argo | Strait of Gibraltar | Gut contents were studied to find that the nudibranch fed on P. vastifica | Megina et al. (2002, as Cliona vastifica) |
Spheciospongia vagabunda | Wrasse, puffer fish and the hawksbill turtle, Eretmochelys imbricata? | Papua New Guinea | Sponges were found with feeding damage and rejected fragments strewn near them. Predators were tentatively identified from the form of the feeding scars | Kelly (1986, as Spirastrella vagabunda) |
Spheciospongia vesparium | Angelfishes, Holacanthus ciliaris, Holacanthus tricolor and Pomacanthus paru | Caribbean | Gut content analysis confirmed that the fishes ate S. verparium | Randall and Hartman (1968) |
Spheciospongia vesparium | Polychaete, Branchiosyllis oculata | Bermuda | Polychaetes changed colour, depending on which sponge they were, and feeding was confirmed by examining the gut content | Pawlik (1983, as Spheciospongia othella) |
Spheciospongia vesparium | Sea star, Oreaster reticulatus | San Blas, Caribbean | The sea star fed on the sponge in a feeding choice experiment | Wulff (1995) |
Spheciospongia sp. | Hawksbill turtle, Eretmochelys imbricata | Seychelles | Oesophageal lavage yielded the material that showed that the turtles were eating Spheciospongia sp. | |
Spheciospongia sp. | Surgeonfish, Acanthurus pyroferus; butterfly fishes, Chaetodon kleinii, Chaetodon vagabundus; and idol, Zanclus cornutus | Wakatobi, Banda Sea | The fishes fed on the sponge | Powell et al. (2015) |
Spirastrella coccinea | Angelfishes, Holacanthus ciliaris, Holacanthus tricolor, Pomacanthus arcuatus and Pomacanthus paru | Caribbean | Gut content analysis confirmed that the fishes ate S. coccinea | Randall and Hartman (1968) |
Spirastrella coccinea | Angelfishes, Pomacanthus arcuatus and Pomacanthus paru | San Blas, Caribbean | During field observations the bites were counted the fishes took from S. coccinea | Wulff (1994) |
Spirastrella coccinea | Hawksbill turtle, Eretmochelys imbricata | Dominican Republic, Caribbean | Oesophageal lavage yielded the material that showed that the turtles were eating S. coccinea | León and Bjorndal (2002) |
Spirastrella cf. cunctatrix | Sea star, Oreaster reticulatus | San Blas, Caribbean | The sea star was observed to feed on the sponge in the field | Wulff (1995) |
Spirastrella decumbens | Angelfishes, Holacanthus passer and Pomacanthus zonipectus | Mexican Pacific | The fishes consumed S. decumbens | Verdín Padilla et al. (2010) |
Spirastrella hartmani | Angelfish, Pomacanthus paru | Brazil | S. hartmani was consumed by the angelfish, as evidenced by gut content | Batista et al. (2012) |
Spirastrella sp. | Angelfishes, Pomacanthus paru, Holacanthus ciliaris and H. tricolor | Bahía, Brazil | Spirastrella sp. was commonly consumed by the angelfishes, as evidenced by gut content | Andréa et al. (2007) |
Thoosa mismalolli | Angelfishes | Mexican Pacific | The fishes consumed T. mismalolli | Verdín Padilla et al. (2010) |
Thoosa sp. | Angelfishes, Holacanthus passer and Pomacanthus zonipectus | Mexican Pacific | The fishes consumed Thoosa sp. | Verdín Padilla et al. (2010) |
Rights and permissions
Copyright information
© 2017 Springer International Publishing AG
About this chapter
Cite this chapter
Schönberg, C.H.L., Fang, J.KH., Carballo, J.L. (2017). Bioeroding Sponges and the Future of Coral Reefs. In: Carballo, J., Bell, J. (eds) Climate Change, Ocean Acidification and Sponges. Springer, Cham. https://doi.org/10.1007/978-3-319-59008-0_7
Download citation
DOI: https://doi.org/10.1007/978-3-319-59008-0_7
Published:
Publisher Name: Springer, Cham
Print ISBN: 978-3-319-59007-3
Online ISBN: 978-3-319-59008-0
eBook Packages: Biomedical and Life SciencesBiomedical and Life Sciences (R0)