Porifera Research: Biodiversity, Innovation and Sustainability - 2007 247 Observations on reef coral undermining by the Caribbean excavating sponge Cliona delitrix (Demospongiae, Hadromerida) Andia Chaves-Fonnegra, Sven Zea(*) Departamento de Biología and Centro de Estudios en Ciencias del Mar – CECIMAR, Universidad Nacional de Colombia, INVEMAR, Cerro Punta de Betín, AA 10-16, Santa Marta, Colombia. [email protected], [email protected] Abstract: Sponges which simultaneously encrust and excavate calcareous substratum are strong space competitors in coral reefs, actively undermining and displacing live coral tissue. On Caribbean reefs, Cliona delitrix colonizes massive corals, encrusting, deeply excavating and aggressively killing entire coral heads. To establish the details of the process of colonization, excavation, undermining and death of corals by this sponge, we carried out observations on sponge-colonized corals at San Andrés Island (SW Caribbean Colombia), and obtained samples for microscopical observation. As it spreads sideward, C. delitrix removed the upper few mm of the coral skeleton, maintaining its surface slightly lower than the surrounding coral, following the curved outline of the coral head. Internal excavation resulted in a solid outer supporting frame and a strongly eroded lace-like internal network. The outer frame was perforated below inhalant papillae by narrow vertical tunnels and below the large oscules by wide and deep spaces. A band of dying or dead coral surrounded the sponge. The sponge sent out a front of tissue using pioneering filaments projecting underneath the coral polyps. Long filaments may surface farther off, forming new bodies that later fuse. From microscopical observations, physical detachment of polyps was ruled out as the cause of coral death, because coral tissue displacement occurred before significant erosion of the polypar skeletal support had taken place. When sponge tissue reached underneath coral tissue, the latter remained healthy when still separated by thin skeletal barriers, but appeared as debris when barriers were broken. Live sponge and coral tissue could occur in direct contact, in which case there was accumulation of granulous cells in the coral tissue. We hypothesize that the mechanism of coral death involves close-range tissue, cell and/or biochemical interactions rather than fluid- or mucus-borne allelochemicals. Keywords: Cliona delitrix, excavation, corals, colonization, cell-cell interactions, Caribbean reefs. Introduction Sessile colonial organisms living on hard substrata often compete for space by overtopping or directly overgrowing their neighbors. Takeover of space could be achieved by fast lateral growth that smothers and kills the overgrown tissue, but the neighbor’s tissue death could precede or parallel space takeover through deployment of aggressive appendages at the boundary and/or release of allelochemical substances (Jackson and Buss 1975, Suchanek and Green 1981, Lang and Chornesky 1990). Upright growing organisms with a limited holdfast area avoid competing for space with more massive or encrusting ones. Similarly, organisms able to penetrate and excavate into the substratum limit competition with organisms dwelling over the surface of the substratum to those points of their body that are exposed (Jackson 1979, Woodin and Jackson 1979). Excavating (burrowing, boring) sponges live in cavities that they themselves bore into calcium carbonate (corals and coralline substratum, mollusk shells, polychaete tubes, calcareous algae) (Goreau and Hartman 1963, Rützler 1975). Excavation is achieved by both mechanical and chemical etching and removal of coarse silt-size grains through filopodial extensions of the basal epithelium cellular membrane (see Rützler and Rieger 1973, Pomponi 1977). Many species only expose papillae and oscula through which food and oxygen are taken and wastes eliminated. However, several species also encrust the excavated substratum and aggressively compete for space with corals and other reef organisms. Some may overgrow live tissue of neighboring organisms (e.g. Vicente 1978). Others, however, avoiding external defense mechanisms of their neighbors, bore directly under them, sending excavating tissue fronts preceded by pioneering tissue filaments, making neighbors detach, apparently by eroding their support (Ward and Risk 1977, Schönberg and Wilkinson 2001, Rützler 2002, López-Victoria et al. 2003, 2006). Some papillated sponges also kill surrounding coral tissue by releasing mucus presumably laden with allelopatic compounds (Sullivan et al. 1983, Sullivan and Faulkner 1990). The encrusting and excavating sponge Cliona delitrix Pang, 1973 (lat. delitrix: a destroyer; Hadromerida: Clionaidae) is considered one of the most destructive bioeroders in reef corals. It appears as an encrusting layer of bright scarlet tissue of closely spaced papillae and interspersed large, high collared oscules in which deep exhalant canals open (Pang 1973). It 248 penetrates deeply (down to 10-12 cm or more) into the coral skeleton, filling existing and newly eroded spaces with tissue. The lateral and vertical expansion of the sponge eventually leads to the overpowering of entire coral heads, sometimes as large as 1 m in diameter (Pang 1973, Rose and Risk 1985). The sponge is often surrounded by a band of dead coral from where live coral tissue has been eliminated (Pang 1973, Rose and Risk 1985), but the exact mechanism by which this is achieved is not known. Cliona delitrix has been reported to increase in abundance in recent decades, at the expense of live corals, in various reef areas subjected to nutrient runoff and organic pollution (Rose and Risk 1985, Ward-Paige et al. 2005, Chaves-Fonnegra et al. in press). With the aim of obtaining a better understanding how encrusting excavating sponges in general, and C. delitrix in particular, confront, erode, and kill reef corals, we undertook detailed field observations on the sponge and its host corals at San Andrés Island (SW Caribbean, Colombia), and histological analyses of samples from the sponge-coral boundary, to establish: (1) substratum preferences and growth forms, (2) overall excavation processes and, (3) details on the undermining and killing of live coral tissue. Materials and methods San Andrés (12°32’N, 81°43’W) is an oceanic island of coralline origin, located in the SW Caribbean and surrounded by a calcareous platform with a windward barrier reef, a lagoon with patch reefs, and leeward and windward fore reef terraces with coral carpets (Díaz et al. 1995, 1996). Observation and sampling took place throughout the leeward, western margin of the island. There, individuals of Cliona delitrix were photographed and observed in detail, noting its host coral species or substratum (pavement, old dead coral), surface characteristics, aspect of the zone of interaction with live coral, etc. To understand why Cliona delitrix tended to grow at a slightly deeper level than the surrounding substratum, we made detailed observations and measured the depth of the sponge at the boundary step using the butt of a caliper (Fig. 1). To study excavation patterns, several live sponges were fragmented with hammer and chisel. By bathing in commercial bleach remains of dead sponges and small coral heads completely colonized by a live sponge, intact clean skeletons were obtained. To obtain a crude estimate of the depth of sponge excavation inside the coral skeleton, a bicycle steel ray was forcefully driven perpendicularly through one sponge papilla, approximately at the center of the sponge (Fig. 1). This was done only in sponges whose host coral was still alive. The ray was then retrieved and the depth of penetration measured with a caliper. The size of the sponge, measured as projected surface area, was statistically correlated to the depth of the ray penetration using Pierson’s product-moment correlation coefficient (Sokal and Rohlf 1981). Surface area was obtained from digital photos using the Coral Count Point Program with Excel extension (NCRI-NOVA). To understand the way in which Cliona delitrix excavates under live coral tissue, portions of the coral at the sponge border were detached with hammer and chisel. Structures were measured with a caliper and sketches of the sections Fig. 1: Cross-section diagram of a massive coral colonized by Cliona delitrix, showing how measurements of the difference in depth between the sponge surface and the surrounding coral skeleton (step), and the approximate depth of excavation (bicycle ray) were measured. were made. Some fragments were fixed for histology in seawater 10% formalin neutralized with methenamine (20 gL-1) for three days, after which they were stored in 70% ethanol. In the laboratory samples were trimmed and cut into 2 mm thick slabs with a petrographic low speed circular diamond saw (Isomet®, Buehler, Chicago). They were then dehydrated, stained (acid fucsin and crystal violet), and embedded in Spurr’s low viscosity resin (ERL 4206, Electron Microscopy Sciences). Resin blocks were cut in two and each cut section was glued onto microscope slides using fresh resin. Each section was then ground in a low speed Polisher/Grinder (Minimet 1000®, Buehler, Chicago) with diamond-coated grinding paper of increasingly finer grain (79-9 μm), and then polished by hand with carburendum 1500 grit paper and metal polishing paste (for details see Rützler 1974, Willenz and Pomponi 1996, López-Victoria 2003). Results Substratum preferences and growth forms Most individuals of Cliona delitrix were found growing on live massive corals or on elevated substratum (old dead coral); none were colonizing branching or thin foliaceous corals and only a few were dwelling directly on the flat calcareous pavement (Fig. 2A, B). There was no mucus on the surface nor was it produced when the sponge was handled. The few small sponge individuals seen were always on dead areas of corals, and consisted generally of an oscule with surrounding papillae, separated or fused (Fig. 2C); individuals larger than 3-5 cm always completely encrusted the surface of the excavated area (Fig. 2D). Sponges had inhalant papillae throughout their surfaces (Fig. 3A), but often the external border of a given colony was comprised of a belt of smooth and level tissue, lacking papillae (Fig. 3B). General observations on the excavation process The surface of Cliona delitrix colonies was 0.1 to 1.7 cm lower than the surrounding substratum (from 164 measuring 249 Fig. 2: Underwater photographs of Cliona delitrix. A. On coral Siderastrea siderea. B. On pavement. C. Young individual on dead coral. D. Small individual growing on coral Siderastrea siderea. points in 30 sponges), being variable within coral species (mean±1 standard deviation; Diploria labyrinthiformis 0.5±0.2 cm, n=4; Porites astreoides 0.9±0.8 cm, n=2; Siderastrea siderea 0.5±0.5 cm, n=24; statistical tests were not carried out because of low sample sizes of all but one coral species). The surfaces of the sponges that were found within about 0.5-1 cm of live coral tissue were only a few mm deeper than that of the coral (Fig. 2D). At greater distances the surrounding substratum could be higher, forming a step, because while the sponge eroded the outer coral skeleton to about the same elevation, the surrounding live coral (or dead coral covered by crustose coralline algae) had grown further upwards (Fig. 3B, C). As the sponge spread, it apparently carved the wall of the step by undermining its base, often with tissue fingers and papillae appearing beyond the wall margin (Fig. 3B; 4A, D). When live coral was at some distance from the sponge, its new upward growth formed a second step (Fig. 3B). Apart from oscular collars and papillae, the sponge did not elevate its tissue above the initial level. A single individual of Cliona delitrix could overtake and completely encrust a medium size (up to ca. 30-50 cm in diameter) coral head (Fig. 3D). In larger coral heads the sponge was frequently characterized by several contiguous mounds, which we assumed were formerly surviving islands of coral that grew upward until the sponge covered them (Fig. 3C, E). Fragmentation of a few whole coral colonies revealed that the sponge could send tissue filaments of about 1 mm in diameter that would extend into the coral skeleton as far as 10 cm from the main sponge body, surfacing to form new sponge bodies, which would later fuse with the main body. From inspection of dead sponges and bleached fragments we found that just below the dermis of the sponge there remained a rather solid frame, 3 to 6 mm thick, perforated by vertical tunnels located below each papilla, and by ample and deep cavities below oscules (Fig. 3F). Vertical tunnels were made directly into each coral calyx, eroding continuously downwards (allowing the insertion of bicycle rays to measure approximate depth of excavation). Below the frame, the skeleton was strongly eroded to a lace-like thinner network, thicker towards the periphery of the sponge, thinner towards the center, traversed by tunnels of the exhalant canals, which converged into oscular cavities. The bicycle rays penetrated 250 Fig. 3: Underwater photographs of Cliona delitrix highlighting: A. Dying and dead coral strands at the sponge-coral border, underlined by sponge excavating tissue filaments. B. The difference in level between the sponge surface and its surrounding substratum, product of further growth of the coral. A first step (left arrow) between the sponge border and the surrounding dead coral band, and a second step (right arrow) formed as the live coral grew upwards further. C. Another example of the step between the sponge and the coral, product of further coral growth, but in this case the coral finally died and has been covered by crustose coralline; the sponge maintains approximately the same curved outline of the original level where it started the excavation. D. An individual completely colonizing a medium size (ca. 30 cm) coral head. E. One individual forming various contiguous mounds, almost completely colonizing a large coral head (ca. 1 m). F. A dying sponge individual showing the naked underlying coral skeleton it had eroded. Notice the rather intact outer frame perforated at the calices under papillae, and deeply eroded areas underneath oscules. up to 10.1 cm inside sponges that had not yet covered a given coral head. For these sponges, penetration depth was rather similar between coral species: Diploria labyrinthiformis, 3.7±1.4 cm, n=3; Montastraea faveolata, 4.7±2.1 cm, n=2; Porites astreoides, 5.2±1.0 cm; n=2; Siderastrea siderea, 4.7±1.6 cm, n=30 (again, no statistical comparisons were carried out because of small sample sizes in most corals). Sponge surface tissue area did not correlate statistically with depth of bicycle ray penetration in Siderastrea siderea (r=0.36, p=0.063, n=28). For sponges larger than 25 cm2, depth of ray penetration varied between 3.5 cm and 6.8 cm, while in smaller sponges it varied between 2 and 3.5 cm. In S. siderea colonies of about 30 cm in diameter by 20-25 cm in height, completely overtaken by C. delitrix, we noticed (but did not measure) that they were excavated almost to their base. Undermining by the sponge vs. coral tissue death Every Cliona delitrix confronting a live coral, regardless of its size, was surrounded by a band of dead or dying coral. When coral tissue was dead, the calices appeared clean (coral tissue was just removed), or already colonized by turf, frondose or crustose algae. Often the band of dead coral appeared rasped by the long-spined urchin Diadema antillarum Philippi 1845, algae being partly removed and coral calices leveled further. Fish bite marks were rare on the edge of coral tissue confronting the sponge. In coral tissue close ≤5 mm to the sponge, 1-2 mm to 1-2 cm-wide unhealthy or dead strips of coral tissue were sometimes seen spreading radially outwards from the sponge border (Fig. 3A). Dislodging of coral tissue with hammer and chisel showed that these affected coral areas were undermined by shallow excavating sponge pioneering tissue filaments, apparently involved in coral 251 death. In relatively narrow bands of dead coral (<2.5 cm), an excavating tissue front 1-3 cm thick advanced 0.5-2 cm below the surface, often penetrating beyond the edge of live coral tissue, preceded by tissue filaments, reaching upwards towards coral polyps or extending horizontally farther ahead (Fig. 4A, B, C). In wider bands of dead coral, the front of sponge tissue reached only a few mm beyond the edge of the sponge, but filaments advanced several cm ahead, sometimes into live coral (Fig. 4D). Thick tissue bridges extended beneath adjacent sponge bodies of the same individual (Fig. 4E). The etching marks characteristic of excavating sponge erosion were evident in ground and polished sections of the coral skeletons inhabited by Cliona delitrix, including the encrusted surface. Beneath live coral tissue, sponge tissue filaments penetrated through existing skeletal spaces, expanding them, proceeding upwards through the columellar space of the calices, breaking through dissepiments, until reaching the base of the polyp. Throughout the filaments there were abundant granulous, naturally pigmented goldenbrown cells of varied shapes, 12-15 µm in diameter (Fig. 5), also common in the outer surface tissue and reminiscent of spherulous cells (see Pang 1973). In several places healthy sponge and coral tissue were separated by still Fig. 4: Schematic drawings showing how Cliona delitrix excavating tissue fronts and pioneering filaments reach out below live coral (A to D), and how two bodies of the same individual are connected under the surface (E). The leftover coral skeleton within the sponge tissue was not drawn. intact dissepiments or walls. But empty calyx spaces where the sponge had partially penetrated often contained what appeared to be dead coral tissue debris. In the few instances where actual sponge and coral tissue contact was seen, coral granulous cells accumulated (Fig. 5, pers. comm. by Esther Peters, July 27 2005). Discussion Our observations have confirmed that Cliona delitrix is a highly aggressive and destructive reef sponge, and added details about its growth form and how it confronts live coral, allowing us to formulate hypotheses on the mechanism by which it kills coral tissue. The few small, young Cliona delitrix observed were growing on dead coral substratum, indicating that the larva, possibly planktonic (see Mariani et al. 2000) settles preferentially on old dead coral. This behavior has been described for several excavating sponges (see reviews by Goreau and Hartman 1963, McKenna 1997, Schönberg and Wilkinson 2001). But for slightly larger individuals, which were completely surrounded by live coral tissue, one may wonder if larval settlement could have occurred directly on live coral tissue. In fact, Rützler (1971) hypothesized that 252 Fig. 5: Photomicrograph of a ground and polished section of the lower part of a live polyp of the coral Siderastrea siderea, being undermined by the sponge Cliona delitrix. It shows the carbonate calyx skeleton (Sk) and the coral tissue (C), traversed by a sponge tissue filament (S, outlined for clarity). Where the sponge and coral tissues touch, there is an accumulation of golden-colored sponge cells (sg) and coral granular cells (cg, slightly lighter gray near the sponge tissue, distinguishable by color under microscope). mucus-laden larva of the excavating sponges of the genus Aka (as Siphonodictyon), which release abundant mucus, might be able smother and kill live coral polyps, then taking root and expanding. But C. delitrix does not release mucus, and recent studies have shown that healthy corals prevent settlement of other organisms on them (Díaz-Pulido and McCook 2004), perhaps through the use of allelochemicals (Fearon and Cameron 1997). As most other encrusting and excavating sponges, Cliona delitrix tends to grow at a level slightly lower than the surrounding substratum (see Acker and Risk 1985, Schönberg and Wilkinson 2001, Rützler 2002, López-Victoria et al. 2003; but see Vicente 1978 for an exception). Rather than directly overgrowing the adjacent substratum, the lateral undermining by these sponges tends to remove its upper layer (elevated septa in corals, crustose and turf algae in fouled substratum). Differences in height between C. delitrix and the surrounding substratum were quite variable within a coral species, showing that other factors apart from the density and texture of the outer skeleton play a role. By biting the edge of the live coral that confronts other encrusting and excavating sponges, corallivorous fish may sometimes be responsible for initiating and maintaining the difference (see López-Victoria et al. 2006). But fish bite marks were rare on coral tissue confronting C. delitrix in San Andrés. Perhaps grazing of the band of dead coral by sea urchins play a similar role, but we could not clearly ascertain this. Overall, for C. delitrix we believe that two opposing factors are responsible: (1) while the sponge maintains its curved surface at the same level of the coral skeleton, upward growth of adjacent coral tissue or of crustose coralline algae increases the height of the substratum around it and, (2) rasping of the dead coral area by sea-urchins decreases the height of dead coral areas. Further shrinkage of the substratum under the live sponge by bioerosion and subsequent lowering of the sponge surface may also occur (Acker and Risk 1985). Microscopical observations on shallow excavating species (Rützler 1971, Zea and Weil 2003) and in C. delitrix (this study) revealed characteristic etching marks on the surface of the external skeleton, showing that some vertical reduction of the substrate level indeed occurs. However, significant substratum shrinking is unlikely to exist in the case of C. delitrix, because its outer skeletal frame remains uniformly thick throughout the sponge. Further substratum shrinkage would occur only if directly eaten and scoured by fish or urchins, which does not seem to be happening, or from mechanical abrasion during storms. In fact, marked individuals and fragments of shallow excavating sponges did not shrink within 1 to 5 years of observation (López-Victoria el al. 2003, S.Z. pers. observations 2005). The curved surface of Cliona delitrix may be maintained as it grows, when the lateral erosion and advance is made preferentially following the same coral skeletal growth bands, which are laid cyclically in different densities in various coral species (e.g., Macintyre and Smith 1974, Huston 1985). Unfortunately, from our skeletal fragments and skeletal sections we could not ascertain whether this was the case. The extent of vertical penetration of Cliona delitrix into a coral while the sponge is still spreading does not seem to be affected by density or texture of the host coral species’ skeleton, and does not increase significantly as the sponge increases in size. Perhaps it penetrates only deeper once it has taken over the entire colony. Similar values for vertical extension of C. delitrix have been reported in other studies (5 cm, Rose and Risk 1985; 10-12 cm, Pang 1973; vs. 10 cm in our study). Vertical penetrations of the substratum as deep as 8 cm occur in other species as well: in Pione lampa 253 de Laubenfels 1950 (see Rützler 1974, as Cliona) and in Aka coralliphaga (Rützler, 1971) (see Glynn 1997). The outer advancing tissue front of Cliona delitrix in massive cerioid corals is similar to the “string of beads” morphology of excavating tissues in non-encrusting excavating sponges such as Cliona vermifera, in which vertical lobes of tissue located within coral calices are interconnected by horizontal excavating filaments of varying diameters; smaller filaments penetrate through the thecal wall, invading another calyx; the calyx is then filled with tissue and eroded vertically and horizontally cutting dissepiments and septae (Ward and Risk 1977). This may be a general way by which excavating sponges erode corals, first filling existing spaces and then eroding walls and obstacles (see review en Schönberg 2003), subsequently varying widely within and among species in further erosion of the coral skeleton. The vertical component of calix erosion is emphasized in C. delitrix in comparison to other shallow excavating encrusting sponges. When they become large enough, some excavating sponge species add tissue and supporting siliceous skeleton above the substratum, becoming massive, and often erode all skeletal connections to the substratum, becoming free-living, in both cases conforming what is called a gamma stage (e.g., Topsent 1888, Vosmaer 1933, Rützler 1971, Vicente 1978, Calcinai et al. 1999). Even shallow encrusting excavating species that spread horizontally in the upper few cm of substratum slightly thicken their tissue when they run out of space (López-Victoria et al. 2003). Owing to its rather soft tissue Cliona delitrix is perhaps not able to grow further upwards. It may compensate its lack of upward growth with deep vertical penetration into the substratum. Its excavation pattern of an outer solid shell and an inner cavernous core provides enough space for the tissue and water-circulation system, while giving stability and support to the sponge. The growth of Cliona delitrix with far-reaching ramifications inside the coral skeleton allows it to simultaneously weaken coral tissue in various portions of the colony. In a similar way, but from a completely eroded central chamber filled with tissue, some species of the genus Aka erode tunnels that reach out to several separated places of the surface of a coral; further expansion of the outgrowths and the central chamber ends up taking over the entire coral head (Rützler 1971). Not penetrating deeply, shallow encrusting and excavating sponges resort to shallow-lying tissue fronts and closer-range pioneering filaments that penetrate directly beneath live tissue coral at their borders (Ward and Risk 1977, Schönberg and Wilkinson 2001, Schönberg 2001, Rützler 2002, López-Victoria et al. 2003, 2006). Our histological observations of the zone of interaction between Cliona delitrix and coral tissues show that coral tissue death occurs before erosion of the calyces is enough to induce coral polyp detachment. Indeed, coral tissue and its skeletal support are so strongly interwoven that polyp detachment seems hardly possible if the skeleton is not thoroughly eroded. This purely physical detachment has been assumed in other works with encrusting and excavating sponges (e.g., López-Victoria et al. 2003, 2006). Coral death in close vicinity of C. delitrix could be the consequences of the release of allelochemicals that can kill coral tissue, and which are known to be present in its organic extract (Chaves-Fonnegra et al. 2005). Similar effects have been observed in the fistulate excavating sponges of the genus Aka (Rützler 1971), and have been attributed to the release of abundant mucus assumed to be carrying known allelopathic compounds (Sullivan et al. 1983, Sullivan and Faulkner 1990). The mucus is a medium that helps spreading and retaining compounds on the surface of corals, facilitating their entrance into tissue (Hay et al. 1998). However, as C. delitrix does not produce mucus, there must be some other means, if any, for the deployment of the potentially harmful substances it produces. Whether they are exuded directly to the water remains to be determined. At any rate, our histological observations show healthy sponge and coral tissues within the coral skeleton just separated by thin carbonate walls, as well as sites of direct contact where the two tissues are still alive. This appears to indicate that chemical substances are not being released into the fluids contained in the coral skeleton. Moreover, the observed accumulation of cells in coral tissue in direct contact with sponge tissue points towards close-range cellular or biochemical processes involved in coral tissue death, which require further study. Acknowledgments This paper is part of the M.Sc. thesis of A.Ch.-F., Marine Biology Program, Universidad Nacional de Colombia at Instituto de Investigaciones Marinas y Costeras – INVEMAR. Supported by the Colombian Science Fund – COLCIENCIAS (grant 110109-13544 to C. Duque and S. Zea), Universidad Nacional de Colombia, and INVEMAR. We are grateful to M. López-Victoria, E. Peters and J. Reyes for their help with histological techniques and interpretation, and to J. C. Márquez, L. Castellanos and Banda Dive Shop for help during field work. Contribution 979 of INVEMAR and 301 of CECIMAR and the Graduate Program in Marine Biology of the Universidad Nacional de Colombia, Faculty of Sciences. Two anonymous reviewers helped greatly to improve the manuscript. References Acker KL, Risk MJ (1985) Substrate destruction and sediment production by the boring sponge Cliona caribbaea on Grand Caiman Island. J Sedim Petrol 55(5): 705-711 Calcinai B, Cerrano C, Bavestrello G, Sará M (1999) Biology of the massive symbiotic sponge Cliona nigricans (Porifera: Demospongiae) in the Ligurian Sea. Mem Qld Mus 44: 77-83 Chaves-Fonnegra A (2006). Mecanismos de agresión de esponjas excavadoras incrustantes y consecuencias sobre corales arrecifales en el Caribe colombiano. M.Sc. Thesis, Universidad Nacional de Colombia - INVEMAR, Santa Marta Chaves-Fonnegra A, Zea S, Gómez ML (in press) Abundance of the excavating sponge Cliona delitrix in relation to sewage discharge at San Andrés Island, SW Caribbean, Colombia. Bol Invest Mar Cost 36 Chaves-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 de Laubenfels MW (1950) The Porifera of the Bermuda Archipelago. Trans Zool Soc London 27: 1-201 Díaz JM, Garzón-Ferreira J, Zea S (1995) Los arrecifes coralinos de la isla de San Andrés, Colombia: estado actual y perspectivas 254 para su conservación. Colección Jorge Alvarez LLeras 7, Acad Col Cienc Exact Fis Nat, Bogotá Díaz JM, Díaz-Pulido G, Garzón-Ferreira J, Geister J, Sánchez JA, Zea S (1996) Atlas de los arrecifes coralinos del Caribe colombiano. I. Complejos arrecifales oceánicos. Serie Publicaciones Especiales 2, INVEMAR, Santa Marta Díaz-Pulido G, McCook L. J (2004) Effects of live coral, epilithic algal communities and substrate type on algal recruitment. Coral Reefs 23: 225-233 Fearon RJ, Cameron AM (1997) Preliminary evidence supporting the ability of hermatypic corals to affect adversely larvae and early settlement stages of hard coral competitors. J Chem Ecol 23(7): 1769-1780 Glynn P (1997) Bioerosion and coral reef growth: a dynamic balance. In: Birkeland C (ed). Life and death of coral reefs. Chapman & Hall, New York. pp. 68-95 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. American Association for the Advancement of Science, Washington DC. pp. 25-54 Hay ME, Stachowicz JJ, Cruz-Rivera E, Bullard S, Deal MS, Lindquist N (1998) Bioassays with marine and freshwater macroorganisms. In: Haynes KF, Millar JG (eds). Methods in chemical ecology: biossay methods. Chapman and Hall. New York. pp. 32-122 Huston M (1985) Variation in coral growth rates with depth at Discovery Bay, Jamaica. Coral Reefs 4: 19-25 Jackson JBC (1979) Morphological strategies of sessile animals. In: Larwood G, Rosen BR (eds). Biology and systematics of colonial organisms. Academic Press, London. pp. 499-555 Jackson JBC, Buss LW (1975) Allelopathy and spatial competition among coral reef invertebrates. Proc Natl Acad Sci USA 72: 51605163 Lang JC, Chornesky EH (1990) Competition between scleractinian reef corals – a review of mechanisms and effects. In: Dubinsky Z (ed). Ecosystems of the world 25: Coral reefs. Elsevier, Amsterdam. pp. 209-252 López-Victoria M (2003) Interacciones entre esponjas excavadoras del complejo Cliona aprica - C. langae - C. caribbaea y corales pétreos en el Caribe colombiano. M.Sc. Thesis, Marine Biology, Universidad Nacional de Colombia - INVEMAR, Santa Marta López-Victoria M, Zea S, Weil E (2003) New aspects on the biology of the excavating sponge complex Cliona caribbaea - C. langae - C. aprica. In: Pansini M, Pronzato R, Bavestrello G, Manconi R (eds). Sponge science in the new millennium. Boll Mus Ist Biol Univ Genova 68: 425-432 López-Victoria M, Zea S, Weil E (2006) Competition for space between encrusting excavating Caribbean sponges and other coral reef organisms. Mar Ecol Progr Ser 312: 113-121 Macintyre IG, Smith SV (1974) X-radiographic studies of skeletal development in coral colonies. Proc 2nd Int Coral Reef Symp, Brisbane 2: 277-287 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 McKenna SA (1997) Interactions between the boring sponge, Cliona lampa and two hermatypic corals from Bermuda. Proc 8th Int Coral Reef Symp, Balboa 2: 1369-1374 Pang RK (1973) The systematics of some Jamaican excavating sponges. Postilla 161: 1-75 Pomponi SA (1977) Etching cells of boring sponges: an ultraestructural analisis. Proc 3rd Int Coral Reef Symp, Miami 2: 485-490 Rose CS, Risk MJ (1985) Increase in Cliona delitrix infestation of Montastrea cavernosa heads on an organically polluted portion of the Grand Cayman fringing reef. PSZN Mar Ecol 6(4): 345-363 Rützler K (1971) Bredin-Archbold Smithsonian Biological Survey of Dominica: burrowing sponges, genus Siphonodictyon Bergquist, from the Caribbean. Smithson Contrib Zool 77: 1-37 Rützler K, Rieger G (1973) Sponge burrowing: fine structure of Cliona lampa penetrating calcareous substrata. Mar Biol 21: 144162 Rützler K (1974) The burrowing sponges of Bermuda. Smithson Contrib Zool 165: 1-32 Rützler K (1975) The role of burrowing sponges in bioerosion. Oecologia (Berl.) 19: 203-216 Rützler K (2002) Impact of crustose clionid sponges on Caribbean reef corals. Acta Geol Hisp 37: 61-72 Schönberg CHL (2001). Estimating the extent of endolithic tissue of a Great Barrier Reef clionid sponge. Senckenberg Marit 31(1): 29-39 Schönberg CHL, Wilkinson CR (2001) Induced colonization of corals by a clionid bioeroding sponge. Coral Reefs 20: 69-76 Schönberg CHL (2003) Substrate effects on the bioeroding Demosponge Cliona orientalis. 2. Substrate colonization and tissue growth. PSZN Mar Ecol 24(1): 59-74 Sokal R.R, Rohlf FJ (1981) Biometry: The principles and practice of statistics in biological research, 2nd edition. W.H. Freeman and Company, San Francisco Suchanek TH, Green DJ (1981) Interspecific competition between Palythoa caribaeorum and other sessile invertebrates on St. Croix reef, U.S. Virgin Islands. Proc 4th Int Coral Reef Symp, Manila 2: 679-684 Sullivan BW, Faulkner DJ (1990) Chemical studies of the burrowing sponge Siphonodictyon coralliphagum. In: Rützler K (ed). New perspectives in sponge biology. Smithsonian Institution Press, Washington DC. pp. 45-50 Sullivan BW, Faulkner DJ, Webb L (1983) Siphonodictidine, a metabolite of the burrowing sponge Siphonodictyon sp. that inhibits coral growth. Science 221: 1175-1176 Topsent, E (1888) Contribution à l’etude des clionides. Arch Zool Exp Gén, Ser 2, 5(bis): 1-165 Vicente VP (1978) An ecological evaluation of the West Indian Demosponge Anthosigmella varians (Hadromerida: Spirastrellidae). Bull Mar Sci 28: 771-777 Vosmaer, GC J (1933) The sponges of the Bay of Naples: Porifera incalcaria. Martinus Nijhoff, The Hague, 828 pp Ward P, Risk M (1977) Boring pattern of the sponge Cliona vermifera in the coral Montastrea annularis. J Paleontol 51 (3): 520-526 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 Willenz P, Pomponi S (1996) A new deep sea coralline sponge from Turks and Caicos Islands: Willardia caicosensis gen. et sp. nov. (Demospongiae: Hadromerida). Bull Inst Royal Sci Nat Belg Biol 66 Suppl: 205-218 Woodin SA, Jackson JBC (1979) Interphyletic competition among marine benthos. Amer Zool 19: 1029-1043 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(3): 348-370
© Copyright 2026 Paperzz