- Marine Record
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First documentation of encrusting specimen of Cliona delitrix on Curaçao: a cause for concern?
Marine Biodiversity Recordsvolume 10, Article number: 10 (2017)
The coral excavating sponge Cliona delitrix is one of the most aggressive and conspicuous excavating sponges on Caribbean reefs. While C. delitrix is very prominent displaying its typical encrusting growth form (β-stage) on the Caribbean island of Bonaire, it is rather elusive and only exhibits a papillated habitus (α-stage) on the neighboring island of Curaçao. Here I document the first two encrusting specimen of C. delitrix on Curaçao and discuss potential explanations for island-specific differences in its habitus and occurrence. An increase of encrusting specimen could have profound consequences for Curaçaoan reefs and should thus be monitored closely.
The coral excavating sponge Cliona delitrix (Pang 1973) (Hadromerida, Demospongiae) is one of the most destructive bioeroders on Caribbean coral reefs (e.g. Chaves-Fonnegra et al. 2007). It can excavate 10–12 cm into coral skeletons and/or the limestone framework (Pang 1973; Zilberberg et al. 2006), and spreads laterally at mean rates of ~1.5 cm y−1 (Chaves-Fonnegra and Zea 2011; Rützler 2002). While doing so it can kill adjacent corals by undermining tissue fronts and filaments (Chaves-Fonnegra and Zea 2007). Initially, C. delitrix forms discrete ostial and oscular papillae (α-stage) (Fig. 1a). Quickly these papillae start to fuse (Fig. 1b), until eventually all papillae are fused and connected by a tough layer of thin tissue, which starts to overgrow the substrate in an encrusting manner (β-stage) (Fig. 1c-d).
Due to its bright red-orange color and increasing abundance, C. delitrix is one of the most conspicuous excavating sponges on many coral reefs throughout the Caribbean and Eastern and North Eastern coast of Brazil (Chaves-Fonnegra et al. 2007; Rose and Risk 1985; Ward-Paige et al. 2005; see map in Van Soest 2010 for distribution range of C. delitrix). Interestingly, C. delitrix is rather elusive on the fringing reefs of the Southern Caribbean island of Curaçao, yet it is very prominent on the neighboring island of Bonaire, merely 41 km off Curaçao (Mueller et al. 2014) (Fig. 2). Fringing reefs on both islands are situated in the same physicochemical province (Chollett et al. 2012) and are characterized by a similar reef geomorphology with a narrow reef terrace and steep reef slope (20–50°) (Van Duyl 1985), as well as comparable reef community structures and reef health conditions (Jackson et al. 2014; Sandin et al. 2008). Despite the close proximity and similarities in environmental conditions of these two islands, C. delitrix on Curaçao appears to solely display the α-stage, with mostly unfused papillae, whereas large encrusting individuals occur commonly around Bonaire. It should be noted that the exclusively-papillated excavating sponge Cliona laticavicola (Pang 1973) (Hadromerida, Demospongiae) closely resembles the α-stage of C. delitrix. However, genetic and spicule analysis confirm that papillated specimen on Curaçao are indeed C. delitrix (Chaves-Fonnegra et al. 2015). Moreover, due to the fact that both species were described from the same reef on Jamaica (C. laticavicola from shallow-rocky habitats and C. delitrix from the reef slope), C. laticavicola has been proposed to be an early life history stage or ecophenotype of C. delitrix (Zea et al. 2014).
This study reports the first documentation of encrusting specimen of C. delitrix from Curaçao and discusses potential explanations for island-specific differences in its habitus and occurrence.
Material and methods
Two encrusting specimen of C. delitrix were photographed during a dive on November 3, 2016 in front of the Sea Aquarium Park on Curaçao (12° 05’ N, 68° 53’ W). The site is characterized by a diverse coral community with >30% live coral cover, high structural complexity, and a steep fore reef slope (>50°) (Van Duyl 1985). The coral community at the drop-off (approx. 8 m depth) is dominated by Orbicella spp.
Two encrusting specimen (β-stage) of C. delitrix were recorded on a single colony of Orbicella faveolata (formerly Montastraea faveolata) at 8 m depth (Fig. 3). Both specimen were located in two separate areas of partial coral-mortality and were surrounded by a band of turf algae. No additional encrusting specimen of C. delitrix were encountered in the vicinity during the 60 min dive.
Cliona delitrix has been reported to occur on Curaçao (Bruckner and Bruckner 2006; Chaves-Fonnegra et al. 2015; Van Soest 1981), yet large encrusting specimen have not been recorded so far and were not encountered in the coral reef monitoring program and/or other research activities of the Carmabi Research Station (pers. comm. M. Vermeij). While it cannot be excluded that more C. delitrix displaying the β-stage exist or existed on Curaçaoan reefs, it is safe to say that this habitus is rare. This raises the question why encrusting C. delitrix are not as abundant as on Bonaire, where such specimen are commonly encountered and densities of 0.03 individuals m−2 have been documented (Mueller et al. 2014)? Possible explanations could include (1) differences in environmental conditions between the two islands and/or (2) genetic differences between the local populations of C. delitrix. However, environmental conditions including geomorphology and community structure are very similar on both islands (Chollett et al. 2012; Sandin et al. 2008; Van Duyl 1985). Given the suggested positive effect of anthropogenic disturbances (e.g. organic pollution) on the abundance of C. delitrix (Chaves-Fonnegra et al. 2007; Rose and Risk 1985; Ward-Paige et al. 2005), a more than five times higher human population density (Centraal Bureau voor de Statistiek 2016; Central Bureau of Statistics Curaçao 2016), more industrial development, and a less restrictive marine resource management policy would rather suggest more favorable conditions on Curaçao than on Bonaire. Slightly higher dissolved organic carbon (DOC) and bacterial concentrations (Mueller et al. 2014) further suggest that food limitation is not a likely cause for the lower prevalence of C. delitrix on Curaçaoan reefs. Moreover, a planktonic larval period between 1 and 10 days (Mariani et al. 2006; Warburton 1958) in combination with the strong Caribbean Currents have been proposed to enable gene flow between populations of Cliona delitrix of up to 500 km across the Southern Caribbean (Chaves-Fonnegra et al. 2015). It is therefore highly likely that the Caribbean Currents flowing from Bonaire to Curaçao with up to 70 cm s−2 (Fratantoni 2001) (Fig. 2), should allow for a good connectivity between C. delitrix populations of both islands (Chaves-Fonnegra et al. 2015), as reported for local coral populations (e.g. Baums et al. 2005; Baums et al. 2006). Thus, as larvae of encrusting specimen of C. delitrix from Bonaire can be expected to seed Curaçaoan reefs, genetic differences are unlikely to be the reason for the lack of specimen displaying the β-stage on Curaçao.
In addition, C. delitrix is reported to spread particularly in the aftermath of catastrophic episodical disturbances, such as hurricanes and bleaching events, where recently deceased coral are rapidly colonized (Chaves-Fonnegra et al. 2015; Chaves-Fonnegra and Zea 2011). In general, Curaçao has not been as strongly affected by bleaching events as other places in the Caribbean. However, during the 2010 bleaching event 12–30% of all coral colonies were affected and on average 10% of those subsequently died (Vermeij 2012). Despite this substantial opening of suitable substrate, no encrusting specimen of C. delitrix were recorded until now. This raises the question if the here reported occurrence constitutes an isolated event or marks the onset of an ongoing trend? Given thefierce competitiveness of Cliona delitrix, its capability to kill live coral, as well as its high excavation rate, this could potentially have profound consequences for Curaçaoan benthic communities and their calcium carbonate budgets and should therefore be monitored closely.
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I thank the staff of Carmabi for their logistic support. Fieldwork was performed under the research permit (#2012/48584) issued by the Curaçaoan Ministry of Health, Environment and Nature (GMN) to the CARMABI Foundation.
The author declares that there was no funding received for this study.
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All data generated or analyzed during this study are included in this published article.
BM conceived and performed the experiment, analyzed the data, and wrote the manuscript.
The author declares that he has no competing interests.
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