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Detection of bioactive compounds in the mucus nets of Dendropoma maxima, Sowerby 1825 (Prosobranch Gastropod Vermetidae, Mollusca).

1. Introduction

The vermetid gastropod Dendropoma maxima, Sowerby 1825 (Vermetidae, Littorinimorpha, Gastropoda) is a dominant, very abundant encrusting species of outer tropical reefs and widespread throughout the IndoPacific [1-3]. In the Red Sea, D. maxima populations can attain substantial densities, a phenomenon largely restricted to that area [4, 5]. Wormsnails mainly live in the infralittoral and upper-circalittoral between the breaker zone and the outer reef edges facing the current [1, 2, 6]. To combat the competition for space and nutrients, wormsnails developed particularly strong substrate preferences. In the Red Sea, substrates are living corals like hydrozoan Millepora spp. (Figure 1(a)) and Porites spp., dead coral rock next to the reef edge, or they can be found on the nonliving reef flat substratum [2, 7].

Vermetids are a rather peculiar and poorly studied family. Although they are common inhabitants of coral reefs and rocky shores, little is known about the basic biology of most species [5]. Wormsnails have an irregularly uncoiled calcareous shell, cemented to or embedded in the substrate [2, 3, 6, 8]. Growth rate of the shell is rather fast and enables the vermetid to escape overgrowth by corals and to maintain access to food [9]. Often, only the proteinaceous operculum is seen forming a plug to the accessible shell aperture whose diameter is a good index of body size [5,10].

Aspects of the feeding ecology of vermetids have been examined in a number of studies (e.g., [3, 6, 8, 9, 11]). Wormsnails are active and passive suspension feeders [9]. Next to ctenidial cilia filter feeding, what is marginally in D. maxima, vermetids excrete a sticky mucus net (containing mucopolysaccharides and mucins (glycosylated proteins)) well adapted to capture near-bed small planktonic organisms consisting mainly of copepods, rhizopods, meiobenthos, and detritus [3, 6, 8, 11, 12].

Analyzing the interspecific interaction between wormsnails and their living coral substratum disclosed that D. maxima depresses coral growth in the region of infestation (Colgan in [9]). Zvuloni et al. [1] reported that the presence of D. maxima in the Gulf of Aqaba (Red Sea) was associated with morphological anomalies and reduced size of corals they live inside. This suggests either that wormsnails harm corals or that they recruit preferentially to degraded coral habitats [13].

The extruded webs seem to be more detrimental on surrounding organisms than the vermetids' body. They often contact neighboring substrates including corals [2,14]. Field experiments clearly demonstrated deleterious effects of vermetid nets on corals [13]. Since the underlying mechanisms are still unknown [13], theories speak of abrasive effects on the coral polyps, the competition for substrate and planktonic food, or the presence of bioactive secondary metabolites [1, 15]. Presumably, there is an additional effect of surrounding invertebrate colonies and associated fish. For example, the guard crab Trapezia serenei ameliorates the strong negative effect of D. maxima on pocilloporid coral growth rate by dislodging and consuming the vermetid mucus (as they do with sediments) [16].

Fishes are notable among vertebrates for having comparatively broad and flexible diets [17, 18]. In the Red Sea, many mucoid (e.g., Labroides spp., Chaetodon spp.) and molluscivore (e.g., Anampses spp., Bodianus spp., Cheilinus spp.) reef fish are known. Until now there is no publication about any predator--besides the guard crab Trapezia serenei as suggested in [16]--that feeds on the wormsnail's mucus even nets are additionally loaded with plankton, mainly copepods, what should be of great interest for plankton feeding reef inhabitants. Already in 1973, it was assumed that vermetid mucus must be distasteful to other animals to function as an effective feeding inhibitor [19].

Molluscs are a dominant group within aquatic invertebrates producing bioactive substances. Among them, opisthobranchs, especially nudibranchs, are mostly preyed on [20]. As molluscs often lack sufficient morphological protective mechanisms, they have adopted an impressive array of defensive strategies [21, 22]. Passive and active chemical defensive (mucus) secretion is known in numerous marine molluscs [23, 24]. Besides mechanical protection, gastropod mucus may contain specific products to render the animal poisonous, distasteful or irritating, or some combination of these known from many mucus producing invertebrates [19, 23, 25]. Experiments with carnivorous fishes as potential predators have indicated the possession of chemical defense mechanisms in opisthobranch gastropods, including the secretion of strongly acidic or noxious substances with ichthyotoxic and antibacterial properties [26-28]. Many of these deterrents are diet-derived or built up in vivo from dietary precursors (e.g., sponges for dorid nudibranchs) and not synthesized de novo [22, 29-31].

Until now, nothing is known either about predators feeding on the plankton-load nets or any interaction between ambient marine organisms (besides corals) and the mucus veils of Vermetidae. No studies have been done analyzing the toxic potential of mucus net ingredients on corals associated with vermetid gastropods, on surrounding reef inhabitants or their potential application in human medicine. Marine invertebrates are one of the most efficient sources for bioactive secondary metabolites with pharmaceutical properties [24, 32-35]. Some have entered preclinical and clinical trials or even made it to the commercial sector [34, 36-38].

Therefore, we made video observations to document the interaction reef fish vermetids concerning the capability as food source and screened the nets for bioactive substances. A recently optimized system (high-performance thin-layer chromatography (HPTLC)/bioassay) for bioactivity screening in invertebrates was used [39].

2. Material and Methods

2.1. Study Area. Field work was carried out in the Gulf of Aqaba (Red Sea) along the Egyptian eastern and western coastline near Dahab (Suleiman Reef), 100 km north of Sharm El Sheikh and at Mangrove Bay (Sharm Fugani), 30 km south of El Quseir (Egypt) during the period from April 15 to December 15, 2010. Dendropoma maxima individuals are very common on the reef crest using corals (Millepora dichotoma, Millepora platyphylla (Figure 1(a)), Porites lutea, and Porites nodifera) as their main substrate, and on the rear reef flat, where organisms are often attached to blocks of dead or live coral rubble. The latter feature makes D. maxima very suited for aquaria experiments. Their habitat is always characterized by intense wave action, strong current, and high abundance of reef fish.

2.2. Documentation and Video Recording. Filming experiments were done in front of several wormsnail populations on the reef flat, edge, and slope, covering more than 12 hours at different day times. Filming was done with a digital camera in an underwater case (PowerShot G9, Canon, Germany). The camera was attached to a small flexible tripod and positioned near a wormsnail community. After focusing, the system was left alone for half an hour in order to not interfere with the organisms. The video material was evaluated by identifying the fish species [40,41] and counting their net attacks or bites.

2.3. In Situ and Ex Situ Sampling of Mucus Nets. In situ sampling was focused on the shallow subtidal zone and done via snorkeling. All individuals exhibited an aperture width of about 15 mm. Secreted mucus nets were collected with a metal wire ring positioned on the outside perimeter of the shell's aperture. Prior to collection, the plankton-load net was wrested from the wormsnail by twisting the metal device. Removing the nets stimulated the wormsnails to start producing a new one within less than a minute. The combined veils were transferred to the laboratory and extracted immediately. Additionally, plankton was caught with a 15 [micro]m pore-sized plankton net and sediments were taken next to the wormsnails' in situ habitat.

Individuals, all of about 15 mm aperture width, used for ex situ net extraction were collected from horizontal surfaces at depths between 0.5 and 1.5 m. Only animals attached to lose coral blocks were transferred to the aquaria without getting exposed to air and brought back after one day and final plankton feeding. Before inserting, the coral blocks were cleaned with a wire brush to get rid of attached microfauna and flora that could diffuse in the ambient water. The plankton-load net produced in situ was removed. The ex situ tank was flushed with filtered seawater at 25[degrees]C (<15 [micro]m pore size) to get rid of most of the suspended particles. Unfiltered seawater contained a high density of visible detrital particles; the filtered seawater appeared clear. The aquarium was equipped with a perforated acrylic glass rack on which coral blocks were positioned. This facilitates a controlled current flow from below and sidewise induced by pumps. The vermetids were triggered to produce the mucus nets floating upwards by this external stimulus. A ventilation-air-stone positioned under the rack provided small air bubbles that attach to the translucent mucus strands rendering the nets visible [8]. The back side of the aquarium was covered with a black plate to enhance the contrast. Collection was done according to in situ sampling. Clear nets from different individuals were combined and covered with solvent.

2.4. Extraction of Mucus Nets. Mucus nets (collected in situ and ex situ) from different individuals were combined in reaction tubes and extracted exhaustively over night in methanol, ethanol, diethyl ether, or ethyl acetate (~ 5 veils [mL.sup.-1] solvent). After centrifugation, the supernatant was transferred in HPTLC prevalent vials. Sediment and plankton samples were weighed and extracted according to the mucus webs (~500 mg [mL.sup.-1] solvent).

2.5. High-Performance Thin-Layer Chromatography (HPTLC). Chromatography was performed on silica gel 60 [F.sub.254] plates (Merck, Darmstadt, Germany). All plates were prewashed by development with methanol, then dried at 100[degrees]C for 15 min, and stored protected in a desiccator. Samples were applied on the plate as 4 mm bands, 9mm apart, 10 mm from the lower edge, and 15 mm from the left edge by means of the Automatic TLC Sampler 4 (ATS4, CAMAG, Switzerland). The application volume of the mucus extracts ranged from 20 to 80 [micro]L per band. Plates were developed with a twelve-step gradient by use of the Automated Multiple Development System (AMD2, CAMAG). The gradient was based on methanol, isopropyl acetate, and n-hexane (all technical grade and distilled before, BASF, Ludwigshafen, Germany) using 4 mm increments for the successively ascending migration distances. The drying time of the last AMD2 step was increased to be 15 min to avoid residual solvent interferences with the subsequent bioassay. Plates were documented by use of the DigiStore 2 Documentation System (CAMAG) at 254 nm, 366 nm, and with white light illumination (reflectance and transmission mode). Data processing for all instrumentation was performed with the software platform winCATS (CAMAG). Digital evaluation (transfer from image into analogue curve) was processed with separate software (VideoScan, CAMAG). The VideoScan settings used were: "track borders and slopes" was selected as integration mode, the Savitsky-Golay filter width was 11, and the offset was set to "yes." The track borders were set outside the fraction to enable background subtraction of the mean area of both borderline pixels.

2.6. Bioluminescence Assay with Vibrio fischeri. The developed plate was automatically immersed at a speed of 3.5 cm [s.sup.-1] and with an immersion time of 1 s, by means of the TLC Chromatogram Immersion Device III (CAMAG), into the luminescent bacteria (Vibrio fischeri) suspension, which was prepared according to the Bioluminex assay protocol (culture medium and buffer from ChromaDex, Boulder, CO, USA). For imaging, the HPTLC plate was placed in the compartment of the BioLuminizer (CAMAG), a dark chamber with a cooled 16-bit high-resolution CCD camera on top, specially designed for HPTLC-bioluminescence detection. In the compartment, the HPTLC plate was covered by a glass plate keeping the bacteria moist for a prolonged time. Images were captured with an exposure time of 30 s over a period of 30 min. This allowed the study any time-dependent changes.

3. Results

3.1. Observations on Coral-Wormsnail Interaction. Observations made at Sharm Fugani (Mangrove Bay, South Sinai, Western Coast, Red Sea) and Suleiman Reef (Dahab, South Sinai, Eastern Coast, Red Sea) showed clear structural deformations of surrounding coral tissue inhabiting Dendropoma maxima. Less affected were fire corals of the genus Millepora (Figure 1(a)), due to the erected and branching growth form and the limited contact area between coral tissue and mucus webs. Most affected were massive corals of the genus Porites. This vermetid-coral association was always characterized by the wormsnail's mucus net covering parts of the coral block. Veils of different individuals often merge together forming huge sheets spread on the reef's surface. Some veils were so thick and dense that they trap gas bubbles, which get in touch with coral surface. Different states of host-coral degeneration were observable, beginning with pigment modification and surface structure flattening (Figure 1(b)) until the exposure of dead coral rock was overgrown by algae (Figure 1(c)).

3.2. Video Observation on Fish-Wormsnail Interaction. The evaluation of the video material does not show any fish biting or interested in the nets, despite the full load of plankton and bacteria accumulated within the web; even though amongst the identified reef fish were well known mucoid and plankton feeding organisms known to consume, for example, nutritious coral mucus aggregates. Observed reef fish sharing wormsnail habitats are listed in Table 1. 3.3. Sampling of Mucus Nets and Screening for Bioactive Metabolites (In Situ and Ex Situ). Preliminary tests preferentially showed unpolar and less polar components accumulated inside the nets. Therefore, ethyl acetate was chosen as extracting agent. Dipping in a Vibrio fischeri suspension leads to an inverse correlation between the concentration of bioactivity-reducing substances and the bioluminescence of bacteria.

Mucus nets with plankton sampled in situ and extracted with ethyl acetate showed at least four V fischeri toxic substances (M1, M3-M5) detected by bioluminescence inhibition (black spots on luminescent background). Additionally, there was one metabolite (M2) enhancing the bioluminescence indicated by a white spot on the HPTLC plate (Figure 2(a)). Because of different application volumes, the more concentrated extracts led to a stronger decrease of luminescence on the plate. When nets are particle enriched (in situ), it is not possible to say whether the wormsnail or the captured plankton is responsible for product synthesis.

Inside the aquaria (ex situ), wormsnails retained producing their mucus nets which were almost invisible due to the lack of adherent particles. Defecation was frequent (2-4 times [h.sup.-1]) and ejected as pellets in batches leading to the cleanup of all facilities as well as the contamination of veils which had to be discarded. Wormsnails kept on generating slime nets for approximately 24 hours, until they stopped and could not be motivated again without additional feeding. During the final analysis, the wormsnails secreted a small bolus of mucus that accumulated on the uppermost lip of the operculum.

Bioactive metabolites, detected in situ, could also be found in extracts from nets collected ex situ (Figure 2(b)). The digital detection of the inverted (grey-scale) bioluminescence signals showed the same intensity of bioluminescence inhibition concerning the most nonpolar substances (M4 and M5) between equal concentrated extracts of in situ and ex situ sampling (Figure 3). All other metabolites disclosed stronger effects in the in situ extracts compared to the ex situ pendants. The ratio of bioluminescence inhibition between metabolite five and one is M1 > M5 in the in situ extracts including plankton and M1 < M5 in ex situ extracts excluding plankton (Figure 3). Same results were obtained for M4. Thus, M4 and M5 seemed to (exclusively) synthesize or accumulate from the wormsnail itself whereas M1 is of planktonic origin. Despite using filtered seawater, the ex situ extracts were not completely free of plankton. This was due to inserting some microfauna and flora attached to the coral blocks the wormsnails live inside. The inserted particles could have been trapped in the veils in small amounts leading to grayish spots (M1) also in the ex situ extracts. Extracts of surrounding sediments and plankton caught by a 15 [micro]m plankton net only exhibited the polar or further non polar bioactive substances eluting later on the HPLTC plate (data not shown). This is the first record of bioactivity in the whole family of Vermetidae.

4. Discussion

4.1. First Record of Bioactivity in the Mucus Nets of Vermetids. This study is the first report of bioactive substances in mucus nets of the family Vermetidae. Although it was already presumed in 1973 by Coles and Strathmann [19] and despite the already known occurrence of toxic compounds in many mucus releasing invertebrates, no study has been completed on the detection of bioactive secondary metabolites in vermetids. The compounds could be either of gastropod's origin synthesized by the wormsnail itself, accumulated via passive suspension feeding, or built up starting from diet-derived precursors. Here we suggest that M4 and M5 are exclusively produced by the vermetid itself due to equal bioluminescence inhibition of these metabolites and the inverse ratio of M1 and M5 (or M1 and M4) between in situ and ex situ extracts (Figure 3). Traces of M1 to M3 along the HPTLC plate of clean extracts are presumably due to small amounts of plankton transferred to the ex situ tanks, for example, microfauna and flora attached to the coral block, that got caught in the mucus veils. In case the bioactive metabolites would not be accumulated by the wormsnail but by the plankton, the ratio of substance amounts--and therefore the intensity of bioluminescence inhibition--between M1 and M4 as well as M5 and all the other metabolites should be constantly equal. This requires the equality of the qualitative and quantitative composition of the remaining planktonic organisms in the ex situ tank and the in situ habitat. The secretion of mucus agglomerates from animals that kept in aquaria for more than 24 hours was also observed by Yonge [42]. These attributes led to the conclusion that D. maxima uses the bolus to consolidate filtered particles prior to ingestion. Since filter feeding is possible but negligible in D. maxima and it is fully adapted to mucus-trap feeding continuously nourishing on slime nets, the bolus seems to be an artifact of ex situ conditions.

4.2. Trophic Significance and Biotoxicity/Ichthyotoxicity of Mucoidal Material. The significance of mucoidal material of either fish or invertebrate origin as food source for tropical marine fishes is well known (e.g., [43-45]). External mucus slime provides the predator with a rich, continuously renewed resource of energy and amino acids that may comprise more than 95% of their diet [46, 47]. Lipids, particularly wax esters, and mucins containing glucose, galactose, glucosamine, galactosamine, and arabinose were found to be a major, consistent component of coral mucus [43, 47]. The molluscan mucus is phylogenetically and functionally different from coelenterate mucins but seems quite similar to them chemically [47]. Predators feeding on mucus are Labroides spp. cleaning wrasses (Labridae) or juvenile angelfish (Pomacanthidae) but also noncleaning fish like cichlids [44, 48]. Further families including mucoid reef fish are the Chaetodontidae (predominant feeding mode), Tetraodontidae, Balistidae, Monacanthidae, Pomacentridae and Scaridae [45]. Corallivores are well known to feed compulsively or facultatively on the nutritious slime of live coral polyps. Several corals (e.g., Acropora spp., Porites spp.) release large aggregates of denatured mucus that becomes suspended and floats in the water column. These flocks, additionally containing algae, occasional protozoa, organic debris, filamentous algae, and crustacean molts, as well as inorganic particles, are highly energy enriched and may be an important food source [19, 43, 47, 49, 50].

However, our study gives no information whether bioactive substances are responsible for coral tissue degeneration or have ichthyotoxic properties concerning habitat sharing reef fish. The antibiotic effect may also be used to reduce the degradation of plankton by bacteria while it is trapped within the net. Bioactive metabolites could be the explanation for mucoid and plankton feeding reef fish not being interested in the veils as noted and presumed before [19]. Our findings that several species of Chromis sp. ignore the mucus nets contradict with the studies completed by Johannes [49], who showed that these fish have a preference for mucus sheets in general. It is also possible that reef fish ignore the webs because of their dimension, as seen with macroscopic mucus aggregates from corals [19]. Further analyses are needed to study the correlation between the separated metabolites and their effect.

4.3. Effect of Vermetids on Coral Morphology and Survival. The deleterious influence of mucus nets on coral morphology leading to, for example, the flattened shape, even surface and air bubble trapping was also previously reported (e.g., [1, 13]). Flattened corals cannot block the horizontal component of the local currents and may enable the gastropods' webs to spread over the coral head. Thus, the mucus net may be secreted over a larger area [1]. A comparable strong coral degradation marked by the exposure of dead tissue overgrown by algae (Figure 1(c)) is also published in [13]. They revealed a negative correlation between the local density of vermetids and the percent cover of live coral. Further time-series recordings are planned to analyze whether the reported different stages of hostcoral interaction reflect a real gradient across time. In contrast to our studies, Zvuloni and coworkers [1] also observed branching corals, for example, the hydrozoan Millepora sp., dramatically affected by the gastropods mucus nets. This may end in the loss of the coral's typical terminal polyps [1]. Until now, there is no explanation for the observed deformations and degenerations of corals. The physiological effects and the exact mechanisms underlying vermetid-coral interactions remain unknown. The following hypotheses were presumed: (1) occluding mucus nets reduce the water flow around the corals and prevent them from feeding on plankton inducing competition pressure (Colgan in [9]), (2) mucus nets have an abrasive effect on coral polyps (own suggestion), (3) D. maxima consumes the coral's (secondary) metabolites and/or their mucus (suggested by Fenner [51]), and (4) mucus nets contain chemicals that influence coral growth (suggested by Zvuloni and coworkers [1], own suggestion in combination with (2)).

4.4. Conclusion/Outlook. This is the first record of bioactive properties in mucus producing organisms belonging to the Vermetidae. Ex situ feeding experiments with isolated substances are in progress to study further potential bioactive properties (e.g., ichthyotoxicity) besides the antimicrobial effect. Additionally, analyses are ongoing to elucidate the structural formula of the acting compounds by HPTLC/HRMS. We suggest that other mucus net producing taxa (e.g., polychaetes) also contain bioactive substances what open a new field in the search for marine natural products with possible application in human medicine.

Conflict of Interests

There is no conflict of interests in the submitted paper.

http://dx.doi.org/10.1155/2013/283506

Acknowledgments

The authors thank the DiveIn, Dahab, all the staff, especially Andreas Tischer, and Hans Lange for their support and providing equipment; the Dahab Marine Research Center (DMRC) and all interns "milking" the wormsnails, Stefan Rauchut, and Tim Cross; furthermore, special thanks to Nils Anthes, University of Tubingen for sparking the interest in wormsnails and providing the literature. The authors are thankful to Merck, Darmstadt, Germany, and CAMAG, Berlin, Germany, for support regarding plate material and instrumentation, respectively.

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Anne Kloppel, (1) Franz Brummer, (1) Denise Schwabe, (2) and Gertrud Morlock (3)

(1) Department of Zoology, Biological Institute, University of Stuttgart, Pfaffenwaldring 57, 70569 Stuttgart, Germany

(2) Animal Evolutionary Ecology, Zoological Institute, University of Tubingen, Auf der Morgenstelle 28, 72076 Tubingen, Germany

(3) Institute of Food Chemistry, University of Hohenheim, Garbenstra[ss]e 28, 70599 Stuttgart, Germany

Correspondence should be addressed to Anne Kloppel; anne.kloeppel@bio.uni- stuttgart.de

Received 31 March 2013; Accepted 24 May 2013

Academic Editor: Horst Felbeck

TABLE 1: List of reef fish and their preferred feeding mode
that share the same habitat like wormsnails.

Family            Genus/species              Feeding

Acanthuridae      Acanthurus sohal           Algae, zooplankton
Acanthuridae      Naso elegans               Brown algae
Acanthuridae      Naso unicornis             Brown algae
Acanthuridae      Zebrasoma xanthurum        Algae
Apogonidae        Apogon spp.                Fishes, crustaceans,
                                             zooplankton
Balistidae        Rhinecanthus assasi        Benthic invertebrates
Blenniidae        Cirripectes castaneus      Benthic algae
Blenniidae        Ecsenius dentex            Thread algae
Blenniidae        Ecsenius gravieri          Thread algae
Chaetodontidae    Chaetodon auriga           Polychaetes, anemones,
                                             coral polyps and mucus,
                                             algae
Chaetodontidae    Chaetodon austriacus       Coral polyps and mucus,
                                             cnidarian tentacles
Chaetodontidae    Chaetodon fasciatus        Cnidarian polyps and
                                             mucus, invertebrates,
                                             algae
Chaetodontidae    Chaetodon paucifasciatus   Coral polyps and mucus,
                                             invertebrates, algae
Chaetodontidae    Heniochus intermedius      Zooplankton, benthic
                                             invertebrates
Cirrhitidae       Paracirrhites forsteri     Fishes, crustaceans
Holocentridae     Sargocentron diadema       Snails, polychaetes,
                                             crustaceans
Labridae          Cheilinus lunulatus        Benthic invertebrates
                                             like molluscs and
                                             crustaceans
Labridae          Gomphosus caeruleus        Small fish, benthic
                                             invertebrates
Labridae          Halichoeres hortulanus     Benthic invertebrates
Labridae          Labroides dimidiatus       Fish parasites, skin and
                                             mucus
Labridae          Thalassoma lunare          Small fish, benthic
                                             invertebrates
Labridae          Thalassoma rueppelii       Small fish, benthic
                                             invertebrates
Mullidae          Parupeneus spp.            Fishes, benthic
                                             invertebrates
Ostraciidae       Ostracion cyanurus         Sessile invertebrates,
                                             sponges, algae
Ostraciidae       Tetrasomus gibbosus        Benthic, sessile
                                             invertebrates
Pomacanthidae     Pygoplites diacanthus      Sponges, tunicates
Pomacentridae     Abudefduf spp.             (zoo)plankton, algae
Pomacentridae     Amblyglyphidodon spp.      Zooplankton, drifting
                                             organic material
Pomacentridae     Chromis spp.               Plankton, algae,
                                             (omnivores)
Pomacentridae     Chromis viridis            Plankton
Pomacentridae     Dascyllus aruanus          Zooplankton, benthic
                                             invertebrates, algae
Pomacentridae     Dascyllus trimaculatus     Algae, planktonic
                                             crustaceans (copepods)
Pomacentridae     Pomacentrus trilineatus    Invertebrates, algae
Pomacentridae     Stegastes nigricans        Algae, gastropods,
                                             sponges, copepods
Pseudochromidae   Pseudochromis spp.         Crustaceans, worms,
                                             zooplankton
Scaridae          Chlorurus gibbus           Benthic grazer of algae
Scaridae          Hipposcarus harid          Thread algae
Scaridae          Scarus spp.                Thread algae, benthic
                                             algae
Serranidae        Cephalopholis sp.          Fishes, crustaceans
Serranidae        Epinephelus fasciatus      Fishes, crustaceans
Serranidae        Epinephelus tauvina        Fishes
Serranidae        Pseudanthias spp.          (zoo)plankton
Tetraodontidae    Arothron diadematus        Invertebrates, algae
Tetraodontidae    Arothron hispidus          Invertebrates (sponges,
                                             tunicates, worms,
                                             crustaceans, corals,
                                             molluscs, echinoderms),
                                             algae

And some unidentified Labridae, Serranidae, Pomacentridae,
and Acanthuridae
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Title Annotation:Research Article
Author:Kloppel, Anne; Brummer, Franz; Schwabe, Denise; Morlock, Gertrud
Publication:Journal of Marine Biology
Article Type:Report
Date:Jan 1, 2013
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