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Article

Trapezia Crabs That Dwell in Distinctive Day/Night Canopy Compartments of a Marine Animal Forest, Forage on Demersal Plankton

1
Marine Biology and Biotechnology Program, Department of Life Sciences, Ben-Gurion University of the Negev, Eilat Campus, Beer-Sheva 84105, Israel
2
Israel Oceanography and Limnological Research, National Institute of Oceanography, Tel-Shikmona, P.O. Box 9753, Haifa 3109701, Israel
3
The Interuniversity Institute for Marine Science, Eilat 88000, Israel
4
Spatial Ecology Laboratory, Department of Life Sciences, Ben Gurion University of the Negev, Beer-Sheva 84105, Israel
*
Author to whom correspondence should be addressed.
J. Mar. Sci. Eng. 2022, 10(10), 1522; https://doi.org/10.3390/jmse10101522
Submission received: 1 August 2022 / Revised: 25 August 2022 / Accepted: 7 October 2022 / Published: 18 October 2022
(This article belongs to the Special Issue Benthic Species and Habitats)

Abstract

:
Canopies of branching corals harbor a wide range of sessile- and mobile-dwelling species that benefit from the physical compartments and the micro-environments created by the complex three-dimensional structures. Although different compartments within canopies are differentially used by inhabitant species, the distribution of mobile animals between coral canopy compartments are not fully explored. Here, we study Stylophora pistillata, a common branching coral in the Gulf of Eilat that harbors obligatory crabs from the family Trapezia. Two in situ surveys elucidated diel dynamics in compartmental distributions of Trapezia species within S. pistillata canopies compartments, associated with the crab’s body size and day/night activities. Whereas all crabs were found within sheltered spaces in the coral canopy understory or in the base during day hours, laboratory experiments revealed that nighttime distributions of small and large crabs (in middle and up compartments, respectively) are not intraspecific competition-borne, but rather, the outcome of preferred crab-size location for a novel feeding type, predation on demersal plankton. This study, thus, disclosed the importance of studying the coral’s three-dimensional structures and within canopies’ compartments for understanding the biology of dwelling species in the animal forests’ canopies.

1. Introduction

Scleractinian branching corals are the major habitat constructors and assemblers for the marine animal forests (MAFs, the living three-dimensional communities dominated by megabenthic suspension feeders) of coral reefs, providing a wide range of ecosystem services [1,2,3]. The complex three-dimensional (3D) structures of their canopies (the aboveground portion of the coral colony, formed by the collection of individual branches and spaces that have important ecological functions [4]) create ecological spaces within the canopies’ compartments (structurally separated spaces) and provide food and shelter [1,5,6] to numerous taxa of sessile and mobile dwelling organisms (organisms that live most or all of their lives in close proximity to a host coral colony [7]). The high biodiversity allied with MAFs in general, and with branching corals in particular [6,8,9], is further associated with the diverse environmental conditions created within the compartmental heterogeneity of the 3D structures [1,2,10,11] and entitle many of the branching coral species as ecosystem engineering species [12,13].
The corals MAFs structurally and functionally resemble terrestrial forests (trees), all made by assembling hierarchical basic units, such as the corals’ polyps and branches, as compared to the trees’ leaves and branches [5,14,15]. Yet, while canopies in terrestrial forests have been intensively studied as the functional structural framework that shape the assemblages and the behaviors of forest-dwelling species [16,17,18,19,20,21], studies on the distributions of the dwelling species within branching coral canopies are lacking [5,22]. Tree canopies may create numerous microclimate conditions, thus, providing unalike resource availabilities, microclimate preferences, various types of refuges, and a wide range of biological and environmental goods and services to the dwelling species [10,19,23,24]. Similarly, a branching coral canopy shapes several micro-environments, defined as compartments, that are different by their location upon the coral canopy from bottom to top. These compartments differ by being subjected to unalike current intensity, light regime, and properties, such as inclusive volume and access to food, altogether creating distinct compartmental distribution for dwelling species, that may also vary from day to night [5]. The distributions of dwelling species within and among canopy compartments and between day/night hours are not fully explored.
One of the widely distributed MAFs species in the northern Gulf of Eilat, Red Sea, is the branching coral Stylophora pistillata (Esper, 1792) (family: Pocilloporidae; Figure 1a). The canopy’s architecture of S. pistillata is designed on iterative processes of polyps and branches [25,26,27], with growing branches typically added via dichotomous bifurcation at the branch tips, while side-growing branches are formed by the budding of lateral up-growing branches. Following colonial astogeny, S. pistillata develops shrub-like and nearly sphere-shaped canopies, inclusive of various compartments, all equipped with a wide range of inter- and intra-compartmental spaces between the structural mesh of up-growing and side-growing branches, spaces that are used by the coral’s dwelling species [15].
Among the common and widely distributed dweller species within S. pistillata canopies are decapods of the genus Trapezia. These crabs are obligatory symbionts within pocilloporid corals [28,29,30,31,32] and are considered to have mutualistic relationships with the host corals, imposing positive impacts on coral growth [33] and health [34] while defending coral from predators [35,36]. The Trapezia species are further considered to be dependent on their coral hosts’ tissues, since earlier findings on feeding behavior and follow-up of photosynthetically labeled carbon indicated that they feed on coral mucus, polyps, and detritus settled on the coral tissues [29,30,37,38,39], further retreating from senescing coral colonies [40]. The demographic structures of Trapezia species and specimens within the coral canopies are determined by the sizes of ecological volumes within canopies and the crabs’ inter- and intraspecific interactions with other dwelling organisms [41,42], all leading to the existence of a single mating pair and several juveniles inhabiting a single coral canopy [22,29,41,43]. Tsuchiya and Taira [22], further suggested that intraspecific competition between adults and young crabs led to microhabitat segregation within canopy. The literature reveals that small corals host only one individual and that there is an association between the coexistence of more than a single Trapezia species per coral, as heterosexual pairs, and as individuals, based on the canopy size [5,22,41,44].
Trapezia crabs were further documented to move during night hours, when most predatory fish species are dormant, from their host canopies to larger canopies, in search of improved territorial sites or mates [37,41], and the larger crabs evict smaller crabs from selected colonies [42,45].
While most studies examined the Trapezia—host relationship primarily during day time, our field surveys on S. pistillata colonies at nighttime in Eilat’s reefs (northern Red Sea) further documented an unnoticed before-feeding strategy for the Trapezia specimen that forage on free-swimming demersal plankton [46], addressing queries for the links between this feeding strategy and the crabs’ positions within coral compartments at day and night hours [5]. To further elucidate the intimate site selection position, we tested the null hypothesis that trapezia activities do not differ between day and night, nor among Trapezia species and different crab sizes. Thus, the spatial and temporal partitioning within and between Trapezia species distributions among canopy compartments were investigated by conducting field surveys and laboratory experiments while studying their feeding behaviors.

2. Materials and Methods

2.1. Canopy Compartment Usage by Trapezia Crabs-Day and Night Field Surveys

Compartments composition of Trapezia species and individual crabs in the Stylophora pistillata canopy [5] were followed in two field surveys using SCUBA and snorkel (June to September of 2020–2021) at the Japanese Gardens, a narrow and shallow (>7 m depth) fringing reef on the west Israeli shoreline of the Gulf of Eilat, Red Sea (29°30′ N, 34°56′ E). In order to avoid repetition of the surveyed corals belt transects (50 × 2 m, >5 m apart, 1–7 m depth) were placed perpendicular to the coastline from the lagoon to the fore-reef (we considered belts containing >10 S. pistillata colonies). Each canopy was visually surveyed twice for 1–3 min (according to the coral complexity and size), first during the day (3:00–5:00 p.m.), and then during nighttime (8:30–11:30 p.m.) for the presence and compartment allocation of the canopy’s dwelling Trapezia species. Daytime surveys also included measurements of canopy attributes (height, diameter, Strahler numbers). The canopies Strahler numbers provided us the tool to sperate the canopy to different compartments [5]. Strahler numbering is a numerical measure of branching complexity, originally introduced in hydrology to define river stream based on a hierarchy of tributaries [47]. In the coral system, ordering initiates at the terminal branches and increases when two branches of equal order meet.
Trapezia individuals were categorized to three size groups (Trapezia cymodoce [Herbst, 1801] carapace width >2 cm = large, 1–2 cm = medium, <1 cm = small; Trapezia digitalis [Latreille, 1828] carapace width large >1.5 cm = large, 1–1.5 cm = medium, and <1 cm = small), and to the canopy compartment they were resident (up, middle, base, understory [5]; Figure 1b). Individual crabs traveling between the coral compartments during the surveys were assigned to all crossed compartments. To reduce artifacts caused by interference with the observer, observations began from a distance of one meter away from the coral colony, and then the observations were confirmed while slowly approaching the coral colony, using a flashlight for meticulous examinations [44]. Each colony was photographed underwater (using a Canon G7X, Tokyo, Japan and Nikon Coolpix W300, Tokyo, Japan) to verify doubtful results or to respond to emerging queries. All observations were made without manipulations or hand contacts to avoid biasing the organisms’ behavior. Rare Trapezia species were considered as species appearing with a total of <10 specimens in all censuses, and they were omitted from further analyses.

2.2. Canopy Compartment Usage by Crabs-Laboratory Experiments

To test the distribution among coral compartments and the dynamics for the different group sizes of T. cymodoce and T. digitalis crabs at day and night and to assess the influence of the large size crabs on the compartmental distribution of smaller crabs (small and medium) within and between species, we conducted five experimental sets (August 2021 to April 2022). Each of these experiments was conducted for two days, on the first day with the presence and then, on the second day, with the absence of large body size T. cymodoce pairs. In each experiment, we documented the compartment locations of Trapezia specimen assigned within the coral canopy at day (12:00–4:00 p.m.) and at night (8:00 p.m.–12:00 a.m.). Prior to each experiment (the night before the experiment startup), crabs (according to each experiment design) were placed in the examined corals, and after the first day and night observations, large crabs were removed from the experiment for the day and night ‘large size absence’ observations.
Each one of the Trapezia individuals was involved only once in the experiments, totaling 237 T. cymodoce (30, 46, 161; small, medium, large, respectively), and 25 T. digitalis individuals (14, 11; small and medium, respectively). All crabs were collected from S. pistillata colonies provided by the Israeli Nature and Parks Authority (INPA) and from S. pistillata colonies (n = 21, sizes 118–2102 cm3; Supplementary Table S1) that were haphazardly sampled by SCUBA. All corals together with their dweller’s Trapezia crabs were sample along the Gulf of Eilat, Red Sea (29°30′ N, 34°56′ E; 3–10 m depths) and were kept in a running seawater tables facility at the Interuniversity Institute for Marine Science in Eilat (IUI).
In all five experiments, we repeatedly used the same sampled S. pistillata colonies (n = 21, sizes 118–2102 cm3) that were first cleared of all other dwelling movable species (e.g., sea urchin, brittle stare, fishes, crabs, etc.), in order to prevent possible influences of interactions between Trapezia crabs and other species. Then, each coral was placed in an isolated closed container supplied by a running open seawater system. The crabs and all other dwelling species were removed from their original coral hosts prior to each experiment by placing the coral above an empty tank filled with seawater and then by pushing the animals out while carefully inserting a plastic Pasteur pipette or a metal stick between coral branches.
In the first experiment, we examined the distribution among the canopy compartments of combined three T. cymodoce body sizes (small, medium, and large), thus, we used the original T. cymodoce populations found on each of the 21 sampled S. pistillata canopies (Large 39, medium 25, and small 15; Figure 2; Supplementary Table S1). In the second and the third experiments, we added to each S. pistillata canopy one large pair of T. cymodoce, together with only one different Trapezia individual, as follows: in the second experiment, one medium-size T. cymodoce individuals/canopy (n = 21.), and in the third experiment, one small-size T. cymodoce individual (n = 15). In the next two experiments, we tested the outcomes of interspecific interactions, by introducing one T. digitalis individual together with T. cymodoce large pairs on each canopy. In these experiments, we used only two size classes of T. digitalis, small (n = 14; 4th exp.) and medium (n = 11; 5th exp.) (Figure 2).

2.3. Feeding on Planktonic Organisms-Laboratory Experiments

A total of 114 T. cymodoce individuals (66 large, 48 medium) were placed in pairs in closed system water tanks (29 × 29 × 29 cm) filled with fresh ambient seawater (23–24 °C, with room light [led illumination]). Trapezia pairs were assigned to one of three treatments designed by the host status: live coral, coral skeleton, and no coral (total 38 individuals per treatment, 11 large and 8 medium-size pairs, respectively). After one hour of acclimatization, each tank received 2–5 mL of live Artemia (1 mL = 5 individuals, 7–16 days old) to test the feeding behaviors of Trapezia crabs. We defined ‘success’ and ‘failure’ outcomes for two feeding behaviors: 1. Reaction—crab’s response, observed by (I) continually flicking their antennas, (II) consistent movements of the maxillipeds (also accompanied with body cleaning behaviors), and both reactions could be accompanied by movements of the second pereiopods along the tomentum on the chela or toward the mouthparts, a behavior that has been described in relation to mucus collection [30]; 2. Predation: The crabs use the chelipeds to catch and eat the prey. Each individual Trapezia was observed for up to 15 min or less (once both behaviors were determined as ‘success’). All experiments were conducted repeatedly from 9:00 a.m. to 2:00 a.m. of the following day. All Trapezia were provided by the INPA and, upon receiving, were kept for 1–3 days with their original coral host in the running sea water facility at the IUI before experimental assignment.

2.4. Statistical Analyses

We used Bray–Curtis dissimilarities matrix with zero adjustments of +1 (dummy variable) to compare the compartmental distribution between and within Trapezia species, between the coral canopies between Trapezia size groups and between the years. For the analyses of field observations, we used a 1.4 power transformation followed by a two-way PERMANOVA and a pairwise permutation MANOVA with false discovery rate adjustment (FDR). First, we used the crab’s body size group with the interaction of time (day, night) as the fixed effects, and canopy sample ID as a random effect. As the outcome was significantly different between the size groups, we grouped each body sizes for each species by the observation time (day/night) and tested the compartmental distributions between years (2020, 2021), which were used as the fixed effects while canopy sample ID was considered as a random effect (R packages: [48,49,50,51]). The same analyses were employed in the laboratory experiments using a power transformation on the dissimilarity matrix data with time and size as the fixed effect, and coral ID as the random effect. For pairwise analyses, we grouped crabs by their body size with the presence or absence of large individuals in addition to the time. For the feeding experiments, we used Pearson’s Chi-square followed by post hoc pairwise tests of independence for nominal data with the Fisher exact adjusted by FDR (R package: [52]). All analyses were performed using RStudio version 1.3.1093, and plots were made with Office software (Excel and PowerPoint).

3. Results

3.1. Day and Night Surveys

A total of 114 and 79 coral canopies were day and night surveyed during the years 2020 and 2021, respectively (Figure 3; Supplementary Table S2 In both years, the most common Trapezia species was T. cymodoce (165/274 [day/night] individuals, in 2020 and 111/187 [day/night] individuals in 2021), followed by T. digitalis (30/126 [day/night] individuals in 2020, and 22/82 [day/night] in 2021). Two other Trapezia species, Trapezia guttata (Rüppell, 1830) (7/4 individual, 2020/2021, respectively), and Trapezia rufopunctata (Herbst, 1799) (6/0 individual, 2020/2021, respectively) were considered rare species and were omitted from our analyses. The compartmental distributions for T. cymodoce and T. digitalis were not different between years (T. cymodoce, p > 0.05, F = 2.45, r2 = 0.004, df= 1; T. digitalis, p > 0.05, F = 2.46, r2 = 0.01, df = 1, two-way PERMANOVA; Supplementary Tables S3 and S4).
The two years cumulative day and night differences for individuals documented in the same coral canopies were close to two-fold for T. cymodoce (276/461 individuals, day/night, respectively) and four-fold for T. digitalis (52/208 individuals, day/night, respectively). Out of the total surveyed canopies (n = 193), T. cymodoce and T. digitalis were found in 75%/92.7%, and 17.6%/48.7% (day/night) observations, respectively. Both species were found together in the same canopy on 9.8%/43.5% (day/night) observations, where T. digitalis individuals were usually of medium and small sizes (8.3%/40.1%, day/night). T. digitalis large individuals were scarce in this survey, found only in 4.1%/4.7% (day/night) observations, coexisting with large T. cymodoce only on 1.6%/2.6% (day/night) observations.
Significant differences in daytime activities were recorded between the two species (p < 0.001, F model = 30.9, r2 = 0.37, df = 11, two-ways PERMANOVA; Supplementary Table S5) and within species size groups (T. cymodoce, p < 0.001, F model = 9.87, r2 = 0.03, df = 2; T. digitalis, p < 0.001 F model 5.17, r2 = 0.04, df = 2, two-ways PERMANOVA; Supplementary Tables S6 and S7). Further, during the night hours, the common distribution design of either size group in both species was associated with the more exposed compartments (middle and up), as compared to the more protected compartmental spaces during day hours (understory and base; Figure 3). Differences were also recorded for compartmental distributions in day and night hours between the large-size groups of T. digitalis and T. cymodoce (p > 0.05, pairwise permutation MANOVA; Supplementary Table S8). Large T. digitalis individuals shared the same canopy compartments with T. cymodoce medium and small individuals at day (understory, base and middle; p > 0.05, pairwise permutation MANOVA; Supplementary Table S8) and night hours only with T. cymodoce medium-size individuals (base, middle, and middle to up; p > 0.05, pairwise permutation MANOVA; Supplementary Table S8). Large T. cymodoce crabs were significantly different from T. digitalis medium and small individuals for day/night compartmental distributions (p < 0.05, pairwise permutation MANOVA; Supplementary Table S8), as at day hours they were found at the lower compartments, while at night they migrated upward to the middle compartments (base 91%/25.86%, base to middle 6%/56.3%, and middle 3%/8.7% individual frequency, day/night, respectively). During day hours, compartmental distributions for medium and small-size T. digitalis were not significantly different from those of medium and small T. cymodoce individuals (p > 0.05, pairwise permutation MANOVA; Supplementary Table S8), indicating the same compartments preference at day hours, which includes the middle, and down to the understory, with higher frequencies at the lower and more sheltered compartments (understory and base; Figure 3). At night hours, the medium-size groups of the two crab species shared the same distribution pattern (p > 0.05, pairwise permutation MANOVA; Supplementary Table S8) and were more prevalent in the middle compartment (61.8% and 68.1% T. cymodoce and T. digitalis, respectively), while small crabs showed different distribution patterns (p < 0.05, pairwise permutation MANOVA; Supplementary Table S8), with T. digitalis individuals more common in the up compartments (86.1% up, 12.5% middle to up) and T. cymodoce individuals more common in the middle compartments (20.4% middle, 27.8% middle to up).
Comparison between day and night distribution shows that all size groups within species were different (p < 0.05, pairwise permutation MANOVA; Supplementary Tables S9 and S10), with the exception of large T. digitalis (p > 0.05, pairwise permutation MANOVA; Supplementary Table S10).

3.2. Canopy’s Compartment Usage by Crabs-Laboratory Experiments

The laboratory observations revealed significant day/night changes in the canopy’s compartmental distributions of both species in all different experimental settings (Figure 4a–e; Supplementary Tables S11–S15) and reflected changes between the different body sizes (p < 0.05, two-ways PERMANOVA; Supplementary Tables S16–S25). Interestingly, in each of the five experiments, the presence or the absence of large-sized T. cymodoce individuals did not change the temporal and the spatial compartmental distributions of the small- and medium-size groups (p > 0.05, pairwise permutation MANOVA; Supplementary Tables S26–S30), except for T. digitalis medium-size group yet, only for day hours. In the presence of large T. cymodoce individuals at day hours, medium T. digitalis were distributed in all coral compartments (understory, base, middle, and up), a distribution that was changed in the absence of large-size T. cymodoce individuals (p < 0.05, pairwise permutation MANOVA; Supplementary Table S29), indicating interference of large T. cymodoce for the day hours (Figure 4).
The distribution patterns along the two days treatments (with and without the presence of large T. cymodoce), and throughout all five experiments, showed that at daytime the canopy “up” compartment was rarely occupied by all size groups (T. digitalis: 13.6% small, and 3.6% medium; T. cymodoce: 1.1% medium, and 2.5% [“base to up”] large size), and most crabs were recorded in the lower compartments (understory, base, and middle). Compartmental distribution changed at night hours, where the “up” compartment was commonly occupied by the small-size groups (T. digitalis 81.8%, and T. cymodoce 85%) and the middle compartment by the medium-size groups (T. digitalis 71.4%, and T. cymodoce 92.4%). The up and middle compartments enabled sheltering of the small-body-size crabs between the small branches (Strahler order 1 and 2) or within the small bifurcation points, and yet to be found at the edge of the canopy (Figure 1c–e).
T. cymodoce large individuals across all treatments (n = 161) were mostly found in the base compartment (67%, 45% day and night, respectively), though, at night, they were also prevalent in the middle compartments (middle: 16%, 35%; base to middle 7%, 18%, day and night, respectively).

3.3. Plankton Foraging-Laboratory Experiments

With the presence of Artemia prey, a reaction behavior was observed in all Trapezia crabs in the ‘live coral’ treatment, and, in all, except a single large individual, in the ‘coral skeleton’ experiment (Supplementary Table S31). Artemia presence in the ‘non-coral’ treatment triggered crabs’ reaction behavior only for 33% of the large body size individuals (12/36).
Most Trapezia crabs in the ‘live coral’ and ‘coral skeleton’ treatments caught and ate Artemia (35/38 in both treatments), with just a single large-size and two medium-sized crabs that failed to catch prey within 15 min from Artemia introduction. When Artemia were introduced to the tanks, the crabs migrated to the more open spaces within the corals’ canopies (middle to up compartments) as part of their food acquisition. In ‘non-coral’ treatments, the crabs did not show any sign of predation behavior (0/38 predation success). Furthermore, the Trapezia crabs ignored the Artemia prey even in cases where the Artemia individuals were swimming towards them or physically contacted their bodies.
For both behaviors, no significant differences were found between crabs in ‘live coral’ and ‘coral skeleton’ treatments, and these two treatments were significantly different from crabs in the ‘non-coral’ treatment (Pearson chi-squared test: p < 0.05, df = 2, 2 = 63.2, and p < 0.05, df = 2, 2 =90.7, ‘reaction’ and ‘predation’ behaviors, respectfully). Differences between the medium- and large-size crabs’ behaviors, were significant only for the reaction behavior in the ‘non-coral’ treatment (Pearson chi-squared test: p < 0.05, df = 1, 2 = 10.36; Table 1).

4. Discussion

Branching coral colonies, such as other MAFs, are known to harbor a wide range of coral-dwelling invertebrates and fishes whose communities’ structures vary over space and time [9,53,54,55,56], reminiscent of the documentations for terrestrial forests [10,19,57,58] and marine algal forests [59,60]. The structures, sizes (that are developed through specific astogenic pathways [15]), and the inclusive special compartments [5] of MAFs canopies are subject to temporal and spatial changes in associated epifauna [7,44,61]. In these coral species that behave like ecosystem engineers, the more structured the living 3D shapes, the increased heterogeneity of interactions are foreseen in the interplay of living communities and space utilization [62,63,64]. Yet, knowledge gaps hinder our abilities to evaluate the ecological properties, as well as the ecological services provided by branching corals’ canopies.
This study focuses on the Stylophora pistillata canopy’s diel compartmental utilization by two Trapezia crab species (specific dwellers in pocilloporid corals [31,32]), in association with the Trapezia crab’s abilities to prey on demersal plankton [46]. Results revealed that the crabs did dwell in different canopy compartments in relation to day/night hours and crabs’ body sizes. During the day hours, crabs reside in the lower and more protected compartments (the understory and base; [5]), while during the night hours, when demersal plankton become available [65,66,67], crabs exploit the more exposed compartments (middle and up; Figure 1). Thus, the coral canopy’s 3D structure and primarily its major compartments (as constructed by the Strahler order number of branches [5]) reveal a phenomenon of compartmental preference by Trapezia crabs that further show temporal variation in diel compartmental allocation and in size distributions. Moreover, this diel compartmental distribution, where Trapezia individuals hide during the day and are more visible during the night might, indicate for a nocturnal activity nature in the crabs’ life history strategies [68].
Throughout the two-year study, Trapezia compartmental distribution patterns in the coral canopy were consistent for the variables crab sizes and daytime. Both Trapezia species use the coral’s 3D structural features that are probably most optimal for vital functions (e.g., protection and feeding). During the day, crabs adopted a cryptic status within the coral’s canopy to minimize the foraging efficiency of predators [68,69] where small and medium-size carbs further benefited from the smaller crevices found at the coral base and understory, and larger crabs were hidden between the lower parts of branches emerging from the coral base (Figure 1). These results are consistent with previous studies on other Trapezia species, revealing that adult crabs reside in the coral central parts, while juveniles dwell in tunnels or crevices in the coral base [22,37,42,43]. Yet, former studies did not examine the nocturnal distributions when daytime predation pressure is reduced [68,69,70]. Comparably with the upward nocturnal movement of most Acropora-dwelling species [71], this study reveals that at nighttime (when predation pressure is low), Trapezia crabs migrate towards the coral-exposed compartments. Small-size crabs are located at the upper compartment (up), medium-size carbs at the middle to up compartments, and large crabs at the base to middle compartments.
As in other crabs [72,73,74], the Trapezia literature indicates a domination related to crabs’ body sizes, where larger crabs expel a smaller one [42]. Yet, only few studies have examined the hierarchy-related class sizes distributions between adults and young on a colony [22,29,42]. The main driver for spatial and temporal distribution patterns of species is the availability of resources [75,76]. With regard to the availability of spatial resources, the Trapezia’s compartmental allocation suggests subordination dynamics between the crab’s different body sizes, where the animal occupies the most desirable portion of its biological niche [77]. During the day hours, large Trapezia individuals are found mostly at the canopy base, the canopy part with the highest Strahler order branches, which is enclosed from above by the structure complexity (e.g., length, shape, width, etc.) of the other lower-order branches. Altogether, these branches construct the deeper spaces inside the canopy, where hosted organisms are less vulnerable to predation [68,78,79], since Trapezia crabs outside the coral host are easily eaten by a wide range of fish species [37]. During the night, large individuals are found within the upper, yet deeper spaces (base and middle compartments), while smaller crabs are relegated to the more external and exposed parts (up and middle compartments) of the canopy [80], thus, circumventing the exhaustive daytime predation pressures [68,69], yet becoming more vulnerable to the less intensive nocturnal predation impacts, by predators, such as the hawkfish Itycirrhitus wilhelmi [69,81].
The fact that smaller size crabs do not switch compartmentation sites in the absence of larger size crabs at night time may further support the view that the different chosen compartments extend beyond the provision of the shelter alone. Further, plankton predation by the Trapezia crabs is probably of prime importance to the crabs’ diet. The common idea is that Trapezia crabs rely primarily on coral tissue and mucus as a food source [30,37,38,39], hence, we may expect that in the absence of the large crab size, the smaller crabs would be evenly distributed on the coral tissues without any distinct compartmental allocation. The current outcome for daytime-specific site distributions highlights the possibility that the different body sizes’ locations are associated with predation efficiencies (or “optimal foraging partitioning”), attesting for the importance of predation on demersal plankton to the biology of the Trapezia crabs. Hence, the large and the small animals at night occupy the most desirable biological niche for demersal foraging, and during the day, the most suitable hiding spaces as predation refuges.
In tropical forests, variable foraging parameters, such as perch sizes, attack types (different strategies for piking or catching food), and foraging height along the vertical axis of the canopy, are important in delineating niches separating between species and within-species body size groups, allowing the coexistence of a wider range of organisms within the same canopy spaces [82,83]. Similarly, the corals’ canopy compartmental systems may create more biological niches, providing additional foraging grounds and features that are exploited differently by different crab sizes. These may further facilitate different food (detritus or demersal plankton) acquisition, and reduce intra- and inter-specific competition by channeling size classes into separate compartments within the canopy [84].
Branching corals, like other MAF organisms, are autogenic ecosystem engineers that are capable of modifying their intimate environments by their own structural complexity. Considering the S. pistillata canopies, these structures may change current flow velocity, modify the mean and turbulent flow structures, and impact sediment resuspension, as suggested for other marine forests [85]. This, in turn, may prolong the residence time of food particles (including demersal plankton) within various canopy compartments [86] and most likely leads to the creation of variable microenvironments characterized by different water dynamics. Therefore, fine analyses of coral canopies using more than a single method (here, we used the Strahler order as an analyzing tool of the coral canopy structure [5]) may shed more light on the biological features of the 3D spaces within a single coral canopy.

5. Conclusions

The coral dwelling Trapezia crabs use different compartments within the coral complex architecture differently between day and night and between different body size. During day hours crabs use the coral compartments primarily as a shelter, while at night shift compartments for predation activity. Lab experiments also showed that the partitioning distribution among the coral compartments of each carbs size groups is associated with the crabs’ body size preference rather than with competition. Lab experiments also documented the relationship of Trapezia crabs with their host status (live, dead skeleton, and without coral), and reveled that crabs do catch and eat free-living plankton.

Supplementary Materials

The following are available online at https://www.mdpi.com/article/10.3390/jmse10101522/s1. Table S1: Stylophora pistillata attributes (n = 21) with their Trapezia cymodoce population for compartment usage in laboratory experiments. Table S2: Day and night survey results (2020–2021) for T. cymodoce and Trapezia digitalis crabs, Tables S3–S7: Two-ways PERMANOVA summary results for T. cymodoce and T. digitalis in day and night survey, Tables S8–S10: Pairwise permutation MANOVA with false discovery rate adjustment (FDR) summary results for T. cymodoce and T. digitalis in day and night survey. Tables S11–15: Summary results for laboratory experiments 1–5 of crabs compartment usage, Tables S16–S25: Two-ways PERMANOVA summary results for laboratory experiments 1–5 of crabs compartment usage, Tables S26–S30: pairwise permutation MANOVA summary results for laboratory experiments 1–5 of crabs compartment usage, Table S31: Summary results for lab feeding behavior experiments.

Author Contributions

Conceptualization, Y.S. and B.R.; survey and methodology, Y.S.; software, Y.S.; validation, Y.S. and B.R.; formal analysis, Y.S.; investigation, Y.S.; resources, B.R.; data curation, Y.S.; writing—original draft preparation, Y.S. and B.R.; writing—review and editing, Y.S., B.R. and Y.Z.; visualization, Y.S.; supervision, B.R. and Y.Z.; project administration, Y.S. and B.R.; funding acquisition, B.R. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Institutional Review Board Statement

The study was conducted according to national guidelines and permits no 42516 by the Israeli Nature.

Informed Consent Statement

Not applicable.

Data Availability Statement

Raw data are appended in the Supplementary Material.

Acknowledgments

We wish to thank to O. Ovadia and Y. Belmaker for statistical consulted, D. Shefy for creative advice, G. Paz for assisting with visualization, and T. Marcus for photo editing. We would like to thank the Interuniversity Institution for Marine Sciences (IUI) and the Underwater Observatory Marine Park in Eilat for logistical support, and to the Israeli Nature and Parks Authority especially to C. Toufikian for their support in this research. We also thank the anonymous reviewers who greatly improved the final manuscript.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Rossi, S.; Bramanti, L.; Gori, A.; Orejas, C. Animal forests of the world: An overview. In Marine Animal Forests: The Ecology of Benthic Biodiversity Hotspots; Rossi, S., Bramanti, L., Gori, A., Orejas, C., Eds.; Springer International Publishing: Berlin/Heidelberg, Germany, 2017; Volume 1, pp. 1–28. ISBN 9783319210117. [Google Scholar]
  2. Graham, N.A.J.; Nash, K.L. The importance of structural complexity in coral reef ecosystems. Coral Reefs 2013, 32, 315–326. [Google Scholar] [CrossRef]
  3. Horoszowski-Fridman, Y.B.; Rinkevich, B. Restoring the animal forests: Harnessing silviculture biodiversity concepts for coral transplantation. In Marine Animal Forests: The Ecology of Benthic Biodiversity Hotspots; Rossi, S., Bramanti, L., Gori, A., Orejas, C., Eds.; Springer International Publishing: Berlin/Heidelberg, Germany, 2017; Volume 3, pp. 1313–1336. [Google Scholar]
  4. Zhao, T.; Cheng, Y.; Fan, Y.; Fan, X. Functional tradeoffs and feature recognition of rural production—Living—Ecological spaces. Land 2022, 11, 1103. [Google Scholar] [CrossRef]
  5. Shmuel, Y.; Ziv, Y.; Rinkevich, B. Strahler ordering analyses on branching coral canopies: Stylophora pistillata as a case study. J. Mar. Sci. Eng. 2022, 10, 121. [Google Scholar] [CrossRef]
  6. Stella, J.S.; Pratchett, M.S.; Hutchings, P.A.; Geoffrey, J.P. Coral-associated invertebrates: Diversity, ecological importance and vulnerability to disturbance. Oceanogr. Mar. Biol. An Annu. Review. 2011, 49, 43–104. [Google Scholar] [CrossRef] [Green Version]
  7. Belmaker, J. Species richness of resident and transient coral-dwelling fish responds differentially to regional diversity. Glob. Ecol. Biogeogr. 2009, 18, 426–436. [Google Scholar] [CrossRef]
  8. Reaka-Kudla, L.M. The global biodiversity of coral reefs: A comparison with rain forests. In Biodiversity II: Understanding and protecting our biological resources; Reaka-Kudla, L.M., Wilson, D.E., Wilson, E.O., Eds.; Joseph Henry Press: Washington, DC, USA, 1997; pp. 83–108. ISBN 0309052270. [Google Scholar]
  9. Pisapia, C.; Stella, J.; Silbiger, N.J.; Carpenter, R. Epifaunal invertebrate assemblages associated with branching Pocilloporids in Moorea, French Polynesia. PeerJ. 2020, 8, e9364. [Google Scholar] [CrossRef]
  10. Ishii, H.T.; Ishii, S.I.; Hiura, T. Exploring the relationships among canopy structure, stand productivity, and biodiversity of temperate forest ecosystems. For. Sci. 2004, 50, 342–355. [Google Scholar] [CrossRef]
  11. McElhinny, C.; Gibbons, P.; Brack, C.; Bauhus, J. Fauna-habitat relationships: A basis for identifying key stand structural attributes in temperate Australian eucalypt forests and woodlands. Pac. Conserv. Biol. 2006, 12, 89–110. [Google Scholar] [CrossRef]
  12. Jones, C.G.; Lawton, J.H.; Shachak, M.; Jones, C.G.; Lawton, J.H.; Shachak, M. Organisms as Ecosystem Engineers. Oikos 1994, 69, 373–386. [Google Scholar] [CrossRef]
  13. Horoszowski-Fridman, Y.B.; Brêthes, J.C.; Rahmani, N.; Rinkevich, B. Marine silviculture: Incorporating ecosystem engineering properties into reef restoration acts. Ecol. Eng. 2015, 82, 201–213. [Google Scholar] [CrossRef]
  14. Connell, J.H. Diversity in tropical rain forests and coral reefs. Science 1978, 199, 1302–1310. [Google Scholar] [CrossRef] [Green Version]
  15. Rinkevich, B. The branching coral Stylophora pistillata: Contribution of genetics in shaping colony landscape. Isr. J. Zool. 2002, 48, 71–82. [Google Scholar] [CrossRef]
  16. Harrison, J.L. The distribution of feeding habits among animals in a tropical rain forest. J. Anim. Ecol. 1962, 31, 53–63. [Google Scholar] [CrossRef]
  17. Pearson, D.L. Vertical stratification of birds in a tropical dry forest. Condor 1971, 73, 46–55. [Google Scholar] [CrossRef] [Green Version]
  18. Colquhoun, M.K.; Morley, A. Vertical zonation in woodland bird communities. J. Anim. Ecol. 1943, 12, 75–81. [Google Scholar] [CrossRef]
  19. Grimbacher, P.S.; Stork, N.E. Vertical stratification of feeding guilds and body size in beetle assemblages from an Australian tropical rainforest. Austral Ecol. 2007, 32, 77–85. [Google Scholar] [CrossRef]
  20. de Souza Amorim, D.; Brown, B.V.; Boscolo, D.; Ale-Rocha, R.; Alvarez-Garcia, D.M.; Balbi, M.I.P.A.; de Marco Barbosa, A.; Capellari, R.S.; de Carvalho, C.J.B.; Couri, M.S.; et al. Vertical stratification of insect abundance and species richness in an Amazonian tropical forest. Sci. Rep. 2022, 12, 1734. [Google Scholar] [CrossRef] [PubMed]
  21. Bates, M. Observations on the distribution of diurnal mosquitoes in a tropical forest. Ecology 1944, 25, 159–170. [Google Scholar] [CrossRef]
  22. Tsuchiya, M.; Taira, A. Population structure of six sympatric species of Trapezia associated with the hermatypic coral Pociliopora damicornis with a hypothesis of mechanisms promoting their coexistence. J. Jpn. Coral Reef Soc. 1999, 1, 9–17. [Google Scholar] [CrossRef]
  23. Ulyshen, M.D. Arthropod vertical stratification in temperate deciduous forests: Implications for conservation-oriented management. For. Ecol. Manag. 2011, 261, 1479–1489. [Google Scholar] [CrossRef]
  24. Nakamura, A.; Kitching, R.L.; Cao, M.; Creedy, T.J.; Fayle, T.M.; Freiberg, M.; Hewitt, C.N.; Itioka, T.; Koh, L.P.; Ma, K.; et al. Forests and their canopies: Achievements and horizons in canopy science. Trends Ecol. Evol. 2017, 32, 438–451. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  25. Shaish, L.; Abelson, A.; Rinkevich, B. Branch to colony trajectory in a modular organism: Pattern formation in the indo-pacific coral Stylophora pistillata. Dev. Dyn. 2006, 235, 2111–2121. [Google Scholar] [CrossRef] [PubMed]
  26. Shaish, L.; Rinkevich, B. Critical evaluation of branch polarity and apical dominance as dictators of colony astogeny in a branching coral. PLoS ONE 2009, 4, e4095. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  27. Shefy, D.; Rinkevich, B. Stylophora pistillata—A model colonial species in basic and applied studies. In Handbook of Marine Model Organisms in Experimental Biology; Boutet, A., Schierwater, B., Eds.; CRC Press: Boca Raton, FL, USA, 2021; pp. 195–216. [Google Scholar] [CrossRef]
  28. Galil, B. The adaptive functional structure of mucus-gathering setae in trapezid crabs symbiotic with corals. Symbiosis 1987, 4, 75–86. [Google Scholar]
  29. Patton, W.K. Community structure among the animals inhabiting the coral Pocillopora damicornis at Heron Island, Australia. In Symbiosis in the Sea; Vernberg, W.B., Ed.; University of South Carolina Press: Columbia, SC, USA, 1974; pp. 219–243. [Google Scholar]
  30. Knudsen, J.W. Trapezia and Tetralia (Decapoda, Brachyura, Xanthidae) as obligate ectoparasites of pocilloporid and acroporid corals. Pac. Sci. 1967, 21, 50–57. [Google Scholar]
  31. Castro, P. Brachyuran crabs symbiotic with scleractinian corals: A review of their biology. Micronesica 1976, 12, 99–110. [Google Scholar]
  32. Patton, W.K. Animals associated with living corals. In Biology and Geology of Coral Reefs; Jones, O.A., Endean, R., Eds.; Academic Press: New York, NY, USA, 1976; Volume 3, pp. 1–37. [Google Scholar]
  33. Glynn, P.W. Increased survivorship on corals harboring crustacean symbionts. Mar. Biol. Lett. 1983, 4, 105–111. [Google Scholar]
  34. Stewart, H.L.; Holbrook, S.J.; Schmitt, R.J.; Brooks, A.J. Symbiotic crabs maintain coral health by clearing sediments. Coral Reefs 2006, 25, 609–615. [Google Scholar] [CrossRef]
  35. Pratchett, M.S. Influence of coral symbionts on feeding preferences of crown-of-thorns starfish Acanthaster planci in the western pacific. Mar. Ecol. Prog. Ser. 2001, 214, 111–119. [Google Scholar] [CrossRef]
  36. Stier, A.C.; Mckeon, C.S.; Osenberg, C.W.; Shima, J.S. Guard crabs alleviate deleterious effects of vermetid snails on a branching coral. Coral Reefs 2010, 29, 1019–1022. [Google Scholar] [CrossRef]
  37. Preston, E.M. Niche Overlap and Competition among Five Sympatric Congeneric Species of Xanthid Crabs. Ph.D. Thesis, University of Hawaii, Honolulu, HI, USA, 1971. [Google Scholar]
  38. Stimson, J. Stimulation of fat-body production in the polyps of the coral Pocillopora damicornis by the presence of mutualistic crabs of the genus Trapezia. Mar. Biol. 1990, 106, 211–218. [Google Scholar] [CrossRef]
  39. Rinkevich, B.; Wolodarsky, Z.; Loya, Y. Coral-crab association: A compact domain of a multilevel trophic system. Hydrobiologia 1991, 216–217, 279–284. [Google Scholar] [CrossRef]
  40. Rinkevich, B.; Loya, Y. Senescence and dying signals in a reef building coral. Experientia 1986, 42, 320–322. [Google Scholar] [CrossRef]
  41. Castro, P. Movements between coral colonies in Trapezia ferruginea (Crustacea: Brachyura), an obligate symbiont of scleractinian corals. Mar. Biol. 1978, 46, 237–245. [Google Scholar] [CrossRef]
  42. Tsuchiya, M.; Yonaha, C. Community organization of associates of the scleractinian coral Pocillopora damicornis: Effects of colony size and interactions among the obligate symbionts. Galaxea 1992, 11, 29–56. [Google Scholar]
  43. Barry, C.K. Ecological Study of the Decapod Crustaceans Commensal with the Branching Coral Pocillopora meandrina var. Nobilis verrill. Master’s Thesis, University of Hawaii, Honolulu, HI, USA, 1965. [Google Scholar]
  44. Counsell, C.W.W.; Donahue, M.J.; Edwards, K.F.; Franklin, E.C.; Hixon, M.A. Variation in coral-associated cryptofaunal communities across spatial scales and environmental gradients. Coral Reefs 2018, 37, 827–840. [Google Scholar] [CrossRef]
  45. Stella, J.S.; Munday, P.L.; Jones, G.P. Effects of coral bleaching on the obligate coral-dwelling crab Trapezia cymodoce. Coral Reefs 2011, 30, 719–727. [Google Scholar] [CrossRef]
  46. Shmuel, Y.; Ziv, Y.; Rinkevich, B. Coral-inhabiting Trapezia crabs forage on demersal plankton. Front. Mar. Sci. 2022, 9, 964725. [Google Scholar] [CrossRef]
  47. Strahler, A.N. Quantitative analysis of watershed geomorphology. Trans. Am. Geophys. Union 1957, 38, 913–920. [Google Scholar] [CrossRef] [Green Version]
  48. Oksanen, J. Vegan: Ecological diversity. R Package Version 2.4-4; R Foundation for Statistical Computing: Vienna, Austria, 2017; p. 11. [Google Scholar]
  49. Goslee, S.C.; Urban, D.L. The ecodist package for dissimilarity-based analysis of ecological data. J. Stat. Softw. 2007, 22, 1–19. [Google Scholar] [CrossRef]
  50. Wheeler, B.; Torchiano, M. lmPerm: Permutation tests for linear models. R Package Version 2.1.0. Available online: https://cran.r-project.org/web/packages/lmPerm/lmPerm.pdf (accessed on 2 August 2016).
  51. Hervé, M. “RVAideMemoire” Testing and plotting procedures for biostatistics, Version 0.9-81.2. Available online: https://cran.r-project.org/web/packages/RVAideMemoire/RVAideMemoire.pdf (accessed on 21 February 2021).
  52. Mangiafico, S. Package ‘rcompanion’ Functions to support extension education program evaluation. R Package Version 2020, 2.3.26. Available online: https://cran.r-project.org/web/packages/rcompanion/rcompanion.pdf (accessed on 5 November 2020).
  53. Britayev, T.A.; Spiridonov, V.A.; Deart, Y.V.; El-Sherbiny, M. Biodiversity of the community associated with Pocillopora verrucosa (Scleractinia: Pocilloporidae) in the Red Sea. Mar. Biodivers. 2017, 47, 1093–1109. [Google Scholar] [CrossRef]
  54. Vytopil, E.; Willis, B.L. Epifaunal community structure in Acropora spp. (Scleractinia) on the Great Barrier Reef: Implications of coral morphology and habitat complexity. Coral Reefs 2001, 20, 281–288. [Google Scholar] [CrossRef]
  55. Carvalho, S.; Cúrdia, J.; Pereira, F.; Guerra-García, J.M.; Santos, M.N.; Cunha, M.R. Biodiversity patterns of epifaunal assemblages associated with the gorgonians Eunicella gazella and Leptogorgia lusitanica in response to host, space and time. J. Sea Res. 2014, 85, 37–47. [Google Scholar] [CrossRef]
  56. Stella, J.S.; Barrier, G.; Marine, R.; Authority, P.; Jones, G.P. Variation in the structure of epifaunal invertebrate assemblages among coral hosts. Coral Reefs 2018, 37, 827–840. [Google Scholar] [CrossRef]
  57. Chmel, K.; Riegert, J.; Paul, L.; Novotný, V. Vertical stratification of an avian community in New Guinean tropical rainforest. Popul. Ecol. 2016, 58, 535–547. [Google Scholar] [CrossRef]
  58. MacArthur, R.H.; MacArthur, J.W. On bird species diversity. Ecology 1961, 42, 59–598. [Google Scholar] [CrossRef]
  59. Ebeling, A.W.; Bray, R.N. Day versus night activity of reef fishes in a kelp forest off Santa Barbara, California. Fish. Bull. 1976, 74, 703–717. [Google Scholar]
  60. Chen, Y.Y.; Cooper, P.; Fulton, C.J.; Fox, R.J. Quantifying epifaunal secondary production within tropical macroalgal meadows: Seasonality and sensitivity to canopy structure. Limnol. Oceanogr. 2021, 66, 4267–4284. [Google Scholar] [CrossRef]
  61. Belmaker, J.; Polak, O.; Shashar, N.; Ziv, Y. Geographic divergence in the relationship between Paragobiodon echinocephalus and its obligate coral host. J. Fish Biol. 2007, 71, 1555–1561. [Google Scholar] [CrossRef]
  62. O’Connor, N. The effects of habitat complexity on the macroinvertebrates colonising wood substrates in a lowland stream. Oecologia 1991, 85, 504–512. [Google Scholar] [CrossRef]
  63. Loke, L.H.L.; Todd, P.A. Structural complexity and component type increase intertidal biodiversity independently of area. Ecology 2016, 97, 383–393. [Google Scholar] [CrossRef]
  64. Yost, D.M.; Wang, L.H.; Fan, T.Y.; Chen, C.S.; Lee, R.W.; Sogin, E.; Gates, R.D. Diversity in skeletal architecture influences biological heterogeneity and Symbiodinium habitat in corals. Zoology 2013, 116, 262–269. [Google Scholar] [CrossRef]
  65. Seben, K.P.; Deriemer, K. Diel cycles of expansion and contraction in coral reef anthozoans. Mar. Biol. 1977, 256, 247–256. [Google Scholar] [CrossRef]
  66. Heidelberg, K.B.; Sebens, K.P.; Purcell, J.E. Composition and sources of near reef zooplankton on a Jamaican forereef along with implications for coral feeding. Coral Reefs 2004, 23, 263–276. [Google Scholar] [CrossRef]
  67. Yahel, R.; Yahel, G.; Genin, A. Near- bottom depletion of zooplankton over coral reefs: I: Diurnal dynamics and size distribution. Coral Reefs 2005, 24, 75–85. [Google Scholar] [CrossRef]
  68. Ory, N.C.; Dudgeon, D.; Duprey, N.; Thiel, M. Effects of predation on diel activity and habitat use of the coral-reef shrimp Cinetorhynchus hendersoni (Rhynchocinetidae). Coral Reefs 2014, 33, 639–650. [Google Scholar] [CrossRef]
  69. Hinojosa, I.A.; Zapata-Hernández, G.; Fowles, A.E.; Gaymer, C.F.; Stuart-Smith, R.D. The awakening of invertebrates: The daily dynamics of fishes and mobile invertebrates at Rapa Nui’s multiple use marine protected area. Aquat. Conserv. Mar. Freshw. Ecosyst. 2020, 31, 290–303. [Google Scholar] [CrossRef]
  70. Azzurro, E.; Pais, A.; Consoli, P.; Andaloro, F. Evaluating day-night changes in shallow Mediterranean rocky reef fish assemblages by visual census. Mar. Biol. 2007, 151, 2245–2253. [Google Scholar] [CrossRef]
  71. Patton, W.K. Distribution and ecology of animals associated with branching corals (Acropora spp.) from the Great Barrier Reef, Australia. Bull. Mar. Sci. 1994, 55, 193–211. [Google Scholar]
  72. Somers, M.J.; Nel, J.A.J. Dominance and population structure of freshwater crabs (Potamonautes perlatus Milne Edwards). South Afr. J. Zool. 1998, 33, 31–36. [Google Scholar] [CrossRef] [Green Version]
  73. Neil, S.J. Size assessment and cues: Studies of hermit crab contests. Behaviour 1985, 92, 22–38. [Google Scholar] [CrossRef]
  74. Edwards, D.H.; Herberholz, J. Crustacean models of aggression. In Biology of Aggression; Nelson, R.J., Ed.; Oxford University Press: New York, NY, USA, 2005; pp. 38–64. ISBN 9780199865444. [Google Scholar]
  75. Stendera, S.; Adrian, R.; Bonada, N.; Cañedo-Argüelles, M.; Hugueny, B.; Januschke, K.; Pletterbauer, F.; Hering, D. Drivers and stressors of freshwater biodiversity patterns across different ecosystems and scales: A review. Hydrobiologia 2012, 696, 1–28. [Google Scholar] [CrossRef]
  76. Floren, A. Sampling arthropods from the canopy by insecticidal knockdown. In Manual on Field Recording Techniques and Protocols for All Taxa Biodiversity Inventories; Eymann, J., Degref, J., Häuser, C., Monje, J.C., Samyn, Y., Vandenspiegel, D., Eds.; ABC Taxa: Brussels, Belgium, 2010; Volume 8, pp. 158–172. [Google Scholar]
  77. Christian, J.J. Social subordination, population density, and mammalian evolution. Science 1970, 168, 84–90. [Google Scholar] [CrossRef]
  78. Rogers, A.; Blanchard, J.L.; Newman, S.P.; Dryden, C.S.; Mumby, P.J. High refuge availability on coral reefs increases the vulnerability of reef-associated predators to overexploitation. Ecology 2018, 99, 450–463. [Google Scholar] [CrossRef] [Green Version]
  79. Holbrook, S.J.; Brooks, A.J.; Schmitt, R.J. Variation in structural attributes of patch-forming corals and in patterns of abundance of associated fishes. Mar. Freshw. Res. 2002, 53, 1045–1053. [Google Scholar] [CrossRef]
  80. Ekman, J. Exposure and time use in willow tit flocks: The cost of subordination. Anim. Behav. 1987, 35, 445–452. [Google Scholar] [CrossRef]
  81. Kulbicki, M.; Bozec, Y.; Labrosse, P.; Letourneur, Y.; Mou-Tham, G.; Wantiez, L. Diet composition of carnivorous fishes from coral reef lagoons of New Caledonia. Aquat. Living Resour. 2005, 18, 231–250. [Google Scholar] [CrossRef] [Green Version]
  82. Styring, A.R.; Bin Hussin, M.Z. Foraging ecology of woodpeckers in lowland Malaysian rain forests. J. Trop. Ecol. 2004, 20, 487–494. [Google Scholar] [CrossRef]
  83. Mansor, M.S.; Mohd Sah, S.A. Foraging patterns reveal niche separation in tropical insectivorous birds. Acta Ornithol. 2012, 47, 27–36. [Google Scholar] [CrossRef]
  84. Mittelbach, G.G. Foraging efficiency and body size: A study of optimal diet and habitat use by bluegills. Ecology 1981, 62, 1370–1386. [Google Scholar] [CrossRef]
  85. Gacia, E.; Duarte, C.M. Sediment retention by a Mediterranean Posidonia oceanica meadow: The balance between deposition and resuspension. Estuar. Coast. Shelf Sci. 2001, 52, 505–514. [Google Scholar] [CrossRef]
  86. Guizien, K.; Ghisalberti, M. Living in the canopy of the animal forest: Physical and biogeochemical aspects. In Marine Animal Forests: The Ecology of Benthic Biodiversity Hotspots; Rossi, S., Bramanti, L., Gori, A., Orejas, C., Eds.; Springer International Publishing: Berlin/Heidelberg, Germany, 2017; Volume 2, pp. 507–528. ISBN 9783319210124. [Google Scholar]
Figure 1. (a) Stylophora pistillata from Eilat’s reef at day time (3 m depth); (b) Schematic illustration of S. pistillata sagittal section for the canopy compartments. Up: the upper most parts of the canopy, that border the ‘outer-colonial’ environment. This compartment outlines the canopy’s internal volume and encloses the first Strahler order branches; Base: the coral most inner part composed by the canopy’s two highest Strahler numbers for each individual coral colony; Middle: inner branches area, a space enclosed between the branches above the base and below branches of the first Strahler order; Understory: the 3D volume exists at the edge of the coral canopy’s base and occupies the spaces between the coral’s substrate plain to the parallel first canopy branches that shade on it; (c) Trapezia digitalis small body size at the up compartment, night time; (d,e) Trapezia cymodoce and T. digitalis distribution among S. pistillata canopy compartments at night, respectively. Arrows: Red—small T. digitalis at ‘Up’ compartment; Yellow—medium T. digitalis at ‘middle’ compartment; Blue—large T. cymodoce at ‘Base’ compartment.
Figure 1. (a) Stylophora pistillata from Eilat’s reef at day time (3 m depth); (b) Schematic illustration of S. pistillata sagittal section for the canopy compartments. Up: the upper most parts of the canopy, that border the ‘outer-colonial’ environment. This compartment outlines the canopy’s internal volume and encloses the first Strahler order branches; Base: the coral most inner part composed by the canopy’s two highest Strahler numbers for each individual coral colony; Middle: inner branches area, a space enclosed between the branches above the base and below branches of the first Strahler order; Understory: the 3D volume exists at the edge of the coral canopy’s base and occupies the spaces between the coral’s substrate plain to the parallel first canopy branches that shade on it; (c) Trapezia digitalis small body size at the up compartment, night time; (d,e) Trapezia cymodoce and T. digitalis distribution among S. pistillata canopy compartments at night, respectively. Arrows: Red—small T. digitalis at ‘Up’ compartment; Yellow—medium T. digitalis at ‘middle’ compartment; Blue—large T. cymodoce at ‘Base’ compartment.
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Figure 2. A pictograph presentation for lab experiments (1–5) design on the canopy compartmental usage by Trapezia crabs, managed by two basic scenarios: with the ‘presence’ or ‘absence’ of large pairs of Trapezia cymodoce.
Figure 2. A pictograph presentation for lab experiments (1–5) design on the canopy compartmental usage by Trapezia crabs, managed by two basic scenarios: with the ‘presence’ or ‘absence’ of large pairs of Trapezia cymodoce.
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Figure 3. Trapezia’s different body sizes (small, medium, large) diel distributions among Stylophora pistillata (n = 193) canopy compartments recorded over two years under in situ surveys (2020–2021). Trapezia cymodoce (a) day and (b) night frequencies (%); and Trapezia digitalis (c) day and (d) night frequencies (%). Total observations by body size (L= large, M= medium, S= small) are marked for each plot. Frequencies were calculated according to the total abundance of each species group size for each day time census. (Un) understory; (B) base; (M) middle; (B-Up) base, middle, and up; (M-Up) middle and up compartments.
Figure 3. Trapezia’s different body sizes (small, medium, large) diel distributions among Stylophora pistillata (n = 193) canopy compartments recorded over two years under in situ surveys (2020–2021). Trapezia cymodoce (a) day and (b) night frequencies (%); and Trapezia digitalis (c) day and (d) night frequencies (%). Total observations by body size (L= large, M= medium, S= small) are marked for each plot. Frequencies were calculated according to the total abundance of each species group size for each day time census. (Un) understory; (B) base; (M) middle; (B-Up) base, middle, and up; (M-Up) middle and up compartments.
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Figure 4. Day and night distribution patterns among Stylophora pistillata canopy compartments of different Trapezia body sizes with the presence or the absence of large Trapezia cymodoce. (a) T. cymodoce medium and small; (b) T. cymodoce medium; (c) T. cymodoce small; (d) Trapezia digitalis medium; (e) T. digitalis small. Color dots indicate significantly different groups (pairwise permutation MANOVA; Supplementary Tables S11–S30).
Figure 4. Day and night distribution patterns among Stylophora pistillata canopy compartments of different Trapezia body sizes with the presence or the absence of large Trapezia cymodoce. (a) T. cymodoce medium and small; (b) T. cymodoce medium; (c) T. cymodoce small; (d) Trapezia digitalis medium; (e) T. digitalis small. Color dots indicate significantly different groups (pairwise permutation MANOVA; Supplementary Tables S11–S30).
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Table 1. Feeding on planktonic organisms by large and medium size Trapezia cymodoce crabs —summary results for laboratory experiments. Pearson’s chi-square followed by Fisher exact pairwise tests of independence for nominal data analyses of predation and reaction behaviors (failure/success) of individuals examined on different substrates: live corals (‘live’); coral skeletons (‘dead’); and without corals (‘none’), following the introduction of live Artemia. Asterisk indicates statistical significance.
Table 1. Feeding on planktonic organisms by large and medium size Trapezia cymodoce crabs —summary results for laboratory experiments. Pearson’s chi-square followed by Fisher exact pairwise tests of independence for nominal data analyses of predation and reaction behaviors (failure/success) of individuals examined on different substrates: live corals (‘live’); coral skeletons (‘dead’); and without corals (‘none’), following the introduction of live Artemia. Asterisk indicates statistical significance.
Treatment TypeBetween
Treatments
LiveDeadNone
Type of behavior Failure/SuccessMediumLarge MediumLarge MediumLarge2p
Predation Failure21 21 162290.7<0.001 *
Success1421142100
Reaction Failure0001161063.2<0.001 *
Success16221621012
Within treatments—
between body sizes
2p2p2p
Predation 0.08>0.05 0.08>0.05 0.95>0.05
Reaction 0.95>0.050110.36<0.001 *
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Shmuel, Y.; Ziv, Y.; Rinkevich, B. Trapezia Crabs That Dwell in Distinctive Day/Night Canopy Compartments of a Marine Animal Forest, Forage on Demersal Plankton. J. Mar. Sci. Eng. 2022, 10, 1522. https://doi.org/10.3390/jmse10101522

AMA Style

Shmuel Y, Ziv Y, Rinkevich B. Trapezia Crabs That Dwell in Distinctive Day/Night Canopy Compartments of a Marine Animal Forest, Forage on Demersal Plankton. Journal of Marine Science and Engineering. 2022; 10(10):1522. https://doi.org/10.3390/jmse10101522

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Shmuel, Yaniv, Yaron Ziv, and Baruch Rinkevich. 2022. "Trapezia Crabs That Dwell in Distinctive Day/Night Canopy Compartments of a Marine Animal Forest, Forage on Demersal Plankton" Journal of Marine Science and Engineering 10, no. 10: 1522. https://doi.org/10.3390/jmse10101522

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