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Summary of fish morphometrics, fates, maximum distance moved from the aggregation and home range areas 

Summary of fish morphometrics, fates, maximum distance moved from the aggregation and home range areas 

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The aim of the study was to estimate home range areas and distance of movement away from a squaretail coralgrouper (Plectropomus areolatus) spawning aggregation site located within a small-scale 1.5km2 Marine Protected Area (MPA) in Pohnpei, Micronesia. Fifteen P. areolatus were acoustically tagged and re-located within a ca. 50km2 search area over...

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The coral trout Plectropomus leopardus (Serranidae)forms the major component of the commercial andrecreational line fishery on the Great Barrier Reef(GBR) in Australia (Kailola et al. 1993). Lately, con-cernshavebeenexpressedregardingrapidincreases infishing effort leading to localized depletion of sometarget species (Mapstone et al. 1996), and additi...

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... covering home range habitats, migratory corridors and spawning aggregation sites) of sites to ensure maximum fishery benefits (Krueck et al., 2018). In these cases, the recovery of spawning stock biomass could potentially be promoted for commercially valuable climate-resilient species such as the squaretail coral grouper (Plectropomus areolatus) (Hutchinson and Rhodes, 2010) and the mangrove red snapper (Lutjanus argentimaculatus) (Honda et al., 2016;Honda et al., 2017) within the boundaries of the MPA itself (McClure et al., 2020;. Catches in the wider area could further benefit due to the potential positive impacts of spill-over, a process by which biomass is exported to adjacent fishing grounds (Di Lorenzo et al., 2016). ...
... The spawning aggregates are temporary and disperse after the spawning. However, the home range of groupers is small, and many fish stay close to their aggregation sites after the spawning [22,19] . The aggregation sites are many, and spread over the entire coral reef (the fringing reef (and patch and barrier reefs) extends along the entire coast at a width of more than 1/2 to 1 km), a very vast area. ...
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... Sites with fewer than 10 individuals were excluded to account for potential biases introduced by small sample sizes. To determine if there was significant variation in individual genetic diversity (H O ) between sites, we conducted a one-way ANOVA in rstatix v 0.7.2 (Kassambara 2023) followed by post-hoc Tukeys tests in multcomp v 1.4-25 (Hothorn et al. 2016). Data were assessed for normality and homogeneity of variance and a single P. laevis site (L21) was omitted due to violating assumptions of normality, likely due to the small sample size (n = 14) at this site. ...
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... In subsequent months, male P. areolatus depart along with females following spawning around the full moon. All three species have been shown or observed utilizing common reproductive migratory corridors to reach and depart the FSA site and at last some individuals travel up to 25 km from the FSA to reach home reefs immediately after spawning [62][63][64]. As previously indicated, the species-specific duration of FSA varies, with P. areolatus and E. fuscoguttatus maintaining aggregations over c. 2 weeks during each reproductive month, while the E. polyphekadion FSA currently extends over 5 days or less [10]. ...
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... To arrive at an aggregation site, fish often use predictable migration routes, such as shelf edges, dropoffs or channels. For example, some resident and transient aggregating species have known migration pathways between spawning and home/feeding sites (Colin 1996, Mazeroll & Montgomery 1998, Whaylen et al. 2004, Hutchinson & Rhodes 2010. Interestingly, there were very few detections on outer aggregation site receivers A and E, indicating fish were not traveling at shallow depths along the wall. ...
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... Both species typically had high individual core use (.50%) and extent (.80%) vKUD overlap between months. This aligns with the reportedly high site fidelity of P. leopardus (Zeller 1997;Bunt and Kingsford 2014), P. laevis (Matley et al., in press a), P. areolatus (Hutchinson and Rhodes 2010) and other grouper species (e.g. Frias-Torres 2006;Pastor et al. 2009;Waldie et al. 2016). ...
... Contrary to several previous studies (e.g. Zeller 1997;Hutchinson and Rhodes 2010;Matley et al. 2015), there was evidence that P. leopardus behaviour patterns changed with size. The mean depth increased ,2-4 m between the smallest (,400 mm FL) and largest (,625 mm FL) individuals. ...
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Prey selection can influence interactions among species, the composition and abundance of prey, and ultimately the movement of energy within the ecosystem. Different species of the exploited coral trout (Plectropomus spp.) often co-occur in reef environments, but their foraging behaviour and ecological niches are largely unknown. To explore niche overlap and resource use of sympatric adult coral trout, stable isotopes (δ13C and δ15N) were quantified for three tissues (muscle, red blood cells, plasma) collected between August 2013 and February 2014 from P. leopardus (n = 117) and P. laevis (n = 36) at four reefs in eastern Australia. Bayesian standard ellipses were used to show that prey selection of P. leopardus varied considerably from P. laevis, particularly the blue-spot colour phase. Size of adult individuals had little influence on δ13C and δ15N values for P. leopardus and both footballer and blue-spot colour phases of P. laevis. Spatio-temporal comparisons of P. leopardus trophic positions, made by adjusting baseline algae and planktonic δ15N at each reef and sampling period, demonstrated that trophic positions varied in time and space, and warrants further investigations. This study highlights that sympatric species of coral trout have distinct ecological roles and will likely react differently to environmental disturbances and/or changes in habitat/prey composition.
... Both species typically had high individual core use (.50%) and extent (.80%) vKUD overlap between months. This aligns with the reportedly high site fidelity of P. leopardus (Zeller 1997;Bunt and Kingsford 2014), P. laevis (Matley et al., in press a), P. areolatus (Hutchinson and Rhodes 2010) and other grouper species (e.g. Frias-Torres 2006;Pastor et al. 2009;Waldie et al. 2016). ...
... Contrary to several previous studies (e.g. Zeller 1997;Hutchinson and Rhodes 2010;Matley et al. 2015), there was evidence that P. leopardus behaviour patterns changed with size. The mean depth increased ,2-4 m between the smallest (,400 mm FL) and largest (,625 mm FL) individuals. ...
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Investigating niche overlap in exploited fish species can reveal behavioural information necessary to improve conservation and fisheries management at a species level. The present study examined spatial and dietary overlap between two co-occurring reef fish, namely Plectropomus leopardus and P. maculatus, at an inshore reef in the Great Barrier Reef Marine Park using acoustic telemetry and stable isotopes. Movements of tagged fish within an acoustic array of 19 receivers deployed along a narrow reef portion of Orpheus Island were monitored for up to 3 years. Although space use was similar between species, spatial overlap was rare and P. maculatus (n = 30) was consistently deeper than P. leopardus (n = 32). Dietary overlap between species was high based on overlapping δ15N and δ13C isotopic niches in muscle tissue (n = 20). The complementary stable isotope and acoustic telemetry data revealed these species had similar isotopic niches but distinct space use patterns, which may be a product of com
... In contrast, newly settled P. maculatus have a strong preference for colonies of corymbose Acropora located over sand and/or rubble (Wen et al. 2013a). As juvenile Plectropomus grow, they relocate to more complex habitats, such that fish [10 cm TL are most often found in areas with high coral cover (Connoll and Kingsford 1998;Hutchinson and Rhodes 2010). Plectropomus' strong association with live coral suggest that corals provide shelter, harbour prey, and/or aid foraging tactics. ...
... In all cases, there is a pronounced lunar influence on the timing of aggregation formation, but this varies between species and locations (Table 3). Plectropomus areolatus, for example, spawns around full moon in Micronesia (Hutchinson and Rhodes 2010;Rhodes et al. 2014) and around new moon in Melanesia (Hamilton et al. 2011(Hamilton et al. , 2012. ...
... Plectropomus are cryptic as juveniles but relatively conspicuous as adults, since they are less sedentary than other groupers. Ultrasonic telemetry data indicate that adult fish occupy distinct home ranges in the order of 1-12 ha for P. areolatus and 1-50 ha for P. leopardus, with no apparent relationship between body size or gender and home range area (Zeller 1997;Hutchinson and Rhodes 2010;Matley et al. 2015). Individuals are diurnally active, regularly using a small number of locations within their home-ranges, and often return to the same location each night (Zeller 1997;Bunt and Kingsford 2014). ...
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Coral grouper (genus Plectropomus), or coral trout, are members of the grouper family (Epinephelidae) and are one of the largest and most conspicuous predatory fishes on Indo-Pacific coral reefs. They are highly-prized food fishes that are targeted by subsistence, artisanal, commercial and recreational fisheries throughout their geographic range. Plectropomus have broadly similar diets and habitat requirements to other tropical groupers, but typically have faster growth and higher natural mortality rates. Although these characteristics are expected to increase population turnover and reduce innate vulnerability to environmental and anthropogenic impacts relative to other groupers, many Plectropomus populations are in decline due to the combined effects of overfishing and habitat degradation. In many locations, stock depletion from uncontrolled fishing, particularly at spawning aggregation sites, has resulted in local fishery collapse. Therefore, improved management of wild populations is urgently required to ensure conservation and sustainable fisheries of Plectropomus. Where possible, a combination of no-take marine reserves, market-based management approaches, and allocation or resurrection of property rights systems are recommended to complement conventional fishery management actions that limit catch and effort. Additional investment in aquaculture propagation is also needed to reduce fishing pressure on wild stocks and support management initiatives. This global synthesis of information pertaining to the biology, fisheries and management of Plectropomus will assist in guiding future management actions that are attempting to address a range of stressors including fishing, reef habitat degradation, and the escalating effects of climate change.