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Location map of Queensland, with Orpheus Island (Palm Island Group) on the central Great Barrier Reef (top). The sample site in Little Pioneer Bay is just north of the Orpheus Island Research Station (OIRS)

Location map of Queensland, with Orpheus Island (Palm Island Group) on the central Great Barrier Reef (top). The sample site in Little Pioneer Bay is just north of the Orpheus Island Research Station (OIRS)

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Coral reefs are under threat, exerted by a number of interacting effects inherent to the present climate change, including ocean acidification and global warming. Bioerosion drives reef degradation by recycling carbonate skeletal material and is an important but understudied factor in this context. Twelve different combinations of pCO(2) and temper...

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... sampling and experimental procedures were conducted at Orpheus Island Research Station (OIRS), located on Orpheus Island, central Great Barrier Reef, Australia (Fig. 1). The local community of bio- eroding sponges is diverse, comparatively well stud- ied (e.g. Schönberg 2000Schönberg , 2001, and has recently in - creased in abundance, possibly as a result of declin- ing reef health related to a heating event resulting in widespread coral death (Schönberg & Ortiz 2009). At the leeward fringing reef, C. ...
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... 2009). At the leeward fringing reef, C. orientalis was core- sampled in 1 to 3 m water depth from massive Porites sp. colonies with an air-drill and hole-saw (inner dia - meter: 30 mm), and later trimmed to 25 mm in length with an air-cutter, so that cores included sponge- penetrated material in the upper half and clean coral skeleton below (see Fig. 1D in Wisshak et al. ...
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... salinity, pH, mean and Δ total alkalinity [TA]) and computed carbonate system parameters (dissolved inorganic carbon [DIC] Tables 2, S1 & S2), no clear relationship with tem - perature could be demonstrated, also evidenced by only few and weakly significant differences found when testing temperature levels pairwise against each other (Fig. 4j, Tables 2, S1 & S2). The weaker and somewhat inconclusive temperature effect was confirmed by the multiple linear re gressions yielding a clear significance for the factor p CO 2 and a neg - ligible contribution of temperature (Table S2). At any given p CO 2 level, bioerosion rates were highest at 25°C (approx. ambient winter temperature), and slightly de ...
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... of the ammonium building up. The highest bioerosion rates were reached at the local ambient temperature of 25°C, decreasing towards colder as well as warmer tem peratures. Overall, the influence of temperature on the bioerosion capacity of C. orientalis appears to be very low to negligible despite other physiological responses caused by heat (Fig. 4, Tables 1, 2, S1 & S2), particularly with respect to ammonium, that can be interpreted as a sign of excretion and/or disintegrative processes (Wright 1995, Francis-Floyd et al. 2009). The ob served signif- icant positive correlation of ammonium with temper- ature (Table 2) likely suggests increasing heat stress, with resulting ammonium and/or ...

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... to correct A T change (Jacques & Pilson, 1980;Wisshak et al., 2013) as ammonium, nitrate and phosphate are naturally modified by the rubble inhabitants and affect A T . The mass of altered calcium carbonate (ΔM CaCO 3 , in μg) was calculated using the equation below (Zundelevich et al., 2007): ...
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... There are shared aspects in the mechanisms of bioerosion that suggest similarities in the forces that drive bioerosion and its ecological outcomes. Recent research has shown that bioerosion intensity increases in response to modern climate change and human-induced impacts, e.g., increased temperature, alkalinity, eutrophication and sea level rise (e.g., Tribollet et al., 2009;Wisshak et al., 2013;Silbiger et al., 2016;Chazottes et al., 2017;Prouty et al., 2017). ...
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... Long-term exposure of experimental denuded dead coral CaCO 3 blocks and sponge-bearing cores to decreased seawater pH in a mesocosm exhibited a significant increase in bioerosion activity (Enochs et al., 2016;Schönberg et al., 2017;Tribollet et al., 2009;Wisshak et al., 2013). Measurements of coral bioeroder activity (species abundance) were carried out along naturally occurring pH gradients in coral reefs showing an increase in activity with decreasing pH . ...
... For a detailed description of seasonal nutrient and chlorophyll dynamics in the GOE, see, for example, Stambler (2006), Lazar et al. (2008), Silverman andGildor (2008), andMeeder et al. (2012). Higher net dissolution of CaCO 3 at lower bulk water Ω arag (e.g., Figure 5a), was also found in dark incubations of a single Acropora, without macro bioeroders (Schneider et al., 2006), in dead corals containing microbial endoliths (Tribollet et al., 2009(Tribollet et al., , 2019 and in the bioerosion activity of Clionaid sponge (Wisshak et al., 2013), which is an important bioeroder in coral reefs (Glynn & Manzello, 2015). Crook et al. (2013) showed that under naturally low pH conditions (Ω arag < 2), there is an increase of boring organism activity in Porites skeletons. ...
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... Numerous laboratory studies have also found elevated sponge bioerosion rates in response to OA conditions (Duckworth & Peterson, 2013;Enochs et al., 2015;Fang et al., 2013;Wisshak et al., 2013Wisshak et al., , 2014. While OA-stimulated bioerosion has been measured for both zooxanthellate and azooxanthellate species, the response is thought to be more pronounced among photosynthetic sponges due to an increase in the photosynthetic efficiency of sponge symbionts associated with OA (Achlatis et al., 2017). ...
... Significant differences across treatment conditions are denoted by *. Figure 2a,b). This response supports prior sponge studies investigating the influence of OA on sponge bioerosion under static conditions (Enochs et al., 2015;Wisshak et al., 2013Wisshak et al., , 2014, further underlining the positive impact of OA on sponge bioeroding capacity. The majority of these studies, however, measured biologically mediated chemical dissolution rather than buoyant weight derived bioerosion, and direct comparisons should be cautiously applied. ...
... Moreso, the CT variable treatment reached the most acidified conditions for a comparably shorter period of time each day (<8.0 pH for 6 hrs, CT variable; 7.80 pH for 24 h, OA static). Based on these discrepancies, results from prior literature would lead us to expect higher bioerosion rates for sponges exposed to the static OA treatment due to the stimulating effect of reduced pH conditions (Enochs et al., 2015;Wisshak et al., 2013Wisshak et al., , 2014. In our present study, however, the similar rates between the two treatments suggest that diel pH variability may modulate the sponge OA response in a way that requires an updated interpretation of the previously described relationship. ...
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... Bioerosion is thought to contribute more to reef degradation globally than physical erosion or passive chemical dissolution (Schönberg et al. 2017) and, thus, plays an important role in carbonate (re)cycling. In warm-water coral reefs, chemical bioerosion by microphytes and excavating sponges was accelerated significantly under ocean acidification (Tribollet et al. 2006(Tribollet et al. , 2009Wisshak et al. 2012Wisshak et al. , 2013, highlighting the need to consider this process in assessments of ocean change impacts (see Schönberg et al. 2017 for a review). Bioerosion has been more extensively studied in shallow-water settings, but Beuck and Freiwald (2005) characterized bioerosion patterns of a L. pertusa coral mound in the northern Porcupine Seabight in the North Atlantic. ...
... To date, there is no experimental data on the influence of pCO 2 on bioerosion rates of microfungi, but bioerosion by phototrophic microborers in tropical coral reefs (chlorophytes and cyanobacteria) significantly increased under simulated ocean acidification (e.g., Tribollet et al. 2006Tribollet et al. , 2009 and as bioeroding microfungi apply a chemical mode of bioerosion as well, we suspect that fungal microbioerosion is similarly stimulated by elevated levels of pCO 2 as supported by our results. As far as bioeroding sponges are concerned, there is solid experimental evidence for several tropical to cold-temperate species that indicate that they accelerate their bioerosion activity (chemical biocorrosion and mechanical extraction of sediment chips in this case) at elevated pCO 2 levels (Wisshak et al. 2012(Wisshak et al. , 2013Stubler et al. 2015). This suggests that ecophysiological responses apply across species and latitudes (Wisshak et al. 2014). ...
... Since related species of the same sponge genera are abundant in cold-water coral reefs, they are likely affected in the same way. Experiments that have included temperature in separate and combined treatments (Wisshak et al. 2013;Stubler et al. 2015) suggest that temperature has comparatively little effect on the sponge's bioerosion rates until critically high temperature stress levels lead to adverse effects, which is supported by our results. ...
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... Sponges have widely been recognised as winners on coral reefs because of changing environmental conditions (see [6,7]) and particularly in response to the impacts of climate change [8]. Sponges are generally very tolerant to the impacts of ocean acidification [9,10] and show a high degree of tolerance to temperatures expected under the more moderate climate change scenarios [11,12]. For example, Bennett et al. [11] tested the thermal tolerance of four abundant Great Barrier Reef species and found all species were generally unaffected by conditions predicted under RCP6.0, ...
Article
Despite the global focus on the occurrence of regime shifts on shallow-water tropical coral reefs over the last two decades, most of this research continues to focus on changes to algal-dominated states. Here, we review recent reports (in approximately the last decade) of regime shifts to states dominated by animal groups other than zooxanthellate Scleractinian corals. We found that while there have been new reports of regime shifts to reefs dominated by Ascidacea, Porifera, Octocorallia, Zoantharia, Actiniaria and azooxanthellate Scleractinian corals, some of these changes occurred many decades ago, but have only just been reported in the literature. In most cases, these reports are over small to medium spatial scales (<4 × 104 m2 and 4 × 104 to 2 × 106 m2, respectively). Importantly, from the few studies where we were able to collect information on the persistence of the regime shifts, we determined that these non-scleractinian states are generally unstable, with further changes since the original regime shift. However, these changes were not generally back to coral dominance. While there has been some research to understand how sponge- and octocoral-dominated systems may function, there is still limited information on what ecosystem services have been disrupted or lost as a result of these shifts. Given that many coral reefs across the world are on the edge of tipping points due to increasing anthropogenic stress, we urgently need to understand the consequences of non-algal coral reef regime shifts.
... Many experiments ranging from three days to twenty weeks suggest acidification may lead to increased sponge bioerosion rates [6,[75][76][77], consequently leading to decreased net calcification of living corals [78] and increased calcium carbonate (CaCO 3 ) dissolution of dead corals [76,[78][79][80]. Here, we also show that a non-photosynthetic encrusting/excavating sponge adjacent to S. radians does not impact net calcification of the coral. ...
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Coral reef community composition, function, and resilience have been altered by natural and anthropogenic stressors. Future anthropogenic ocean and coastal acidification (together termed “acidification”) may exacerbate this reef degradation. Accurately predicting reef resilience requires an understanding of not only direct impacts of acidification on marine organisms but also indirect effects on species interactions that influence community composition and reef ecosystem functions. In this 28-day experiment, we assessed the effect of acidification on coral–algal, coral–sponge, and algal–sponge interactions. We quantified growth of corals (Siderastrea radians), fleshy macroalgae (Dictyota spp.), and sponges (Pione lampa) that were exposed to local summer ambient (603 μatm) or elevated (1105 μatm) pCO2 seawater. These species are common to hard-bottom communities, including shallow reefs, in the Florida Keys. Each individual was maintained in isolation or paired with another organism. Coral growth (net calcification) was similar across seawater pCO2 and interaction treatments. Fleshy macroalgae had increased biomass when paired with a sponge but lost biomass when growing in isolation or paired with coral. Sponges grew more volumetrically in the elevated seawater pCO2 treatment (i.e., under acidification conditions). Although these results are limited in temporal and spatial scales due to the experimental design, they do lend support to the hypothesis that acidification may facilitate a shift towards increased sponge and macroalgae abundance by directly benefiting sponge growth which in turn may provide more dissolved inorganic nitrogen to macroalgae in the Florida Keys.
... Without protective coral tissue, dead framework is directly exposed to the corrosive seawater and becomes increasingly unstable (Hennige et al. 2015(Hennige et al. , 2020. Further, acidification facilitates bioerosion by sponges, accelerating dead framework degradation (Wisshak et al. 2012(Wisshak et al. , 2013(Wisshak et al. , 2014. If reef erosion is no longer balanced by coral growth, the reef structure becomes flatter and eventually disappears (Perry et al. 2013, Büscher et al. 2019, Perry and Alvarez-Filip 2019, Hennige et al. 2020. ...