Seasonal to decadal scale influence of environmental drivers on Ba/Ca and Y/Ca in coral aragonite from the southern Great Barrier Reef
Graphical abstract
Introduction
Coral reefs are integral parts of marine ecosystems and support immense biodiversity. Nearshore reefs located close to river mouths have been subjected to high rates of disturbance in many parts of the world. In addition to the variety of changing global climate parameters (e.g., ocean acidification, tropical cyclones, and CO2 induced rise in sea surface temperature (SST)) that affect offshore reefs, inshore reef systems face significant threats from more localized anthropogenic inputs (e.g., pollution from increased terrestrial sediment and nutrient loads, dredging and dumping, agri-chemicals and industrial toxins and metals) (Brodie, 2014; Brodie et al., 2013; De'ath et al., 2012; Hughes, 1994; Hughes et al., 2003; Pandolfi et al., 2003). Hence, although inshore reef communities tend to be adapted to higher turbidity environments (Larcombe et al., 2001; Perry and Smithers, 2010; Perry et al., 2012), they are increasingly at risk from anthropogenic pressures. In order to protect such reefs and potentially predict their future responses to changing water conditions, it is critical to develop specific environmentally linked proxies to extend our understanding of water quality before instrumental records (De'ath and Fabricius, 2010; De'ath et al., 2012; Greer et al., 2009; Wooldridge and Done, 2009).
Annually banded coral skeletons can record a variety of environmental data in marine settings and have proven to be useful archives of various proxies for high-resolution temporal reconstruction of past environment and climate. The great value of coral archives resides in their wide geographic distribution, long temporal span (up to a thousand years) and their resistance to erosion and breakage (Fleitmann et al., 2007; Veron, 2000). For example, elemental proxies in coral skeletons have been used commonly to reconstruct SST (Beck et al., 1992; Duprey et al., 2012; Felis et al., 2009; Gagan et al., 1998; Jimenez et al., 2018; Kawakubo et al., 2017; McCulloch et al., 1994; Min et al., 1995; Mitsuguchi et al., 1996; Sadler et al., 2016; Wang et al., 2018), salinity (Shen and Dunbar, 1995), terrestrial runoff (Alibert et al., 2003; Brenner et al., 2017; Jiang et al., 2017; Jupiter et al., 2008; McCulloch et al., 2003; Prouty et al., 2010; Sinclair, 2005), precipitation (Grove et al., 2013; Horta-Puga and Carriquiry, 2012; Moyer et al., 2012) and upwelling (Lea et al., 1989; Montaggioni et al., 2006; Reuer et al., 2003; Watanabe et al., 2017). Spatio-temporal variations in coral trace element proxies have been used increasingly to monitor coastal marine water quality affected by anthropogenic activities (e.g., land use change, dredging and dumping, sewage discharge, mining and oil pollution) (Fallon et al., 2002; Fleitmann et al., 2007; Nguyen et al., 2013). A current review concluded that among numerous elemental ratios, Ba/Ca and Y/Ca proxies have been shown to have close links to sediment loads delivered by river systems to inshore marine environments (Saha et al., 2016). However, some studies reported anomalous peaks of these proxies that are decoupled from terrestrial runoff and other known events, suggesting that these proxies are not solely controlled by runoff. Other factors (e.g., upwelling, regional hydrodynamics, biological activities, sediment resuspension and groundwater seeps) also can have significant influence on their temporal records (Alibert et al., 2003; Lea et al., 1989; Lewis et al., 2012; Montaggioni et al., 2006; Sinclair, 2005). Hence, the reliability of these elemental ratios as runoff proxies should be validated before interpreting their extended records in a particular region.
Corals can preserve a record of changes in water quality because many trace elements are incorporated into the coral's aragonite skeleton in close proportion to their abundance in ambient seawater (LaVigne et al., 2016; Shen et al., 1987). Thus their concentrations can reflect seasonal, annual, and decadal variability in water quality where the corals grew. The mechanisms for incorporation of trace elements into coral skeleton from ambient seawater have been widely studied (Allison, 1996; Allison and Finch, 2004; Amiel et al., 1973; Barnard et al., 1974; Brown et al., 1991; Mitterer, 1978; Shen et al., 1991; St John, 1974), but they are not fully understood owing in part to the effects of various biological factors (so-called “vital effects”) and subsequent, but early, diagenetic alteration. Trace elements in coral skeleton can substitute for Ca in the crystal lattice, be trapped in pore spaces, adsorbed on exposed skeletal surfaces, or form complexes with organic matter (for details, Saha et al., 2016). Hence, interpretation of skeletal elemental proxies can be complicated, but there is strong empirical support for their use in environmental archives (Beck et al., 1992; Gagan et al., 2000; Gagan et al., 1998; Lewis et al., 2012; McCulloch et al., 2003).
Records of Ba/Ca and Y/Ca proxies in high-latitude inshore coral reefs of the southern GBR are basically absent from the literature (Fig. 1a, b), but such data are required in both space and time in order to better develop their links with specific environmental drivers. In this study, we present Ba/Ca and Y/Ca proxies in core recovered from a Porites coral colony with 53 years of recorded growth (from December 1957 to July 2010) from near-shore Great Keppel Island, southern GBR. The Keppel Islands are located north of the mouth of the Fitzroy River, which drains a catchment that has been extensively modified as a result of land clearing for grazing in both coastal and inland regions as well as urban development since European colonisation in the mid-19th century. Increased sediment loads from the catchment have decreased local water quality causing smothering of inshore corals and seagrass communities (GBRMPA, 2013). Here, the integrity of high-resolution Ba/Ca and Y/Ca proxies were tested against environmental drivers (Fitzroy River discharge and rainfall) over seasonal, annual and decadal time scales. Our results should improve understanding of these proxies in this particular region, and thus allow better interpretation of the impact of key environmental drivers in modulating the time series geochemical data. That improved understanding should have application for interpreting local records in older corals, prior to instrumental measurements, and potentially the interpretation of data from other regions.
Section snippets
Study area
The Keppel Islands, located ~18 km from the mainland, include 16 islands of Keppel Bay and represent one of the largest inshore reef systems of the southern GBR (Fig. 1). These continental islands are located in a macro-tidal setting with a maximum tidal range of ~5 m and are surrounded by fringing reefs with relatively high coral cover dominated by branching Acropora sp. (Leonard et al., 2016). The Porites core sample was recovered from the northern side of the Great Keppel Island (23.15° S,
Establishing chronology using SST proxy in coral
The commonly used SST proxy, coral skeleton Sr/Ca (Beck et al., 1992; Bolton et al., 2014; Gagan et al., 1998), showed clear seasonal cyclicity in this study (Fig. 2). Intra-colony variability was assessed statistically by performing independent sample t-test between overlapping elemental ratios of different tracks (SI Table S1). No statistically significant (p > 0.05) differences between the mean values of overlapping tracks were observed, indicating precise splicing of the tracks. Thereafter,
Discussion
Trace metals in near-shore coral skeletons can record historical environmental changes in associated catchments (see review by Saha et al., 2016). This study provided a 53-year record of terrestrial runoff based on coral geochemical proxies for the Keppel Reefs, GBR. However, as with similar studies in different parts of the world (Saha et al., 2016), these data also revealed instances of anomalous behavior that were uncorrelated with river discharge. These anomalous deviations of coralline
Conclusions
The need for understanding long-term, especially pre-instrumental responses of corals and coral reefs to environmental changes and perturbations is increasingly acknowledged (Hughes et al., 2010; Pandolfi and Kiessling, 2014; Roche et al., 2011). Geochemical proxies (Ba/Ca and Y/Ca) in coral skeleton from Great Keppel in southern GBR show that environmental influences are recorded on seasonal to decadal time scales. Overall, Ba/Ca and Y/Ca showed seasonal fluctuations related to summer floods,
Acknowledgements
The authors would like to thank Sander Scheffers, Catalina Reyes, and Peter Williams for their assistance during fieldwork. Collection of coral cores were performed under the GBRMPA permit number G10/33402.1. We also thank Michael Gagan, Heather Scott-Gagan, Malcolm McCulloch and Juan Pablo D'Olivo for their support when the cores were sectioned. We also thank three anonymous reviewers of the manuscript for their insightful comments. This work was partially funded by Tropical Ecosystem Project
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