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Front. Mar. Sci., 12 April 2019
Sec. Deep-Sea Environments and Ecology
Volume 6 - 2019 |

First ROV Exploration of the Perth Canyon: Canyon Setting, Faunal Observations, and Anthropogenic Impacts

  • 1School of Earth Sciences and UWA Oceans Institute, The University of Western Australia, Perth, WA, Australia
  • 2Oceans Graduate School and UWA Oceans Institute, The University of Western Australia, Perth, WA, Australia
  • 3Istituto di Scienze Marine, Consiglio Nazionale delle Ricerche, Venice, Italy
  • 4Laboratoire des Sciences du Climat et de l’Environnement, Gif-sur-Yvette, France
  • 5Stazione Zoologica Anton Dohrn, Naples, Italy
  • 6Biology Department, Woods Hole Oceanographic Institution, Woods Hole, MA, United States
  • 7Marine and Atmospheric Research, Commonwealth Scientific and Industrial Research Organization, Hobart, TAS, Australia
  • 8Western Australian Museum, Welshpool, WA, Australia
  • 9Australian Nuclear Science and Technology Organisation, Kirrawee, NSW, Australia
  • 10ARC Centre of Excellence for Coral Reef Studies, The University of Western Australia, Perth, WA, Australia

This study represents the first ROV-based exploration of the Perth Canyon, a prominent submarine valley system in the southeast Indian Ocean offshore Fremantle (Perth), Western Australia. This multi-disciplinary study characterizes the canyon topography, hydrography, anthropogenic impacts, and provides a general overview of the fauna and habitats encountered during the cruise. ROV surveys and sample collections, with a specific focus on deep-sea corals, were conducted at six sites extending from the head to the mouth of the canyon. Multi-beam maps of the canyon topography show near vertical cliff walls, scarps, and broad terraces. Biostratigraphic analyses of the canyon lithologies indicate Late Paleocene to Late Oligocene depositional ages within upper bathyal depths (200–700 m). The video footage has revealed a quiescent ‘fossil canyon’ system with sporadic, localized concentrations of mega- and macro-benthos (∼680–1,800 m), which include corals, sponges, molluscs, echinoderms, crustaceans, brachiopods, and worms, as well as plankton and nekton (fish species). Solitary (Desmophyllum dianthus, Caryophyllia sp., Vaughanella sp., and Polymyces sp.) and colonial (Solenosmilia variabilis) scleractinians were sporadically distributed along the walls and under overhangs within the canyon valleys and along its rim. Gorgonian, bamboo, and proteinaceous corals were present, with live Corallium often hosting a diverse community of organisms. Extensive coral graveyards, discovered at two disparate sites between ∼690–720 m and 1,560–1,790 m, comprise colonial (S. variabilis) and solitary (D. dianthus) scleractinians that flourished during the last ice age (∼18 ka to 33 ka BP). ROV sampling (674–1,815 m) spanned intermediate (Antarctic Intermediate Water) and deep waters (Upper Circumpolar Deep Water) with temperatures from ∼2.5 to 6°C. Seawater CTD profiles of these waters show consistent physical and chemical conditions at equivalent depths between dive sites. Their carbonate chemistry indicate supersaturation (Ωcalcite ∼ 1.3–2.2) with respect to calcite, but mild saturation to undersaturation (Ωaragonite ∼ 0.8–1.4) of aragonite; notably some scleractinians were found living below the aragonite saturation horizon (∼1,000 m). Seawater δ13C and nuclear bomb produced Δ14C compositions decrease in the upper canyon waters by up to ∼0.8‰ (<800 m) and 95‰ (<500 m), respectively, relative to measurements taken nearby in 1978, reflecting the ingress of anthropogenic carbon into upper intermediate waters.


Submarine canyons are recognized as a key feature of continental-shelf margins and, depending on their mode of formation, geomorphology, and location on the shelf, can serve various important functions (Würtz, 2012; Huang et al., 2014; Fernandez-Arcaya et al., 2017). These canyon systems are of primary ecological importance in terms of biodiversity hotspots and ecosystem dynamics, so are increasingly the focus of interdisciplinary research (De Leo et al., 2010; McLain and Barry, 2010; de Vos et al., 2014; Huvenne and Davies, 2014; Quattrini et al., 2015; Bargain et al., 2018). Among the most prominent inhabitants of deep submarine canyons are cold-water corals, which can play important habitat-forming roles, however, the vast majority of information is limited to the Atlantic and Mediterranean regions (Morris et al., 2013; Angeletti et al., 2014; Brooke and Ross, 2014; Cordes et al., 2017; Fabri et al., 2017; Taviani et al., 2017; van den Beld et al., 2017).

As shown by visual surveys, submarine canyons are not immune to direct anthropogenic threats, such as fishery practices, dumping of waste, littering, shipping activities, and oil and gas operations (Orejas et al., 2009; Fabri et al., 2014; Daly et al., 2018; Taviani et al., 2019). Active canyon systems can be flushed by cascading shelf waters (Canals et al., 2006; Trincardi et al., 2007) that act as conduits for transporting terrestrial and coastal-sourced pollutants into deep waters, however, their impacts on deep-sea ecosystems are still to be fully assessed (Koenig et al., 2013). Such observations indicate that deep-sea canyon habitats require proper management and governance to ensure their health, integrity, and hence environmental importance (Company et al., 2012; Davies et al., 2014; Fernandez-Arcaya et al., 2017; Lo Iacono et al., 2018).

While some canyon systems represent the sub-sea extension of large river systems, transporting terrestrial sediments across the shelf to the deep-sea ocean basins, many submarine canyon systems have no direct landward connection so are largely isolated from terrestrial inputs. This latter class of canyons may be confined either to the more steeply dipping edge of the shelf-slope, or occasionally deeply incise the main shelf margin as in the case of the Perth Canyon (Harris and Whiteway, 2011; Huang et al., 2014). Previous studies of the Perth Canyon system have been confined to very limited dredge sampling and bathymetry (Marshall et al., 1989; Heap et al., 2008) or opportunistic ship-based characterization of its water masses (Woo and Pattiaratchi, 2008; Rennie S.J. et al., 2009; Rennie S. et al., 2009). Located in an oligotrophic environment with low primary production, the canyon is mainly influenced by the Leeuwin Undercurrent (LU) where subsurface upwelling occurs which is suspected to effect productivity and biodiversity in the upper reaches of the canyon (Woo and Pattiaratchi, 2008; Rennie S. et al., 2009). The canyon is known as a seasonal feeding-ground for migratory mega-fauna such as sharks and whales (Rennie S. et al., 2009), especially at the head of the canyon. However, virtually nothing was known about the deep-water invertebrate inhabitants of this canyon prior to this study.

Although relatively isolated, the unique deep-sea communities inhabiting submarine canyons are nevertheless vulnerable to anthropogenic warming and ocean acidification, which have been registered within shallow marine environments worldwide (e.g., Sabine et al., 2004; Orr et al., 2005). With rising levels of anthropogenic CO2, the carbonate saturation horizon in the oceans is expected to rise by ∼100 m to ∼300 m by the year 2100 (Orr et al., 2005). This is likely to have severe consequences (Roberts et al., 2006), especially on deep-sea biota that precipitate carbonate skeletons (e.g., corals, molluscs, echinoderms) which are subject to the combined effects of reduced calcification as carbonate saturation state decreases, and increased dissolution of their skeletons as ambient canyon waters become more corrosive (Thresher et al., 2011; McCulloch et al., 2012). Being near the south-eastern Indian Ocean margin (115°E, 32°S), a largely unstudied region sourced by Southern Ocean waters, the Perth Canyon represents a prime location for studying changes in the ocean-climate system and their impacts on deep-sea ecosystems.

This first ROV-based multi-disciplinary study of the Perth Canyon investigates the main geo-biological, oceanographic, and chemical characteristics of this unique, previously unexplored, inactive canyon system. Our key goals were to: (1) strategically sample and document deep-sea corals, and (2) characterize habitat conditions and anthropogenic impacts within the canyon. Here, we characterize the canyon, its environments, and provide an overview of the faunas encountered. The environmental data is also central to constraining geochemical proxy analyses of the coral skeletons now underway, which will be used to reconstruct long-term environmental changes in the canyon. This study therefore establishes a much-needed baseline for future work focused on understanding the functioning of this canyon system, and the vulnerability of its inhabitants to the impacts of climate change and ocean acidification.

Geological Setting

The canyon is surprisingly poorly understood despite being located only ∼27 nautical miles (50 km) offshore Perth, the main population center and capital city of Western Australia. Its formation is somewhat enigmatic, being subject to controversy due to the lack of connectivity to the nearby Swan River and the now passive nature of the western Australian continental margin.

The canyon resides within the Vlaming sub-basin, a pull-apart basin (Marshall et al., 1989) that formed during the separation of greater India from the western margin of the Australian continent, which concluded by the Early Cretaceous (∼134–137 Ma). Structural analysis by Marshall et al. (1989) indicates that the canyon is delineated by these pre-existing rift related fault structures, with both the NE–SW and SE–NW trending canyon tributaries apparently aligned with several transfer faults, and the head of the canyon defined by a small WNW trending graben (Marshall et al., 1989).

It has also been suggested that the canyon’s incision into the continental slope is related to sub-aerial palaeo-drainage patterns carved by the adjacent Swan River when it formed part of a larger river system (von der Borch, 1968; Playford et al., 1976; Seddon, 2004). Although the canyon lies adjacent to the mouth of the Swan River, there is however no Cenozoic geomorphological evidence for any direct connectivity between the Swan River and the head of the submarine canyon. This is also the case during Quaternary periods of low sea level stands (∼120 m) where there is little evidence for the seaward migration of the Swan River mouth that could account for the extent of shelf-edge incision represented by the canyon. However, this does not preclude the possibility that a much more dynamic palaeo-Swan River drainage system provided precursor structures for the Perth Canyon, the initial uplift and down-cutting associated with either the late Jurassic-Early Cretaceous rifting of India from the western Australian margin, and/or the Late Cretaceous (mid-Santonian) breakup of Antarctic from the southern Australian margin (Exon et al., 2005).

Although the Perth Canyon is one of the few examples of significant incision into the Australian shelf-edge margin (Heap et al., 2008), its formation appears to be a result of tectonic controls along pre-existing basin structures, together with more recent (Tertiary) over steepening of shelf-edge sediments inducing submarine mass flow deposits and large-scale canyon cutting as observed in the Albany canyons (Exon et al., 2005). Given that the western Australian shelf edge is part of a passive margin, the timing of this incision event or events remain poorly constrained except that they cut the youngest sediments (i.e., Miocene).

Prior studies (Marshall et al., 1989; Shafik, 1991; Heap et al., 2008) of the canyon geology and biostratigraphy are based on dredge samples collected during the 1988 RV Rig Seismic expedition (BMR Cruise 80). These variably lithified limestones, shale/mudstones, and sandstones yielded foraminifer and nannofossil ages ranging mostly from Late Cretaceous to Early Miocene (Marshall et al., 1989; Shafik, 1991), and palynomorph ages between the Middle Cretaceous and Permian (Marshall et al., 1989). The depositional environments have been interpreted as varying from shallow marine to estuarine facies associated with the Swan River palaeo-drainage system (Playford et al., 1976; Quilty, 1978).

Oceanographic Setting

In general, the influence of a submarine canyon on the circulation, and therefore ecology, depends mainly on the configuration of the continental shelf and slope irrespective of the forcing characteristics of the circulation. Important parameters are the continental shelf depth, canyon depth below the shelf, canyon width, canyon length, canyon’s distance from the coast, the canyon’s intrusion into bay areas, and the depth of the canyon mouth. The interaction between shelf and slope current systems causes localized flow patterns, which influence the ecology in the canyon’s vicinity. The Perth Canyon is mainly influenced by the Leeuwin Current System (Pattiaratchi and Woo, 2009) particularly the Leeuwin Current (LC) and the LU. The LC is a surface current system (0–300 m) that transports warmer, less saline, nutrient poor waters of tropical origin southward while the LU is a subsurface (350–800 m) current that transports higher oxygen water, formed south of Australia, northward (Wijeratne et al., 2018).

The influence of the LC is limited to the upper 300 m and so does not play a major role in the dynamics of the canyon. Thus, the canyon’s influence on the LC dynamics is limited to the canyon head. However, the curvature of the continental shelf in the vicinity of the canyon and the separation of the LC from the continental shelf forms anticlockwise eddies at the surface, particularly during the winter (Rennie S. et al., 2009). The main influence within the canyon is through the LU. Field measurements (Rennie S.J. et al., 2009) and numerical studies (Rennie S. et al., 2009) have indicated that circulation within the canyon is temporally variable with few repeated flow patterns. Strong vertical stratification and current shear occur at water depths of 300–350 m, at the interface between the LC and LU. The interaction between the LU and the canyon generates eddies that form over periods of 5–10 days, migrate offshore, which are replaced by newly formed eddies within the canyon. Eddies within the canyon are cyclonic and thus favor upwelling in their center. Eddies are initially confined to the canyon and then migrated offshore; however, at least one eddy, even if weak, is present in the canyon at any given time (Rennie S. et al., 2009).

The LC water consists of surface water of tropical origin (TSW, warmer, lower salinity) and South Indian Central Water (higher salinity) whist the LU transports Subantarctic Mode Water (SAMW, higher dissolved oxygen). Other water masses present within the canyon include Antarctic Intermediate water (AAIW) and Upper Circumpolar Deep Water (UCDW) (Woo and Pattiaratchi, 2008).

Materials and Methods

The Perth Canyon cruise, FK150301, was undertaken in the early austral autumn from March 1st to 12th, 2015, aboard the RV Falkor, the research vessel of the philanthropic Schmidt Ocean Institute. We used the Falkor’s CTD Rosette for seawater sampling, and multi-beam sonars for high-resolution bathymetric mapping. A Sub-Atlantic Comanche 2,000 m ROV, operated by Neptune Marine Services, was employed for the strategic sampling of key megabenthos from six dive sites (comprising nine dives) and to record video imagery during each dive. Continuous video footage and still photographs were taken automatically at 20 s intervals throughout each of the dives. Additional still photographs were captured manually as required. Two dive sites (A, B) are located at the head of the canyon in the east, two (C, D) are in the south near the sharp junction of the main canyon valleys, and two are in the northwest near the canyon mouth (E) and above the canyon on the upper northern plateau (F). The geology of the canyon and surrounding shelf is captured by video footage and observations recorded in the dive event logs. A suite of bathymetry maps were generated post-cruise at different spatial resolutions (see below), which depict the overall canyon system as well as localized topographic features at each of the ROV dive locations where sampling was undertaken. Additional geological information has been gathered from spot sampling of rocks and sediments from the substrate, canyon walls, and plateau. A list of all samples collected during the cruise encompassing seawater, biological, and geological samples as well as complementary datasets are reported in the SOI Cruise FK150301 Final Report1 (McCulloch et al., 2017). The dive numbers in the figures and tables relate to the nine ROV survey and faunal collection dives only, so are offset by one from SOI D07 that was the USBL recovery dive. Specimens collected during the cruise have been deposited with the Western Australian Museum, and samples identified for geochemical analysis are held at the University of Western Australia.

Multibeam Bathymetric Analysis

High-resolution bathymetric data were acquired using Kongsberg EM 302 and 710 multi-beam echo sounders. Post-cruise, bathymetry maps of the canyon and all dive sites were generated at different spatial resolutions. The multi-beam echo-sounder data was processed using CARIS HIPS and SIPS 7.0 software. After loading raw data and applying tide corrections, the data were ‘cleaned’ using the Swath Editor that consists of interactively selecting and rejecting soundings as well as filtering functions, which automatically detected and rejected outliers. Following data correction and cleaning, a digital terrain model (DTM) was generated at 20 m resolution for the entire canyon (Figure 1), and at 10 m resolution for the ROV dive areas (Figures 24). The DTMs were exported in ASCII ESRI format and analyzed with ArcGIS 10.2. The ArcGIS Spatial Analyst tool was applied to derive the hill shade from the DTM with a vertical exaggeration of 1.5.


Figure 1. Satellite images of the location of the Perth Canyon and bathymetry map. Bathymetry map (right) prepared from multi-beam sonar data taken during the RV Falkor cruise. Location of the six ROV dive surveys (Sites A–F) are indicated. Note the lack of connectivity of the canyon to the coast (bottom left).


Figure 2. High-resolution bathymetry maps and photos of lithologies of the canyon walls and substrates at ROV dive Sites A and B (note insets), located in the northeast region of the canyon system. Black lines on the bathymetry maps depict ROV tracks, with each dive number indicated.


Figure 3. High-resolution bathymetry maps and photos of lithologies of the canyon walls and substrates at ROV dive Sites C and D (note insets), located in the southern region of the canyon system. Black lines on the bathymetry maps depict ROV tracks, with each dive number indicated.


Figure 4. High-resolution bathymetry maps and photos of lithologies of the canyon walls and substrates at ROV dive Sites E and F (note insets), located in the western region of the canyon system. Black lines on the bathymetry maps depict ROV tracks, with each dive number indicated.

Seawater Collection and Analyses

Water samples (n = 59, Supplementary Table 1) were collected between 15 and 2,000 m from five of the dive sites (A–C, E–F) using 12L Niskin bottles mounted on a Rosette system equipped with a Seabird SBE 9plus CTD, with a SBE 43 dissolved oxygen sensor and Wet Labs ECO-FLNTU. Water column profiles are based on 59 measurements of temperature (T), salinity (S), dissolved oxygen (DO), chlorophyll a concentration (Σchla, via water column fluorescence), total alkalinity (TA), dissolved inorganic carbon (DIC), and dissolved inorganic nutrients, together with calculations to determine the full suite of carbonate chemistry parameters. Seawater TA was measured on board by single-point titration based on spectrophotometric measurement of the end-point pH (Yao and Byrne, 1998). Seawater DIC was measured on board using an Apollo SciTech Dissolved Inorganic Carbon analyzer. Dissolved inorganic nutrients, including ammonium (NH4+), nitrate+nitrite (commonly referred to as just ‘nitrate’ or NO3-), phosphate (HPO42-), and silica [Si(OH)4] were analyzed at the University of Western Australia on a Lachat autoanalyzer using standard spectrophotometric methods. Seawater pH, pCO2, calcite saturation state (Ωcalcite), and aragonite saturation state (Ωaragonite) were calculated post-cruise using MATLAB version 1.1 of the CO2SYS software (van Heuven et al., 2011).

Stable C and O isotope measurements of 29 seawater samples from five sites (A: n = 9, B: n = 9, E: n = 11) were undertaken in the West Australian Biogeochemistry Centre at The University of Western Australia. The stable isotope compositions of oxygen and hydrogen were analyzed using an Isotopic Liquid Water Analyzer Picarro L1115-i. Each sample was analyzed six times and then the first four results were discarded in order to minimize any instrument memory effect. The δ2H and δ18O raw values of samples were normalized to the Vienna Standard Mean Ocean Water (VSMOW) scale, based on three laboratory standards, each replicated twice and reported in per mil (‰) following the principles of the three-point normalization (Skrzypek, 2013). All laboratory standards were calibrated against international reference materials that determine the VSMOW-SLAP scale (Coplen, 1996), provided by the International Atomic Energy Agency (for VSMOW2 δ2H and δ18O of equal 0‰ and for SLAP equal δ2H = -428.0‰ and δ18O = -55.50‰). The long-term analytical uncertainty (1σ) was determined as <1.0‰ for δ2H and <0.1‰ for δ18O (Skrzypek and Ford, 2014). The stable carbon isotope composition of DIC was analyzed using a Thermo-Fisher GasBench II coupled with Delta XL Isotope Ratio Mass Spectrometer. Prior water sample injection, 12 mL vials with 0.1 mL of 100% phosphoric acid were flushed with ultra-high purity helium (99.999%), and then reacted at 25°C for 24 h (Paul and Skrzypek, 2006). The water volumes of samples were adjusted accordingly in order to match the peak heights of reference materials and avoid the linearity effect. All results were expressed using the standard delta-notation (δ13C) and were reported in per mil (‰) after normalization to Vienna Pee Dee Belemnite isotope scale (VPDB). The multi-point normalization was based on three international standards NBS18, NBS19, and L-SVEC for δ13C, each replicated twice (Skrzypek, 2013). The analytical uncertainty was ≤ ±0.1‰ (1σ).

Radiocarbon (14C) analyses of 20 seawater samples collected from five sites (A–C and E, F) were undertaken at the Australian Nuclear Science and Technology Organisation (ANSTO). DIC of seawater (40–60 mL) was stripped out as CO2 by acidifying the samples with 85% H3PO4 (5 mL), which was carried out in a custom-built extraction line by sparging the acidified water with He gas for 15 min. The gas was recirculated, passing through two dry ice/ethanol traps to remove water, and a LN2 trap to condense the sample CO2. Following removal of the He and other incondensable gasses, the CO2 was converted to graphite using the H2/Fe method (Hua et al., 2001). A portion of graphite was used for the determination of δ13C for isotopic fractionation correction using a Micromass IsoPrime elemental analyzer/isotope ratio mass spectrometer (EA/IRMS). Accelerator mass spectrometry (AMS) 14C analysis was conducted using the STAR facility at ANSTO (Fink et al., 2004), with a typical analytical precision of better than 0.35% (1σ). Oxalic acid I (HOx-I) was used as the primary standard for AMS 14C determination, and oxalic acid II (HOx-II) and IAEA-C7 reference material were employed as secondary standards. The AMS results are presented in Δ14C, the per mil deviation from the absolute radiocarbon standard (Stuiver and Polach, 1977).

CTD-Rosette data were visualized using the Ocean Data View software (version 4.7.10), and all graphs of seawater parameters discussed above have been generated using this program.

Faunal Sampling and Descriptions

The ROV was used to collect megabenthos during each dive. Sampling mainly targeted deep-sea corals, especially those that precipitate carbonate skeletons given their suitability for geochemical proxy studies, which are ongoing. Faunal descriptions (see section “Canyon Fauna”) are mostly based on real-time observations of video footage that were recorded in event logs during the cruise, with subsequent identifications undertaken post-cruise on hand samples collected by the ROV. Taxonomic identifications are either to genus or species level where possible, however, specialist taxonomic research with publications are expected to be produced in the future. Faunal lists of samples collected by ROV can be found in the SOI Cruise FK150301 Final Report (McCulloch et al., 2017; see footnote 1), and vouchers of collected specimens have been deposited with the Western Australian Museum, Perth.

U-Th Dating of Corals

Absolute ages were determined by the uranium-thorium (238U–230Th) series decay technique for 28 fossil coral specimens (n = 31) collected at two ROV dive sites spanning a depth range of 691–1,788 m. Subsamples were extracted from the fossil skeletons of Desmophyllum dianthus (Esper, 1794) and Solenosmilia variabilis (Duncan, 1873), using a dental drill with diamond-encrusted blades and burs. The subsamples were first mechanically cleaned with the drill then crushed in an agate mortar and pestle. Aliquots of ∼20 to ∼50 mg were lightly leached in 0.1N HCl, dissolved in dilute HCl and spiked with enriched 229Th, 233U, and 236U tracers. Uranium and thorium were extracted from 3N HNO3 sample solutions using Eichrom UTEVA ion exchange chromatography resin following the procedure of Douville et al. (2010). All U-Th measurements were carried out on a Thermo Scientific Neptune Plus MC-ICPMS equipped with a jet interface and a desolvation system yielding an overall ion efficiency of 2–3%. The 238U signal was collected using a 1010 Ω amplifier, allowing signal intensities for 238U of >100 V. U samples and bracketing standard CRM 112-A were spiked with reference material IRMM-3636a to correct for mass bias and yield drift of the SEM. Additional corrections were applied for tailing and hydride generation. For Th determinations, 229Th-spiked samples were bracketed against IRMM-3636a, with specific attention given to maximize washout of 230Th between samples. Using U as the bracketing standard for Th may introduce some uncertainty from differential mass bias behavior, however, no suitable Th standard was available and errors from mass bias correction are generally smaller (<1‰) than errors from counting statistics on 230Th alone (∼3–8‰). Activity ratios for 230Th/238U and 234U/238U were then calculated using the decay constants and reference values given in Jaffey et al. (1971) and Cheng et al. (2013), but calibrating the [230Th/238U] = 1 for Harwell Uraninite HU-1 assuming secular equilibrium, and using δ234U = -38.5‰ for CRM112-A. Analytical uncertainty for δ234U derived from repeated determinations of HU-1 was 0.8‰ (2σ; n = 30), whereas errors on [230Th/238U] strongly depend on 230Th counting statistics and minor blank/washout corrections, and ranged from ∼2.8‰ (2σ; n = 30) for HU-1 to 8.3‰ (2σ; n = 12) for very young samples (e.g., CRM112-A). Total procedural blanks were typically on the order of ∼30 attograms for 230Th and ∼12 femtograms for 238U, which are considered negligible. Ages were calculated through iterative age estimation (Ludwig and Titterington, 1994) and assuming the initial non-radiogenic [230Th/232Th] = 2 (±1) then calibrated to the year 1950 (i.e., BP). All samples were prepared and analyzed in the Advanced Geochemical Facility for Indian Ocean Research at the University of Western Australia.

Geological Samples

Several geological ‘spot’ samples were collected using the ROV robotic arm. Foraminiferal biostratigraphy, palaeo-bathymetry, and lithologies have been determined from a selection of nine geological samples from four dive sites (A, D–F). Seven friable to partly friable samples were disaggregated in water and the washed sand fractions examined under a stereomicroscope. Samples of wackestone and chert were examined in thin section. The samples investigated were from depths of 1,603 m (FPC-15 D05-S01), 1,241 m (FPC-D05-S08), 1,032 m (FPC-D07-S05), 746–716 m (FPC-15 D09-S01, S02, S04) and 701 m (D08-S03). The biostratigraphy of these samples was determined from planktonic foraminiferal associations and the palaeo-bathymetry from benthic foraminiferal assemblages.

The strontium (Sr) isotopic compositions (87Sr/86Sr) were also undertaken to date some lithologies from the canyon wall. Sediments were sampled from the basal holdfasts of eight deep-water corals together with seven rock samples from five dive sites (A, B, D–F). Sediments extracted from coral holdfasts were from depths of 1,472 m (Site E D05-S03, live Vaughanella), 936 m (Site B D04-S01, live and fossil Desmophyllum and fossil Solenosmilia sampled from the same colony), 739 m (Site F D09-S02, live Polymyces), 701 m (Site A D08-S03, recently dead Polymyces), and 675 m (Site A D08-S05, live Caryophyllia). Sample collection D09-S2 was from a small boulder sitting on the substrate. Rock analyses were of subsamples from well-consolidated mudstone units sampled from the canyon wall at 1,444 m (Site E D05-S04 mudstone) and 1,032 m (Site D D07-S05), as well as soft, friable mudstone nodules collected from the shallower depths at 746 m (Site F D09-S01), 716 m (Site F D09-S04), and 701.3 m (Site A D08-S3). Collection D09-S02 comprises loose debris that was scooped from the substrate. The very small size and preservation of the foraminifers made them unsuitable for isotope analysis, thus precluding comparative Sr analysis of the host rocks and microfossils that were used for biostratigraphy.

Strontium was separated from 10 mg carbonate aliquots by ion exchange chromatography using Eichrom Sr Resin. All Sr isotopic compositions were measured in solution using the Thermo Scientific Neptune Plus housed in the Advanced Geochemical Facility of Indian Ocean Research at the University of Western Australia. Averages of standard 87Sr/86Sr measurements from two analytical sessions gave NBS SRM987 = 0.710299 (n = 7) and 0.710283 (n = 4), with analytical uncertainties at 95% confidence limits of 0.000015 and 0.000004, respectively. The instrumental mass fractionation was corrected using a stable isotopic ratio of 86Sr/88Sr of 0.1194 and an exponential law. 87Sr/86Sr measurements of the sample unknowns were normalized to 0.710248 to determine their Sr ages using the SIS Look-up Table v4:08/03 (McArthur et al., 2001).

Supplementary Oceanographic Data

The Perth Canyon region includes a range of oceanographic infrastructure that has been established as part of the Australian Integrated Marine Observing System (IMOS) and an overview of the different data streams is provided in Mihanović et al. (2016). These include oceanographic moorings that contain Acoustic Doppler Current Profilers (ADCP), surface currents measured by HF Radar, sea surface temperature from satellites and ocean glider transects. Data streams collected during the period of the RV Falkor voyage were abstracted from the IMOS data portal2.

Hourly data collected by the HF Radar systems were averaged over 24 h for March 9, 2015, and was overlain over the satellite derived sea surface temperature image for that date. Velocity profiles over the period March 1–15, 2015, from within the canyon were available from an IMOS mooring located in ∼500 m water depth (31.7867°S 114.9400°E). The Teledyne RDI Workhorse Long Ranger 75 kHz instrument was mounted on the sea bed and collected data at 15-min intervals in 16 m bins through the water column from 48 to 480 m from the seabed.

Ocean gliders are autonomous vehicles that utilize a buoyancy engine to move through the water column in a saw-tooth pattern (Pattiaratchi et al., 2017). During the RV Falkor voyage a Seaglider, developed by the University of Washington was deployed in the Perth Canyon and undertook east–west transects to a maximum depth of 1,000 m. The sensors on the Seaglider included those for temperature, salinity, and DO (Seabird Electronics SBE41 CTD and SBE 43 DO sensor) and optical sensors for Chlorophyll fluorescence (BBFL2SLO 3 parameter optical sensor). IMOS data streams are provided in NetCDF-4 format with ocean glider data files containing meta-data and scientific data for each glider mission. Subsequent to the ocean glider recovery, all data collected by the glider are subject to QA/QC procedures that include a series of automated and manual tests (Woo, 2018).


Canyon Morphology and Geology

The Perth Canyon is described as long, deep, narrow, steep-sided and intruding into the continental shelf. It is characterized by two main tributaries forming a sinuous or V-shaped configuration, which initially trends SW from the canyon head, then sharply diverges to the NW toward the mouth of the canyon (Figure 1). The 50 m depth contour marks the uppermost incision into the continental shelf, which expands to ∼10 km wide around the canyon head, meanders for ∼120 km to the west, and reaches depths of >4,000 m. At the canyon head, the depth plunges from 170 to 1,000 m. A series of approximately right-angle bends mark the major changes in the canyon’s orientation at distances of ∼10 km, 40 km, 50 km, and ∼100 km from the tip (the head’s closest point to the coast). From the easternmost tip, the canyon’s orientation at 0–10 km trends in a ∼SE–WNW direction, at 10–40 km it runs NE–SW, at 40–50 km it trends roughly E–W, at 50–100 km it changes to a ∼SE–NW direction, and at ∼100–120 km the mouth follows a near westerly direction as it opens onto the abyssal ocean plain. A morphologically more complex zone occurs in the region ∼40–50 km from the tip, where the canyon’s floor narrows in parts to <1 km in width and its orientation changes abruptly thus defining the major canyon bend (Site C). This main juncture at ∼50 km is joined by a short southern arm, a ∼15 km long trench of a similar morphology to the main (inshore) canyon head. The width of the canyon varies from roughly 2–5 km wide near the head, broadening to ∼10 km in the 10–40 km region, narrowing again to ∼5–8 km at Site C, and eventually expanding to ∼20 km at the mouth as it forms a large submarine fan. The walls of the canyon typically have ∼30° to 40° gradients although some parts are near vertical (Sites C and E). Broad terraces occur at the shallower sites near the canyon head (Sites A and B), and a distinctive NE trending scarp transects the northern canyon sites (E and F). Toward the mouth of the canyon, a steep walled, large arcuate terrace is reminiscent of a terrestrial amphitheater and waterfall (Site E).

Muddy substrates feature at the base of all six dive transects. Near the head of the canyon (Sites A and B) muds transition sharply to a coarse bedded vertical cliff-face with fissures and prismatic jointing. Lithologies comprised intervals of brecciated rock, interbeds of light-colored blocks with deformation indicative of slumping, mudstones and roughly eroded (karstified) chalky, friable layers of varying thickness, and thin nodular lenses. Similar lithologies are observed in the northernmost, shallow site on the canyon plateau (F), which also featured small fallen blocks, pebbles, and extensive fossil coral rubble deposits. The deepest sites (C and E) are characterized by steep canyon walls, sometimes near vertical, ∼500–600 m high, with massive blocky and jointed strata, and well-bedded consolidated units. Large muddy aprons containing masses of fossil coral deposits occur between the cliff walls (Site C). Layered mudstones, chert, large collapsed blocks, and steep walls transition to soft clay beds at the top of Site D. Other sedimentary features, such as cross-bedding (Site C), slump structures and wavy laminations (Site E), were also observed. Figures 24 show bathymetry maps for each dive site together with some lithologies observed during the surveys. Additional images of canyon lithologies observed during the dives are shown in Supplementary Figures 1, 2, and the ROV video footage available on the SOI website3.

Stratigraphy and Paleobathymetry

The nine geological samples examined represent a roughly 900 m sedimentary section that comprises three distinct facies of Late Paleocene, Middle-Late Eocene, and Early Oligocene in age (Supplementary Table 2) that were determined by planktonic foraminiferal biostratigraphy. Strontium (Sr) isotope analyses of rocks and/or sediments from remnant host rock attached to coral holdfasts are broadly consistent with biostratigraphic ages, except those of the youngest and shallowest samples (Supplementary Figure 3 and Supplementary Table 2). The paleobathymetry determined from benthic foraminifers from the RV Falkor samples indicate consistent upper bathyal to upper middle bathyal (200–700 m) depths throughout these Late Paleocene to Early Oligocene deposits. The Oligocene samples were probably deposited at a depth similar to the present-day water depth at Sites A and F, which are the shallowest dive sites. There is no evidence of down-slope movement of sediment from a neritic shelf environment so we assume the assemblages are in situ.

The co-occurrence of Globanomalina pseudomenardii and Acarinina soldadoensis in a wackestone collected at 1,602 m (Site E) indicates a Late Paleocene (Zone P4c) age of ∼56–56.5 Ma (Olsson et al., 1999). At 1,241 m (Site E), a wackestone containing Globigerinatheka index together with probable G. subconglobata and rare Acarinina sp., suggest a probable Middle Eocene age (zones E10–E12) of ∼40–44 Ma (Pearson et al., 2006). The presence of Globigerinatheka in an indurated wackestone collected at 1,032 m (Site D) indicates a Middle or Late Eocene (zones E8–E16) age of ∼34–48 Ma. The absence of distinct Acarinina or Morozovelloides may indicate an age no older than zone E12, late Middle Eocene (no older than ∼40 Ma). Wackestones collected from depths of 746 to 701 m (Sites A and F) contain foraminifera of the same age. The presence of Catapsydrax dissimilis, C. unicavus, Ciperoella anguliofficinalis, Globoturborotalita ouachitaensis, and Dentoglobigerina tripartita and the absence of Globigerinatheka, Hantkenina, and Turborotalia cerroazulensis, which are characteristic of the Late Eocene, as well as Globigerinoides that is characteristic of the Miocene, suggest that these samples are likely Oligocene in age. The lack of abundant Ciperoella, including the C. ciperoensis (Bolli) group of species, as well as Dentoglobigerina binaiensis (Koch) indicate an early Oligocene (zone O1–2) age of ∼30–33 Ma (Wade et al., 2018). For further details of the biostratigraphic analyses and paleobathymetry, see Supplementary Data.

The 87Sr/86Sr compositions of samples from 1,472 and 1,444 m (Site E) gave the lowest 87Sr/86Sr ratios (0.707775–0.707774), which equate to a broad range of Eocene ages (55.6–35.0 Ma) due to the non-linearity of the Sr isotope seawater curve for this period. These Sr ages are consistent with the Late Paleocene and Late Eocene biostratigraphic ages below and above these depths. The sample from 1,032 m (Site D) also yielded low 87Sr/86Sr ratios (0.707781 and 0.707794), and hence multiple possible Sr ages (45.1–35.3 Ma) between the Middle to Late Eocene, however, the inferred Middle Eocene biostratigraphic age constrains the Sr age between 43.9 and 45.1 Ma. Sediments from coral holdfasts as well as loose soft, friable, mudstone and siltstone nodules from shallower depths (936–675 m) at Sites A, B, and F, gave latest Oligocene to Early Miocene ages; for this time interval the Sr seawater curve is unidirectional and steep thus yielding single ages. Various samples from 936 m (Site B) gave consistent Early Miocene Sr ages (20.3, 20.1, and 19.8 Ma); there are no biostratigraphic ages for samples from this site for comparison. Early Miocene ages (22.0 to 17.0 Ma) were also determined from different samples types, collected between 746 and 716 m (Site F). Similarly young Sr ages, of Late Oligocene (23.9 Ma) and Early Miocene (22.4 17.6 Ma) were determined from various samples from depths of 701 to 675 m (Site A).

Chemical and Physical Oceanography

Structure and Chemical Compositions of Canyon Waters

The waters in and around the Perth Canyon (Sites A–C, E, F) are very similar in their physical structure and compositions (Supplementary Figures 47) and are consistent with previous studies (e.g., Woo and Pattiaratchi, 2008). Temperatures in the canyon range from ∼24°C to ∼2°C in the deepest water sampled (2,000 m). The salinities ranged between 34.4 and 35.6. The DO content ranged between ∼250 μmol kg-1 (300–550 m) and ∼150 μmol kg-1 (below 1,000 m). The major water masses in the canyon were identified based on their temperature (T), salinity (S), and DO content (Figure 5 and Supplementary Figure 4) and are summarized below:

1. Tropical Surface Waters (TSW: 0–100 m) found in the surface layer associated with the LC with T > 23.5°C and S ∼35.5.

2. South Indian Central Water (SICW: ∼100–300 m), an intermediate upper ocean water mass also associated with the LC with T = 16°–22°C and with a subsurface salinity maximum at S ≥ 35.7.

3. Subantarctic Mode Water (SAMW: >300 to ∼750 m) characterized by maxima in DO (>250 μmol kg-1) and associated with the LU with T = 8°–15°C and a salinity decrease from 35.4 to 34.6.

4. Antarctic Intermediate Water (AAIW: ∼750 to ∼1,000 m) with T = 4.5°–7°C and with a salinity maximum at 34.4.

5. Upper Circumpolar Deep Water (UCDW, ∼1,000 to ∼2,000 m) with T < 4.5° and salinity increasing from 34.5 with lower oxygen (∼150 μmol kg-1).


Figure 5. Temperature–salinity (left) and temperature–oxygen (right) plots for Potential Temperature Depth of Perth Canyon waters with water masses indicated. TSW, Tropical Surface Water; SICW, Subtropical Indian Central Water; SAMW, Subantarctic Mode Water; AAIW, Antarctic Intermediate Water; UCDW, Upper Circumpolar Deep Water. Isopycnals calculated with the reference pressure at 0 m.

The δ18O profile (Supplementary Figure 5A) shows a similar depth dependent trend to that of DO with a peak in δ18O. This is confirmed by the good correlation between salinity and δ18O (Supplementary Figure 5C). The hydrogen isotope profile (Supplementary Figure 5B) also shows a similar pattern as the δ18O, consistent with the higher salinity of the upper ∼200–300 m water masses having elevated δ2H.

Profiles of total chlorophyll exhibit a somewhat ‘noisy’ but persistent sub-surface maximum of 0.25–1.0 mg m-3 that occurs between ∼60 and 90 m at all locations, except the northernmost site (Site F) where the maximum of 0.36 mg m-3 is much deeper at ∼150 m (Supplementary Figure 6A). The water column nutrients throughout the Perth Canyon are generated almost entirely in situ, as indicated by the ratio of total dissolved inorganic nitrogen (nitrate plus ammonium) to total dissolved inorganic phosphorus (SRP) being close to the idealized Redfield-Richards ratio (17.4 ± 0.4 vs. 16). The nitrate plus nitrite and soluble reactive phosphorus increase monotonically with depth (Supplementary Figures 6B,C). TA and DIC are similar across the canyon sites (Supplementary Figures 7A,B). TA has a somewhat similar profile as salinity whereas DIC increases more monotonically with depth. There is a concomitant decrease in pH and increase in pCO2 with depth (Supplementary Figures 7C,D), and substantial monotonic declines of ∼75% in both calcite and aragonite saturation with depth relative to surface values (Supplementary Figures 7E,F). Although all waters within the Perth Canyon and surrounds remain oversaturated with respect to calcite, waters deeper than ∼1,000 m are undersaturated with respect to aragonite thus defining the aragonite saturation horizon at this depth.

The carbon isotope (δ13C) compositions of the canyon waters are consistent at the three sites measured near the head and mouth of the canyon (Site A, B, E). The δ13C composition initially decreases in depth within the uppermost ∼200 m (∼0.8–0.6‰), then rapidly increases to a maximum at ∼420 m (∼1.2‰), before decreasing to ∼0.4 from ∼1,200 m (Supplementary Figure 8A). Seawater radiocarbon (Δ14C) compositions also show consistent profiles (Sites B and E), ranging from 42.9 to -191.2 from surface to deep waters, showing similar compositions within the upper ∼500 m (Supplementary Figure 8B and Supplementary Table 3). These profiles are compared with δ13C and Δ14C profiles determined from earlier cruises undertaken in the region (Figure 6) to assess the uptake of anthropogenic carbon uptake over time (see section “Anthropogenic Impacts”).


Figure 6. Representative vertical profiles of seawater δ13C (top left) and Δ14C (top right) compositions from the Perth Canyon compared with data from earlier cruises in the region: GEOSECS (1978, station 436), WOCE (1995, station 435), and US CLIVAR/CO2 (2009, station 189). Satellite map (bottom) show relevant sampling sites from the Falkor (Perth Canyon), GEOSECS, WOCE, and CLIVAR cruises.

Canyon Hydrography

During the period of the RV Falkor cruise, surface currents reflected the typical summer circulation pattern in the study region. Here, the warm LC flows southward across the Perth Canyon (Supplementary Figure 9). On the continental shelf, the colder northward flowing Capes Current (CC) is present, driven by southerly winds. An anti-clockwise eddy forms at the surface centered at the head of the canyon (115.0°E) due to the current shear generated by the opposing currents (LC and CC) and the shoreline orientation. The warmer LC becomes spread laterally across the canyon: i.e., to the north and south of the canyon the LC is narrow but over the canyon it is much broader (Supplementary Figure 9).

The vertical current profiles obtained during the study period indicated evidence of strong diurnal–inertial resonance from March 1 to March 10, 2015 (Figure 7). Here, currents, in both the north–south and east–west components in the upper 200 m show strong oscillations that alternate between positive and negative values over each 24-h period. The winds changed after March 10, with no sea breeze events leading to cessation of the diurnal–inertial resonance and the generation of near-inertial waves. In the depth range of 200–450 m, the north–south component of the currents indicated persistent northward flow with mean currents ∼0.2 m s-1, which represents the LU. The time series indicate strong current shear between the upper layer (0–200 m) that include the diurnal oscillations, and the southward LC and the northward flowing LU below (Figure 7).


Figure 7. Time series of (A) east–west component; and (B) north–south component of currents recorded March 1–15, 2015 within the Perth Canyon at 500 m water depth (see location in Supplementary Figure 9). Positive values represent currents to the east and to the north.

The water properties observed with the Seaglider provided additional information to that obtained from the CTD casts. The temperature and salinity contours show downward tilting toward the coast (a vertical change of ∼100 m from east to west across the transect; Figure 8) due to the downwelling nature of the LC. The warmer (>23°C), lower salinity (<35.6) water forms only a shallow surface layer (<50 m) at the surface and a strong thermocline is present between 50 and 100 m (Figure 8A). The subsurface salinity maximum (>35.6) is present although at the western end of the transect it is at the surface (Figure 8B). The DO maximum layer present between 200 and 550 m (Figure 8C) indicates the SAMW associated with the LU. The other two deeper water masses present in the canyon, AAIW (750–1,000 m) and UCDW (1,000–2,000 m), were captured in the CTD casts (see section “Structure and Chemical Compositions of Canyon Waters”) and the ocean glider. Chlorophyll fluorescence indicated a persistent subsurface chlorophyll maximum centered at 80 m water depth (Figure 8D) across the canyon and was associated with the thermocline.


Figure 8. Ocean glider transect across the canyon showing: (A) temperature, (B) salinity, (C) dissolved oxygen, and (D) chlorophyll fluorescence. Note that the chlorophyll fluorescence is shown for the upper 200 m.

Canyon Fauna

One of the shallowest ROV surveys was conducted near the head of the canyon (Site A: 663–743 m) within AAIW. Here, crabs (e.g., Chaceon albus, Davie, Ng and Dawson, 2007) were the common mobile megabenthos. Demersal species were represented by grenadiers and deep-sea dories, and pelagic sea-cucumbers. The canyon walls harbored polychaete tube worms, glass sponges including a new species Amphidiscella sp. nov., occasional echinoderms (sea urchins, crinoids, and sea stars), lobsters (Figure 9A) (Projasus parkeri, Stebbing, 1902), and the zoanthid bearing hermit crab Sympagurus sp. (Figure 9B). The first cnidarians were seen at 716 m (sea anemone and cup corals), with species richness greater near the top of the cliff where antipatharians (e.g., Figures 9C,D) and solitary live and sub-fossil scleractinians (D. dianthus, Caryophyllia sp., and Polymyces sp.) were common. A selection of cup corals, D. dianthus, Caryophyllia sp., and Polymyces sp. (e.g., Figures 9E,F), were collected between 716 m and 674 m. Two Acesta sp. nov. bivalves (Figure 9G) and a hexactinellid sponge were collected from the canyon wall nearby between 675 and 695 m, also from rough karstified beds (e.g., Figure 9G and Supplementary Figure 1C), albeit more weakly lithified that sometimes fragmented during sampling. The gorgonian Narella sp. (Supplementary Figure 1E), was collected at 695 m from the canyon wall (that also accommodated serpulid tube worms) that was well-lithified and incorporated distinctive large white clasts and lenses (e.g., Figure 9C and Supplementary Figures 1E,F); a similar substrate was also present at the northernmost shallow Site F. A non-branching bamboo coral (Lepidisis sp.) was collected at 679 m and one large black coral (antipatharian) was sampled at 678 m (Figure 9D) where the canyon wall was composed of a massive, well-lithified, and relatively featureless matrix. Soft corals were uncommon and colonial scleractinians were not observed.


Figure 9. Images of some faunas observed during the ROV dives. Site A: Lobster Projasus parkeri (A), hermit crab Sympagurus sp. with zoanthid Epizoanthus sp. (B), antipatharian corals (C,D), cup corals Desmophyllum dianthus (E) and Polymyces sp. (F), Acesta sp. bivalve (G). Site B: bamboo coral (H). Site C: Corallium ‘community’ hosting various taxa (I), crinoid on Corallium sp. (J), crinoids and brittle stars on dead bamboo coral (K), hexactinellid sponge (L), fossil coral deposits predominantly D. dianthus (M). Site D: Walteria sp. glass sponge with comensal shrimp and bamboo coral (N), Solenosmilia variabilis colony (O). Site E: brittle stars, Anthomastus sp. and dead cup corals (P), Corallium sp. with brittle stars and D. dianthus (Q), Mn-coated dead Corallium stump (R). Site F: hexactinellid sponges, crinoids, and fossil coral deposits predominantly S. variabilis (S), pelagic holothurian and antipatharian coral (T), Bigeye Ocean Perch Helicolenus sp. and stylasterids (U).

During the slightly deeper dive at Site B (directly opposite Site A), we observed live and dead scleractinian corals, serpulid tube worms, brachiopods, verrucid barnacles, crustaceans (crabs and squat lobster), and the first sighting of the large glass sponges (Walteria sp., also at Site D) near the edge of the ridge. A sea anemone (1,079 m) and a gorgonian (probably Narella sp. at 1,010 m) were the deepest cnidarians observed. Coral diversity and abundance appeared markedly higher between ∼950 and 930 m. Within this range, several live but ∼20 dead (i.e., ferromanganese coated) D. dianthus were observed, and a dead colony of S. variabilis was collected at 936 m at the top of a ledge composed of coarse friable rock. This dead S. variabilis colony contained a single live polyp, as well as live and sub-fossil D. dianthus and numerous newly settled polyps (seemingly D. dianthus), the latter as small round dots on dead coral skeletons. Between 930 and 950 m were a moderately large number of bamboo corals (nominally Keratoisis), one collected at 933 m (Figure 9H) from the weakly lithified beds often observed throughout this shallower part of the canyon system. Gold corals (Chrysogorgia and Iridogorgia) and purple soft coral seen between 937 and 930 m.

The deepest dive surveyed was at Site C (1,512–1,821 m) within the UCDW, near the junction of the two main canyon tributaries. Depth ranges for different and widely distributed taxa included sea anemones (1,537–1,817 m), live bamboo corals (nominally Acanella, Keratoisis, and Lepidisis at 1,536–1,816 m), live black corals (1,572–1,789 m) and live D. dianthus (1,556–1,773 m). Over smaller depth ranges, or in smaller numbers, were Narella sp. (1,749–1,766 m), the gold corals Chrysogorgia and Metallogorgia (1,605–1,796 m; the former collected at 1,793 m), Anthomastus spp. (1,567 m), Paragorgia (collected at 1,739 m), Corallium (1,574–1,690 m), a large purple soft coral (1,561 m), unidentified soft corals (1,548–1,606 m), and gorgonians (1,568–1,577 m). Sea pens (Pennatulacea, at 1,528–1,612 m) were occasionally observed on the soft muddy substrates. Crinoids and brittle stars commonly colonized dead and live octocorals (Figures 9I,J), isidids (Figure 9K), and hexactinellids (Figure 9L). Most notably, a spectacularly diverse community of organisms was hosted by a large Corallium frame (collected at 1,557 m), which included Venus flytrap sea anemones (Actinoscyphia sp.), a new species of bivalve mollusc (Acesta sp. nov.), basket stars (Euryalina sp.), crinoids, and a new species of hexactinellid sponge (Farrea sp. nov., Figure 9I). This sample, like other octocorals that dominated this dive, was attached to hard massive rock that characterized the steep canyon walls at this site. Live scleractinians were rare in these deep waters, however, extensive coral graveyards protruded from the fine sediment aprons (reflecting the quiescent environment) between the canyon walls, at depths of ∼1,560–1,790 m. Potentially thousands of predominantly fossil cup corals, apparently D. dianthus (collected at 1,788 m; Figure 9M and Supplementary Figures 1J,L) together with fossil S. variabilis indicate substantial reef development in the past. Scattered on the cliff top were numerous bases of sub-fossil bamboo corals (1,550–1,795 m), much larger than the live specimens observed.

The nearby dive Site D on the opposite (southeast) side of the canyon was surveyed at shallower intermediate depths (834–1,210 m), within AAIW and close to the AAIW–UCDW interface (∼1,000 m). Walteria glass sponges (Figure 9N and Supplementary Figure 1C) were especially numerous along the ridge crest, and one specimen collected at 986 m was hosting a commensal shrimp, Paralebbeus sp. nov. Demersal faunas, such as oreodories and grenadiers, were often observed throughout this dive. The occasional sea anemone (maximum depth 1,209 m), black coral (1,186 m), and an unidentified “soft coral” (1,131 m) were also observed. The diversity and abundance of megabenthos increased markedly from ∼1,080 m depth, remaining high to the top of the cliff face at ∼990 m. Within that depth range were numerous live Anthomastus spp. (1,004–1,072 m), a stylasterid (1,022 m), gold coral (Metallogorgia spp. at 1,077 m), a moderately large number of live bamboo corals (nominally Keratoisis and Lepidisis at 1,046–1,077 m), and other octocoral species (probably Corallium spp. at 988 m). Several large sub-fossil bamboo corals were observed at the base of the cliff. Both live and dead octocoral samples were collected at 1,050 and 1,040 m. Some dead scleractinian cup corals, likely D. dianthus, were observed at 1,049–1,178 m, and seemingly long-dead colonies of the colonial S. variabilis occurred at 1,040–1,073 m. Part of a recently dead colony of S. variabilis was collected at 1,073 m from the canyon wall (Figure 9O). Brachiopods were also observed hanging from the walls under small ledges (Supplementary Figure 2A).

The westernmost dive, Site E, near the mouth of the canyon has steep topography and was surveyed within the deep UCDW waters (1,241–1,728 m) at similar depths to Site C. Sparse megabenthos at ∼1,600 m were mainly comprised of occasional whip-like black coral. Live cup corals (D. dianthus and Vaughanella sp.) were sparse (1,357–1,603 m) and occasional dead specimens were attached to the bedrock (Figure 9P). A live Vaughanella was collected from the canyon wall at 1,472 m (Supplementary Figure 2L), and dead D. dianthus were collected at 1,498 and 1,444 m. Live bamboo coral (nominally Keratoisis and Lepidisis) were seen at 1,381 m, one collected at 1,377 m, and scattered individuals were moderately abundant up to the shallowest survey depth of the dive (1,228 m). A Corallium collected at 1,357 m (Figure 9Q) hosted a small community including colonial and cup corals (S. variabilis and D. dianthus), a new species of hexactinellid glass sponge (Farrea sp. nov.) with its commensal polynoid scale worm, a large ophiuroid (Ophioplinthaca sp.), stalked barnacle [Glyptelasma orientale (Calman, 1919)], and squat lobster (Munidopsis sp.). Here, the canyon wall comprised well-lithified thin interbedded strata with distinctive deformation structures (Supplementary Figure 2I). A dead manganese-coated octocoral basal stump (Figure 9R) was collected at 1,247 m at the top of the traverse, where the substrate comprised thinly bedded irregularly eroded siltstones.

Above the canyon rim on the northern plateau, Site F represents one of the shallowest dive sites (682–760 m) surveyed within AAIW. Here, extensive coral graveyards (Figure 9S and Supplementary Figures 2N,R) carpeted the substrate (up to 100% of cover in places), together with large numbers of the hexactinellid sponge, Aphrocallistes sp., which comprised the dominant live benthos (Figure 9S). These remnants of extensive ancient coral reefs were dominated by the colonial species S. variabilis but also contained large numbers of cup corals (D. dianthus and Caryophyllia). Large scoops of fossil coral rubble and accompanying sponges were collected from 746 to 691 m, the associated hash having contained various taxa including gastropod (e.g., corallivorous epitoniids and Coralliophila sp.), bivalves, and thecosomatous pteropod shells. A number of sub-fossil octocoral bases were observed at 692 m (Keratoisis magnifica, Dueñas, Alderslade and Sánchez, 2014), 690 m (Corallium sp.), one thick and highly eroded sample collected at 683 m, but no bamboo corals were observed. Live cnidarians were sparse, with few representatives of antipatharians (742–745 m, e.g., Figure 9T), sea anemones (702–751 m), soft corals, unidentified octocorals (682–747 m), and cup corals (Polymyces sp., collected at 739 m), with stylasterids observed throughout the dive. The cup corals were observed close to the substrate, attached to ledges or small overhangs of well-lithified low-lying beds or fallen blocks. Mobile benthos included various crustaceans, including squat lobsters, hermit crabs (Sympagurus sp.) with the commensal zoanthid (Epizoanthus sp.), a solitary king crab (Paralomis dofleini, Balss, 1911) that is the southernmost record of the species, and few occurrences of echinoderms (sea stars and sea urchins). Large amounts of plankton in the water were observed, such as krill, ctenophores, and salp chains. Pelagic faunas observed included holothurians (Figure 9T), various fish (e.g., Bigeye Ocean Perch, Helicolenus sp., Figure 9U), and a shark.

The most common live scleractinian coral found was the cup coral Desmophyllum dianthus, which typically occurred in groups. Other solitary corals observed and collected were Caryophyllia sp., Polymyces sp., and Vaughanella sp. The only colonial scleractinian, Solenosmilia variabilis, was found alive as a small colony hosted by Corallium (Site E) and as a single polyp on a recently dead colony (Site B). Calcitic octocorals (e.g., Corallium, Lepidisis) were also present and collected during most surveys. Live corals were collected from intermediate waters (AAIW) at dive Sites A, B, D, F, and from deep waters (UCDW) at Sites C and E. The main coral taxa found and their associated water masses at each survey depth range are shown in Figure 10. Further details of observations and samples collected during the Perth Canyon cruise can be found in the events logs and final cruise report (McCulloch et al., 2017), which can be accessed from the Schmidt Ocean Institute website (see footnote 1). Taxonomic analysis of the collected specimens is ongoing (see section “Future Work”).


Figure 10. Key coral taxa observed alive during the ROV dives and the relationship of water masses to the dive survey depths. Salinity-depth profile of the canyon waters (bottom) show neutral density contours (kg/m3), water masses, depth range of each dive (white vertical bars), and CTD casts (white vertical lines). Inset shows path of section to generate seawater profile which is interpolated between sites. TSW, Tropical Surface Water; SICW, Subtropical Indian Central Water; SAMW, Subantarctic Mode Water; AAIW, Antarctic Intermediate Water; UCDW, Upper Circumpolar Deep Water. Sectors of pie charts are not proportional to abundance. Seawater profile generated using Ocean Data View.

Ages of Coral Taphocoenoses

U/Th ages determined from the skeletons of dead colonial (S. variabilis) and solitary (D. dianthus) scleractinians from the two coral graveyard deposits (Sites C and F) are similar, although specimens from the deeper waters span a wider age range (Figure 11 and Supplementary Table 4). Corals collected from deposits of mostly S. variabilis (Figure 9S), which covered the substrate north of the canyon (Site F) at intermediate water depths (690–720 m), range in age from ∼22 ka to ∼27 ka (BP). The deep water (1,560–1,790 m) deposits with prolific D. dianthus (Figure 9M) protruding from sediments between the canyon walls in the south of the canyon (Site C), yielded ages from ∼18 ka to ∼33 ka (BP).


Figure 11. U/Th ages relative to depth distribution of scleractinian corals from the Perth Canyon collected from two dive sites. These fossil coral ‘graveyard’ deposits occur at Sites C (∼1,500–1,800 m) and F (∼700 m). LGM, Last Glacial Maximum; MIS, Marine Isotope Stage; HS, Heinrich-Stadial.


This study has provided the first video footage and important information about the canyon and its inhabitants, including indicators of anthropogenic effects registered by these waters, which are discussed in detail below. The variably lithified shales/mudstones and sandstones most commonly observed throughout the canyon are similar to reports from earlier studies (Marshall et al., 1989; Shafik, 1991) undertaken on dredge samples recovered from the canyon walls and continental slope during the 1988 RV Rig Seismic expedition (BMR Cruise 80). Our Late Paleocene to possibly Early Miocene biostratigraphic ages are also consistent with the main stratigraphic units previously ascribed to the Perth Canyon (Supplementary Figure 3), which comprise the Upper Paleocene-Lower Eocene Kings Park Formation, Middle Eocene Porpoise Bay Formation, Upper Eocene Challenger Formation, and the Lower-Middle Miocene Stark Bay Formation (Marshall et al., 1989; Shafik, 1991). We note the discrepancies between our Early Oligocene biostratigraphic ages and late Oligocene-Early Miocene Sr ages for loose samples from the shallower dive sites at the canyon head and plateau (A and F). Here we invoke caution given the potential for dissolution (diagenetic) effects or mixed sampling, however, Miocene foraminifer and nannofossil ages have been reported from prior sampling surveys (Shafik, 1991; Marshall et al., 1998). Notably, the Challenger 1 drill core (WAPET 1975; oil exploration well), collected approximately 50 km south of the Perth Canyon, represents a condensed section (∼240 m thick) of dominantly carbonate lithologies with Late Palaeocene to Late Miocene (Quilty, 1978) planktonic foraminifera, which is equivalent in age to our much thicker Perth Canyon section (∼900 m).

The oceanographic data collected during the cruise are in agreement with all of the previous studies (e.g., Woo and Pattiaratchi, 2008; Rennie S. et al., 2009; Rennie S.J. et al., 2009). Our data re-iterate that, although the LC has a minimal influence on the circulation within the canyon, the LU has a significant influence in water depths of 200–800 m. The LU transports SAMW, containing high DO water that originates from the Southern Ocean, to depths of 200–750 m within the canyon. The CTD on the ROV and ocean glider data sampled to maximum depths of 2,000 m and identified AAIW and UCDW, both containing lower DO concentrations beneath SAMW. Below UCDW (i.e., in depth >2,000 m), previous studies (Woo et al., 2006) have identified Lower Circumpolar Deep Water (LCDW: depth range 2,500–3,500m) and Antarctic Bottom Water (AABW: depth range >3,500 m). The persistent sub-surface chlorophyll maximum present at depths ∼80 m associated with vertical thermal stratification is similar to results reported by Twomey et al. (2007).

Faunal Communities and Habitat Conditions

This expedition located and collected a variety of deep-sea fauna, especially deep-sea corals, and has provided the first ‘snap-shots’ of this large previously unexplored canyon system, mostly within the depth range where cold water corals normally flourish (∼200–2,000 m). Overall, sessile marine benthos typically inhabited the harder surfaces of the canyon walls, but were sparsely distributed throughout the dives. A variety of organisms were often observed in close spatial association forming diverse communities; for example, various echinoderms, including basket stars were often attached to large coral colonies such as Corallium sp., illustrating the tendency of deep-sea marine life to cluster around habitat forming species. Similarly spectacular, was the row of the large glass sponge Walteria along the top of the ridge at Site D (also present at Site B) these being the first record of this genus in Australian waters and the Indian Ocean, having previously been reported only from Japan, Kermadec Ridge, and Hawaii. Bivalves (Acesta), occasional brachiopods, and most commonly groups of cup corals (Scleractinia) were found along ledges and overhangs on the canyon walls. Sometimes rows of cup corals, Desmophyllum dianthus especially, were found suspended along the moderately lithified and often heavily karstified beds common near the canyon head (Supplementary Figure 1C), which provided numerous ledges, crevices, and attachment surfaces. Presumably, this part of the canyon within the upper intermediate waters together with its apparently karstified walls is favorable for these relatively small sessile filter feeders by providing a sufficiently stable substrate, protection from predators, and adequate nutrient supply. However, live specimens of the larger colonial coral S. variabilis are conspicuously rare throughout the dives, which contrasts to their common occurrence in the Tasman seamounts in the South Pacific and Southern Ocean (Thresher et al., 2011). The predominance of this relatively soft and friable lithology, especially in the shallower sites of intermediate water depths, might have played a role in restricting the development of larger mega-benthos, such as colonial coral structures. Gorgonian (Corallium, Narella) and bamboo (Lepidisis) corals inhabited the greatest depth range through deep and intermediate waters surveyed in the canyon, which is expected given the greater depth of calcite saturation (see below).

The corals were of specific interest, being the target for subsequent geochemical analysis given their importance as environmental archives. They inhabited the cold deep (UCDW) and intermediate (AAIW) waters where temperatures (∼2.5–6°C), pH (7.84–7.98), and DO concentrations (∼150–250 μmol kg-1) are within the ranges commonly reported from other deep sea and/or shallow cold and low pH environments (e.g., fjords) where corals flourish. These water masses are sourced from the Southern Ocean, their compositions including nutrients being almost entirely advected from the south, apart from minimal local contributions via biological export from the surface waters. Furthermore, changes in local hydrography (eddies, upwelling) are essentially limited to shallower depths above the canyon (limited to depths <300 m) and often develop further offshore, thereby affecting the surface water biota as reported elsewhere (Rennie S. et al., 2009; Rennie S.J. et al., 2009). The deeper waters within the canyon appear to be quiescent and lack strong currents (tides have negligible influence), as revealed by expanses of sediment drapes and that ROV deployments did not encounter strong turbulence below the surface currents (>300 m). Thus, the canyon topography has little effect on much of the canyon waters, which is also supported by the consistent seawater characteristics at respective depths across all dive sites.

The absence of sediment input together with the passive deep-water conditions characteristic of the Perth Canyon differ markedly from other canyon systems where rich ecosystems of cold-water corals occur. A dynamic bottom-water regime, such as vigorous bottom currents, internal tides and waves, and downwelling of nutrient-rich surface waters, are critical for enhancing food distribution through the water column, which is important for the development of large coral ecosystems (White et al., 2005; Duineveld et al., 2007; Dullo et al., 2008; Freiwald et al., 2009; Roberts et al., 2009; Rüggeberg et al., 2011; Hebbeln et al., 2014, 2016; Mohn et al., 2014; De Clippele et al., 2018). The relatively sporadic distribution of fauna observed during the Perth Canyon expedition is consistent with a passive canyon scenario, however, we acknowledge that our spatially limited faunal observations might not be representative of the ecosystems potentially inhabiting this large canyon system.

The distribution of calcifiers should also be partly controlled by the carbonate saturation state and pH of the ambient waters. The carbonate chemistry determined from these waters (Sites B, C, and E; Supplementary Figures 7E,F) show that the calcite saturation state is above unity (Ωcalcite > 1) at all depths sampled (i.e., to 2,000 m), which is consistent with the presence of calcitic corals at the deepest survey depths. Conversely, aragonite saturation reaches unity (Ωaragonite ∼ 1) at ∼1,000 m, thus waters below this depth are undersaturated with respect to aragonite yet some aragonitic scleractinian corals (D. dianthus and Vaughanella sp.) were observed and/or collected from depths of ∼1,360–1,770 m. Similar observations have been made from the Tasman seamounts where corals inhabit waters in which both aragonite and calcite are undersaturated by up to 40% (Thresher et al., 2011). Such observations clearly indicate that scleractinians can calcify their skeletons in undersaturated waters, where the low pH corrosive waters do not appear to have significantly adverse effects on their carbonate skeletons. Existing hypotheses suggest that tissues and organic layers may protect the skeletons from dissolution (Ries et al., 2009; Rodolfo-Metalpa et al., 2011), and prior studies have shown that cold-water scleractinian corals significantly up-regulate their internal pH and saturation state in order to enhance calcification (Anagnostou et al., 2012; McCulloch et al., 2012), which is especially important in these low temperature and low pH environments.

The abundance of coral-bearing taphocoenoses (D. dianthus and S. variabilis) in the Perth Canyon is also a very significant find. Notably these deposits were discovered at two spatially disparate sites through a large depth range, which clearly indicates that both colonial and solitary cold-water corals flourished during the last ice age. Their ages span the Marine Isotope Stage (MIS) 3–2 transition and the Last Glacial Maximum (LGM) into early Heinrich Stadial 1 (HS-1), with the latter marking the onset of the deglaciation. These ages are equivalent to those of D. dianthus recovered from high latitude waters of the Southern Ocean south of Tasmania (Hines et al., 2015) that were collected from depths (∼1,400 to ∼1,800 m) equivalent to the deeper D. dianthus deposits (Site C) in the Perth Canyon. The abundance of LGM S. variabilis is an interesting contrast to their present-day occurrence, being very rare at the locations we surveyed. These fossil corals will also be important for geochemical studies reconstructing environmental conditions prior to and during the LGM, which is often modeled to understand ocean-climate dynamics and constraining the carbon budget that underpin predictions of future climate change scenarios.

Anthropogenic Impacts

Despite the proximity of the Perth Canyon waters to a major city and commercial port, the physical imprint of human activities is remarkably absent. The only indicators observed were a stranded oceanographic glider and very minor traces of litter including a fishing net at shallower depths (Sites A and F). Conversely, isotope analyses of seawater samples have shown the ingress of anthropogenic carbon within surface waters, from both nuclear bomb tests and CO2 emissions, the latter also registered in upper intermediate water depths.

The general profile of δ13C is similar to those reported previously by Kroopnick (1985) for the eastern Indian Ocean, as well as Sonnerup et al. (2000) and Quay et al. (2003) for the central subtropical (∼20°S) Indian Ocean waters. Those samples were collected further offshore and north of the Perth Canyon during earlier the GEOSECS (1978) and WOCE (1995) cruises. Comparison of prior δ13C measurements closest to the Perth Canyon, undertaken in 1978 (GEOSECS, station 436), 1995 (WOCE, station 435), and 2009 (US CLIVAR/CO2, station 189), show continued depletion of 13C within the upper ∼800 m, the 2015 Perth Canyon data having the greatest negative offset of up to ∼0.8‰ (at ∼200 m) from the 1978 profile (Figure 6). The highest δ13C values of ∼1.1‰ of the Perth Canyon waters occur at a depth of ∼500 m, which coincides with the north flowing high oxygen SAMW (Figure 5), this being consistent with the global pattern of apparent oxygen utilization as shown by Eide et al. (2017b). This is indicative of the close link between higher O2 and biologically induced fractionation of 13C/12C. Furthermore, these results illustrate the complexities of the depth-dependent carbon cycle, with this biologic enrichment in δ13C being partially nullified by the ingress into surface and upper intermediate water depths of low δ13C fossil fuel derived carbon (-28‰, Andres et al., 1996). This latter process is commonly referred to as the δ13C Suess effect, which counters the near surface biologically controlled fractionation of 13C/12C. Between the years 1978 and 2015, the overall rate of change in seawater δ13C within the Perth Canyon region that can be ascribed to the δ13C Suess effect is -0.23‰ per decade. Similar mean decadal declines in 13C have been reported previously for the Indian Ocean and Atlantic subtropics (0.18–0.25‰) with slightly lower means given for the global ocean (Bacastow et al., 1996; Gruber et al., 1999; Sonnerup et al., 1999; Körtzinger et al., 2003; Quay et al., 2003; Eide et al., 2017a).

Seawater radiocarbon (Δ14C) compositions show a similar depth trend to that of existing profiles for the region determined in 1978 (GEOSECS, station 436), 1995 (WOCE station, 435 B), and 2009 (US CLIVAR/CO2, station 189 B). These profiles systematically diverge within the upper ∼500 m reflecting a decrease of ∼95‰ from 1978 to 2015 in this region. This systematic decrease in upper ocean 14C reflects a combination of processes: (1) the 14C Suess effect, whereby the nuclear bomb 14C produced in the late 1950s and early 1960s is effectively diluted by highly 14C depleted anthropogenic CO2 released into the atmosphere from fossil fuel burning, reflecting the geologic age (>107 years) of fossil fuels; (2) the uptake of 14C by both the terrestrial biosphere and upper ocean sinks, the latter process being evident in the depth transects (Figure 6); and (3) the decay of 14C (T1/2 5680 years). Recognizing the minor difference in site locations between past oceanographic surveys and this study of Perth Canyon waters, the rate in 14C decline in the upper waters is on average about 28‰ per decade between 1978 and 2015, however, the decadal rate has effectively halved between the two collection intervals, from 40‰ (1978–1995) to 20‰ (1995–2015).

The decline in seawater 14C in this region is approximately ⅓ of the atmospheric rate of decline (∼80‰ per decade) for that period (Orr et al., 2017; Turnbull et al., 2017), consistent with the longer timescales required for isotopic equilibration of the atmosphere and upper ocean, and the ongoing dilution of 14C in the atmosphere by fossil fuel emissions. However, given the competing factor of variable biologically enhanced fractionation of δ13C as evident in SAMW, reliable deconvolution of the δ13C Suess effect has significant uncertainties especially in the absence of seasonal profiling. Nevertheless, the penetration depth of 14C (∼500 m) is clearly defined and less than that of 13C (∼800 m), which is consistent with relative penetration depths modeled for mean anthropogenic CO2, 13C, and 14C and their relative time histories (Quay et al., 2003). Below the upper ∼650 m, the radiocarbon content decreases from -25.6‰ (±2.7, 1σ) to -191.2‰ (±2.6, 1σ) between 651 m and 2,000 m, reflecting the gradual increase in age with depth (from ∼210 to 1,700 years) (Supplementary Table 3) and thus the very low 14C content of those older waters.

Future Work

Taxonomic analysis of the collected specimens is ongoing at the Western Australian Museum, with species descriptions for the hexactinellid sponges (J. Fromont, personal communication), Acesta sp. nov. (L. Kirkendale, personal communication), and crinoids (N. Wilson, personal communication) currently in preparation. Further details and analysis of specific faunal habitats will require thorough analysis of all ROV video footage by various specialist taxonomists and ecologists, which is beyond the scope of this study. A large analytical program is currently underway on geochemical proxy studies of both young and fossil corals, a major aim of the cruise being to collect suitable coral species for that work. These archives will provide important environmental records of intermediate to deep waters through major climate events, from the last glacial period as well as modern (pre-industrial to industrial) intervals. Such data are needed to help discriminate long-term natural variations from recent anthropogenic effects that are beginning to impact the deep ocean. Deep-water corals can therefore play an important role both as archives of environmental change in these poorly studied yet critical areas within the ocean-climate system, and in determining the inherent vulnerabilities and future responses of deep-water ecosystems to global climate change.


This study represents our first observations and analysis of samples collected from the Perth Canyon, which have revealed the following:

1. This is a remarkably quiescent ‘fossil’ canyon system.

2. Fauna are sparse but concentrate in groups forming relatively diverse communities along the canyon walls and rim.

3. Calcifying megabenthos occur throughout the intermediate and deep waters, with some cup corals living below the aragonite saturation horizon (∼ 1000 m).

4. Extensive coral graveyards reveal that deep-water corals thrived in the canyon during the last ice age (∼33 to ∼18 ka BP), prior to and during the Last Glacial Maximum.

5. The carbon isotope (Δ14C and δ13C) compositions of the canyon waters show that anthropogenic carbon has entered upper intermediate water depths between ∼600 and 800 m, which has important consequences for the deep-sea calcifiers inhabiting the canyon given the already adverse seawater conditions (Ω ∼ 1) under which they must form their carbonate skeletons.

Author Contributions

JT, MM, and CP conceived the study. JT, MM, CP, PM, MT, JF, RT, and AH performed fieldwork and data collection. JT, MM, CP, JF, PM, MT, QH, FF, and DH analyzed the samples and/or interpreted the data. JT led the writing of the manuscript. All authors read and approved the final manuscript.


This work was supported by research funding from the Australian Research Council to MM (FL120100049) and JT (FT160100259), the Italian National Programme of Antarctic Research (PNRA16-00069 Graceful Project) to PM and MT, the Australian Institute of Nuclear Science and Engineering to MM, JT, JF, RT, MT, PM (AINSE Award 16/009). Supplementary oceanographic data are funded through Integrated Marine Observing System (IMOS) supported by the Australian Government.

Conflict of Interest Statement

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.


The authors gratefully acknowledge the Schmidt Ocean Institute for providing the RV Falkor and all necessary equipment and crew that enabled us to undertake this cruise (FK150301). The Falkor crew and the ROV pilots from Neptune Marine Services are thanked for their expert assistance during the cruise. Kai Rankenburg (UWA) is thanked for assistance with U/Th mass spectrometry. Ana Hara, Jane Fromont, Oliver Gomez, Lisa Kirkendale, Glenn Moore, and Corey Whisson (from WAM) are thanked for assistance with identifications and specimen processing. The ocean glider and HF Radar data were collected by the IMOS Ocean Glider and ocean Radar facilities located at the University of Western Australia. The mooring data used in this paper were collected by the CSIRO, a sub-facility of the Australian National Mooring Network (ANMN). This is ISMAR-CNR, Bologna scientific contribution n. 1994. Note that some aspects of this paper appear in the pre-print of Trotter et al. (2018) in Biogeo-sciences Discussions (

Supplementary Material

The Supplementary Material for this article can be found online at:


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Keywords: Perth Canyon, deep-sea coral, oceanography, south-west Australia, remotely operated vehicle

Citation: Trotter JA, Pattiaratchi C, Montagna P, Taviani M, Falter J, Thresher R, Hosie A, Haig D, Foglini F, Hua Q and McCulloch MT (2019) First ROV Exploration of the Perth Canyon: Canyon Setting, Faunal Observations, and Anthropogenic Impacts. Front. Mar. Sci. 6:173. doi: 10.3389/fmars.2019.00173

Received: 21 December 2018; Accepted: 18 March 2019;
Published: 12 April 2019.

Edited by:

Cristina Gambi, Polytechnical University of Marche, Italy

Reviewed by:

Cristina Linares, University of Barcelona, Spain
Saskia Brix, Senckenberg Museum, Germany

Copyright © 2019 Trotter, Pattiaratchi, Montagna, Taviani, Falter, Thresher, Hosie, Haig, Foglini, Hua and McCulloch. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.

*Correspondence: Julie A. Trotter,