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Locations of megafaunal surveys during ABYSSLINE cruise 01 (AB01) in the eastern Clarion-Clipperton Zone.: (a) The location of the UK-1 exploration contract area in the Pacific Ocean. (b) The location of UK-1 Stratum A in relation to the UK-1 contract area and the AB01 ROV dive site, EPIRB, which was approximately 250 km east of the UK-1 contract area. (c) A bathymetric map of UK-1 Stratum A with the locations of ROV dives indicated by circles with the dive number. All maps were created by Seafloor Investigations Ltd. for the ABYSSLINE Project using ArcGIS software (https://www.arcgis.com/features/). (c) was created using unpublished ship-based bathymetry collected during AB01.

Locations of megafaunal surveys during ABYSSLINE cruise 01 (AB01) in the eastern Clarion-Clipperton Zone.: (a) The location of the UK-1 exploration contract area in the Pacific Ocean. (b) The location of UK-1 Stratum A in relation to the UK-1 contract area and the AB01 ROV dive site, EPIRB, which was approximately 250 km east of the UK-1 contract area. (c) A bathymetric map of UK-1 Stratum A with the locations of ROV dives indicated by circles with the dive number. All maps were created by Seafloor Investigations Ltd. for the ABYSSLINE Project using ArcGIS software (https://www.arcgis.com/features/). (c) was created using unpublished ship-based bathymetry collected during AB01.

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There is growing interest in mining polymetallic nodules in the abyssal Clarion-Clipperton Zone (CCZ) in the Pacific. Nonetheless, benthic communities in this region remain poorly known. The ABYSSLINE Project is conducting benthic biological baseline surveys for the UK Seabed Resources Ltd. exploration contract area (UK-1) in the CCZ. Using a Remot...

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... five most abundant morphotypes observed during AB01 dominated the megafaunal community, comprising nearly half (45%) of all individuals. The remaining morphotypes were generally rare, as indicated by the rank order abundance curve (see Supplementary Figure S1), with 62% of the morphotypes (84 of 136) observed fewer than ten times, and 24% (33 morphotypes) seen only once in quantitative transects. There was greater com- munity similarity at the transect level within sites (> 80% similarity) than between sites (< 68% similarity) (see Supplementary Figure S2). ...
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... UK-1 exploration contract area is located in the eastern CCZ ( Fig. 1) and has an annual POC flux to the abyssal seafloor of roughly 1 gCm −2 y −1 , i.e., ~two-fold higher than in the western CCZ 50 . During the first cruise (ABYSSLINE Project cruise AB01, RV Melville cruise MV1313, 3-27 October, 2013), we focused on a 30 × 30 km stratum (UK-1 Stratum A) centered at 13°49′ N, 116°36′ W (Fig. 1). Multibeam ...
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... in the eastern CCZ ( Fig. 1) and has an annual POC flux to the abyssal seafloor of roughly 1 gCm −2 y −1 , i.e., ~two-fold higher than in the western CCZ 50 . During the first cruise (ABYSSLINE Project cruise AB01, RV Melville cruise MV1313, 3-27 October, 2013), we focused on a 30 × 30 km stratum (UK-1 Stratum A) centered at 13°49′ N, 116°36′ W (Fig. 1). Multibeam bathymetric surveys during the cruise indicated an abyssal seafloor characterized by ridges and valleys running from NNW to SSE at 3900-4400 m depth (Fig. 1). Bottom-water temperatures were ~2 °C, bottom-water oxygen concentrations were ~3.2 ml L −1 , and our observations revealed abyssal current velocities below sediment ...
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... first cruise (ABYSSLINE Project cruise AB01, RV Melville cruise MV1313, 3-27 October, 2013), we focused on a 30 × 30 km stratum (UK-1 Stratum A) centered at 13°49′ N, 116°36′ W (Fig. 1). Multibeam bathymetric surveys during the cruise indicated an abyssal seafloor characterized by ridges and valleys running from NNW to SSE at 3900-4400 m depth (Fig. 1). Bottom-water temperatures were ~2 °C, bottom-water oxygen concentrations were ~3.2 ml L −1 , and our observations revealed abyssal current velocities below sediment erosion thresholds throughout our 16 days on station (unpublished data, ABYSSLINE ...
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... commercial Remotely Operated Vehicle (ROV) Remora III, operated by Phoenix International Holdings, Inc., performed video surveys and sample collections at five randomly-located sites: four within UK-1 Stratum A, and one ~250 km to the east of the UK-1 contract area at a site here called 'EPIRB' centered at 13°40′ N, 114°24′ W (Fig. 1). Our original study design involved surveys at random sites within Stratum A, but ROV failures limited us to four sites. Work at the EPIRB site was dictated by an emergency response to an EPIRB distress signal and, although unplanned, provided a useful broader context for our study. The ROV was equipped with two manipula- tors, four ...
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... and all metazoan specimens sequenced for a range of DNA markers at the Natural History Museum, London, with tissue samples subsequently archived and made openly-available for future taxonomic work 37,38,62 . ROV megafaunal video surveys. ROV still images and video were collected at all five sites for the "qual- itative" analysis of megafauna (Fig. 1). This analysis utilized all video from both "pilot" and "science" cameras (covering roughly 8000 m 2 ) whereas the quantitative analysis only used the high-definition imagery from the Scientific RepoRts | 6:30492 | DOI: 10.1038/srep30492 "science" camera. Due to ROV failures and altitude instability during surveys, we were able to ...
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... only used the high-definition imagery from the Scientific RepoRts | 6:30492 | DOI: 10.1038/srep30492 "science" camera. Due to ROV failures and altitude instability during surveys, we were able to obtain only four 1-km surveys, two at each of two sites (Sites 6 and EPIRB), of sufficient quality to be utilized in the quantitative assessment ( Fig. 1 and see Supplementary Table S4). At each site, both transects were conducted along random headings, with the second transect beginning within 100 m of the end of the ...

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... Commonly employed sampling methods associated with exploration activities, such as core collection (box cores, multiple or piston samplers) and EBS, could deepen the SML, with some flocculent surficial sediment being completely removed and/or laterally transported and redeposited nearby (Amon et al., 2016;Jung et al., 1998). ...
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... microbes, foraminifera, invertebrate metazoans (e.g., nematodes, polychaetes, copepods, sponges, and echinoderms), fish, and, to a lesser extent, mammals (Amon et al., 2016;Pape et al., 2013;Rabone et al., 2023). Importantly, species diversity remains poorly described for both terrestrial and oceanic ecosystems, with an estimated 91% and 86% of eukaryotic species expected yet to be discovered in the ocean and on land, respectively (Mora et al., 2011). ...
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The crises of climate change and biodiversity loss are interlinked and must be addressed jointly. A proposed solution for reducing reliance on fossil fuels, and thus mitigating climate change, is the transition from conventional combustion‐engine to electric vehicles. This transition currently requires additional mineral resources, such as nickel and cobalt used in car batteries, presently obtained from land‐based mines. Most options to meet this demand are associated with some biodiversity loss. One proposal is to mine the deep seabed, a vast, relatively pristine and mostly unexplored region of our planet. Few comparisons of environmental impacts of solely expanding land‐based mining versus extending mining to the deep seabed for the additional resources exist and for biodiversity only qualitative. Here, we present a framework that facilitates a holistic comparison of relative ecosystem impacts by mining, using empirical data from relevant environmental metrics. This framework (Environmental Impact Wheel) includes a suite of physicochemical and biological components, rather than a few selected metrics, surrogates, or proxies. It is modified from the “recovery wheel” presented in the International Standards for the Practice of Ecological Restoration to address impacts rather than recovery. The wheel includes six attributes (physical condition, community composition, structural diversity, ecosystem function, external exchanges and absence of threats). Each has 3–5 sub attributes, in turn measured with several indicators. The framework includes five steps: (1) identifying geographic scope; (2) identifying relevant spatiotemporal scales; (3) selecting relevant indicators for each sub‐attribute; (4) aggregating changes in indicators to scores; and (5) generating Environmental Impact Wheels for targeted comparisons. To move forward comparisons of land‐based with deep seabed mining, thresholds of the indicators that reflect the range in severity of environmental impacts are needed. Indicators should be based on clearly articulated environmental goals, with objectives and targets that are specific, measurable, achievable, relevant, and time bound.
... Nodules offer hard substrata in an otherwise soft sediment environment and host a specific nodule-associated fauna. More than 60% of megafauna depend on the nodules for attachment and survival (Amon et al., 2016;Vanreusel et al., 2016;Simon-Lledoé t al., 2019a). In order to be able to quantify the impact of potential deep-sea mining on nodule associated fauna, there is an urgent need for extensive ecological baselines to understand the natural biodiversity, variation (spatial and temporal) and possible resilience of fauna to mining impacts. ...
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... Most of the fauna lives in the upper 5 cm of the sediment (Spiess et al. 1987;Smith and Demopoulos 2003) or even uses the nodules themselves as a habitat (Thiel et al. 1993;Veillette et al. 2007;Vanreusel et al. 2016;Drennan et al. 2021;Pape et al. 2021;Sanchez et al. 2022). The latter will be lost for the nodule-obligate biota following PMN extraction (Amon et al. 2016). In addition, sediment plumes of returned mining fines or collector-generated, whirled-up seafloor sediments have been modelled to travel well beyond the actual mining block (e.g. ...
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... Although areas of potentially commercially viable nodule abundances are known, commercial extraction has yet to commence, though experimental works with nodule-gathering vehicles and on investigating the potential disturbance impacts on seafloor structure and communities are ongoing. The topic remains controversial as it is assumed that mining will have negative impacts on the deep-sea ecosystem, at least on the local scale, with the hard substrate provided by the nodules being wholly removed from the seafloor/ ocean interface (Amon et al. 2016;Jones et al. 2017;Stratmann et al. 2018;Smith et al. 2020). In general, soft sediments form much of this interface across the abyssal plains, though in regions where polymetallic nodules occur, these nodules provide a hard substrate, creating a complex which supports a highly diverse range of sessile fauna (Vanreusel et al. 2016), as well as adding complexity to the local hydrodynamic regime on the local scale. ...
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... Although they analysed polychaetes mostly at the family level, this localscale study was able to reveal a positive significant relationship between polychaete abundance and nodule densities (supported by Bonifácio et al. 2020 but not by Washburn et al. 2021a). This positive relationship is best known for sessile mega-and macrofauna requiring hard substrate for settling (Mullineaux 1987;Vanreusel et al. 2016;Amon et al. 2016). For example, Vanreusel et al. (2016) observed mega-epifaunal densities more than twice as high in nodule-rich areas, with some taxa (e.g. ...
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