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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Mar. Sci.</journal-id>
<journal-title>Frontiers in Marine Science</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Mar. Sci.</abbrev-journal-title>
<issn pub-type="epub">2296-7745</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fmars.2025.1603902</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Marine Science</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Internal tides drive spatial variation in impact areas of deep-sea mining plumes at seamounts</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Saito</surname>
<given-names>Naoki</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<xref ref-type="author-notes" rid="fn001">
<sup>*</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/1953046/overview"/>
<role content-type="https://credit.niso.org/contributor-roles/conceptualization/"/>
<role content-type="https://credit.niso.org/contributor-roles/formal-analysis/"/>
<role content-type="https://credit.niso.org/contributor-roles/methodology/"/>
<role content-type="https://credit.niso.org/contributor-roles/writing-original-draft/"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Washburn</surname>
<given-names>Travis W.</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<xref ref-type="aff" rid="aff3">
<sup>3</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/590065/overview"/>
<role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Nagao</surname>
<given-names>Masayuki</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<role content-type="https://credit.niso.org/contributor-roles/data-curation/"/>
<role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Kamoshida</surname>
<given-names>Hiroko</given-names>
</name>
<xref ref-type="aff" rid="aff4">
<sup>4</sup>
</xref>
<role content-type="https://credit.niso.org/contributor-roles/project-administration/"/>
<role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Suzuki</surname>
<given-names>Atsushi</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/869831/overview"/>
<role content-type="https://credit.niso.org/contributor-roles/data-curation/"/>
<role content-type="https://credit.niso.org/contributor-roles/project-administration/"/>
<role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/>
</contrib>
</contrib-group>
<aff id="aff1">
<sup>1</sup>
<institution>Integrated Research Center for Nature Positive Technology, National Institute of Advanced Industrial Science and Technology (AIST)</institution>, <addr-line>Tsukuba</addr-line>,&#xa0;<country>Japan</country>
</aff>
<aff id="aff2">
<sup>2</sup>
<institution>Geological Survey of Japan, National Institute of Advanced Industrial Science and Technology (AIST)</institution>, <addr-line>Tsukuba</addr-line>,&#xa0;<country>Japan</country>
</aff>
<aff id="aff3">
<sup>3</sup>
<institution>Department of Physical and Environmental Science, Texas A&amp;M University - Corpus Christi</institution>, <addr-line>Corpus Christi, TX</addr-line>, <country>United States</country>
</aff>
<aff id="aff4">
<sup>4</sup>
<institution>Japan Organization for Metals and Energy Security (JOGMEC)</institution>, <addr-line>Tokyo</addr-line>,&#xa0;<country>Japan</country>
</aff>
<author-notes>
<fn fn-type="edited-by">
<p>Edited by: <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/127955/overview">Elva G. Escobar-Briones</ext-link>, National Autonomous University of Mexico, Mexico</p>
</fn>
<fn fn-type="edited-by">
<p>Reviewed by: <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/1243334/overview">Bo-Shian Wang</ext-link>, National Academy of Marine Research (NAMR), Taiwan</p>
<p>
<ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/946994/overview">Dongfeng Xu</ext-link>, Ministry of Natural Resources, China</p>
</fn>
<fn fn-type="corresp" id="fn001">
<p>*Correspondence: Naoki Saito, <email xlink:href="mailto:n.saito@aist.go.jp">n.saito@aist.go.jp</email>
</p>
</fn>
</author-notes>
<pub-date pub-type="epub">
<day>20</day>
<month>08</month>
<year>2025</year>
</pub-date>
<pub-date pub-type="collection">
<year>2025</year>
</pub-date>
<volume>12</volume>
<elocation-id>1603902</elocation-id>
<history>
<date date-type="received">
<day>01</day>
<month>04</month>
<year>2025</year>
</date>
<date date-type="accepted">
<day>31</day>
<month>07</month>
<year>2025</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2025 Saito, Washburn, Nagao, Kamoshida and Suzuki.</copyright-statement>
<copyright-year>2025</copyright-year>
<copyright-holder>Saito, Washburn, Nagao, Kamoshida and Suzuki</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/">
<p>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.</p>
</license>
</permissions>
<abstract>
<p>Deep-sea mining at seamounts can generate large amounts of suspended particles, or sediment plumes, which have the potential to cause environmental impacts. The physical oceanography at seamounts, including internal tides, is expected to complicate plume behavior. However, research incorporating numerical simulations to evaluate this influence is virtually nonexistent. In this study, we conducted hydrodynamic modeling and simulated dispersal and deposition of plumes across the entire seamount summit. The simulations were based on a crust excavation test conducted in 2020 and targeted suspended particles of &#x2265;30 &#x3bc;m, which accounted for the majority of the plume volume. The modeled near-bottom tidal currents at the summit were &#x2264;7 times stronger than those outside the seamount, indicating the occurrence of internal tides, with tidal current strength varying spatially across the summit. The deposition distances of plumes varied by a factor of &#x2264;6.5 (~120&#x2013;800 m), depending on the discharge location. Plumes tended to be deposited farther and in a thinner layer around sites with stronger tidal currents, whereas they were deposited closer and thicker around sites with weaker tidal currents. This study suggests that the spatial variability in tidal current strength, driven by internal tides, can alter the extent of plume dispersal and deposition by several-fold depending on the mining site. Understanding oceanographic heterogeneity within seamount summits can be crucial for assessing and mitigating the environmental impacts of mining.</p>
</abstract>
<kwd-group>
<kwd>cobalt-rich crust</kwd>
<kwd>deep-sea mining</kwd>
<kwd>environmental impact assessment</kwd>
<kwd>northwest pacific</kwd>
<kwd>REMP</kwd>
<kwd>sediment plume</kwd>
</kwd-group>
<counts>
<fig-count count="6"/>
<table-count count="1"/>
<equation-count count="0"/>
<ref-count count="44"/>
<page-count count="11"/>
<word-count count="5844"/>
</counts>
<custom-meta-wrap>
<custom-meta>
<meta-name>section-in-acceptance</meta-name>
<meta-value>Deep-Sea Environments and Ecology</meta-value>
</custom-meta>
</custom-meta-wrap>
</article-meta>
</front>
<body>
<sec id="s1" sec-type="intro">
<label>1</label>
<title>Introduction</title>
<p>The deep-sea seamounts of the Northwest Pacific are covered with cobalt-rich crusts (&#x201c;crusts&#x201d;), which are potential mineral resources and expected to be the setting for future mining. Thick crusts typically form on seamount summits at ~800&#x2013;2500 m depth (<xref ref-type="bibr" rid="B18">Hein et&#xa0;al., 2009</xref>, <xref ref-type="bibr" rid="B19">2013</xref>). To be economically feasible, approximately 260 km<sup>2</sup> of seafloor per seamount may need to be mined over a period of up to 20 years (<xref ref-type="bibr" rid="B18">Hein et&#xa0;al., 2009</xref>, <xref ref-type="bibr" rid="B19">2013</xref>). The International Seabed Authority (ISA) is currently working on developing Regional Environmental Management Plans (REMPs) in waters beyond national jurisdiction in anticipation of deep-sea mining. However, a major challenge to proper management is that the environmental impacts of mining have not been adequately studied (<xref ref-type="bibr" rid="B34">Smith et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B2">Amon et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B4">Blanchard et&#xa0;al., 2023</xref>).</p>
<p>One of the particular concerns in deep-sea mining is the environmental impact of large quantities of suspended particles, or sediment plumes. These plumes are expected to result from the movement of mining machines, excavation of crusts, and discharge of unwanted collected sediments (<xref ref-type="bibr" rid="B8">Drazen et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B35">Spearman et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B28">Peacock and Ouillon, 2023</xref>). Once released, the plumes can be dispersed and deposited near mining areas or farther away (<xref ref-type="bibr" rid="B8">Drazen et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B35">Spearman et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B28">Peacock and Ouillon, 2023</xref>). Plumes may affect biodiversity and ecosystem functions, in addition to other potential stressors such as direct habitat removal, noise, and cumulative impacts involving other human activities (<xref ref-type="bibr" rid="B17">Glover and Smith, 2003</xref>; <xref ref-type="bibr" rid="B41">Washburn et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B2">Amon et&#xa0;al., 2022</xref>).</p>
<p>Although there is an urgent need to accumulate environmental impact estimates prior to the start of mining, data on plumes generated by crust mining are extremely limited. No publicly available commercial excavator designs or operational plans exist for crust mining, making it difficult to predict the physical properties of plumes (<xref ref-type="bibr" rid="B42">Weaver et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B28">Peacock and Ouillon, 2023</xref>). A small-scale excavation test conducted at Takuyo-Daigo Seamount in 2020 is the only published case study of crust excavation (<xref ref-type="bibr" rid="B32">Saito et&#xa0;al., 2023</xref>; <xref ref-type="bibr" rid="B40">Washburn et&#xa0;al., 2023</xref>). <xref ref-type="bibr" rid="B40">Washburn et&#xa0;al. (2023)</xref> compared areas where the plume from excavation was likely deposited with areas where it was likely not and reported that densities of mobile organisms such as fish and sea cucumbers were depressed in the deposition area one year after the excavation. <xref ref-type="bibr" rid="B35">Spearman et&#xa0;al. (2020)</xref> is the only simulated case of plumes at seamounts to our knowledge, and they estimated the physical properties of the crust plume particles based on field disturbance experiments and dredging of weak, weathered rocks. Most existing studies of plumes produced by deep-sea mining focus on the mining of manganese nodules (&#x201c;nodules&#x201d;) in the abyssal plains of the eastern Pacific (i.e., Clarion-Clipperton Zone) (<xref ref-type="bibr" rid="B30">Rolinski et&#xa0;al., 2001</xref>; <xref ref-type="bibr" rid="B1">Aleynik et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B16">Gillard et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B29">Purkiani et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B26">Mu&#xf1;oz-Royo et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B13">Gazis et&#xa0;al., 2025</xref>), with limited attention to crust mining at seamounts. Simulations in these studies have shown the influence of relatively stable flows in the abyssal plains, generally with velocities on the order of 1 cm/s (<xref ref-type="bibr" rid="B1">Aleynik et&#xa0;al., 2017</xref>), on plume dispersion and deposition.</p>
<p>Despite a dearth of evidence, there has been speculation of the importance of complex flow fields at seamounts on plume behavior. Seamounts act as obstacles to passing flows, disturbing the ocean interior. As a result, seamounts cause spatial variations in the flow field, both locally and globally, ranging from turbulent scales to scales of tens of kilometers or more (<xref ref-type="bibr" rid="B12">Garrett, 2003</xref>; <xref ref-type="bibr" rid="B3">Baines, 2007</xref>; <xref ref-type="bibr" rid="B24">Lavelle and Mohn, 2010</xref>). Thus, the relationship between flow and plume behavior in seamount mining is expected to be much more complex than that in nodule mining in the relatively flat abyssal plains (<xref ref-type="bibr" rid="B35">Spearman et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B28">Peacock and Ouillon, 2023</xref>).</p>
<p>Internal tides may be a particularly important physical oceanographic feature influencing the transport of suspended sediments at seamounts. Seamounts impede the progress of tidal waves and convert some of the tidal energy into oscillations of internal isopycnal surfaces, or internal tides (<xref ref-type="bibr" rid="B12">Garrett, 2003</xref>; <xref ref-type="bibr" rid="B3">Baines, 2007</xref>; <xref ref-type="bibr" rid="B24">Lavelle and Mohn, 2010</xref>). Internal tides strengthen tidal currents on seamount summits several times more than those in the open ocean, and velocities can be on the order of 10 cm/s (<xref ref-type="bibr" rid="B15">Genin et&#xa0;al., 1989</xref>; <xref ref-type="bibr" rid="B11">Eriksen, 1991</xref>). The only previous plume simulation conducted at a seamount (<xref ref-type="bibr" rid="B35">Spearman et&#xa0;al., 2020</xref>) found that internal tides may have a dominant effect on the direction and distance of plume dispersion. However, in that simulation, the plume was discharged from only one location on the seamount. Crust mining is expected to cover approximately 20% (~260 km<sup>2</sup>) of the average surface area of seamounts shallower than 2500 m depth (<xref ref-type="bibr" rid="B18">Hein et&#xa0;al., 2009</xref>). Thus, simulations over a wide area of the seamount summit are needed to understand the interaction of the plume with the physical oceanography of the entire seamount.</p>
<p>This study explored the potential effects of internal tides on plume dispersion and deposition across the entire summit of a seamount. The target seamount, Scripps Guyot, is considered a potential mining site (<xref ref-type="bibr" rid="B20">International Seabed Authority, 2024</xref>). Hydrodynamic modeling was conducted to characterize the tidal currents around the seamount. The model was validated using <italic>in situ</italic> flow observations from three sites. Based on this model, plume discharges from different points across the seamount summit were simulated. Plume properties and mining operations were set based on measurements from small-scale crust excavation test conducted in 2020 (<xref ref-type="bibr" rid="B32">Saito et&#xa0;al., 2023</xref>; <xref ref-type="bibr" rid="B40">Washburn et&#xa0;al., 2023</xref>). This study focuses on plume dynamics during the phase being passively transported by ocean currents, after moving away from the immediate vicinity of the excavator (<xref ref-type="bibr" rid="B28">Peacock and Ouillon, 2023</xref>). The purpose of this study is to fill a fundamental gap in physical oceanographic knowledge concerning sediment plumes and to contribute to the development of environmental management plans at seamounts.</p>
</sec>
<sec id="s2" sec-type="materials|methods">
<label>2</label>
<title>Materials and methods</title>
<sec id="s2_1">
<label>2.1</label>
<title>Study area</title>
<p>The Scripps Guyot has a nearly flat top at a depth of ~1200&#x2013;1500 m and rises approximately 4000 m above the surrounding abyssal plain (<xref ref-type="fig" rid="f1">
<bold>Figures&#xa0;1A, B</bold>
</xref>). The summit extends 40 km in the north-south direction and 25 km in the east-west direction. The Japan Organization for Metals and Energy Security (JOGMEC) was issued an exploration contract for the area by the ISA (<xref ref-type="bibr" rid="B20">International Seabed Authority, 2024</xref>). In this study, the seamount summit was defined as the seafloor at a depth of &#x2264;1500 m with a slope of less than 2&#xb0;, as calculated using QGIS (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Figure S1</bold>
</xref>).</p>
<fig id="f1" position="float">
<label>Figure&#xa0;1</label>
<caption>
<p>Study area. <bold>(A, B)</bold> show the map of the Scripps Guyot. In <bold>(B)</bold>, black points indicate observation sites. <bold>(C)</bold> shows observation depth at each site. In <bold>(C)</bold>, orange bars indicate single point current meters, blue triangles indicate ADCPs, and blue bars indicate ADCP observation layers.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-12-1603902-g001.tif">
<alt-text content-type="machine-generated">Map and diagram showing ocean depth and instrument placement. (A) Regional map with bathymetry, depth from 1000 to 6000 meters. (B) Detailed bathymetry of a seamount with labeled summit, slope, and base. (C) Depth profiles with symbols indicating ADCP instruments and current meters at summit, slope, and base locations.</alt-text>
</graphic>
</fig>
</sec>
<sec id="s2_2">
<label>2.2</label>
<title>Hydrodynamic modeling</title>
<p>Modeling around the seamount was carried out using the numerical model Delft3D (<xref ref-type="bibr" rid="B7">Deltares, 2022</xref>). The mathematical principle of Delft3D is to solve the Reynolds-averaged Navier-Stokes equations for incompressible fluids using finite difference methods. The model was set to be three-dimensional and hydrostatic. Turbulent processes were modeled based on eddy viscosity. The vertical eddy viscosity and eddy diffusion coefficients were calculated using the <italic>k-&#x3f5;</italic> model, a method that derives turbulent kinetic energy <italic>k</italic> and turbulent kinetic energy dissipation rate <italic>&#x3f5;</italic> obtained from the transport equations (<xref ref-type="bibr" rid="B7">Deltares, 2022</xref>).</p>
<p>The model area was 4.2&#xb0; &#xd7; 4.4&#xb0; (157.3&#x2013;161.5&#xb0; E, 21.6&#x2013;26.0&#xb0; N) and the area near the seamount (158.6&#x2013;160.0&#xb0; E, 23.15&#x2013;24.4&#xb0; N) was increased in resolution by two-way nesting (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Figure S2</bold>
</xref>). The horizontal resolution was set to <inline-formula>
<mml:math display="inline" id="im1">
<mml:mrow>
<mml:mi>&#x394;</mml:mi>
<mml:mi>x</mml:mi>
</mml:mrow>
</mml:math>
</inline-formula> = <inline-formula>
<mml:math display="inline" id="im2">
<mml:mrow>
<mml:mi>&#x394;</mml:mi>
<mml:mi>y</mml:mi>
</mml:mrow>
</mml:math>
</inline-formula> = 1/50&#xb0; (&#x2248; 2.2 km) in the outer region and <inline-formula>
<mml:math display="inline" id="im3">
<mml:mrow>
<mml:mi>&#x394;</mml:mi>
<mml:mi>x</mml:mi>
</mml:mrow>
</mml:math>
</inline-formula> = <inline-formula>
<mml:math display="inline" id="im4">
<mml:mrow>
<mml:mi>&#x394;</mml:mi>
<mml:mi>y</mml:mi>
</mml:mrow>
</mml:math>
</inline-formula> = 1/250&#xb0; (&#x2248; 0.44 km) in the inner region. The vertical resolution was set at 36 layers in the Z-coordinate system, extending from the surface to the abyssal plain of 5500 m depth (see <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Figure S3</bold>
</xref> for details). The finest vertical resolution was <inline-formula>
<mml:math display="inline" id="im5">
<mml:mrow>
<mml:mi>&#x394;</mml:mi>
<mml:mi>z</mml:mi>
</mml:mrow>
</mml:math>
</inline-formula> = 27.5 m directly above the summit seafloor and the coarsest resolution was <inline-formula>
<mml:math display="inline" id="im6">
<mml:mrow>
<mml:mi>&#x394;</mml:mi>
<mml:mi>z</mml:mi>
</mml:mrow>
</mml:math>
</inline-formula> = 440 m directly above the abyssal plain. The calculation target period spanned 15 days, from December 1 to December 15, 2019. The time step was set at 0.6 minutes. The target period was preceded by a 10-day spin-up period, resulting in a total calculation period from November 21 to December 15, 2019.</p>
<p>The model focused on tidal currents, with the main forcing provided by the tides at the open boundaries. Note that this model does not include the effects of background baroclinic currents and mesoscale eddies. To avoid model complexity, tidal components were calculated only for M2 (semi-diurnal) and K1 (diurnal), which are more dominant than inertial oscillation components in field flow measurements at the summit (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Figure S4</bold>
</xref>, see below for observation details). The tidal levels for the open boundary conditions were taken from the tidal model TPXO9-atlas (1/30&#xb0; resolution) (<xref ref-type="bibr" rid="B10">Egbert and Erofeeva, 2002</xref>). In addition, Delft3D was configured to include tide generating forces at open boundaries, incorporating the contribution of gravitational forces to the motion of large water masses in the deep sea (<xref ref-type="bibr" rid="B7">Deltares, 2022</xref>). The direction of tidal waves propagating over the model area was predominantly from west-northwest to east-southeast (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Figure S5</bold>
</xref>). To weaken the reflection of waves propagating from the inside of the model to the boundary, a reflection parameter <inline-formula>
<mml:math display="inline" id="im7">
<mml:mrow>
<mml:mi>&#x3b1;</mml:mi>
<mml:mo>=</mml:mo>
<mml:mi>T</mml:mi>
<mml:msqrt>
<mml:mrow>
<mml:mi>H</mml:mi>
<mml:mo stretchy="false">/</mml:mo>
<mml:mi>g</mml:mi>
</mml:mrow>
</mml:msqrt>
</mml:mrow>
</mml:math>
</inline-formula> was set at the western and southern lateral boundaries, where <italic>T</italic> is the time it takes for a free surface wave to travel from one open boundary to the boundary in the opposite direction, <italic>H</italic> is the water depth, and <italic>g</italic> is the gravitational acceleration. Multiplying <inline-formula>
<mml:math display="inline" id="im8">
<mml:mi>&#x3b1;</mml:mi>
</mml:math>
</inline-formula> by the time derivative of the Riemann invariant and adding it to the water level resulted in the water surface boundary condition <inline-formula>
<mml:math display="inline" id="im9">
<mml:mrow>
<mml:msub>
<mml:mi>F</mml:mi>
<mml:mrow>
<mml:mi>&#x3b6;</mml:mi>
<mml:mo>&#xa0;</mml:mo>
</mml:mrow>
</mml:msub>
<mml:mo stretchy="false">(</mml:mo>
<mml:mi>t</mml:mi>
<mml:mo stretchy="false">)</mml:mo>
</mml:mrow>
</mml:math>
</inline-formula>. That is, <inline-formula>
<mml:math display="inline" id="im10">
<mml:mrow>
<mml:msub>
<mml:mi>F</mml:mi>
<mml:mrow>
<mml:mi>&#x3b6;</mml:mi>
<mml:mo>&#xa0;</mml:mo>
</mml:mrow>
</mml:msub>
<mml:mo stretchy="false">(</mml:mo>
<mml:mi>t</mml:mi>
<mml:mo stretchy="false">)</mml:mo>
<mml:mo>=</mml:mo>
<mml:mi>&#x3b6;</mml:mi>
<mml:mo>+</mml:mo>
<mml:mi>&#x3b1;</mml:mi>
<mml:mfrac>
<mml:mo>&#x2202;</mml:mo>
<mml:mrow>
<mml:mo>&#x2202;</mml:mo>
<mml:mi>t</mml:mi>
</mml:mrow>
</mml:mfrac>
<mml:mo>{</mml:mo>
<mml:mi>U</mml:mi>
<mml:mo>&#xb1;</mml:mo>
<mml:mn>2</mml:mn>
<mml:msqrt>
<mml:mrow>
<mml:mi>g</mml:mi>
<mml:mi>H</mml:mi>
</mml:mrow>
</mml:msqrt>
<mml:mo>}</mml:mo>
</mml:mrow>
</mml:math>
</inline-formula>, where <inline-formula>
<mml:math display="inline" id="im11">
<mml:mi>&#x3b6;</mml:mi>
</mml:math>
</inline-formula> is the free surface elevation above the still water level, and <italic>U</italic> is the horizontal velocity (<xref ref-type="bibr" rid="B7">Deltares, 2022</xref>).</p>
<p>Water temperature and salinity for initial and open boundary conditions were taken from <italic>in situ</italic> CTD data at the base observation site (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1B</bold>
</xref>). CTD profiles, from the surface to a depth of ~5200 m, were obtained from 7:00 to 12:00 on October 24, 2019, by vertically deploying an SBE 911 plus (Sea-Bird Scientific) from the research vessel, with a measurement interval of 1 m. Meteorological conditions, i.e., air temperature, relative humidity, fraction cloud coverage, and net solar radiation, were obtained from the meteorological reanalysis data NCEP/NCAR Reanalysis 1 (2.5&#xb0; resolution) (<xref ref-type="bibr" rid="B22">Kalnay et&#xa0;al., 1996</xref>) and used to calculate heat fluxes between the atmosphere and sea surface. Topographic data were obtained from the GEBCO 2022 Grid (1/240&#xb0; resolution) (<xref ref-type="bibr" rid="B14">GEBCO Compilation Group, 2022</xref>). In order to focus specifically on the interaction between the topography of Scripps Guyot and flow, convex topography was removed from the model domain outside Scripps Guyot and two small adjacent seamounts (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1B</bold>
</xref>). Topography was smoothed by a moving average of 10 neighboring cells.</p>
<p>Modeled tidal currents were validated by comparison of modeled results with <italic>in situ</italic> flow observations from mooring systems at three sites: the summit, slope, and base (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1B</bold>
</xref>). A total of 13 single point current meters (DW-Aquadopp, Nortek AS) and two 75 kHz acoustic Doppler current profilers (ADCPs) (WorkHorse, Teledyne RD Instruments) were installed. The instruments and observed depths for each site are illustrated in <xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1C</bold>
</xref>. The observation period was from October 21, 2019 to August 11, 2020. The measurement interval was one hour for both instruments. There were 30 observation layers for ADCPs, each with a thickness of 20 m. The accuracies of both instruments were &#xb1; 0.5 cm/s. For more details on field flow observations, see <xref ref-type="bibr" rid="B31">Saito et&#xa0;al. (2024)</xref>. In the observations and model results, the tidal ellipses, which represent the amplitudes and directions of the tidal currents by their magnitude and orientation, were determined by the analysis package UTide for Python (<xref ref-type="bibr" rid="B5">Codiga, 2011</xref>).</p>
</sec>
<sec id="s2_3">
<label>2.3</label>
<title>Plume simulation</title>
<p>The physical properties of the plume from modeled mining operations were set based on a small-scale crust excavation test at Takuyo-Daigo Seamount in 2020 (<xref ref-type="bibr" rid="B32">Saito et&#xa0;al., 2023</xref>; <xref ref-type="bibr" rid="B40">Washburn et&#xa0;al., 2023</xref>). In the test, the excavator was equipped with a drum cutter head and a cyclone tank for material collection. Crusts, with accompanying rocks and sediments, were collected from an area of ~100 m<sup>2</sup>. During excavation, ore and seawater were separated inside the cyclone tank, and seawater was discharged through the outlet 3.75 m above the seafloor. Fine particles, primarily composed of crustal material, were released along with seawater, forming sediment plumes near the seafloor. The discharge rate of the crust particles was estimated to be 0.022 m<sup>3</sup>/h. Seawater containing the plume was collected using Niskin bottles attached to the ROV, and the size distribution and settling velocity of the particles in the plume was determined (Suzuki et&#xa0;al., in preparation). For more details on observations of the excavation test, see <xref ref-type="bibr" rid="B32">Saito et&#xa0;al. (2023)</xref> and <xref ref-type="bibr" rid="B40">Washburn et&#xa0;al. (2023)</xref>. The discharge height, discharge speed, and particle size distribution of the plume in the excavation test were used as settings in the simulation.</p>
<p>The simulation focused on the dispersion and deposition of plume particles in the vicinity of the mining site. The modeled plume consisted of particles larger than 30 &#x3bc;m in diameter that accounted for 81% of the plume volume in samples collected during the crust excavation test (<xref ref-type="table" rid="T1">
<bold>Table&#xa0;1</bold>
</xref>). Finer particles (i.e., less than 30 &#x3bc;m), which were excluded from this study, are expected to remain suspended for longer periods and to disperse over a wider area at very low concentrations (<xref ref-type="bibr" rid="B30">Rolinski et&#xa0;al., 2001</xref>; <xref ref-type="bibr" rid="B16">Gillard et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B35">Spearman et&#xa0;al., 2020</xref>), making them difficult to observe and model. This study focused on relatively high concentrations of particles, which are of particular concern for the ecological impacts (<xref ref-type="bibr" rid="B17">Glover and Smith, 2003</xref>; <xref ref-type="bibr" rid="B41">Washburn et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B2">Amon et&#xa0;al., 2022</xref>). Four particle sizes were used for simulated discharges: 30 &#x3bc;m, 50 &#x3bc;m, 90 &#x3bc;m, and 230 &#x3bc;m (<xref ref-type="table" rid="T1">
<bold>Table&#xa0;1</bold>
</xref>), which were representative sizes of the sediment plume measured in the excavation test. Settling velocities ranged from 0.954 mm/s for 30 &#x3bc;m particles to 56.1 mm/s for 230 &#x3bc;m particles (<xref ref-type="table" rid="T1">
<bold>Table&#xa0;1</bold>
</xref>). Particles were discharged from 3.75 m above the seafloor, the location of the cyclone tank outlet. Particles were assumed to have been deposited when they settled 3.75 m below the discharge height. The effects of resuspension and of terrain features smaller than the model&#x2019;s spatial resolution were not considered. With the above setup, particles of all four sizes were always deposited within 1.09 hours of discharge. This simulation was targeted for the flat-top with slopes of 2&#xb0; or less, and the process of sliding downslope was not included. Note that these simplifying assumptions may lead to underestimation of the spatial extent of deposit thickness.</p>
<table-wrap id="T1" position="float">
<label>Table&#xa0;1</label>
<caption>
<p>Physical properties of plume particles from crust excavation.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="middle" align="center">Size (&#x3bc;m)</th>
<th valign="middle" align="center">Volume (%)</th>
<th valign="middle" align="center">Settling velocity (mm/s)</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="middle" align="center">&#x2264;8.0</td>
<td valign="middle" align="center">19.0</td>
<td valign="middle" align="center">&#x2264;0.0679</td>
</tr>
<tr>
<td valign="middle" align="center">30</td>
<td valign="middle" align="center">33.1</td>
<td valign="middle" align="center">0.954</td>
</tr>
<tr>
<td valign="middle" align="center">50</td>
<td valign="middle" align="center">16.9</td>
<td valign="middle" align="center">2.65</td>
</tr>
<tr>
<td valign="middle" align="center">90</td>
<td valign="middle" align="center">13.3</td>
<td valign="middle" align="center">8.59</td>
</tr>
<tr>
<td valign="middle" align="center">230</td>
<td valign="middle" align="center">17.7</td>
<td valign="middle" align="center">56.1</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>The values were based on measurements in the small-scale crust excavation test (<xref ref-type="bibr" rid="B32">Saito et&#xa0;al., 2023</xref>; <xref ref-type="bibr" rid="B40">Washburn et&#xa0;al., 2023</xref>). Only particles &#x2265;30 &#x3bc;m were used in the simulation.</p>
</fn>
</table-wrap-foot>
</table-wrap>
<p>The simulations were performed by Lagrangian particle tracking analysis and used the Python package Parcels (<xref ref-type="bibr" rid="B6">Delandmeter and van Sebille, 2019</xref>). The trajectories of the particles were calculated by the following equation: <inline-formula>
<mml:math display="inline" id="im12">
<mml:mrow>
<mml:mi>X</mml:mi>
<mml:mo stretchy="false">(</mml:mo>
<mml:mi>t</mml:mi>
<mml:mo>+</mml:mo>
<mml:mi>&#x394;</mml:mi>
<mml:mi>t</mml:mi>
<mml:mo stretchy="false">)</mml:mo>
<mml:mo>=</mml:mo>
<mml:mi>X</mml:mi>
<mml:mo stretchy="false">(</mml:mo>
<mml:mi>t</mml:mi>
<mml:mo stretchy="false">)</mml:mo>
<mml:mo>+</mml:mo>
<mml:msubsup>
<mml:mo>&#x222b;</mml:mo>
<mml:mi>t</mml:mi>
<mml:mrow>
<mml:mi>t</mml:mi>
<mml:mo>+</mml:mo>
<mml:mi>&#x394;</mml:mi>
<mml:mi>t</mml:mi>
</mml:mrow>
</mml:msubsup>
<mml:mi>v</mml:mi>
<mml:mo stretchy="false">(</mml:mo>
<mml:mi>x</mml:mi>
<mml:mo>,</mml:mo>
<mml:mo>&#xa0;</mml:mo>
<mml:mi>&#x3c4;</mml:mi>
<mml:mo stretchy="false">)</mml:mo>
<mml:mi>d</mml:mi>
<mml:mi>&#x3c4;</mml:mi>
<mml:mo>+</mml:mo>
<mml:mi>&#x394;</mml:mi>
<mml:msub>
<mml:mi>X</mml:mi>
<mml:mi>b</mml:mi>
</mml:msub>
<mml:mo stretchy="false">(</mml:mo>
<mml:mi>t</mml:mi>
<mml:mo stretchy="false">)</mml:mo>
<mml:mo>,</mml:mo>
</mml:mrow>
</mml:math>
</inline-formula> where <italic>X</italic> is the position of the particle, <inline-formula>
<mml:math display="inline" id="im13">
<mml:mrow>
<mml:mi>v</mml:mi>
<mml:mo stretchy="false">(</mml:mo>
<mml:mi>x</mml:mi>
<mml:mo>,</mml:mo>
<mml:mo>&#xa0;</mml:mo>
<mml:mi>&#x3c4;</mml:mi>
<mml:mo stretchy="false">)</mml:mo>
</mml:mrow>
</mml:math>
</inline-formula> is the three-dimensional velocity field at that location, and <inline-formula>
<mml:math display="inline" id="im14">
<mml:mrow>
<mml:mi>&#x394;</mml:mi>
<mml:msub>
<mml:mi>X</mml:mi>
<mml:mi>b</mml:mi>
</mml:msub>
<mml:mo stretchy="false">(</mml:mo>
<mml:mi>t</mml:mi>
<mml:mo stretchy="false">)</mml:mo>
</mml:mrow>
</mml:math>
</inline-formula> is a change in vertical position due to settlement. The velocity field was obtained from a hydrodynamic model, with linear interpolation applied for values finer than the model&#x2019;s spatial and temporal resolution. The focus was on particle advection, so random diffusion due to turbulence or thermal motion was not considered. The calculation time step was 1 minute. At the seamount summit, particles were discharged from a total of 604 locations spaced at 880 m intervals. Particles representing the four particle sizes were emitted from all emission points, one per hour. The simulation period was set to one week, from December 1 to December 7, 2019, covering a tidal cycle from spring tide to neap tide (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Figure S6</bold>
</xref>). Thus, a total of 672 particles were calculated for each site and 405,888 particles across all sites. As the hydrodynamic model was primarily driven by tidal forcing, the simulation results were expected to exhibit periodicity and to be free from statistical noise (see also the Results section).</p>
<p>The &#x201c;deposition distance&#x201d; was defined as the distance from the discharge point to the farthest deposited particle. The deposition thickness <italic>T</italic> for each 50 m &#xd7; 50 m area was calculated using the following equation: <inline-formula>
<mml:math display="inline" id="im15">
<mml:mrow>
<mml:mi>T</mml:mi>
<mml:mo>=</mml:mo>
<mml:msub>
<mml:mo>&#x2211;</mml:mo>
<mml:mi>s</mml:mi>
</mml:msub>
<mml:mo stretchy="false">(</mml:mo>
<mml:msub>
<mml:mi>V</mml:mi>
<mml:mi>s</mml:mi>
</mml:msub>
<mml:mo stretchy="false">/</mml:mo>
<mml:mi>A</mml:mi>
<mml:mo stretchy="false">)</mml:mo>
<mml:mo>,</mml:mo>
</mml:mrow>
</mml:math>
</inline-formula> where <italic>s</italic> is the particle size, <inline-formula>
<mml:math display="inline" id="im16">
<mml:mrow>
<mml:msub>
<mml:mi>V</mml:mi>
<mml:mi>s</mml:mi>
</mml:msub>
</mml:mrow>
</mml:math>
</inline-formula> is the volume of deposited particles of size <italic>s</italic>, and <italic>A</italic> is the area of 50 m &#xd7; 50 m. The volume of particles of each size released per hour, <inline-formula>
<mml:math display="inline" id="im17">
<mml:mrow>
<mml:msub>
<mml:mi>v</mml:mi>
<mml:mi>s</mml:mi>
</mml:msub>
</mml:mrow>
</mml:math>
</inline-formula>, was determined by: <inline-formula>
<mml:math display="inline" id="im18">
<mml:mrow>
<mml:msub>
<mml:mi>v</mml:mi>
<mml:mi>s</mml:mi>
</mml:msub>
<mml:mo>=</mml:mo>
<mml:mi>v</mml:mi>
<mml:mo>&#xd7;</mml:mo>
<mml:mo stretchy="false">(</mml:mo>
<mml:msub>
<mml:mi>P</mml:mi>
<mml:mi>s</mml:mi>
</mml:msub>
<mml:mo stretchy="false">/</mml:mo>
<mml:mn>100</mml:mn>
<mml:mo stretchy="false">)</mml:mo>
</mml:mrow>
</mml:math>
</inline-formula>, where <italic>v</italic> is the plume emission rate of 0.022 m<sup>3</sup>/h from the excavation test (<xref ref-type="bibr" rid="B32">Saito et&#xa0;al., 2023</xref>; <xref ref-type="bibr" rid="B40">Washburn et&#xa0;al., 2023</xref>), and <inline-formula>
<mml:math display="inline" id="im19">
<mml:mrow>
<mml:msub>
<mml:mi>P</mml:mi>
<mml:mi>s</mml:mi>
</mml:msub>
</mml:mrow>
</mml:math>
</inline-formula> is the percentage of the plume volume for each particle size. For example, particles of 30 &#x3bc;m, which accounted for 33.1% of the plume volume, had a calculated emission rate of <inline-formula>
<mml:math display="inline" id="im20">
<mml:mrow>
<mml:msub>
<mml:mi>v</mml:mi>
<mml:mi>s</mml:mi>
</mml:msub>
</mml:mrow>
</mml:math>
</inline-formula> = 0.0073 m<sup>3</sup>/h.</p>
</sec>
</sec>
<sec id="s3" sec-type="results">
<label>3</label>
<title>Results</title>
<sec id="s3_1">
<label>3.1</label>
<title>Characteristics of tidal currents</title>
<p>Modeled tidal currents were stronger over the seamount summit compared to the surrounding area (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2</bold>
</xref>), indicating the occurrence of internal tides (<xref ref-type="bibr" rid="B3">Baines, 2007</xref>; <xref ref-type="bibr" rid="B24">Lavelle and Mohn, 2010</xref>) here. At 3.75 m above the seafloor, which corresponds to the plume discharge depth, the tidal currents at the summit were &#x2264;7 times stronger than those outside the seamount.</p>
<fig id="f2" position="float">
<label>Figure&#xa0;2</label>
<caption>
<p>Modeled tidal current strengths over the seamount summit. Colors indicate the amplitude of the tidal current at 3.75 m above the seafloor, corresponding to the plume discharge depth. <bold>(A)</bold> shows the semi-diurnal M2 component and <bold>(B)</bold> shows the diurnal K1 component. Topographic contours are at intervals of 1000 m for thick lines and 100 m for thin lines.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-12-1603902-g002.tif">
<alt-text content-type="machine-generated">Maps showing tidal amplitude around a seamount at 23.5 to 24.0 degrees north latitude and 159.2 to 159.5 degrees east longitude. Panel A displays semidiurnal (M2) tides, and Panel B shows diurnal (K1) tides. Color gradients represent amplitude in centimeters per second, ranging from blue to red, with a scale bar indicating 10 kilometers.</alt-text>
</graphic>
</fig>
<p>Tidal current strengths were uneven across the summit. At 3.75 m above the seafloor, the amplitude of M2 tidal currents varied by &#x2264;9.6 times (ranging from 0.5 cm/s to 4.8 cm/s), while the amplitude of the K1 tidal currents varied by &#x2264;8.0 times (ranging from 0.4 cm/s to 3.6 cm/s) within the summit. The tidal currents were strongest at the northern tip of the summit for both M2 and K1. The distribution patterns of the tidal current strength differed between M2 and K1. The M2 tidal currents were relatively stronger (&gt;3 cm/s) at the western edge of the summit, whereas K1 tidal currents were relatively stronger (&gt;2 cm/s) at the center of the summit.</p>
<p>The modeled tidal currents were validated by comparing them with field observations. For both M2 and K1 tidal components, field observations showed that the tidal currents were &#x2264;4.1 times stronger at &#x2264;200 m above the seafloor at the summit than in other areas, and the model was able to reproduce this trend (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3</bold>
</xref>). At 1100 m depth, the difference in tidal current amplitude between the model and observations was less than 1.0 cm/s for both the M2 and K1 (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Tables S1, S2</bold>
</xref>). The modeled M2 amplitude (2.2 &#xb1; 0.06 cm/s, &#xb1; indicates 95% confidence interval) was 0.1 cm/s larger than the field observation value (2.1 &#xb1; 0.1 cm/s), while the modeled K1 amplitude (2.2 &#xb1; 0.1 cm/s) exceeded the field observation value (1.4 &#xb1; 0.1 cm/s) by 0.8 cm/s. The difference between the model and the field observations for the direction of the maximum tidal current was within ~30&#xb0; for both M2 and K1. The difference was 5.7&#xb0;for M2 (model: 169.9 &#xb1; 2.6&#xb0;, observation: 164.2 &#xb1; 7.1&#xb0;) and 31.1&#xb0;for K1 (model: 47.8 &#xb1; 9.1&#xb0;, observation: 16.7 &#xb1; 65.2&#xb0;).</p>
<fig id="f3" position="float">
<label>Figure&#xa0;3</label>
<caption>
<p>Comparison of tidal currents between the model and <italic>in situ</italic> observations. Tidal current ellipses are shown for each site and depth, where the size represents tidal current strength, and the orientation represents current direction. <bold>(A, B)</bold> show semi-diurnal M2 and diurnal K1 components from <italic>in situ</italic> observations, and <bold>(C, D)</bold> show the corresponding model results. See <xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1B</bold>
</xref> for locations of summit, slope, and base observation sites.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-12-1603902-g003.tif">
<alt-text content-type="machine-generated">Four panels showing ocean current profiles with depth in meters on the y-axis and labeled Summit, Slope, and Base. Panels A and C depict M2 observations and models in blue, while panels B and D show K1 observations and models in red. A scale bar indicates current speed at 5 centimeters per second. A gray area at the bottom indicates the terrain profile.</alt-text>
</graphic>
</fig>
</sec>
<sec id="s3_2">
<label>3.2</label>
<title>Plume dispersal and deposition</title>
<p>Deposition distances varied by a factor of &#x2264;6.5 depending on the particle discharge points, ranging from 122 m to 798 m (<xref ref-type="fig" rid="f4">
<bold>Figures&#xa0;4</bold>
</xref>, <xref ref-type="fig" rid="f5">
<bold>5</bold>
</xref>). The average deposition distance among all the discharge points was 346 m, with a standard deviation (SD) of 121 m. The median was nearly identical at 347 m. The deposition distances corresponded to the tidal current strength at the discharge points. Longer deposition distances occurred at the northern tip, where both M2 and K1 were strong (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2</bold>
</xref>). Short deposition distances occurred predominantly from the eastern margin, where both M2 and K1 were weak (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2</bold>
</xref>). The deposition distances were highly correlated with M2 (<italic>R</italic> = 0.77; <italic>p</italic> &lt; 0.001) and K1 (<italic>R</italic> = 0.66; <italic>p</italic> &lt; 0.001) amplitudes. Due to the periodicity of the tidal currents, particles were deposited in an elliptical region centered on each discharge point (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;5</bold>
</xref>), with no particles deposited at exceptionally distant locations that could introduce statistical noise.</p>
<fig id="f4" position="float">
<label>Figure&#xa0;4</label>
<caption>
<p>The distance of the farthest deposited plume particles from each discharge location. Each point represents one of the 604 discharge locations across the summit, with colors indicating the deposition distance. Redder colors indicate a greater distance of deposition for the particles released at that location. Sites <bold>(A&#x2013;D)</bold> represent the locations illustrated in <xref ref-type="fig" rid="f5">
<bold>Figures&#xa0;5</bold>
</xref> and <xref ref-type="fig" rid="f6">
<bold>6</bold>
</xref>.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-12-1603902-g004.tif">
<alt-text content-type="machine-generated">Contour map of a geographic area marked with points labeled A, B, C, and D. Colors represent deposition distances from 100 to 800 meters. Latitude and longitude coordinates are shown alongside contour lines indicating elevation. A color bar on the right provides the scale for deposition distances.</alt-text>
</graphic>
</fig>
<fig id="f5" position="float">
<label>Figure&#xa0;5</label>
<caption>
<p>Examples of simulated dispersion trajectories of plume particles. Results are shown for the smallest particle size in the simulation, 30 &#x3bc;m. Each panel shows the results for sites <bold>(A&#x2013;D)</bold> in <xref ref-type="fig" rid="f4">
<bold>Figure&#xa0;4</bold>
</xref>. Black stars indicate plume discharge points, light blue lines indicate dispersion trajectories, and blue circles indicate deposition points.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-12-1603902-g005.tif">
<alt-text content-type="machine-generated">Four scatter plots labeled A to D show deposition points around a central discharge point, marked with a star, on W-E and S-N distance axes in meters. Blue lines indicate trajectories from the discharge point to deposition points, marked by circles. St. A and St. B show widespread patterns, St. C has a more concentrated pattern, and St. D shows a compact pattern. Legend indicates symbols for discharge point, trajectory, and deposition point.</alt-text>
</graphic>
</fig>
<p>Plumes dispersed farther and resulted in thinner depositional layers at discharge points with stronger tidal currents, while being closer and thicker at discharge points with weaker tidal currents (<xref ref-type="fig" rid="f6">
<bold>Figure&#xa0;6</bold>
</xref>). At the site with the maximum tidal currents (<xref ref-type="fig" rid="f6">
<bold>Figure&#xa0;6A</bold>
</xref>), the depositional thickness was &#x2264;0.31 mm within 50 m from the plume discharge points, &#x2264;0.045 mm at 50&#x2013;150 m, and &#x2264;0.0087 mm beyond 150 m. In contrast, at the site with the weakest tidal currents (<xref ref-type="fig" rid="f6">
<bold>Figure&#xa0;6D</bold>
</xref>), the depositional thickness nearly doubled, with &#x2264;0.57 mm within 50 m from the discharge points, &#x2264;0.074 mm at 50&#x2013;150 m, and no deposition occurred beyond 119 m.</p>
<fig id="f6" position="float">
<label>Figure&#xa0;6</label>
<caption>
<p>Examples of simulated deposition thickness of plume particles. The center of each panel is the plume discharge point. Redder colors indicate thicker deposition in that area. Each panel shows the results for sites <bold>(A&#x2013;D)</bold> in <xref ref-type="fig" rid="f4">
<bold>Figure&#xa0;4</bold>
</xref>.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-12-1603902-g006.tif">
<alt-text content-type="machine-generated">Four contour maps labeled (A) St. A, (B) St. B, (C) St. C, and (D) St. D show deposition thickness in a range of colors from dark blue (lowest) to red (highest). The maps illustrate deposition across south-north and west-east distances. A color scale on the right indicates deposition thickness from 0.00 to 0.30 millimeters.</alt-text>
</graphic>
</fig>
<p>Relatively coarse particles (&#x2265;90 &#x3bc;m) were deposited within ~7 minutes (<xref ref-type="table" rid="T1">
<bold>Table&#xa0;1</bold>
</xref>), forming thicker sediment layers (&#x2265;0.3 mm) within ~50 m of all discharge points. The finer the particles, the longer they remained in suspension, leading to greater variation in deposition distances among the discharge points (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Figure S7</bold>
</xref>). For 230 &#x3bc;m particles, the difference between maximum and minimum deposition was 30 m, whereas for 30 &#x3bc;m particles, it was 676 m (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S3</bold>
</xref>). The SD of deposition distance was only 5 m for 230 &#x3bc;m particles but 121 m for 30 &#x3bc;m particles. The average deposition distances per particle size were 15&#xa0;m for the 230 &#x3bc;m particles, 47 m (SD = 16 m) for the 90 &#x3bc;m particles, 131 m (SD = 44 m) for the 50 &#x3bc;m particles, and 346 m for the 30 &#x3bc;m particles.</p>
</sec>
</sec>
<sec id="s4" sec-type="discussion">
<label>4</label>
<title>Discussions</title>
<p>The modeled tidal currents at the seamount summit were &#x2264;7 times stronger than those in other areas (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2</bold>
</xref>), indicating the occurrence of internal tides (<xref ref-type="bibr" rid="B3">Baines, 2007</xref>; <xref ref-type="bibr" rid="B24">Lavelle and Mohn, 2010</xref>). The tidal current strengths exhibited spatial variability across the summit (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2</bold>
</xref>). Model validation against field observations showed a difference of less than 1.0 cm/s in tidal current amplitude (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Tables S1, S2</bold>
</xref>). The deposition distance of simulated plumes varied by a factor of &#x2264;6.5 among discharge points (<xref ref-type="fig" rid="f4">
<bold>Figure&#xa0;4</bold>
</xref>) and was positively correlated with tidal current strengths. At sites with stronger tidal currents, the plume was deposited farther (up to 800 m) as thinner layers, while at sites with weaker tidal currents, deposition occurred closer (as little as 120 m) and thicker (<xref ref-type="fig" rid="f5">
<bold>Figures&#xa0;5</bold>
</xref>, <xref ref-type="fig" rid="f6">
<bold>6</bold>
</xref>). These results suggest that the extent of plume dispersion and deposition at seamounts may vary by several times, depending on the local tidal current strength at the mining site.</p>
<p>Spatial variability of flows on relatively small scales, a few to tens of kilometers, has received little attention in previous studies of deep-sea mining plumes. This is partly because much of the previous research concentrated on nodule mining in the abyssal plains, considered the first deep-sea mineral resource to be exploited (<xref ref-type="bibr" rid="B2">Amon et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B4">Blanchard et&#xa0;al., 2023</xref>). In these environments, flow patterns are relatively homogenous over large spatial scales (hundreds of kilometers) compared to seamounts (<xref ref-type="bibr" rid="B1">Aleynik et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B28">Peacock and Ouillon, 2023</xref>). Previous studies of nodule mining plumes focused on regional or global physical oceanographic processes, such as those associated with El Ni&#xf1;o and La Ni&#xf1;a (<xref ref-type="bibr" rid="B30">Rolinski et&#xa0;al., 2001</xref>) and mesoscale eddies (<xref ref-type="bibr" rid="B1">Aleynik et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B16">Gillard et&#xa0;al., 2019</xref>). On the other hand, our findings emphasize that physical oceanographic processes with smaller spatial scales, including internal tides, can also be important for crust mining. Thus, to properly assess and predict the environmental impacts of the plumes generated by crust mining, it is likely insufficient to simply extrapolate from knowledge of nodule mining plumes.</p>
<p>Differences in plume dispersal and deposition between sites may warrant consideration when assessing the habitats affected by crust mining. Seamounts are heterogeneous habitats where benthic organisms are patchily distributed at scales of ~100 m (<xref ref-type="bibr" rid="B25">McClain et&#xa0;al., 2010</xref>; <xref ref-type="bibr" rid="B33">Shen et&#xa0;al., 2021</xref>). Therefore, differences in plume deposition distances of a few hundred meters, as shown in this study (<xref ref-type="fig" rid="f4">
<bold>Figure&#xa0;4</bold>
</xref>), can alter the affected communities and species composition. The environmental impact assessment of the small-scale crust excavation test (<xref ref-type="bibr" rid="B40">Washburn et&#xa0;al., 2023</xref>) reported a decline in organisms within and near the plume deposition area over scales of 10 to 100 m, underscoring the importance of survey design for proper assessment. Based on this study, the area examined for environmental impact assessments may need to be larger at mining sites with relatively strong tidal currents. Very little is currently known about the threshold for the suspended concentrations and deposition thicknesses of plume at which deep-sea organisms are damaged (<xref ref-type="bibr" rid="B36">Stenvers et&#xa0;al., 2023</xref>). However, given the naturally low levels of suspended solids concentrations and slow sedimentation rates on the deep-sea floor, even small increases in them may impact organisms (<xref ref-type="bibr" rid="B17">Glover and Smith, 2003</xref>; <xref ref-type="bibr" rid="B41">Washburn et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B2">Amon et&#xa0;al., 2022</xref>). The plumes simulated in this study were deposited on the order of 0.1 mm per week in areas &gt;50 m from the discharge sites (<xref ref-type="fig" rid="f5">
<bold>Figure&#xa0;6</bold>
</xref>), which is tens to thousands of times faster than the natural sedimentation rate at seamount summits in the Northwest Pacific (11.4 &#xb1; 7.9 mm/kyr) (<xref ref-type="bibr" rid="B27">Ota et&#xa0;al., 2022</xref>).</p>
<p>The role of internal tides in material transport at seamount summits has also been highlighted in previous oceanographic and sedimentological studies. It has been suggested that the heterogeneous distribution of sediments over seamount summits reflects active nondeposition, erosion, and resuspension driven by strong tidal currents associated with internal tides (<xref ref-type="bibr" rid="B38">Turnewitsch et&#xa0;al., 2008</xref>, <xref ref-type="bibr" rid="B37">2013</xref>). Although direct comparisons between plume behavior and sediment distribution are difficult, the sedimentological field data are consistent with our finding that internal tides occurring at seamounts largely determine mass transport patterns across the entire summit of the seamount. The modeled distribution of tidal current amplitude differed between the semi-diurnal M2 component and the diurnal K1 component (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2</bold>
</xref>). These distributions were consistent with previous modeling studies of flat-topped seamounts (<xref ref-type="bibr" rid="B23">Lavelle, 2006</xref>; <xref ref-type="bibr" rid="B39">Vlasenko et&#xa0;al., 2018</xref>). The flow components that can have major influences at seamounts include tidal currents and impinging steady currents (<xref ref-type="bibr" rid="B24">Lavelle and Mohn, 2010</xref>). Between these, impinging steady currents are not included in this model, and investigating their influence on plume behavior is a future issue. However, in this study, the annual mean velocity of 0.7 cm/s observed just above the seafloor at the seamount summit (1190 m depth), which may be attributed to impinging steady currents, was much smaller than the velocities attributed to tidal currents there (M2 amplitude was 2.1 cm/s and K1 was 1.4 cm/s). This suggested that, as with field observations at other seamounts (<xref ref-type="bibr" rid="B15">Genin et&#xa0;al., 1989</xref>; <xref ref-type="bibr" rid="B11">Eriksen, 1991</xref>), tidal currents may have a much larger influence on local current strength than impinging steady currents at the seamount summit targeted in this study.</p>
<p>Given the current uncertainty regarding the details involved with commercial mining of crusts, this study should be interpreted as a preliminary examination of the influence of physical oceanography on plume behavior at seamounts. Plume behavior is dependent on particle size, discharge speed, and discharge height, among other things, and these parameters are determined in large&#xa0;part by the mining machine design and mining operations (<xref ref-type="bibr" rid="B42">Weaver et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B28">Peacock and Ouillon, 2023</xref>). Currently, there are no publicly available crust mining plans, so their simulation must involve a certain degree of uncertainty. The simulation in this study used field measurements from small-scale excavation test (<xref ref-type="bibr" rid="B32">Saito et&#xa0;al., 2023</xref>; <xref ref-type="bibr" rid="B40">Washburn et&#xa0;al., 2023</xref>) as the best available data, but plume release rates and resulting sediment deposition in commercial mining may differ substantially. For more realistic simulations, more field data on crust mining are needed, for example, data on the numerous <italic>in situ</italic> tests in the abyssal plains simulating nodule mining (e.g., <xref ref-type="bibr" rid="B21">Jones et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B26">Mu&#xf1;oz-Royo et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B13">Gazis et&#xa0;al., 2025</xref>). Accumulating such field data would also facilitate the simulation of plume dynamics on finer scales, accounting for turbulence in the immediate vicinity of excavators (<xref ref-type="bibr" rid="B26">Mu&#xf1;oz-Royo et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B28">Peacock and Ouillon, 2023</xref>). However, despite the above limitations, the basic trends in plume deposition in this study are consistent with previous studies. In this study, the majority of the volume of plume particles was deposited in the vicinity (&#x2264;50 m) of the mining site. Similar trends were observed during the small-scale crust excavation test (<xref ref-type="bibr" rid="B40">Washburn et&#xa0;al., 2023</xref>), as well as in the only previous numerical simulation on crust mining (<xref ref-type="bibr" rid="B35">Spearman et&#xa0;al., 2020</xref>), and multiple nodule mining simulations (<xref ref-type="bibr" rid="B30">Rolinski et&#xa0;al., 2001</xref>; <xref ref-type="bibr" rid="B16">Gillard et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B29">Purkiani et&#xa0;al., 2021</xref>).</p>
<p>Investigating the influence of strong tidal currents driven by internal tides may be crucial for developing best practices in deep-sea mining that mitigate environmental impacts at seamounts. Efforts to reduce the environmental impacts of deep-sea mining have been addressed primarily through excavator design (<xref ref-type="bibr" rid="B42">Weaver et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B28">Peacock and Ouillon, 2023</xref>) and designation of environmental conservation areas (<xref ref-type="bibr" rid="B43">Wedding et&#xa0;al., 2013</xref>, <xref ref-type="bibr" rid="B44">2015</xref>; <xref ref-type="bibr" rid="B9">Dunn et&#xa0;al., 2018</xref>). However, the variation in plume dispersal and deposition areas shown in this study suggests that careful consideration of environmental conditions may help in choosing mining sites that minimize the spatial extent of environmental impacts. Mining in areas with weak tidal currents could limit plume dispersal and deposition to a relatively smaller area compared to mining in locations with strong tidal currents. In contrast, if a primary goal is to ensure a limited thickness of deposited sediments, then areas with especially weak tidal currents may need to be avoided. The results of our study also support spatial planning of mining operations to avoid ecologically sensitive zones, especially under the framework of ISA&#x2019;s REMP development. This study underscores the importance of understanding oceanographic variability within seamount summits to effectively assess and mitigate the environmental impacts of deep-sea mining.</p>
</sec>
</body>
<back>
<sec id="s5" sec-type="data-availability">
<title>Data availability statement</title>
<p>The raw data supporting the conclusions of this article will be made available by the authors, without undue reservation.</p>
</sec>
<sec id="s6" sec-type="author-contributions">
<title>Author contributions</title>
<p>NS: Conceptualization, Formal Analysis, Methodology, Writing &#x2013; original draft. TW: Writing &#x2013; review &amp; editing. MN: Data curation, Writing &#x2013; review &amp; editing. HK: Project administration, Writing &#x2013; review &amp; editing. AS: Data curation, Project administration, Writing &#x2013; review &amp; editing.</p>
</sec>
<sec id="s7" sec-type="funding-information">
<title>Funding</title>
<p>The author(s) declare that financial support was received for the research and/or publication of this article. This project was commissioned by Japan's Ministry of Economy, Trade and Industry. This study was also supported by Integrated Research Center for Nature Positive Technology at AIST.</p>
</sec>
<ack>
<title>Acknowledgments</title>
<p>We would like to thank Professor Shinichiro Yano (Kyushu University) for guidance.</p>
</ack>
<sec id="s8" sec-type="COI-statement">
<title>Conflict of interest</title>
<p>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.</p>
</sec>
<sec id="s9" sec-type="ai-statement">
<title>Generative AI statement</title>
<p>The author(s) declare that no Generative AI was used in the creation of this manuscript.</p>
<p>Any alternative text (alt text) provided alongside figures in this article has been generated by Frontiers with the support of artificial intelligence and reasonable efforts have been made to ensure accuracy, including review by the authors wherever possible. If you identify any issues, please contact us.</p>
</sec>
<sec id="s10" sec-type="disclaimer">
<title>Publisher&#x2019;s note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
</sec>
<sec id="s11" sec-type="supplementary-material">
<title>Supplementary material</title>
<p>The Supplementary Material for this article can be found online at: <ext-link ext-link-type="uri" xlink:href="https://www.frontiersin.org/articles/10.3389/fmars.2025.1603902/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fmars.2025.1603902/full#supplementary-material</ext-link>
</p>
<supplementary-material xlink:href="DataSheet1.pdf" id="SM1" mimetype="application/pdf"/>
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