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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.2023.1110830</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Marine Science</subject>
<subj-group>
<subject>Methods</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Novel infrastructure for coral gardening and reefscaping</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Schmidt-Roach</surname>
<given-names>Sebastian</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="author-notes" rid="fn001">
<sup>*</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/772516"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Klaus</surname>
<given-names>Rebecca</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Al-Suwailem</surname>
<given-names>Abdulaziz M.</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/452284"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Prieto</surname>
<given-names>Alejandro R.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Charri&#xe8;re</surname>
<given-names>Julian</given-names>
</name>
<xref ref-type="aff" rid="aff3">
<sup>3</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/2177650"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Hauser</surname>
<given-names>Charlotte A. E.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="aff" rid="aff4">
<sup>4</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/1500571"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Duarte</surname>
<given-names>Carlos M.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="aff" rid="aff4">
<sup>4</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/135333"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Aranda</surname>
<given-names>Manuel</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/136736"/>
</contrib>
</contrib-group>
<aff id="aff1">
<sup>1</sup>
<institution>Red Sea Research Center, King Abdullah University of Science and Technology</institution>, <addr-line>Thuwal</addr-line>, <country>Saudi Arabia</country>
</aff>
<aff id="aff2">
<sup>2</sup>
<institution>Beacon Development Company, King Abdullah University of Science and Technology</institution>, <addr-line>Thuwal</addr-line>, <country>Saudi Arabia</country>
</aff>
<aff id="aff3">
<sup>3</sup>
<institution>Studio Julian Charri&#xe8;re</institution>, <addr-line>Berlin</addr-line>, <country>Germany</country>
</aff>
<aff id="aff4">
<sup>4</sup>
<institution>Computational Bioscience Research Center (CBRC), King Abdullah University of Science and Technology</institution>, <addr-line>Thuwal</addr-line>, <country>Saudi Arabia</country>
</aff>
<author-notes>
<fn fn-type="edited-by">
<p>Edited by: Fraser Januchowski-Hartley, Independent researcher, Swansea, United Kingdom</p>
</fn>
<fn fn-type="edited-by">
<p>Reviewed by: Lisa Bostr&#xf6;m Einarsson, Lancaster University, United Kingdom; Jes&#xfa;s Ernesto Arias Gonz&#xe1;lez, Instituto Polit&#xe9;cnico Nacional de M&#xe9;xico (CINVESTAV), Mexico</p>
</fn>
<fn fn-type="corresp" id="fn001">
<p>*Correspondence: Sebastian Schmidt-Roach, <email xlink:href="mailto:Sebastian.schmidtroach@kaust.edu.sa">Sebastian.schmidtroach@kaust.edu.sa</email>
</p>
</fn>
<fn fn-type="other" id="fn002">
<p>This article was submitted to Coral Reef Research, a section of the journal Frontiers in Marine Science</p>
</fn>
</author-notes>
<pub-date pub-type="epub">
<day>10</day>
<month>02</month>
<year>2023</year>
</pub-date>
<pub-date pub-type="collection">
<year>2023</year>
</pub-date>
<volume>10</volume>
<elocation-id>1110830</elocation-id>
<history>
<date date-type="received">
<day>29</day>
<month>11</month>
<year>2022</year>
</date>
<date date-type="accepted">
<day>25</day>
<month>01</month>
<year>2023</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2023 Schmidt-Roach, Klaus, Al-Suwailem, Prieto, Charri&#xe8;re, Hauser, Duarte and Aranda</copyright-statement>
<copyright-year>2023</copyright-year>
<copyright-holder>Schmidt-Roach, Klaus, Al-Suwailem, Prieto, Charri&#xe8;re, Hauser, Duarte and Aranda</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>Since 1950, coral abundance has declined worldwide by an estimated 60%, and further dramatic declines are predicted. Although global reductions in carbon emissions are essential to prevent further loss, coral reef restoration has become imperative to maintain the ecosystem services that coral reefs provide to humans at local scales. Yet, currently coral restoration and gardening efforts are too expensive to scale up due to the labor-intensive nature of the methods and low success rates. Here, we present a suite of technologies that improve coral reef restoration and rehabilitation&#x2019;s scalability, efficiency, and effectiveness. Our modular technologies are designed to streamline <italic>in</italic> and <italic>ex situ</italic> nursery workflows, reduce maintenance times, solve problems in transporting corals to outplanting sites, and enable rapid outplanting on natural and artificial substrates. These novel structures can act as coral seeding hubs, which placed strategically, can have the capacity to enhance coral reproduction and replenish degraded nearby reefs with larvae. They can be applied to coral restoration and reefscaping, complemented by unique eco-friendly, low-carbon-emission structures for the creation of architecturally and visually appealing habitats and underwater landscapes. Our technologies integrate novel monitoring approaches that support intelligent solutions to track genotypes, optimize and control stock management, apply assisted evolution approaches, and adaptive management through long-term monitoring.</p>
</abstract>
<kwd-group>
<kwd>restoration</kwd>
<kwd>maritechture</kwd>
<kwd>coral nursery</kwd>
<kwd>adaptive management</kwd>
<kwd>selective propagation</kwd>
<kwd>blue architecture</kwd>
<kwd>coral seeding hubs</kwd>
</kwd-group>
<contract-sponsor id="cn001">King Abdullah University of Science and Technology<named-content content-type="fundref-id">10.13039/501100004052</named-content>
</contract-sponsor>
<counts>
<fig-count count="5"/>
<table-count count="1"/>
<equation-count count="0"/>
<ref-count count="65"/>
<page-count count="10"/>
<word-count count="5214"/>
</counts>
</article-meta>
</front>
<body>
<sec id="s1" sec-type="intro">
<label>1</label>
<title>Introduction</title>
<p>In the last 70 years live hard coral cover on coral reefs has declined by approximately 60 percent globally, which has been accompanied by a decline in the capacity of coral reefs to provide ecosystem services (<xref ref-type="bibr" rid="B17">Eddy et&#xa0;al., 2021</xref>). Even under moderate warming scenarios, a further loss of 75 to 95% of extant coral reefs is predicted by the end of this century (<xref ref-type="bibr" rid="B19">Frieler et&#xa0;al., 2013</xref>; <xref ref-type="bibr" rid="B58">van Hooidonk et&#xa0;al., 2016</xref>; <xref ref-type="bibr" rid="B28">IPCC, 2022</xref>). Increases in the frequency and severity of marine heat waves are expected to cause significant reductions in coral productivity, calcification, and survival in the next two decades (<xref ref-type="bibr" rid="B31">Klein et&#xa0;al., 2022</xref>). Therefore, substantial reductions in global carbon emissions and strict commitments to the Paris Agreement are essential to reduce a further loss (<xref ref-type="bibr" rid="B32">Kleypas et&#xa0;al., 2021</xref>). Provided the extent of realized and projected losses, coral reef restoration has become imperative to maintain the ecosystem services that coral reefs provide to humans at local scales (<xref ref-type="bibr" rid="B24">Hein et&#xa0;al., 2021</xref>). However, the biggest challenge remains implementing marine restoration efforts at scale, which are the most expensive and inefficient for coral reefs (<xref ref-type="bibr" rid="B16">Duarte et&#xa0;al., 2020</xref>). Currently, coral restoration projects are generally small, measuring only 500 m<sup>2</sup> per project in median (<xref ref-type="bibr" rid="B8">Bostr&#xf6;m-Einarsson et&#xa0;al., 2018</xref>). One of the most extensive coral restoration efforts to date was completed at Badi Island in Indonesia which involved the deployment of 7,000 m<sup>2</sup> of structures within an area of two hectares (<xref ref-type="bibr" rid="B64">Williams et&#xa0;al., 2019</xref>). However, <xref ref-type="bibr" rid="B44">Razak et&#xa0;al. (2022)</xref> describes a project in Indonesia creating up to 74.3 hectares distributed over five areas in Bali; notably with the effort of 10,000 people employed to plant nearly 96,000 units of artificial reef.</p>
<p>Unlike the culture of other marine species targeted for aquaculture, where productivity and yield have evolved over decades with dramatic technological innovations over the last 50 years, coral farming is still at the microscale due to a lack of industrial tools and difficult access to the marine environment (<xref ref-type="bibr" rid="B21">Gibbs, 2021</xref>). This contributes to the high costs associated with coral restoration, which is priced at a median of 404,147 $US ha<sup>-1</sup> (at the base year 2010) (<xref ref-type="bibr" rid="B5">Bayraktarov et&#xa0;al., 2019</xref>), with an uncertain success rate as few projects monitor survival long term beyond the time frame of the project (<xref ref-type="bibr" rid="B8">Bostr&#xf6;m-Einarsson et&#xa0;al., 2018</xref>). A recent review of patent and scientific literature data in the field of coral restoration highlighted a disconnect between technological innovation indicated by patent registrations, scientific findings and actual needs of coral restoration practitioners (<xref ref-type="bibr" rid="B47">Roch et&#xa0;al., 2023</xref>). The authors stress that research findings are often not translated into innovative and tangible management solutions. Further, market needs are not addressed by the majority of the technological innovations filed. Although the demand for coral restoration is rapidly growing, most projects are the size of a backyard, created using custom tools and solutions often specific to each project. Synthesizing the return-on-effort for the cost-effectiveness and viability of restoration efforts, <xref ref-type="bibr" rid="B52">Suggett et&#xa0;al. (2019)</xref> found no apparent change indicative of improved methodology over time. Large-scale projects demanding the implementation and driving the innovation needed for more industrial approaches and off-the-shelf solutions are still absent.</p>
<p>While restoration <italic>via</italic> transplantation on natural substrate is the most commonly practiced strategy, one-fifth of all projects create or add substratum such as artificial reefs (<xref ref-type="bibr" rid="B7">Bostr&#xf6;m-Einarsson et&#xa0;al., 2020</xref>). Artificial structures may be used for the augmentation of the reefscape to increase suitable substrates for coral transplantation, foster fish abundance <italic>via</italic> habitat creation, or tourist experiences (<xref ref-type="bibr" rid="B8">Bostr&#xf6;m-Einarsson et&#xa0;al., 2018</xref>). Working on ecosystems that are already suffering from carbon emission driven climate change and pollution, restoration efforts should aim to use environmentally friendly materials, avoid or minimize the use of plastic and target a low carbon footprint. Previously failed initiatives using old car tires for artificial reef construction, which had to be recovered at great expense (<xref ref-type="bibr" rid="B51">Sherman and Spieler, 2006</xref>), underscore the need to carefully select the materials used in reef restoration.</p>
<p>To reach ecologically meaningful scales in coral restoration, new solutions are needed to maximize efficiency in particular for marine operations. A significant bottleneck are the dive operations needed for outplanting and <italic>in situ</italic> coral bottleneck. For example, adhesion of a single coral during transplantation <italic>via</italic> epoxy takes up to ten minutes (<xref ref-type="bibr" rid="B9">Chamberland et&#xa0;al., 2017</xref>), adhesion with cement requires over five minutes per coral (<xref ref-type="bibr" rid="B57">Unsworth et&#xa0;al., 2021</xref>). One of the fastest methods for fragment attachment are the Coral clips, nails equipped with a metal clip to fixate the outplant, which require approximately one minute per coral (<xref ref-type="bibr" rid="B53">Suggett et&#xa0;al., 2020</xref>).</p>
<p>To reduce marine operations, coral aquaculture has been proposed as an ecological and economically viable solution for scalable reef restoration (<xref ref-type="bibr" rid="B11">CoralVita, 2019</xref>). To date coral aquaculture facilities are small-scale and frequently use conventional techniques such as tiles or plugs on plastic egg crates (<xref ref-type="bibr" rid="B65">Yanong, 2008</xref>; <xref ref-type="bibr" rid="B12">Craggs et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B26">Humanes et&#xa0;al., 2021</xref>). These types of facility require regular manual cleaning making maintenance of corals in nursery systems very labor-intensive. Although land-based systems are more easily accessible and, therefore, easier to maintain than <italic>in situ</italic> coral nurseries (<xref ref-type="bibr" rid="B40">O&#x2019;Neil, 2015</xref>), the workforce has been identified as the main challenge across different coral gardening methods (<xref ref-type="bibr" rid="B24">Hein et&#xa0;al., 2021</xref>). While integrating volunteers or citizen scientists can in part compensate for high workforce requirements in smaller projects (<xref ref-type="bibr" rid="B25">Hesley et&#xa0;al., 2017</xref>), commercial endeavors at scale would not be able to rely on this approach. Hence, more innovative and advanced technologies are required to streamline workflows and reduce labor-intensity to reach meaningful industrial scales of production.</p>
<p>Here we describe the first-ever modular suite of coral restoration technologies, invented specifically to simplify and increase the efficiency of critical workflows, from coral husbandary, substrate creation and outplanting. Each coral restoration technology described is inter-compatible, and can be used alone or in combination, targeting flexibility, scalability and cost effectiveness. We provide a solution for rapid reefscaping using quickly deployable artificial structures. Rethinking coral restoration efforts from an industrial scale perspective, the presented technologies are the first engineered solution with the potential to enable large scale farming operations.</p>
</sec>
<sec id="s2">
<label>2</label>
<title>Materials and equipment</title>
<p>The designs described here are registered under the trademark Maritechture&#x2122; and patented to ensure they are consistently engineered and to facilitate economies of scale at the point of production, thereby reducing the cost of each element.</p>
<sec id="s2_1">
<label>2.1</label>
<title>Screwable coral tiles</title>
<p>Maritechture&#x2122; screwable coral tiles have an internal thread that allows quick and tool free attachment to several other products outlined below in the following. Tiles are made from cement and shapes can be modified to cater for different propagation pathways, e.g. fragmentation, microfragmentation (<xref ref-type="bibr" rid="B18">Forsman et&#xa0;al., 2015</xref>) and recruitment (<xref ref-type="fig" rid="f1">
<bold>Figures&#xa0;1E, B, C</bold>
</xref>). We chose a hexagon shape for propagation of larger fragments, which allow easy screwing (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1D</bold>
</xref>). For propagation <italic>via</italic> micro-fragmentation, where a larger flatter surface is preferable, we developed a flatter hexagonal shape to promote the overgrowth of the surface (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1B</bold>
</xref>). For sexual propagation <italic>via</italic> larvae settlement, we developed a shape with multiple cavities to promote settlement. An RFID (radio frequency identification) chip can be embedded within the cement tiles, enabling long-term labelling of individual tiles (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1F</bold>
</xref>) and allowing for the identification and tracking of origin, performance and survival throughout restoration or enhancement efforts.</p>
<fig id="f1" position="float">
<label>Figure&#xa0;1</label>
<caption>
<p>Maritechture&#x2122; Screwable coral tiles (patent pending, U.S. Patent Application No. 17/767,251Filed April 7, 2022). <bold>(A)</bold> Different shapes to cater to different propagation pathways. <bold>(B)</bold> Microframentation tile. <bold>(C)</bold> Recruitment tile. <bold>(D)</bold> Fragment tile. <bold>(E)</bold> Coral tiles attached to the coral crate. <bold>(F)</bold> Trackable tiles are RFID microchipped and can be identified using a conventional chip reader, which can be operated underwater. White bar indicates 1&#xa0;cm in width.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-10-1110830-g001.tif"/>
</fig>
</sec>
<sec id="s2_2">
<label>2.2</label>
<title>Coral crates</title>
<p>Maritechture&#x2122; coral crates (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2</bold>
</xref>) are racks of durable, UV-resistant ABS plastic that allow coral tiles to be attached <italic>via</italic> threaded pins erected vertically from linear extrusions (<xref ref-type="fig" rid="f1">
<bold>Figures&#xa0;1A, B</bold>
</xref>). The design allows multiple tiles to be attached per frame, arranged in a uniform and equally spaced pattern. The crates are stackable and click into each other, creating a 10&#xa0;cm gap between each level. Each row is pre-labelled, and the crates can be equipped with RFID tags or QR codes for organization of tiles. In their current design, each unit measures 50 x 50 x 15.5&#xa0;cm and can hold up to 56 fragments. The crates have holes in their legs for horizontal connection of multiple crates, allowing, for example, the quick set-up of <italic>in situ</italic> nurseries.</p>
<fig id="f2" position="float">
<label>Figure&#xa0;2</label>
<caption>
<p>Maritechture&#x2122; Coral crate (patent pending, 63/187,218 and 29/783,128, &#x201c;Coral farm crate and methods of use thereof&#x201d; May 11, 2021). <bold>(A)</bold> Stackable coral crate. White bar indicates 10&#xa0;cm in width. <bold>(B)</bold> Coral tiles on coral frame. <bold>(C)</bold> Easy and safe transport of corals.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-10-1110830-g002.tif"/>
</fig>
</sec>
<sec id="s2_3">
<label>2.3</label>
<title>Coral outplanting/nursery devices</title>
<p>The modular tile system allows for easy attachment and removal of propagated corals by screwing and provides great flexibility for different types of coral gardening and outplanting. Maritechture&#x2122; Reef Nails (patent pending) are threaded nuts that, when combined with a standard stainless-steel concrete/masonry nail, can be easily embedded in solid reef substrates and expose a thread that matches the coral tiles (<xref ref-type="fig" rid="f3">
<bold>Figures&#xa0;3A, B</bold>
</xref>). The nut fits tightly around the nail to avoid rotation but can be secured with additional adhesives if needed. Maritechture&#x2122; Reef Wall Plugs (patent pending) have the same function but are attached with a steel screw similar to a standard wall dowel (<xref ref-type="fig" rid="f3">
<bold>Figures&#xa0;3C, D</bold>
</xref>). They allow for quick and solid attachment of coral tiles to surfaces with predrilled holes, such as artificial structures.</p>
<fig id="f3" position="float">
<label>Figure&#xa0;3</label>
<caption>
<p>Devices for different outplanting/nursery types. <bold>(A, B)</bold> Maritechture&#x2122; Reef nails for outplanting on natural substrate (patent pending) <bold>(C, D)</bold>7 Reef wall plug for outplanting on coral pods, harbor walls, etc. (patent pending) <bold>(E-H)</bold>. Tools to equip existing nurseries. <bold>(E)</bold> Clip for PCV pipe nurseries. <bold>(F)</bold> Adapter for steel/bar nurseries. <bold>(G)</bold> Adapter for aluminum frame/grid nurseries. <bold>(H)</bold> Adapter for rope nurseries. White bar indicates 5&#xa0;mm in width.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-10-1110830-g003.tif"/>
</fig>
<p>To equip existing coral gardening infrastructures with our technology, we have developed several solutions (patents pending): Maritechture&#x2122; Clips for PVC pipe nurseries [e.g., coral tree nursery&#xa9; (<xref ref-type="bibr" rid="B38">Nedimyer et&#xa0;al., 2011</xref>)(<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3E</bold>
</xref>)], Maritechture&#x2122; adapters for steel rod/metal frame nurseries (e.g. <xref ref-type="bibr" rid="B64">Williams et&#xa0;al., 2019</xref>) that can be fastened with cable ties (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3F</bold>
</xref>), Maritechture&#x2122; adapters for aluminum frame/grid nurseries (e.g. <xref ref-type="bibr" rid="B52">Suggett et&#xa0;al., 2019</xref>) that can be fastened with cable ties (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3G</bold>
</xref>), and adapters for rope nurseries (e.g. <xref ref-type="bibr" rid="B34">Levy et&#xa0;al., 2010</xref>) that can be twisted into the rope and expose two sides for tile attachment (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3H</bold>
</xref>).</p>
</sec>
<sec id="s2_4">
<label>2.4</label>
<title>Coral pods</title>
<p>To provide a stable artificial substrate for coral outplants where this is lacking, we developed Maritechture&#x2122; Coral Pods, which are limestone structures consisting of two plates that can be assembled at 90-degree angles to form a quattro pod (four-legged stand) like structure (<xref ref-type="fig" rid="f4">
<bold>Figure&#xa0;4</bold>
</xref>). Drilled holes along the top edge allow coral fragments to be attached with cable ties or Maritechture&#x2122; Reef Wall Plugs (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3C</bold>
</xref>). Additional holes in the center of the segments provide an ideal place for massive corals to be attached using our tile system. The shape and size (with individual panels approximately 145&#xa0;cm long, 47&#xa0;cm high, and 3&#xa0;cm thick) aim to minimize waste during production and allow ergonomic handling, so the weight of each limestone segment is limited to approximately 20&#xa0;kg (<xref ref-type="fig" rid="f4">
<bold>Figure&#xa0;4C</bold>
</xref>). The design provides stability in low to medium-energy environments. However, these dimensions and design (including number of stacked plates) can be adjusted depending on the available limestone slab sizes and the intended use.</p>
<fig id="f4" position="float">
<label>Figure&#xa0;4</label>
<caption>
<p>Maritechture&#x2122; Coral pods (patent pending, U.S. Patent Application No. 62/954,435| Filed December 28, 2019). <bold>(A)</bold> Illustration of coral pod design. White bar indicates 20&#xa0;cm in width. <bold>(B)</bold> Diver placing coral pod underwater. <bold>(C)</bold> Coral pod with coral fragments <italic>in situ</italic>. <bold>(D)</bold> Arrangement of coral pods.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-10-1110830-g004.tif"/>
</fig>
</sec>
</sec>
<sec id="s3">
<label>3</label>
<title>Method description</title>
<p>Our modular infrastructure for coral restoration and reefscape enhancement has been designed to streamline various elements of the coral gardening process from husbandry to outplanting (<xref ref-type="fig" rid="f5">
<bold>Figure&#xa0;5</bold>
</xref>) and facilitate data logging and monitoring.</p>
<fig id="f5" position="float">
<label>Figure&#xa0;5</label>
<caption>
<p>Schematic workflow illustration of an adaptive management approach.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-10-1110830-g005.tif"/>
</fig>
<sec id="s3_1">
<label>3.1</label>
<title>Donor</title>
<p>With our technologies, corals may originate from sustainable harvesting (<xref ref-type="bibr" rid="B45">Rinkevich, 1995</xref>; <xref ref-type="bibr" rid="B2">Barton et&#xa0;al., 2017</xref>), fragments of hope (<xref ref-type="bibr" rid="B20">Garrison and Ward, 2012</xref>), coral relocation sites (<xref ref-type="bibr" rid="B30">Kenny et&#xa0;al., 2012</xref>), or nursery/growth operations (<xref ref-type="bibr" rid="B46">Rinkevich and Shafir, 2000</xref>; <xref ref-type="bibr" rid="B2">Barton et&#xa0;al., 2017</xref>). Propagation can be asexual by fragmentation (<xref ref-type="bibr" rid="B45">Rinkevich, 1995</xref>) or sexual by cultured (<xref ref-type="bibr" rid="B42">Petersen and Tollrian, 2001</xref>) or wild-caught larvae (<xref ref-type="bibr" rid="B15">Doropoulos et&#xa0;al., 2019</xref>) (<xref ref-type="fig" rid="f5">
<bold>Figure&#xa0;5</bold>
</xref>). Regardless of origin, it is critical to collect as much metadata as possible on the corals to inform husbandry conditions and to direct downstream applications (<xref ref-type="bibr" rid="B4">Baums et&#xa0;al., 2011</xref>). This includes the GPS coordinates of the sample location in the case of wild-sourced corals or the origin of the donor/parental lineages in the case of husbandry. The sampling date, size, species, depth, temperature, light conditions, etc., should also be provided. These data should be recorded and stored in a central database (<xref ref-type="fig" rid="f5">
<bold>Figure&#xa0;5</bold>
</xref>) to inform performance assessments and optimize future deployments.</p>
</sec>
<sec id="s3_2">
<label>3.2</label>
<title>Screwable coral tiles</title>
<p>Transplanting fragments or seeding larvae using trackable Maritechture&#x2122; Coral Tiles allows metadata to be associated with individuals <italic>via</italic> RFID tags. This information can guide culturing conditions during husbandry, for example, regarding light levels. Embedding the RFID tag into the transplant or seeding substrate allows for permanent long-term identification and efficient stock management (<xref ref-type="bibr" rid="B48">Schmidt-Roach et&#xa0;al., 2020</xref>). It will enable monitoring and tracking of individual colony performance, stress susceptibility, health and survival during culture and beyond, all of which can be related back to colony origin and history. If individuals die, the tiles can be cleaned and reused.</p>
<p>Tagged tiles are equipped with passive integrated transponders (PIT) based on radio frequency identification (RFID) with low-frequency operation (134.2 kHz) and 64-bit identification. The tags can be read with any PIT reader compatible with the ISO 11785 standard. When used in conjunction with inventory management software, this solution allows corals to be tracked as they are propagated or moved between tanks <italic>ex situ</italic> or sites/structures <italic>in situ</italic> to automatically update records. This enables real-time automated stock management to coordinate aquaculture and allocate harvestable colonies to outplanting efforts. We are currently prototyping software customized for this purpose.</p>
<p>For fragmentation, we use various standard cutting techniques such as bone cutters or a Gryphon Diamond Band Saw (AquaSaw). Adhesion of coral fragments to tiles or plugs is performed using various methods, including epoxy (e.g. <xref ref-type="bibr" rid="B23">Hein et&#xa0;al., 2020</xref>) or ultraviolet (UV)-curable oligomer-based adhesives (<xref ref-type="bibr" rid="B56">Takeuchi et&#xa0;al., 2019</xref>), or commercially available gel-based cyanoacrylate adhesives. It is important that the fragment&#x2019;s tissue has grown over the tiles prior to outplanting, as the adhesion of the adhesive often wears off over time. It has been shown that coral fragments from branching species attached upside down grew significantly wider and faster over the tiles than corals attached right side up (<xref ref-type="bibr" rid="B55">Tagliafico et&#xa0;al., 2018</xref>), and we recommend this technique to promote rapid tile overgrowth.</p>
<p>The shape of the tile can be adjusted to the propagation pathway (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1</bold>
</xref>). For fast-growing, branching species, we recommend small hexagonal tiles (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1E</bold>
</xref>). For slow-growing, massive species, we recommend larger tiles that allow the use of standard microfragmentation protocols (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1B</bold>
</xref>) (<xref ref-type="bibr" rid="B18">Forsman et&#xa0;al., 2015</xref>). For recruitment, we recommend structured tiles with small cavities, which have been shown to promote larval settlement (<xref ref-type="bibr" rid="B39">Nozawa et&#xa0;al., 2011</xref>; <xref ref-type="bibr" rid="B43">Randall et&#xa0;al., 2021</xref>).</p>
</sec>
<sec id="s3_3">
<label>3.3</label>
<title>Coral crates</title>
<p>Attachment of the tiles to the Maritechture&#x2122; Coral Crates supports the strategic organization of corals. The crates allow coral genotypes to be organized in rows divided into seven tiles per bar (labelled A-H on the crate) (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2A</bold>
</xref>). Secure attachment by the screw system avoids friction and damage to the colonies (<xref ref-type="supplementary-material" rid="SF1">
<bold>Video 1</bold>
</xref>). The coral crate units facilitate easy handling in air and underwater and simplifies cleaning during aquaculture because of their smaller surface area compared to commonly used egg crate grids. The crates can also be tagged with RFID technology, allowing for automated inventory management. For transportation, the units can be safely stacked and transported directly to the outplanting site underwater. In addition, the horizontal connection of multiple crates and attachment to the seafloor enables the rapid establishment of <italic>in situ</italic> nurseries, e.g. for temporary storage.</p>
</sec>
<sec id="s3_4">
<label>3.4</label>
<title>Coral outplanting/nursing devices</title>
<p>We have developed several solutions for outplanting (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3</bold>
</xref>). The advantage of our modular, screwable tile system is that coral crops can be quickly interchanged between crates and different structures or outplanted directly onto a natural or artificial substrate. We have developed adapters for the most common types of coral nursery structures including PVC pipes, metal rods, metal grids and ropes (<xref ref-type="bibr" rid="B7">Bostr&#xf6;m-Einarsson et&#xa0;al., 2020</xref>). This allows existing structures to be quickly modified and outfitted to accommodate our technologies.</p>
<p>Our Maritechture&#x2122; Reef Nails attach quickly (within seconds) to suitable reef substrate and create a solid bond that promotes attachment of the fragments to the reef substrate. A single dive buddy team can outplant over 50 fragments from a coral crate onto reef substrate in 30 minutes. For artificial structures that can be drilled with holes prior to deployment, we developed Maritechture&#x2122; Reef Wall Plugs. Similar in function to a conventional dowel, these allow for a solid connection of our tiles to artificial substrates such as Maritechture&#x2122; Reef Pods, jetty walls, floating villas or bridge piers.</p>
</sec>
<sec id="s3_5">
<label>3.5</label>
<title>Coral pods</title>
<p>We developed Maritechture&#x2122; Coral Pods as an environmentally friendly underwater landscaping tool to enhance reef landscapes and provide new substrate for coral outplanting and nursing where this is lacking. With our methods, we envision their use for the creation of artistically planned and curated underwater landscapes, whereby the structures can be arranged in geometric patterns for visual and orientation purposes. The units can be stacked flat on top of one another to minimize space requirements and ease transport and logistics costs. On-site, the coral pods can be quickly assembled either on board a vessel or underwater. The corals can be attached with Maritechture&#x2122; Reef Wall Plugs or cable ties.</p>
<p>In their current design, each assembled structure can accommodate up to 16 coral fragments. Given an area of 1.5 m<sup>2</sup> for coral growth per structure, we recommend a density of one structure per 3 m<sup>2</sup>. With 14-16 corals per structure, this results in an outplanting density of approximately five corals per square meter, which may increase further with spontaneous natural recruitment, given that the material is highly suitable for coral settlement. By mounting the structures onboard a vessel, corals can be quickly attached before the pods are placed in the water, reducing dive time. In this way, a team of six can deploy up to 30 structures per dive, with four team members assembling the structures, stocking them with coral and lowering them with a crane, while two divers receive and position the structures on the seabed at the deployment depth. On rotation, a six-person construction team can place 90 structures in four hours, with each team member performing only a single dive. This allows for up to 250 square meters of reef landscape to be created in half a day.</p>
</sec>
</sec>
<sec id="s4" sec-type="discussion">
<label>4</label>
<title>Discussion</title>
<p>Coral restoration efforts are still limited by a lack of industrial-scale commercially available tools to facilitate cost-effective operations at scale. Although there is no one-size-fits-all solution for coral restoration, our modular technologies provide flexibility to create new or to adapt to and upgrade and improve existing infrastructure and techniques. Our technologies address aquaculture, coral gardening, substrate creation, outplanting and monitoring workflows, providing the first holistic, modular toolset for coral restoration and reef expansion, and enabling an adaptive management approach. Previous technologies only targeted individual applications or workflows and often have limited scalability.</p>
<p>For substrate creation, Reef Balls&#x2122; (<xref ref-type="bibr" rid="B50">Sherman et&#xa0;al., 2002</xref>) or similar derivations, are likely the most widely distributed commercial solution for reef habitat creation and coastal protection. Attachment of corals to these structures is usually achieved using epoxy, which is time intensive and carries risks of toxicity. Although not commercially distributed as off-the-shelf-product, Mars Reef Stars offer a standardized design for metal frames that can be interconnected to restore damaged reefs (<xref ref-type="bibr" rid="B64">Williams et&#xa0;al., 2019</xref>). These structures are usually custom made at each location from steel rods coated with epoxy and sand, and corals are then attached <italic>via</italic> cable ties. The Maritechture&#x2122; Coral Pods presented here are similar in functionality to Mars Reef Stars, however, due to their innate weight they do not require interconnection. Further, unlike steel, limestone is an environmentally friendly material known to enhance coral recruitment (<xref ref-type="bibr" rid="B49">Schmidt-Roach et&#xa0;al., 2008</xref>). Hence the structures are self-seeding and with their relatively large surface (approximately 2.5 m<sup>2</sup>) quickly develop a natural reef-like patina on their surface. Per square meter, our Maritechture&#x2122; Coral Pods have an estimated carbon footprint of about 80 times less than Mars Reef Stars and over 800 times less than a standard Reef Ball (<xref ref-type="table" rid="T1">
<bold>Table&#xa0;1</bold>
</xref>). Constructed from natural limestone, our structures are reef-like and do not alter the water chemistry. Further, they have no plastic coatings that may break down to micro-plastic over time.</p>
<table-wrap id="T1" position="float">
<label>Table&#xa0;1</label>
<caption>
<p>Carbon footprint of different coral support structures. Greenhouse gases produced associated with construction is estimated based on <xref ref-type="bibr" rid="B22">Hammond and Jones (2008)</xref>.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="bottom" align="left">Type</th>
<th valign="top" align="left">Material</th>
<th valign="bottom" align="left">Approx. weight kg</th>
<th valign="bottom" align="left">KgCO<sub>2</sub> emission/kg</th>
<th valign="bottom" align="left">kgCO<sub>2</sub>
<break/>emission<break/>per unit</th>
<th valign="bottom" align="left">Area in m<sup>2</sup>
</th>
<th valign="bottom" align="left">kgCO<sub>2</sub>/m<sup>2</sup> emission</th>
<th valign="bottom" align="left">Reference</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="bottom" align="left">Maritechture&#x2122; <italic>Coral pod</italic>
</td>
<td valign="top" align="left">Limestone</td>
<td valign="bottom" align="left">40</td>
<td valign="bottom" align="left">0.017</td>
<td valign="bottom" align="left">0.68</td>
<td valign="bottom" align="left">1.5</td>
<td valign="bottom" align="left">0.5</td>
<td valign="bottom" align="left">This study</td>
</tr>
<tr>
<td valign="bottom" align="left">
<italic>Mars Reef Star</italic>
</td>
<td valign="top" align="left">Steel rod (excluding epoxy)</td>
<td valign="bottom" align="left">8</td>
<td valign="bottom" align="left">1.71</td>
<td valign="bottom" align="left">13.68</td>
<td valign="bottom" align="left">0.34</td>
<td valign="bottom" align="left">40.6</td>
<td valign="bottom" align="left">(<xref ref-type="bibr" rid="B64">Williams et&#xa0;al., 2019</xref>)</td>
</tr>
<tr>
<td valign="bottom" align="left">
<italic>Reef Ball</italic>
</td>
<td valign="top" align="left">Cement (Portland)</td>
<td valign="bottom" align="left">1364</td>
<td valign="bottom" align="left">0.83</td>
<td valign="bottom" align="left">1132.12</td>
<td valign="bottom" align="left">2.63</td>
<td valign="bottom" align="left">430.5</td>
<td valign="bottom" align="left">
<uri xlink:href="http://www.reefball.org/technicalspecs">www.reefball.org/technicalspecs</uri>
</td>
</tr>
</tbody>
</table>
</table-wrap>
<sec id="s4_1">
<label>4.1</label>
<title>Towards coral restoration at scale</title>
<p>To increase scalability and overcome time intensive adhesion during outplanting, <xref ref-type="bibr" rid="B53">Suggett et&#xa0;al. (2020)</xref> developed Coral Clips&#xae;, a fast solution to outplant fragments or tiles <italic>via</italic> a metal clip attached to a nail hammered into the reef. Similar in function to the Maritechture&#x2122; Coral Nails presented here, these work well on hard substrate and allow strategic placement of fragments during outplanting. While Coral Clips&#xae; are ideal to reattach so-called fragments of hope (lose fragments broken of larger colonies for example during storms), growing and attaching coral directly to their outplanting substrate <italic>via</italic> our Maritechture&#x2122; Coral Tiles minimizes the stress that may occur during detachment of corals after an intermediate gardening phase. Further, our tiles have the advantage of enabling long-term monitoring.</p>
<p>To avoid the need for dive operations at all during outplanting, <xref ref-type="bibr" rid="B9">Chamberland et&#xa0;al. (2017)</xref> proposed ceramic tetrapod structures seeded with coral recruits to be deployed from vessels into reefs. Although this permits the economic deployment of a large number of structures, tests need to be conducted to understand survival rates compared to recruitment tiles strategically placed using the Coral Clips&#xae; or Maritechture&#x2122; Reef Nail technology. <xref ref-type="bibr" rid="B15">Doropoulos et&#xa0;al. (2019)</xref> went a step further to propose industrial-scale harvesting of larvae <italic>via</italic> large vessels for relocation, whereby the mass of harvesting of coral larval slicks can be deported to foreign reefs to overcome the low survivorship of settlers. However, large scale pilot studies are still to be conducted.</p>
<p>Our Maritechture&#x2122; technologies provide the basis to enable the automation of coral reef restoration workflows in the future. Coral aquaculture can achieve higher production rates by optimizing conditions for increased growth, e.g. by adjusting light or temperature, or by co-culturing of beneficial biota and reducing algae growth (<xref ref-type="bibr" rid="B12">Craggs et&#xa0;al., 2019</xref>). However, optimal husbandry conditions can be species-specific (<xref ref-type="bibr" rid="B35">Merck et&#xa0;al., 2022</xref>). The organized placement of coral colonies on the coral crates allows quick and strategic performance assessments to ensure individuals are fostered under ideal conditions. Having coral fragments in fixed positions in the tanks may eventually facilitate AI-driven automated phenotyping, for example, <italic>via</italic> repeated structure from motion photometry using robotic solutions. Similar techniques are already in place in terrestrial systems to increase production rates and promote selective breeding (<xref ref-type="bibr" rid="B27">Humpl&#xed;k et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B10">Chawade et&#xa0;al., 2019</xref>). High-throughput phenotyping could enable big data analytics, which could dramatically increase production rates and the effectiveness of coral nursery efforts. Considering the current rise of applied use of robotic systems in fish farming (<xref ref-type="bibr" rid="B63">Wang et&#xa0;al., 2021</xref>) or even more distant sectors as part of the industry (<xref ref-type="bibr" rid="B29">Javaid et&#xa0;al., 2021</xref>), automatization of workflows is likely to play a significant role in reducing associated labor costs and achieving scale.</p>
</sec>
<sec id="s4_2">
<label>4.2</label>
<title>A tool for stakeholder engagement, outreach, and education</title>
<p>The ability to create detailed records and to trace performances over time using our trackable Maritechture&#x2122; Coral Tile technology enables unique information tools for stakeholder engagement. Creating cloud-based inventories and data records can not only guide coral restoration practitioners during their daily efforts, but it can also be used to inform stakeholders (e.g. governments or private entities investing into these efforts) about the success. Measuring and publishing performance can promote transparency and assist moderate expectations of the success of restoration efforts. Trust has been shown to significantly strengthen willingness to pay for restoration (<xref ref-type="bibr" rid="B36">Metcalf et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B1">Bakaki and Bernauer, 2016</xref>). In addition to building trust, communicating success as well as challenges on websites or social media may motivate public engagement and foster awareness. Projects could use this mechanism to transport positive messages of hope, which are important to gain public acceptance for government-funded restoration projects (<xref ref-type="bibr" rid="B33">Le et&#xa0;al., 2022</xref>).</p>
</sec>
<sec id="s4_3">
<label>4.3</label>
<title>Integrating selective propagation</title>
<p>For selective propagation efforts, it is vital to create detailed records to trace performances over time to permit adaptive management (<xref ref-type="bibr" rid="B48">Schmidt-Roach et&#xa0;al., 2020</xref>) and identify possible tradeoffs associated with the selected traits. Different pathways for thermal heat selection have been identified (<xref ref-type="bibr" rid="B3">Baums et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B41">Parkinson et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B48">Schmidt-Roach et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B61">Voolstra et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B54">Suggett et&#xa0;al., 2022</xref>). However, when comparing individuals from different environments, it should be considered that these may be phenotypically acclimated to different conditions, which may alter their performance in acute thermal stress assessments. Common-garden nurseries <italic>ex</italic> or <italic>in situ</italic> offer the advantage that individuals can be acclimated to similar conditions prior to testing, which may reduce acclimation biases during performance assessments. Although different strategies for selective breeding of corals for assisted evolution have been suggested (<xref ref-type="bibr" rid="B60">van Oppen et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B59">van Oppen et&#xa0;al., 2017</xref>) and partially tested (<xref ref-type="bibr" rid="B26">Humanes et&#xa0;al., 2021</xref>), the long-term effect and success of these strategies still remain uncertain. Our trackable tile system <italic>via</italic> RFID technology supports long-term monitoring efforts and permits informed adjustment of selective propagation strategies. In addition to RFID identification, the embedded stainless-steel nail in our reef nail solution can be detected using a metal detector similar to CoralClips&#xae; (<xref ref-type="bibr" rid="B53">Suggett et&#xa0;al., 2020</xref>).</p>
<p>Strategic outplanting can further increase genetic diversity and stress resilience, as restored corals have been observed to be reproductively active (<xref ref-type="bibr" rid="B14">Diraviya Raj et&#xa0;al., 2015</xref>). Coral pods and reef nails can be used to create coral seeding hubs (CSH), where different genotypes of conspecifics are planted in clusters strategically placed in the reef to promote reproduction and increase genetic diversity in the offspring (<xref ref-type="bibr" rid="B48">Schmidt-Roach et&#xa0;al., 2020</xref>). A portion of these transplants can be sourced from selected, higher stress resistant colonies to increase the frequency of favorable alleles in the population while maximizing genetic diversity (<xref ref-type="bibr" rid="B48">Schmidt-Roach et&#xa0;al., 2020</xref>). However, not all genotypes should be selected for increased single stress performance, and genetic diversity should be maximized to account for unforeseen stressors such as disease (<xref ref-type="bibr" rid="B37">Moriarty et&#xa0;al., 2020</xref>).</p>
</sec>
<sec id="s4_4">
<label>4.4</label>
<title>Towards a blue architecture and landscaping approach in coral restoration</title>
<p>In contrast to present coastal developments that rarely extend beyond the shoreline, we advocate for a &#x201c;blue architecture&#x201d; and landscaping approach that extends landscaping of coastal developments into the sea. Community-conscious coastal developments that integrate the marine environment may secure natural capital (<xref ref-type="bibr" rid="B13">Cziesielski et&#xa0;al., 2021</xref>). <xref ref-type="bibr" rid="B48">Schmidt-Roach et&#xa0;al. (2020)</xref> stressed the mutual benefit of integrating coral restoration efforts in coastal developments to rehabilitate natural habitats and foster and secure blue natural capital as part of development assets. In addition to conventional restoration operations, the elements, tools and processes presented here allow easy and quick beautifications of jetty walls and other coastal structures with corals, turning these into meaningful resources to grow corals for restoration and to create or restore fully functional habitats.</p>
<p>A blue architecture and landscaping approach to coral restoration requires the contribution of a multidisciplinary team including marine ecologists, engineers, architects and artists, forming a community of practice that extends well beyond the competencies applied in conventional coral restoration projects. Applying a landscaping approach, our techniques allow the creation of scientifically and artistically curated underwater habitats resembling land-based botanical gardens. Architecture that extends into the sea connects coastal residents with their natural marine resources, engages citizens with restoration, raises awareness, promotes responsible stewardship, and boosts local economies. This may especially be of interest for ecotourism projects providing a dual benefit of attracting visitors and increasing resilience hence securing investments (<xref ref-type="bibr" rid="B48">Schmidt-Roach et&#xa0;al., 2020</xref>). Visionary plans for floating cities to address sea-level rise and overpopulation have become more concrete (<xref ref-type="bibr" rid="B6">Bolonkin, 2011</xref>; <xref ref-type="bibr" rid="B62">Wang, 2019</xref>) and offer unique opportunities for integrating marine landscape designs into marine urban projects. Massive tropical floating cities such as Oxagon envisioned by NEOM (<uri xlink:href="https://www.neom.com/en-us/regions/oxagon">https://www.neom.com/en-us/regions/oxagon</uri>) or Oceanix by BIG (<uri xlink:href="https://big.dk/#projects-sfc">https://big.dk/#projects-sfc</uri>) could be easily adjusted to harbor coral farming using the technologies presented here.</p>
<p>In conclusion, our platform aims to provide simple, eco-friendly and flexible infrastructure that caters towards a variety of different coral restoration and reefscaping efforts with a view of rendering coral restoration more cost-effective, scalable and sustainable. This is achieved by reducing workflow times as outlined above and ease of handling. Integrating novel monitoring tools, our approach delivers an intelligent solution to optimize and control stock management and enables adaptive management. The modularity of the tools aims to allow greater flexibility as different components can be added in the future to increase efficiency and effectiveness. We aim to make the above-described solutions available as the first modular off-the-shelf coral restoration technology, targeting production at scale to drive down costs, and to make them universally available.</p>
</sec>
</sec>
<sec id="s5" sec-type="data-availability">
<title>Data availability statement</title>
<p>The original contributions presented in the study are included in the article/<xref ref-type="supplementary-material" rid="s11">
<bold>Supplementary Material</bold>
</xref>. Further inquiries can be directed to the corresponding author.</p>
</sec>
<sec id="s6" sec-type="ethics-statement">
<title>Ethics statement</title>
<p>Written informed consent was obtained from the individual(s), and minor(s)&#x2019; legal guardian/next of kin, for the publication of any potentially identifiable images or data included in this article.</p>
</sec>
<sec id="s7" sec-type="author-contributions">
<title>Author contributions</title>
<p>SS-R invented, designed, and prototyped the technologies with contributions of all authors. SS-R prepared the manuscript, which was revised and improved by all authors. All authors contributed to the article and approved the submitted version.</p>
</sec>
</body>
<back>
<sec id="s8" sec-type="funding-information">
<title>Funding</title>
<p>The project was funded by KAUST Research Translation Fund RTF2020 (REI/1/4203-01-01).</p>
</sec>
<sec id="s9" sec-type="COI-statement">
<title>Conflict of interest</title>
<p>The patents for the technologies were filed by King Abdullah University for Science and Technology KAUST with SS-R, MA, CD, and CH as inventors. SS-R, CD, MA, AA-S, and RK are shareholders of Ocean Revive Company (<uri xlink:href="https://ocean-revive.com">ocean-revive.com</uri>), which targets to commercially distribute the technologies and make them available to coral restoration scientists and practitioners globally. Author JC is the founder of company Studio Julian Charrière.</p>
<p>The remaining author declares 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="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.2023.1110830/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fmars.2023.1110830/full#supplementary-material</ext-link>
</p>
<supplementary-material xlink:href="Video_1.mp4" id="SF1" mimetype="video/mp4">
<label>Supplementary Video 1</label>
<caption>
<p>Deployment and use of the Maritechture&#x2122; technologies.</p>
</caption>
</supplementary-material>
</sec>
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<title>References</title>
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