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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Mar. Sci.</journal-id>
<journal-title-group>
<journal-title>Frontiers in Marine Science</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Mar. Sci.</abbrev-journal-title>
</journal-title-group>
<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.2026.1760162</article-id>
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<article-categories>
<subj-group subj-group-type="heading">
<subject>Original Research</subject>
</subj-group>
</article-categories>
<title-group>
<article-title>Identifying drivers and dynamics of phytoplankton in the Black Sea: application of a neural emulator</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" corresp="yes">
<name><surname>Smith</surname><given-names>Philip A. H.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="corresp" rid="c001"><sup>*</sup></xref>
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<name><surname>Chauhan</surname><given-names>Anshul</given-names></name>
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<name><surname>Gr&#xe9;goire</surname><given-names>Marilaure</given-names></name>
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<name><surname>Vandenbulcke</surname><given-names>Luc</given-names></name>
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<name><surname>Christensen</surname><given-names>Asbj&#xf8;rn</given-names></name>
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<name><surname>St John</surname><given-names>Michael A.</given-names></name>
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<name><surname>Mariani</surname><given-names>Patrizio</given-names></name>
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<aff id="aff1"><label>1</label><institution>National Institute for Aquatic Resources, Technical University of Denmark</institution>, <city>Lyngby</city>,&#xa0;<country country="dk">Denmark</country></aff>
<aff id="aff2"><label>2</label><institution>FOCUS-MAST Research Group, Department of Astrophysics, Geophysics and Oceanography, University of Li&#xe8;ge</institution>, <city>Li&#xe8;ge</city>,&#xa0;<country country="be">Belgium</country></aff>
<aff id="aff3"><label>3</label><institution>Department of Technology, Management and Economics, Technical University of Denmark</institution>, <city>Lyngby</city>,&#xa0;<country country="dk">Denmark</country></aff>
<aff id="aff4"><label>4</label><institution>Pioneer Centre for Artificial Intelligence</institution>, <city>Copenhagen</city>,&#xa0;<country country="dk">Denmark</country></aff>
<author-notes>
<corresp id="c001"><label>*</label>Correspondence: Philip A. H. Smith, <email xlink:href="mailto:pahsm@aqua.dtu.dk">pahsm@aqua.dtu.dk</email></corresp>
</author-notes>
<pub-date publication-format="electronic" date-type="pub" iso-8601-date="2026-03-04">
<day>04</day>
<month>03</month>
<year>2026</year>
</pub-date>
<pub-date publication-format="electronic" date-type="collection">
<year>2026</year>
</pub-date>
<volume>13</volume>
<elocation-id>1760162</elocation-id>
<history>
<date date-type="received">
<day>03</day>
<month>12</month>
<year>2025</year>
</date>
<date date-type="accepted">
<day>02</day>
<month>02</month>
<year>2026</year>
</date>
<date date-type="rev-recd">
<day>27</day>
<month>01</month>
<year>2026</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2026 Smith, Chauhan, Gr&#xe9;goire, Vandenbulcke, Rodrigues, Christensen, St John and Mariani.</copyright-statement>
<copyright-year>2026</copyright-year>
<copyright-holder>Smith, Chauhan, Gr&#xe9;goire, Vandenbulcke, Rodrigues, Christensen, St John and Mariani</copyright-holder>
<license>
<ali:license_ref start_date="2026-03-04">https://creativecommons.org/licenses/by/4.0/</ali:license_ref>
<license-p>This is an open-access article distributed under the terms of the <ext-link ext-link-type="uri" xlink:href="https://creativecommons.org/licenses/by/4.0/">Creative Commons Attribution License (CC BY)</ext-link>. 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.</license-p>
</license>
</permissions>
<abstract>
<p>We present a spatiotemporal convolutional U-Net emulator model to forecast phytoplankton chlorophyll concentrations and key nutrient fields (nitrate and ammonium) in the Black Sea, using simulation data from 1950&#x2013;2014. The emulator achieved substantially higher predictive skill compared to baseline approaches, with a 41% improvement for chlorophyll and 59% for phosphate, while accurately capturing both spatial and temporal variability in biogeochemical dynamics. In addition to forecasting, interpretability of the model was obtained through Sobol sensitivity analysis, complemented by derivative-based global sensitivity measures (DGSM) and elasticity analysis. These revealed pronounced spatial and seasonal variations in the dominant environmental drivers across the basin, enabling exploration of &#x201c;what-if&#x201d; scenarios through targeted perturbations of key physical and biogeochemical drivers. Overall, light availability and nutrient concentrations (particularly nitrate, ammonium, and phosphate) emerged as key contributors, with a transition from predominantly light-driven short-term sensitivity toward increasing nutrient influence at longer lead times, modulated by strong regional and seasonal variability. The ability of the model to forecast biogeochemical states and to identify their dominant drivers highlights its potential as an early warning tool for detecting ecosystem changes and supporting adaptive management of the Black Sea.</p>
</abstract>
<kwd-group>
<kwd>biogeochemical modeling</kwd>
<kwd>Black Sea</kwd>
<kwd>chlorophyll</kwd>
<kwd>deep learning</kwd>
<kwd>marine ecosystems</kwd>
<kwd>model emulation</kwd>
<kwd>neural networks</kwd>
<kwd>nutrient dynamics</kwd>
</kwd-group>
<funding-group>
<funding-statement>The author(s) declared that financial support was received for this work and/or its publication. This work was primarily supported by the BRIDGE-BS project, funded by the European Union&#x2019;s Horizon 2020 Research and Innovation Programme under grant agreement No. 101000240. Additional support was provided through the MISSION ATLANTIC project (grant agreement No. 862428).</funding-statement>
</funding-group>
<counts>
<fig-count count="9"/>
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<equation-count count="6"/>
<ref-count count="106"/>
<page-count count="20"/>
<word-count count="12107"/>
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<custom-meta-group>
<custom-meta>
<meta-name>section-at-acceptance</meta-name>
<meta-value>Marine Biogeochemistry</meta-value>
</custom-meta>
</custom-meta-group>
</article-meta>
</front>
<body>
<sec id="s1" sec-type="intro">
<label>1</label>
<title>Introduction</title>
<p>Anthropogenically induced climate change and biodiversity loss are among the most significant global drivers reshaping the functioning and dynamics of marine ecosystems at a global scale (<xref ref-type="bibr" rid="B74">P&#xf6;rtner et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B40">Halpern et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B24">Franco et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B65">Meyer et&#xa0;al., 2024</xref>; <xref ref-type="bibr" rid="B83">Serpetti et&#xa0;al., 2025</xref>). These stressors act in combination with the natural modes of climate variability, making it challenging to predict consequences for ocean health and sustainable exploitation (<xref ref-type="bibr" rid="B88">Smale et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B46">Holbrook et&#xa0;al., 2020</xref>). Other key pressures such as ocean warming, acidification, deoxygenation, nutrient loading, and circulation changes interact in intricate and complex dynamics modifying ecosystem structure and function across spatial and temporal scales (<xref ref-type="bibr" rid="B27">Gattuso et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B5">Breitburg et&#xa0;al., 2018</xref>; <xref ref-type="bibr" rid="B73">Podymov et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B1">Akoglu, 2023</xref>).</p>
<p>Given their inherent nonlinear nature, interactions between drivers and ecosystems can give rise to compound impacts, anomalies and extreme events, potentially leading to irreversible crossing of tipping points (<xref ref-type="bibr" rid="B15">Council et&#xa0;al., 1998</xref>; <xref ref-type="bibr" rid="B37">Gruber et&#xa0;al., 2021</xref>). For instance, the 2015&#x2013;2016 marine heatwave in the Pacific Ocean resulted in a large volume of warm water &#x201c;The Blob&#x201d; which produced unprecedented changes in marine ecosystems, including mass die-offs of marine species, as well as disruptions to fisheries and food webs (<xref ref-type="bibr" rid="B19">Di Lorenzo and Mantua, 2016</xref>). In the Black Sea, harmful algal blooms (HABs) driven by eutrophication and changes in stratification have repeatedly created extensive hypoxic zones, severely impacting fish populations and local economies (<xref ref-type="bibr" rid="B14">Cooley et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B54">Lan et&#xa0;al., 2024</xref>; <xref ref-type="bibr" rid="B55">Lazar et&#xa0;al., 2024</xref>). Thus, physical, chemical, and biological drivers can amplify disturbances and create profound ecosystem impacts.</p>
<p>Process-based dynamic ocean models, built on the numerical integration of coupled physical and biogeochemical models, provide a powerful means to simulate these dynamics (<xref ref-type="bibr" rid="B23">Fennel et&#xa0;al., 2022</xref>). Simulations are typically based on partial differential equations (PDEs) describing the evolution of ocean state variables such as temperature, salinity, currents, nutrient and chlorophyll concentrations. In the Black Sea, high-resolution ocean-biogeochemical models have been coupled to regional atmospheric models demonstrating skills in simulating and forecasting a wide range of dynamics, including temperature, salinity, currents, nutrients, as well as food web interactions and biogeochemical cycles (<xref ref-type="bibr" rid="B33">Gr&#xe9;goire et&#xa0;al., 2008</xref>; <xref ref-type="bibr" rid="B34">Gr&#xe9;goire and Soetaert, 2010</xref>; <xref ref-type="bibr" rid="B32">Grailet et&#xa0;al., 2024</xref>; <xref ref-type="bibr" rid="B35">Gr&#xe9;goire et&#xa0;al., 2025</xref>).</p>
<p>In addition to reproducing ecosystem dynamics, these models have been used to analyze interactions between stressors and ecosystem components, enabling the investigation of both historical and future scenarios under changing environmental conditions (<xref ref-type="bibr" rid="B25">Fulton et&#xa0;al., 2003</xref>; <xref ref-type="bibr" rid="B36">Grimm et&#xa0;al., 2005</xref>). However, alongside their strengths, high-resolution simulations are computationally intensive, and any modification to initial or boundary conditions typically requires re-running the entire model setup, making rapid scenario testing and sensitivity analyses a challenging task (<xref ref-type="bibr" rid="B80">Rose et&#xa0;al., 2010</xref>; <xref ref-type="bibr" rid="B72">Payne et&#xa0;al., 2016</xref>).</p>
<p>Recent advances in machine learning, particularly deep learning, offer promising solutions to these challenges. Neural networks have demonstrated strong capabilities in capturing complex, nonlinear relationships within environmental systems and can serve to develop emulators (also called surrogate models) that approximate the behavior of traditional process-based models without requiring directly solving PDEs (<xref ref-type="bibr" rid="B95">Tang et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B102">Xu et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B18">Dheeshjith et&#xa0;al., 2024</xref>). These emulators can be trained using existing process-based model data, using several environmental drivers in inputs to provide, as outputs, ocean state variables, through embedding their statistical relationships (<xref ref-type="bibr" rid="B57">Leeds et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B93">Sudakow et&#xa0;al., 2022</xref>). Once trained and tested, they enable fast and computationally efficient predictions for new input scenarios, thus supporting large-scale sensitivity analyses, forecasting, and exploration of ecosystem management options (<xref ref-type="bibr" rid="B86">Singh et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B96">Taylor and Feng, 2022</xref>; <xref ref-type="bibr" rid="B38">Gupta et&#xa0;al., 2023</xref>; <xref ref-type="bibr" rid="B18">Dheeshjith et&#xa0;al., 2024</xref>).</p>
<p>Traditional emulator modeling forms an important foundation of environmental sciences. Methods such as polynomial regression offer simple global approximations but lack flexibility for complex dynamics. Splines and generalized additive models (GAMs) improve this with smoother, locally adaptive fits useful for gradual nonlinear responses, but they struggle as dimensionality and variable interactions grow (<xref ref-type="bibr" rid="B97">Wahba, 1990</xref>; <xref ref-type="bibr" rid="B43">Hastie, 2017</xref>). Kernel and geostatistical approaches such as radial basis functions and Kriging capture spatial structure and correlations, but exact training is computationally expensive and scales poorly to large datasets (<xref ref-type="bibr" rid="B6">Buhmann, 2000</xref>; <xref ref-type="bibr" rid="B51">Kleijnen, 2009</xref>). <xref ref-type="bibr" rid="B44">Hemmings et&#xa0;al. (2015)</xref> developed a 1D site-based mechanistic emulator of the MEDUSA biogeochemical model to enable efficient parametric analysis and calibration. While the approach proved effective at selected ocean sites, its reliance on simplified site-specific simulations and assumptions about the mean environment highlights its limitations in capturing spatial heterogeneity and dynamic interactions present in fully 3D models. These limitations have motivated a growing shift toward deep learning&#x2013;based emulators. While traditional methods such as PCA aim to capture dominant variability through linear projections, deep learning architectures such as autoencoders and convolutional encoder&#x2013;decoders (e.g. variations such as U-Nets) can serve as nonlinear dimensionality reduction methods, learning compressed representations that extract key physical and biogeochemical patterns from complex input data (<xref ref-type="bibr" rid="B45">Hinton and Salakhutdinov, 2006</xref>; <xref ref-type="bibr" rid="B106">Zhu and Zabaras, 2018</xref>).</p>
<p>Recently, deep learning-based emulators have been developed for a wide range of oceanic and environmental processes, from global ocean circulation to coastal hydrodynamics and atmospheric precipitation. Deep neural networks have been used to forecast mesoscale eddy dynamics in the North Pacific, achieving skill comparable to numerical simulations at a fraction of the computational cost (<xref ref-type="bibr" rid="B16">Cui et&#xa0;al., 2025</xref>). Convolutional U-Net architectures have also been implemented to emulate high-resolution coastal circulation with substantial computational speedup (<xref ref-type="bibr" rid="B103">Xu et&#xa0;al., 2024</xref>), and have been used to model Arctic sea-ice thickness for operational forecasting applications (<xref ref-type="bibr" rid="B20">Durand et&#xa0;al., 2024</xref>). Fourier Neural Operators and OceanNet have gained traction for efficiently emulating large-scale and regional ocean dynamics (<xref ref-type="bibr" rid="B94">Sun et&#xa0;al., 2024</xref>; <xref ref-type="bibr" rid="B10">Chattopadhyay et&#xa0;al., 2024</xref>). Emulators have further been applied to the prediction of coastal hazards, such as storm surge dynamics on evolving landscapes under climate change scenarios (<xref ref-type="bibr" rid="B29">Gharehtoragh and Johnson, 2024</xref>), as well as to probabilistic fluid dynamics and precipitation modeling (<xref ref-type="bibr" rid="B63">Maulik et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B99">Weber et&#xa0;al., 2020</xref>). While most of these studies target physical processes, machine learning has also been widely applied to chlorophyll and other biogeochemical variables, particularly for observation-driven surface mapping, gap-filling, and short-term prediction in both marine and limnological contexts (<xref ref-type="bibr" rid="B9">Chang et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B87">Skakala et&#xa0;al., 2023</xref>; <xref ref-type="bibr" rid="B59">Li et&#xa0;al., 2024</xref>; <xref ref-type="bibr" rid="B82">Sammartino et&#xa0;al., 2025</xref>). However, deep-learning emulation of coupled physical&#x2013;biogeochemical dynamics remains comparatively limited. A recent work used neural network emulators to estimate surface chlorophyll from physical fields in Earth system models (<xref ref-type="bibr" rid="B101">Wu et&#xa0;al., 2025</xref>), but such approaches have primarily addressed surface products or static spatial inference rather than forecasting the spatiotemporal evolution of biogeochemical fields.</p>
<p>In this study, we develop a deep learning&#x2013;based surrogate model to emulate the spatiotemporal evolution of modeled phytoplankton and nutrient dynamics in the Black Sea, accounting for its distinct ecological and physical characteristics, such as strong stratification, sharp salinity gradients, and diverse phytoplankton communities (<xref ref-type="bibr" rid="B78">Ricour et&#xa0;al., 2021</xref>). We designed a 3D (2D+time) convolutional U-Net (<xref ref-type="bibr" rid="B79">Ronneberger et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B20">Durand et&#xa0;al., 2024</xref>) that ingests time series of spatial maps of physical and chemical drivers, such as temperature, salinity, and nutrients, and predicts chlorophyll and nutrient distributions over subsequent days. Chlorophyll concentration is used as a proxy for phytoplankton biomass, providing an ecologically meaningful target for forecasting (<xref ref-type="bibr" rid="B41">Hammond et&#xa0;al., 2020</xref>). The model is trained using simulation outputs from the coupled NEMO&#x2013;BAMHBI ocean&#x2013;biogeochemical model, a state-of-the-art framework that has been extensively evaluated for the Black Sea (<xref ref-type="bibr" rid="B32">Grailet et&#xa0;al., 2024</xref>; <xref ref-type="bibr" rid="B35">Gr&#xe9;goire et&#xa0;al., 2025</xref>).</p>
<p>The main objectives of this study are (1) to develop and validate a deep learning-based emulator that can reproduce the spatiotemporal variability of modeled chlorophyll and nutrient concentrations in the Black Sea, with performance evaluated against different baselines, and (2) to identify and quantify the key drivers of chlorophyll variability using a complementary set of interpretability methods. Variance-based global sensitivity analysis using Sobol indices (<xref ref-type="bibr" rid="B81">Saltelli et&#xa0;al., 2008</xref>; <xref ref-type="bibr" rid="B70">Owen, 2014</xref>), derivative-based sensitivity measures (DGSM) (<xref ref-type="bibr" rid="B89">Sobol and Kucherenko, 2010</xref>; <xref ref-type="bibr" rid="B53">Kucherenko and Song, 2016</xref>), and spatially resolved elasticity analyses are employed to assess the relative importance of physical and biogeochemical predictors, as well as the spatial and temporal scales over which they influence the emulator predictions. While the emulator is designed with general applicability in mind, its potential utility for exploratory applications such as early-warning assessments of extreme events (e.g., harmful algal blooms) is discussed as a broader extension of this framework.</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>Black Sea emulator</title>
<sec id="s2_1_1">
<label>2.1.1</label>
<title>Formulation</title>
<p>In the following, we provide a formal description of the emulator, which is constructed using a 3D (2D+time) U-Net architecture to forecast future spatiotemporal fields of selected oceanographic variables in the Black Sea. The emulator E<italic><sub>&#x3b8;</sub></italic> is parameterized by neural network weights <italic>&#x3b8;</italic> and is trained to map sequences of past multivariate spatial fields to future distributions of key biogeochemical variables. Each input frame <inline-formula>
<mml:math display="inline" id="im1"><mml:mrow><mml:msubsup><mml:mtext>s</mml:mtext><mml:mi>t</mml:mi><mml:mrow><mml:mtext>in</mml:mtext></mml:mrow></mml:msubsup><mml:mo>&#x2208;</mml:mo><mml:msup><mml:mi>&#x211d;</mml:mi><mml:mrow><mml:mi>H</mml:mi><mml:mo>&#xd7;</mml:mo><mml:mi>W</mml:mi><mml:mo>&#xd7;</mml:mo><mml:msub><mml:mi>N</mml:mi><mml:mrow><mml:mtext>in</mml:mtext></mml:mrow></mml:msub></mml:mrow></mml:msup></mml:mrow></mml:math></inline-formula> contains values of <italic>N</italic><sub>in</sub> variables (e.g., temperature, salinity, nutrients; see Section 2.3) on a spatial grid of <italic>H</italic> &#xd7; <italic>W</italic> points, along the latitudinal and longitudinal directions.</p>
<p>The target output consists of <italic>q</italic> time steps of future frames, each <inline-formula>
<mml:math display="inline" id="im2"><mml:mrow><mml:msubsup><mml:mtext>s</mml:mtext><mml:mi>t</mml:mi><mml:mrow><mml:mtext>out</mml:mtext></mml:mrow></mml:msubsup><mml:mo>&#x2208;</mml:mo><mml:msup><mml:mi>&#x211d;</mml:mi><mml:mrow><mml:mi>H</mml:mi><mml:mo>&#xd7;</mml:mo><mml:mi>W</mml:mi><mml:mo>&#xd7;</mml:mo><mml:msub><mml:mi>N</mml:mi><mml:mrow><mml:mtext>out</mml:mtext></mml:mrow></mml:msub></mml:mrow></mml:msup></mml:mrow></mml:math></inline-formula>, representing the predicted variable(s). In principle, the output channel dimension <italic>N</italic><sub>out</sub> may include multiple variables (e.g., chlorophyll and nutrients). However, the results presented in this manuscript are obtained using separately trained models for each target variable, for which <italic>N</italic><sub>out</sub> = 1. At each time step <italic>t</italic>, the emulator receives <italic>w</italic> consecutive spatial fields:</p>
<disp-formula>
<mml:math display="block" id="M1"><mml:mrow><mml:msub><mml:mi>X</mml:mi><mml:mi>i</mml:mi></mml:msub><mml:mo>&#xa0;</mml:mo><mml:mo>:</mml:mo><mml:mo>=</mml:mo><mml:mo>{</mml:mo><mml:msubsup><mml:mtext>s</mml:mtext><mml:mrow><mml:mi>t</mml:mi><mml:mo>&#x2212;</mml:mo><mml:mi>w</mml:mi></mml:mrow><mml:mrow><mml:mtext>in</mml:mtext></mml:mrow></mml:msubsup><mml:mo>,</mml:mo><mml:msubsup><mml:mtext>s</mml:mtext><mml:mrow><mml:mi>t</mml:mi><mml:mo>&#x2212;</mml:mo><mml:mi>w</mml:mi><mml:mo>+</mml:mo><mml:mn>1</mml:mn></mml:mrow><mml:mrow><mml:mtext>in</mml:mtext></mml:mrow></mml:msubsup><mml:mo>,</mml:mo><mml:mo>&#x2026;</mml:mo><mml:mo>,</mml:mo><mml:msubsup><mml:mtext>s</mml:mtext><mml:mrow><mml:mi>t</mml:mi><mml:mo>&#x2212;</mml:mo><mml:mn>1</mml:mn></mml:mrow><mml:mrow><mml:mtext>in</mml:mtext></mml:mrow></mml:msubsup><mml:mo>}</mml:mo><mml:mo>,</mml:mo></mml:mrow></mml:math>
</disp-formula>
<p>and aims to reproduce the following <italic>q</italic> consecutive future reference frames:</p>
<disp-formula>
<mml:math display="block" id="M2"><mml:mrow><mml:msub><mml:mi>Y</mml:mi><mml:mi>i</mml:mi></mml:msub><mml:mo>&#xa0;</mml:mo><mml:mo>:</mml:mo><mml:mo>=</mml:mo><mml:mo>{</mml:mo><mml:msubsup><mml:mtext>s</mml:mtext><mml:mi>t</mml:mi><mml:mrow><mml:mtext>out</mml:mtext></mml:mrow></mml:msubsup><mml:mo>,</mml:mo><mml:msubsup><mml:mtext>s</mml:mtext><mml:mrow><mml:mi>t</mml:mi><mml:mo>+</mml:mo><mml:mn>1</mml:mn></mml:mrow><mml:mrow><mml:mtext>out</mml:mtext></mml:mrow></mml:msubsup><mml:mo>,</mml:mo><mml:mo>&#x2026;</mml:mo><mml:mo>,</mml:mo><mml:msubsup><mml:mtext>s</mml:mtext><mml:mrow><mml:mi>t</mml:mi><mml:mo>+</mml:mo><mml:mi>q</mml:mi><mml:mo>&#x2212;</mml:mo><mml:mn>1</mml:mn></mml:mrow><mml:mrow><mml:mtext>out</mml:mtext></mml:mrow></mml:msubsup><mml:mo>}</mml:mo><mml:mo>.</mml:mo></mml:mrow></mml:math>
</disp-formula>
<p>Different values are tested for the sliding window length <italic>w</italic> (the length of historical input sequences) and the forecast horizon <italic>q</italic> (the number of output time steps) during training, validation, and testing. The total period of the ecological dataset <italic>T</italic> is divided into training (<italic>T</italic><sup>train</sup>), validation (<italic>T</italic><sup>val</sup>), and test (<italic>T</italic><sup>test</sup>) sets. For each training sample indexed by <italic>i</italic> = 1<italic>,&#x2026;, T</italic><sup>train</sup>, the emulator produces a prediction.</p>
<disp-formula>
<mml:math display="block" id="M3"><mml:mrow><mml:msub><mml:mover accent="true"><mml:mi>Y</mml:mi><mml:mo>^</mml:mo></mml:mover><mml:mi>i</mml:mi></mml:msub><mml:mo>=</mml:mo><mml:msub><mml:mi mathvariant="script">E</mml:mi><mml:mi>&#x3b8;</mml:mi></mml:msub><mml:mo stretchy="false">(</mml:mo><mml:msub><mml:mi>X</mml:mi><mml:mi>i</mml:mi></mml:msub><mml:mo stretchy="false">)</mml:mo><mml:mo>.</mml:mo></mml:mrow></mml:math>
</disp-formula>
<p>Here, <inline-formula>
<mml:math display="inline" id="im3"><mml:mrow><mml:msub><mml:mover accent="true"><mml:mi>Y</mml:mi><mml:mo>^</mml:mo></mml:mover><mml:mi>i</mml:mi></mml:msub><mml:mo stretchy="false">[</mml:mo><mml:mi>j</mml:mi><mml:mo>,</mml:mo><mml:mtext>x</mml:mtext><mml:mo stretchy="false">]</mml:mo></mml:mrow></mml:math></inline-formula> denotes the predicted value at lead time <italic>j</italic> and spatial&#x2013;variable index <inline-formula>
<mml:math display="inline" id="im4"><mml:mrow><mml:mtext>x</mml:mtext><mml:mo>=</mml:mo><mml:mo stretchy="false">(</mml:mo><mml:mi>h</mml:mi><mml:mo>,</mml:mo><mml:mi>k</mml:mi><mml:mo>,</mml:mo><mml:mi>n</mml:mi><mml:mo stretchy="false">)</mml:mo></mml:mrow></mml:math></inline-formula>, and is given by <inline-formula>
<mml:math display="inline" id="im5"><mml:mrow><mml:msub><mml:mi mathvariant="script">E</mml:mi><mml:mi>&#x3b8;</mml:mi></mml:msub><mml:mo stretchy="false">(</mml:mo><mml:msub><mml:mi>X</mml:mi><mml:mi>i</mml:mi></mml:msub><mml:mo stretchy="false">)</mml:mo><mml:mo stretchy="false">[</mml:mo><mml:mi>j</mml:mi><mml:mo>,</mml:mo><mml:mtext>x</mml:mtext><mml:mo stretchy="false">]</mml:mo></mml:mrow></mml:math></inline-formula>, while <inline-formula>
<mml:math display="inline" id="im6"><mml:mrow><mml:msub><mml:mi>Y</mml:mi><mml:mi>i</mml:mi></mml:msub><mml:mo stretchy="false">[</mml:mo><mml:mi>j</mml:mi><mml:mo>,</mml:mo><mml:mtext>x</mml:mtext><mml:mo stretchy="false">]</mml:mo></mml:mrow></mml:math></inline-formula> denotes the corresponding reference value. During training, the network parameters <italic>&#x3b8;</italic> are optimized by minimizing a Mean Absolute Error (MAE) loss between predicted and reference outputs:</p>
<disp-formula>
<mml:math display="block" id="M4"><mml:mrow><mml:mi mathvariant="script">L</mml:mi><mml:mo stretchy="false">(</mml:mo><mml:mi>&#x3b8;</mml:mi><mml:mo stretchy="false">)</mml:mo><mml:mo>=</mml:mo><mml:mfrac><mml:mn>1</mml:mn><mml:mrow><mml:msup><mml:mi>T</mml:mi><mml:mrow><mml:mtext>train</mml:mtext></mml:mrow></mml:msup><mml:mtext>&#x2009;</mml:mtext><mml:mi>q</mml:mi><mml:mtext>&#xa0;</mml:mtext><mml:mo>|</mml:mo><mml:mi mathvariant="script">X</mml:mi><mml:mo>|</mml:mo></mml:mrow></mml:mfrac><mml:munderover><mml:mo>&#x2211;</mml:mo><mml:mrow><mml:mi>i</mml:mi><mml:mo>=</mml:mo><mml:mn>1</mml:mn></mml:mrow><mml:mrow><mml:msup><mml:mi>T</mml:mi><mml:mrow><mml:mtext>train</mml:mtext></mml:mrow></mml:msup></mml:mrow></mml:munderover><mml:munderover><mml:mo>&#x2211;</mml:mo><mml:mrow><mml:mi>j</mml:mi><mml:mo>=</mml:mo><mml:mn>0</mml:mn></mml:mrow><mml:mrow><mml:mi>q</mml:mi><mml:mo>&#x2212;</mml:mo><mml:mn>1</mml:mn></mml:mrow></mml:munderover><mml:munder><mml:mo>&#x2211;</mml:mo><mml:mrow><mml:mtext>x</mml:mtext><mml:mo>&#x2208;</mml:mo><mml:mi mathvariant="script">X</mml:mi></mml:mrow></mml:munder><mml:mo>|</mml:mo><mml:msub><mml:mover accent="true"><mml:mi>Y</mml:mi><mml:mo>^</mml:mo></mml:mover><mml:mi>i</mml:mi></mml:msub><mml:mo stretchy="false">[</mml:mo><mml:mi>j</mml:mi><mml:mo>,</mml:mo><mml:mtext>x</mml:mtext><mml:mo stretchy="false">]</mml:mo><mml:mo>&#x2212;</mml:mo><mml:msub><mml:mi>Y</mml:mi><mml:mi>i</mml:mi></mml:msub><mml:mo stretchy="false">[</mml:mo><mml:mi>j</mml:mi><mml:mo>,</mml:mo><mml:mtext>x</mml:mtext><mml:mo stretchy="false">]</mml:mo><mml:mo>|</mml:mo><mml:mo>,</mml:mo></mml:mrow></mml:math>
</disp-formula>
<p>where <inline-formula>
<mml:math display="inline" id="im7"><mml:mrow><mml:msup><mml:mi>T</mml:mi><mml:mrow><mml:mtext>train</mml:mtext></mml:mrow></mml:msup></mml:mrow></mml:math></inline-formula> is the number of training samples, and <inline-formula>
<mml:math display="inline" id="im8"><mml:mi mathvariant="script">X</mml:mi></mml:math></inline-formula> represents all combinations of the indices <inline-formula>
<mml:math display="inline" id="im9"><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:mi>h</mml:mi><mml:mo>,</mml:mo><mml:mi>k</mml:mi><mml:mo>,</mml:mo><mml:mi>n</mml:mi><mml:mo stretchy="false">)</mml:mo></mml:mrow></mml:math></inline-formula>, with <inline-formula>
<mml:math display="inline" id="im10"><mml:mrow><mml:mo>|</mml:mo><mml:mi mathvariant="script">X</mml:mi><mml:mo>|</mml:mo></mml:mrow></mml:math></inline-formula> being the number of elements of <inline-formula>
<mml:math display="inline" id="im11"><mml:mi mathvariant="script">X</mml:mi></mml:math></inline-formula>.</p>
</sec>
<sec id="s2_1_2">
<label>2.1.2</label>
<title>3D U-Net architecture</title>
<p>The emulator <inline-formula>
<mml:math display="inline" id="im12"><mml:mrow><mml:msub><mml:mi mathvariant="script">E</mml:mi><mml:mi>&#x3b8;</mml:mi></mml:msub></mml:mrow></mml:math></inline-formula> is based on a 3D U-Net neural network (<xref ref-type="fig" rid="f1"><bold>Figure&#xa0;1</bold></xref>), selected for its ability to effectively process and analyze complex spatiotemporal data (<xref ref-type="bibr" rid="B106">Zhu and Zabaras, 2018</xref>) and comprising approximately 69.74 million trainable parameters. The encoder compresses spatiotemporal features across the input window (<italic>w</italic>) into a lower-dimensional latent representation, facilitating the extraction of dominant patterns and relationships within the data. The decoder then reconstructs the output based on these learned patterns, preserving fine-scale features to predict future states of phytoplankton and nutrient distributions.</p>
<fig id="f1" position="float">
<label>Figure&#xa0;1</label>
<caption>
<p>Representation of the 3D U-Net architecture used in this study. The model takes <italic>w</italic> = 32 days of multivariate input sequences and predicts <italic>q</italic> = 16 subsequent days. The network includes an encoder, decoder, and skip connections, with 3D convolutional layers (namely, Conv3D and Conv3DTranspose) to process spatiotemporal data.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-13-1760162-g001.tif">
<alt-text content-type="machine-generated">Diagram of the 3D U-Net architecture used to forecast spatiotemporal ocean variables. The model processes 32 days of multivariate input fields and predicts 16 subsequent days. The architecture consists of an encoder that progressively downsamples spatial and temporal dimensions using Conv3D and MaxPooling3D layers, and a decoder that reconstructs the forecast using Conv3DTranspose layers. Skip connections link corresponding encoder and decoder levels to preserve fine-scale information. A temporal slicing operation ensures the output matches the forecast window. Tensor dimensions and layer operations are indicated throughout the network.</alt-text>
</graphic></fig>
<p>The architecture processes spatiotemporal tensors with dimensions (<italic>w, H, W, N</italic><sub>in</sub>), where <italic>w</italic> is the temporal window length, <italic>H</italic> and <italic>W</italic> are the spatial dimensions, and <italic>N</italic><sub>in</sub> is the number of input channels (variables). The encoder path progressively downsamples spatial and temporal features using stacked 3D convolutional (Conv3D) and max pooling (MaxPooling3D) layers, compressing the data into a latent representation. The decoder path reconstructs the output using Conv3DTranspose layers and skip connections, which preserve fine-scale details by concatenating features from matching encoder levels. To align the output with the desired forecast window (i.e., <italic>q</italic> days), a temporal slicing operation is applied at the output layer, ensuring that the predictions cover the target period. The final (1 &#xd7; 1 &#xd7; 1) Conv3D layer then maps the extracted features to the output variables. For detailed descriptions of the underlying neural network operations (e.g., convolution, pooling, and skip connections), see <xref ref-type="bibr" rid="B56">LeCun et&#xa0;al. (2015)</xref>; <xref ref-type="bibr" rid="B31">Goodfellow et&#xa0;al. (2016)</xref>. An illustration of the full architecture and tensor-dimension flow is provided in <xref ref-type="fig" rid="f1"><bold>Figure&#xa0;1</bold></xref>.</p>
<p>Alternative architectures were tested, including a 2D U-Net variant where the time and variable dimensions were collapsed into a single input dimension (<xref ref-type="bibr" rid="B79">Ronneberger et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B86">Singh et&#xa0;al., 2021</xref>). These models were evaluated using the same training&#x2013;validation splits and a consistent baseline training configuration. The 2D formulations generally exhibited lower validation performance as additional variables and time steps were included, suggesting limitations associated with collapsing spatiotemporal structure into a single input dimension in this setting.</p>
<p>Other 3D convolutional architectures were also explored, including deeper and shallower variants, architectures with additional skip connections, attention-based modules, and hybrid designs incorporating convolutional LSTMs (ConvLSTMs) (<xref ref-type="bibr" rid="B84">Shi et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B96">Taylor and Feng, 2022</xref>). While some of these architectures showed comparable short-range skill, they did not yield consistent improvements in these exploratory tests over the baseline 3D U-Net under comparable baseline tuning effort, and often exhibited increased sensitivity to hyperparameter choices or reduced training stability.</p>
<p>The final 3D U-Net was therefore selected based on a combination of quantitative performance, training stability, and its suitability for preserving multi-scale spatiotemporal structure, which is critical for forecasting coupled physical&#x2013;biogeochemical fields. These findings should not be interpreted as a general assessment of the relative strengths of different architectures, nor do they imply that alternative architectures are inherently inferior or unable to achieve comparable skill. Rather, the choice reflects a balance between predictive performance, robustness, and architectural transparency within the scope of the present study.</p>
<p>Following this selection, model hyperparameters and training strategy were optimized for the chosen 3D U-Net using a combination of backward feature elimination and grid search. Network depth was found to be optimal at six convolutional layers per block, beyond which validation performance degraded due to overfitting. Full details of the optimization procedure and training configuration are provided in <xref ref-type="supplementary-material" rid="s12"><bold>Supplementary Material</bold></xref> (Section S1.1). During training, we used cosine-annealing learning-rate scheduling with warm restarts to improve convergence and generalization (<xref ref-type="bibr" rid="B60">Loshchilov and Hutter, 2016</xref>; <xref ref-type="bibr" rid="B90">S&#xf8;rensen et al., 2022</xref>). The final architecture was selected based on a combination of predictive performance and stable convergence observed across repeated training runs using identical temporal splits.</p>
</sec>
</sec>
<sec id="s2_2">
<label>2.2</label>
<title>NEMO-BAMHBI outputs in the Black Sea</title>
<p>The dataset used to train the network was sourced from simulations produced by the coupled NEMO-BAMHBI modeling system (<xref ref-type="bibr" rid="B33">Gr&#xe9;goire et&#xa0;al., 2008</xref>; <xref ref-type="bibr" rid="B34">Gr&#xe9;goire and Soetaert, 2010</xref>; <xref ref-type="bibr" rid="B35">Gr&#xe9;goire et&#xa0;al., 2025</xref>). NEMO (v4.2) solves the ocean primitive equations and is coupled online to the <italic>BiogeochemicAl Model for Hypoxic and Benthic Influenced areas</italic> (BAMHBI; <xref ref-type="bibr" rid="B35">Gr&#xe9;goire et&#xa0;al., 2025</xref>). This modeling framework simulates the marine carbon, nitrogen, oxygen, and sulfur cycles from bacteria up to mesozooplankton, explicitly representing processes in the anoxic layer through a 28-variable pelagic and 6-variable benthic biogeochemical formulation (<xref ref-type="bibr" rid="B61">Mac&#xe9; et&#xa0;al., 2024</xref>; <xref ref-type="bibr" rid="B35">Gr&#xe9;goire et&#xa0;al., 2025</xref>).</p>
<p>The coupled model is forced by a regional atmospheric model (MAR) (<xref ref-type="bibr" rid="B26">Gall&#xe9;e and Schayes, 1994</xref>; <xref ref-type="bibr" rid="B32">Grailet et&#xa0;al., 2024</xref>), which provides high-resolution atmospheric forcing (wind, heat fluxes, precipitation) over the Black Sea. For the hindcast simulation considered here (1950&#x2013;2014), MAR was forced at its lateral boundaries by global atmospheric fields from MPI-ESM (<xref ref-type="bibr" rid="B30">Giorgetta et&#xa0;al., 2013</xref>), ensuring regional meteorological conditions consistent with large-scale climate variability. The resulting atmospheric fields drive the coupled NEMO&#x2013;BAMHBI system, enabling the simulation of physically and biogeochemically consistent historical conditions in the Black Sea.</p>
<p>The NEMO&#x2013;BAMHBI configuration used in this study has a horizontal resolution of approximately 0.14<sup>&#xb0;</sup> in latitude and 0.18<sup>&#xb0;</sup> in longitude, corresponding to roughly 15 &#xd7; 15 km in the Black Sea region. The model outputs are provided at daily temporal resolution and include 59 vertical levels from the surface to 2400 m, with enhanced vertical resolution in the upper ocean to better resolve biologically active layers. This configuration does not include online data assimilation; however, different versions of the NEMO&#x2013;BAMHBI system have been extensively evaluated against available observations in the Black Sea. In particular, <xref ref-type="bibr" rid="B35">Gr&#xe9;goire et&#xa0;al. (2025)</xref> document the validation of BAMHBI simulations against satellite-derived chlorophyll (after 1997), dissolved oxygen, nitrate, and Argo-based chlorophyll observations, supporting the ability of the model to represent key physical and biogeochemical features of the basin.</p>
<p>From the comprehensive set of modeled physical and biogeochemical variables produced by the coupled system, a subset was selected and used as input predictors for the U-Net emulator, as summarized in <xref ref-type="table" rid="T1"><bold>Table&#xa0;1</bold></xref>. These variables constitute the selected dynamic ocean state fields from the full NEMO&#x2013;BAMHBI output, while spatial and temporal contextual predictors are introduced separately during data preparation.</p>
<table-wrap id="T1" position="float">
<label>Table&#xa0;1</label>
<caption>
<p>Subset of physical and biogeochemical variables extracted from the NEMO&#x2013;BAMHBI simulations and used as dynamic input predictors by the U-Net emulator.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="middle" align="left">Category</th>
<th valign="middle" align="left">Variables</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="middle" align="left">Physical fields</td>
<td valign="middle" align="left">Temperature, Salinity, Sea Surface Height (SSH),<break/>Wind Speed, Mixed Layer Depth (MLD)</td>
</tr>
<tr>
<td valign="middle" align="left">Ocean currents</td>
<td valign="middle" align="left">Zonal velocity (u), Meridional velocity (v), Vertical velocity (w)</td>
</tr>
<tr>
<td valign="middle" align="left">Nutrients</td>
<td valign="middle" align="left">Ammonium, Nitrate, Phosphate, Silicate</td>
</tr>
<tr>
<td valign="middle" align="left">Other tracers</td>
<td valign="middle" align="left">Dissolved Oxygen</td>
</tr>
<tr>
<td valign="middle" align="left">Light-related</td>
<td valign="middle" align="left">Shortwave Radiation (SWR), Photosynthetically Active Radiation (PAR)</td>
</tr>
<tr>
<td valign="middle" align="left">Biological</td>
<td valign="middle" align="left">Chlorophyll Concentration</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s2_3">
<label>2.3</label>
<title>Data preparation and implementation</title>
<p>The NEMO-BAMHBI dataset was vertically averaged over the upper 50 meters of the water column, a reference depth commonly used as an approximation of the euphotic zone in the Black Sea (<xref ref-type="bibr" rid="B83">Serpetti et&#xa0;al., 2025</xref>), where photosynthetic activity and phytoplankton biomass are concentrated. This choice reduces noise from deeper, less biologically relevant layers and ensures that the analysis focuses on surface-driven variability. For each variable, the mean and standard deviation were computed across all spatial grid cells and all time steps in the training periods, and the same normalization parameters were applied to the validation and test sets to avoid information leakage. Other normalization approaches (e.g., log transformations, min&#x2013;max scaling, and Yeo&#x2013;Johnson transformations) were explored to better accommodate the diverse distributions of variables, but standardization consistently yielded the most stable and reliable results in preliminary tests and was retained as the default.</p>
<p>Input sequences of length <italic>w</italic> = 32 days were constructed as model input, with a forecast horizon of <italic>q</italic> = 16 days. These values were selected based on exploratory experiments evaluating model performance across a range of candidate temporal windows, with details summarized in the <xref ref-type="supplementary-material" rid="s12"><bold>Supplementary Material</bold></xref> (Section S1.1). Increasing the input window improved forecast skill up to approximately one month, beyond which performance gains saturated and sensitivity to noise increased. Similarly, forecast skill declined rapidly for horizons beyond approximately two to three weeks, consistent with the limited intrinsic predictability of daily chlorophyll variability.</p>
<p>Marginal improvements were occasionally observed for larger input windows when additional mechanisms were introduced to help organize and extract information from the extended temporal context, such as early attention modules (<xref ref-type="bibr" rid="B47">Hu et&#xa0;al., 2018</xref>). This suggests that longer input windows may be beneficial when combined with architectures explicitly designed to manage longer-term dependencies, a point that remains open for future investigation. To expand the effective training set while limiting redundancy, input sequences were generated using a sliding window with a stride of 15 days. Smaller strides (e.g., 1 day) led to excessive overlap and overfitting, while fully non-overlapping sequences reduced data availability and degraded performance.</p>
<p>Exploratory feature-selection analyses further guided the final choice of input and output variables&#x201d;, using a backward feature elimination strategy (<xref ref-type="bibr" rid="B39">Guyon and Elisseeff, 2003</xref>). All physical and biogeochemical variables listed in <xref ref-type="table" rid="T1"><bold>Table&#xa0;1</bold></xref> were retained as input predictors. While both joint and single-output configurations were explored during model development, the analyses presented here focus on models trained to predict a single target variable at a time (chlorophyll or an individual nutrient). Since chlorophyll is the&#xa0;primary indicator of phytoplankton biomass, the main results&#xa0;and&#xa0;sensitivity analyses focus on chlorophyll for interpretability,&#xa0;with&#xa0;corresponding nutrient results provided in the <xref ref-type="supplementary-material" rid="s12"><bold>Supplementary Material</bold></xref>.</p>
<p>The dataset was split into distinct periods for training, validation, and testing to ensure robust evaluation. After testing multiple partitioning strategies, the final setup used two non-contiguous training periods (1950&#x2013;1969 and 1976&#x2013;2010), with validation data from 1971&#x2013;1975 and test data from 2011&#x2013;2014. This configuration ensured that model performance was assessed on data temporally distant from the training set. A one-month buffer period was added between the splits to reduce potential contamination and bias. Although trained on full-basin data, the model was also applied to smaller sub-regions to investigate localized ecosystem variability and drivers. Four pilot sites were selected to capture contrasting physical and biogeochemical regimes within the Black Sea (<xref ref-type="fig" rid="f2"><bold>Figure&#xa0;2</bold></xref>). The northwestern Black Sea shelf is strongly influenced by riverine nutrient inputs, particularly from the Danube River, which enhance coastal productivity and shape local biogeochemical gradients (<xref ref-type="bibr" rid="B75">Ragueneau et&#xa0;al., 2002</xref>). Basin-scale circulation in the Black Sea includes western and eastern gyres, a dominant rim current, and mesoscale variability that contribute to regional contrasts in circulation and mixing (<xref ref-type="bibr" rid="B91">Stanev and Beckers, 1999</xref>). The Bosporus region reflects exchange dynamics between the Black Sea and the Mediterranean, with distinct effects on stratification and hydrographic structure (<xref ref-type="bibr" rid="B71">&#xd6;zsoy and &#xdc;nl&#xfc;ata, 1997</xref>). The southwestern shelf exhibits different shelf&#x2013;basin interactions compared to the northwestern shelf, while the offshore open-ocean site represents basin-scale conditions where coastal forcing is minimal. These regions reflect contrasting oceanographic regimes representative of major coastal and offshore environments in the Black Sea.</p>
<fig id="f2" position="float">
<label>Figure&#xa0;2</label>
<caption>
<p>Map of the Black Sea with the selected pilot sites: Northwestern Black Sea (red), Bosporus Site (green), Southwestern Black Sea (purple), and an open ocean site (blue). These regions reflect contrasting oceanographic conditions, from coastal riverine influence to offshore environments.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-13-1760162-g002.tif">
<alt-text content-type="machine-generated">Map of the Black Sea showing four selected pilot sites highlighted in different colors. The Northwestern Black Sea is shown in red, the Bosporus Site in green, the Southwestern Black Sea in purple, and an open ocean site in blue. Coastlines and geographic coordinates are displayed. The colored regions mark the selected pilot site locations within the basin.</alt-text>
</graphic></fig>
<p>In addition to the physical and biogeochemical input variables, spatial and temporal information was included to help the model learn location-specific and seasonal patterns. Spatial information was provided through input channels for latitude, longitude, bathymetry, and distance to coast. Temporal information was encoded as the day of the year (DOY) using a standard cyclic sine&#x2013;cosine transformation, day<sub>1</sub> = cos(2<italic>&#x3c0;</italic> DOY<italic>/</italic>365) + 1 and day<sub>2</sub> = sin(2<italic>&#x3c0;</italic> DOY<italic>/</italic>365) + 1, allowing the network to represent seasonal phase without a discontinuity at the year boundary. This helps the network capture repeating seasonal dynamics across the dataset. The contribution of these spatio-temporal predictors was assessed as part of the backward feature elimination procedure described in the <xref ref-type="supplementary-material" rid="s12"><bold>Supplementary Material</bold></xref> (Section S1.1).</p>
</sec>
<sec id="s2_4">
<label>2.4</label>
<title>Evaluation metrics</title>
<p>Model performance is assessed using complementary metrics that quantify both magnitude errors and spatial pattern agreement. Prediction accuracy is evaluated using the root mean squared error (RMSE) and mean absolute error (MAE), which measure the average deviation between predicted and reference values. Spatial pattern correspondence is quantified using the Pearson correlation coefficient, which measures the strength of linear association between predicted and reference maps (<xref ref-type="bibr" rid="B13">Cohen et&#xa0;al., 2009</xref>).</p>
<p>To further assess spatial structural similarity beyond pixel-wise (grid-point) errors, the multi-scale structural similarity index (MS-SSIM) (<xref ref-type="bibr" rid="B98">Wang et&#xa0;al., 2003</xref>) is employed. MS-SSIM compares predicted and reference fields across multiple spatial scales and accounts for differences in contrast, gradients, and structural organization. Although originally developed for image analysis, MS-SSIM has been used in geoscience and meteorological applications to quantify structural realism and spatial coherence in gridded fields (<xref ref-type="bibr" rid="B42">Harris et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B21">Fang et&#xa0;al., 2025</xref>).</p>
<p>Forecast skill as a function of lead time is evaluated using a basin-mean spatial RMSE, obtained by averaging the grid-point RMSE over the full basin for each lead day. A relative RMSE is additionally computed by normalizing the RMSE by the mean chlorophyll concentration of the reference field over the evaluated domain (e.g., at each grid cell for spatial maps or over a pilot site for regional time series), yielding a dimensionless, scale-aware error metric. Relative RMSE was preferred over percentage-based metrics such as the mean absolute percentage error (MAPE) or mean absolute percentage deviation (MAPD) because it remains well defined in low-chlorophyll regimes, where normalization by instantaneous values can lead to unstable or misleading errors.</p>
<p>A daily climatology over the period 1950&#x2013;2014 was constructed as the multi-year mean for each day of the year. To isolate robust seasonal signals, the climatology was smoothed using a Gaussian filter (<xref ref-type="bibr" rid="B92">Steinacker, 2021</xref>) with a temporal standard deviation of 3 days and a spatial standard deviation of [2, 2] grid cells. This smoothed climatology serves both as a baseline reference and for the computation of deseasonalized anomalies, which were obtained by subtracting the climatological mean from each daily field prior to model training.</p>
<p>Several persistence-based benchmarks were used to evaluate the emulator relative to progressively more realistic reference forecasts. Pure persistence assumes that the future state remains equal to the most recent observed value at all lead times (<xref ref-type="bibr" rid="B100">Wilks, 2011</xref>). An anomaly persistence baseline was also considered, where the initial deseasonalized anomaly is assumed to persist and is added back to the corresponding climatological mean (<xref ref-type="bibr" rid="B17">DelSole et&#xa0;al., 2011</xref>; <xref ref-type="bibr" rid="B50">Kirtman et&#xa0;al., 2014</xref>). This removes trivial skill linked to the seasonal cycle.</p>
<p>Finally, a damped anomaly persistence model was implemented,</p>
<disp-formula>
<mml:math display="block" id="M5"><mml:mrow><mml:mi>A</mml:mi><mml:mo>(</mml:mo><mml:mi>t</mml:mi><mml:mo>+</mml:mo><mml:mi>&#x3c4;</mml:mi><mml:mo>)</mml:mo><mml:mo>=</mml:mo><mml:mi>A</mml:mi><mml:mo>(</mml:mo><mml:mi>t</mml:mi><mml:mo>)</mml:mo><mml:mtext>exp</mml:mtext><mml:mo>(</mml:mo><mml:mo>&#x2212;</mml:mo><mml:mi>&#x3c4;</mml:mi><mml:mo stretchy="false">/</mml:mo><mml:msub><mml:mi>&#x3c4;</mml:mi><mml:mi>d</mml:mi></mml:msub><mml:mo>)</mml:mo><mml:mo>,</mml:mo></mml:mrow></mml:math>
</disp-formula>
<p>where <italic>A</italic>(<italic>t</italic>) denotes the anomaly of the target variable at time <italic>t</italic>, <italic>&#x3c4;</italic> is the forecast lead time, and <italic>&#x3c4;<sub>d</sub></italic> is a decorrelation time scale estimated from the temporal autocorrelation of the anomaly time series. This formulation represents the gradual loss of memory in the system and is commonly used as a realistic null model for predictable climate and ocean variability (<xref ref-type="bibr" rid="B67">Newman, 2013</xref>; <xref ref-type="bibr" rid="B68">Niraula and Goessling, 2021</xref>).</p>
</sec>
<sec id="s2_5">
<label>2.5</label>
<title>Model interpretability across global, local, and spatial sensitivities</title>
<p>To interpret the relationships learned by the neural network and quantify the influence of environmental drivers on chlorophyll predictions, a combination of global variance-based, derivative-based, and spatial sensitivity analyses was employed. Together, these methods allow not only the identification of the most influential variables, but also the spatial and temporal scales over which they act.</p>
<sec id="s2_5_1">
<label>2.5.1</label>
<title>Global variance-based sensitivity: Sobol indices</title>
<p>Global sensitivity was assessed using Sobol indices (<xref ref-type="bibr" rid="B70">Owen, 2014</xref>; <xref ref-type="bibr" rid="B22">Fel et&#xa0;al., 2021</xref>) to interpret the predictions produced by the neural network and quantify the relative influence of each input variable on chlorophyll variability. Sobol analysis decomposes the variance of the model output into contributions from individual input variables alone (i.e., first-order indices) and their combined interactions (i.e., total-order indices), thereby enabling quantification of both main and interaction effects.</p>
<p>Because classical Sobol sampling over the full input space is not physically meaningful for ocean states, the analysis was intentionally restricted to a smaller, physically realistic subset of the input-value space, centered on values from the test dataset. Specifically, quasirandom Sobol sequences were generated within a &#xb1;10% interval around the original value of each variable, thereby sampling combinations of all inputs within this constrained range. This perturbation range was chosen as a tradeoff between maintaining physical realism and allowing sufficiently large deviations to elicit a measurable model response, consistent with local sensitivity analysis around climatologically relevant conditions. The analysis thus represents a localized application of the Sobol framework, focused on climatologically relevant conditions rather than a full global exploration of the input space.</p>
<p>First- and total-order Sobol indices were estimated following standard sampling designs that integrate over the joint distributions of all inputs. A total of <italic>N</italic><sub>sobol</sub> = 16386 quasirandom samples were generated per variable, with this number determined from convergence tests to ensure stable estimates of both first- and total-order indices. Each sample was propagated through the trained emulator, and the resulting variance in predicted chlorophyll was used to compute the Sobol sensitivity indices.</p>
</sec>
<sec id="s2_5_2">
<label>2.5.2</label>
<title>Gradient-based sensitivity: DGSM</title>
<p>To complement the variance-based Sobol analysis, Derivative-based Global Sensitivity Measures (DGSM) (<xref ref-type="bibr" rid="B89">Sobol and Kucherenko, 2010</xref>; <xref ref-type="bibr" rid="B53">Kucherenko and Song, 2016</xref>) were computed. DGSM quantify the expected magnitude of squared partial derivatives of the emulator output with respect to each input. Whereas Sobol indices measure the contribution of an input to the output variance, DGSM reflect the instantaneous sensitivity of the model to infinitesimal perturbations in the state space. Consequently, a variable with relatively low Sobol importance may still exhibit high DGSM values if it exerts a strong local dynamical influence on the prediction. One could also examine the sign of the local derivatives to infer the direction of influence, although the present analysis focuses on the overall magnitude to provide a consistent measure of sensitivity across variables and regions.</p>
</sec>
<sec id="s2_5_3">
<label>2.5.3</label>
<title>Local elasticity and spatial scale of influence</title>
<p>Neither Sobol indices nor DGSM indicate whether the model predictions rely on local information or on inputs originating from spatially remote regions. To assess the spatial structure of sensitivities, local elasticity kernels were calculated as</p>
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</disp-formula>
<p>which represent the squared relative influence of perturbing an input variable at grid cell (<italic>i, j</italic>) on the predicted chlorophyll at <inline-formula>
<mml:math display="inline" id="im13"><mml:mrow><mml:mo stretchy="false">(</mml:mo><mml:msub><mml:mi>i</mml:mi><mml:mn>0</mml:mn></mml:msub><mml:mo>,</mml:mo><mml:msub><mml:mi>j</mml:mi><mml:mn>0</mml:mn></mml:msub><mml:mo stretchy="false">)</mml:mo></mml:mrow></mml:math></inline-formula>.</p>
<p>For each test sample and forecast lead, two-dimensional elasticity fields were radially averaged around the grid cell corresponding to the maximum chlorophyll concentration in the predicted chlorophyll field for that sample and lead time. That is, for each spatial map, the single grid cell with the highest chlorophyll value was identified and used as the center for the radial averaging. The radial average was computed by binning all grid cells according to their distance from this center and averaging <italic>E<sub>i,j</sub></italic> within each distance bin. To reduce small-scale noise and emphasize coherent spatial patterns, the elasticity fields were smoothed using a Gaussian kernel with a standard deviation of 75 km prior to averaging. The resulting radial decay profiles describe how the average elasticity amplitude decreases with increasing distance from the chlorophyll maximum (<xref ref-type="bibr" rid="B12">Chelton et&#xa0;al., 2007</xref>, <xref ref-type="bibr" rid="B11">2011</xref>). From these profiles, the e-folding length scale is derived, <italic>L</italic><sub>e</sub>, defined as the distance at which the mean radial elasticity decreases to 1<italic>/</italic>e (approximately 37%) of its maximum value. Small <italic>L</italic><sub>e</sub> values indicate predominantly local control (e.g., vertical mixing or self-dependence), whereas large <italic>L</italic><sub>e</sub> values imply advective or otherwise non-local influence.</p>
<p>Although the emulator uses basin-scale inputs and produces full spatial output maps, the sensitivity analyses were also evaluated separately across regions and seasons. By restricting the evaluation to specific subdomains within the output grid, it becomes possible to quantify regional contrasts in driver importance. Similarly, applying the analyses to selected seasons within the test period allows differences in variable importance across the annual cycle to be assessed. This spatiotemporal breakdown provides a more nuanced interpretation of the learned dependencies of the emulator and improves the ecological relevance of the sensitivity results.</p>
<p>It is important to note that several of the physical and biogeochemical drivers used here are not statistically independent (e.g., MLD, SST, and nutrient concentrations), reflecting genuine oceanographic coupling rather than statistical redundancy. All sensitivity analyses in this study were therefore applied locally around realistic climatological states. The resulting sensitivity metrics should be interpreted as effective sensitivities that account for both direct and correlated influences within the sampled domain, rather than as strictly orthogonal decompositions of independent input effects.</p>
</sec>
</sec>
</sec>
<sec id="s3" sec-type="results">
<label>3</label>
<title>Results</title>
<p>The predictive skill of the emulator was first evaluated in the test period (2011&#x2014;2014) using chlorophyll as the output variable. Performance metrics, spatial error distributions, and the temporal evolution of forecast accuracy are presented below, together with sensitivity analyses to identify key drivers of chlorophyll variability.</p>
<sec id="s3_1">
<label>3.1</label>
<title>Overall model performance</title>
<p>The model demonstrates substantial skill in forecasting chlorophyll changes across the Black Sea (<xref ref-type="fig" rid="f3"><bold>Figure&#xa0;3</bold></xref>). As expected, the prediction error (RMSE) increases with forecast lead time. However, the neural network emulator consistently outperforms all baseline predictions, including climatology and all persistence formulations. After the first two forecast days, the model also surpasses pure persistence, anomaly persistence, and damped anomaly persistence, which assume varying degrees of temporal memory in the initial conditions (<xref ref-type="fig" rid="f3"><bold>Figure&#xa0;3a</bold></xref>). Variability across test samples is illustrated for the emulator to provide context on forecast robustness. Since Climatology is computed by shifting the forecast window in time, it appears constant across lead days and does not reflect increasing forecast uncertainty like the model or persistence do.</p>
<fig id="f3" position="float">
<label>Figure&#xa0;3</label>
<caption>
<p><bold>(a)</bold> Temporal evolution of basin-mean (spatially averaged) RMSE for chlorophyll as a function of forecast lead time, computed over the 2011&#x2013;2014 test period. The neural network emulator (red) is compared against climatology (green dashed), pure persistence (blue), anomaly persistence (purple), and damped anomaly persistence (orange). The shaded envelope indicates emulator variability, quantified as the interquartile range (IQR, 25th&#x2013;75th percentile). <bold>(b)</bold> Spatial distribution of chlorophyll RMSE derived from emulator predictions only, averaged over all forecast lead times (1&#x2013;16 days). <bold>(c)</bold> Spatial distribution of mean relative RMSE (unitless), computed from emulator predictions only by normalizing the RMSE by the local mean chlorophyll concentration and averaged over all lead times.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-13-1760162-g003.tif">
<alt-text content-type="machine-generated">Three-panel figure. Panel (a) shows a line graph of basin-mean root mean square error (RMSE) for chlorophyll over a 16-day forecast lead time. Five prediction methods are compared: neural network emulator (red), climatology (green dashed), persistence (blue), anomaly persistence (purple), and damped anomaly persistence (orange). A shaded region indicates emulator variability using the interquartile range. Panel (b) presents a map of spatially averaged RMSE from emulator predictions across all lead times. Panel (c) shows a map of mean relative RMSE, normalized by local chlorophyll concentration, averaged over all lead times. The maps display spatial distributions of RMSE and relative RMSE across the basin.</alt-text>
</graphic></fig>
<p>During the initial short-range forecast period (<italic>&lt;</italic> 4 days), the basin-mean RMSE increases approximately linearly with lead time. This is followed by a steeper, weakly nonlinear growth, consistent with the gradual loss of predictability as the model and the real system diverge. At longer lead times, the rate of error growth decreases and the RMSE asymptotically approaches the climatological error level, indicating a transition toward the limit of intrinsic predictability for daily chlorophyll variability. Spatially, the model can capture basin-scale chlorophyll patterns, but with heterogeneous performances (<xref ref-type="fig" rid="f3"><bold>Figure&#xa0;3b</bold></xref>). Lower RMSE values are observed across much of the open ocean and eastern Black Sea, while higher errors are concentrated along the northwestern shelf and western coastal regions. This likely reflects the increased physical and biogeochemical variability in coastal and shelf zones, where shallow depths, strong riverine input (for example from the Danube), and complex circulation generate rapid, localized changes in nutrient supply and phytoplankton blooms. Such dynamic environments are inherently harder to forecast than the more stable, stratified open sea, where variability is lower and thus more predictable.</p>
<p>However, the northwestern coastal regions also exhibit substantially higher absolute chlorophyll concentrations, which further contribute to the elevated absolute RMSE in these areas. When considering the relative RMSE, a different spatial pattern emerges (<xref ref-type="fig" rid="f3"><bold>Figure&#xa0;3c</bold></xref>), with higher relative errors in the transitional zone between the northwestern shelf and the deeper basin, as well as in the dynamically active southern central basin east of the Sinop Peninsula.</p>
<p>While RMSE quantifies absolute error, complementary metrics such as MS-SSIM assess spatial structure preservation, and Pearson correlation captures temporal variability. The model improves RMSE by approximately 39&#x2013;60% across variables and also achieves gains of +7&#x2013;12% in MS-SSIM and +11&#x2013;20% in correlation. This demonstrates that the model not only reduces error magnitudes but also effectively captures coherent spatial patterns and regional dynamics, even when pixel-level discrepancies remain (<xref ref-type="table" rid="T2"><bold>Table&#xa0;2</bold></xref>). In addition to the basin-scale metrics reported in <xref ref-type="table" rid="T2"><bold>Table&#xa0;2</bold></xref>, spatiotemporal validation results for nitrate and ammonium are presented in the <xref ref-type="supplementary-material" rid="s12"><bold>Supplementary Material</bold></xref> (Section S1.3).</p>
<table-wrap id="T2" position="float">
<label>Table&#xa0;2</label>
<caption>
<p>Comparison of model and climatology (Clim) performance for chlorophyll (CHL), nitrate (NOS), ammonium (NHS), and phosphate (PO<sub>4</sub>) predictions.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="middle" align="left">Variable</th>
<th valign="middle" align="center">Clim RMSE</th>
<th valign="middle" align="center">RMSE</th>
<th valign="middle" align="center">Clim MS-SSIM</th>
<th valign="middle" align="center">MS-SSIM</th>
<th valign="middle" align="center">Clim Pearson</th>
<th valign="middle" align="center">Pearson</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="middle" align="left">CHL</td>
<td valign="middle" align="center">0.923</td>
<td valign="middle" align="center">0.547 (40.7%)</td>
<td valign="middle" align="center">0.912</td>
<td valign="middle" align="center">0.984 (7.9%)</td>
<td valign="middle" align="center">0.863</td>
<td valign="middle" align="center">0.956 (10.8%)</td>
</tr>
<tr>
<td valign="middle" align="left">Nitrate</td>
<td valign="middle" align="center">1.088</td>
<td valign="middle" align="center">0.656 (39.8%)</td>
<td valign="middle" align="center">0.876</td>
<td valign="middle" align="center">0.983 (12.3%)</td>
<td valign="middle" align="center">0.787</td>
<td valign="middle" align="center">0.916 (16.3%)</td>
</tr>
<tr>
<td valign="middle" align="left">Ammonium</td>
<td valign="middle" align="center">0.428</td>
<td valign="middle" align="center">0.227 (46.9%)</td>
<td valign="middle" align="center">0.887</td>
<td valign="middle" align="center">0.985 (11.0%)</td>
<td valign="middle" align="center">0.778</td>
<td valign="middle" align="center">0.937 (20.4%)</td>
</tr>
<tr>
<td valign="middle" align="left">Phosphate</td>
<td valign="middle" align="center">0.087</td>
<td valign="middle" align="center">0.036 (58.8%)</td>
<td valign="middle" align="center">0.949</td>
<td valign="middle" align="center">0.990 (4.3%)</td>
<td valign="middle" align="center">0.792</td>
<td valign="middle" align="center">0.954 (20.5%)</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>Metrics include RMSE, MS-SSIM, and Pearson correlation, with relative improvements of the model over climatology shown in parentheses.</p></fn>
</table-wrap-foot>
</table-wrap>
<p>Among the nutrient variables, phosphate exhibits the strongest relative improvement across all metrics, with a 58.8% reduction in RMSE and a 20.5% increase in Pearson correlation compared to climatology (<xref ref-type="table" rid="T2"><bold>Table&#xa0;2</bold></xref>). In contrast to chlorophyll, whose RMSE increases rapidly beyond the first few forecast days, phosphate errors increase approximately linearly and more gradually with forecast horizon. Although mean forecast skill for nitrate and ammonium remains high, both variables exhibit a wider spread in prediction variability across test samples, indicating reduced forecast stability relative to phosphate (<xref ref-type="supplementary-material" rid="SF3"><bold>Supplementary Figures S1</bold></xref> and <xref ref-type="supplementary-material" rid="SF4"><bold>S2</bold></xref>). These differences may suggest that phosphate follows more stable and slowly evolving dynamics, while nitrate and ammonium are more sensitive to episodic and spatially heterogeneous processes.</p>
<p>It is worth noticing that large areas of the basin maintain persistently low chlorophyll levels, naturally limiting RMSE and SSIM sensitivity when averaged over the full basin performance while significant improvements relative to the considered baselines are particularly pronounced in biologically active regions. These results confirm that the model delivers meaningful improvements over baseline methods, producing forecasts that are both more accurate and more ecologically realistic at sub-basin and basin scales.</p>
<p>Overall, the results highlight that the emulator is able to minimize absolute errors relative to the outputs of the process-based model, while maintaining both structural and dynamic fidelity in its forecasts. These are critical attributes that support the applications of this emulator in short-term predictions and driver analyses, something which can contribute to more informed and effective ecosystem management in the Black Sea.</p>
<sec id="s3_1_1">
<label>3.1.1</label>
<title>Forecast of bloom dynamics</title>
<p>To illustrate the ability of the model to forecast temporal and spatial dynamics in the Black Sea, <xref ref-type="fig" rid="f4"><bold>Figure&#xa0;4</bold></xref> presents examples of chlorophyll predictions for lead times of <italic>q</italic> = 1 day and <italic>q</italic> = 16 days, respectively. The neural network output is compared with the simulated ground truth (i.e., the NEMO-BAMHBI model), calculating the absolute error across the numerical domain.</p>
<fig id="f4" position="float">
<label>Figure&#xa0;4</label>
<caption>
<p>Example chlorophyll forecasts at lead times of 1 day (<bold>a</bold>, 2012-03-13) and 16 days (<bold>b</bold>, 2012-03-28). Each row shows the simulated reference from NEMO&#x2013;BAMHBI (left), the emulator prediction (center), and the residual (difference between BAMHBI and the emulator, right). Forecast skill remains high at day 1, while larger residuals appear by day 16, particularly in dynamic coastal regions.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-13-1760162-g004.tif">
<alt-text content-type="machine-generated">Example of chlorophyll forecasts at two lead times. The top row (a) corresponds to a 1-day forecast (2012-03-13), and the bottom row (b) to a 16-day forecast (2012-03-28). Each row contains three maps of the Black Sea: the NEMO–BAMHBI reference simulation (left), the emulator prediction (center), and the residual representing the difference between the reference and emulator (right). Colorbars indicate chlorophyll concentration in milligrams per cubic meter, and a separate scale shows residual values.</alt-text>
</graphic></fig>
<p>For short lead times (<italic>q</italic> = 1 day), the forecast reproduces the overall spatial structure of chlorophyll concentrations, with small residuals across most of the basin. Although the network does not perfectly replicate the simulated chlorophyll values or localized peaks, it preserves the main spatial gradients and patterns (<xref ref-type="fig" rid="f4"><bold>Figure&#xa0;4</bold></xref>). For the <italic>q</italic> = 16 day case, residual magnitudes increase, particularly in the northwestern shelf and coastal regions, where physical and biogeochemical variability is highest. Still, in both cases the model reproduces the large-scale distribution and the rapid increase in chlorophyll associated with bloom development. The results indicate that the network captures the underlying spatial and temporal progression toward a bloom, despite underestimating some peak magnitudes. This suggests that the trained network has learned statistical dependencies in the NEMO&#x2013;BAMHBI simulation that are consistent with the emergence of bloom-like conditions over time. An alternative visualization using logarithmic color scaling to emphasize variability in low-chlorophyll regions is provided in the <xref ref-type="supplementary-material" rid="s12"><bold>Supplementary Material</bold></xref> (Section S1.4).</p>
</sec>
<sec id="s3_1_2">
<label>3.1.2</label>
<title>Forecasting at pilot sites</title>
<p>Chlorophyll forecasts at a <italic>q</italic> = 16 days lead time for selected pilot sites are shown in <xref ref-type="fig" rid="f5"><bold>Figure&#xa0;5</bold></xref>. Despite increased uncertainty at this range, the model preserves key spatial gradients and bloom structures. While localized chlorophyll peaks are occasionally underestimated, the neural network captures the broader evolution of phytoplankton concentrations, indicating skill in forecasting regional dynamics. The results show strong agreement between the NEMO-BAMHBI outputs and the emulator predictions across all pilot sites, effectively capturing the seasonal evolution and the timing of major bloom events in both coastal and offshore regions. Quantitative skill metrics (Pearson correlation and normalized RMSE; <xref ref-type="fig" rid="f5"><bold>Figure&#xa0;5</bold></xref>) indicate high overall predictive performance across all regions. Visual inspection of the time series further reveals that while the emulator reproduces the dominant variability well, some sharp chlorophyll peaks and high-frequency fluctuations are occasionally smoothed or slightly underestimated. Despite these localized effects, the emulator consistently reproduces key ecological signals and demonstrates strong predictive skill across diverse environments.</p>
<fig id="f5" position="float">
<label>Figure&#xa0;5</label>
<caption>
<p>Chlorophyll forecasts at a 16-days lead time across the pilot sites from <xref ref-type="fig" rid="f2"><bold>Figure&#xa0;2</bold></xref>. The blue line represents simulation outputs, the red dashed line shows neural network predictions, and the green line indicates the climatological baseline. Panels report Pearson correlation (<italic>r</italic>) and normalized RMSE (NRMSE) computed from regionally averaged time series.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-13-1760162-g005.tif">
<alt-text content-type="machine-generated">Time series plots of chlorophyll concentration at four Black Sea pilot sites: Northwestern Black Sea, Open Ocean, Bosporus Site, and Southwestern Black Sea. Each panel shows regionally averaged chlorophyll forecasts at a 16-day lead time for the period 2011–2014. Three lines are displayed: NEMO–BAMHBI simulation output (blue), neural network emulator prediction (red dashed), and climatological baseline (green). Chlorophyll concentration is shown on the vertical axis and time on the horizontal axis. Each panel reports Pearson correlation (r) and normalized RMSE (NRMSE) values for the emulator relative to the reference simulation.</alt-text>
</graphic></fig>
</sec>
</sec>
<sec id="s3_2">
<label>3.2</label>
<title>Identifying dominant drivers</title>
<p>All basin-scale and spatially averaged results reported here are based on the 2011&#x2013;2014 test period and on sensitivity analyses computed for the emulator trained with the final selected configuration and temporal split, providing a consistent reference framework for interpreting driver importance. In addition to forecasting chlorophyll and nutrient distributions, the emulator model enables analyses of the key environmental drivers influencing these predictions. Specifically, it enables the assessment of which features most directly influence emulator predictions, either alone or in combination with other inputs. Sobol indices have been calculated across the entire Black Sea, as well as within each of the four pilot sites to investigate regional and seasonal differences in dominant drivers. In this context, sensitivity metrics are interpreted at the level of individual predictors, acknowledging that some inputs are physically co-varying, in order to facilitate interpretation of emulator behavior (see <xref ref-type="supplementary-material" rid="s12"><bold>Supplementary Section S1.2</bold></xref>). Alternative approaches, such as grouping correlated variables prior to sensitivity analysis, could provide complementary perspectives, but would reduce variable-level interpretability, which is a central objective of the present analysis.</p>
<p>The sensitivity analysis demonstrates that chlorophyll is the dominant driver for future chlorophyll predictions that typically explains <italic>&gt;</italic> 50% of the variance of the model across the basin and throughout the year (<xref ref-type="fig" rid="f6"><bold>Figure&#xa0;6</bold></xref>). This is not surprising and indicates strong temporal autocorrelation in the dataset. The influence of chlorophyll is highest for short time predictions (<italic>&lt;</italic> 2 days) and decreases toward <italic>q</italic> = 16 days. This decline in feature importance is even more pronounced for the secondary drivers like PAR, whose contribution nearly halves from the first to the last timestep of the forecast horizon. Conversely, important drivers such as ammonium and phosphate show the opposite pattern. Indeed they have negligible impact at the initial timestep but explain 10% of total variance for the last forecast day. Physical variables such as temperature, salinity, mixed layer depth, and shortwave radiation have only modest contributions (1&#x2013;2%), while other drivers, including ocean currents, SSH, and vertical velocity, are negligible (<italic>&lt;</italic> 1%).</p>
<fig id="f6" position="float">
<label>Figure&#xa0;6</label>
<caption>
<p>Total-order Sobol sensitivity indices (<italic>S<sub>T</sub></italic>) for 16 input variables, computed at the basin scale and averaged over the full year. Variables are grouped into low (left panel; mean <italic>S<sub>T</sub></italic> &#x2264; 0.035) and high (right panel; mean <italic>S<sub>T</sub> &gt;</italic> 0.035) sensitivity categories, based on the forecast-period mean (orange bars). The high-sensitivity variables primarily reflect autocorrelation (chlorophyll) and direct light forcing (PAR), which are expected contributors to forecast skill. Bars indicate <italic>S<sub>T</sub></italic> at three temporal aggregations: initial timestep of the forecast (<italic>t</italic><sub>0</sub>, blue), mean over the forecast period (orange), and final timestep of the forecast (<italic>t<sub>q</sub></italic> = 16 days, green). Error bars show the associated confidence intervals.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-13-1760162-g006.tif">
<alt-text content-type="machine-generated">Bar charts showing total-order Sobol sensitivity indices (ST) for 16 input variables, computed at the basin scale. The figure is divided into two panels: the left panel displays variables with lower mean ST values, and the right panel shows variables with higher mean ST values. For each variable, three colored bars represent different forecast aggregations: initial timestep (blue), mean over the forecast period (orange), and final timestep at 16 days (green). Error bars indicate confidence intervals. The horizontal axis lists environmental variables, and the vertical axis shows ST values.</alt-text>
</graphic></fig>
<sec id="s3_2_1">
<label>3.2.1</label>
<title>Seasonal and regional variability in driver importance</title>
<p>While the basin-scale, annually averaged results highlight dominant drivers across the whole Black Sea, the importance of secondary variables appears to vary substantially by region and season. Chlorophyll remains the most important input feature in the forecast, but in specific regions and periods other inputs become important (<xref ref-type="fig" rid="f7"><bold>Figure&#xa0;7</bold></xref>). In particular, light availability, i.e., PAR, shows a considerable regional effect with the Northwestern region having the weakest relative dependency (<xref ref-type="fig" rid="f7"><bold>Figure&#xa0;7</bold></xref>). Additionally, light availability emerges as a significant contributor in winter in the open ocean, in winter and summer in the Southwestern Black Sea, and in summer and autumn in the Bosporus region, where it occasionally exceeds chlorophyll in feature importance. This behavior is consistent with previous observational and modeling studies showing that Black Sea phytoplankton dynamics are strongly regulated by irradiance and mixing-controlled light exposure, particularly during bloom initiation and stratified periods (<xref ref-type="bibr" rid="B66">Mikaelyan et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B52">Kubryakov et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B78">Ricour et&#xa0;al., 2021</xref>). In this context, regional and seasonal variations in the sensitivity of PAR and other light-related predictors reflect how the emulator leverages correlated radiative information, rather than implying distinct or independently identifiable physical processes.</p>
<fig id="f7" position="float">
<label>Figure&#xa0;7</label>
<caption>
<p>Normalized total-order Sobol sensitivity indices (<italic>S<sub>T</sub></italic>) for 16 environmental input variables, computed for chlorophyll predictions at the final forecast timestep (<italic>t<sub>q</sub></italic>). Results are shown across four pilot regions, Northwestern Black Sea, Open Ocean, Bosporus Site, and Southwestern Black Sea, and split by season (winter, spring, summer, autumn). Each column represents a specific region-season combination, while rows correspond to the input variables.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-13-1760162-g007.tif">
<alt-text content-type="machine-generated">Heatmap displaying normalized total-order Sobol sensitivity indices (ST) for 16 environmental input variables. Rows correspond to input variables, and columns represent combinations of four Black Sea regions (Northwestern Black Sea, Open Ocean, Bosporus Site, Southwestern Black Sea) and four seasons (winter, spring, summer, autumn). Each cell is color-coded to indicate the magnitude of the normalized ST value, with a color scale ranging from low to high values. The heatmap displays spatial and seasonal variation in sensitivity across regions and forecast conditions at the final timestep.</alt-text>
</graphic></fig>
<p>In the Northwestern site, the availability of nutrients emerges in the model as a major driver of chlorophyll dynamics. This likely reflects the nutrient-rich and shallow shelf environment, strongly influenced by runoff from the Danube River. In this setting, primary production is less constrained by light and more shaped by biogeochemical processes, including fluctuations in nutrient availability, recycling, and regeneration. Although chlorophyll autocorrelation remains dominant, nutrients such as ammonium and phosphate contribute 8&#x2013;12% to the model sensitivity in summer, when stratification strengthens and nutrients become more influential. This interpretation is consistent with previous observational and modeling studies, which identify nutrient supply and recycling as dominant controls on phytoplankton variability on the northwestern Black Sea shelf (<xref ref-type="bibr" rid="B104">Yunev et&#xa0;al., 2007</xref>; <xref ref-type="bibr" rid="B33">Gr&#xe9;goire et&#xa0;al., 2008</xref>; <xref ref-type="bibr" rid="B105">Yunev et&#xa0;al., 2021</xref>). Ocean currents (u, v, w) have a larger role in regions like the Bosporus and Southwestern Black Sea. This likely reflects the importance of ocean transport and mixing processes in these coastal areas. Variables like dissolved oxygen and short wave radiation also show elevated sensitivity in several regions. While they are not a direct driver of phytoplankton dynamics, they emerge as important features in the model and they may serve as proxies for phytoplankton states. Indeed they are variables tightly linked to water column stratification and biological activity, hence perturbations in oxygen and short wave radiation indirectly affect predictions through nonlinear correlations learned by the model.</p>
</sec>
<sec id="s3_2_2">
<label>3.2.2</label>
<title>Local and derivative-based sensitivity analyses</title>
<p>While Sobol indices quantify the proportion of output variance attributable to each input, they do not directly describe how steeply or locally the model output responds to perturbations in those inputs. To complement the variance-based perspective, Derivative-based Global Sensitivity Measures (DGSM) were computed, which estimate the mean squared gradient of the emulator output with respect to each input variable. Using DGSM, the overall responsiveness of the model is captured, integrating local derivative information across the input distribution.</p>
<p>In <xref ref-type="fig" rid="f8"><bold>Figure&#xa0;8</bold></xref>, the median DGSM shares are shown for the top non-chlorophyll drivers, aggregated for early (Days 1&#x2013;3) and late (Days 11&#x2013;15) forecast windows across the four pilot regions. Although chlorophyll itself is consistently the strongest driver in absolute terms, it is omitted from the figure to better highlight the environmental variables that modulate or enable chlorophyll predictions beyond simple autocorrelation. During the early forecast horizon, light availability (PAR) emerges as the most important external driver across most regions, indicating that short-term chlorophyll predictability is strongly linked to surface irradiance and growth potential. At longer lead times, nutrients, particularly ammonium and nitrate, become increasingly influential, reflecting a transition toward nutrient-controlled biomass accumulation. Physical variables such as mixed-layer depth and salinity maintain moderate but regionally consistent contributions. Dissolved oxygen also appears, not as a causal driver but likely as a proxy for stratification and biological activity.</p>
<fig id="f8" position="float">
<label>Figure&#xa0;8</label>
<caption>
<p>Derivative-based global sensitivity measures (DGSM) showing the top four non-chlorophyll drivers for early (days 1&#x2013;3) and late (days 11&#x2013;15) forecast horizons. Bars represent median driver shares normalized over all non-chlorophyll inputs, grouped by region and colored by driver category.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-13-1760162-g008.tif">
<alt-text content-type="machine-generated">Bar chart matrix displaying derivative-based global sensitivity measures (DGSM) for the top four non-chlorophyll input drivers. Results are shown for two forecast periods: early (Days 1–3) and late (Days 11–15). Separate panels correspond to different regions, including Basin, Northwestern, Open Ocean, Bosporus, and Southwestern Black Sea. Within each panel, bars represent median driver shares normalized across non-chlorophyll inputs. Bars are color-coded by driver category: physical (blue), nutrients (green), light-related variables (orange), and other variables (gray). Percentage values are shown above each bar.</alt-text>
</graphic></fig>
</sec>
<sec id="s3_2_3">
<label>3.2.3</label>
<title>Seasonal locality of influence</title>
<p>To assess whether the emulator relies on local or spatially remote inputs, we analyze the seasonal evolution of the elasticity length scale <italic>L<sub>e</sub></italic> derived from the radial decay of the elasticity kernels. <xref ref-type="fig" rid="f9"><bold>Figure&#xa0;9</bold></xref> summarizes the seasonal evolution of <italic>L<sub>e</sub></italic> for the most influential variables (as ranked by DGSM), allowing us to evaluate whether their predictive influence is predominantly local or extends over larger spatial scales. Chlorophyll exhibits a significant decrease in <italic>L<sub>e</sub></italic> with increasing lead time across most seasons, indicating that the emulator increasingly relies on local information as the forecast progresses. This behavior could indicate a strong temporal autocorrelation of chlorophyll. Once a chlorophyll patch is present, its short-term evolution is largely determined by local persistence, biological growth or decay, and vertical mixing, rather than by lateral inputs. Over time, horizontal gradients weaken, spatial coherence decreases, and the most informative predictor of future chlorophyll becomes the chlorophyll already present at the same location. As a result, the influence radius of chlorophyll contracts rather than expands with lead time.</p>
<fig id="f9" position="float">
<label>Figure&#xa0;9</label>
<caption>
<p>Seasonal evolution of non-locality in emulator sensitivities. Each panel shows one season: <bold>(A)</bold> Winter, <bold>(B)</bold> Spring, <bold>(C)</bold> Summer, and <bold>(D)</bold> Autumn. The e-folding length scale (<italic>L<sub>e</sub></italic>) is shown at the initial forecast time (<italic>t</italic><sub>0</sub>, open circles) and the final lead time (<italic>t<sub>q</sub></italic>, filled circles). Line color encodes &#x394;<italic>L<sub>e</sub></italic>, where red indicates increasing spatial influence, blue indicates contraction. Variables are ordered by decreasing DGSM sensitivity.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-13-1760162-g009.tif">
<alt-text content-type="machine-generated">Four grouped horizontal scatter panels labeled Winter, Spring, Summer, and Autumn show e-folding length scale (Le) values for seven variables: chlorophyll, PAR, nitrate, ammonium, v, salinity, and silicate. The x-axis represents Le in kilometers, and variables are listed vertically. Open circles indicate initial timestep values (t₀), and filled black circles indicate final timestep values (t_q). Horizontal colored lines connect the two points for each variable, with color representing the change in Le (ΔLe). A vertical color bar on the right shows ΔLe in kilometers, ranging from blue (negative change) to red (positive change). A legend identifies circle symbols.</alt-text>
</graphic></fig>
<p>In contrast, nutrient variables such as nitrate and ammonium often show increasing <italic>L<sub>e</sub></italic> with lead time, particularly in spring and summer. Their influence does not act instantaneously or locally. Instead, elevated nutrient concentrations at one location may stimulate chlorophyll growth elsewhere, after being transported by advection or mixing into well-lit surface waters. The resulting biomass may only reach the prediction location several days later. Thus, nutrient influence is inherently both indirect and spatially displaced in time, giving rise to a growth in <italic>L<sub>e</sub></italic> with forecast time. Rather than indicating model instability, this increase in spatial range reflects realistic ecosystem dynamics, nutrients act as slowly varying background conditions that modulate bloom development over broader regions.</p>
<p>The opposite evolution of <italic>L<sub>e</sub></italic> for chlorophyll and nutrients therefore highlights two different forms of predictability in the emulator. Chlorophyll predictions at short lead times are dominated by persistence and local memory (low <italic>L<sub>e</sub></italic> that decreases with time), whereas at longer lead times the model increasingly relies on basin-scale nutrient gradients and other environmental drivers whose influence becomes more spatially extensive.</p>
</sec>
</sec>
</sec>
<sec id="s4" sec-type="discussion">
<label>4</label>
<title>Discussion</title>
<sec id="s4_1">
<label>4.1</label>
<title>General features and applications</title>
<p>A neural network-based emulator (i.e., surrogate model) has been developed and tested to forecast the output of a process-based ocean&#x2013;biogeochemical model for chlorophyll and nutrient concentrations in the Black Sea. The results show that the model can reproduce the spatiotemporal variability of both chlorophyll and nutrients with high accuracy and low errors. This suggests that the machine learning model has effectively learned the key ecosystem dynamics simulated by the more complex process-based ocean model for the Black Sea.</p>
<p>The availability of an accurate emulator offers several key advantages in predicting and understanding dynamics in the Black Sea. First, it dramatically reduces computational costs, enabling faster simulations that are particularly important for real-time forecasting and scenario analysis. For reference, the NEMO&#x2013;BAMHBI configuration used in this study (15 km horizontal resolution, without data assimilation) requires on the order of one hour of wall-clock time to simulate one model year using approximately 192 CPU cores. In contrast, once trained, the neural network emulator produces a 16-day chlorophyll forecast in a fraction of a second on a single GPU, while training the emulator requires on the order of a few hours on a modern GPU. This represents several orders of magnitude reduction in computational cost for inference compared to the original process-based model. Second, it facilitates extensive sensitivity analyses and ensemble simulations that would be very expensive with the original process-based model. Sensitivity analyses including variance-based (Sobol), derivative-based (DGSM), and elasticity-based locality metrics can be used in combination to analyze the feature importance of the input variables used in the model, thus helping to understand ecological surface-layer drivers of specific ecosystem components. Additionally, the emulator can capture essential dynamics of the marine ecosystem, hence it can serve as an effective tool for exploring responses of the system to changing environmental conditions or management interventions. This is particularly important for supporting decision-making in marine resource management and climate adaptation planning.</p>
<p>The developed emulator, trained to forecast multivariate data up to <italic>q</italic> = 16 days ahead, provides considerable skill for short-term forecasting and adaptive environmental management in the Black Sea. The 16-day forecast window considered here is illustrative in that respect. Indeed, the emulator framework can be tailored to specific regional or application needs, which can be done by increasing the length of the input window <italic>w</italic>, adjusting the forecast horizon <italic>q</italic>, or moving from chlorophyll and nutrients to other target variables. On the other hand, the suitability of a given forecasting range also depends on the local temporal dynamics and predictability. In more stable regions, longer forecasts may remain reliable, while highly dynamic areas may benefit from shorter high-frequency updates. The use in inputs of high-resolution observations can also be considered to improve the characterization of local dynamics and to improve predictive skill. This theme has not been directly addressed in this paper, but it may provide an interesting future research direction.</p>
<p>Within the flexible framework, the emulator can support a range of potential, model-based application domains. When trained on oxygen fields from a biogeochemical model, short-range forecasts could be explored as part of numerical experiments or prototype early-warning systems for hypoxic conditions in the Black Sea. Similarly, emulator-based forecasts of modeled nutrient dynamics (e.g., nitrate and phosphate) may be used to investigate the sensitivity of nutrient distributions to episodic inputs, such as rainfall-driven runoff or seasonal agricultural activity, within scenario-based analyses. In fisheries and ecosystem management contexts, the emulator may serve as a rapid exploratory tool to assess how modeled environmental conditions relevant to spawning habitats or migration corridors respond to changing physical or biogeochemical drivers.</p>
<p>A promising application of this framework may lie in the investigation of extreme or rapidly evolving events, such as harmful algal blooms (HABs), which pose serious threats to marine ecosystems, fisheries, and coastal livelihoods. However, the present study does not explicitly evaluate predictive skill during strongly anomalous years, and the temporal test period primarily reflects typical variability rather than rare extremes. In addition, part of the short-term forecast skill arises from the strong autocorrelation of chlorophyll and nutrient fields, which may reduce predictive capability during abrupt regime shifts or externally forced events.</p>
<p>Within these limitations, the emulator could nevertheless be used to explore the emergence of bloom-like conditions in numerical simulations by identifying modeled precursors, such as rapid chlorophyll accumulation or elevated nutrient availability. Recent work has demonstrated the feasibility of ML-based HAB prediction. For instance, <xref ref-type="bibr" rid="B38">Gupta et&#xa0;al. (2023)</xref> developed a machine learning model to forecast cyanobacterial bloom intensity in Lake Erie at sub-monthly lead times using meteorological and remote sensing data. On a broader scale, <xref ref-type="bibr" rid="B101">Wu et&#xa0;al. (2025)</xref> proposed a global deep learning framework to predict surface chlorophyll concentrations from physical oceanographic inputs, demonstrating strong performance across multiple marine regions. Within this context, the emulator developed here provides a complementary basin-scale forecasting capability for both chlorophyll and nutrient dynamics, enabling future HAB early-warning applications.</p>
</sec>
<sec id="s4_2">
<label>4.2</label>
<title>Model training and limitations</title>
<p>The emulator was trained on NEMO&#x2013;BAMHBI simulation data spanning 1950&#x2013;2014, which naturally constrains what it can learn about the behavior of the system. This &#x223c;65-year period captures a range of historical conditions, including the mid-20th century eutrophication and subsequent ecosystem regime shifts in the Black Sea (<xref ref-type="bibr" rid="B64">Mee, 1992</xref>; <xref ref-type="bibr" rid="B69">Oguz and Velikova, 2010</xref>).</p>
<p>It must be noted that the emulator is not simply interpolating patterns from the past but learns underlying statistical and dynamical relationships between key biogeochemical and physical variables as represented in the NEMO&#x2013;BAMHBI model. This enables the emulator to capture consistent dependencies and interactions within the NEMO&#x2013;BAMHBI system, allowing it to generate plausible responses under a range of input conditions that remain within the domain of the training data. As a result, the emulator can be used to explore and anticipate potential future states of the Black Sea ecosystem within the modeled framework, particularly when these remain similar to the historical variability represented in the training period. However, this predictive capability is inherently constrained by the boundaries of the training data (1950&#x2013;2014). While the emulator may generalize to near-future scenarios, its reliability diminishes when exposed to forcing conditions or extreme events that lie well outside the historical range. Hence, while the emulator provides a powerful tool for efficient scenario testing and short- to medium-term forecasting, caution must be exercised when interpreting results under strongly non-stationary future climates.</p>
<p>To address these limitations, future work could incorporate simulation outputs extending to future scenarios, comparing model performance when trained on different time periods. Training the emulator on both historical and projected data would allow it to learn evolving ecosystem responses under climate change as represented in numerical models and improve its robustness when applied to novel conditions. This would also enable investigation of how dominant phytoplankton drivers, and their relative importance as inferred from sensitivity analyses, may shift over time, for instance from nutrient-driven dynamics in the past to increased control by temperature, light, or salinity in a more stratified and saline future (<xref ref-type="bibr" rid="B74">P&#xf6;rtner et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B73">Podymov et&#xa0;al., 2021</xref>). An additional important extension would be to explicitly enforce biogeochemical mass-balance constraints within the neural network, for example by ensuring consistency between phytoplankton growth and nutrient uptake according to Redfield-type stoichiometric relationships (<xref ref-type="bibr" rid="B77">Redfield, 1958</xref>; <xref ref-type="bibr" rid="B28">Geider and La Roche, 2002</xref>). Such physics- and ecology-informed constraints could further enhance the physical realism and long-term stability of emulator-based forecasts and could be implemented within a physics-informed neural network (PINN) framework (<xref ref-type="bibr" rid="B76">Raissi et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B48">Karniadakis et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B4">Battina et&#xa0;al., 2025</xref>).</p>
<p>The spatial and vertical resolution of the surrogate model is inherently constrained by the resolution of the underlying NEMO&#x2013;BAMHBI simulation data, which provides daily outputs at approximately 15 km horizontal resolution. While sufficient for capturing mesoscale and large submesoscale variability, this resolution limits the ability of the model to represent fine-scale coastal processes such as narrow boundary currents, sharp frontal gradients, and localized river plumes. Such sub-grid features may be smoothed or underrepresented, potentially leading to an underestimation of extreme values and ecological hotspots. Vertically, this study averaged the upper 50 m of the water column to focus on the photosynthetically active layer and reduce model complexity. While this approach emphasizes the biologically productive zone, it inevitably obscures vertical structure. The Black Sea is known for exhibiting a pronounced deep chlorophyll maximum (DCM) around 30&#x2013;40 m depth, which can contribute substantially to the total chlorophyll inventory (<xref ref-type="bibr" rid="B78">Ricour et&#xa0;al., 2021</xref>). Averaging across this depth range may flatten key features associated with stratification and vertical nutrient gradients, reducing model sensitivity to processes such as nutrient entrainment from below the mixed layer. Alternative strategies such as mixed-layer-informed averaging or retaining vertical resolution in a simplified multi-layer format could offer improved representation of subsurface dynamics without compromising computational efficiency. Future work may explore these directions to further enhance emulator accuracy and ecological realism at the basin scale. Consequently, interpretations of sensitivity and feature-importance results should be understood as reflecting correlations within the vertically averaged surface layer and their consistency with known physical and biogeochemical processes, rather than as a direct resolution of underlying vertical mechanisms such as mixing or nutrient entrainment.</p>
<p>Beyond resolution-related constraints, an additional limitation concerns the choice of input predictors. In addition to physical and biogeochemical predictors, the emulator was provided with explicit spatial (latitude, longitude, bathymetry, distance to coast) and temporal (cyclic day-of-year) context. These variables were evaluated implicitly during backward feature elimination and were retained because their removal resulted in a modest but systematic degradation of validation performance, particularly affecting spatial coherence and seasonal phase alignment. While a 3D U-Net can infer relative spatio-temporal structure from multivariate input fields alone, explicit context variables reduce ambiguity in a geographically heterogeneous basin such as the Black Sea. Importantly, these predictors act as conditioning information rather than mechanistic drivers, and their inclusion may reduce generalization under strongly nonstationary or climate-change conditions where spatial&#x2013;seasonal relationships evolve beyond the training distribution. For this reason, sensitivity analyses in this study emphasize physical and biogeochemical variables, and future work will explicitly isolate, quantify, and compare the contribution of spatio-temporal context predictors, both individually and in grouped form, to better assess their influence, interpretability, and potential spatio-temporal biases.</p>
<p>A related consideration is that several candidate predictors are partially redundant or physically co-varying, which can complicate attribution and mask more physically interpretable drivers. As mentioned in <xref ref-type="supplementary-material" rid="s12"><bold>Supplementary Material</bold></xref> (Section S1.1), most available outputs from NEMO&#x2013;BAMHBI were initially included as potential inputs. A stepwise elimination approach was then used to remove variables that did not improve model performance, retaining only those that showed a measurable effect. While this strategy helped identify the most influential drivers, it also introduced the risk that redundant inputs could mask the importance of more physically meaningful ones.</p>
<p>For example, SWR was initially retained due to its moderate importance scores. However, SWR is not a direct forcing term in the chlorophyll dynamics; its main role is as a surface heat source in the temperature equation of NEMO&#x2013;BAMHBI. Since temperature was already included as an input, SWR may have partially masked the relative importance of temperature in the model. Furthermore, PAR captures the biologically relevant component of incoming light more directly than SWR. This suggests that the sensitivity attributed to SWR primarily reflects shared variance with thermodynamic and radiative predictors rather than an independent biological effect.</p>
<p>Moreover, the sensitivity analyses, including variance-based Sobol indices, derivative-based DGSM, and elasticity-based locality metrics, revealed that the importance of different drivers varies markedly across regions and seasons. For instance, nutrient variables such as ammonium, nitrate, and phosphate exerted greater influence at later forecast lead times, particularly in coastal areas and during spring bloom periods, whereas light-related variables such as PAR dominated during summer. This spatiotemporal heterogeneity underscores the value of regionalized model interpretation: chlorophyll dynamics in the Black Sea are not governed by uniform processes, but by distinct environmental drivers that vary with both location and time. Recognizing this variation is important for designing targeted monitoring strategies and region-specific management interventions.</p>
</sec>
<sec id="s4_3">
<label>4.3</label>
<title>Outlook for deep learning emulators in oceanography</title>
<p>Recent advances in hybrid machine learning approaches have shown promising results for improving the transferability of surrogate models to real-world observations. Neural networks pre-trained on large numerical model simulations and subsequently fine-tuned on observational data, such as satellite-derived sea surface height, SST, chlorophyll, or <italic>in situ</italic> measurements, have been shown to achieve superior predictive skill, improved generalization, and greater physical consistency than models trained solely on either data source (<xref ref-type="bibr" rid="B7">Buongiorno Nardelli et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B85">Shin et&#xa0;al., 2024</xref>; <xref ref-type="bibr" rid="B62">Martin et&#xa0;al., 2024</xref>; <xref ref-type="bibr" rid="B101">Wu et&#xa0;al., 2025</xref>). For instance, hybrid training has been successfully applied to sharpen altimeter sea level maps (<xref ref-type="bibr" rid="B3">Archambault et&#xa0;al., 2024</xref>), upscale air&#x2013;sea CO<sub>2</sub> fluxes (<xref ref-type="bibr" rid="B49">Kim et&#xa0;al., 2024</xref>), and reconstruct subsurface properties (<xref ref-type="bibr" rid="B58">Lentz et&#xa0;al., 2025</xref>). In the study by <xref ref-type="bibr" rid="B2">Amadio et&#xa0;al. (2024)</xref>, a neural network was used to reconstruct nitrate profiles from Argo oxygen data, and the output was assimilated into a Mediterranean biogeochemical model, improving basin-scale nitrate and oxygen dynamics.</p>
<p>Applying a similar approach in this study, by adapting the emulator architecture to align better with available observational data and fine-tuning it on real chlorophyll or nutrient measurements (such as satellite ocean color or Argo profiles), may reduce simulation-derived biases and enable forecasting directly from observation-based inputs, thereby bridging the gap between model training and operational use. However, such posterior neural network&#x2013;based assimilation should not be seen as a replacement for established data assimilation systems like 4DVAR (<xref ref-type="bibr" rid="B8">Carrassi et&#xa0;al., 2018</xref>), which have a better theoretical basis and are physically rigorous. Its main advantage lies in practicality, as it allows additional observations to be incorporated without requiring access to the source code of the numerical model, adjoint system, or involvement of model developers, which is often time-consuming and costly.</p>
<p>Finally, as computational power and GPU capabilities continue to advance, modeling the entire water column, or at least a part of it, using neural networks may become feasible. This approach would allow for a more comprehensive representation of vertical ecosystem dynamics, eliminating the need for depth averaging and potentially improving the ability of the surrogate model to simulate processes occurring throughout the full depth range of the Black Sea. Exploring these possibilities in future studies could further enhance the robustness and applicability of neural network-based approaches for marine ecosystem modeling.</p>
</sec>
</sec>
<sec id="s5" sec-type="conclusions">
<label>5</label>
<title>Conclusion</title>
<p>In this study, we successfully developed neural network&#x2013;based emulator models for the Black Sea capable of forecasting chlorophyll and nutrient dynamics. The emulators reproduced both the spatial distribution and regional-scale time series of key biogeochemical variables with low error scores.</p>
<p>Beyond forecasting skill, the emulator framework enabled a comprehensive sensitivity analysis using variance-based Sobol indices, derivative-based global sensitivity measures (DGSM), and elasticity-based locality metrics. Sobol indices showed that chlorophyll predictions were largely driven by temporal autocorrelation, while variables such as PAR and nutrients (e.g., ammonium and phosphate) also played substantial roles at the basin scale. DGSM revealed a shift from light to nutrient control across forecast horizons, and elasticity analyses demonstrated that chlorophyll influence remained predominantly local, whereas nutrient effects operated over broader spatial and temporal scales.</p>
<p>Importantly, the influence of these drivers varied considerably across regions and seasons, reflecting the heterogeneity of environmental controls within the Black Sea ecosystem. Overall, the results demonstrate that neural network emulators trained on&#xa0;ocean simulation data can serve not only as fast and efficient&#xa0;scenario-testing tools, but also as effective frameworks for&#xa0;conducting targeted &#x201c;what-if&#x201d; experiments and for understanding&#xa0;marine ecosystem dynamics through sensitivity-based interpretation of their inputs. In a system such as the Black Sea, where eutrophication, stratification, and harmful algal blooms remain major concerns, this approach offers clear potential for early-warning applications and for supporting region-specific ecosystem management. Future work should focus on extending the training to include climate-change scenarios and on incorporating biogeochemical conservation constraints to further&#xa0;enhance physical realism and robustness under non-stationary conditions.</p>
</sec>
</body>
<back>
<sec id="s6" sec-type="data-availability">
<title>Data availability statement</title>
<p>Publicly available datasets were analyzed in this study. The underlying NEMO&#x2013;BAMHBI hindcast simulations can be found here: <uri xlink:href="http://ftp.climato.be/BRIDGE-BS/ULiege-MAR_MPI-hindcast_DAILY/">http://ftp.climato.be/BRIDGE-BS/ULiege-MAR_MPI-hindcast_DAILY/</uri>. The derived emulator outputs and processed datasets are available from the corresponding author upon reasonable request.</p></sec>
<sec id="s7" sec-type="author-contributions">
<title>Author contributions</title>
<p>PS: Data curation, Visualization, Resources, Conceptualization, Validation, Formal Analysis, Project administration, Writing &#x2013; review &amp; editing, Methodology, Investigation, Writing &#x2013; original draft, Software. ACha: Formal Analysis, Writing &#x2013; original draft, Investigation, Visualization, Writing &#x2013; review &amp; editing, Conceptualization. MG: Data curation, Methodology, Validation, Investigation, Resources, Writing &#x2013; review &amp; editing. LV: Data curation, Methodology, Validation, Investigation, Resources, Writing &#x2013; review &amp; editing. FR: Conceptualization, Investigation, Methodology, Validation, Writing &#x2013; review &amp; editing, Supervision, Visualization, Writing &#x2013; original draft. AChr: Conceptualization, Methodology, Visualization, Validation, Supervision, Writing &#x2013; original draft, Investigation, Writing &#x2013; review &amp; editing. MS: Supervision, Funding acquisition, Writing &#x2013; review &amp; editing, Writing &#x2013; original draft, Investigation, Conceptualization, Validation, Visualization, Methodology. PM: Project administration, Validation, Supervision, Methodology, Visualization, Funding acquisition, Conceptualization, Investigation, Writing &#x2013; original draft, Writing &#x2013; review &amp; editing.</p></sec>
<sec id="s9" sec-type="COI-statement">
<title>Conflict of interest</title>
<p>The author(s) declared that this work 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="ai-statement">
<title>Generative AI statement</title>
<p>The author(s) declared that generative AI was used in the creation of this manuscript. Generative AI was used to assist with grammar and language polishing, and to streamline and debug plotting and TensorFlow scripts. All analyses, interpretations, and conclusions were conceived, verified, and approved by the authors, who take full responsibility for the scientific content of the 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="s11" 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="s12" 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.2026.1760162/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fmars.2026.1760162/full#supplementary-material</ext-link></p>
<supplementary-material xlink:href="DataSheet1.pdf" id="SF1" mimetype="application/pdf"><label>Supplementary Table&#xa0;1</label>
<caption>
<p>Hyperparameter ranges explored during architecture selection and training of the 3D U-Net emulator. Bold values indicate the final configuration used in the experiments.</p>
</caption></supplementary-material>
<supplementary-material xlink:href="DataSheet1.pdf" id="SF2" mimetype="application/pdf"><label>Supplementary Table&#xa0;2</label>
<caption>
<p>Strong pairwise Spearman rank correlations (|<italic>&#x3c1;</italic>| &#x2265; 0.6) among dynamic input variables used in the sensitivity analyses (Sobol, DGSM, and elasticity). Variable names follow the categories and terminology in <xref ref-type="table" rid="T1"><bold>Table&#xa0;1</bold></xref>.</p>
</caption></supplementary-material>
<supplementary-material xlink:href="DataSheet1.pdf" id="SF3" mimetype="application/pdf"><label>Supplementary Figure&#xa0;1</label>
<caption>
<p>Nitrate forecast performance. <bold>(a)</bold> Basin-mean RMSE as a function of lead time for the emulator (red), persistence (blue), anomaly persistence (purple), damped anomaly persistence (orange), and climatology (green dashed). Shaded regions indicate emulator variability across test samples. <bold>(b)</bold> Spatial distribution of mean RMSE and <bold>(c)</bold> relative RMSE over the test period (2011&#x2013;2014).</p>
</caption></supplementary-material>
<supplementary-material xlink:href="DataSheet1.pdf" id="SF4" mimetype="application/pdf"><label>Supplementary Figure&#xa0;2</label>
<caption>
<p>Ammonium forecast performance. <bold>(a)</bold> Basin-mean RMSE as a function of lead time for the emulator (red), persistence (blue), anomaly persistence (purple), damped anomaly persistence (orange), and climatology (green dashed). Shaded regions indicate emulator variability across test samples. <bold>(b)</bold> Spatial distribution of mean RMSE and <bold>(c)</bold> relative RMSE over the test period (2011&#x2013;2014).</p>
</caption></supplementary-material>
<supplementary-material xlink:href="DataSheet1.pdf" id="SF5" mimetype="application/pdf"><label>Supplementary Figure&#xa0;3</label>
<caption>
<p>Phosphate forecast performance. <bold>(a)</bold> Basin-mean RMSE as a function of lead time for the emulator and baseline methods. Shaded regions indicate emulator variability across test samples. <bold>(b)</bold> Spatial distribution of mean RMSE and <bold>(c)</bold> relative RMSE over the test period (2011&#x2013;2014).</p>
</caption></supplementary-material>
<supplementary-material xlink:href="DataSheet1.pdf" id="SF6" mimetype="application/pdf"><label>Supplementary Figure&#xa0;4</label>
<caption>
<p>Example phosphate forecasts at lead times of 1 day <bold>(a)</bold> and 32 days <bold>(b)</bold>. Each row shows the simulated reference from NEMO&#x2013;BAMHBI (left), the emulator prediction (center), and the absolute error (right). Forecast skill is high at short lead time, while larger errors emerge at longer lead times, although the large-scale spatial structure and basin-scale variability are retained.</p>
</caption></supplementary-material>
<supplementary-material xlink:href="DataSheet1.pdf" id="SF7" mimetype="application/pdf"><label>Supplementary Figure&#xa0;5</label>
<caption>
<p>Logarithmic visualization of the chlorophyll forecast examples shown in <xref ref-type="fig" rid="f4"><bold>Figure&#xa0;4</bold></xref>. Panels show the NEMO&#x2013;BAMHBI reference simulation (left) and emulator prediction (right) for lead times of 1 day <bold>(a)</bold> and 16 days <bold>(b)</bold>. Logarithmic color scaling enhances variability in low-concentration regions while retaining the overall spatial patterns.</p>
</caption></supplementary-material>
<supplementary-material xlink:href="DataSheet1.pdf" id="SF8" mimetype="application/pdf"><label>Supplementary Figure&#xa0;6</label>
<caption>
<p>Seasonal basin-mean RMSE as a function of forecast lead time for winter, spring, summer, and autumn. Results are shown for the emulator (red), persistence baseline (blue), and climatology (green dashed). Shaded regions indicate emulator variability across test samples.</p>
</caption></supplementary-material>
<supplementary-material xlink:href="DataSheet1.pdf" id="SF9" mimetype="application/pdf"><label>Supplementary Figure&#xa0;7</label>
<caption>
<p>Regional basin-mean RMSE as a function of forecast lead time for four representative subregions of the Black Sea: Northwestern Black Sea, Open Ocean, Bosporus site, and Southwestern Black Sea. Curves and shading follow the same conventions as in <xref ref-type="supplementary-material" rid="SF6"><bold>Supplementary Figure S6</bold></xref>.</p>
</caption></supplementary-material></sec>
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<fn-group>
<fn id="n1" fn-type="custom" custom-type="edited-by">
<p>Edited by: <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/705615">Catherine Marie Schmechtig</ext-link>, UMS3455 Observatoire des sciences de l&#x2019;Univers Paris-Centre Ecce Terra (ECCE TERRA), France</p></fn>
<fn id="n2" fn-type="custom" custom-type="reviewed-by">
<p>Reviewed by: <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/1804394">Flavien Petit</ext-link>, Sorbonne Universit&#xe9;s, France</p>
<p><ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/2051493">Joana Roussillon</ext-link>, Institut de Recherche Pour le D&#xe9;veloppement (IRD), France</p></fn>
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