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            <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/dataset/1010420.rdf" xlink:actuate="onRequest">Larval fish observations, environmental data, and associated analysis code from 1995-2018 from Mexico, USA, and Canada</gmx:Anchor>
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            <gco:CharacterString>Cite this dataset as: Dale, K., Ciannelli, L., Fiechter, J., Asch, R. G., Pozo Buil, M., Brodeur, R. D., García Gómez, R., Field, J., Galbraith, M., Howard, R. (2026) Larval fish observations, environmental data, and associated analysis code from 1995-2018 from Mexico, USA, and Canada. Biological and Chemical Oceanography Data Management Office (BCO-DMO). (Version 1) Version Date 2026-10-21 [if applicable, indicate subset used]. doi:10.26008/1912/bco-dmo.1010420.1 [access date]</gco:CharacterString>
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        <gco:CharacterString>Spatiotemporal tradeoffs manuscript Dataset Description:  Methods and Sampling: &amp;lt;p&amp;gt;We collated larval fish density data in larvae/m&amp;lt;sup&amp;gt;3&amp;lt;/sup&amp;gt; from six long-term ichthyoplankton sampling programs covering the region between the southern part of the Baja California Peninsula to the Alaska Peninsula in the western Gulf of Alaska. These surveys were the National Oceanic and Atmospheric Administration (NOAA) Ecosystems and Fisheries Oceanography Coordinated Investigations (EcoFOCI), multiple compiled surveys organized by Fisheries &amp;amp;amp; Oceans Canada, the NOAA Pre-recruit Survey, Newport Hydrographic Line, California Cooperative Oceanic Fisheries Investigations and the Investigaciones Mexicanas de la Corriente de California. All surveys sampled to 100-200 m depth (or bottom depth, if shallower) with net meshes ranging between 200-505 μm. Only bongo nets or ring net tows within the 200 nm Exclusive Economic Zone were retained within this study. We examined years 1995-2018. Larvae from sixteen species from three adult habitat categories (coastal pelagics, groundfishes, and mesopelagics) were retained. All species were of interest for their importance in commercial or recreational fisheries, as forage fish, or due to high biomass. Species varied in their geographic spread, from regional to coastwide. For instance, of selected mesopelagics, Panama lightfish (&amp;lt;em&amp;gt;Vinciguerria lucetia&amp;lt;/em&amp;gt;) and Mexican lampfish (&amp;lt;em&amp;gt;Triphoturus mexicanus&amp;lt;/em&amp;gt;) are both restricted to southern California and the Baja Peninsula, while Northern lampfish (&amp;lt;em&amp;gt;Stenobrachius leucopsarus&amp;lt;/em&amp;gt;) and blue lanternfish (&amp;lt;em&amp;gt;Tarletonbeania crenularis&amp;lt;/em&amp;gt;) are abundant throughout the entire study domain.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;The full datasets of the surveys compiled are available through the following locations/contacts:&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;- EcoFOCI:&amp;amp;nbsp;By request: https://apps-afsc.fisheries.noaa.gov/ichthyo/index.php&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;- Department of Fisheries &amp;amp;amp; Oceans Canada: By request (current contacts are R. Ian Perry or Moira Galbraith)&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;- NH-Line:&amp;amp;nbsp;By request: https://www.integratedecosystemassessment.noaa.gov/regions/california-current/newport-hydrographic-line&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;- Pre-Recruit Survey:&amp;amp;nbsp;By request: https://www.fisheries.noaa.gov/inport/item/18603&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;- CalCOFI: ERDDAP, https://coastwatch.pfeg.noaa.gov/erddap/tabledap/erdCalCOFIlrvcnt.html (Dataset ID: &amp;amp;nbsp;erdCalCOFIlrvcnt)&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;- IMECOCAL: By request: https://imecocal.cicese.mx/wp/base-de-datos/&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Environmental data&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;For environmental variables, we used a hindcast developed with the Regional Ocean Modeling System (ROMS), configured for the eastern North Pacific at 10-km resolution and encompassing the period from 1995-2020. The model was forced with daily atmospheric fields from the ERA5 reanalysis produced by European Centre for Medium-Range Weather Forecasts (Hersbach et al. 2020) and open ocean boundary conditions from the 1/12° Global Ocean Reanalysis and Simulation (Lellouche et al. 2021) provided every five days. We extracted sea surface temperature (SST), sea surface salinity (SSS), sea surface height (SSH), and “spiciness” from ROMS data. Spiciness combines salinity and temperature and is an indicator of water mass changes. We additionally extracted bottom depth using R package &amp;lt;em&amp;gt;marmap&amp;lt;/em&amp;gt; (Flament 2002). SST, SSS, and SSH were surface values, which is appropriate given the near-surface distribution for most fish larvae. Spiciness was averaged over the upper 250 m of the water column, approximately corresponding to the deepest depth that nets reached across all programs. Each empirical tow was matched to ROMS data using bilinear interpolation. ROMS data is available by request from Jerome Fiechter (fiechter@ucsc.edu).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;References:&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Flament P. 2002. A state variable for characterizing water masses and their diffusive stability: spiciness. Prog Oceanogr. 54(1–4):493–501. https://doi.org/10.1016/S0079-6611(02)00065-4&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Hersbach H, Bell B, Berrisford P &amp;lt;em&amp;gt;et al.&amp;lt;/em&amp;gt; The ERA5 global reanalysis. &amp;lt;em&amp;gt;Quarterly Journal of the Royal Meteorological Society&amp;lt;/em&amp;gt; 2020;&amp;lt;strong&amp;gt;146&amp;lt;/strong&amp;gt;(730):1999–2049. https://doi.org/10.1002/QJ.3803.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Lellouche JM, Eric G, Romain BB &amp;lt;em&amp;gt;et al.&amp;lt;/em&amp;gt; The Copernicus Global 1/12° Oceanic and Sea Ice GLORYS12 Reanalysis. &amp;lt;em&amp;gt;Front Earth Sci (Lausanne)&amp;lt;/em&amp;gt; 2021;&amp;lt;strong&amp;gt;9&amp;lt;/strong&amp;gt;:698876. https://doi.org/10.3389/FEART.2021.698876.&amp;lt;/p&amp;gt;

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The investigators are using statistical and biophysical modeling techniques to examine the characteristics and drivers of timing (phenology) and distribution (geography) of fish eggs, larvae, and juveniles. They are focusing on the California Current and western Gulf of Alaska regions of the Northeast Pacific. Changes in phenology and geography are anticipated responses of marine organisms to global change in climate, with consequences for food web interactions, species abundance and productivity, and local extinctions. These responses, in turn, will have important implications for marine conservation, resource management, and the economies of coastal communities that depend on marine resources for sustenance and livelihoods. Data analysis is in collaboration with fisheries scientists at National Oceanic and Atmospheric Administration, and results will be of interest to resource managers. One of the investigators is an early-career female scientist, and the study provides training for REU students, other undergraduates, graduate students, and a postdoctoral scientist. Educational outreach includes development of online classroom and lab modules.&lt;/p&gt;
&lt;p&gt;The overarching objective of this project is to examine the drivers and characteristics of phenology and geography of fish early life history stages (ELS) in the Northeast Pacific Ocean. Most research on how climate change impacts marine organisms has focused on adult life history stages, even though existing literature indicates that early life history stages may be more vulnerable to climate stressors. During ELS, marine fish and invertebrates can be limited in their ability to move in space and time due to strong ecological, physiological, physical, and evolutionary constraints. For these species, their ability to adapt to global change in climate through shifts in distribution and phenology depends on the events that occur during the early portion of their life cycle. Similarly, climate change impacts on organismal distribution and phenology have principally been studied separately, without any consideration of interactions between these two types of responses to changing oceanic conditions. The investigators are conducting modeling analyses based on ELS collected since the mid-1950s to test the null hypotheses that: 1) fish ELS will experience similar spatio-temporal variability in relation to ocean climate regardless of the life history strategy; 2) changes will be greater at the leading edge of a species' distribution and that the start of the spawning season will exhibit the greatest change in phenology; 3) species with large distribution changes will have smaller changes in phenology, and vice versa; and 4) historical and future projections of fish distribution that include life history information will be more skillful than those that do not include life history.&lt;/p&gt;
&lt;p&gt;This award reflects NSF's statutory mission and has been deemed worthy of support through evaluation using the Foundation's intellectual merit and broader impacts review criteria.&lt;/p&gt;</gco:CharacterString>
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                <gco:CharacterString>&amp;lt;p&amp;gt;We collated larval fish density data in larvae/m&amp;lt;sup&amp;gt;3&amp;lt;/sup&amp;gt; from six long-term ichthyoplankton sampling programs covering the region between the southern part of the Baja California Peninsula to the Alaska Peninsula in the western Gulf of Alaska. These surveys were the National Oceanic and Atmospheric Administration (NOAA) Ecosystems and Fisheries Oceanography Coordinated Investigations (EcoFOCI), multiple compiled surveys organized by Fisheries &amp;amp;amp; Oceans Canada, the NOAA Pre-recruit Survey, Newport Hydrographic Line, California Cooperative Oceanic Fisheries Investigations and the Investigaciones Mexicanas de la Corriente de California. All surveys sampled to 100-200 m depth (or bottom depth, if shallower) with net meshes ranging between 200-505 μm. Only bongo nets or ring net tows within the 200 nm Exclusive Economic Zone were retained within this study. We examined years 1995-2018. Larvae from sixteen species from three adult habitat categories (coastal pelagics, groundfishes, and mesopelagics) were retained. All species were of interest for their importance in commercial or recreational fisheries, as forage fish, or due to high biomass. Species varied in their geographic spread, from regional to coastwide. For instance, of selected mesopelagics, Panama lightfish (&amp;lt;em&amp;gt;Vinciguerria lucetia&amp;lt;/em&amp;gt;) and Mexican lampfish (&amp;lt;em&amp;gt;Triphoturus mexicanus&amp;lt;/em&amp;gt;) are both restricted to southern California and the Baja Peninsula, while Northern lampfish (&amp;lt;em&amp;gt;Stenobrachius leucopsarus&amp;lt;/em&amp;gt;) and blue lanternfish (&amp;lt;em&amp;gt;Tarletonbeania crenularis&amp;lt;/em&amp;gt;) are abundant throughout the entire study domain.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;The full datasets of the surveys compiled are available through the following locations/contacts:&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;- EcoFOCI:&amp;amp;nbsp;By request: https://apps-afsc.fisheries.noaa.gov/ichthyo/index.php&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;- Department of Fisheries &amp;amp;amp; Oceans Canada: By request (current contacts are R. Ian Perry or Moira Galbraith)&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;- NH-Line:&amp;amp;nbsp;By request: https://www.integratedecosystemassessment.noaa.gov/regions/california-current/newport-hydrographic-line&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;- Pre-Recruit Survey:&amp;amp;nbsp;By request: https://www.fisheries.noaa.gov/inport/item/18603&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;- CalCOFI: ERDDAP, https://coastwatch.pfeg.noaa.gov/erddap/tabledap/erdCalCOFIlrvcnt.html (Dataset ID: &amp;amp;nbsp;erdCalCOFIlrvcnt)&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;- IMECOCAL: By request: https://imecocal.cicese.mx/wp/base-de-datos/&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Environmental data&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;For environmental variables, we used a hindcast developed with the Regional Ocean Modeling System (ROMS), configured for the eastern North Pacific at 10-km resolution and encompassing the period from 1995-2020. The model was forced with daily atmospheric fields from the ERA5 reanalysis produced by European Centre for Medium-Range Weather Forecasts (Hersbach et al. 2020) and open ocean boundary conditions from the 1/12° Global Ocean Reanalysis and Simulation (Lellouche et al. 2021) provided every five days. We extracted sea surface temperature (SST), sea surface salinity (SSS), sea surface height (SSH), and “spiciness” from ROMS data. Spiciness combines salinity and temperature and is an indicator of water mass changes. We additionally extracted bottom depth using R package &amp;lt;em&amp;gt;marmap&amp;lt;/em&amp;gt; (Flament 2002). SST, SSS, and SSH were surface values, which is appropriate given the near-surface distribution for most fish larvae. Spiciness was averaged over the upper 250 m of the water column, approximately corresponding to the deepest depth that nets reached across all programs. Each empirical tow was matched to ROMS data using bilinear interpolation. ROMS data is available by request from Jerome Fiechter (fiechter@ucsc.edu).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;References:&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Flament P. 2002. A state variable for characterizing water masses and their diffusive stability: spiciness. Prog Oceanogr. 54(1–4):493–501. https://doi.org/10.1016/S0079-6611(02)00065-4&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Hersbach H, Bell B, Berrisford P &amp;lt;em&amp;gt;et al.&amp;lt;/em&amp;gt; The ERA5 global reanalysis. &amp;lt;em&amp;gt;Quarterly Journal of the Royal Meteorological Society&amp;lt;/em&amp;gt; 2020;&amp;lt;strong&amp;gt;146&amp;lt;/strong&amp;gt;(730):1999–2049. https://doi.org/10.1002/QJ.3803.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Lellouche JM, Eric G, Romain BB &amp;lt;em&amp;gt;et al.&amp;lt;/em&amp;gt; The Copernicus Global 1/12° Oceanic and Sea Ice GLORYS12 Reanalysis. &amp;lt;em&amp;gt;Front Earth Sci (Lausanne)&amp;lt;/em&amp;gt; 2021;&amp;lt;strong&amp;gt;9&amp;lt;/strong&amp;gt;:698876. https://doi.org/10.3389/FEART.2021.698876.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;</gco:CharacterString>
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              <gmd:description>
                <gco:CharacterString>&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;R scripts provided:&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;The modeling procedure generally began with modelPrediction.R, which iteratively compares models with different environmental covariates for each species (&amp;lt;em&amp;gt;runEnviroCovariatesComparison() &amp;lt;/em&amp;gt;and&amp;lt;em&amp;gt; evaluateEnviroCovariates()&amp;lt;/em&amp;gt;). Once the most predictive covariates are identified for each species, we then compare four spatiotemporal models through a similar process (&amp;lt;em&amp;gt;runTradeoffModelComparison()&amp;lt;/em&amp;gt; and &amp;lt;em&amp;gt;evaluateTradeoffs()&amp;lt;/em&amp;gt;). This script uses getMesh.R and getSpeciesData.R, as well as the covariates.xlsx and timeblocks.xlsx files.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;modelPrediction.R contains all remaining analyses, beginning with generating a new prediction grid and predicting larval densities across this grid (&amp;lt;em&amp;gt;createPredictionObjects()&amp;lt;/em&amp;gt;).&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Phenology.Rproj - &amp;lt;/strong&amp;gt;R project shell, for running code without the need to redefine working directory variable.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;modelComparison.R&amp;lt;/strong&amp;gt; - To run model comparison loops for environmental covariates and for tradeoff models.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;getMesh.R&amp;lt;/strong&amp;gt; - For creating sdmTMB meshes. Called by modelComparison.R.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;getSpeciesData.R&amp;lt;/strong&amp;gt; - For extracting both positive tows and zero stations for a specific species. Called by modelComparison.R and createPredictionGrid.R.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;createPredictionGrid.R&amp;lt;/strong&amp;gt; - Creates prediction grid of points and links this to ROMS outputs. ROMS data available by request from Jerome Fiechter (fiechter@ucsc.edu)&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;modelPrediction.R&amp;lt;/strong&amp;gt; - For creating prediction objects based on stacked spatiotemporal models, then complete analyses on subsequent modeled output (calculate and analyze tradeoff metrics; calculate niche hypervolume; create figures; run ridge regression).&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;linkRoms.R &amp;lt;/strong&amp;gt;- For linking ROMS output with points in new prediction grids. Called by createPredictionGrid.R. ROMS data available by request from Jerome Fiechter (fiechter@ucsc.edu).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;amp;nbsp;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Non-data spreadsheets:&amp;lt;/strong&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Covariates.xlsx&amp;lt;/strong&amp;gt; - Used in modelComparison.R to compare models with different sets of environmental covariates. Also called by modelPrediction.R.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Timeblocks.xlsx&amp;lt;/strong&amp;gt; - Timeblock designations for 1995-2018, used to link year in datasets to a character timeblock string. Required in modelPrediction.R, getSpeciesData.R, and modelComparison.R.&amp;lt;br /&amp;gt;
&amp;amp;nbsp;&amp;lt;/p&amp;gt;


Package | Version | Files | General purpose | Citation

• blockCV | 3.2-0 | modelComparison | Analysis | Valavi et al. (2019)
• boot | 1.3-32 | modelPrediction | Analysis | Canty &amp;amp; Ripley (1999)
• Cairo | 1.7-0 | modelPrediction, modelComparison | Visualization | Urbanek &amp;amp; Horner (2025)
• cmocean | 0.3-2 | modelPrediction | Visualization | Thyng et al. (2016)
• colorspace | 2.1-2 | modelPrediction | Visualization | Zeileis et al. (2020)
• corrplot | 0.95 | modelPrediction, modelComparison | Analysis | Wei &amp;amp; Simko (2024)
• cowplot | 1.2.0 | modelPrediction | Visualization | Wilke (2025)
• dplyr | 1.2.1 | modelPrediction, modelComparison, linkRoms, getSpeciesData | Data management | Wickham et al. (2014)
• fmesher | 2.3.2 | getMesh | Analysis | Lindgren (2023)
• ggeffects | 0.5.2 | modelPrediction | Analysis | Lüdecke (2018)
• ggnewscale | 4.0.2 | modelPrediction | Visualization | Campitelli (2025)
• ggplot2 | 0.6.3 | modelPrediction, modelComparison, createPredictionGrid | Visualization | Hadley Wickham (2016)
• ggpubr | 0.1.2 | modelPrediction | Visualization | Kassambara (2026)
• ggtext | 4.1-10 | modelPrediction | Visualization | Wilke &amp;amp; Wiernik (2022)
• glmnet | 1.9.5 | modelPrediction | Analysis | Friedman et al. (2010)
• lubridate | 1.0.12 | linkRoms | Data management | Grolemund &amp;amp; Wickham (2011
• marmap | 1.9-4 | createPredictionGrid | Data access | Pante &amp;amp; Simon-Bouhet (2013)
• mgcv | 0.2.1 | modelPrediction | Analysis | Wood (2011)
• mgcViz | 1.24 | modelPrediction | Analysis | Fasiolo et al. (2020)
• ncdf4 | 1.2.2 | linkRoms | Data access | Pierce (2025)
• purrr | 1.4.5 | modelComparison | Data management | Wickham &amp;amp; Henry (2025)
• readxl | 1.4 | modelPrediction, modelComparison, getSpeciesData | Data management | Wickham &amp;amp; Bryan (2026)
• scales | 1.0.0 | modelPrediction | Visualization | Wickham et al. (2025)
• sdmTMB | 0.0.5 | modelPrediction, modelComparison, getMesh | Analysis | Anderson et al. (2022)
• sdmTMBextra | 1.1-0 | getMesh | Analysis | Anderson et al. (2022)
• sf | 1.6.0 | modelPrediction, modelComparison, getSpeciesData, getMesh, createPredictionGrid | Mapping | Pebesma &amp;amp; Bivand (2023)
• stringr | 1.9-11 | modelPrediction | Data management | Wickham (2025)
• terra | 1.3.2 | linkRoms | Data management | Hijmans et al. (2026)
• tidyr | 0.6.5 | modelPrediction, linkRoms, getSpeciesData, createPredictionGrid | Data management | Wickham &amp;amp; Bryan (2026)
• viridis | 1.5.4 | modelPrediction | Visualization | Garnier et al. (2024)
• writexl | 0.6.5 | modelPrediction, modelComparison | Data management | Ooms (2025)
• xlsx | 3.2-0 | modelPrediction, modelComparison | Data management | Dragulescu &amp;amp; Arendt (2020)</gco:CharacterString>
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