Description of the sub-mesoscale filament
In late July 2017 a ~ 7 km wide sub-mesoscale filament occurred under a 50 km long and only 500 m wide nearly straight streak of sea ice at 2.5°E/79°N in the marginal ice zone of Fram Strait. It was characterized by a thin surface meltwater layer above a layer of denser water, which extended to > 250 m depth [11]. Outside the filament, meltwater occupied the upper 15 m of the water column, leading to a strong stratification of the surface ocean. Here, Polar water was located directly below the meltwater layer at 20–40 m depth, while Atlantic water occupied the deeper water layers below 50 m. Inside the filament, the meltwater layer was thicker and occupied the top ~ 25 m, below which Atlantic water was found. High-resolution physical measurements revealed a frontal system of two strong currents flowing in opposite directions along the filament, leading to a horizontal inward-flow from both sides and mixing mostly in the upper 100 m inside the filament. Furthermore, the authors hypothesized that denser waters at ca. 100 m in the filament were in the process of subduction [11].
Sampling
The samples were collected in July 2017 during the RV Polarstern cruise PS107 in Fram Strait (Fig. 1). To address horizontal variability in plankton biodiversity samples were collected on one hand underway on five transects with a spatial resolution of ~ 2.5 km (1.5 nm) at a depth of ~ 10 m with the Automated filtration device for marine microorganisms AUTOFIM [15], permanently installed on RV Polarstern. Additionally at five selected sites across the sub-mesoscale filament, samples from deeper water layers were taken with a rosette sampler equipped with 24 Niskin bottles (12 L per bottle) and sensors for Chl a fluorescence, temperature and salinity (CTD). Samples collected with the rosette were taken during the up-casts at 10, 20–30, 50, 100, 200 and 400 m depth. Subsamples of 2 L were transferred from the Niskin bottles into PVC bottles. Particulate organic matter for molecular analyses was collected by sequential filtration of each water sample through three mesh sizes (10 µm, 3 µm, 0.4 µm) on 45 mm diameter Isopore Membrane Filters at 200 mbar using a Millipore Sterifil filtration system (Millipore, USA). Here, two liters of seawater were collected and filtered on a filter with 0.4 µm pore size at 200 mbar. Subsequent to filtration, particulates are stored at -80°C until further processing in the laboratory.
Environmental parameters: Data for temperature and salinity are available via PANGAEA (doi.org/10.1594/PANGAEA.894189; doi.org/10.1594/PANGAEA.889535). Samples with a volume of ~ 50 ml were taken in parallel to AUTOFIM sampling from the ship's pump system and from the CTD. The samples were directly frozen at -80°C for subsequent nutrient analyses in the laboratory. Nutrients were analyzed with an Alliance Evolution III continuous flow autoanalyzer (Alliance Instruments GmbH, Freilassing, Germany). The water samples were measured unfiltered. Measurements were made simultaneously on five channels: Phosphate [19], silicate [20], nitrite, nitrate [21] and ammonium [22]. All measurements were calibrated with a five nutrient standard cocktail (All from Merck, traceable to SRM from NIST) diluted in artificial seawater (ASW), and ASW was used as wash-water between the samples. Data were all standardized by the same in-house reference material obtained from CTD water bottles. Each run we checked our standards with Reference Material for Nutrients in Seawater (CRM 7602-a + CRM 7603a) produced by NMIJ. Our standards and methods have been proven by inter-calibration exercises like ICES and Quasimeme. Nutrient concentrations are provided in the supplements (S1).
Total Chl a biomass and fractions of phytoplankton groups: Chl a concentrations and other phytoplankton pigments were determined using the high-pressure liquid chromatography (HPLC) on samples collected in parallel to the samples collected for eDNA analyses [17, 23]. These data were also used to develop an algorithm for obtaining a continuous dataset along the ship transect (at ~ 250 m resolution) of the concentration of Chl a and major phytoplankton pigments from underway hyperspectral spectrophotometry [17, 24]. For this study, we applied the diagnostic pigment analysis developed previously by Vidussi [25] and further refined by Uitz [26] to derive Chl a concentrations (conc.) of fucoxanthin, 19-hexanoyl fucoxanthin, 19-butanoyl fucoxanthin, peridinin, zeaxanthin, and chlorophyll b from HPLC samples. of the seven major phytoplankton groups that characterize the global ocean: Diatoms, prymnesiophytes, dinoflagellates, chlorophytes (which include the prasinophyte group), chrysophytes, cryptophytes, and prokaryotic microbes. We used the derived data set to calculate for each group its fraction on the total phytoplankton Chl a conc. (total Chl a). Looking at the phytoplankton group Chl a data considered within this study from the HPLC, diatoms contribute between 39%-70%, prymnesiophytes between 0–18%, dinoflagellates between 0–31%, chlorophytes between 5 to 46% to the total Chl a, while chrysophytes and prokaryotic phytoplankton have marginal contributions (0–4% and 1 to 2%). In order to derive a high resolution surface Chl a conc. data of the four major phytoplankton groups (diatoms, dinoflagellates, prymnesiophytes and chlorophytes) identified in the HPLC data set, we applied also the same diagnostic pigment analysis as for the HPLC data to the spectrophotometric pigment data set. For the three other phytoplankton groups no diagnostic pigments could be retrieved from the underway spectroscopy data, however, there contribution was found to be minimal for the Chl a in our study area (0–5%). We calculated the fraction of each phytoplankton group in respect to its Chl a compared to the total Chl a for both data sets.
Chl a conc. data for all phytoplankton (and for major phytoplankton groups) were obtained from Sentinel-3A sensor OLCI (downloaded in full resolution (300m) from EUMETSAT at https://www.eumetsat.it/new-release-l2-reprocessed-dataset/; EUMETSAT 2022) within the area and timing of the study and used to upscale Chl a point measurements from HPLC water sample analysis and underway spectrophotometry.
LOKI-casts and image analyses
LOKI casts were conducted from 400m to the surface at each of the five stations, that were also sampled via CTD for eDNA analyses. The system continuously takes images (max. 19 frames sec-1) during the up-cast from mesozooplankton organisms that are concentrated by a 150µm plankton net, leading to a flow-through chamber with a 6.1 mp camera (for a detailed description of LOKI see [18]). All images were loaded into the LOKI browser, a software that assigns optical parameters (hue factors, gray scale, skewness etc.) to each image and links the images to the respective metadata. Then, the image quality was enhanced and double takes of objects were removed using the software ZooMi. Subsequently, the images were uploaded to the EcoTaxa website (ecotaxa.obs-vlfr.fr), an application that facilitates the annotation, i.e. assignment of taxonomic categories, to the organisms presented on the images. Due to the high resolution of the LOKI images, it was often possible to identify families and sometimes-even species, thus tackling their fine scale distribution in the water column.
DNA-isolation
Isolation of genomic DNA from the field samples was carried out using the NucleoSpin Plant Kit (Machery-Nagel, Germany) following the manufacturer’s protocol. Samples were processed around one to two weeks subsequent to sampling. The resulting DNA-extracts were stored at -20°C.
Illumina-Sequencing 18S rDNA
For Illumina-Sequencing, a fragment of the 18S rDNA containing the hypervariable V4 region was amplified with the primer set 528iF(GCGGTAATTCCAGCTCC) and 964iR(ACTTTCGTTCTTGATYRR) [15]. All PCRs (polymerase chain reaction) had a final volume of 50 µL and contained 0.02 U Phusion Polymerase (Thermo Fisher, Germany), the 10-fold polymerase buffer according to manufacturer’s specification, 0.8 mM (each) dNTP (Eppendorf, Germany), 0.2 µmol L− 1 of each Primer and 1µL of template DNA. PCR amplification was performed in a thermal cycler (Eppendorf, Germany) with an initial denaturation (94°C, 2 min) followed by 35 cycles of denaturation (94°C, 20 sec), annealing (58°C, 30 sec), and extension (68°C, 30 sec) with a single final extension (68°C, 10 min). The PCR products were purified from an agarose gel 1% [w/v] with the NucleoSpin Gel Kit (Machery-Nagel, Germany) and Minelute PCR Purification kit (Qiagen, Germany). Subsequent to purification of the 18S rDNA fragment the DNA concentration of the samples was determined using the Quantus Fluorometer (Promega, USA). Prior to the library preparation, the DNA fragments were diluted with TE-buffer to a concentration of 0.2 ng/µL. The library preparation was based on the 16S metagenomic protocol of Illumina (Illumina, USA). Finally, sequencing of the DNA-fragments was carried out using a MiSeq-Sequencer (Illumina, USA). Raw sequences had an approximate length of ~ 200 bp. Sequences generated in this study have been deposited via GfBio [27] in the European Nucleotide Archive (ENA) with the accession number PRJEB66268.
Sequence analyses and annotation
Further bioinformatic processing of the raw sequences was done with the dada2 package v.1.18 in R v.4.0 [28]. Realignment of the sequences, as well as the removal of the forward and reverse primer, was done by the bioinformatic tool Cutadapt v.3.4 [29]. To improve the evaluation of sequences, low-quality-3’ ends were trimmed based on a visual review of the quality plots [30]. By filtering the sequences based on the expected error, a minimum quality was guaranteed for sequence pairs. The remaining probable sequencing errors were identified using the error profile and rectified by dada2 [28]. Remaining sequence pairs were merged to amplicon sequence variants (ASVs) by dada2, when having an overlap of at least 25 base pairs without a mismatch (Callahan et al., 2016). The Protist Ribosomal Reference database (PR2) was used to taxonomically classify each ASV [31]. Potential chimeres, caused by the polymerase chain reaction, were discarded [28]. Further statistical analyses were performed using R v.4.0.3 (R Core Team, 2021) in R Studio v.1.2.5001 (R Studio Team, 2019). The rrarefy function from the vegan package v.2.5-7 was used for rarefaction and normalization [32]. Visualizations and further calculations were done with ampvis2 v.2.6.7, ggplot2 v.3.3.5, FactoMineR v.2.4, factoextra v.1.0.7.999, cluster v.2.1.4 and vegan [33, 34, 35, 36, 37]. Further editing (e.g.increasing the size of text and legends in graphs) were performed with Inkscape (version 1.1.1). The mapping of the stations as well as the nutrient distribution in the surface samples was done using QGIS (QGIS.org, 2022). The significance level was set at p < 0.05 for all calculations.