Absence of photophysiological response to iron addition in autumn phytoplankton in the Antarctic sea-ice zone

The high nutrient–low chlorophyll condition of the Southern Ocean is generally thought to be caused by the low bioavailability of micronutrients, particularly iron, which plays an integral role in phytoplankton photosynthesis. Nevertheless, the Southern Ocean experiences seasonal blooms that generally initiate in austral spring, peak in summer, and extend into autumn. This seasonal increase in primary productivity is typically linked to the seasonal characteristics of nutrient and light supply. To better understand the potential limitations on productivity in the Antarctic sea-ice zone (SIZ), the photophysiological response of phytoplankton to iron addition (2.0 nM FeCl3) was investigated during autumn along the Antarctic coast off Dronning Maud Land. Five short-term (24 h) incubation experiments were conducted around Astrid Ridge (68 S) and along a 6 E transect, where an autumn bloom was identified in the region of the western SIZ. Surface iron concentrations ranged from 0.27 to 1.39 nM around Astrid Ridge, and 0.56 to 0.63 nM along the 6 E transect. Contrary to expectation, the photophysiological response of phytoplankton to iron addition, measured through the photosynthetic efficiency and the absorption cross-section for photosystem II, showed no significant responses. It is thus proposed that since the autumn phytoplankton in the SIZ exhibited a lack of an iron limitation at the time of sampling, the ambient iron concentrations may have been sufficient to fulfil the cellular requirements. This provides new insights into extended iron replete postbloom conditions in the typically assumed iron deficient high nutrient–low chlorophyll Southern Ocean.


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A. Singh et al.: Absence of photophysiological response to iron addition in autumn phytoplankton born et al., 2019) and several essential trace metals (Sunda, 1989;Lindsey and Scott, 2010;Wu et al., 2019;Browning et al., 2021;Hawco et al., 2022), particularly iron, which is a crucial co-factor for the functioning of photosynthetic proteins (Raven, 1990;Raven et al., 1999;Strzepek and Harrison, 2004). In addition, iron is needed for nitrate reductase, which is responsible for the reduction of nitrate to nitrite (Sunda, 1989;Milligan and Harrison, 2000;de Baar et al., 2005;Bazzani et al., 2023) and is also required for the synthesis of chlorophyll and the quenching of reactive oxygen species (Sunda and Huntsman, 1995;Diaz and Plummer, 2018). However, nitrate assimilation has a high iron (Milligan and Harrison, 2000;de Baar et al., 2005) and light Moore et al., 2007a, b) demand, which drives the high nutrient-low chlorophyll (HNLC) conditions characteristic of the Southern Ocean (Price et al., 1994;Milligan and Harrison, 2000;Lucas et al., 2007;Cochlan, 2008;Moore et al., 2013). Thus, independent of adequate amounts of macronutrient concentrations in surface waters, any limitation on the bioavailability of iron will potentially decrease the efficiency of these processes (Martin and Fitzwater, 1988;Moore et al., 2001;Lis et al., 2015;Yoon et al., 2018), affecting nutrient drawdown, photosynthesis, primary productivity, biomass accumulation, and community composition of surface phytoplankton in the Southern Ocean (de Baar et al., 1990;Geider and La Roche, 1994;Martin et al., 1991;Martin and Fitzwater, 1988;Biggs et al., 2022). Furthermore, any light limitation will exacerbate iron limitation due to the increase in iron demand under low light conditions (Strzepek et al., , 2019Boyd and Abraham, 2001), thus driving the frequent occurrence of iron-light co-limitation conditions in the Southern Ocean Tagliabue et al., 2014;Ryan-Keogh et al., 2017;Trimborn et al., 2019).
Although the Southern Ocean is typically considered an "iron-limited" region, iron availability or limitation is not uniform and instead varies spatially and temporally. For instance, iron limitation is commonly associated with the pelagic waters of the Southern Ocean (Mitchell et al., 1991;Yoon et al., 2018), where summer dissolved iron (dFe) concentrations in surface waters are typically < 0.5 nM (Sedwick et al., 1999;Coale et al., 1999;Vink and Measures, 2001;Klunder et al., 2011); however, there are a number of regional exceptions. These include regions with an external iron source such as sea-ice and iceberg meltwaters (Lannuzel et al., 2008;Boyd and Ellwood, 2010;Smith et al., 2010;Boyd et al., 2012), hydrothermal vents (Klunder et al., 2011;Tagliabue et al., 2017;Ardyna et al., 2019), atmospheric dust (Martin and Fitzwater, 1988;Mahowald et al., 2005), continental margin input (Sedwick et al., 2008;Bowie et al., 2009), and island wake inputs Blain et al., 2008). Internal processes such as remineralization (Tagliabue et al., 2017), resupply through deep winter mixing (Tagliabue et al., 2014), cross-frontal mixing (Lutjeharms et al., 1985;Moore and Abbott, 2002), and storm-driven entrainment  can also provide iron to surface waters in support of phytoplankton production. Most of these sources vary seasonally; for example, in winter, iron is not generally considered limiting, as deep winter mixing entrains a seasonal resupply of iron (Tagliabue et al., 2014;Mtshali et al., 2019). Instead, due to the deep seasonal mixed layers, ice cover, and low sun angles, the availability of photosynthetically active radiation (PAR) can be suboptimal and considered the dominant factor limiting phytoplankton production in winter. In spring, phytoplankton blooms are initiated when there is sufficient light, driven by a shoaling of the mixed layer (Moore and Abbott, 2002;Thomalla et al., 2011) as well as retreating sea ice (Taylor et al., 2013) to support phytoplankton growth under nutrient replete conditions (Swart et al., 2015;de Baar et al., 1990;Hauck et al., 2015;Martin et al., 1990). Blooms typically subside when nutrients such as iron are depleted in late summer or early autumn (Tagliabue et al., 2014;Soppa et al., 2016;Hiscock et al., 2008). Grazing (Lancelot et al., 1993;Moreau et al., 2020;Kauko et al., 2021), bacteria, and viruses (Biggs et al., 2021) may also accelerate the blooms' demise. Iron supply mechanisms during a bloom, such as advection from continental margins (Sedwick et al., 2008;Bowie et al., 2009), remineralization (Tagliabue et al., 2017), and storm-driven entrainment (Swart et al., 2015;Nicholson et al., 2019) may sustain phytoplankton growth for an extended duration. However, it is not clear how applicable these resupply processes are to the Southern Ocean as a whole, and where and when each of these dominate.
In general, experiments that investigate the degree of iron limitation by testing the impact of iron addition on metabolic functions of phytoplankton have largely focussed on summer conditions in the open Southern Ocean. There is thus minimal information on the impact of iron addition in the sea-ice zone (SIZ) in autumn, when iron concentrations are expected to be low (Tagliabue et al., 2014;Lannuzel et al., 2016). One exception was a study by Van Oijen et al. (2004), where a single iron-light perturbation experiment examined carbon uptake in the marginal ice zone in autumn, but no conclusions were made on the driving factors of enhanced uptake. To address this knowledge gap, we undertook a number of iron addition experiments using active chlorophyll-a (Chl-a) fluorescence in the SIZ off Dronning Maud Land (DML) in autumn (March). Active Chl-a fluorescence is a key indicator of the photophysiological state of phytoplankton (Hughes et al., 2018;Brown et al., 2019;Schuback et al., 2021) and provides a powerful tool for evaluating the photophysiological response of phytoplankton to iron addition. This is done by measuring the photosynthetic efficiency, F v /F m , and the absorption cross-section of photosystem II, σ PSII (Geider, 1993;Geider and La Roche, 1994;Kolber et al., 1988;Hughes et al., 2018). Any photophysiological response measured through active Chl-a fluorescence can, however, be due to both changes in cellular structure, i.e. a response seen on short timescales (milliseconds to femtoseconds), and changes in community composition, i.e. a response seen on longer timescales (usually > 24 h). Since different phytoplankton groups tend to have different photophysiological signatures (Suggett et al., 2009), any measured response in photophysiology over longer time periods (> 24 h) is difficult to interpret, as it reflects both the cellular and community adjustments. This makes it difficult to resolve the physiological response of phytoplankton to iron addition in manipulation incubation experiments from community composition adjustments (Suggett et al., 2009).
Many iron addition incubation experiments previously conducted in the Southern Ocean (de Baar et al., 1990;Hinz et al., 2012;Ryan-Keogh et al., 2018;Viljoen et al., 2018; among others) were run for long time periods (> 96 h) and showed evidence of substantial changes in community composition, which are likely to influence the photophysiological signal and consequently the interpretation of iron limitation (Ryan-Keogh et al., 2013;Suggett et al., 2009). In this paper, we opted instead for short-term (24 h) incubation experiments to isolate changes in photophysiology, i.e. F v /F m and σ PSII . This is in line with a study by Ryan-Keogh (2014), which tested whether 24 h was sufficient to allow a measurable photophysiological response in Southern Ocean phytoplankton, where low temperatures may control uptake kinetics. Ryan-Keogh (2014) compared the photophysiology between incubations running for 24 and 48 h in summer and found that the samples were iron-limited (i.e. the differences between unamended control and iron addition incubations were significant). However, no significant differences were observed in photophysiology following iron addition when comparing the incubations of 24 vs. 48 h, supporting the robustness of a representative response in photophysiology within 24 h. During this timeframe, the community composition is not expected to change, nor would we expect to see any adjustments in biomass or nutrient drawdown (Browning et al., 2014a;Ryan-Keogh et al., 2013. As such, this study reported here provides a unique investigation of the short-term photophysiological response of phytoplankton to iron addition in the SIZ in autumn, a season where iron limitation may be expected and a season and region that is under sampled. The experiments test the hypothesis that phytoplankton in the SIZ off DML experience iron limitation during post-bloom conditions in autumn.

Materials and methods
The focus of this study is on five short-term (24 h) incubation experiments performed in March during the Southern Ocean Ecosystem Cruise (cruise number DML2019702) between 28 February and 10 April 2019, on-board the Norwegian R/V Kronprins Haakon in the SIZ of the Kong Håkon VII Hav off the Dronning Maud Land coast, as well as the region surrounding the Astrid Ridge ( Fig. 1). Ancillary data (i.e. Chl-a concentrations, macronutrient concentrations, and dFe concentrations) from surface water samples provide in-formation on the regional conditions surrounding the five incubation experiments at the time of the cruise.

Underway and surface CTD seawater sampling and measurements
Underway seawater was obtained from the ship's clean seawater sampling system at ∼ 4 m depth between incubation stations. Samples were collected for determining Chla concentration, macronutrient concentrations (nitrate, phosphate, and silicate), and photophysiology (F v /F m and σ PSII ) (Kauko et al., 2020(Kauko et al., , 2021(Kauko et al., , 2022aChierici and Fransson, 2020;Singh et al., 2022). Additionally, surface seawater samples were collected using a Seabird CTD (conductivitytemperature-depth) rosette sampler and similarly analysed for Chl-a, macronutrients, and photophysiology in addition to phytoplankton community composition (Kauko et al., 2020(Kauko et al., , 2021(Kauko et al., , 2022aChierici and Fransson, 2020;Singh et al., 2022). Sample processing and analysis are further detailed in Sect. 2.4 for phytoplankton photosynthetic photophysiology and Sect. 2.5-2.10 for ancillary data. In addition, initial in situ conditions for the incubation experiments from CTD surface samples are detailed below in Sect. 2.3 (incubation set-up and sub-sampling).

Surface seawater sampling for incubation experiments
Seawater samples for experimental station Exp01 were collected at 20 m depth using a Watson-Marlow Varmeca (MG0723) peristaltic pump connected to PTFE tubing with a 10 mm inner diameter at a flow rate of 1.6 L min −1 . All sampling tubing (peristaltic and PTFE) and 1 L Polycarbonate bottles (Thermo Fisher Scientific Nalgene) were acid washed following GEOTRACES protocols (Cutter et al., 2017). Next, inside a custom-made HEPA air-filtered Class-100 trace metal clean "plastic bubble" that consisted of a clean, steady laminar flow hood (AirClean-600 PCR Workstation), the seawater was pumped into seven 1 L polycarbonate bottles, all this under strict trace metal clean conditions. For the other experiments (Exp02, Exp03, Exp04, and Exp05), a Teflon-lined, trace metal clean, external closure 8 L GoFlo bottle (General Oceanics) was deployed on an aramid rope (VGP Industries), using a dedicated winch and Teflon-coated messenger to ∼ 20-30 m depth for surface incubation seawater (i.e. for experimental stations Exp02, Exp03, Exp04, and Exp05). At each of the five experimental stations (see Fig. 2a and Table 1 for locations), seven 1 L polycarbonate bottles were filled unscreened (i.e. no large grazers were excluded from the bottles) with the incubation seawater to represent 1 times the initial sample (hereafter "initial"), 3 times the unamended control samples (hereafter "Control"), and 3 times the iron addition samples (hereafter "Fe"), which were spiked with 2.0 nM iron (III) chloride (FeCl 3 TraceCERT ® ; Sigma-Aldrich) prepared in 2 ‰ HCl (30 % Suprapur HCl; Merck), to reach a final concentration of 2.0 nM Fe. The bottle caps of the Control and Fe samples were sealed with Parafilm™, and the bottles were doublebagged in clear polyethylene bags (Ziploc™) to avoid sample contamination. All incubation bottle filling, spiking, and subsampling were performed under a clean, laminar flow hood (AirClean-600 PCR Workstation), inside a makeshift HEPA air-filtered Class-100 trace metal clean bubble on-board, under strict trace metal clean conditions.

Incubation set-up and sub-sampling
The incubation bottles were placed inside an on-deck incubator under natural sunlight, with flowing seawater, which fluctuated with the ocean temperature, passing through the incubator to mimic in situ seawater temperatures. The seawater temperature was measured at the ship's intake by a thermosalinograph. Light levels inside the polycarbonate bottles were approximated using a handheld 4π PAR sensor (Biospherical QSL 2100, Biospherical Instruments Inc.) with the Logger 2100 software. A green mesh was used to filter out a fraction of the PAR on Exp01, with the PAR approximated inside the incubator bottle being 37 % of sea surface PAR, whilst the remaining experiments had no filters on the incubators, and the average PAR inside the incubator bottle corresponded to 43 % PAR at the sea surface. After each 24 h period, the incubation bottles were removed from the incubator and sub-sampled under the clean, laminar flow hood (AirClean-600 PCR Workstation) inside the makeshift HEPA air-filtered Class-100 trace metal clean plastic bubble onboard as described above in Sect. 2.2. All incubation bottles were sub-sampled for photophysiological parameters using active Chl-a fluorescence measured through Fast Repetition Rate fluorometry (FRRf) (see Sect. 2.4), Chl-a concentra-tion (see Sect. 2.5), and macronutrients (see Sect. 2.6). A complete list of sampling locations, initial parameters for the photophysiology, and ancillary data, as well as other relevant information (cumulative photon dose, MLD, euphotic depth, and sea surface layer temperatures), is provided in Table 1.

Phytoplankton photosynthetic photophysiology
Active Chl-a fluorescence was measured with a FastOcean™ FRRf incorporating a FastAct™ laboratory system (Chelsea Technology Group), operated with the single-turnover protocol set with a flash saturation sequence (100 × 1 µs flashlets with a 2 µs interval) and a relaxation sequence (25 × 1 µs with an interval of 84 µs). The power of the excitation LED (λ 450 nm ) was adjusted between samples to saturate the observed transients following manufacturer specifications. All samples were dark acclimated for ∼ 30 min under in situ temperatures prior to measurement of the photophysiological (fluorescence) parameters (F v /F m and σ PSII ) (Roháček, 2002) and were each blank corrected using carefully prepared 0.2 µm filtrates (Cullen and Davis, 2003). The FRRf measurements were recorded with the FastPro8 software (v1.0.55), and post-processing analysis was done in Python 3.7, using the customized package Phytoplankton Photophysiology Utilities (Ryan-Keogh and Robinson, 2021). The fluorescence response data were fitted to the saturation phase of the biophysical model of Kolber et al. (1998), with a constant connectivity coefficient ρ of 0.3 (Suggett et al., 2001) to derive F o , F m , and F v /F m . The sample means and the standard deviation (SD) were calculated for F v /F m and σ PSII from each set of triplicate samples. Statistical t tests were performed to compare the mean F v /F m and σ PSII values between the Control and Fe samples. This was done using a Levene test to check for equal variance: if the data were of Table 1. Sampling location information for the incubation stations and the associated CTD-Rosette water column station numbers from the cruise (CTD cast identifier) and mean (n = 3) initial parameters for the photophysiology (F v /F m and σ PSII ), as well as the associated ancillary data (i.e. Chl-a concentrations, macronutrient concentrations, and dFe concentrations). Cumulative photon dose and euphotic depth were calculated as defined in materials and methods. Mixed layer depth (MLD) was obtained from Kauko et al. (2021). The sea surface layer temperatures (SSLTs) averaged for depths 15 to 30 m were obtained from the CTD sensor. Dominant phytoplankton community composition was taken from a combination of microscopy and CHEMTAX data from Kauko et al. (2022a, b and (h) dFe concentration (nM). Discrete seawater samples from the underway system, surface CTD-Rosette and the GoFlo (from initial incubations), all sampled within the study region in March, are collectively presented in panels (b)-(g) along with the average sea-ice edge (concentration at 15 %) for March 2019 (blue line). Plot (h) shows the dFe concentrations which were sampled at all the GoFlo stations. All data for incubation stations are given in Table 1, and incubation stations are indicated by a black circle outline in panels (b)-(h).
equal variance, a standard Student's t test was applied, while in the case of unequal variance, a Welch's t test was applied.
Results of the t tests are reported as statistically significant at the 95 % confidence level (p value < 0.05).

Chlorophyll-a (Chl-a)
A volume of 500-1000 mL of seawater was filtered for Chla extraction onto GF/F filters (nominal pore size 0.7 µm; GE HealthCare) under low vacuum pressure (ca. −30 kPa). Chl-a was extracted with 100 % methanol at 4 • C in the dark for 24 h (Holm-Hansen and Riemann, 1978) and was subsequently measured on-board using a Turner 10AU Fluorometer (Turner Designs), which was calibrated prior to the cruise using a standard calibration curve from raw Chl-a (Sigma C6144). The uncertainty in Chl-a values was estimated as 5.5 % of the measured values during an earlier campaign utilizing the same method and instrument .

Macronutrients
The seawater samples for macronutrient analysis (nitrate, phosphate, and silicate) were collected in 50 mL Falcon tubes for the incubation experiments and underway samples, whereas water column samples from the CTD-Rosette were collected in 20 mL vials. All samples were preserved with 250 µL of chloroform (saturated solution with 1 % ethanol for stabilization). The samples were kept cold (at 4 • C in a fridge) and in the dark until post-cruise analysis was performed using a spectrophotometric method following standard procedures (Grasshoff et al., 2009) at the Institute of Marine Research, Bergen, Norway, on a Skalar autoanalyser (Gundersen et al., 2022). The analyser was calibrated using reference seawater from Ocean Scientific International Ltd. The detection limits were 0.5 µM for nitrate, 0.06 µM for phosphate, and 0.7 µM for silicate. The uncertainty for nitrate and silicate was < 0.2 %, and it was < 1 % for phosphate (Gundersen et al., 2022).

Dissolved Fe (dFe)
Seawater samples for dFe measurements were collected from the clean GoFlo bottles (5 L General Oceanics) at seven stations in the study region (unfortunately, a dFe sample is not available for experimental station Exp01) into acid-washed 125 mL low-density polyethylene (LDPE, Nalgene, Thermo Scientific) sampling bottles. The LDPE bottles were acid cleaned according to the GEOTRACES protocols (Cutter et al., 2017) prior to the cruise. The dFe samples were filtered through sequential Sartorius capsule filters (0.45 and 0.2 µm pore size filtration) using acid-washed Tygon tubes inside the trace metal clean plastic bubble. During filtration, an additional HEPA air-filter cartridge (HEPA-CAP/HEPA VENT, 75 mm, Whatman) was connected to the pressure relief valve of the GoFlo bottles to ensure that the air in contact with the sample during the filtration was clean. All samples were acidified to pH < 2 with 600 µL of ∼ 3 M double quartz distilled ultrapure HNO 3 (VWR, AnalaR NORMAPUR ® analytical reagent), double-bagged, and stored at room temperature (> 2 years) until analysis at Stellenbosch University (TracEx, https://tracexsite.wordpress.com/ (last access: 25 July 2023), South Africa) as described in Samanta et al. (2021) using online pre-concentration methods. Although the samples were stored for more than 2 years before analysis, the dFe concentration is unlikely to be affected. The long-term analyses (2017-2021) of GEOTRACES and certified reference standards, which yielded consistent dFe concentrations, support this conclusion (Samanta et al., 2021). All samples were measured in duplicate. The detection limit of Fe was 0.08 nM, and the precision was 11 % (Samanta et al., 2021).

Satellite chlorophyll data
Ocean colour data (8 d, 4 km) were obtained from the ocean colour climate change initiation (OC-CCI) (Sathyendranath et al., 2019). In order to deduce missing data, satellitederived Chl-a values were first re-gridded to a 4 km regular grid by averaging all data points within the new pixel dimensions. Gaps in the data were filled by applying a linear interpolation scheme as defined in Racault et al. (2014). The data were smoothed by applying a moving average filter of the previous and next time step (for more details on this method see Salgado-Hernanz et al., 2019). Two boxes were defined for the respective regions of this study and averaged to get the annual cycle of Chl-a concentration: 6 • E SIZ (62-72 • S; 0-9 • E) and Astrid Ridge (62-72 • S; 9-16 • E) (Fig. 3).

PAR sensor data
The cumulative photon dose for each experiment (mol photons m −2 d −1 ) was calculated as the cumulative sum of the PAR measured above the sea surface by a Biospherical/Licor Chelsea PAR sensor on the ship's mast, starting from the time of experimental commencement until experiment termination (i.e. summed over 24 h). Values were adjusted by ∼ 43 % to account for shading within the incubator in accordance with the measured sea surface PAR inside the incubator.
2.10 Bathymetry data, stratification, the mixed layer depth (MLD), euphotic depth, and sea-ice concentration The ETOPO1 bathymetry data for the study region were extracted from National Geophysical Data Center/NESDIS-/NOAA (U.S. Department of Commerce, 2011). The degree of stratification was obtained from the Brunt-Väisälä frequency (N 2 ; s −1 ) (Millard et al., 1990), which was calculated using the seawater temperature, salinity, and potential density (σ ) at each experimental station. The MLD for each exper-imental station was obtained from Kauko et al. (2021), and the respective euphotic depth was determined as the depth at which PAR is 1 % of surface PAR, based on Kirk (1994). The sea-ice concentration was plotted at 15 % concentration for the sea-ice edge around Antarctica (Figs. 1 and 2) (Brodzik and Stewart, 2016).

Results
In previously published work from this cruise (Kauko et al., 2021), two distinct regions were identified in the DML SIZ. Both regions were visited in post-bloom conditions during the month of March (Kauko et al., 2021) but differed in the peak Chl-a concentrations, i.e. in the bloom amplitude (Fig. 3). The first region was in shallower bathymetry (2556 ± 724 m depth; 11-14 • E, 67-69 • S) around Astrid Ridge (Fig. 2a). Two short-term iron addition incubation experiments, Exp02 and Exp03, were conducted in this region, north and east of Astrid Ridge, respectively (Table 1; Fig. 2a). The second region in deeper bathymetry (3042 ± 1129 m depth, 5-7 • E, 67-70 • S) was located on a 6 • E transect to the west of the Astrid Ridge in the openocean SIZ (6 • E SIZ) (Fig. 2a), where the experimental station Exp01 was conducted. Despite being occupied in postbloom conditions from a seasonal perspective (Fig. 3), Exp01 was, nonetheless, considered to represent autumn bloom conditions (Kauko et al., 2021;Moreau et al., 2023), albeit in decline, with a high Chl-a concentration (0.73 µg L −1 , Table 1). Experimental stations Exp04 and Exp05 were sampled 2 weeks after Exp01, which was after the seasonal bloom (Chl-a = 0.18 µg L −1 and 0.14 µg L −1 , respectively) within the same 6 • E SIZ region. We note that the starting time of each incubation was not synchronized (Table 1) and may lead to issues in interpreting photophysiological responses due to diurnal variation (Schuback et al., 2016). However, we found no distinct diurnal differences in both F v /F m and σ PSII across the 6 • E SIZ and Astrid Ridge regions ( Fig. A3 in Appendix A), with both parameters showing very little variability between local sunrise and sunset.
Here, we first describe the general conditions in these two regions (n = 34) and then focus specifically on the five experimental stations. The Chl-a concentrations were lower around Astrid Ridge, ranging from 0.03 to 0.26 µg L −1 (mean 0.12 ± 0.07 µg L −1 ; n = 16). Concentrations between 0.07 and 1.02 µg L −1 (mean 0.25 ± 0.24 µg L −1 ; n = 18) were observed in the 6 • E region of the SIZ (Fig. 2b; Table B1 in Appendix B). The mean values of F v /F m (Fig. 2c) were higher (p value < 0.05) at Astrid Ridge (0.28 ± 0.04) compared to the 6 • E SIZ (0.24 ± 0.06). The 6 • E SIZ showed a much larger range in F v /F m , with a minimum of 0.07 and a maximum of 0.34, whilst a narrower range in F v /F m , with a higher minimum in particular, was seen around Astrid Ridge (0.21 to 0.36). The σ PSII (Fig. 2d) was typically higher in the 6 • E SIZ region, ranging from 2.48 to 5.63 nm 2 (mean 3.41 ± 0.71 nm 2 ) and lower around the Astrid Ridge, 1.93 to 3.56 nm 2 (mean 2.66 ± 0.37 nm 2 ).
Surface nitrate concentrations showed some spatial variability, but the mean values were similar (p value > 0.05) for the 6 • E SIZ (mean 23.8 ± 0.8 µM) and Astrid Ridge (mean 24.0 ± 1.2 µM) (Fig. 2e). Despite a similarity in the range of phosphate concentrations observed for both the regions from 1.57 to 1.96 µM in the 6 • E SIZ (mean 1.75 ± 0.10 µM), and from 1.68 to 1.92 µM at Astrid Ridge (mean 1.82 ± 0.06 µM), the phosphate concentrations between the regions were significantly different (p value < 0.05) (Fig. 2f). Silicate concentrations showed a higher mean (48 ± 1 µM, p value < 0.05) and less variability around Astrid Ridge, with concentrations ranging from 46 to 52 µM, compared to a lower mean (46 ± 2 µM) and larger range (41 to 49 µM) observed in the 6 • E SIZ (Fig. 2g). Despite the limited number of dFe measurements, a wide range of surface concentrations (Fig. 2h) were evident around Astrid Ridge, with concentrations as low as 0.27 nM and as high as 1.39 nM (mean 0.64 ± 0.49 nM). Mean dFe concentrations in the 6 • E SIZ were slightly lower (0.59 ± 0.05 nM) compared to Astrid Ridge and varied over a narrow range between 0.56 and 0.63 nM. However, it is noted that only a fraction of the dFe is bioavailable to the phytoplankton, where this fraction can vary regionally and thus influence the variability in iron stress, which may not mirror the ambient concentrations (Lis et al., 2015). Furthermore, the mean PAR in the mixed layer for the 6 • E SIZ was lower (29.71 µmol photons m −2 s −1 ) in comparison to the Astrid Ridge (59.37 µmol photons m −2 s −1 ).
In the following, we focus particularly on the upper ocean conditions at stations where incubation experiments were conducted (Table 1). Initial conditions in surface Chl-a ranged from high concentrations at the bloom station Exp01 (0.73 µg L −1 ) to concentrations as low as 0.02 µg L −1 at Exp03 in the Astrid Ridge. Similar to the general oceanographic conditions, both nitrate and phosphate showed very little variability between experiments, whereas silicate concentrations were slightly lower for all three stations in the 6 • E SIZ (43-44 µM) in comparison to the Astrid Ridge (48 µM). Unfortunately, the initial dFe concentration at the bloom station Exp01 is not available; however, dFe concentrations tended to be lower at the remaining stations (Exp04 and Exp05) in the 6 • E SIZ (0.56-0.63 nM) compared to the Astrid Ridge (0.86-1.39 nM) ( Table 1). The cumulative photon doses over 24 h (Table 1; Fig. A1) were substantially different, as Exp01, Exp02, and Exp03 (124-160 mol photons m −2 d −1 ) had much higher doses compared to Exp04 and Exp05 (92-93 mol photons m −2 d −1 ). The MLD at all experimental stations showed little variability (Kauko et al., 2020(Kauko et al., , 2021 Table 1; Fig. A2), ranging between 27 and 38 m (mean 31 ± 5 m). The degree of stratification, however, ranged substantially, being particularly stratified at the bloom station (Exp01), with a high degree of variability in the Brunt-Väisälä frequency (N 2 ) at the MLD, and comparatively weakly stratified at Exp05, with very little variability in the profile of N 2 (Fig. A2). The euphotic depth ranged from 31 to 53 m at the three stations where CTD profiles were collected during daylight hours (Table 1). Since the euphotic depth was typically deeper than the MLD, these stations may unlikely be light-limited. However, mean PAR in the mixed layer had a broad range from 16.65 µmol photons m −2 s −1 (Exp01) to 134.08 µmol photons m −2 s −1 (Exp05) that likely reflects the degree of cloudiness (since time of day was similar), thus preventing us from making any definitive conclusions on light limitation. Although still in the negative, surface layer temperatures were warmer at the bloom station Exp01 (−0.33 • C) and cooler at the remaining stations (−1.16 to −1.86 • C) ( Table 1).
Given the variability described above, it is anticipated that initial conditions of F v /F m and σ PSII would vary between incubation stations (Table 1; Fig. 4). The F v /F m was lower in the 6 • E SIZ (mean 0.27 ± 0.01) compared to Astrid Ridge (mean 0.35 ± 0.01) and much lower at the bloom station Exp01 (0.20 ± 0.01). The opposite was true for σ PSII , with initial conditions being higher in the 6 • E SIZ (mean 3.35 ± 0.28 nm 2 ) and the highest σ PSII at Exp01 (3.99 ± 0.37 nm 2 ), with the lowest σ PSII at the Astrid Ridge (mean 2.59 ± 0.05 nm 2 ). The differences in these initial conditions, i.e. seasonal timing and bloom amplitude, dFe surface concentrations, and F v /F m and σ PSII , indicate that some variability in the photophysiological response to iron addition could be anticipated. Nonetheless, despite these initial differences in conditions, very little variability was observed in the photophysiological response to iron addition (Fe) relative to the Controls ( Fig. 4; Table 2). A statistical t test between Fe and Control samples confirmed this, with no significant differences (p value > 0.05) in the photophysiology (F v /F m or σ PSII ) evident for any of the incubation experiments between treatments (Table 2). Similarly, no significant differences (p value > 0.05) were observed in either macronutrient or Chl-a concentrations (Table 2) between the Fe and Control incubations.

Discussion
The majority of Southern Ocean incubation studies have shown that phytoplankton are iron-limited (de Baar et al., 1990;Viljoen et al., 2018;Ryan-Keogh et al., 2017Browning et al., 2014a, b). However, no studies, to our knowledge, have been conducted in the SIZ during autumn. Furthermore, the majority of these iron addition incubation studies were conducted as longer-term incubations (> 96 h). The complexity induced by longer-term nutrient addition incubations is exacerbated by artefacts that cause an isolated system to be devoid of natural factors. These natural factors include nutrient resupply and grazing, which differs between the initial and incubated samples, whilst retaining only a spe-  cific sampled section from the water column as representative of the entire system (Geider and La Roche, 1994). While short-term incubations, within 24 h, are also an isolated system devoid of these natural factors, the impacts of these factors are reduced in the shorter incubation timeframe and increased by the longer incubation timeframe. Thus, shortterm incubation studies provide a sufficient period for eliciting a measurable photophysiological response (e.g. Ryan-Keogh et al., 2017), while at the same time minimizing the possibilities of artefacts in the incubation, as evidenced by the absence of any significant differences in phytoplankton biomass or nutrient concentrations between the Control samples after incubation and the initial samples before incubation. Indeed, other studies in the Southern Ocean have also reported significant changes in F v /F m within 24 h following iron addition (Boyd and Abraham, 2001;Hinz et al., 2012;Browning et al., 2014a, b;Ryan-Keogh et al., 2017), suggesting that it is possible to determine rapid (< 24 h) responses of photophysiology in iron-limited phytoplankton. An annual time series of satellite-derived Chl-a averaged over the Astrid Ridge and 6 • E SIZ region depicts the timing of the cruise relative to the seasonal cycle (Fig. 3) and clearly shows that both regional occupations were towards the end of the seasonal bloom. Therefore, it was anticipated that the region would be iron-limited and would respond favourably to iron addition. The study also covered a broad range of conditions when comparing the Astrid Ridge and 6 • E SIZ regions (Fig. 2), i.e. shallower versus deeper bathymetry, lower versus higher biomass, lower versus higher dFe concentrations, lower versus higher F v /F m , and higher versus lower σ PSII . Similarly, the average phytoplankton community composition between the two regions differed substantially (Kauko et al., 2022a, b), where pennate diatoms (72 %) and centric diatoms (56 %) dominated in the Astrid Ridge region (Exp02 and Exp03), while the 6 • E SIZ region consisted mostly of flagellates (Exp04 and Exp05, 45 %), with the exception of Exp01 that together with flagellates had a high abundance of diatoms (74 %). Despite contrasting conditions in physics (density, stratification, cumulative photon dose, mean PAR in the mixed layer), chemistry (nitrate, silicate, and dFe) and biology (Chl-a, F v /F m , σ PSII , and community composition), none of the five iron incubation experiments displayed any significant differences between the Fe and the Controls for photophysiology, or for any of the ancillary parameters (Table 1 and Figs. A1 and A2). As such, iron was not considered limiting to photosynthesis at any of the autumn stations in the DML SIZ. This unexpected finding implies that despite the timing of the cruise occupation relative to the seasonal bloom termination, iron was unlikely the primary driver of the bloom's termination (Kauko et al., 2021). Coincidently, Ryan-Keogh et al. (2023) proposed a greater probability of iron limitation in spring and summer in comparison to autumn and winter, which aligns with the results of our study. Furthermore, upon evaluating the initial dFe : nitrate (nmol : µmol) and dFe : phosphate (nmol : µmol) ratios (Table 1) for the experimental stations, it is worthy to note that the dFe : nitrate ratios appear to be higher than the reported values, for example, the wintertime assessment of dFe and nitrate distributions of Ellwood et al. (2008) in the south Tasman Sea of the Southern Ocean. Ellwood et al. (2008) reported a low range of dFe : nitrate ratios (0.005-0.018 nmol : µmol) further south from ∼ 52 • S, which corresponded with other HNLC regions that reported iron-limiting conditions under low dFe : nitrate ratios (∼ 0.01 nmol : µmol) (Ellwood et al., 2008 and references therein). Based on this evidence, the high dFe : nitrate ratios from our study (0.022-0.055 nmol : µmol, Table 1) indicate very little probability for an iron limitation but rather limitations on light and other trace metals such as manganese instead (Wu et al., 2019;Browning et al., 2021;Hawco et al., 2022). The observed iron concentrations and these results suggest either an internal short-term or continuous supply of dFe that prevent the bloom from exhausting a finite dFe reservoir that would otherwise be expected so late in the growing season from a stratified water column. An example of the former mechanism could be a dFe supply from remineralization, in which high bacterial abundance could serve as a proxy (Boyd et al., 2010a;Tagliabue et al., 2017;Bressac et al., 2019) based on seasonal timing of the cruise occupation (i.e. post-bloom peak in autumn). This high bacterial abundance has been observed previously by Richert et al. (2019) during spring and summer in the Amundsen Sea, who suggested high bacterial abundance as a contributing factor to sustaining and promoting phytoplankton growth in autumn beyond the spring to summer bloom season. However, the bacterial abundance observed at both the Astrid Ridge (3.8 × 10 5 cells mL −1 ) and in the southern section of the bloom region along the 6 • E transect (3.9 × 10 5 cells mL −1 ) was only slightly higher than at the bloom station Exp01 (2.6 × 10 5 cells mL −1 ) (Kauko et al., 2021). These ranges were similar to the bacterial abundance previously observed in other Southern Ocean studies (Evans and Brussaard, 2012) and during different bloom phases (Fourquez et al., 2015;Christaki et al., 2021). Conversely, the external, continuous supply of dFe may be more viable, where anomalies in the easterly winds could drive sea ice southwards, favouring the upwelling of iron-rich, warmer deep water as suggested by Moreau et al. (2023). In addition, Kauko et al. (2021) utilized ∼ 20 years of satellite-derived ocean colour data to suggest that the high bloom magnitude in this region was enhanced by flow patterns in the Weddell Gyre and tidal current interactions with seafloor topography enhancing primary productivity by natural fertilization. And finally, considering factors that determine the bloom end, instead of a bottom-up or micronutrient limitation (e.g. a coastal manganese limitation; Wu et al., 2019;Browning et al., 2021), other factors such as high concentrations of krill swarms, which was observed by Kauko et al. (2021) around the 6 • E transect, could suggest high levels of phytoplankton grazing, particularly in the Exp01 region (Moreau et al., 2023). Furthermore, bacteria, viral lysis, ice formation, wind mixing, and decreasing incident light may all be considered more important in curtailing the seasonal bloom in this particular region. Indeed, the ambient iron concentrations within the study region at the time of sampling may have been sufficient to fulfil the cellular requirements of the phytoplankton (Strzepek et al., 2011).

Conclusions
The results from this study show that although in theory it is expected that parts of the Southern Ocean are iron-limited during autumn, it is not necessarily true for the sea-ice zone region surrounding Astrid Ridge and along the 6 • E transect. The observed in situ F v /F m and σ PSII is suggestive of efficient photophysiology, since the iron addition did not lead to increased efficiency in phytoplankton photophysiology. The primary drivers of sustained iron supply to the region in support of phytoplankton growth late in the season are being potentially provided both from below (i.e. vertical supply from shallow bathymetry interactions with currents, as well as upwelling of iron-rich, warmer deep water) and from within (i.e. bacterial-driven remineralization). However, further examination of these sources and the type of iron being supplied is required to confirm the dominant resupply mechanism. It is recommended that future studies in this region help to bridge the knowledge gaps by studying the varying impacts of light in tandem with iron and other trace metals, which may instead be limiting during this time of the year, with an emphasis on short-term studies to understand the photophysiological response of phytoplankton in the absence of community induced responses.   Appendix B: Table   Table B1. Associated numbers (n), minimum, maximum, and mean ( ± standard deviations) parameters for the 6 • E SIZ and the Astrid Ridge for Chl-a concentrations (µg L −1 ), F v /F m , σ PSII (nm 2 ), macronutrients nitrate, phosphate, and silicate (µM) and the dFe concentrations (nM). Data availability. All datasets on the underway samples (chlorophyll-a, photophysiology (F v /F m and σ PSII ) and nutrients (nitrate, phosphate, and silicate)), as well as the incubation data which appear in this paper, are available on Zenodo https://doi.org/10.5281/Zenodo.6322942 (Singh et al., 2022); the CTD-Rosette surface photophysiology data and the surface iron data from the GoFlo can also be found at this link. Full datasets for the other CTD-Rosette water column data are available at the Norwegian Polar Data Centre; Norwegian Polar Institute, https://doi.org/10.21334/npolar.2021.5e510f85 (chlorophyll-a and mixed layer depth; Kauko et al., 2020); and Norwegian Marine Data Centre, https://doi.org/10.21335/NMDC-1503664923 (nutrients; Chierici and Fransson, 2020).
Author contributions. TJRK and SJT conceptualized the study. AS and TJRK collected the data and performed the data analysis. MVA, NS, and AS conducted the trace metal clean water collection and sampling. SM planned the general biological sampling of the cruise. SM and HMK assisted in collecting and analysing the chlorophylla data and all the CTD-Rosette samples. SS and AS analysed the dissolved iron samples, SS performed the data analysis, and ANR guided the analysis of the dissolved iron samples. AF was the PI for the SANOCEAN and SOPHY-CO 2 project and was involved in cruise planning of the water column sampling onboard the cruise. MC was responsible for water column collection and analyses of all the nutrient samples obtained from the underway, water column, and incubation experiments. TNM supported preparations for the iron addition incubations. AS and TJRK produced the figures. AS wrote the initial paper. TJRK, SF, SJT, and AS contributed to the study design, interpretation of the results, and writing of the paper. All authors contributed to commenting on the paper.
Competing interests. The contact author has declared that none of the authors has any competing interests.
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Special issue statement. This article is part of the special issue "The Weddell Sea and the ocean off Dronning Maud Land: unique oceanographic conditions shape circumpolar and global processes -a multi-disciplinary study (OS/BG/TC inter-journal SI)". It is not associated with a conference.