Articles | Volume 1-osr7
https://doi.org/10.5194/sp-1-osr7-10-2023
https://doi.org/10.5194/sp-1-osr7-10-2023
27 Sep 2023
 | OSR7 | Chapter 3.1
 | 27 Sep 2023 | OSR7 | Chapter 3.1

Dissolved oxygen as an indicator of multiple drivers of the marine ecosystem: the southern Adriatic Sea case study

Valeria Di Biagio, Riccardo Martellucci, Milena Menna, Anna Teruzzi, Carolina Amadio, Elena Mauri, and Gianpiero Cossarini
Abstract

Oxygen is essential to all aerobic organisms, and its dynamics in the ocean involve interconnected physical and biological processes that form the basis of the functioning of the marine ecosystem. The study of dissolved oxygen (DO) variations under multiple drivers is currently one of the main goals of climate and marine-ecological scientific communities, and the quantification of DO levels is essential for the assessment of the environmental status, especially in coastal areas.

We investigate the 1999–2021 interannual variability in DO in the southern Adriatic Sea, a marginal area of the Mediterranean Sea, where deep-water formation processes occur, contributing significantly to the ventilation of the eastern Mediterranean Basin. Following the Marine Strategy Framework Directive, which promotes the integration of different observational platforms, we use DO modelled by the Copernicus Marine Mediterranean Sea biogeochemical reanalysis, which assimilates satellite chlorophyll concentrations and to which we apply a bias correction using DO Argo float measurements in 2014–2020. A correlation analysis of the time series of the first three modes of variability (86 % of the total variance) of the DO profiles extracted from the bias-corrected reanalysis with key meteo-marine indicators shows a link with (i) net heat fluxes related to oxygen solubility, (ii) vertical mixing, (iii) biological production at the surface and in subsurface layers, and (iv) circulation associated with the entrance of northern Adriatic waters. The alternating entrance of Levantine and Atlantic waters through the North Ionian Gyre (NIG) appears to be the driver of the fourth mode of variability, which explains 8 % of the total variance. Moreover, we find that the first temporal mode of variability is the main driver of the negative anomaly of DO in the 0–600 m layer in 2021 with respect to the 1999–2020 climatology. We ascribe the lower content of DO in 2021 to a negative anomaly of the subsurface biological production in the same year, in agreement with the previous correlation analysis, but not to heat fluxes. Indeed, in agreement with previous studies, we observe a sharp increase in salinity favoured by the cyclonic circulation of NIG from 2019 onwards. We interpret this as a possible regime shift that is not captured by the time series analysis and whose possible consequences for Ionian–Adriatic system ventilation and for marine organisms should be carefully monitored in the near future.

Dates

Table 1Products used in the present work. Prod. ref. nos. 4 and 5 are a forcing for prod. ref. nos. 1 and 2, and prod. ref. no. 8 is a forcing for prod. ref. nos. 4 and 5.

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1 Introduction

Dissolved oxygen (DO) is a key indicator for monitoring the marine ecosystem functioning because it is the result of several atmospheric, hydrodynamic, and biogeochemical driving processes (such as air–sea fluxes, vertical convection and mixing, horizontal transport, and biological production and consumption; Keeling and Garcia, 2002; Oschlies et al., 2018; Pitcher et al., 2021). Indeed, DO is currently being studied under the global warming scenarios by climate and marine-ecological scientific communities (e.g. IPCC, 2019; Kwiatkowski et al., 2020; Garcia-Soto et al., 2021), as oxygen depletion has been observed in the global ocean as well as at the local scale (Breitburg et al., 2018). Climate models predict a reduction in global-ocean dissolved oxygen content (Matear et al., 2000; Oschlies et al., 2008; Stramma et al., 2010; Reale et al., 2022), so this parameter is of primary interest, especially in those areas where oceanic processes connect surface and deep layers.

The southern Adriatic Sea (SAdr; Fig. 1a) is one of these areas, as it is an area of deep-water formation (Gačić et al., 2002; Pirro et al., 2022) and represents one of the deep engines of the eastern Mediterranean thermohaline circulation (Malanotte-Rizzoli et al., 1999), which is crucial for the eastern basin ventilation. The Adriatic Sea (Fig. 1a) is an elongated, semi-enclosed, and roughly north–south-oriented basin characterized by a shallow northern shelf (shallower than 80 m) and a deep pit in its southern part (maximum depth of approximately 1200 m) which is connected to the Ionian Sea (central Mediterranean Basin) through the Otranto Strait (with a maximum depth of 800 m). The Adriatic Sea is characterized by a cyclonic circulation governed by several drivers: river runoff, wind stress, surface buoyancy fluxes, and mass exchanges through the Otranto Strait (Cushman-Roisin et al., 2013).

https://sp.copernicus.org/articles/1-osr7/10/2023/sp-1-osr7-10-2023-f01

Figure 1(a) Southern Adriatic area (blue square) within the Mediterranean Sea. (b) Cross-correlation map of surface oxygen, nitrate, and chlorophyll concentration provided by Copernicus biogeochemical reanalysis (prod. ref. nos. 1 and 2, Table 1) in the southern Adriatic area with respect to the central point of the pit indicated by the red star; the black contour line delimits the area with cross-correlation equal to or higher than 0.9; dashed lines indicate the trajectories of BGC-Argo floats (in situ TAC data, prod. ref. no. 3) passing the area. (c) Hovmöller diagrams of the dissolved oxygen concentration from in situ TAC data (prod. ref. no. 3) within the 0.9 cross-correlation area (b). Data have been interpolated for readability of the plot. (d) Hovmöller diagrams of dissolved oxygen concentration from Copernicus biogeochemical reanalysis (prod. ref. nos. 1 and 2), spatially averaged within the area of cross-correlation equal to 0.9 (a) in the time period of 1999–2021, after the bias correction procedure based on in situ TAC data (prod. ref. no. 3).

The SAdr is strongly influenced by the inflow of water masses from the northern Adriatic Sea (i.e. North Adriatic Dense Water; Querin et al., 2016) and the Ionian Sea. In particular, the inflow of southern water masses is triggered by the periodic reversal of North Ionian Gyre circulation (Gačić et al., 2002; Civitarese et al., 2010; Menna et al., 2019; Gačić et al., 2021). This oscillating system, called the Adriatic–Ionian Bimodal Oscillating System (BiOS), changes the circulation of the North Ionian Gyre from cyclonic to anticyclonic and vice versa, modulating the advection of water masses in the Adriatic Sea (Gačić et al., 2010; Rubino et al., 2020). The cyclonic circulation of the North Ionian Gyre causes the advection of saline water masses of Levantine origin (i.e. Levantine Intermediate Water, LIW; Cretan Intermediate Water; Ionian Surface Water; and Levantine Surface Water; Manca et al., 2006), while the anticyclonic circulation favours the inflow of Atlantic Water and a relative decrease in salinity in the SAdr (Gačić et al., 2011; Menna et al., 2022a). This feature has a strong influence on the biogeochemical properties of the SAdr, affecting nutrient availability (Civitarese et al., 2010), phytoplankton blooms (Gačić et al., 2002; Civitarese et al., 2010), and species composition (Batistić et al., 2014; Mauri et al., 2021).

While hydrodynamic and biogeochemical properties of the SAdr have been widely described in several studies (e.g. Civitarese et al., 2010; Cushman-Roisin et al., 2013; Lipizer et al., 2014; Kokkini et al., 2018, 2020; Mavropoulou et al., 2020; Mihanović et al., 2021; Menna et al., 2022b), to the best of our knowledge DO dynamics in the area in connection with relevant driving processes over decadal timescales have not been addressed yet.

Investigating the DO multidecadal variability is crucial for quantifying the state of the marine environment (Marine Strategy Framework Directive, MSFD: EU-COM, 2008; Oesterwind et al., 2016) and for understanding anthropogenic impacts on the marine environment (IPCC, 2022). The emerging ecosystem-based management method proposed by the MSFD (2008/56/EC) promotes the use of different observational platforms, allowing information on the space-time distribution of important parameters related to water quality to be synoptically collected (Martellucci et al., 2021).

In this context, the present work integrates the state-of-the-art approach of in situ measurements (in 2014–2020, distributed by Copernicus In Situ Thematic Centre, INS TAC) with the Copernicus biogeochemical reanalysis in the Mediterranean Sea at high resolution (Cossarini et al., 2021) with the aim of characterizing the DO dynamics in the SAdr in the time period of 1999–2021. In particular, we aim to assess DO interannual variability in an area (SAdr) sensitive to multiple drivers (e.g. atmospheric forcing, Mediterranean circulation, and biological processes) and to evaluate the relative importance of the different drivers in this area.

2 Data and methods

In the present study the DO concentration in the SAdr area (Fig. 1a) was assessed by combining data from the Copernicus biogeochemical reanalysis in the Mediterranean Sea (product reference numbers – prod. ref. nos. – 1 and 2 in Table 1; Cossarini et al., 2021) in 1999–2021 and the Copernicus in situ dataset (prod. ref. no. 3), available for the period 2014-2020 (Figs. 1b-c). The temporal evolution of the combined model–in situ DO concentration profile in the time period of 1999–2021 is shown in Fig. 1d.

In particular, we used the Biogeochemical Argo (BGC-Argo) float measurements of in situ DO to compute a bias correction of the daily DO concentrations simulated by the biogeochemical reanalysis at 1/24 horizontal resolution. In fact, the biogeochemical reanalysis does not include BGC-Argo float DO assimilation and displays an average RMSD (root mean square difference) of 15 mmol m−3 for DO in the 0–600 m depth layer with respect to the observations in the area (Cossarini et al., 2021; Teruzzi et al., 2022). Quantile mapping, a technique largely used for climate simulations (e.g. Hopson and Webster, 2010; Jakob Themeßl et al., 2011; Gudmundsson et al., 2012), was adopted to perform the reanalysis bias correction. The quantile mapping technique adjusts the cumulative distribution of the data simulated for the past or future period by applying a transformation between the quantiles of the simulated and observed data in the present. In our application, we adapted the code publicly provided by Beyer et al. (2020) at https://doi.org/10.17605/OSF.IO/8AXW9 (Beyer, 2023) and included available in situ data of daily DO (Fig. 1c) within a representative area (Fig. 1b) of the southern Adriatic in the period 2014–2020 and DO reanalysis data for the same days of measurements. The representative area was identified by applying a spatial cross-correlation analysis (Martellucci et al., 2021) to the biogeochemical reanalysis centred on the SAdr pit and selecting the correlation threshold of 0.9 (Fig. 1b). Specifically, we considered the cross-correlation between the surface data of DO, nitrate, and chlorophyll concentrations in the central point of the pit and those at each spatial grid point in the domain to identify the area that displayed the same dynamics at the surface from a phenomenological perspective. Further details of the quantile mapping bias correction are included in Appendix A.

We then applied the empirical orthogonal function (EOF) analysis (e.g. Thomson and Emery, 2014) to the vertical profiles in Fig. 1d to describe DO variability in the SAdr area in the period 1999–2021. The EOF analysis allows us to identify the spatial patterns of variability (i.e. EOF vertical patterns), describe how they change in time by means of time series (i.e. EOF time series), and associate the explained variance with each mode.

Finally, we performed a Pearson correlation analysis between the EOF time series in 1999–2021 and the following series of forcing indexes (reported in Fig. 2), providing evidence of the mechanisms driving oxygen concentration and dynamics in the area:

  • heat fluxes in the SAdr as a proxy for thermal and mixing and stratification cycles (from prod. ref. no. 8 in Table 1; Fig. 2a);

  • mixed-layer depth in the SAdr as a proxy for both local vertical mixing and water residence times in the pit (prod. ref. nos. 4 and 5; Escudier et al., 2021; Fig. 2b);

  • chlorophyll concentration at the surface and in the subsurface in the SAdr as a proxy for biological production in spring and late spring–summer, respectively (prod. ref. nos. 1 and 2; Fig. 2c–d);

  • heat fluxes in the northern Adriatic Sea (NAdr), as a proxy for oxygen-rich dense-water formation in the NAdr and its transport into the pit (prod. ref. no. 8; Fig. 2e);

  • North Ionian Gyre (NIG) vorticity derived from satellite altimetry, as a proxy for the inflow of Levantine waters and Atlantic Water (AW) (prod. ref. nos. 6 and 7; Fig. 2f).

In particular, the temporal phases of the NIG are defined as cyclonic and anticyclonic, respectively, when the vorticity field is positive and negative, as highlighted by the de-seasonalized time series in Fig. 2f.

https://sp.copernicus.org/articles/1-osr7/10/2023/sp-1-osr7-10-2023-f02

Figure 2Time series of the main forcing in the time period of 1999–2021: (a) net heat fluxes in SAdr (prod. ref. no. 8 in Table 1), (b) mixed-layer depth (prod. ref. nos. 4 and 5), (c) surface chlorophyll concentration (prod. ref. nos. 1 and 2), (d) subsurface chlorophyll concentration (30–80 m layer in which deep chlorophyll maximum, DCM, is located; prod. ref. nos. 1 and 2), (e) net heat fluxes in the NAdr (prod. ref. no. 8), and (f) NIG current vorticity (grey line) and de-seasonalized time series as obtained by applying a low-pass filter of 13 months (thick black line) (prod. ref. nos. 6 and 7).

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Mixed-layer depth (computed in prod. ref. nos. 4 and 5 considering the 0.03 kg m−3 density difference with respect to the near-surface value at 10 m depth) and the chlorophyll at the surface and in the subsurface (30–80 m, where the deep chlorophyll maximum is located) were spatially averaged in the SAdr area (41.6–42.1 N, 17.6–18.1 E; to consider the whole volume of the pit); heat fluxes were calculated in both the SAdr area and in the NAdr area (44.5–45.5 N, 13–13.5 E), while current vorticity was computed in the northern Ionian Sea (37–39 N, 17–19.5 E).

In the correlation analysis, the time series of the heat fluxes in the NAdr (Fig. 2e) has been temporally lagged by 2 months as an estimated mean time for the entrance in the SAdr pit of waters originating in the northern Adriatic area (Vilibić and Mihanović, 2013; Querin et al., 2016; Mihanović et al., 2021). Moreover, we tested the significance of the correlation coefficients between EOF and driver time series using a parametric t test (with a reference significance level of 0.05).

3 Results

3.1 Temporal scales of variability in connection with drivers

Dissolved oxygen in the southern Adriatic area (Fig. 1a) shows in the subsurface layers an alternation between periods of enrichment (in 2004–2006, 2010–2013, 2016–2017) and sharp declines that impacted the oxygen minimum layer (OML), located between 100 and 300 m. Low concentration values are also observed in the years between 1999 and 2003.

The EOF analysis was performed on the vertical profiles of the oxygen anomaly, derived by removing the mean profile in the period 1999–2021 and then normalized dividing by their standard deviation.

The time series of the first four EOF modes, which explain up to 95 % of the oxygen variability in the water column, are shown along with the corresponding vertical patterns in Fig. 3a, c, e, g and Fig. 3b, d, f, h, respectively.

https://sp.copernicus.org/articles/1-osr7/10/2023/sp-1-osr7-10-2023-f03

Figure 3EOF time series (a, c, e, g) and vertical patterns (b, d, f, h) of the first four modes computed on the bias-corrected dissolved oxygen concentration in the southern Adriatic area shown in Fig. 1d. The explained variances of the four modes are 48.9 %, 19.7 %, 17.7 %, and 8.4 %.

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The EOFs are interpreted considering the correlation of the EOF time series (Fig. 3a, c, e, g) with the time series of the forcing indicators shown in Fig. 2 (see Table 2), with heat fluxes in the northern Adriatic Sea time-lagged by 2 months as the estimated time of entry of the NAdr dense water in the SAdr pit.

Table 2Correlations between the first four temporal modes of EOFs of DO (Fig. 3a, c, e, g) and the forcing fields (with heat fluxes in the northern Adriatic Sea time-lagged by 2 months; Fig. 2). Non-statistically significant correlations are identified by a significance level higher than 0.05 and indicated by “n.s.” in the table.

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The first mode (Fig. 3a–b), accounting for 48.9 % of the explained variance, can be associated with the seasonal cycle of oxygen concentration in the upper layers: its vertical pattern mainly affects the first levels (Fig. 3b), the corresponding time series shows relative maximum values in spring (Fig. 3a), and it shows a statistically significant but moderate correlation (r=0.56) with heat flux and a lower correlation with the subsurface chlorophyll concentration (r=0.43) in the SAdr area (first column in Table 2).

The second and third modes (Fig. 3c–d and Fig. 3e–f, respectively), describing 19.7 % and 17.7 % of the variance, respectively, affected both the upper and deeper layers. Both modes display relative maximum values in summer, but they have different correlation coefficients with the explanatory factors. The time series of the second mode (second column in Table 2) shows a significant but low correlation with multiple drivers, exceeding 0.4 only for surface chlorophyll (r=-0.41) and waters from the NAdr area (r=0.48). The time series of the third mode (third column, same table) is moderately correlated with both surface chlorophyll (r=-0.61) and NAdr waters (r=0.68 correlation), but also with heat fluxes in the area (r=0.51) and, to a lower extent, with mixed-layer depth (r=-0.41) and subsurface chlorophyll (r=0.48).

The fourth mode (Fig. 3g–h), which describes 8 % of the variance, can be ascribed mainly to the vorticity of the NIG (r=-0.37, last column in Table 2), which affects the oxygen concentration in the intermediate layer (100–500 m depth), filled by LIW, and acts in the opposite direction in the upper and deeper layers (Fig. 3h).

Analysing the four modes in order of decreasing explained variance, we ascribe the seasonal variability connected with solubility mainly to the first mode, whereas we associate the biological contribution to oxygen dynamics to multiple interacting modes. In fact, the first mode explains the onset of the subsurface oxygen maximum (SOM) in spring, while the summer dynamics of the SOM are partially related to the third mode. The second mode, whose time series is correlated with surface chlorophyll evolution among other factors, can explain that part of the oxygen variability that is related to winter surface productivity.

The SOM, evident in summer oxygen profiles in Fig. 1c–d at about 40 m depth, is a feature that has already been observed in a great part of oligotrophic oceans (Riser and Johnson, 2008; Yasunaka et al., 2022) and of the Mediterranean Sea (e.g. Kress and Herut, 2001; Copin-Montégut and Bégovic, 2002; Manca et al., 2004; Cossarini et al., 2021; Di Biagio et al., 2022), and it represents an emerging property resulting from multiple interacting ecosystem processes (i.e. air–sea interactions, transport, mixing, and biological production and consumption) and is, indeed, captured by multiple modes.

The third mode, which also describes the high concentration values in the deep layers in the period 2005–2006 and 2012–2014, is also moderately associated with a multiannual signal of the inflow of deep, denser, and oxygenated water from the northern Adriatic Sea (r=0.68, third column in Table 2; Querin et al., 2016). Finally, it is worth noting that an EOF analysis of detrended DO time series (not shown) yields fairly similar results but with the third mode only weakly correlated with the forcing indexes (r<0.4). Indeed, we can conclude that the third mode captures a signal of long-term evolution of oxygen concentration associated with changes in heat fluxes and chlorophyll concentration.

3.2 The 2021 anomaly

The year 2021 shows an overall negative anomaly in the oxygen concentration profile (Fig. 4b) compared to the 1999–2020 climatological profiles (Fig. 4a). In particular, the anomaly affects a layer that thinned during the year, moving from 0–600 m depth in winter–early spring to 30–400 m in late spring–summer and 0–80 m in autumn. The (absolute) maximum values correspond to 25–30 mmol m−3 at the surface in spring and at the SOM depth in summer.

https://sp.copernicus.org/articles/1-osr7/10/2023/sp-1-osr7-10-2023-f04

Figure 4Hovmöller diagrams of 1999–2020 mean of daily oxygen concentration computed from Copernicus biogeochemical reanalysis (prod. ref. nos. 1 and 2, Table 1) after the bias correction procedure based on in situ TAC data (prod. ref. no. 3) (a) and anomaly in 2021 with respect to the period of 1999–2020 (b).

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We verified that, among the EOF modes, the negative anomaly of the first mode is the main contributor to the 2021 negative oxygen anomaly (not shown). The time series of the first mode (Fig. 3a) is actually negative from 2019 and corresponds to the negative anomaly of only one of its drivers (Table 2), i.e. subsurface chlorophyll (Fig. 2d), and not heat fluxes (Fig. 2a). In particular, we estimated a mean negative anomaly approximately equal to 6 % with respect to the climatological mean (1999–2020) for subsurface chlorophyll in 2021.

One of the causes of the decrease in total oxygen concentration in the SAdr could be due to the exceptional salinization observed in the SAdr since 2017 (Mihanović et al., 2021; Menna et al., 2022b). This increase was related to the inflow of new, warmer, and noticeably saltier water masses from the north-eastern Ionian Sea (Mihanović et al., 2021; Menna et al., 2022b). The inflow of saltier and warmer water masses is also evident by observing the temporal evolution of these parameters through the Strait of Otranto (Fig. B1). In particular, in the upper layer (0–150 m) both temperature and salinity show an overall positive trend throughout the period 1999–2021, whereas the decrease observed in 2006–2011 and 2017–2018 can be associated with the inflow of less saline AW, triggered by the anticyclonic circulation of the NIG (Fig. 2f). In the intermediate layer (150–600 m), salinity shows a positive trend in 1999–2021, while no clear trend is observed for temperature. Moreover, a sharp increase in salinity (∼0.1) is observed in 2019. This increase occurred after the NIG inversion from anticyclonic to cyclonic (Fig. 2f), resulting in a further increase in salinity due to both the decrease in AW advection and the increase in LIW inflow.

4 Conclusions

Merging the Copernicus biogeochemical reanalysis in the Mediterranean Sea with in situ TAC data of biogeochemical Argo floats allowed us to characterize the interannual variability in dissolved oxygen in the southern Adriatic Sea in the time period of 1999–2021 and the 2021 anomaly with respect to the mean over 1999–2020. This study enriches our knowledge of the dissolved oxygen state and long-term dynamics in the area by proposing a seamless time and space perspective that is complementary to previous climatologies and data aggregation information (e.g. Lipizer et al., 2014) and adding an explanatory framework for the driving mechanisms in the marine environment.

The EOF statistical analysis that we conducted on the vertical oxygen profiles yielded two key results. First, in contrast with a climatological view, the analysis was able to capture most of the interannual oxygen variability associated with variability in the main drivers (i.e. heat fluxes affecting solubility, biological productivity, vertical mixing). We do not detect a clear deoxygenation trend in the subsurface layer, while the multiannual variability is characterized by an alternation of enrichment and reduction phases, whose dominant correlations with the drivers for each EOF time series are in the (absolute) range of 0.40–0.70. The possibility of observing such cyclic signals is enhanced by the relatively small volume and short residence time of the SAdr pit waters (Querin et al., 2016) with respect to other Mediterranean areas (Coppola et al., 2018). This feature makes the SAdr a potential efficient probe to detect a rapid response to changes in its meteo-marine drivers, i.e. circulation and atmospheric patterns.

Indeed, as our second result, the variability that is not explained by the EOF decomposition appears to be connected with a possible regime shift, associated with the entrance of new water masses that are warmer, markedly saltier, and less oxygenated which were not previously observed in the analysed time period.

The exceptional increase in salinity occurring after 2019 has already been documented (Mihanović et al., 2021; Menna et al., 2022b) and also observed north of the SAdr pit. Further monitoring of such anomalously high salinity values and assessment of their potential impact on the marine food web are of great importance, as picoplankton groups are sensitive to this environmental variable (Mella-Flores et al., 2011), and changes in biomass and production due to salinity have already been observed in previous studies in the Adriatic Sea (Beg Paklar et al., 2020; Mauri et al., 2021). Moreover, if such a strong negative oxygen anomaly as that observed in 2021 were to persist, it could have direct impacts on local marine organisms, as well as on the cycling of dissolved chemical elements (Conley et al., 2009), potentially altering the energy flux towards the higher trophic levels (Ekau et al., 2010). The importance of the relationship between dissolved oxygen and the catch distribution of some marine species has already been proved in the Adriatic Sea (Chiarini et al., 2022).

By integrating model and in situ data, our study demonstrates the importance of following up the oxygen content in a seamless spatial and temporal way, as it is a fundamental indicator of good environmental status (GES; Oesterwind et al., 2016) and a factor that significantly affects fishing activities and the economy.

Appendix A: Quantile mapping bias correction of DO concentration profiles

Figures A1 and A2 show the modelled DO concentration profiles and histogram distributions before and after the quantile mapping bias correction, respectively, conducted by using the BGC-Argo float measurements available in 2014–2020 (Fig. 1c). The quantile mapping, better than other methods (i.e. additive delta change, multiplicative delta change, and variance scaling; results not shown), acted on the profiles by modifying the values of the concentrations (as indicated by the different colour bars in Fig. A1a and A1b) but, at the same time, maintaining the main dynamics observed before the correction: mixing and stratification at the surface during the year, subsurface oxygen maximum onset in spring and development in summer, and interannual variability related to the mixed-layer-depth dynamics in the intermediate layers. The distributions of the values of the model output before and after the quantile mapping bias correction and the values from BGC-Argo floats are displayed in Fig. A2. The correction actually changed the modelled values (Fig. A2a) to reproduce the shape of the distribution of the observations (Fig. A2c). In particular, after the correction (Fig. A2b) the modelled data show higher variability and a more skewed distribution toward the higher values, similarly to the observations.

https://sp.copernicus.org/articles/1-osr7/10/2023/sp-1-osr7-10-2023-f05

Figure A1Hovmöller diagram of the modelled oxygen concentrations spatially averaged within the area of autocorrelation equal to 0.9, indicated in Fig. 1b, before the bias correction by quantile mapping (a) and after the procedure (b).

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https://sp.copernicus.org/articles/1-osr7/10/2023/sp-1-osr7-10-2023-f06

Figure A2Frequency histogram of modelled oxygen concentrations before the bias correction by quantile mapping (a) and after the procedure (b), compared with BGC-Argo observations (c).

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Appendix B: Time series of surface and intermediate temperature and salinity at the Otranto Strait
https://sp.copernicus.org/articles/1-osr7/10/2023/sp-1-osr7-10-2023-f07

Figure B1Time series of temperature (a) and salinity (b), averaged in the vertical layers 0–150 m (red lines) and 150–600 m (black lines) of the Otranto Strait (39.8 N, 18.5–19.5 E) in the time period of 1999–2021. In panel (a), light red and dark red indicate data before and after de-seasonalization, respectively. Data are provided by Copernicus physical reanalysis (prod. ref. nos. 4 and 5, Table 1).

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Data availability

Publicly available datasets were analysed in this study. Modelling and in situ data can be found at the Copernicus Marine Service, with references and DOIs indicated in Table 1 of the paper.

Author contributions

VDB and GC conceived the idea. VDB, RM, and MM conducted the analysis. VDB, RM, and GC wrote the first draft, with contributions from the other co-authors. All the authors discussed and reviewed the submitted manuscript.

Competing interests

The contact author has declared that none of the authors has any competing interests.

Disclaimer

Publisher’s note: Copernicus Publications remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Acknowledgements

This study has been conducted using EU Copernicus Marine Service Information.

Financial support

This study has been partly funded by the Copernicus Mediterranean – Monitoring Forecasting Centre (contract LOT reference: 21002L5-COP-MFC MED-5500, issued by Mercator Ocean) within the framework of the Marine Copernicus Service.

Review statement

This paper was edited by Marilaure Grégoire and reviewed by three anonymous referees.

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Oxygen is essential to all aerobic organisms, and its content in the marine environment is continuously under assessment. By integrating observations with a model, we describe the dissolved oxygen variability in a sensitive Mediterranean area in the period 1999–2021 and ascribe it to multiple acting physical and biological drivers. Moreover, the reduction recognized in 2021, apparently also due to other mechanisms, requires further monitoring in light of its possible impacts.
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