1 Introduction
Ocean ecosystems play a critical role in the Earth's carbon (C) cycle (IPCC, 2014). The quantification of their impacts of both present conditions and future predictions remains one of the greatest challenges in oceanography (Siegel et al., 2016). In essence, the biological C pump is termed for the numerous processes involved in maintaining the vertical gradient in dissolved inorganic C. This includes processes such as organic matter production at the surface, its export and subsequent remineralization. Most of marine snow organic C conversion (i.e., remineralization) into by heterotrophic organisms (i.e., respiration) occurs in the mesopelagic zone (100–1000 m) (Martin et al., 1987; Buesseler and Boyd, 2009). Globally, the flux of C exported below 1000 m depth is the key determinant of ocean carbon storage capacity (Henson et al., 2011). However, there is no consensus on C transfer efficiency estimations from field experiments, leading to an imbalance of the water column C budget (Giering et al., 2014). Resolving this imbalance is at the core of numerous studies in the global ocean, but also regionally, especially in the Mediterranean Sea (MedSea). Due to limited exchanges with the adjacent basin and the existence of an intense overturning circulation qualitatively resembling the global one (but with shorter timescales), the MedSea is often considered a laboratory to observe and understand the impact of transient climate variability on ecosystems and biogeochemical cycles (Malanotte-Rizzoli et al., 2014). In a context of climate changes, better constraining C fluxes and the ocean C storage capacity is of crucial importance.
Figure 1
(a) Schematic representation of the convergence of the different estimators of oxygen consumption and C remineralization rates from the “oxygen dynamics”, “barium proxy” and “prokaryotic activity” tools; (b) location of the BATMAN cruise at the ANTARES observatory site in the NW Mediterranean Sea (4248 N, 610 E). The location of the DYFAMED station is reported for comparison (Sternberg et al., 2008); (c) potential temperature–salinity–depth plots and isopycnals for BATMAN profiles. SW: Surface Water; WIW: Winter Intermediate Water; LIW: Levantine Intermediate Water; DMW: Deep Mediterranean Water. Graph constructed using Ocean Data View (Schlitzer, 2002; Ocean Data View;
[Figure omitted. See PDF]
Particulate barium in excess (, i.e., biogenic Ba from total particulate Ba after correction for lithogenic Ba) is a geochemical tracer of particulate organic carbon (POC) remineralization in the mesopelagic layer (Dehairs et al., 1997). mostly occurs in the form of barite microcrystals () at these depths. In a global ocean undersaturated with respect to barite, studies report that would precipitate inside oversaturated biogenic micro-environments during POC degradation by heterotrophic prokaryotes in the mesopelagic zone, through sulfate and/or barium enrichment (Bertram and Cowen, 1997). The first-ever studies on mesopelagic reported coinciding maxima with depths of dissolved minimum and maximum (Dehairs et al., 1987, 1997). By using an 1D advection–diffusion model applied to profiles in the Atlantic sector of the Southern Ocean (ANTX/6 cruise; Shopova et al., 1995), Dehairs et al. (1997) established an algorithm converting mesopelagic concentration into consumption rate () and remineralized organic C (POC remineralization rate). This transfer function has been widely used until now (Cardinal et al., 2001, 2005; Dehairs et al., 2008; Jacquet et al., 2008a, b, 2011, 2015). Yet its validity has never been tested in other oceanic provinces. In the North Atlantic, Lemaitre et al. (2018) reported a – (obtained from apparent oxygen utilization divided by the water mass age) relationship not significantly different to that reported in Dehairs et al. (1997). Furthermore, significant progress was made in relating and dynamics to prokaryotic heterotrophic activity (Jacquet et al., 2015). These advancements clearly show that is closely related with the vertical distribution of prokaryote heterotrophic production (PHP) (the rate of change with depth), reflecting the temporal progression of POC remineralization processes. Also, in a first attempt to test the validity of the Dehairs transfer function in other locations, Jacquet et al. (2015) compared oxygen consumption rates () from direct measurements (dark community respiration, DCR) to derived from data (using the transfer function) in the Kerguelen area (Indian sector of the Southern Ocean). We revealed good convergence of rates from these two approaches, further supporting the Dehairs function to estimate POC remineralization rates in different biogeochemical settings of the Southern Ocean.
Here, we further investigate relationships between the mesopelagic proxy, prokaryotic activity and oxygen dynamics (Fig. 1a) in the northwestern Mediterranean Sea (MedSea), a different biogeochemical setting to those already studied (see references above). Today, observations of the various components of the MedSea biological C pump provide organic C remineralization fluxes varying by at least an order of magnitude (Santinelli et al., 2010; Ramondenc et al., 2016). Malanotte-Rizzoli et al. (2014) reviewing unsolved issues and future directions for MedSea research highlighted the need to further investigate biogeochemical processes at intermediate (mesopelagic) and deep layers to reconciliate the C budget in the Mediterranean basin. The previous particulate dataset is very scarce in the NW MedSea, with generally very low vertical sampling resolution (Sanchez-Vidal et al., 2005) or very restricted studied areas (Dehairs et al., 1987; Sternberg et al., 2008). Here we discuss , PHP and (from optode measurement during incubations) at the ANTARES / EMSO-LO observatory site (Fig. 1a and b). We hypothesize that the Dehairs transfer function converting into POC remineralization also applies in a different ocean ecosystem from the Southern Ocean. We suggest that the proxy can be used as routine tracer to estimate local-scale processes of mesopelagic POC remineralization in the Mediterranean basin.
2 Methods2.1 Study site
The BATMAN cruise (10.17600/16011100, 10–16 March 2016, R/V L'EUROPE) took place at the ANTARES/EMSO-LO observatory site (4248 N, 610 E; Tamburini et al., 2013), 40 km off the coast of Toulon, southern France (Fig. 1b). The hydrological and biogeochemical conditions at this site are monitored monthly in the framework of the MOOSE (Mediterranean Ocean Observing System for the Environment) program and of the EMSO (European Multidisciplinary Subsea Observatory) observation program. The hydrography displays the general three-layer MedSea system with surface, intermediate and deep waters (Hainbucher et al., 2014). Briefly, the main water masses can be distinguished (see potential temperature–salinity diagram during the BATMAN cruise in Fig. 1c): (1) Surface Water (SW); (2) Winter Intermediate Water (WIW); (3) Levantine Intermediate water (LIW); (4) Mediterranean Deep Water (MDW). LIW is present at intermediate depths (around 400 m at ANTARES) and is characterized by temperature and a salinity maxima.
2.2 Sampling and analyses
For particulate barium, 4 to 7 L of seawater sampled using Niskin bottles was filtered onto 47 mm polycarbonate membranes (0.4 m porosity) under slight overpressure supplied by filtered air. Filters were rinsed with a few milliliters of Milli-Q grade water to remove sea salt, dried (50 C) and stored in petri dishes. Thirteen depths between the surface and 1000 m were sampled by combining different casts sampled closely in time and space (total of 28 samples) with similar potential temperature–salinity profiles. No major changes in water mass characteristics occurred over the 3 d sampling period (Fig. 1c). In the laboratory, we performed a total digestion of filters using a concentrated triacid (0.5 mL HF, 1.5 mL , HCl 1 mL; all Optima grade) mixture in closed teflon beakers overnight at 95 C in a clean pressurized room. After evaporation close to dryness, samples were re-dissolved into 10 mL of 2 %. The solutions were analyzed for Ba and other elements of interest (Na and Al) by HR-ICP-MS (high-resolution inductively coupled plasma mass spectrometry; ELEMENT XR Thermo Fisher). Based on analyses of external certified reference standards, accuracy and reproducibility were both within %. Details on sample processing and analysis are given in Cardinal et al. (2001) and Jacquet et al. (2015). The presence of sea salt was checked by analyzing Na, and the sea salt particulate Ba contribution was found negligible ( % of total Ba). Particulate biogenic barium in excess (hereafter referred to as ) was calculated as the difference between total Ba and lithogenic Ba using Al as the lithogenic reference element. The lithogenic Ba concentration was determined using Al concentration and the upper continental crust (UCC) Ba : Al molar ratio (Taylor and McLennan, 1985). The biogenic Ba fraction ranged from 51 % to 91 % of the total particulate Ba signal (see Sect. 3.1). The standard uncertainty (Ellison, 2000) on concentration ranges between 5.0 % and 5.5 %. The term “in excess” is used to indicate that concentrations are larger than the background. The background (or residual value) is considered to be “preformed” at zero oxygen consumption left over after transfer and partial dissolution of produced during degradation of previous phytoplankton growth events. The background is set at 130 pM in this study.
Oxygen concentrations were measured using oxygen optode Aanderaa® 4330 for at least 24 h (on a 30 s time step) on samples taken at four depths in the mesopelagic layer (175, 250, 450 and 1000 m). Samples were placed into sealed 1 L borosilicate glass bottles incubated at a constant temperature of 13 C in thermoregulated baths. Optodes were calibrated using a homemade calibration facility. Oxygen consumption rates (later referred to as -Opt) were derived from a linear model calculation. Associated errors to the linear model fit are below 0.01 M h. Each oxygen consumption experiment has been duplicated for each depth. Average and standard deviation of the duplicates are reported in Fig. 3a. The larger associated errors are related to the differences between each duplicate, especially at the surface, reflecting potential heterogeneity of the microbial community during sampling.
Prokaryotic heterotrophic production (PHP) estimation was measured over time course experiments at in situ temperature (13 C) following the protocol described in Tamburini et al. (2002). -leucine-labeled tracer (Kirchman, 1993) was used. For water sample collected with Niskin bottles, we have performed measurements in three replicates of 20 and 40 mL seawater volume for the depth ranging from 0 to 800 m with 20 nM of leucine at final concentration. Concerning depth above 800 m depth, PHP was measured in three replicate of 40 mL of seawater with 10nM at final concentration of Leucine. Samples were incubated 2, 6 and 10 h respectively for samples ranging between 0–200 m, 200–600 m and up to 800 m depth. To calculate prokaryotic heterotrophic production, we used the empirical conversion factor of 1.55 ng C pmol of incorporated leucine according to Simon and Azam (1989), assuming that isotope dilution was negligible under these saturating concentrations.
Figure 2
(a) Particulate biogenic (pM) and particulate Al (nM) profiles next to the biogenic Ba fraction (%) in the upper 1000 m at ANTARES. The grey area represents a biogenic Ba fraction larger than 80 %. BKG: background. profile (pM) at DYFAMED: data from Sternberg et al. (2008). (b) ANTARES ratio plot (green square) of integrated PHP in the upper 100 m over integrated PHP in the upper 500 m versus depth-weighted average (DWA) mesopelagic (pM) over the 100–500 m depth interval. Regression of the same ratio is reported for KEOPS1 (light blue symbols; out plateau stations) and KEOPS2 (dark blue symbols; Southern Ocean, Jacquet et al., 2015) and DY032 (red square; PAP station, NE Atlantic; pers. data) cruises. The blue line represents the trend obtained during KEOPS2 (Jacquet et al., 2015).
[Figure omitted. See PDF]
3 Results and discussion3.1
Particulate vertical distribution
Particulate biogenic , particulate Al (pAl) and biogenic Ba fraction profiles in the upper 1000 m at ANTARES are reported in Fig. 2a. concentrations range from 12 to 719 pM. The biogenic Ba fraction ranges from 51 % to 91 % of the total particulate Ba signal. Particulate Al concentrations (pAl) range from 8 to 170 nM. concentrations are low in surface water ( pM) where the lithogenic fraction reaches 43 % to 49 % in the upper 70 m. From previous studies we know that in surface waters is distributed over different, mainly non-barite biogenic phases and incorporated into or adsorbed onto phytoplankton material. As such these do not reflect POC remineralization processes, in contrast to mesopelagic waters where is mainly composed of barite formed during prokaryotic degradation of organic matter. Focus in the present study is on the mesopelagic layer. The profile at ANTARES indeed displays a mesopelagic maximum between 100 and 500 m, reaching up to 719 pM at 175 m. Ba is mostly biogenic at these depths ( %). concentrations then decrease below 500 m to reach a background value of around 130 pM (see BKG in Fig. 2). Note that the MedSea is largely undersaturated with respect to barite, with saturation state ranging between 0.2 and 0.6 over the basin (Jacquet et al., 2016; Jullion et al., 2017). For comparison, the background value in the Southern Ocean reaches 180 to 200 pM below 1000 m (Dehairs et al., 1997; Jacquet et al., 2015). Previously, Sternberg et al. (2008) reported the seasonal evolution of profiles at the DYFAMED station (4325 N, 752 E; BARMED project) northeast from ANTARES (Fig. 1c) in the NW MedSea. The present profile at ANTARES (March 2016) is very similar to the profile measured in March 2003 at DYFAMED (Fig. 2a). The slight difference between profiles in the upper 75 m suggests more Ba bounded and/or adsorbed onto phytoplankton material during BARMED. Both profiles present a maximum in the upper mesopelagic zone between 150 and 200 m. Below this maximum, concentrations gradually decrease to reach around 130 pM between 500 and 1000 m (this study). A similar value was reached between 500 and 600 m at the DYFAMED station over the whole studied period (between February and June 2003; Sternberg et al., 2008).
3.2 Prokaryotic heterotrophic productionThe particulate Ba in excess is centered in the upper mesopelagic zone between 100 and 500 m and reflects the fact that POC remineralization mainly occurred at this depth layer (Fig. 2a). Depth-weighted average (DWA) content (409 pM), i.e., the inventory divided by the depth layer considered, was calculated between 100 and 500 m. Figure 2b shows the column-integrated PHP at 100 m over that at 500 m (PHP). Our PHP ratio at ANTARES station is 0.90 and is compared to results obtained during KEOPS1 (summer) and KEOPS2 (spring; out plateau stations) cruises in the Southern Ocean (Jacquet et al., 2008a, 2015) and the DY032 cruise (July 2015, R/V Discovery) at the PAP (Porcupine Abyssal Plain) observatory in the northeast Atlantic (49 N, 16.5 W) (personal data). Results at the ANTARES/EMSO-LO site follow the trend previously reported in the Southern Ocean (blue line in Fig. 2b; Jacquet et al., 2015), indicating higher DWA in situations where a significant part of column-integrated PHP is located deeper in the water column (high Int. PHPx1 IntPHPx2 ratio; Fig. 2b). These previous studies revealed that the shape of the column-integrated PHP profile (i.e., the attenuation gradient) is important in setting the signal in the mesopelagic zone (Dehairs et al., 2008; Jacquet et al., 2008a, 2015). Indeed, mesopelagic DWA appears reduced when most of the column-integrated PHP is limited to the upper layer, i.e., indicating an efficient remineralization at the surface. In contrast, mesopelagic DWA appears higher when most of the column-integrated PHP is located in the mesopelagic layer, i.e., reflecting significant deep PHP activity, POC export and subsequent remineralization (Fig. 2b). Results at the PAP site reflect a similar situation as observed during KEOPS2 for time series stations at the plateau site and in a meander of the polar front area (not show in Fig. 2b). At these stations, Jacquet et al. (2015) reported a shift toward the KEOPS1 trend reflecting the temporal evolution (season advancement) and patchiness of the establishment of mesopelagic remineralization processes within the same area. Overall, our MedSea result is located along the trend defined in the Southern Ocean during the KEOPS1 cruise. It is generally considered that (barite) forms inside sulfate and/or barium oversaturated biogenic micro-environments during POC degradation by heterotrophic prokaryotes. However, it is unclear whether barite formation at mesopelagic depths is (directly or indirectly) bacterially induced or bacterially influenced (Martinez-Ruiz et al., 2018, 2019). In any case our results strengthen the close link between the water column distribution and respiration (organic matter degradation).
3.3 Oxygen–barium relationship
The relationship we obtained at ANTARES between concentrations and oxygen consumption rates from optode measurements (-Opt) is reported in Fig. 3a. -Opt ranges from 0.11 to 5.85 mol L d. The relationship indicates higher concentrations with increasing -Opt. An interesting feature is the intercept at zero -Opt (around 128 pM) which further supports the Ba BKG value at ANTARES (130 pM) determined from measured profiles (Fig. 3a).
Figure 3
(a) Relationship between concentrations (pM) and oxygen consumption rates (mol L d) from optode measurements (-Opt) at ANTARES; (b) confrontation of oxygen consumption rates (; mmol m d) obtained from different methods: optode measurements (this study; green square), dark community respiration (DCR) (Winkler titration; red triangles; -DCR; Jacquet et al., 2015; KEOPS1) and Dehairs's transfer function calculation (Dehairs et al., 1997) based on contents. The black line corresponds to the correlation obtained during KEOPS1 (Jacquet et al., 2015); (c) Dehairs's relationship between depth-weighted average (DWA) mesopelagic (pM) and (mol L d) compared to the ANTARES result (this study), KEOPS1 data (Southern Ocean; Jacquet et al., 2015) and GEOVIDE correlation (North Atlantic; Lemaitre et al., 2018).
[Figure omitted. See PDF]
In Fig. 3b we applied a similar approach as reported in Jacquet et al. (2015) where we show the correlation between obtained from dark community respiration DCR (Winkler titration, -DCR) data integration in the water column and based on content (Dehairs's transfer function, later referred to as -Ba). Similarly, to estimate -Ba in the present study, we used the following equation (Dehairs et al., 1997) (Fig. 3c): 1 A Ba BKG value of 130 pM was used (see above). -Ba is compared to -Opt integrated over the same layer depth (between 175 and 450 m; Fig. 3b). rates are of the same order of magnitude (-Ba 4.59 mmol m d and -opt 3.14 mmol m d). The slight difference could be explained by the integration time of both methods: a few hours to days for the incubations vs. a few days to weeks for (seasonal build-up; Jacquet et al., 2007). rates calculated in the present work are 3 times higher than those reported in the Southern Ocean during KEOPS1 (Jacquet et al., 2015), but they are in good agreement with the vs. trend (Fig. 3b). DWA and measured during KEOPS1 (Jacquet et al., 2015) and at the ANTARES site (this study) are compared to Dehairs's relationship in Fig. 3c. The correlation obtained in Lemaitre et al. (2018) in the North Atlantic is also reported ( was calculated from apparent oxygen utilization divided by water mass age). Note that this relationship is not significantly different from the Dehairs equation (Lemaitre et al., 2018). Overall, results at the ANTARES site are in line with the Southern Ocean – correlation. This further supports the validity of the Dehairs transfer function in the present study.
3.4 Estimated particle remineralization rates and implicationsIn order to provide a -derived estimate of POC remineralization rate (MR) at the ANTARES/EMSO-LO observatory during the BATMAN cruise, we converted -Ba into C respired using the Redfield (RR) C molar ratio (; Broecker et al., 1985) multiplied by the depth layer considered (, 175–450 m) (Dehairs et al., 1997):
2 We obtain a POC remineralization rate of 11 mmol C m d (10 % RSD, relative standard deviation). This is within the range of dissolved Ba-derived fluxes of POC remineralization (13 to 29 mmol C m d) reported in the Mediterranean Sea previously (Jacquet et al., 2016; Jullion et al., 2017). Following calculations reported in Jullion et al. (2017), our MR rate would correspond to a flux of around 0.01 mol m d. This is in reasonable agreement with barium fluxes (0.01 to 0.08 mol m d) presented in Jullion et al. (2017). Previously published barium fluxes from sediment traps range from 0.27 to 0.36 mol m d at the DYFAMED station (Sternberg et al., 2007) and from 0.39 to 1.07 mol m d in the Alboran Sea (Sanchez-Vidal et al., 2005). The POC remineralization rate from the present study is in the range of previously published carbon export fluxes (a few to tens of mmol m d) from thorium-derived data (Speicher et al., 2006) or from combining drifting sediment traps and underwater vision profilers (Ramondenc et al., 2016). Constraining POC flux attenuation and remineralization rates in the Mediterranean is far from being achieved, especially regarding seasonal changes and inter-basin variations, but the concordance of the different approaches is promising.
4 ConclusionsThis paper presents the first insight into the connections of , PHP and at the ANTARES/EMSO-LO observatory site in the northwestern Mediterranean Sea during the BATMAN (2016) cruise. Our results reveal a strong relationship between contents and measured rates. Also, DWA vs. column-integrated PHP and measured vs. -based relationships follow trends previously reported in the Southern Ocean where the Dehairs function was first established to estimate POC remineralization rate. Results from the present study would indicate that this function can also be applied in the Mediterranean basin provided that adequate background values are estimated. From a global climate perspective, the tool will help to better balance the MedSea water column C budget. It will contribute to gaining focus on the emerging picture of the C transfer efficiency (strength of the biological pump).
Data availability
All data and metadata will be made available at the French INSU/CNRS LEFE CYBER database (scientific coordinator: Hervé Claustre; data manager, webmaster: Catherine Schmechtig) (INSU/CNRSLEFE CYBER, 2020).
Author contributions
SHMJ and DL designed the experiment for . SHMJ, CT and MG designed the experiments for PHP measurements. SHMJ and FACLM managed barium sampling during the cruise. NB managed CTD deployment at sea. MG, SG and MR managed PHP. All co-authors contributed to writing.
Competing interests
The authors declare that they have no conflict of interest.
Acknowledgements
We thank the officers and crew of R/V L'EUROPE for their assistance during work at sea.
Financial support
This research was supported by the French national LEFE/INSU “REPAP” project (PI is Stéphanie H. M. Jacquet). It was co-funded by the “ROBIN” project (PIs are Christian Tamburini, Frédéric A. C. Le Moigne) of Labex OT-Med (ANR-11-LABEX-0061) funded by the Investissements d'Avenir and the French Government project of the ANR, through the A*Midex project (ANR-11-IDEX-0001-02). The authors have benefited from the support of the SNO-MOOSE and SAM-MIO. BATMAN is a contribution to the “AT – POMPE BIOLOGIQUE” of the Mediterranean Institute of Oceanography (MIO) and to the international IMBER program. The instrument (ELEMENT XR, Thermo Fisher) was provided in 2012 by the European Regional Development Fund (ERDF).
Review statement
This paper was edited by Carolin Löscher and reviewed by two anonymous referees.
You have requested "on-the-fly" machine translation of selected content from our databases. This functionality is provided solely for your convenience and is in no way intended to replace human translation. Show full disclaimer
Neither ProQuest nor its licensors make any representations or warranties with respect to the translations. The translations are automatically generated "AS IS" and "AS AVAILABLE" and are not retained in our systems. PROQUEST AND ITS LICENSORS SPECIFICALLY DISCLAIM ANY AND ALL EXPRESS OR IMPLIED WARRANTIES, INCLUDING WITHOUT LIMITATION, ANY WARRANTIES FOR AVAILABILITY, ACCURACY, TIMELINESS, COMPLETENESS, NON-INFRINGMENT, MERCHANTABILITY OR FITNESS FOR A PARTICULAR PURPOSE. Your use of the translations is subject to all use restrictions contained in your Electronic Products License Agreement and by using the translation functionality you agree to forgo any and all claims against ProQuest or its licensors for your use of the translation functionality and any output derived there from. Hide full disclaimer
© 2021. This work is published under https://creativecommons.org/licenses/by/4.0/ (the “License”). Notwithstanding the ProQuest Terms and Conditions, you may use this content in accordance with the terms of the License.
Abstract
In the ocean, remineralization rate associated with sinking particles is a crucial variable. Since the 1990s, particulate biogenic barium (
You have requested "on-the-fly" machine translation of selected content from our databases. This functionality is provided solely for your convenience and is in no way intended to replace human translation. Show full disclaimer
Neither ProQuest nor its licensors make any representations or warranties with respect to the translations. The translations are automatically generated "AS IS" and "AS AVAILABLE" and are not retained in our systems. PROQUEST AND ITS LICENSORS SPECIFICALLY DISCLAIM ANY AND ALL EXPRESS OR IMPLIED WARRANTIES, INCLUDING WITHOUT LIMITATION, ANY WARRANTIES FOR AVAILABILITY, ACCURACY, TIMELINESS, COMPLETENESS, NON-INFRINGMENT, MERCHANTABILITY OR FITNESS FOR A PARTICULAR PURPOSE. Your use of the translations is subject to all use restrictions contained in your Electronic Products License Agreement and by using the translation functionality you agree to forgo any and all claims against ProQuest or its licensors for your use of the translation functionality and any output derived there from. Hide full disclaimer