the Creative Commons Attribution 4.0 License.
the Creative Commons Attribution 4.0 License.
Marine particles and their remineralization buffer future ocean biogeochemistry response to climate warming
Joeran Maerz
Katharina D. Six
Soeren Ahmerkamp
Tatiana Ilyina
Transport and fate of particulate organic carbon (POC) and nutrients through marine particles co-determine the future response of ocean biogeochemistry and oceanic carbon uptake under climate warming. This makes the parametrization of the biological carbon pump in Earth system models (ESMs) an important model component and motivates us to compare the recently developed, particle composition-dependent sinking scheme (M4AGO; Maerz et al., 2020) to the current CMIP6 default Martin curve-like sinking scheme in MPI-ESM1.2-LR (see Mauritsen et al., 2019) under the future shared socio-economic pathway high-emission scenario SSP5-8.5. In their global response, the two model versions are similar, showing a decrease of integrated net primary production between the historical (1985–2014) and future (2070–2099) period of about 8.1 % and 9.7 % for the CMIP6 and M4AGO version, respectively. However, the models response differs latitudinally. In M4AGO, the temperature-dependent remineralization offsets the future increase in sinking velocity caused by a higher CaCO3 to POC ratio in the low latitudes. There, M4AGO thus buffers the export loss of nutrients to the mesopelagic, visible in little future changes of the export to net primary production ratio (the peg ratio), while the CMIP6 version shows more pronounced changes with regionally declining or increasing peg ratio. In the Arctic Ocean, the projected future increase of net primary production in the CMIP6 version is diminished with M4AGO through its higher POC transfer efficiency in high latitude regions. Hence, the more mechanistic and to environmental changes-responding M4AGO scheme shows a stronger buffering regional response to climate warming than the CMIP6 model version. The higher transfer efficiency leads to enhanced CO2 uptake in high latitude regions while the tropical regions turn later into a net sink with M4AGO compared to the standard CMIP6 version. Next to ballasting, we identified the particle microstructure as vigorous determinant for future changes of POC sinking velocity. Microstructure co-determines particle porosity and particle density. Processes governing the microstructure thus can be regarded as decisive to understand for reducing uncertainty of future POC fluxes.
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In the euphotic zone of the oceans, primary producers and subsequent grazers fuel the particulate organic matter (POM) pool that can sink in form of marine particles. Their settling velocity and remineralization eventually determines, how much particulate organic carbon (POC) escapes the euphotic zone as export production, estimated to range between 4 Pg C yr−1 to 11.2 Pg C yr−1 (Laws et al., 2000; Najjar et al., 2007; Henson et al., 2012), recently constrained to 7.36 ± 2.12 Pg C yr−1 (Yamaguchi et al., 2024), to the mesopelagic zone of the oceans. The subsequent attenuation of POC fluxes in the mesopelagic zone determines the deep oceans fluxes and thereby the storage capacity due to the biological carbon pump (Wilson et al., 2022). This makes the investigation of processes potentially affecting export production and attenuation of POC fluxes crucial for understanding the evolution and the feedback of the biological carbon pump on the Earth system under climate change (Ilyina and Friedlingstein, 2016). Recently, Maerz et al. (2020) provided an advanced parametrization of the biological carbon pump by explicitly representing particle properties in the HAMburg Ocean Carbon Cycle (HAMOCC) model in an ocean standalone setup under climatological atmospheric conditions. With the present work, we present and discuss the effects of this more realistic representation of the biological carbon pump on primary production and biogeochemical fluxes under projected future climate warming in the framework of the Max Planck Institutes Earth system model (MPI-ESM1.2-LR configuration; Mauritsen et al., 2019) of which HAMOCC (Six and Maier-Reimer, 1996; Ilyina et al., 2013; Paulsen et al., 2017) is the ocean biogeochemistry component.
Constraining the export production and fate of marine particles is afflicted with high uncertainties, partially even in the sign of response to projected future climate warming (Laufkötter et al., 2015; Henson et al., 2022). To understand export fluxes and their attenuation in the mesopelagic zone has thus led to joint efforts in studying the twilight zone (Martin et al., 2020; Henson et al., 2022). Among ESMs taking part in the Coupled Model Intercomparison Project (CMIP), the response of export production to climate warming is closely related to the represented ecosystem structure and organic matter routing in the euphotic zone and the linked process of particle formation and remineralization (Laufkötter et al., 2016). Temperature-dependent remineralization contributes to ecosystem shifts with ocean heat uptake and increased stratification under climate warming (Segschneider and Bendtsen, 2013; Crichton et al., 2021). In comparison to models with globally constant remineralization rates, diatoms experience higher silicate limitation and calcifiers are favoured (Segschneider and Bendtsen, 2013). Calcification leads to loss of alkalinity with negative consequences for the oceanic carbon dioxide (CO2) sink (Planchat et al., 2023). Both, opal and CaCO3, can act as ballasting material for POC (Armstrong et al., 2002; Passow, 2004) and can increase the POC transfer efficiency through the mesopelagic zone (Klaas and Archer, 2002; Balch et al., 2010; Cram et al., 2018). In addition to gravitational sinking, active vertical migration of higher organisms with their fecal pellet production are expected to contribute to vertical POC fluxes (Archibald et al., 2019). These active biological fluxes have yet to be considered in CMIP6 models (Henson et al., 2022). Zooplankton vertical migration (Bandara et al., 2021) potentially increases global POC export flux by about 14 % to 20 % (Aumont et al., 2018; Archibald et al., 2019; Pinti et al., 2023) which thus induces potential biases in present CMIP6 ESMs. Physical mechanisms, like the eddy pump (Boyd et al., 2019) and sub-mesoscale to mesoscale eddy-driven particle size-dependent export (Lévy et al., 2012; Dever et al., 2021) additionally affect POC fluxes with partially uncertain response in a future climate. Molecular sea water viscosity decreases with warming oceans in future which can lead to enhanced sinking velocities, while its overall effect on future POC fluxes is with about 3 % on export production likely minor (Taucher et al., 2014; Henson et al., 2022). Attenuation of sinking fluxes ultimately occurs through remineralization of POM whose underlying microbial processes are temperature-dependent (Dell et al., 2011). Since remineralization is energetically favourable under oxic conditions, oxygen deficit zones (ODZs) hamper remineralization and thus attenuation of POC fluxes (Le Moigne et al., 2017; Weber and Bianchi, 2020; Cram et al., 2022). This makes ODZs to regions of high transfer efficiency of exported POC to greater depth (Roullier et al., 2014; Weber et al., 2016; Maerz et al., 2020; Weber and Bianchi, 2020) while being harmful to higher organisms (Heinze et al., 2021). Recently, fragmentation of larger particles has been recognized as potential mechanism that contributes to longer residence time of generated smaller particles in the water column (Briggs et al., 2020), which allows for stronger decline of POC fluxes through ongoing remineralization. Particularly in the wind-driven mixed layer of the ocean, turbulence-induced shear can fragment particles (Takeuchi et al., 2019). In addition, zooplankton can break up particles while swimming (Dilling and Alldredge, 2000) or handling of particles (Mayor et al., 2014, 2020). Aggregation processes of particles, but also their susceptibility to fragmentation, are linked to the particle compounds, the 'primary particles', and the particles internal microstructure, which is affected by the compounds size and stickiness (Meakin, 1988; Song et al., 2023) or the generating process (Jiang and Logan, 1991), for example through zooplankton egestion (Kilps et al., 1994). Eventually, particle size and density, and to certain extent shape, determine the terminal sinking velocity in non-stratified waters (Ahmerkamp et al., 2022).
The representation of the complex processes in a heterogeneous ocean (Azam and Malfatti, 2007) to great detail in ESMs is unrealistic due to both, large process uncertainties and high computational costs. Hence, only climate-relevant processes are represented in an often aggregated or simplified form. However, simplified representations tend to be stiffer and exhibit less model fidelity in their response to climate change induced perturbations, while more comprehensive ones potentially respond more realistically and can thus better capture e.g. local variability and interact with a changing ocean biogeochemistry state in a variable climate.
The generally heterogeneous sources of particles and the transformation and loss processes that they can undergo, make it challenging to study their dynamics in situ and to represent in models. Dedicated model studies contribute to understand the potential implications of marine particles on both, ocean food webs and biogeochemistry (e. g. Jackson, 1990; Kriest and Evans, 2000; Armstrong et al., 2002; Stemmann et al., 2004b, a; Jackson and Burd, 2015; Jokulsdottir and Archer, 2016; Gloege et al., 2017). Uncertain parameters and high computational costs typically hinder to include processes to greater detail in ESMs (Dinauer et al., 2022). In ESMs, simplifications for gravitational particle sinking range from constant sinking velocity (Ilyina et al., 2013), power law assumptions of POC fluxes (Martin curve; Martin et al., 1987; Kriest and Oschlies, 2008; Mauritsen et al., 2019), to more advanced sinking schemes, where POM quality (Aumont et al., 2017), ballasting (Heinemann et al., 2019; Karakuş et al., 2025; Armstrong et al., 2002; Stock et al., 2020, the latter two including mineral protection of POC), or particle size distributions are considered (Kriest and Evans, 1999, 2000; Gehlen et al., 2006; Schwinger et al., 2016). However, the heterogeneity and structural complexity of marine particles and related microbial dynamics become more and more acknowledged to be important for determining POC fluxes (Omand et al., 2020; Nguyen et al., 2022). With the recently developed M4AGO (Microstructure, Multiscale, Mechanistic, Marine Aggregates in the Global Ocean) sinking scheme, Maerz et al. (2020) explicitly represent the heterogeneous composition, microstructure and size spectrum of marine particles in combination with a temperature- and oxygen-dependent remineralization rate. M4AGO thus explicitly disentangles compositional and structural effects on the sinking of marine particles. This comprehensive approach makes it a valuable representation to consider for climate change projections in order to provide insights into potential responses of biogeochemical fluxes.
With the present study, we (i) present and discuss effects of the more comprehensive particle representation via the M4AGO-extended MPI-ESM1.2-LR on net primary production and CO2 fluxes compared to the standard CMIP6 (Coupled Model Intercomparison Project phase 6) model version of MPI-ESM1.2-LR (Paulsen et al., 2017; Mauritsen et al., 2019) and (ii) investigate implications for future particle properties and ocean biogeochemical fluxes.
2.1 Brief model description
For the present study, we extended HAMOCC (Six and Maier-Reimer, 1996; Ilyina et al., 2013; Paulsen et al., 2017; Mauritsen et al., 2019) as part of the MPI-ESM1.2-LR (Mauritsen et al., 2019) with the M4AGO sinking scheme (Maerz et al., 2020). The low resolution (LR) setup of MPI-ESM1.2 refers to a nominal Max-Planck-Institute Ocean and sea ice Model (MPIOM; Marsland et al., 2003; Jungclaus et al., 2013) resolution of 1.5° and 40 uneven vertical layers with finer resolution in the near-surface. The ocean component is coupled to the atmospheric component ECHAM 6.3 and experiences riverine fresh water discharge from land via the hydrological model (Hagemann and Dümenil, 1997; Mauritsen et al., 2019).
For a detailed description of M4AGO, please refer to Maerz et al. (2020) who evaluated the novel sinking scheme and its effects on the global biogeochemistry in a MPIOM standalone setup under climatological atmospheric conditions (Röske, 2005). In brief, M4AGO explicitly represents spatio-temporally variable, heterogeneously composed marine particles that feature a microstructure and power law size spectrum with slope b. The particles are composed of primary particles which exhibit an attributed size, density and stickiness. Primary particle numbers are calculated from the local concentration of particle-forming HAMOCC tracers, namely detritus, opal, CaCO3 and dust. The mean particle stickiness heuristically defines the microstructure of particles, the fractal dimension df. The number of primary particles and their attributed properties in combination with the fractal dimension enables to calculate mean primary-particle density and size, 〈ρp〉 and 〈dp〉, respectively. Fractal dimension, together with the mean primary particle size, defines a variable particle porosity throughout the size spectrum that extends from 〈dp〉 to the maximum diameter dmax which is defined through a critical particle Reynolds number. In summary, M4AGO distinguishes between structure and composition based on sub-particle scale properties which leads to variable particle excess densities and sinking velocities. In the MPI-ESM1.2-LR M4AGO setup, the particle-forming tracers eventually sink with the locally derived mass concentration-weighted mean sinking velocity. A brief summary of model differences between the CMIP6 version and M4AGO is provided in Table 1.
Table 1Brief overview of model differences between the CMIP6 and the M4AGO version. [O2] represents the oxygen concentration, µmol L−1 the half-saturation constant for oxygen limitation of aerobic remineralization and T the local water temperature. Flow diagram of M4AGO sinking scheme schematics taken from Maerz et al. (2020) licensed under https://creativecommons.org/licenses/by/4.0/ (last access: 5 March 2026; CC BY 4.0).
In the MPI-ESM setup with M4AGO, opal dissolution and aerobic, oxygen concentration-dependent detritus remineralization are temperature-dependent, following a Q10 approach with a Q10 factor of 2.6 and 2.1, respectively (literature range for the latter: 1.5 to 2.5 ± 0.2; Mislan et al., 2014; Laufkötter et al., 2017; DeVries and Weber, 2017). In the CMIP6 standard version of HAMOCC, detritus features a sinking velocity that is constant (3.5 m d−1) up to the export depth, zexp (zexp defined as being 100 m in HAMOCC) and linearly increases with depth below, following a globally uniform Martin curve (Martin et al., 1987) representation according to Kriest and Oschlies (2008). In the standard setup, the aerobic remineralization rate is only oxygen concentration-dependent and opal dissolution depends linearly on temperature. For further details of the CMIP6 MPI-ESM1.2-LR standard model, refer to Mauritsen et al. (2019). In both model setups, CaCO3 can dissolve below the dynamically evolving lysocline, while dust is transported inert to chemical reactions after aeolian deposition. In contrast to M4AGO, the CMIP6 version features constant, independent sinking velocity for dust, opal and CaCO3 and thus no spatio-temporal variability in their sinking speeds.
2.2 Experimental model setup, spinup and analysis
For the setup of the CMIP6 standard version of HAMOCC, refer to Mauritsen et al. (2019). CMIP6 MPI-ESM1.2-LR output is publicly available through the ESGF portal (Cinquini et al., 2014).
As initialization for the MPI-ESM1.2-LR M4AGO setup, we adopted the well spun-up biogeochemical state from M4AGO-MPIOM HAMOCC (in total, about 1700 years of simulation time with climatological forcing, Maerz et al., 2020) and adjusted the inventories for phosphate, nitrate, dissolved inorganic carbon (DIC) and total alkalinity, AT, according to the CMIP6 MPI-ESM1.2-LR standard model. We kept the silicate inventory untouched, since (i) the CMIP6 run exhibits a too high silicate inventory, and (ii) in contrast to the CMIP6 standard version, opal production affects detritus sinking velocity in M4AGO. We combined the adjusted HAMOCC restart outputs with the physical spun-up state of the MPI-ESM1.2-LR standard pre-industrial control (piCtrl) run. To allow for an adjustment of the biogeochemical tracer distribution to the MPI-ESM1.2-LR piCtrl ocean circulation, we spun up the model for about 700 years under pre-industrial climatological atmospheric CO2 concentration (284.3 ppm), nitrogen deposition (Hegglin et al., 2016) and climatological dust deposition (Mahowald et al., 2005). During the spin-up time, we adjusted the weathering rates to account for loss of POC, CaCO3 and silicate due to sediment burial. The final weathering rates were then kept constant (here provided for non-leap years with 365 d: 107.2 Gmol P yr−1 dissolved phosphorus, 4.54 Tmol Si yr−1 dissolved silicon, and 30.3 Tmol C yr−1 as DIC and the corresponding amount to surface alkalinity as DIC:2 AT) during the subsequent piCtrl run under the same pre-industrial CO2 forcing, in which negligible drifts in surface variables were visible (year mean CO2 oceanic uptake: 0.029 Tg C yr−1, trend for uptake: 0.009 Tg C yr−1 century−1. No further parameter adjustments were carried out. Starting from the piCtrl state and keeping the weathering rates constant, we ran the MPI-ESM1.2-LR M4AGO setup with the CMIP6 historical forcings for the years 1850 to 2014, followed by the high-emission shared socio-economic pathway (SSP) scenario SSP5-8.5 (Riahi et al., 2017) for the time period 2015 to 2099 to showcase responses under an extreme scenario, while acknowledging that it likely overestimates future CO2 emissions (Hausfather and Peters, 2020). For climatological means, we refer to the 30-year time period 1985 to 2014 as historical and 2070 to 2099 as future period, if not otherwise stated. In the concentration-driven scenario, there is no feedback from ocean biogeochemistry on the atmosphere, ocean and sea ice dynamics and land biogeochemistry. Therefore, the physical ocean in the M4AGO version exhibits the same climatological internal variability as the CMIP6 version. The physical fields of the M4AGO simulation could thus be regarded as an additional realisation to the 10 existing MPI-ESM1.2-LR CMIP6 ensemble members available on the ESGF repository. Hence, where applicable, we compare the results with the M4AGO scheme with a run of MPI-ESM1.2-LR carried out for the Coupled Model Intercomparison Project phase 6.
The results and discussion section is divided into two main parts. In Sect. 3.1 to 3.3, we provide and discuss the large scale pattern of biogeochemical variables and indicators and compare the MPI-ESM1.2-LR CMIP6 (hereafter: CMIP6) to the MPI-ESM1.2-LR M4AGO (hereafter: M4AGO) model version. A general evaluation of the two simulations is provided in Appendix A. For a detailed analysis of the ocean dynamics in MPI-ESM refer to Jungclaus et al. (2013). In Sect. 3.4 to 3.5, we investigate and discuss the consequences of changing export fluxes in M4AGO on marine particle dynamics, flux attenuation and consequently on the biological carbon pump. Each subsection is subdivided into a results-oriented and discussion part. This section is completed with a general discussion (Sect. 3.6).
3.1 Primary and export production
Large scale circulation pattern and vertical mixing determine the availability of nutrients in the euphotic zone of the oceans and thus co-determine, together with light availability, primary production. Ongoing ocean warming tends to increase stratification and to decrease vertical mixing, thus mixed layer depths, which impinges on nutrient availability in the euphotic zone and thus net primary production. By contrast, ongoing summer sea ice loss, particularly in the Arctic Ocean, increases light availability for primary producers.
Figure 1Depth-integrated net primary production (NPP). Zonally integrated and maps for the historical period and anomalies in the future period. (a) Zonally integrated NPP in the historical and the future period for the CMIP 6 and M4AGO run. (b) Absolute changes of the zonally integrated NPP for the CMIP 6 and M4AGO run between the future and historical period. (c) Percentage changes for the zonally integrated NPP between the future and historical period. The regional absolute and percentage values refer to the latitudinal regions indicated by the grey lines. (d, e) Vertically integrated NPP in the historical period for the CMIP6 and M4AGO model version. (f, g) Changes of climatological mean NPP in future projections relative to the historical period.
For the historical period, the global depth-integrated net primary production (NPP) in the M4AGO run is with 55.0 Gt C yr−1 about 7.9 Gt C yr−1 higher than the CMIP 6 run (47.1 Gt C yr−1). Particularly in the low latitudes, M4AGO exhibits higher NPP than the CMIP 6 run (Fig. 1). Until the end of the century, the simulations show a global decline in NPP of ≈ 9.7 % and 8 % in M4AGO and CMIP6, respectively. The zonal response, however, differs and M4AGO shows with −15.8 % a 2.4 % larger decline of NPP in the low latitudes (30° S to 30° N) compared to the CMIP 6 run (−13.4 %). In the southern mid-latitudes (66° S to 30° S) M4AGO shows a lower decline in NPP, while a stronger decline of NPP in the northern mid-latitudes (30 to 66° N; −8.1 % versus −6.3 % in the CMIP 6 run). In the northern latitudes (> 66° N), NPP is generally low due to the ice cover at present day, and general seasonality. With continuing warming of the Artic Ocean, NPP increases by 20.3 % in the M4AGO run and with 26.9 % even more in the CMIP 6 run in the future period.
The loss of biologically bound CO2 through gravitational POC fluxes, FPOC(z), at the export depth z=zexp is considered as export production. We here use the commonly applied standard of zexp=100 m as export depth. In the historical period, global FPOC(zexp) differs between the two models and the CMIP6 version features with ≈ 5.89 Gt C yr−1 a higher export production than M4AGO with 5.36 Gt C yr−1. Under the SSP5-8.5 scenario, global export productions decrease by ≈ 11.8 % and ≈ 12.6 % to ≈ 5.2 Gt C yr−1 and ≈ 4.68 Gt C yr−1 for CMIP6 and M4AGO, respectively. The general pattern of the fluxes is qualitatively consistent between the two model versions and follow the primary production (cmp. Fig. 2 with Fig. 1; see also Appendix C for POC and biogenic mineral fluxes in M4AGO). NPP and associated biotic mineral production as well as dust and their ratios determine the particle properties and export fluxes in M4AGO. In Sect. 3.5, we thus discuss future changes in export fluxes and associated particle properties in M4AGO.
Figure 2(a, c) Climatological POC export fluxes for the historical period (1985–2014) and (b, d) their difference between the future projection (2070–2099) and the historical period for CMIP6 and M4AGO.
POC export fluxes are often set in relation to depth-integrated NPP, the so-called export efficiency (pe ratio; Dunne et al., 2005; Brix et al., 2006). We define it here based on gravitational POC fluxes at export depth (note its equivalence to the e-ratio in Laufkötter et al., 2016)
It provides the fraction of NPP-bound CO2 and associated nutrients lost due to gravitational sinking from the euphotic zone at export depth.
Figure 3(a, c) Climatological export efficiency (peg ratio) for the historical period (1985–2014) and (b, d) its difference between the future projection (2070–2099) and the historical period for CMIP6 and M4AGO.
Noticeable, the CMIP6 model version features a strong latitudinal pattern of peg, with values up to about 0.3 in the subtropical gyres regions (maximum ≈ 0.34) and lower values in extra-tropical regions (Fig. 3) ranging globally around 0.13 ± 0.04. By contrast, M4AGO shows a less pronounced and more balanced latitudinal picture and the peg ratio ranges typically around 0.10 ± 0.01. Particularly in the tropical and subtropical regions, the peg ratio response to future climate warming differs and the model versions even show opposite signs in their anomalies (Fig. 3). The CMIP6 model version shows positive future peg ratio anomalies in the eastern equatorial and subtropical regions, while in the M4AGO version, the peg ratio declines in that region. In the high latitudes, the two model versions agree in the sign and peg ratios tend to increase in both model versions. Overall, the response in M4AGO seem to be more buffered to future changes and peg ratios experience lower changes than the CMIP6 model.
Both, the absolute differences in NPP, export fluxes and peg ratio, but also the response to projected future warming of the two model versions are related to their process representation. In contrast to CMIP6, M4AGO features a temperature-dependent remineralization and a dynamically evolving, primarily latitudinally variable sinking velocity of marine particles. Globally, the two model versions show similar NPP response to the future projection. At the latitudinal and regional scale, however, their different process representations imprint on the response to future warming. Generally, temperature is expected to be a major driver of ecosystem dynamics through its effect on enzymatic kinetics and thus growth, respiration and remineralization processes (Dell et al., 2011). M4AGO represents the temperature-dependent detritus remineralization with subsequent consequences for particle properties and thus sinking velocity (see Sect. 3.5). The higher remineralization particularly in the tropical and subtropical regions featured by M4AGO (see Fig. D1c, d) cause the higher NPP and the lower peg ratio compared to CMIP6 and being globally close to recent estimates of 53±7 Gt C yr−1 (Johnson and Bif, 2021). Rising water temperatures with ongoing future warming tend to strengthen stratification and the concurrent weaker mixing recovers less of the exported nutrients (see Appendix B and Fig. B1). As a consequence, higher peg ratios can be expected to result in higher loss of nutrients and thus lower NPP with increasing stratification. This is particularly the case in the tropical and subtropical regions for the CMIP6 model. By contrast, even though M4AGO shows increasing sinking velocities (see Sect. 3.5), the increasing remineralization in M4AGO buffers the effect of increasing stratification. This is visible in the peg ratios decline in future in these regions. Despite this, we see a stronger decline in nitrate concentration in the Panama basin in the course of the future projection, likely caused by increased oxygen deficit zones (ODZs) in M4AGO (see also next Sect. 3.2) which can cause the stronger NPP decline. As a result, this leads to slightly stronger relative reduction of NPP (15.8 %) in tropical and subtropical regions compared to CMIP6 (13.4 %; Fig. 1), while the buffering through lower peg ratios and their changes is similar to findings of Segschneider and Bendtsen (2013) for temperature-dependent remineralization. While the two model versions substantially differ in their latitudinal peg ratio pattern, neither of them features the high peg ratios in high latitudes as suggested by observation-based estimates while large uncertainties still persist (see DeVries and Weber, 2017). The lower peg ratios in the high latitudes potentially affect CO2 fluxes and sequestration in both, the historical and future period. In the Arctic Ocean, the prominent future increase in both, NPP and peg ratios in both simulations can be explained by complete sea ice loss in summer month and concurrent higher light availability for primary producers. Nonetheless, difference of relative latitudinal response is most noticeable for the Arctic Ocean. While both models agree in their sign, M4AGO only suggests a 20.3 % NPP increase compared to 26.9 % in CMIP6 while the peg ratios are similar or even higher in CMIP6. In addition to changes in peg, the deep sequestration of nutrients below the winter mixed layer depth (MLD) contributes to the response. M4AGO exhibits a higher POC transfer efficiency in high latitudes (Maerz et al., 2020, see also next section) and hence associated nutrients are sequestered deeper. In comparison to the Southern Ocean, vertical mixing is weaker in the Arctic Ocean and sequestered nutrients are less effectively mixed back or transported into the euphotic zone. Despite future weakening of Arctic Ocean stratification during summer months (see Fig. B2), this can contribute to a weaker increase of NPP in M4AGO (see also Sect. 3.4 and Fig. D1).
In summary, the global response of both model versions to future climate warming are comparable to other ESMs that show changes of NPP of about −15 % to 30 % under high emission Representative Concentration Pathway scenario RCP8.5 (Laufkötter et al., 2015) and of export fluxes by about −41 % to 1.8 % for the SSP5-8.5 scenario (Henson et al., 2022).
3.2 Future transfer efficiency changes associated to oxygen deficit zones and Arctic warming
Export production can be transferred to greater depth, where longer storage of nutrients, POC and ultimately CO2 can take place. Deep storage potential is often expressed as mesopelagic transfer efficiency that provides an aggregated measure on which exported fraction reaches greater depth, typically z=1000 m,
here calculated for the model grid-defined 960 m depth instead of the 1000 m horizon (Fig. 4).
Figure 4M4AGO transfer efficiency of POC. (a) Mesopelagic transfer efficiency in the historical period. (b) Change of the transfer efficiency in future with respect to the historical period. (c) Regional mean and standard deviation comparison to present day calculation of Weber et al. (2016). CMIP6 run for comparison. (d) Interannual standard deviation of the transfer efficiency during the historical period and (e) changes of the interannual standard deviation of the transfer efficiency in the future period with respect to the historical time period. Note that the pattern of the CMIP6 model version is comparable to the ocean-only setup in Maerz et al. (2020). Ocean regions like shelf seas with water depths represented smaller than 1000 m are neglected and are displayed in white.
In the historical period, the transfer efficiency in M4AGO exhibits a latitudinal pattern with higher values in the high latitudes compared to subtropical gyre regions (Fig. 4a). High transfer efficiencies are also found in upwelling areas of low and mid latitude regions, where oxygen deficit zones prevail in the mesopelagic. Under oxygen limitation, POC remineralization rates are substantially lower than in oxygenated waters which increases transfer efficiency in ODZs.
In the future period (2070–2099), the largest effects on transfer efficiency are associated to regional changes of vertical ODZs extension (cmp. Fig. 4b with Fig. 5). Ocean warming generally decreases oxygen solubility and thus leads to reduced oxygen concentrations in the future (Schmidtko et al., 2017) which contributes to ODZs developments. The ODZs further respond to changes in NPP and export fluxes. As a consequence, the future decline of NPP leads to decreasing ODZs in upwelling regions. This is well visible along the south and north American Pacific coast, in the African Atlantic upwelling areas and the northern Indian Ocean where decreasing ODZs reduce the transfer efficiency. Note the small changes in the central Panama Basin can be attributed to persistent extended ODZs thoughout both periods. West of the Panama basin, however, vertical ODZ fraction expands in the mesopelagic (Fig. 5) which increases transfer efficiency. This behavior is likely associated to future shallower MLD and increasing stratification in these areas (see Fig. B1) which decrease oxygen ventilation. By contrast, the westward extension of ODZs decreases in future, likely due to decreasing equatorial export fluxes (see Fig. C1 g). In the high latitudes, the Arctic Ocean shows a decreasing transfer efficiency in future. The increasing NPP (Fig. 1) shifts the particle composition towards a higher detritus fraction. The additional detritus compared to ballasting minerals increases the buoyancy of marine particles on average and thus decreases settling velocity. In combination with temperature-enhanced remineralization due to Arctic Ocean amplification (Shu et al., 2022), this decreases future transfer efficiency in the Arctic Ocean in M4AGO (see Sect. 3.5 for further details).
Figure 5Change of vertical extent of the mesopelagic ODZ water column fraction in the M4AGO simulation. Positive values imply greater and negative values smaller vertical extent of ODZs in the future than in the historical period. Units are in vertical meter extend of waters with O2 < 20 µmol L−1 per vertical extend of the mesopelagic zone.
Maerz et al. (2020) showed that transfer efficiency varies on seasonal time scales, particularly in high latitudes. We find that it also varies interannually due to changes in (i) export ratios, (ii) positions of circulation pattern and associated frontal regions, and (iii) internal variability of e.g. temperature and mixing with effects on remineralization and ventilation of ODZs. The variability of transfer efficiency potentially affects the biologically induced CO2 drawdown and hence variability of CO2 fluxes. The largest interannual standard deviation of transfer efficiency is associated to the most dynamical ocean regions, i.e. the Southern Ocean and particularly in the Weddell and Ross Sea (Fig. 4c). Noticeably, ODZs also feature an increased interannual standard deviation of transfer efficiency compared to well-ventilated open ocean regions. In future, the interannual standard deviation tends to decrease in the Southern Ocean and in some of the upwelling regions, where ODZs expansion declines in the mesopelagic.
Simulated future changes in transfer efficiency as such cannot directly be related to changes of biologically induced CO2 fluxes, since transfer efficiency only expresses a ratio and not absolute amount of fluxes and thus of deep CO2 drawdown. Nevertheless, strong future changes of transfer efficiency are associated to changing NPP and export ratios (as in the Arctic). Further, any future change of extensions and thickness of ODZs affects the transfer efficiency. We therefore briefly provide insights into the ODZs evolution over the full historical and future simulation. As summarized in Maerz et al. (2020), M4AGO features positive feedbacks on ODZs development. Namely, the lower remineralization and thus higher detritus accumulation in ODZs lead to decreased sinking velocities, since the detritus to ballast ratio increases. This contributes to the overestimation of ODZs, which generally can be attributed to sluggish circulation and too little mixing particularly in equatorial regions (Aumont et al., 1999; Dietze and Loeptien, 2013; Kuntz and Schrag, 2020; Duteil et al., 2021). We therefore follow the strategy of Bindoff et al. (2019) and compare the relative changes of ODZ volume over time to enable comparison of the response of ODZs to changing environmental conditions under ongoing climate warming. We compare the changes of global ODZs volume with O2 below 20 µmol L−1 (“suboxic”), where significant reduction of remineralization rates are simulated in the model with the discussed consequences on transfer efficiency, and a threshold of 80 µmol L−1 (“hypoxic”). The latter encompasses the former and is relevant for higher organisms that are already affected by oxygen levels lower than 80 µmol L−1 (Heinze et al., 2021, and references therein).
Figure 6Relative change of ODZ volumes in CMIP6 and M4AGO. For both simulations and each examined depth horizon, the drift of the piCtrl simulation (calculated relative to the mean of time period 1850–1900) was subtracted and the result normalized to the mean volume in the period 1850–1900. Note that the pre-industrial control simulation in M4AGO showed an increase of global ODZ size due to increasing deep ocean ODZs evolution, while CMIP6 showed a decline. The mesopelagic refers to 100–1000 m and deep ocean region to ocean depths larger 1000 m. Note the different y-axis.
The relative suboxic ODZ volume shows a decline in the future scenario, particularly in the mesopelagic ocean (Fig. 6a). The global as well as the deep ocean ODZs respond similar in both simulations, showing a decline of about 2 %, while in the mesopelagic, the M4AGO simulation shows a stronger decline and features a relatively smaller suboxic ODZ volume by the end of the future scenario (about 16 % loss compared to 13 % in CMIP6). In absolute terms, however, M4AGOs ODZ is still larger than in the CMIP6 simulation. The slightly stronger decline in M4AGO could be associated to the different peg ratio. Lower peg ratio, a stronger declining NPP in subtropical and tropical regions can lead to lower sustaining of ODZs volumes in the mesopelagic. The response of the relative global hypoxic volume for the mesopelagic is less pronounced and exhibit only a slight (CMIP6) or even no (M4AGO) decline (Fig. 6b). In contrast to the evolution of suboxic ODZ, the relative hypoxic volume increases by about 1.5 % and 2 % to 4 % globally and in the deep ocean, respectively. In summary, the global trends with contracting suboxic ODZs and little declining to expanding hypoxic ODZs are in line with other ESMs of the CMIP6 cohort which show similar trends for the Pacific Ocean (Busecke et al., 2022). Ensemble simulations with M4AGO could shed light on the significance of the different mesopelagic suboxic ODZs trend compared to the CMIP6 simulation and provide insights, in how far not only the peg ratio, but also the internal dynamics and feedbacks between sinking and remineralization drive the ODZs evolution.
3.3 Historical and future evolution of CO2 fluxes
To date, oceanic yearly mean CO2 fluxes are afflicted with high uncertainties and generally, ESMs are challenged to represent these fluxes well (Gruber et al., 2023). On average, CO2 fluxes are largely driven by the global circulation field and related physical transport and mixing of carbon, mainly in the form of DIC, across the mixed layer interface (Levy et al., 2013). In most ocean regions, the gravitational POC flux across the mixed layer interface is small compared to absolute values of these physics-driven DIC fluxes (Levy et al., 2013). However, the physical solubility pump accounts for only about 17 % to 40 % to the present day observed global vertical DIC gradient, while the biological pump with contributions from the carbonate and soft-tissue pump account for about 21 % and 62 %, respectively (Bacastow and Maier-Reimer, 1990; DeVries, 2022). The changed transfer efficiency pattern between the CMIP6 and the M4AGO model have an effect on the vertical DIC gradients and seasonal dynamics of nutrient availability for primary production, both imprinting on CO2 fluxes. Thus, we here compare the two simulations to the mean of the harmonized CO2 flux products by Fay et al. (2021) based on three wind (Atlas et al., 2011; Hersbach et al., 2020; Kobayashi et al., 2015) and six different surface ocean pCO2 products (Chau et al., 2020; Denvil-Sommer et al., 2019; Gregor et al., 2019; Rödenbeck et al., 2013; Iida et al., 2020; Landschützer et al., 2014, 2020; Zeng et al., 2014) for the time period January 1990 to end of 2019. Both, local, point-wise means of the observational products and simulations feature an internal variability whose phases not necessarily align over the 30 year time period. We thus calculate the 30 year trend based on monthly mean values to reduce the effect of seasonal to decadal scale internal variability on the analysis. We perform a trend comparison and significance testing. For testing (i) the significance of trends and (ii) the significance of trend differences, we follow Santer et al. (2000) and apply their methods in combination with the adjusted standard error and the adjusted degrees of freedom.
Figure 7Trends in CO2 fluxes for (a) the CMIP6 and (b) the M4AGO simulation. Yellow hatching indicates significant trends or trend difference. (c) Comparing the trend difference between M4AGO and CMIP6 to the standard deviation across of trends across the difference CO2 products. Hatching indicates significant trend differences between M4AGO and CMIP6. (d) Trend of the mean of CO2 products. (e, f) trend difference between CMIP6 or M4AGO and mean observational product trend.
Both simulations show a negative trend of CO2 fluxes in southern high latitudes (Fig. 7a, b). In mid and low latitudes, the picture is less clear. The CMIP6 simulation indicates a slightly increasing outgassing over the 30 year period and decrease in the eastern equatorial region, while in M4AGO, the CO2 fluxes remain neutral or even indicate a negative trend, yet outgassing (see below). However, only few areas show the significance of those trends, for example the eastern equatorial Pacific in the CMIP6 simulation and boundaries of the high productive equatorial Pacific region in M4AGO. The trends of the mean CO2 product show a clear latitudinal pattern with negative trends in the North Pacific and North Atlantic, negative trends in the Southern Ocean polar frontal region and positive trends in the mid and low latitudes (Fig. 7d). A larger area fraction of those areas show significance in these trends than the simulations. Comparing the simulation trend differences to the standard deviation of trends across the different CO2 products, most of the differences are within the standard deviation (i.e. within the range {−1, 1} of the ratio) indicating the simulations rather being compliant with observed trends, while some regions like the North Atlantic and Kuroshio region show significant trend differences between the simulations (Fig. 7c). When comparing the trend differences between the simulations and the observational product, particularly the coastal regions shine up as being significantly different in their trends as well as parts of the Arctic Ocean, and areas of the mid and North Atlantic and some areas in the eastern Pacific (Fig. 7e, f). The coastal region trend differences are likely caused by the coarse resolution of the models, as coastal and shelf regions are spatially underrepresented, but also in terms of process representation. Overall and with slightly less spatial extend of trends with significant difference, M4AGO seems to slightly improve the trend representation. Nevertheless, for most areas, trends in observations are not discernible from trends in the simulations. In summary, the trend comparison highlights the fact that yet the model simulations still show significant differences in CO2 fluxes and their trends for the time period 1990 to 2019 and representing CO2 fluxes remains challenging.
Figure 8Time-evolution of sea-air CO2 flux anomaly (positive into air; base are the global means of the piCtrl simulations for the entire period). (a, b) Zonally integrated monthly CO2 flux anomalies. Green and magenta lines indicate the annual zero mean flux isoline for the CMIP6 and the M4AGO simulation, respectively, when the ocean switches from net source/sink to sink/source. In (b) CMIP6 green line is drawn for comparison. (c) 10-year moving standard deviation of monthly zonally integrated CO2 fluxes as indicator for the seasonal amplitude for CMIP6 and (d) the difference (M4AGO – CMIP6). (e) Time-cumulative of zonally integrated CO2 fluxes for CMIP6 and (f) the difference between M4AGO and CMIP6. (g) latitudinal cumulative zonal sum of the difference shown in (f) for the time snap shot 12/2099. The ≈ 2221 Mt C indicates an about 2.2 Gt C lower oceanic uptake by M4AGO over the full time period. Negative values at the zero latitude indicate a reduced oceanic north-south CO2 transport in M4AGO compared to CMIP6.
Despite the dominating factor of circulation on CO2 fluxes, the changed pattern of transfer efficiency in M4AGO compared to CMIP6 can affect the regional CO2 fluxes and their evolution in future. We thus investigate the seasonal changes of zonally integrated CO2 fluxes from 1850 through 2100 with a focus on seasonal variability and changed cumulative uptake. To reduce the imprint of sub-decadal internal variability of the circulation on our results, we compare the 10-years moving standard deviation based on monthly mean values, defining the seasonal amplitude, between the two simulations and analyze the time-cumulative of zonally integrated CO2 fluxes (Fig. 8).
The seasonal variability of CO2 fluxes is particularly increasing in the high latitudes (Fig. 8a–d) due to changes in the marine carbon chemistry (increasing Revelle factor; Landschützer et al., 2018). Throughout the entire simulated historical and future time period, the seasonal amplitude in the M4AGO simulation is increased in the northern latitudes, particularly around the 50° N latitudinal band, associated with the North Atlantic and parts of the North Pacific. By contrast, most of the latitudes south of 50° S M4AGO shows smaller seasonal amplitudes until mid of the last century. Parts of the Southern Ocean (SO; around 60° S) features higher and the northern SO smaller seasonal amplitudes by the end of this century. North of the SO boundary, the seasonal amplitude in CO2 fluxes is increased in M4AGO and increases further in future. The SO thus undergoes a more rapid change in seasonal amplitudes of CO2 fluxes than in the CMIP6 model version. By contrast, in the equatorial regions, the seasonal amplitude was enhanced in the historical period while tends to decrease compared to the CMIP6 simulation in future. When comparing the time-cumulative zonally integrated CO2 fluxes (see Fig. 8e, f), the M4AGO simulation features an increased downward flux component in the SO and northern latitude region, while featuring a stronger upward component in equatorial regions. This makes the 50° S band becoming a net sink for CO2 in the M4AGO simulation earlier and the equatorial region later than the CMIP6 model version (Fig. 8a, b), which is in line with a deeper sequestration of biologically bound CO2 in the high latitudes and shallower in the equatorial regions due to the changed transfer efficiency pattern. By end of this century, the M4AGO simulation has taken up about 2.2 Gt C less anthropogenic CO2 than the CMIP6 model version, which is a small, but non-negligible lower contribution to carbon sequestration by the biological carbon pump through the changed transfer efficiency pattern. 2.2 Gt C correspond to about 0.5 % of the total oceanic CO2 uptake until the end of the century or equivalently to about one year of present day oceanic CO2 uptake. However, the simulation still falls into the range of the MPI-ESM grand ensemble (MPI-GA; Maher et al., 2019) that resolves internal variability to great extend. The more pronounced CO2 uptake particularly in the SO in M4AGO is likely offset by the stronger decline in net primary production in low latitudes and thus lower CO2 uptake. Changes in CO2 uptake over the coming decades to century are dominated by physical solubility and ocean circulation changes (DeVries, 2022; Visser, 2025). For example, this has been shown for the North Atlantic where the uptake is strongly determined by the Atlantic Meridional Overturning Circulation strength (Goris et al., 2023). In turn, difference in transfer efficiency pattern on high latitude CO2 uptake has thus far not been rigorously analyzed. However, a generally small effect of the transfer efficiency pattern on transient CO2 uptake is expected since strong changes in ocean biogeochemistry would be required to affect the solubility pump-dominated ocean transient response in carbon sequestration (see also comment of Broecker, 1991). Hence, ensemble simulations with M4AGO in comparison to the MPI-GA could provide a more detailed answer, to what extend a changed transfer efficiency pattern affects the transient response of the biological contribution to CO2 uptake under climate change.
3.4 Evolution of remineralization length scales
In a warming climate, the ocean takes up heat leading to rising sea water temperature. From the present day to the future period, particularly the northern and partially also the southern high latitudes experience a strong warming by regionally more than 100 % (Fig. 9a).
Figure 9Historical period zonal mean values, absolute and percentage change of the zonal mean value in the future period for (a) temperature, (b) remineralization length scales (RLS) for detritus and (c) RLS for opal in M4AGO. Note that the RLS are not weighted by fluxes and thus do not necessarily translate into zonal changes of vertical fluxes of the shown components. For the spatial distribution of RLS of POC at export depth, see also Fig. D1.
In the low latitudes, the near-surface waters and the upper mesopelagic also experience rising temperatures of about 1.5 to 2.0 °C. In the M4AGO run, these rising temperatures decrease the molecular viscosity of sea water, leading to regional reductions of up to about −10 %, which increases settling velocities of particles. A major impact of the rising temperature is on the remineralization rate, which can strongly affect the remineralization length scales of detritus and opal (Fig. 9, for a spatial map at export depth, see Fig. D1). The remineralization length scale (RLS; the e-folding depth) for the individual particle component is defined by
where we stick to the terminology of RLS irrespective of the processes of remineralization (in the case of detritus) or dissolution (in the case of opal). RLS combine the effect of 〈ws〉 and remineralization (or dissolution) and ultimately aggregate effects into a length scale that determines flux attenuation. Note that in the CMIP6 simulation, the RLS for detritus is fixed and linearly increases with depth below zexp except for ODZs.
Generally, the RLS for opal are much larger than for detritus. In M4AGO, the faster remineralization of detritus through rising temperature leads to a loss of particles buoyancy and thus to relatively larger RLS of opal, while the increased dissolution of opal can cause less ballasting and even smaller RLS for detritus. The relative changes of dissolution and remineralization of opal and detritus, respectively, due to temperature, determined via the different Q10 factors, also contribute to these linked effect on RLS. In the subtropical gyres, where coccolithophores produce ballasting CaCO3, the loss of buoyancy through increasing temperature-driven, faster detritus remineralization and repacking can lead to longer RLS. This is particularly true up to the depth of the lysocline, until which CaCO3 experiences little dissolution in HAMOCC. Thus, in M4AGO, the relative contribution of the individual particle components locally co-determine the individual RLS and thus their changes with climate warming while they are closely linked to structural changes in the phytoplankton and zooplankton community.
The linkages between the individual particle components and export processes lead to a complex response of the RLS (Fig. 9b, c). In the low latitudes, RLS experience an increase, primarily driven through temperature-driven, faster remineralization of detritus in the euphotic zone partially accompanied by an enhanced CaCO3 to opal export ratio. In the subtropical gyre region, the RLS decrease. In the equatorial region and deep ocean the effect of ODZs on the RLS of POC is well visible. The decreasing remineralization under oxygen limitation increases the RLS leading to the higher transfer efficiency in ODZ regions (see Sect. 3.2). The decline of the POC RLS between 20 to 40° N at 1000 to 2000 m in the equatorial and northern subtropical region are thus likely linked to changing geometries of and declining deep ODZs. In the northern high latitudes, the Arctic Ocean, NPP increases through sea ice loss and produced detritus adds particle buoyancy leading to strongly declining RLS (Fig. 9). Changes of RLS in the mesopelagic region can affect resupply and sustaining of nutrients in the euphotic zone in combination with vertical mixing and short term and seasonal excursions of the mixed layer depth (Leung et al., 2021). Overall, the Arctic Ocean presents a hotspot, where RLS and thus transfer efficiency substantially decrease. This contributes to the increased NPP (see Sect. 3.1 and 3.2) and thus poses a positive feedback loop to NPP that is currently not represented in the CMIP6 model version.
3.5 Future particle property changes and research implications
Primary production and associated biotic minerals as well as aeolian dust input determine the particle composition and export fluxes (for export fluxes, see Appendix C and Fig. C1). Future changes in particle composition can thus affect particle properties, sinking velocity and eventually the RLS and transfer efficiency.
Figure 10Percentage changes of particle properties, remineralization length scales, dynamic molecular viscosity and particulate fluxes in the Arctic Ocean and equatorial tropical Pacific. Note that the individual radial axes can hold different percentage changes. Further note that particularly for the Arctic Ocean fluxes were small in Northern hemisphere winter, early spring and autumn month, thus high percentage changes still reflect small absolute particulate fluxes. For other major ocean regions refer to Figs. E1 and E2.
M4AGO simulates marine particles of organic origin less compact and dense than strongly mineral-dominated particles. Modeled detritus-dominated particles are composed of small, lightweight primary particles of mean diameter 〈dp〉 and mean density 〈ρp〉, and have low sinking velocities and thus reach the critical particle Reynolds number for fragmentation at larger maximum particle diameter dmax than mineral-dominated particles. In calcifiers-dominated regions, the small, but dense coccoliths lead to fast sinking, compact, relatively small particles after remineralization of the buoyancy-adding detritus. In diatom-dominated areas, freshly decaying diatoms (i.e. detritus to opal ratio close to that of living diatoms), feature an increased stickiness, thus low fractal dimension df, high buoyancy and a slowly decaying particle number size distribution with slope b, mimicking the influence of transparent exopolymer particles with their sticky, buoyant nature on particle formation and sinking (Alldredge et al., 1993; Passow, 2002; Azetsu-Scott and Passow, 2004). Primary particle size is large due to the opal frustule represented as a hollow sphere. With increasing remineralization, the buoyancy gets reduced and compaction of particles increases (df increases), leading to an increase of mean sinking velocity, while dmax decreases.
In the future, NPP and associated mineral production responds to changing environmental conditions as well as light and nutrient availability. In the Arctic Ocean, where a transition from frequently ice-covered or at least ice-influenced to seasonally ice-free happens in future, increased NPP and detritus production (see Sect. 3.1) accordingly leads to, on average, looser, less compact, larger particles. This is accompanied by increased export fluxes and a decreased molecular dynamic viscosity, μ. Overall, sinking velocity is decreased in the future Arctic Ocean and temperature-increased remineralization additionally reduce the RLS at export depth (Fig. 10), leading to the lower future transfer efficiency compared to M4AGO in the historical period (see Sect. 3.2, Fig. 4).
By contrast, for example in the equatorial tropical Pacific, the increasing temperature leads to stronger remineralization, while increasing stratification favors ballasting CaCO3 compared to opal production. This shifts the detritus to ballasting ratio towards the ballasting CaCO3, resulting in higher df, denser primary particles, stronger decaying particle number spectrum (slightly increased b) and smaller dmax, while yet increasing sinking velocity. Overall, the temperature-effect of remineralization is large and RLS tend to become shorter (Fig. 10; note that spatially, RLSs show a mixed response in this region, see Fig. D1e, f). For other major ocean regions changes, please refer to Figs. E1 and E2.
With M4AGO, we have the opportunity to investigate potential consequences of composition changes on particle sinking and flux attenuation in a scheme where all these individual aspects are mechanistically linked together. In the following, we aim at illuminating potential future research needs from a particle modeling perspective by diagnosing contributions of model parameters to future mean sinking velocity changes. High future impacts of particle properties on sinking velocity suggest high uncertainty in these particle properties, which thus qualify as potential future research needs.
Figure 11Relative contribution of changes in climatological mean particle properties and dynamic viscosity between the historical (1985–2014) and future (2070–2099) period to changes in sinking velocity at export depth (Eq. 4). The mean sinking velocity determining diagnostic model parameters are: 〈ρp〉: mean density of primary particles; 〈dp〉: mean diameter of primary particles; df: fractal dimension of the particles (microstructure); μ: molecular dynamic viscosity of sea water; dmax: maximum particle diameter; b: the slope of the particle number distribution
In order to identify diagnostic model parameters that affect future settling velocity most, we define the relative contribution of changes of parameters, , to changes in mean sinking velocity as follows
where is the partial derivative of the mass concentration-weighted mean sinking velocity with respect to diagnostic parameter Xi and is the absolute change of the climatological diagnostic parameter mean between the historical, Xi,hist, and the future projected Xi,proj, time period. By neglecting higher order terms in the derivatives, we only provide a first order estimate of parameters influence on future changes in sinking velocity (for historical 〈ws〉 and absolute changes in the future projection, see Appendix D, Fig. D1).
We defined the relative contribution, RC, in such a way that it provides the sign of response, the relative percentage change of the historical settling velocity in the future due to parameter Xi, and . Strongest RC appear from changes in mean primary particle density, 〈ρp〉, and fractal dimension of particles, df (Fig. 11). Sinking velocity in future response less to dynamic molecular viscosity, μ, and changes in mean primary particle size, 〈dp〉 and even lesser to changes in maximum particle diameter, dmax, and the number distribution slope, b.
The changes in these diagnostic particle properties and their individual contributions are closely connected to changes in concentration of tracers that sink together and thus to export fluxes (see Appendix C and Fig. C1). In the tropical, subtropical and North Pacific region, changes in the CaCO3 to POC export ratios affect the co-varying 〈ρp〉 and df and makes ballasting CaCO3 a strong driver. In these silicate-deprived regions, the ballasting with CaCO3 makes particles more prone to fragmentation and repacking, generating more compact particles with higher fractal dimension, and thus decreases maximum particle diameters in the future. In regions, where the opal to POC export flux ratio increases in the future period, mean primary particle size increases which contributes to increased sinking velocities. The increase of water temperature in most parts of the euphotic zone and upper mesopelagic of the oceans leads to lower dynamic sea water viscosity and thus contributes to increasing sinking velocities.
The tendencies drawn from the diagnostically evolving particle properties and their physical environment generally agree with former studies. Production of ballasting material has been suggested to decrease in future and thus its effect on export fluxes (Henson et al., 2022). In HAMOCC with M4AGO, ballasting fluxes are projected to decline in equatorial regions, and slightly increase in subtropical regions (see Appendix C). In the subtropical regions, particle composition shift towards a more ballast-affected particle regime with denser mean primary particles and being more compact, less porous due to lower stickiness. This leads to increased sinking velocities. However, as in these regions also the POC remineralization increases due to the overall warming, the combined effects lead to reduced RLS and export fluxes of POC compared to NPP which is visible in the reduced peg ratio in future (Sect. 3.1). Enhanced remineralization in future due to temperature-dependency has thus a two fold effect on particles in M4AGO in these regions: (i) an increase in primary particle density and (ii) decreasing porosity, which together lead to denser, faster sinking particles with less detritus content. Hence, changes of the ratio between in biogenic mineral shell material and aggregated detritus appear as driver for changes in settling velocity and to lesser extent, the amount of ballasting material alone. The effect on export flux is thus not purely additive and thus contrasts to approaches like in Hofmann and Schellnhuber (2009). At export depth, the molecular dynamic viscosity has a fairly strong influence on sinking velocity, with RCμ of about 10 % to 30 % in many ocean regions. Its relevance, however, decreases when considering the full water column and its contribution to increased sinking fluxes is estimated to be about 3 % (Taucher et al., 2014; Henson et al., 2022). Only few regions of the oceans show proportionally extremely increasing temperatures in the mesopelagic (see Sect. 3.4). Among them the Arctic Ocean, where temperature increase by more than 100 % in the mesopelagic, which translates to decreasing viscosity by about 8 % to 10 %. While the mesopelagic in the subtropics is also warming, the effect is less and extrapolating the shown relative contribution of viscosity on sinking velocity to depth would thus overestimate its contribution.
Based on a model study, Leung et al. (2021) suggested variable particle distributions in combination with temperature-dependent remineralization and temperature effects on phytoplankton size structure could lead to a negative feedback on export production due to smaller, slower sinking particles. Indeed, in subtropical regions, the simulated maximum particle size tends to decrease which is in some areas accompanied by an increasing distribution slope (i.e. a shift towards smaller particles), both congruent with the analysis of Leung et al. (2021). However, in M4AGO this is associated by increasing primary particle density and fractal dimension, leading to denser particles and thus faster sinking velocity. In M4AGO, the suggested negative feedback by Leung et al. (2021) is thus at least partially offset by an increasing particle density due to lower porosity and denser compounds. M4AGO potentially underestimates the relative contributions of the variable size distribution slope, since it exhibits limited variability. In order to better understand and quantify the feedback proposed by Leung et al. (2021), incorporation of ballasting material and potentially associated microstructure changes of particles in their approach would be thus helpful.
In summary, major future changes and uncertainties relevant for sinking fluxes are associated to mean primary particle density, related to ballasting minerals and fecal pellet production, and microstructure of particles. Given that particle fluxes theoretically offer a better constrain on ocean biogeochemistry models than nutrient tracer distributions alone (Kriest et al., 2023), our present study informs about sensitive particle properties that may be changing and affecting fluxes under climate change and thus qualify as present-day observational and process-based modeling targets. Particularly processes that lead to and affect microstructure are highly uncertain while seeming important to understand the response of sinking velocity and thus POC fluxes under a changing climate. Studies by e.g Khelifa and Hill (2006); Sanders et al. (2010) and Spencer et al. (2021) cast doubt on the assumption of statistically well-homogenized particle size distributions. The studies rather suggest certain clusters, in which e.g. minerals prevail in smaller, compacted particles, while large, loose particles are dominated by high organic to inorganic ratios. The underlying physical basis could be in the different physico-chemical surface properties of the components and different timescales of aggregation and intra-size distribution homogenization through e.g. recurring aggregation and fragmentation processes, which all affect particle composition, mass distribution across the size spectrum and microstructure. Among the constituents and processes that affect particle structure likely most, are the production of sticky extracellular polymeric substances such as transparent exopolymer particles (TEPs; Mari et al., 2017; Quigg et al., 2021), effects of compounds on overall particle aggregation efficiency and susceptibility to fragmentation and re-packing processes (Briggs et al., 2020; Song et al., 2023), but also biologically mediated processes such as packing in fecal pellets (Kilps et al., 1994) through zooplankton ingestion of phytoplankton or during coprophagie. Initially investigated tediously via SCUBA sampling (Alldredge and Gotschalk, 1988), theoretically (Jiang and Logan, 1991; Logan and Kilps, 1995), or under controlled laboratory conditions (Hamm, 2002; Passow and De La Rocha, 2006), the role of variable composition and microstructure for particle transport (Omand et al., 2020; Trudnowska et al., 2021; Cael et al., 2021), but also for optical properties (Organelli et al., 2018; Anitas, 2020; Wang et al., 2022) relevant for satellite inversions and underwater light climate are increasingly acknowledged. However, little information is thus far available on processes governing particle microstructure in a microbially structured, complex, heterogeneous ocean (Azam and Malfatti, 2007) and how to incorporate these less heuristically and more mechanistically in models like M4AGO to reduce the associated uncertainties.
3.6 General Discussion
The response of net primary production and associated export fluxes from the euphotic into the mesopelagic zone under projected climate warming are thus far afflicted with high uncertainties, and ESMs even disagree in the sign of response (Laufkötter et al., 2015; Henson et al., 2022). This limits the ability to constrain the future biological carbon pump and thus carbon sequestration with vast consequences on e.g. fisheries management decision making and deep ocean diversity management. The response of the net primary production, export production and generally biological carbon pump in ESMs is linked to the incorporated processes and their representation (Laufkötter et al., 2015, 2016). For example, ESMs only partially represent relevant mechanisms for present-day and future export fluxes (Henson et al., 2022). To some extend, this is due to limited observations, unknown constraints and thus the ability to adequately represent the processes. By simplifying or ignoring processes, compensating effects might be excluded and biases are introduced during the model tuning which, as a consequence, induces uncertainties in future projections (Henson et al., 2022). With the present work we therefore aimed at increasing the processes representations in HAMOCC as part of MPI-ESM and the understanding how that affects the future export fluxes and biological carbon pump.
The comparison of the two MPI-ESM1.2-LR model versions, CMIP6 and M4AGO, enabled to investigate the response of ocean biogeochemical fluxes and biogeochemistry to two different sinking schemes and remineralization parametrizations under ongoing climate warming. Studying the two sinking schemes with the same physical model, the differences between the simulations are attributed to responses to the changed sinking dynamics. The most striking changes associated to the different sinking schemes are related to the change in remineralization length scales in the euphotic zone and upper ocean. Maerz et al. (2020) showed that both, sinking velocity and temperature-dependent remineralization contribute to changes in RLS of POC. M4AGOs RLS are particularly shorter in the euphotic zone of the low latitudes than in the standard CMIP6 version. This promotes higher NPP and buffering of its future decline in the low latitudes (Segschneider and Bendtsen, 2013). The different export flux and transfer efficiency pattern imprints also on the latitudinal CO2 flux pattern and the timing, when the low latitudes turn into a net-sink of CO2. Despite regional differences between the two model versions, the response of the global CO2 fluxes are comparable with a 0.5 % difference in totally taken up CO2 during the simulated time between 1850 and 2100. Internal variability-elucidating ensemble simulations need to be carried out to further detail effects of transfer efficiency pattern on oceanic carbon sequestration potential.
M4AGO reproduces well the transfer efficiency pattern, constrained by diagnosed phosphate fluxes and inverse modeling, found by Weber et al. (2016) and by others (DeVries and Weber, 2017; Cram et al., 2018; Dinauer et al., 2022; Sulpis et al., 2023). Yet, e.g. Marsay et al. (2015) proposed a different pattern and general uncertainties on transfer efficiency and their future changes remain. Observational-based short term-derived transfer efficiency potentially suffers from too large dependency on vertically time-lagged fluxes (e. g. Giering et al., 2017; Maerz et al., 2020, see Fig. C1 in the latter), localization and environmental conditions which makes it difficult to directly compare them with ESMs. However, on annual time scales, POC fluxes pose a valuable constrain on ESMs (Kriest et al., 2023). Fluxes and associated transfer efficiency eventually determine nutrient and DIC distributions in combination with the underlying circulation pattern on the long term (O(1000 years)). Despite the high logistical and costly requirements for such observational endeavor, we therefore highly advocate for year-long-integrated regional measurements to enable direct observational constrains on POC fluxes and transfer efficiency. Ideally, this could be accompanied by measurements on processes affecting the the RLS over the water column to enable bridging between observations and process representations in models.
In addition to an advanced representation of marine particles, M4AGO is computationally inexpensive compared to size class-based models (e. g. MSPACMAM; Dinauer et al., 2022, see also Appendix F for a brief comparison) that require one tracer per size class and settling component which, for example, doubles the number of advected tracers for a two size class model. The low computational costs and explicit representation of ballasting effects also of dust on particles suggest M4AGO also as candidate in paleo studies (Liu et al., 2024), e.g. for understanding dust contributions to atmospheric CO2 variations during glacial-interglacial cycles. M4AGO's mechanistic representation of particle dynamics also enabled its successful application in a global ocean biogeochemistry model dedicated to seamlessly integrate a high resolution coastal ocean, ICON-COAST (Mathis et al., 2022, 2024). The new sinking scheme performed reasonable well even under highly dynamic conditions, including benthic-pelagic coupling, typical for coastal and shelf sea regions and was able to reproduce characteristic spatio-temporal properties of particles. These features make an application in high-resolution, sub-mesoscale resolving ocean models possible and promising (Jungclaus et al., 2022; Hohenegger et al., 2023; Nielsen et al., 2025). However, the thus far limited representation of size distribution dynamics, namely through a fixed functional form and lower represented variability than measured, and internal homogeneous particle composition still poses challenges to represent particle dynamics in high resolution models adequately.
Summarizing the discussion briefly, uncertainties and limited process understanding still poses a challenge, but introducing the complexity of particles and their dynamics in ocean biogeochemical models opens new research avenues to investigate the evolution of the future biological carbon pump.
The development of M4AGO offered the possibility to study the response of net primary production, export fluxes and the biological carbon pump to future climate warming via an explicit and thus more realistic process representation of marine particles in an ESM. The global effect of M4AGO on future NPP, export fluxes and carbon fluxes are comparable to the MPI-ESM1.2-LR CMIP6 version while they both compare well to results of other ESMs of the CMIP6 cohort. Largest differences between the CMIP6 and the M4AGO version of MPI-ESM1.2-LR occur at regional scale and their response differ particularly latitudinally. With M4AGO, MPI-ESM shows stronger buffering, yet a slightly stronger future decline of NPP in the tropical and subtropical regions due to nitrate loss in more extended ODZs. In the Arctic, the future increase of NPP due to ice-free seasons is weakened in M4AGO by its higher transfer efficiency and thus nutrient loss compared to the CMIP6 version. The different latitudinal pattern with M4AGO compared to the CMIP6 model version imprints on CO2 fluxes. Higher latitudes, particularly the Southern Ocean, gain more importance in oceanic CO2 uptake which also delays the timing of low latitudes becoming a net-sink of CO2.
M4AGOs mechanistic representation of particles links modeled particle fluxes closer to observations. Despite comprising a number of uncertain parameters, M4AGO thus contributes in making research needs transparent, i.e. on microstructure of particles in a heterogeneous ocean which together with composition (i) determines settling behavior and (ii) turned out to strongly affect future sinking velocities of particles and thus indicating a considerable uncertainty for future fluxes. In addition to microstructure, the temperature-dependent POC remineralization and mineral dissolution co-determine and affect the remineralization length scales and indirectly the vertical evolution of settling velocities in M4AGO. Better understanding mineral to POC associations, and potential changes in primary particle sizes will aid in further constraining the ballasting and size effects on the biological carbon pump in a future climate.
In conclusion, at the regional scale the more mechanistic sinking scheme M4AGO that responds dynamically to changing environment and primary production, buffers future ocean biogeochemistry more compared to the stiff Martin curve-like POC flux representation.
On long time scales, circulation in combination with the spatial pattern and amount of export production and attenuation of detritus fluxes imprints on nutrient distributions. Particularly the high transfer efficiency in high latitudes and the shallower remineralization in subtropical and equatorial regions in M4AGO compared to the CMIP6 version can therefore be expected to lead to changes in nutrient, DIC and alkalinity distributions. Generally, MPI-ESM1.2-LR circulation cannot be expected to fully represent real world circulation in all details, which introduces biases not only in physical variables (Jungclaus et al., 2013; Mauritsen et al., 2019), but also in ocean biogeochemistry. We therefore briefly evaluate the two model versions via Taylor diagrams (Taylor, 2001) on an unweighted grid point comparison basis. Since the grid spacing roughly varies with the Rossby radius of deformation in MPI-ESM1.2-LR, the unweighted grid point-based comparison enables to put similar weights between low- and high latitude regions. In an area-weighted approach, high latitude regions would have lower influence on model biases in our show cases.
Figure A1Taylor diagrams for historical period. We compare simulated historical climatological means of silicate, phosphate, oxygen and nitrate distributions to the World Ocean Atlas (WOA) version 13 (Boyer et al., 2013; Garcia et al., 2014a, b). For total alkalinity and DIC, we compare to the Global Ocean Data Analysis Project (GLODAPv2) climatology (Lauvset et al., 2016; Olsen et al., 2016). Note that Si is outside the axis in the euphotic Atlantic, where both models show a correlation of about 0.5, normalized standard deviations of about and , and RMSD of and , for M4AGO/CMIP6 at 6 and 100 m depth, respectively.
Analogue to Maerz et al. (2020), we distinguish between two different ocean regions, the Pacific and the Atlantic ocean, to account for their different circulations and water mass ages and compare them to gridded climatological data products at four different depth (Fig. A1). Overall, the two model versions show very similar biogeochemical tracer distributions and biases compared to observational products, despite their structural differences. There is no clear tendency of improvement or deterioration of M4AGO compared to the CMIP6 model. One potential exception with regards to the overall agreement between the two model versions is silicate, for which the differences between the two model versions peak out and CMIP6 showing higher normalized standard deviations and root mean square deviations (RMSD) than M4AGO. It is noteworthy to mention again that the CMIP6 version exhibits a too high silicate inventory, which is not the case in the M4AGO version (see Sect. 2.2). These CMIP6 biases of Si concentrations are particularly high in the deep ocean (not shown). We would, however, expect the surface ocean to be most influenced by biogeochemical processes like uptake, sinking and dissolution, which would suggest a structural influence on the model representation of silicate particularly in euphotic waters. Typically, silicate, together with phosphate, are regarded as less influenced by biogeochemical processes, e.g. compared to nitrogen species, and are thus indications for the goodness of ocean circulation. In M4AGO, silicate dynamics is stronger linked to biogeochemical processes due to the coupling of settling velocities and remineralization that can take more effect. Further, we observe a too high residence time and thus dissolution in ODZs, which is closely linked to sluggish circulation inherent to general ocean circulation models of resolution classically used in ESMs (Najjar et al., 1992; Aumont et al., 1999; Dietze and Loeptien, 2013; Duteil et al., 2021). Likely, we additionally overestimate opal dissolution in these ODZs, since we do not account for potential oxygen limitations of the microbially mediated dissolution rates (Bidle et al., 2002). Generally, the overestimated ODZs impinge on nutrient, DIC and alkalinity biases in deeper ocean regions.
The seasonal excursion of the mixed layer depth (MLD) indicates, in how far the euphotic zone and thus primary production can be replenished and refueled by nutrients accumulated in deeper ocean regions. In large areas of the ocean, the MLD remains similar or decreases in future (see Fig. B1a, b). Only in a few regions the MLD increases in future, e.g. in Atlantic sector of the Arctic Ocean and in frontal regions like the south Indic front to the Southern ocean. In the central Pacific, the MLD tends to decline, decreasing replenishment of surface nutrients and thus contributes to the simulated decline of NPP (Sect. 3.1, Fig. 1). In addition, throughout most parts of the ocean, the vertical stratification increases in future, which additionally contributes to declining exchange between the shallower nutrient-depleted and the nutrient-enriched deeper waters (see Fig. B1c, d). The Atlantic sector and some coastal areas of the Arctic Ocean that become ice-free in summer in the future, poses most prominent exceptions and vertical stratification declines in these regions, contributing to nutrient availability and thus increased net primary production. In the central and Pacific sector of the Arctic Ocean the stratification is reduced in future summers (see Fig. B2), particularly in August, contributing to more extended summer growth of phytoplankton due to improved light conditions.
Maerz et al. (2020) showed that mean sinking velocity of particle mass concentration is strongly linked to particle properties, among them most influential primary particle density, size and particle microstructure, which in M4AGO are all determined by settling tracer concentrations and their ratios. In the following, we therefore showcase POC and biogenic mineral fluxes, their ratios and their changes, which affect particle properties in future (see Sect. 3.5). We here focus on export fluxes at the export depth, since they also determine to great extend, how sinking particles and their properties populate through the water column and thus determine future changes of sinking velocity (Sect. 3.5), and the attenuation of fluxes reflected by remineralization length scales (Sect. 3.4).
The general pattern of POC export fluxes, FPOC, follows, as expected, the net primary production (cmp. Figs. C1 and 1). Highest FPOC occur in nutrient-rich upwelling regions and in the equatorial eastern Pacific, where in addition equatorial jets sustain mixing and thus high nutrient delivery into the euphotic zone. Significant opal production and subsequent sinking and export to the mesopelagic is associated and confined to these upwelling as well as well-mixed or seasonally less stratified regions. The close connection between POC and opal production through phytoplankton growth and decay in HAMOCC leads to an opal to POC ratio pattern at export depth with lower ratios in equatorial and subtropical regions than in high latitude regions. This latitudinal pattern emerges since detritus remineralization is generally faster than opal dissolution and detritus remineralization is strongly enhanced in the warmer regions. The latitudinal pattern is closely linked to the higher temperature-dependent detritus remineralization leading to higher detritus losses compared to opal. Inherent to HAMOCC, once bulk phytoplankton and zooplankton become silicate-limited, organisms are assumed to start producing shell material via calcification which is mainly confined to lower latitudes. Highest CaCO3 export fluxes are found in the westward wake of the opal production region in the equatorial jet of the Pacific. Here, nutrient availability is still high through remineralization, while silicate is diminished due to opal production, export and slow dissolution. High remineralization rates, non-shell producing plankton including cyanobacteria shift the highest CaCO3 to POC export ratios further westward and into the southern subtropical gyre. The rather sequentially process order of silification and calcification, dependent on silicate availability, leads to a distinct latitudinal opal to CaCO3 export ratio with high values in opal-dominated regions.
In line with changes of the peg ratio and NPP discussed in Sect. 3.1, future POC fluxes decline in most parts of the subtropical and tropical regions. An exception is associated to the recirculation of the Humboldt current, where increased POC export production are found in the projection, similarly in CMIP6 (not shown). In higher latitudes, increased fluxes appear in the Subantarctic frontal region and in the Arctic Ocean. A similar pattern of opal export fluxes appear. By contrast, the opal to POC flux ratio shows a bipolar pattern in northern and southern high latitudes. While in the silicate-rich Southern Ocean, the ratio marginally changes, the ratio declines in the northern Pacific and Arctic Ocean. In the case of CaCO3 fluxes, the northern Pacific, North Atlantic and the subtropical gyres show increasing CaCO3 export production in the future period. The CaCO3 to POC export ratio increases strongly in most subtropical and tropical regions, but also in the northern higher latitudes. The formerly described bipolar future response in northern and southern high latitudes for opal export fluxes manifests also in the opal to CaCO3 export production ratio. CaCO3 gains higher relevance compared to opal export production in the future northern latitudes according to M4AGO.
For most ocean regions, biogenic mineral (opal and CaCO3) relative to POC export increases in future and thus provides relative more ballasting (including primary particle size effects; Maerz et al., 2020) to particles. The future decrease in POC to mineral ballast ratio at export depth can primarily be attributed to increased remineralization due to rising surface ocean temperatures. The changes in opal and CaCO3 export production are a consequence of declining NPP and changing availability of silicate. The latter is primarily associated to changing stratification. In regions of future intensifying stratification, silicate lost early in the growth season cannot be mixed up easily again into the euphotic zone to sustain or promote further silicification. By contrast, the continuous strong mixing in the Southern Ocean is sustaining the ongoing opal production-dominated phytoplankton community.
To briefly summarize, the interplay of changes due to temperature-dependent remineralization, NPP and stratification-related dissolved silicate availability imprint on export fluxes and their ratios which also manifest in particle property changes, discussed in Sect. 3.5.
In Fig. D1, the climatological mean for the historical period and the respective changes for the future period are shown for M4AGO for the export depth (100 m) for sinking velocity, the remineralization rates and the POC remineralization length scales.
Figure D1Climatological year mean for the historical period and changes in the future period in M4AGO at export depth for (a, b) mass concentration-weighted sinking velocity, 〈ws〉; (c, d) Q10- and O2-dependent remineralization rate, μremin; (e, f) remineralization length scales, RLS, of POC (see also Eq. 3 for definition). Note that particularly sinking velocity and the RLS feature a strong seasonal variability in the high latitudes due to changes in particle composition. For comparison, the CMIP6 version features a globally constant sinking velocity of 3.5 m d−1 between 0 to 100 m depth, a remineralization rate of 0.026 d−1 (times oxygen limitation) and thus a RLS(POC) ≈ 135 m at export depth (assuming no oxygen limitation here for simplicity).
Equivalent to Fig. 10, the future changes in particle properties, remineralization length scales, dynamic molecular viscosity and particulate fluxes in major ocean regions are presented for other major ocean regions (see Figs. E1 and E2).
Figure E1Percentage changes of particle properties, remineralization length scales, dynamic molecular viscosity and particulate fluxes in major ocean regions. Note that the individual radial axes can hold different percentage changes.
In order to facilitate comparison to particle flux models like MSPACMAM (Dinauer et al., 2022) that consider small and large particles for sinking fluxes, we here calculate the injection fraction of large particles at export depth , where:
with n(d) and m(d) being the number distribution and particle mass, respectively. We here follow Dinauer et al. (2022) and set the splitting diameter to ds=250 µm.
We find a similar latitudinal pattern as Dinauer et al. (2022) with higher POC injection to large particles in the high latitudes and upwelling regions (Fig. F1). However, our model shows higher injection fraction to large particles in the subtropical gyres and tropical regions than used in Dinauer et al. (2022). Generally, the high latitudes exhibit a higher variability of the injection ratio due to higher variability in large particle formation in our simulation, visualized as standard deviation of monthly injection fraction.
Figure F1Climatological mean (a) and standard deviation (b) of the monthly injection fraction of large particles (250 µm; following Dinauer et al., 2022) at export depth for the historical period. (c) Injection fraction applied by Dinauer et al. (2022). (d) Difference of the injection fraction between M4AGO and Dinauer et al. (2022).
MPIOM model code for the M4AGO simulation, git sha ID: 32878f1ca68e9ad62e60a5baee688ff69e45694, is available upon request to the author. The same M4AGO code is also implemented in the current MPIOM master as part of MPI-ESM. For The MPI-ESM code and licensing, refer to Model Development Team Max-Planck-Institut für Meterologie (2024) (https://doi.org/10.17617/3.H44EN5). M4AGO is under active development and available at https://github.com/jmaerz/M4AGO-sinking-scheme (last access: 5 March 2026) as a submodule. Main primary data and analysis scripts are stored and made available through the Open Research Data Repository of the Max Planck Society, Edmond: Maerz (2025), https://doi.org/10.17617/3.UPQW7H.
Conceptualization: JM, KDS and TI conceptualized the research goals. Data curation: KDS and JM took care of the simulations. Formal analysis: JM carried out the analysis of model results. Funding acquisition: TI wrote and acted as PI of the initial MARMA proposal. JM and SA wrote the follow-up proposal for MARMA. TI received the CLICCS project grant and thanks to Christoph Heinze, who got granted the ESM2025 funding under which JM is working; JM received funding through BioGeoSea. Investigation: JM conducted the experiments and research with support by KDS and Irene Stemmler. Methodology: JM earlier developed the advanced sinking scheme. Project administration: TI had the responsibility for the project administration. Resources: The DKRZ provided the HPC resources, where all computations and post-processing were carried out. Software: The earlier implementation of the new sinking scheme was performed by JM, with technical support and code review by Irene Stemmler and KDS. Supervision: No supervision involved. Validation: Evaluation of the model was performed by JM. Visualization: Visualization of model experiments was carried out by JM. Writing – original draft preparation: JM prepared the original draft of the manuscript. Writing – review & editing: KDS and SA contributed significantly by reviewing the manuscript. JM performed the editing.
The contact author has declared that none of the authors has any competing interests.
Publisher's note: Copernicus Publications remains neutral with regard to jurisdictional claims made in the text, published maps, institutional affiliations, or any other geographical representation in this paper. The authors bear the ultimate responsibility for providing appropriate place names. Views expressed in the text are those of the authors and do not necessarily reflect the views of the publisher.
The authors thank Hongmei Li for the internal review and comments on the manuscript and Irene Stemmler for technical and scientific support of the work. Many thanks to the two anonymous reviewers who provided constructive and valuable comments on the manuscript. All simulations and post-processing were carried out at the German Climate Computing Center (DKRZ). The authors thank Thyng et al. (2016) and Crameri et al. (2020) for providing their python colormaps packages.
The Max Planck Society (MPG) funded the project “Multiscale Approach on the Role of Marine Aggregates (MARMA)” within which a dominant part of the work was carried out. The research has been further supported by the Deutsche Forschungsgemeinschaft (Germany’s Excellence Strategy – EXC 2037 “CLICCS – Climate, Climatic Change, and Society” – project no. 390683824, contribution to the Center for Earth System Research and Sustainability (CEN) of Universit ¨at Hamburg), the European Commission EU H2020 (Earth system models for the future – ESM2025, grant no. 101003536), the European Union's Horizon Europe research and innovation programme (BioGeoSea – Enhancing Biogeochemical Essential Ocean Variables for European and Global Assessments, grant no. 101216427) and Novo Nordisk Foundation (“Shallow Water Processes and Transitions to the Baltic Scale” grant no. 0079370).
The article processing charges for this open-access publication were covered by the Max Planck Society.
This paper was edited by Olivier Sulpis and reviewed by two anonymous referees.
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- Abstract
- Introduction
- Methods
- Results and Discussion
- Conclusions
- Appendix A: General Evaluation
- Appendix B: Future changes of mixed layer depth and stratification
- Appendix C: Future changes in mineral export fluxes in M4AGO
- Appendix D: Simulated particle sinking velocity, remineralization rate and RLS and their future changes in M4AGO
- Appendix E: Future regional changes of particle property and particulate fluxes
- Appendix F: Injection fraction of large particles at export depth
- Code and data availability
- Author contributions
- Competing interests
- Disclaimer
- Acknowledgements
- Financial support
- Review statement
- References
- Abstract
- Introduction
- Methods
- Results and Discussion
- Conclusions
- Appendix A: General Evaluation
- Appendix B: Future changes of mixed layer depth and stratification
- Appendix C: Future changes in mineral export fluxes in M4AGO
- Appendix D: Simulated particle sinking velocity, remineralization rate and RLS and their future changes in M4AGO
- Appendix E: Future regional changes of particle property and particulate fluxes
- Appendix F: Injection fraction of large particles at export depth
- Code and data availability
- Author contributions
- Competing interests
- Disclaimer
- Acknowledgements
- Financial support
- Review statement
- References