Skip to main content
Proceedings of the National Academy of Sciences of the United States of America logoLink to Proceedings of the National Academy of Sciences of the United States of America
. 2021 Apr 27;118(18):e2023544118. doi: 10.1073/pnas.2023544118

Redox control on the tungsten isotope composition of seawater

Florian Kurzweil a,1, Corey Archer b, Martin Wille c, Ronny Schoenberg d,e, Carsten Münker a, Olaf Dellwig f
PMCID: PMC8106329  PMID: 33906947

Significance

The fate and transport of tungsten (W) in aquatic environments is still poorly constrained. To identify the processes that control the abundance of dissolved W, we applied a sophisticated analytical approach that enables the accurate determination of the seawater W isotopic composition. Our results indicate that the removal of W from seawater mainly occurs via adsorption onto oxide minerals. The marine inventory of W is therefore intimately linked to the areal extension of oxic marine conditions. Concurrently, the limited scavenging of W in anoxic marine settings seems a unique characteristic of W, highlighting that W isotopes can help to reconstruct the earliest rise of oceanic oxygen in Earth’s history.

Keywords: stable tungsten isotopes, seawater, euxinic porewater, Mn-oxide, paleoredox

Abstract

Free oxygen represents an essential basis for the evolution of complex life forms on a habitable Earth. The isotope composition of redox-sensitive trace elements such as tungsten (W) can possibly trace the earliest rise of oceanic oxygen in Earth’s history. However, the impact of redox changes on the W isotope composition of seawater is still unknown. Here, we report highly variable W isotope compositions in the water column of a redox-stratified basin (δ186/184W between +0.347 and +0.810 ‰) that contrast with the homogenous W isotope composition of the open ocean (refined δ186/184W of +0.543 ± 0.046 ‰). Consistent with experimental studies, the preferential scavenging of isotopically light W by Mn-oxides increases the δ186/184W of surrounding seawater, whereas the redissolution of Mn-oxides causes decreasing seawater δ186/184W. Overall, the distinctly heavy stable W isotopic signature of open ocean seawater mirrors predominantly fully oxic conditions in modern oceans. We expect, however, that the redox evolution from anoxic to hypoxic and finally oxic marine conditions in early Earth’s history would have continuously increased the seawater δ186/184W. Stable W isotope compositions of chemical sediments that potentially preserve changing seawater W isotope signatures might therefore reflect global changes in marine redox conditions.


Tungsten (W) belongs to the transition group VI elements and is dissolved as the tetrahedral oxyanion tungstate (WO42−) in the modern oceans. Despite its relatively low concentration of 0.041 to 0.067 nM, a moderately long residence time between 14,000 to 61,000 y suggests a homogenous distribution of W in the oceans (13). Riverine and hydrothermal sources, assumed to be the main inputs for marine W, have dissolved W concentrations that may be orders of magnitudes higher (rivers: 0.02 to 1029 nM; hydrothermal fluids: 0.22 to 123 nM), arguing for an efficient scavenging of W in estuarine and marine environments (36). While the stable W isotope composition of rivers and hydrothermal fluids is still unknown, a pioneering study of Fujiwara et al. (7) indicates that the seawater stable W isotope composition of the Northern Pacific is homogeneous with δ186/184W of +0.55 ± 0.12 ‰ (Eq. 1). Thus, the seawater dissolved W inventory is isotopically significantly heavier than modern igneous rocks [δ186/184W of +0.096 ± 0.076 ‰ (8, 9)], the ultimate source for marine W. This suggests stable W isotope fractionation during processes such as weathering, hydrothermal alteration of the oceanic crust, or the scavenging of dissolved marine W.

In euxinic environments, the sequestration of dissolved W is limited because of its increased solubility as thiotungstate species (WOxS4−x2−) that form when WO42− is exposed to elevated H2S(aq) levels (e.g., ref. 10). However, particle shuttling by Mn-oxides and Fe-hydroxides acting at pelagic redoxclines efficiently scavenges dissolved WO42− and may cause strong authigenic enrichments of W in modern chemical sediments (e.g., ref. 3). Adsorption of WO42− onto these (hydr)oxides triggers a change in coordination from tetrahedral to octahedral (11). Because the bonding in octahedral coordination is longer and weaker, isotopically light W is preferentially adsorbed (12). Kashiwabara et al. (2017) experimentally determined similar stable W isotopic differences between dissolved and adsorbed W species for Mn-oxides and Fe-hydroxides, respectively, with Δ186/184WMn-oxides = δ186/184Wdissolved − δ186/184Wadsorbed = 0.59 ± 0.14 ‰ and Δ186/184WFe-hydroxides = δ186/184Wdissolved − δ186/184Wadsorbed = 0.51 ± 0.06 ‰ (12). Thus, adsorption processes in oxic marine environments may provide the key mechanism for the build-up of an isotopically heavy ocean.

Molybdenum (Mo), the geochemical twin of W, also exists as a dissolved oxyanion (MoO42−) species and is homogeneously distributed in the modern ocean with a higher concentration of around 105 nM (13). As for W, the stable Mo isotope composition of seawater [δ98/95Mo = 2.34 ± 0.10 ‰ (14, 15)] is distinctly heavy compared to the bulk crust [δ98/95Mo = +0.47 ± 0.12 ‰ (16)]. In analogy to WO42−, adsorption of MoO42− onto Mn-oxides also causes a change in coordination from tetrahedral to octahedral. However, there are some key differences in the redox sensitivity of W and Mo. During adsorption of MoO42− onto Fe-hydroxides, the tetrahedral coordination is partially retained (11). The experimentally determined isotopic difference between dissolved MoO42− and adsorbed Mo species is therefore significantly smaller for Fe-hydroxides [Δ98/95MoFe-hydroxides = δ98/95Modissolved − δ98/95Moadsorbed = 1.11 ± 0.15 ‰ (17)] than for Mn-oxides [Δ98/95MoMn-oxides = δ98/95Modissolved − δ98/95Moadsorbed = 2.67 ± 0.18 ‰ (18)]. In euxinic environments, MoO42− is successively thiolated with increasing H2S(aq), forming predominantly thiomolybdate (MoS42−) at H2S(aq) > 11 µM (19). In contrast to WS42−, MoS42− is particle reactive and readily removed from solution by forming Fe–Mo–S clusters (20). In restricted and euxinic basins such as the modern Black Sea, the near quantitative sequestration of MoS42− results in the preservation of the seawater Mo isotopic signature in Black Sea sediments (21). However, incomplete scavenging of MoOxS4−x2− species in less restricted and/or weakly euxinic environments with H2S(aq) < 11 µM leads to the preferential burial of isotopically light Mo (21, 22). Therefore, adsorption processes in oxic marine environments but also the incomplete sequestration of Mo in euxinic settings may increase the δ98/95Mo of seawater. On the other hand, temporal variations in the δ186/184W of seawater and authigenic sediments might be more intimately linked to adsorption and deposition of oxide minerals. The difference in sensitivity to changing redox environments suggests that combined W and Mo proxy data may be a powerful way to trace subtle changes in oxygenation levels of the early surface Earth, particularly if further combined with other redox-sensitive trace metal proxies. Increasingly, multiple-proxy approaches are being used to remove the ambiguities that may be associated with individual paleoredox proxies (e.g., refs. 2326). Thus, stable W isotope analyses may represent a complementary tool for paleo-redox reconstructions that is particularly sensitive to oxide mineral formation in oxic marine environments. However, future paleo-redox applications require a better understanding of the processes that fractionate W isotopes and their definite implication on the seawater and sedimentary δ186/184W as offered by modern systems characterized by changing redox conditions.

In this study, we present W concentrations and stable W isotope compositions of oceanic water column profiles from the Southern Atlantic Ocean, the South China Sea in the Western Pacific Ocean, and from the Landsort Deep, a redox-stratified basin within the more restricted Baltic Sea (SI Appendix, Fig. S1). The dataset is complemented by stable W isotope compositions of suspended particles that form at the pelagic redoxcline of the Landsort Deep and euxinic porewaters from this site. Our results confirm the initial assumption of a deep ocean homogeneous in isotopically heavy W. Furthermore, we highlight the major redox-related processes that cause variations in the abundance and stable isotope composition of marine W. Overall, these findings provide the initial framework essential for the future application of stable W isotopes as a paleo-redox proxy.

Results and Discussion

To further constrain the δ186/184W of open ocean seawater, samples were analyzed from the Southern Atlantic and the South China Sea. The δ186/184W and W concentrations of Southern Atlantic seawater are relatively constant throughout the water column (+0.510 to +0.579 ‰ and 0.049 to 0.054 nM; Fig. 1A). We note that very small differences between Antarctic Intermediate Water (+0.510 to +0.543 ‰; 0.053 to 0.054 nM) and subjacent North Atlantic Deep Water (+0.553 to +0.579 ‰; 0.049 nM) can be barely resolved. In contrast, Western Pacific waters from the South China Sea show a clearly resolvable variability in δ186/184W and W concentrations. Surface waters exhibit highest W concentrations (up to 0.067 nM) and correspondingly have the lowest δ186/184W (as low as +0.445 ‰; Fig. 1B). With increasing water depth, W concentrations (as low as 0.050 nM) and δ186/184W (up to +0.556 ‰) approach an Atlantic-like open ocean value. Importantly, deep water masses in the South China Sea reflect open Pacific waters that intrude through the Luzon Strait as indicated by Pacific-like εNd values (27). However, the proximity of this site to the continent (SI Appendix, Fig. S1) makes it prone to riverine discharges (e.g., Pearl River) to surface waters, showing a slightly lower salinity (Dataset S1) and lower εNd values (27). Moreover, elevated concentrations of dissolved Mn in surface waters (Dataset S1) might indicate redissolution of particles enriched in Mn-oxide supplied by rivers or aerosols and the concurrent release of adsorbed W. Thus, increasing W concentrations and decreasing δ186/184W in shallower waters might reflect binary mixing of W supplied from rivers/aerosols and the open Pacific, respectively. Excluding the locally affected surface seawater samples from the South China Sea, the open ocean seawater samples have an average δ186/184W of +0.543 ± 0.046 ‰ (2SD; n = 10) and an average W concentration of 0.050 ± 0.007 nM (2SD; n = 10; Datasets S1 and S2). The new seawater δ186/184W data from both the South Atlantic Ocean and the South China Sea are perfectly consistent but more precise than a previous estimate on Northern Pacific seawater [+0.55 ± 0.12 ‰ (7)] and clearly indicate a relatively homogeneous seawater stable W isotope composition beneath the permanent thermocline.

Fig. 1.

Fig. 1.

Seawater W concentrations (open symbols) and W isotope compositions (closed symbols) for water column profiles of the Southern Atlantic Ocean (A) and the South China Sea in the Western Pacific Ocean (B). The error bars of δ186/184W values indicate the long-term repeatability of our in-house standard or the internal error of the measurement (2SE), whichever is larger. For W concentration measurements, we assume a relative SD (2RSD) of 5% based on repeated analyses of various reference materials (41). In the Southern Atlantic, Antarctic Intermediate Water exhibits higher W concentrations and slightly lower δ186/184W than North Atlantic Deep Water below. In the South China Sea, W concentrations decrease with depth, whereas δ186/184W increases, indicating a riverine and/or aerosol contribution of W to surface waters. Overall, our data suggest an open ocean δ186/184W of +0.543 ± 0.046 ‰ (2SD; n = 10; blue shading).

In contrast to the open ocean, water samples from the Landsort Deep (site LD1), the deepest basin in the more restricted Baltic Sea, show large variability in dissolved W concentrations (0.051 to 0.232 nM) and δ186/184W (+0.347 to +0.810 ‰; Fig. 2 and Dataset S3). In this basin, a pelagic redoxcline at around 80 to 88 m water depth (3, 28) separates oxic surface waters with high δ186/184W (+0.615 to +0.638 ‰) and low dissolved W (0.072 to 0.073 nM) from a deeper weakly euxinic water body (≥150 m) with lower δ186/184W (+0.409 to +0.417) and higher dissolved W (0.159 to 0.174 nM). The largest variability in δ186/184W of dissolved W is observed in the intermediate water column (80 to 105 m) including the redoxcline. In the upper part of the redoxcline, upward-diffusing dissolved Mn2+/3+ ions are oxidized to Mn(IV)-oxide particles (29), which efficiently scavenge trace metals such as W (Fig. 2; e.g., refs. 3, 30). Due to the preferential adsorption of isotopically light W onto Mn-oxides (12), the formation of Mn-oxides causes an increase in the δ186/184W of dissolved W from +0.638 ‰ in oxic surface waters up to +0.810 ‰ in the upper part of the redoxcline (Fig. 2). The chemically and/or microbially mediated dissolution of sinking Mn-oxides below and the concurrent release of adsorbed trace metals increases concentrations of dissolved W (up to 0.232 nM) and shifts the δ186/184W of dissolved W back to considerably lower values (down to +0.347 ‰ in 105 m depth). Consistently, Mn-oxide–rich particles that were filtered from the seawater across the redoxcline show even lower δ186/184W (+0.096 to +0.335 ‰; Fig. 2 and Dataset S4). The observed isotopic difference between the dissolved and the particulate phase is roughly in line with the experimentally predicted isotopic difference of Δ186/184W = δ186/184Wdissolved − δ186/184Wadsorbed = 0.59 ± 0.14 ‰ (12). However, unlike dissolved W, the particulate δ186/184W shows no distinct trend with depth, which is most likely due to slowly sinking Mn-oxide particles (31) that obscure a direct relation between depth of particle formation and sampling depth. The isotopic difference between dissolved and particulate W is therefore not expected to be constant with depth. Interestingly, the particulate W component (average δ186/184W of +0.211 ‰) is isotopically lighter than seawater but still significantly heavier than modern igneous rock suites [δ186/184W: +0.096 ± 0.076 ‰ (8, 9)]. Thus, extremely high δ186/184W values of Baltic seawater still cause relatively high δ186/184W values in the authigenic W component, although Mn-oxides preferentially adsorb isotopically light W (Fig. 3).

Fig. 2.

Fig. 2.

Water column profiles of dissolved and particulate Mn (A) and W (B) concentrations in the Landsort Deep (Baltic Sea). Oxic surface waters (blue shading) are separated from euxinic deeper waters (gray shading). (C) Water column profile of stable W isotope compositions. The error bars in all panels are smaller than symbol sizes. The preferential adsorption of isotopically light W onto Mn oxides causes increasing seawater δ186/184W in the upper part of the redoxcline but decreasing seawater δ186/184W below, where Mn-oxides are dissolved again. The diagenetic release of W from Mn-rich sediments might cause relatively low porewater δ186/184W (see also SI Appendix, Fig. S2 for more details).

Fig. 3.

Fig. 3.

Stable W isotope compositions of various reservoirs on Earth and their interrelations. The δ186/184W of igneous rocks (8, 9, 43), the ultimate source of marine W, is distinctly lower than the δ186/184W of seawater. It is still unclear if stable W isotope fractionation occurs during weathering, adsorption of W during riverine transport or hydrothermal alteration of the oceanic crust, thereby changing the δ186/184W of the marine input. However, our results indicate that the adsorption of marine W onto Mn-oxides is the most likely process that causes very high δ186/184W of open ocean seawater (mass balance constraints in the SI Appendix, Fig. S3). We highlight that the δ186/184W of open ocean seawater is lower than the δ186/184W of (shallow) Baltic seawater possibly due to the efficient sequestration of isotopically light W via adsorption onto Mn-oxides in deep basins such as the Landsort Deep and only restricted water exchange with the open ocean via Skagerrak. Accordingly, δ186/184W values of Mn-oxides deposited in open marine settings are expected to be lower than the δ186/184W of Mn-oxide particles from the Landsort Deep. The partial dissolution of Mn-oxides during diagenesis in the Landsort Deep sediments may result in δ186/184W of sediment pore waters and basinal deep waters that are distinctly lower than the δ186/184W of (shallow) Baltic seawater.

Euxinic deep water samples from site LD1 (dissolved H2Stotal between 30.2 and 34.2 µM) exhibit constant δ186/184W of +0.414 ± 0.008 ‰ (2SD; n = 4) as well as constant concentrations of dissolved W (0.164 ± 0.011 nM; 2SD; n = 7) and dissolved Mn (2.48 ± 0.27 µM; 2SD; n = 7), arguing against significant scavenging or dissolution in water depths below ∼150 m, as expected from the virtual absence of particulate Mn (Fig. 2). In the corresponding sediments at site LD1, the porewater concentrations of dissolved Mn (83.4 to 901 µM), dissolved W (23.0 to 219 nM), and dissolved H2Stotal (935.7 to 3,042 µM) increase with sediment depth and are significantly higher than in the water column [SI Appendix, Fig. S2 and Dataset S5 (3)]. The increasing dissolved H2Stotal levels cause the successive thiolation of WO42− (32). While WO42− is the predominant species in the weakly euxinic water column of the Landsort Deep (>98%), it is significantly less abundant in the highly euxinic porewaters (e.g., only 15.6% in the deepest porewater sample; SI Appendix, Fig. S2 and Dataset S5). Because W–S bonds are expected to be slightly longer and weaker than W–O bonds (33), more thiolated W species might be isotopically lighter. Indeed, the δ186/184W of the euxinic porewater (+0.301 ± 0.059 ‰; 2SD; n = 6) is resolvably lower than the δ186/184W of the weakly euxinic water column (Fig. 2). However, relatively constant porewater δ186/184W values at highly variable porewater H2S(aq) concentrations and variable abundances of different WOxS4−x2− species argue against this hypothesis (SI Appendix, Fig. S2). Alternatively, the partial diagenetic release of isotopically light W that was previously adsorbed onto Mn-oxides could cause relatively lower porewater δ186/184W values. This assumption is consistent with strong authigenic Mn and W enrichments in modern sediments from the Landsort Deep (3). The strong gradient between the W concentration of the uppermost porewaters and the deeper water column suggests the release of isotopically lighter porewater W back into the water column. Thus, the constant and intermediate δ186/184W of basinal deep waters might reflect a zone of chemical equilibrium between isotopically lighter porewaters and isotopically heavier oxic seawater.

Summary and Implications.

Relative to a clearly defined homogenous open ocean δ186/184W value of +0.543 ± 0.046 ‰, seawater from more restricted basins in the vicinity of continents can exhibit larger variation in dissolved W concentrations and δ186/184W (Fig. 4). For example, Western Pacific seawater from the South China Sea shows lower δ186/184W in surface waters that are influenced by river discharge. The large internal variation in Baltic seawater δ186/184W values is most likely related to W scavenging by Mn-oxides in redox stratified basins (e.g., Landsort Deep) and the limited water exchange with the open ocean. As such, the preferential scavenging of isotopically light W by Mn-oxides causes lower δ186/184W in suspended particles, in euxinic deep waters where these particles are redissolved, and in the sediment porewaters. In contrast, residual seawater from the upper oxic water column of the Landsort Deep exhibits higher δ186/184W than the open ocean (Fig. 4). Thus, globally high seawater δ186/184W is likely a result of the preferential scavenging of isotopically light W onto oxide minerals such as Mn-oxides [Figs. 3 and 4 and SI Appendix, Fig. S3 (7)]. In times of reduced Mn-oxide mineral formation (e.g., the predominantly anoxic Archean), seawater δ186/184W as well as the δ186/184W of authigenic sediments such as carbonates or iron formations may have been significantly lower (mass balance constraints in SI Appendix, Fig. S3). Such a relationship has already been demonstrated for other redox-sensitive transition metals, which have an affinity to Mn-oxides (34, 35). For example, the preferential adsorption of isotopically light Mo onto Mn-oxides is the main cause for the modern isotopically heavy seawater inventory of Mo (15, 18). However, nonquantitative scavenging of Mo in euxinic settings can additionally fractionate Mo isotopes and also influence the seawater Mo isotope composition in the same direction (21). Increasing δ98/95Mo in sediments that might capture the seawater Mo isotope composition could therefore reflect enhanced burial of Mn-oxide minerals in oxic marine settings or the relative extension of euxinic conditions. In contrast to Mo, W is more soluble in euxinic settings (3, 10). Thus, the stable W isotope composition of seawater is expected to be independent of the global extension of euxinic conditions but more intimately linked to Mn-oxide formation in oxic marine settings. We also note that WO42− has a relatively stronger affinity to Mn-oxides than MoO42− (11), causing a distinctly lower Mo/Wmolar ratio in ferromanganese crusts (∼7) than in seawater [∼1,800 (1)]. Consistently, the particulate fraction from the water column of the Landsort Deep exhibits a strong covariation between Mn and W contents (r2 = 0.97) but lacks a similarly clear covariation between Mn and Mo contents (r2 = 0.51; SI Appendix, Fig. S4 and Dataset S3). Thus, Mn-oxide formation in well-oxygenated marine environments has a particularly strong control on the inventory and isotope composition of marine W.

Fig. 4.

Fig. 4.

Graph illustrating W concentrations and stable W isotope compositions of dissolved and particulate compounds. The open ocean (black squares: Southern Atlantic; black circles: South China Sea) shows relatively homogeneous W concentrations and δ186/184W. Larger variation in the δ186/184W of Baltic seawater from the Landsort Deep is related to preferential adsorption of isotopically light W onto Mn-oxides that form along the redoxcline. Porewaters that are highly enriched in W exhibit lower δ186/184W than seawater, likely due to the diagenetic release of light W associated with Mn-rich sediments. The error bars for samples of this study are smaller than symbol sizes. The yellow circles with larger internal SEs (2SE) indicate Northern Pacific waters (7).

In early Earth history, the oceans were predominantly anoxic, thereby inhibiting Mn-oxide formation. Because Fe-hydroxides already form at lower O2 than Mn-oxides and possibly even in fully anoxic environments via photoautotrophic bacteria (36), the adsorption of WO42− onto Fe-hydroxides might have controlled the marine inventory of W in times of O2 deficiency. In favor of this argument, W (but also Mo) contents in ca. 2.44 Ga old stromatolitic carbonates that were deposited before a major environmental oxygenation event (i.e., the Great Oxidation Event) positively covary with Fe contents (r2 = 0.82; SI Appendix, Fig. S5) but not with Mn contents (37). The enrichment of Fe and siderite formation in stromatolitic carbonates was explained by oxidation of organic compounds via Fe-hydroxides during diagenesis as indicated by a negative correlation between Fe content and δ13CCarb (37). Thus, either organic matter or Fe-hydroxides might have been the carrier phase that caused the authigenic enrichment of W and Mo in these stromatolitic carbonates. In analogy to Mn-oxides, Fe-hydroxides would have preferentially adsorbed isotopically light W and Mo, thereby increasing the δ186/184W and δ98/95Mo of seawater (12, 17). We note, however, that WO42− forms stronger complexations with Fe-hydroxides than MoO42−, causing distinctly larger fractionation during adsorption (12) and a more distinct enrichment of heavy isotopes in seawater. Thus, the stable W isotope composition of authigenic sediments might be a more sensitive tracer for Fe-hydroxide deposition and the earliest and slightest increase of marine oxygen concentrations in early Earth history.

The relationship between seawater δ186/184W and authigenic, chemically precipitated sediments needs to be determined in more detail by future studies in order to constrain whether ancient sedimentary archives really preserve changes in the global seawater δ186/184W. However, authigenic enrichments of marine W in carbonates and iron formations (SI Appendix, Fig. S5) indicate that there is a high potential that the δ186/184W of such chemical sediments help to better reconstruct the evolution of the marine redox state through Earth history. The relatively homogeneous isotopic composition of modern seawater is clearly advantageous for using stable W isotopes as a global paleo-redox proxy. Furthermore, the combination of multiple paleo-redox proxies may allow a particularly detailed understanding of ancient environmental conditions and their evolution through time (2326). For example, enhanced deposition of Mn-oxides in well-oxygenated oceans may have increased the δ98/95Mo and δ186/184W of seawater, while enhanced deposition of Fe-hydroxides in still barely oxygenated oceans may have mainly increased the δ186/184W of seawater. In contrast, the extension of (weakly) euxinic conditions may have raised the δ98/95Mo of seawater while keeping the δ186/184W of seawater unchanged.

Materials and Methods

A detailed description of sampling sites and the sampling procedure can be found in SI Appendix. Tungsten was preconcentrated from its seawater matrix in the clean laboratory facilities of the Institute of Geochemistry and Petrology, ETH Zurich, using an ethylenediaminetriacetic acid chelating resin, sold commercially as Nobias PA1 [Hitachi High Technologies (38)] and using the protocols as described in ref. 39. Briefly, prior to preconcentration, 1 to 2 L of seawater samples acidified to pH 2 were equilibrated for 24 h with an appropriate amount of 180W–183W double spike. The addition of the double spike and sample-spike homogenization prior to preconcentration accounts for kinetic mass-dependent isotope fractionation during chemical purification of W and subsequent mass spectrometric measurement of W isotope abundances (40, 41). Samples were then adjusted to pH 5 ± 0.3 using an ammonium acetate buffer, made up to a final acetic acid concentration of 30 mM, before loading onto the column. Matrix cations, principally Na+, Mg2+, and Ca2+ were eluted with 100 mL of 30 mM ammonium acetate buffer, followed by the elution of W using 30 mL 1 M HNO3. The subsequent chemical separation of W from preconcentrated water samples, filtered particles, and powdered reference materials was carried out at the clean laboratory facilities of the University of Cologne using 18.2 MΩ cm water, distilled acids, and precleaned Savillex PFA labware. An adequate amount of a 180W–183W double spike (41) was added to powdered reference materials and filtered particles prior to dissolution in a concentrated HF–HNO3 mixture (3:1). Dried down sample material was subsequently taken up in concentrated HCl to dissolve potentially formed fluorides. The separation of W comprises a three-step column chemistry (BioRad AG 50 W-X8, 200 to 400 mesh; BioRad AG 1-X8, 100 to 200 mesh; Eichrom TEVA) that is described in detail in SI Appendix, Table S1 and in ref. 41. For preconcentrated water samples, the first column (BioRad AG 50 W-X8, 200 to 400 mesh) was skipped because the abundance of cations was already very low. The setup of the mass spectrometer for W concentration and W isotope measurements (ThermoFisher Scientific© NeptunePlus multicollector inductively coupled plasma mass spectrometer at the University of Cologne) is summarized in SI Appendix, Table S2 and in ref. 41. We present our data in the δ-notation and relative to National Institute of Standards and Technology Standard Reference Material (NIST SRM) 3163 in ‰:

δ186/184W=((W186W184)Sample(W186W184)NISTSRM31631)×1,000. [1]

During measurement sequences, the standard NIST SRM 3163 and an Alfa Aesar reference solution were repeatedly measured. The NIST SRM 3163 has a defined δ186/184W of 0.000 ‰ and a long-term repeatability of ±0.012 ‰ (2SD; n = 192). The Alfa Aesar reference solution is isotopically slightly heavier with an average δ186/184W of +0.055 ‰ and a long-term repeatability of ±0.015 ‰ (2SD; n = 192). SI Appendix, Fig. S6 shows the long-term δ186/184W of NIST SRM 3163 and Alfa Aesar measurements (circles) and their sessional averages (squares) since May 2017. The average isotopic difference between Alfa Aesar and NIST SRM 3163 during 29 different measurement sessions was very constant with Δ186/184W = 0.055 ± 0.009 ‰ (2SD), which is consistent with previous measurement sessions at the University of Tübingen (41). The United States Geological Survey reference material NOD-P-1 was repeatedly measured, also including individual processing through the complete chemical separation procedure. Results for NOD-P-1 (+0.159 ± 0.012 ‰; 2SD; n = 9) are consistent with previous reports for this reference material (41, 42) and indicate a 2SD intermediate precision of ±0.012 ‰ for samples that consist of Mn-oxide–rich suspended particles. We note, however, that the error bars presented in our figures are slightly larger because the long-term repeatability of our in-house standard is with ±0.015 ‰ (2SD) somewhat inferior. The error bars of seawater samples also indicate this long-term repeatability of our in-house standard or the internal error of the measurement (2SE), whichever is larger. Larger internal errors for some seawater samples stem from lower signal intensities during measurements due to lower sample weights. The relative SD (2RSD) of W concentration measurements is ∼5% based on repeated analyses of various reference materials (41). Two procedural blanks of 17 and 24 pg, respectively, indicate a blank contribution of less than 1% of total processed sample W during the processing of filtered particles. The blank contribution to water samples (including preconcentration and subsequent separation of W) was between 132 and 170 pg (n = 3) accounting for less than 1% of total processed W.

Supplementary Material

Supplementary File
Supplementary File
pnas.2023544118.sd01.xlsx (10.4KB, xlsx)
Supplementary File
Supplementary File
Supplementary File
pnas.2023544118.sd04.xlsx (10.1KB, xlsx)
Supplementary File
pnas.2023544118.sd05.xlsx (11.7KB, xlsx)

Acknowledgments

We thank the crews and captains of Research Vessels Elisabeth Mann Borgese, Royal Research Ship James Cook, and Hai Yang 10. We also thank Maeve Lohan and Angela Milne for sample collection along the GA10 South Atlantic section (UK-Geotraces, Natural Environment Research Council Grant No. NE/H004475/1). Furthermore, we acknowledge two anonymous reviewers and the editor for constructive criticism and suggestions that helped improve the manuscript. This study was financially supported by the German Research Foundation (Grant No. KU 3788/1-1) as part of the priority program 1833 “Building a Habitable Earth,” Federal Ministry of Education and Research project Megapol (No. 03F0786A), and the Leibniz Association through Grant SAW-2017-IOW-2 649 (BaltRap).

Footnotes

The authors declare no competing interest.

This article is a PNAS Direct Submission.

This article contains supporting information online at https://www.pnas.org/lookup/suppl/doi:10.1073/pnas.2023544118/-/DCSupplemental.

Data Availability

All study data are included in the article and/or supporting information.

References

  • 1.Sohrin Y., Isshiki K., Kuwamoto T., Nakayama E., Tungsten in north Pacific waters. Mar. Chem. 22, 95–103 (1987). [Google Scholar]
  • 2.Firdaus M. L., Norisuye K., Nakagawa Y., Nakatsuka S., Sohrin Y., Dissolved and labile particulate zr, hf, nb, ta, mo and W in the western North Pacific Ocean. J. Oceanogr. 64, 247–257 (2008). [Google Scholar]
  • 3.Dellwig O., Wegwerth A., Schnetger B., Schulz H., Arz H. W., Dissimilar behaviors of the geochemical twins W and Mo in hypoxic-euxinic marine basins. Earth Sci. Rev. 193, 1–23 (2019). [Google Scholar]
  • 4.Kishida K., Sohrin Y., Okamura K., Ishibashi J.-i., Tungsten enriched in submarine hydrothermal fluids. Earth Planet. Sci. Lett. 222, 819–827 (2004). [Google Scholar]
  • 5.Bauer S., Conrad S., Ingri J., Geochemistry of tungsten and molybdenum during freshwater transport and estuarine mixing. Appl. Geochem. 93, 36–48 (2018). [Google Scholar]
  • 6.Johannesson K. H.; W. B. Lyons; E. Y. Graham; K. A. Welch , Oxyanion concentrations in eastern Sierra Nevada rivers–3. Boron, molybdenum, vanadium, and tungsten. Aquat. Geochem. 6, 19–46 (2000). [Google Scholar]
  • 7.Fujiwara Y., Tsujisaka M., Takano S., Sohrin Y., Determination of the tungsten isotope composition in seawater: The first vertical profile from the western North Pacific Ocean. Chem. Geol. 555, 119835 (2020). [Google Scholar]
  • 8.Kurzweil F., et al., The stable tungsten isotope composition of modern igneous reservoirs. Geochim. Cosmochim. Acta 251, 176–191 (2019). [Google Scholar]
  • 9.Mazza S. E., Stracke A., Gill J. B., Kimura J.-I., Kleine T., Tracing dehydration and melting of the subducted slab with tungsten isotopes in arc lavas. Earth Planet. Sci. Lett. 530, 115942 (2020). [Google Scholar]
  • 10.Mohajerin T. J., Helz G. R., White C. D., Johannesson K. H., Tungsten speciation in sulfidic waters: Determination of thiotungstate formation constants and modeling their distribution in natural waters. Geochim. Cosmochim. Acta 144, 157–172 (2014). [Google Scholar]
  • 11.Kashiwabara T., et al., Tungsten species in natural ferromanganese oxides related to its different behavior from molybdenum in oxic ocean. Geochim. Cosmochim. Acta 106, 364–378 (2013). [Google Scholar]
  • 12.Kashiwabara T., et al., Stable isotope fractionation of tungsten during adsorption on Fe and Mn (oxyhydr) oxides. Geochim. Cosmochim. Acta 204, 52–67 (2017). [Google Scholar]
  • 13.Collier R. W., Molybdenum in the Northeast Pacific Ocean 1. Limnol. Oceanogr. 30, 1351–1354 (1985). [Google Scholar]
  • 14.Nägler T. F., et al., Proposal for an international molybdenum isotope measurement standard and data representation. Geostand. Geoanal. Res. 38, 149–151 (2014). [Google Scholar]
  • 15.Siebert C., Nägler T. F., von Blanckenburg F., Kramers J. D., Molybdenum isotope records as a potential new proxy for paleoceanography. Earth Planet. Sci. Lett. 211, 159–171 (2003). [Google Scholar]
  • 16.Willbold M., Elliott T., Molybdenum isotope variations in magmatic rocks. Chem. Geol. 449, 253–268 (2017). [Google Scholar]
  • 17.Goldberg T., Archer C., Vance D., Poulton S. W., Mo isotope fractionation during adsorption to Fe (oxyhydr) oxides. Geochim. Cosmochim. Acta 73, 6502–6516 (2009). [Google Scholar]
  • 18.Barling J., Anbar A. D., Molybdenum isotope fractionation during adsorption by manganese oxides. Earth Planet. Sci. Lett. 217, 315–329 (2004). [Google Scholar]
  • 19.Erickson B. E., Helz G. R., Molybdenum (VI) speciation in sulfidic waters: Stability and lability of thiomolybdates. Geochim. Cosmochim. Acta 64, 1149–1158 (2000). [Google Scholar]
  • 20.Helz G. R., et al., Mechanism of molybdenum removal from the sea and its concentration in black shales: EXAFS evidence. Geochim. Cosmochim. Acta 60, 3631–3642 (1996). [Google Scholar]
  • 21.Neubert N., Nägler T. F., Böttcher M. E., Sulfidity controls molybdenum isotope fractionation into euxinic sediments: Evidence from the modern Black Sea. Geology 36, 775–778 (2008). [Google Scholar]
  • 22.Wegwerth A., et al., Redox evolution during Eemian and Holocene sapropel formation in the Black Sea. Palaeogeogr. Palaeoclimatol. Palaeoecol. 489, 249–260 (2018). [Google Scholar]
  • 23.Brüske A., et al., Correlated molybdenum and uranium isotope signatures in modern anoxic sediments: Implications for their use as paleo-redox proxy. Geochim. Cosmochim. Acta 270, 449–474 (2020). [Google Scholar]
  • 24.Lu X., Dahl T. W., Zheng W., Wang S., Kendall B., Estimating ancient seawater isotope compositions and global ocean redox conditions by coupling the molybdenum and uranium isotope systems of euxinic organic-rich mudrocks. Geochim. Cosmochim. Acta 290, 76–103 (2020). [Google Scholar]
  • 25.Kendall B., et al., Uranium and molybdenum isotope evidence for an episode of widespread ocean oxygenation during the late Ediacaran Period. Geochim. Cosmochim. Acta 156, 173–193 (2015). [Google Scholar]
  • 26.Ostrander C. M., et al., Fully oxygenated water columns over continental shelves before the Great Oxidation Event. Nat. Geosci. 12, 186–191 (2019). [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 27.Wu Q., et al., New insights into hydrological exchange between the South China Sea and the Western Pacific Ocean based on the Nd isotopic composition of seawater. Deep Sea Res. Part II Top. Stud. Oceanogr. 122, 25–40 (2015). [Google Scholar]
  • 28.Dellwig O., et al., A new particulate Mn–Fe–P-shuttle at the redoxcline of anoxic basins. Geochim. Cosmochim. Acta 74, 7100–7115 (2010). [Google Scholar]
  • 29.Dellwig O., Schnetger B., Brumsack H.-J., Grossart H.-P., Umlauf L., Dissolved reactive manganese at pelagic redoxclines (part II): Hydrodynamic conditions for accumulation. J. Mar. Syst. 90, 31–41 (2012). [Google Scholar]
  • 30.Bauer S., Blomqvist S., Ingri J., Distribution of dissolved and suspended particulate molybdenum, vanadium, and tungsten in the Baltic Sea. Mar. Chem. 196, 135–147 (2017). [Google Scholar]
  • 31.Glockzin M., Pollehne F., Dellwig O., Stationary sinking velocity of authigenic manganese oxides at pelagic redoxclines. Mar. Chem. 160, 67–74 (2014). [Google Scholar]
  • 32.Cui M., Mohajerin T. J., Adebayo S., Datta S., Johannesson K. H., Investigation of tungstate thiolation reaction kinetics and sedimentary molybdenum/tungsten enrichments: Implication for tungsten speciation in sulfidic waters and possible applications for paleoredox studies. Geochim. Cosmochim. Acta 287, 277–295 (2020). [Google Scholar]
  • 33.Schauble E. A., Applying stable isotope fractionation theory to new systems. Rev. Mineral. Geochem. 55, 65–111 (2004). [Google Scholar]
  • 34.Planavsky N. J., et al., Evidence for oxygenic photosynthesis half a billion years before the Great oxidation Event. Nat. Geosci. 7, 283–286 (2014). [Google Scholar]
  • 35.Kurzweil F., Wille M., Gantert N., Beukes N. J., Schoenberg R., Manganese oxide shuttling in pre-GOE oceans–evidence from molybdenum and iron isotopes. Earth Planet. Sci. Lett. 452, 69–78 (2016). [Google Scholar]
  • 36.Kappler A., Newman D. K., Formation of Fe (III)-minerals by Fe (II)-oxidizing photoautotrophic bacteria. Geochim. Cosmochim. Acta 68, 1217–1226 (2004). [Google Scholar]
  • 37.Schier K., Bau M., Muenker C., Beukes N., Viehmann S., Trace element and Nd isotope composition of shallow seawater prior to the Great Oxidation Event: Evidence from stromatolitic bioherms in the Paleoproterozoic Rooinekke and Nelani formations, South Africa. Precambrian Res. 315, 92–102 (2018). [Google Scholar]
  • 38.Sohrin Y., et al., Multielemental determination of GEOTRACES key trace metals in seawater by ICPMS after preconcentration using an ethylenediaminetriacetic acid chelating resin. Anal. Chem. 80, 6267–6273 (2008). [DOI] [PubMed] [Google Scholar]
  • 39.Archer C., Vance D., Milne A., Lohan M. C., The oceanic biogeochemistry of nickel and its isotopes: New data from the South Atlantic and the Southern Ocean biogeochemical divide. Earth Planet. Sci. Lett. 535, 116118 (2020). [Google Scholar]
  • 40.Rudge J. F., Reynolds B. C., Bourdon B., The double spike toolbox. Chem. Geol. 265, 420–431 (2009). [Google Scholar]
  • 41.Kurzweil F., Münker C., Tusch J., Schoenberg R., Accurate stable tungsten isotope measurements of natural samples using a 180W-183W double-spike. Chem. Geol. 476, 407–417 (2018). [Google Scholar]
  • 42.Tsujisaka M., Takano S., Murayama M., Sohrin Y., Precise analysis of the concentrations and isotopic compositions of molybdenum and tungsten in geochemical reference materials. Anal. Chim. Acta 1091, 146–159 (2019). [DOI] [PubMed] [Google Scholar]
  • 43.Kurzweil F., Münker C., Hoffmann J. E., Tusch J., Schoenberg R., Stable W isotope evidence for redistribution of homogeneous W-182 anomalies in SW Greenland. Geochem. Perspect. Lett. 14, 53–57 (2020). [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials

Supplementary File
Supplementary File
pnas.2023544118.sd01.xlsx (10.4KB, xlsx)
Supplementary File
Supplementary File
Supplementary File
pnas.2023544118.sd04.xlsx (10.1KB, xlsx)
Supplementary File
pnas.2023544118.sd05.xlsx (11.7KB, xlsx)

Data Availability Statement

All study data are included in the article and/or supporting information.


Articles from Proceedings of the National Academy of Sciences of the United States of America are provided here courtesy of National Academy of Sciences

RESOURCES