Oceanic iron inputs must be traced and quantified to learn how they affect primary productivity and climate. Chemical reduction of iron in continental margin sediments provides a substantial dissolved flux to the oceans, which is isotopically lighter than the crust, and so may be distinguished in seawater from other sources, such as wind-blown dust. However, heavy iron isotopes measured in seawater have recently led to the proposition of another source of dissolved iron from ‘non-reductive’ dissolution of continental margins. Here we present the first pore water iron isotope data from a passive-tectonic and semi-arid ocean margin (South Africa), which reveals a smaller and isotopically heavier flux of dissolved iron to seawater than active-tectonic and dysoxic continental margins. These data provide in situ evidence of non-reductive iron dissolution from a continental margin, and further show that geological and hydro-climatic factors may affect the amount and isotopic composition of iron entering the ocean.
Iron (Fe) inputs to the surface ocean may stimulate photosynthesis and have an impact on the uptake of carbon dioxide in the ocean on glacial to inter-glacial timescales of climate change1. Global ocean reservoir-flux models2 indicate that 90% of Fe used by marine phytoplankton in the present day surface ocean is supplied from the deep water below, but the sources of dissolved Fe to this deep water are still poorly constrained. Therefore, quantifying and tracking iron supplied to the ocean will provide key information to resolve climate models and sensitivity to the Fe cycle3,4.
Measurable differences in the isotopic composition of Fe between various sources to the ocean have prompted widespread interest in seawater Fe isotope determintions5,6,7, which can potentially be used to track Fe inputs and assess the relative importance of different sources of dissolved Fe to the oceanic reservoir. Microbial sediment respiration supports a major flux of dissolved and isotopically light Fe to the global ocean8,9,10, by catalysing the reductive dissolution (RD) of Fe oxyhydroxide minerals during organic matter decomposition11. Reduction of Fe oxyhydroxide enriches soluble Fe(II)(aq) in sediment pore water, which diffuses into bottom water when the oxygenated layer of surface sediment is adequately shallow9,12, most notably from oxygen-deficient continental margins8,9,10. Benthic fluxes of Fe are mixed in bottom waters and can be transported to open ocean and surface waters13,14, where Fe may control the efficacy of the biological carbon pump15,16.
Dissolved Fe(II)(aq) produced by RD initially has δ56Fe values 0.5–2.0‰ lighter than the original substrates17, and at isotopic equilibrium, experiments show δ56Fe(II)(aq) is −1.05 to −3.99‰ relative to the common reactive Fe oxides haematite17, goethite18 and ferrihydrite17,19,20. Similar light δ56Fe values (−1.82 to −3.45‰) have been observed in both the pore waters21,22,23 and overlying seawater9,24 of river-dominated and dysoxic margins, and light Fe isotopic compositions are recorded in ocean basin sediments coeval with past episodes of ocean oxygen deficiency, consistent with seawater transport of light Fe from ferruginous shelf sediments to ocean basins25. Thus, benthic fluxes of isotopically light Fe appear to be distinguishable from other sources of Fe to the ocean, such as atmospheric dust dissolution (δ56Fe=+0.13±0.18‰)26 and river discharge (δ56Fe=+0.14±0.28‰)27.
Paradoxically, however, equatorial Pacific seawater originating from the continental margin of New Guinea contains elevated Fe concentrations with heavy Fe isotopic compositions (δ56Fe=+0.37±0.15‰)28. These and other seawater isotope measurements have led to the proposition of an additional ‘non-reductive dissolution’ (NRD) mechanism for Fe28,29, albeit with existing Fe isotope evidence from continental margin sediments indicating otherwise9,24. These findings coincide with a growing need to evaluate the geographical variability of benthic Fe fluxes to effectively model carbon cycling in the ocean3,4, where models presently rely on global extrapolations from potentially unrepresentative regions.
Here we characterise the pore water isotopic composition and corresponding flux of dissolved Fe from the Cape margin, South Africa—a semi-arid passive margin derived from deeply weathered saprolite soils and surrounded by oxygenated South Atlantic seawater. These sites are distinct from most previous sites of benthic Fe flux investigation, which have focused on active margins next to areas of rapid uplift with oxygen-deficient shelf waters (Fig. 1). This study reveals that the amount of dissolved Fe released from the Cape margin is less than predicted by benthic Fe flux relationships8 widely used to model ocean Fe–CO2 interaction3,4. We report solid-phase compositional data that suggests that the small pore water Fe flux reflects geological and hydro-climatic influences on reactive Fe substrate delivery to the shelf. Isotopically heavy Fe present in ‘oxidizing’ pore waters of the Cape margin—a zone previously beyond analytical resolution—provides in situ evidence for the role of ‘NRD’ of Fe proposed by Radic et al.28 These discoveries have implications for past and present oceanic Fe cycles and the parameterization of ocean biogeochemical models.
Cape margin sediments originate from Palaeozoic sedimentary sequences of the Cape Supergroup (quartz arenites, subgreywackes, shales and sandstones) that were formed by weathering of ancient Kalahari, Patagonia and Río de la Plata Cratons and deposited along rifted margins of Southern Gondowanda ~480–300 Ma 30(ref. 30). The modern Berg and Olifants Rivers drain the Cape Supergroup and outflow 100–200 km north of our study area, slowly delivering mature siliciclastic material to the Cape shelf (<3 cm kyr−1) (ref. 31), where shelf deposits have been further re-worked by Neogene sea-level fluctuations32. Consequently, winnowed glauconitic sands and quartzose muddy sands occupy the outer shelf and upper-shelf slope31, from where we collected surface sediments from three sites at 733, 1,182 and 2,602 m water depth (Fig. 1). South Atlantic water masses intersecting the sample sites are replete with oxygen, with a small oxygen minimum (174 μmol l−1) associated with Upper Circumpolar Deep Water intersecting the 1,182 m study site.
Cape margin sediment composition
The presence of quartz, plagioclase and K-feldspars, calcite and clay fractions of illite and glauconite were confirmed by XRD and scanning electron microscopy (SEM) analyses. Iron was often associated with Ti and O as illmenite minerals, whereas Fe-S phases were not identified by XRD or energy-dispersive X-ray spectroscopy (EDS) point analysis. The Cape margin sediments contained substantially fewer reducible Fe oxide minerals (FeHR) than have been observed in river-dominated margin sediments from around the world (Fig. 2; Table 1). Furthermore, total Fe in Cape margin sediments largely reflects the average crustal abundance in contrast to areas influenced by river discharge or dysoxic ocean waters that are typically enriched above crustal Fe concentrations and therefore have a more replete Fe reservoir for dissolution processes. Thus, Cape margin sediments provide a previously missing case study to link earth surface processes with the nature of seawater Fe supply from the continents.
Cape margin pore water composition
The upper-shelf slope of the Cape margin (733, 1,182 and 2,602 m water depth) contains sufficient organic carbon (means 2.2, 1.7 and 1.4 wt%; 0–20 cm) to consume dissolved O2 within just a few millimetres of the sediment–water interface (Fig. 3; Table 1). Subsequent down-core chemical zonations of dissolved NO3−, Mn and Fe in the pore water are consistent with control by organic matter decomposition (Fig. 3). Sub-surface dissolved Fe maxima (between 3 and 6 μmol l−1) are clearly identified in what have been termed ‘ferruginous’ zones between relatively ‘oxidizing’ (O2 and NO3− in the pore water) and ‘sulphidic’ (Fe depletion consistent with SO4− reduction33) zones. However, dissolved Fe values remain 10–100 times lower than pore waters from California8,9,12,21,23, Oregon9,12,21 and Peru10 margins, where previous benthic Fe flux investigations have been focused. The speciation of dissolved Fe in the sampled pore water is not known, but the near-surface abundance of electron acceptors means dissolved Fe in the oxidizing zone may be present as either Fe(II)(aq) colloidal oxyhydroxides34 or organic complexes.
Cape margin iron isotope signatures
We observe a wide range in the Fe isotopic composition of Cape margin pore waters (δ56Fe=−3.09 to +1.22‰ relative to IRMM-14), but with distinct and reproducible down-core behaviour between sulphidic, ferruginous and oxidizing zones in the sediments (Fig. 3; Table 1). We find δ56Fe of the bulk solid phase to be +0.08±0.2‰ (n=11), equal to the average weathering product of the continental crust (+0.09±0.7‰) described by previous workers36. Relatively heavy ‘sulphidic’ zone pore water Fe isotopes at depth in these sediments are consistent with control by low-solubility sulphide minerals observed elsewhere21, and supported by experimental studies of pyrite formation, in which pore water Fe(II)(aq) may reach +1.3‰ when not in equilibrium with the solid phase37. We observe the lightest Fe isotopic compositions (−0.34 to −3.09‰) in the ferruginous zone at each study site, which is characteristic of microbially catalysed RD seen in marine sediments elsewhere9,21,23 and supported by incubation experiements17,20. However, the isotopic composition of Fe in the most oxidizing layer of surface sediments shows a systematic and previously unidentified transition towards heavier, near-crustal values at the sediment–water interface.
The pore water Fe isotopic concentration variations that we observe could not have been generated by oxidation or sorption of the reduced Fe pool, and nor could they be oxidation-related sampling artifacts. Precipitation of Fe(II)(aq) by oxidation and/or sorption has a kinetic isotope effect that lowers the residual δ56Fe(II)(aq)17 (ref. 17). We hypothesize that the near-surface transition to heavier Fe isotopic compositions reflects mixing with a heavier end-member Fe input, which is only discernable because of the very low abundance of dissolved Fe supplied by RD at these sites compared with previous continental margin studies (Fig. 4).
Potential sources of heavy Fe isotopes include dissolution of sulphide, oxide and silicate minerals. The equilibrium isotopic fractionation between Fe(II)(aq) and FeS(s) has been experimentally determined (−0.32±0.29‰)37, but previous field observations of Fe(II)(aq) in the presence of FeS(s) have been restricted below the ferruginous zone21, where pore waters do not reflect equilibrium conditions37. In surface sediments, FeS(s) is commonly unstable and readily forms Fe oxyhydroxide minerals38. Multiple solid-phase spectroscopic analyses did not identify any FeS or FeS2 minerals in the oxidizing surface layer of the Cape margin study sites. Therefore, any Fe-S minerals physically entrained in the surface layers have probably already contributed to the authigenic pool of reactive Fe oxide minerals.
Isotopically heavy Fe in pore water Fe could be attributed to an equilibrium isotopic effect during NRD of oxide and/or silicate weathering products on the Cape margin; for example, the isotopic composition of Fe in oxidizing pore waters is also heavy (+0.16±0.05‰)23 in deep-sea volcanogenic turbidites, where dissolved Fe is dominated by colloids formed by inorganic dissolution of volcanic minerals34. Other disparate lines of evidence exist for a common equilibrium isotopic effect; first, dissolved Fe released to seawater from atmospheric dust is heavy (δ56Fe of +0.13±0.18‰)26, and confirmed beneath Saharan dust plumes in the North Atlantic where elevated surface ocean Fe concentrations have a δ56Fe of +0.33±0.05‰39 (ref. 39); second, dissolved Fe in river water is heavy (δ56Fe of +0.14±0.28‰)27 and persevered through the estuarine mixing zone despite intense removal during flocculation, indicative of isotopic equilibration with suspended solids; and finally, dissolved Fe in New Guinea coastal waters influenced by sediment re-suspension has a δ56Fe of 0.37±0.15‰, 0.2‰ heavier than the suspended particles28. The remarkable consistency in dissolved Fe isotopic compositions across a diverse set of oxygenated sediment–seawater interactions is used here to predict the mean isotopic fingerprint of dissolved Fe released by NRD at our study sites (mean δ56Fe=+0.22±0.18‰), and we find this consistent with the predictions of Radic et al.28
We consider the amount of Fe in surface sediment pore waters that may originate from NRD on the Cape margin using the estimated end-member isotopic composition of dissolved Fe supplied by reductive and NRD processes. We derive isotope-mixing lines in Fig. 4 with a standard two-component mixing calculation, where the slope (a) and intercept (b) describe the relationship between δ56Fe and [Fe] in equation (1). Equations (2) and (3) define terms a and b, where the two end-member isotopic compositions and their respective concentrations in the pore water are set by reasoned constraints from the literature and values befitting to the Cape margin data set;
Fe supplied by RD (FeRD) is defined as having δ56FeRD=−3.0‰ (17,20), and a hypothetical concentration of 1.75 μmol l−1, whereas δ56FeNRD=0.22±0.18‰. When [FeNRD] is set between 0.07 and 0.6 μmol l−1 in the surface sediment (a majority of the observed pore water [Fe]), these parameters provide two mixing lines (Fig. 4), which approximate the observed relationship between δ56Fe and [Fe] between ferruginous and oxidizing zones on the Cape margin. Pore water Fe isotopic data and the implied mechanism of pore water Fe supply have implications for the isotopic composition and flux of Fe from the Cape margin, as well as the geographical distribution and isotopic diversity of Fe supply to the global ocean.
Iron supply from the Cape margin
A one-dimensional diffusion-oxidation calculation using pore water Fe and O2 concentration data40 has previously been used to estimate the benthic flux of Fe from sites on the California and Oregon shelves, where it was validated by direct field comparison with in situ and ex situ incubation techniques12. We use the same approach to estimate the benthic flux of Fe to bottom waters from the Cape margin. The flux (mol cm−2 s−1) of Fe2+ (J) is described in equation (4), where ϕ is the sediment porosity, L is the thickness (cm) of the oxygenated layer of surface sediment and Cp is the concentration (g cm−3) of Fe2+ in the pore water beneath L.
The rate constant for Fe2+ oxidation is described by k1 (s−1) in equation (5), as a function of bottom water O2 concentration (mol kg−1), pH and the value of k (3.54 × 10−1 kg mol−1 s−1) derived from the relationships between temperature (6 °C) and salinity (34) with Fe2+ oxidation in seawater41.
The diffusion coefficient42 of Fe2+ in muddy shelf sediment pore waters (cm2 s−1) is described in equation (6), as a function of ϕ, corrected for tortuosity, and temperature T (°C).
We use a ϕ value of 0.77 determined by Multi-Scan Core Logging of archived sediment cores at the National Oceanography Centre (NOC), and in the absence of direct determination, pore water pH is assumed to be 7.5±0.1 (ref. 12). Bottom water [O2] is derived from shipboard Winkler titrations of near-bottom water samples of 201 and 174 μmol l−1 at 733 and 1,182 m, respectively. Values of L are derived from O2 microsensor determinations from sites 733 and 1,182 m of 1.05 and 0.62 cm, respectively, and we use a depth-corrected pore water [Fe] beneath L to derive corresponding Cp values of 0.84 and 0.24 μmol l−1. The calculated fluxes of Fe to bottom water from the 733 and 1,182 m Cape margin sites are 0.11±0.13 and 0.23±0.17 μmol m−2 d−1, respectively.
We find values of benthic Fe flux to be 2–4 orders of magnitude smaller than widely cited and most recent constraints from active-tectonic and dysoxic continental margins8,9,10,43. Furthermore, the flux of Fe is substantially lower than predicted by the application of the Elrod et al.8 relationship to organic C oxidation rate; Elrod et al.8 show that benthic Fe fluxes correlate with rates of organic C oxidation for numerous sites along the California margin, and the relationship is used to extrapolate benthic fluxes of Fe from organic C fluxes for ocean biogeochemical models3,4. Using a one-dimensional steady-state O2 diffusion-consumption model, we approximate the rate of organic C oxidation by fitting calculated outputs to the observed down-core profiles of O2 concentration determined by microsensors (Fig. 5). The approach follows Berner44, in which a single pool of reactive organic C is assumed to be the only mechanism of O2 utilization (for example Papadimitriou et al.45), and the influence of biophysical mixing, seasonal accumulation rates and porosity structure are ignored. The rates of organic C oxidation for sites 733 and 1,182 m (3.5 and 5.1 mmol m−2 d−1) are derived from the modelled flux of O2 and the stoichiometry of organic matter remineralization, and are equivalent to rates of organic matter decomposition from previous sites of benthic Fe flux determination8. Following Elrod et al.8, we predict a benthic Fe flux of 2.4–3.5 μmol m−2 d−1 from the Cape margin (Fig. 5), and find this an order of magnitude more than we calculate from pore water Fe data. Thus, Cape margin sediments appear to deviate from the relationship between sediment respiration and benthic Fe supply rates observed on North American river-dominated and dysoxic margins of the Pacific Ocean.
Cape margin sediments indicate that the supply of Fe to the southeast Atlantic Ocean is smaller and isotopically heavier than current models of Fe cycling would suggest8,9,24 (Fig. 6). Both of these findings have widespread implications for the marine Fe cycle. It appears that the relationship proposed by Elrod et al.8, which for a decade has provided the most widely used constraint on the benthic flux of Fe to the global oceans, may overestimate benthic Fe flux from margin sediments with lower reactive Fe inventories or less-effective mechanisms for Fe enrichment.
Continental margin sediments are a reservoir for reactive iron mineral substrates, which supply dissolved Fe to the oceans and thereby support ocean life. Globally, rivers provide three quarters of the particulate Fe content of continental margins46, where on average sediments comprise 1 wt% highly reactive Fe oxides (FeHR)47. Tectonic uplift enhances sediment transport to the ocean from active orogenic belts due to many factors (fractured and brecciated rocks, over-steepened slopes and seismic and volcanic activity) in addition to elevation/relief48. Hydro-climatic conditions provide a second-order influence on sediment transport to the oceans48,49, where continental run-off intensity increases the FeHR enrichment of sediment carried by rivers47. For example, Indian margin sediments record monsoon intensity with enrichments of FeHR and total Fe (FeT) to Al ratios nearly double the continental average on decadal timescales50,51. Therefore, tectonics and climate are effective ways to mediate the supply and enrichment of FeHR at ocean margins.
The Cape margin is depleted in FeHR (0.17 wt%, 0–20 cm) compared with the global average of continental margins47 (Fig. 2). Prolonged tectonic stability in this region and a semi-arid climate have probably contributed to the relatively slow rate of sediment accumulation31—perhaps allowing the rate of FeHR reduction and dissolution to meet or exceed the rate of FeHR supply and produce the low FeHR content observed. We consider the limited abundance of reactive Fe oxide minerals as the most likely means of restricting the flux of dissolved Fe to seawater in this region. Thus, shifting patterns in tectonic and hydro-climatic conditions might have influenced the Fe inventory of margin sediments in the past, with unknown impact on regional and global inputs of dissolved Fe to seawater.
The limited amount of RD on the Cape margin reveals the co-existence of a NRD process, releasing Fe in the oxidizing layer of surface sediments. The discovery is consistent with predictions based on seawater isotopic compositions of Fe and Nd measured elsewehere28,52. Dissolution rates may be slower than microbially catalysed RD, but the process could be widespread. Non-reductive Fe dissolution is likely to reflect physical and compositional variations in sediments influenced by geological provenance and weathering rates, as indicated by the high abundance of Fe in oxidizing volcanic sediments around the Crozet Islands (Fig. 4). Using a sediment respiration parameter to estimate Fe supply from marine sediments is unlikely to account for the distribution and magnitude of Fe released by NRD of marine sediment. Readily weathered volcanic and oxygenated sediments are prevalent across ocean basins34, and dilute sediment suspensions can be transported hundreds of kilometres offshore where they influence primary production13,53, so multiple mechanisms for Fe dissolution may have a far-reaching influence on seawater isotopic compositions and productivity.
Cape margin Fe isotopic data remain consistent with interpretations of isotopically light Fe in modern marine and ancient sediment records25,54 in which anoxic seawater is suggested to shuttle isotopically light Fe from ferruginous margin sediments to ocean basins. However, the measured or inferred absence of light Fe isotopic compositions in seawater would be a poor assessment of the oceanic Fe inventory and its impact on primary productivity, given that we now need to consider the variables of non-reductive Fe dissolution.
Cape margin sediments shed light on Fe exchange between a semi-arid tectonically passive continental margin and oxygenated ocean. The sediments host distinct mechanisms of Fe dissolution, resulting in a smaller, isotopically heavier input to seawater than predicted. Semi-arid passive margin environments are common, and their distribution varies over time, thus requiring appraisal when reconstructing past ocean conditions. In addition to the distribution of ocean anoxia, we predict that the proportion of dissolved Fe supplied to the ocean by reductive and non-reductive sediment dissolution will reflect patterns in continental weathering and transport to ocean margins. Slow rates of reactive Fe substrate delivery to ocean margins may limit the benthic flux of Fe by RD relative to organic C oxidation rates. In addition, young volcanic terrains that are easily weathered are likely to release greater amounts of Fe by NRD compared with the mature sediment lithologies of the Cape margin. Regional constraints on oceanic Fe supply are missing links for modelling the coupled ocean-atmosphere carbon cycle3,4. Therefore, evaluating Fe supply from additional and diverse ocean boundaries remains an essential goal for modelling climate.
Sediment and pore water sampling
A Bowers and Connelly Megacore and Box core sampled shallow (<0.4 m) sediment and pore water from three sites on the Cape margin (733, 1,182 and 2,602 m; Fig.1, Table 1) during the UK GEOTRACES A10 expedition from the RRS Discovery (D357) in October–November 2010. Sub-samples for oxygen profiling and pore water extraction were collected by polycarbonate push core, and shipboard processing was performed at ambient bottom water temperatures.
Rhizon samplers collected dissolved pore water and overlying seawater constituents for elemental analysis (filtration cut-off of 0.15 μm). Rhizon samplers (50 × 2.5 mm) were pre-soaked in 18.2 MΩ de-ionized water and inserted through pre-drilled holes in core tubes at 1–3 cm intervals down-core. A ‘BD Discardit’ 20 ml syringe (pre-cleaned: 72 h 10% Decon; 72 h 6 M HCl; 72 h 6 M HNO3; rinsed by 18.2 MΩ de-ionized water) and secured to each Rhizon by Luer-lock connection. A brace inserted between each syringe housing and plunger applied suction to Rhizons. The first 0.5 ml of sample was discarded. Rhizons drew ~6 ml of pore water (10–20 min) and were divided for macronutrient and metal analysis. The aliquot for metals was acidified (pH<2) directly through the syringe tip (6 μl of 6 M quartz-distilled (Q-)HCl per ml of pore water) and transferred to low-density polyethylene (LDPE) pots. Residual sediments were divided for elemental analyses by extruding and slicing cores with a Teflon sheet at 1–2 cm depth intervals. Sediments were later freeze-dried and homogenized by agate pestle and mortar.
Sediment digestion and leaching procedures
Heated Aqua Regia and combined HF-HClO4 acid dissolved sediment samples following an established protocol at the NOC in Southampton34. Digested sediment residues were re-dissolved in 6 M HNO3 in preparation for analysis by Inductively Coupled Plasma-Mass Spectrometry (ICP-MS). Digestion of the certified standards SCO-1, SGR-1 (United States Geological Survey) and BCSS-1 (National Research Council Canada) allowed for the recovery of Fe, Mn and Al within consensus values (Table 2).
Highly reactive Fe (FeHR) is operationally defined as Fe liberated by dissolution during a 2-h reaction with Na dithionite designed to target reducible Fe oxide phases (for example, ferrihydrite, lepidocrosite, goethite and haematite)55. A 10 ml aliquot of 50 g l−1 Na-dithionite solution buffered to pH 4.8 with 0.35 M acetic acid and 0.2 M Na citrate was reacted at room temperature with ~100 mg of dry sediment sample. The resultant solution was spun for 8 min by centrifuge at 9,000 g. Supernatant containing dissolved Fe was decanted into LDPE before analysis by ICP-MS.
Element abundance by ICP-MS
A Perkin Elmer Element X2 ICP-MS measured the concentration of Fe and Mn in pore water, and Fe and Al in sediment solutions at the NOC. Sediment digests were diluted 1,000 times, and pore water samples 100 times, with a 0.48 M Q-HNO3 solution containing 2 ng g−1 Re, Rh and Sc and 5 ng g−1 Be as internal standards. External calibration standards were prepared from certified stock solutions. For dilute pore water analyses, standards were matrix matched with 1% seawater (NASS-5; National Research Council Canada), effectively adding a small known amount of Fe (35 pmol l−1) and Mn (160 pmol l−1) to the standards that is corrected for during external calibration.
Samples were introduced by an Elemental Scientific SC-4 DX Autosampler and PC3 Peltier cooled inlet system with integrated cyclonic spray chamber at 100 μl min−1. Masses 56Fe, 55Mn and 27Al were measured in medium resolution mode. Internal standards were monitored throughout and used to correct for the reduction in signal intensity over time. The accuracy of the method was verified by the intermittent analysis of blank-bracketed SLRS-5 within certified values (Table 2), with a relative s.d. <0.5%. The detection limits (3 s.d. of analytical blanks, n=11) for Fe, Mn and Al were 24, 4 and 14 nmol l−1, respectively. Mean procedural blanks (n=4) for pore water sampling and analyses were 85±3.5 nmol l−1 for Fe and below detection for Mn.
Fe isotope determinations by Multi-Collector ICP-MS
The isotopic composition of Fe in pore waters and sediments was assessed using a modification of John and Adkins7. Sample solutions containing 17–115 ng of Fe were quantitatively spiked with a 57Fe–58Fe double spike56 using a spike:sample ratio of 2:1. Spike-sample mixtures were dried in Savillex PFA Teflon vials and re-dissolved with 5 M Q-HCl+0.001% v/v Fisher Scientific Optima. A 135 μl aliquot of acid-cleaned AG-MP1 anion exchange resin was used in LDPE columns (pre-cleaned: 72 h 10% v/v decon, 1 week 6 M HCl) for the separation of Fe from sample matrices. Resin-filled columns were rinsed with 2M Q-HNO3 and conditioned with 5 M Q-HCl+0.001% v/v H2O2 before loading spiked samples in 100 μl aliquots. Loaded columns were rinsed by 12 × 100 μl aliquots of 5 M Q-HCl+0.001% v/v H2O2. Fe was eluted by 800 μl of 1 M Q-HCl into Savillex PFA Teflon vials, dried and re-dissolved in 2 ml of 0.1 M Q-HNO3 before analysis by Multi-Collector (MC) ICP-MS. Column calibrations assessed procedural blanks (2.7±0.6 ng of Fe, n=2) and recovery of Fe (>95%). Calibrations also confirmed the effective separation of Fe from major salts (Ca) and interferences (58Ni and 54Cr).
A Thermo Scientific (Neptune) MC ICP-MS-measured Fe isotope ratios at the University of South Carolina. Samples and standards were introduced by a Teflon PFA nebulizer and an (ESI) Apex-Q desolvating system at 150 μl min−1, with an Al ‘X’ skimmer cone. High-resolution mode resolved Fe from polyatomic interferences (ArN+, ArO+ and ArOH+). Signal intensity was measured for atomic masses 53, 54, 56, 57, 58, 60 and 61, with 53Cr and 60Ni used to correct for isobaric interferences on 54Fe and 58Fe, respectively. Signal intensity was measured over 50 cycles of 4.2 s. The first 12 cycles were discarded due to uptake and stabilization time. Any cycles with ratios more than 3 s.d. of the remaining 38 cycles were also discarded. Memory effects were minimized by a 3-min rinse (0.32 M Q-HNO3) between analyses. All sample intensities were blank-corrected with the mean of 38 cycles from periodic 0.1 M HNO3 analyses. Fe isotope ratios were calculated using a double-spike data-reduction scheme based on the iterative approach of Siebert et al.57, and are expressed relative to IRRM-14 using standard delta notation (δ56Fe):
Sample ratios are expressed relative to the average of IRMM-14 standards mixed with the 57Fe–58Fe double spike in equivalent proportions and concentrations as samples. Standard-spike ratios and concentrations were assessed for deviation in IRRM-14 determination but none was found. Each sample was analysed twice, and the average is shown (Table 1). Uncertainty for δ56Fe is expressed as the mean s.e. of the isotope ratio over each 160 s analysis, based on previous demonstration that uncertainty of Fe isotopic measurement of a natural sample by double-spike MC ICP-MS is dominated by internal error56.
Pore water O2 profiling
Unisense equipment was used to for shipboard O2 determination in surface sediments as previously described34. Linear calibrations were performed between aerated seawater and anoxic (N2 saturated) seawater before each use, with a detection limit <0.3 μmol l−1. A micromanipulator and SensorTracePro software controlled down-core profiling at 100 μm depth intervals. Data were converted to dissolved O2 concentration using empirical constraints for O2 saturation in seawater. Pore water profiles are surface-normalized to bottom water O2 determinations from shipboard Winkler titrations.
Pore water NO3 − and NO2 − determination
Pore water samples (2 ml) were diluted with 18.2 MΩ de-ionized water to a volume of 30 ml. A 5-channel Bran and Luebbe AAIII segmented flow colorimetric autoanalyser was used to determine NO3− and NO2− concentration using standard analytical techniques at sea58. Data presented are combined NO3−+NO2−, with an analytical uncertainty of ±0.2 μmol l−1. Accuracy was verified by determination of nutrient standards (Ocean Scientific International) within 5% of certified values.
Sediment mineralogical description
Polarized light microscopy, XRD and SEM with EDS assessed bulk sample mineralogy. A Philips X'Pert pro instrument with Cu-Kα radiation performed XRD. Elemental composition of targeted mineral grains was assessed from EDS generated from a Princeton Gamma Tech (IMIX-PTS) X-ray beam with a 2–3 μm diameter connected to an LEO 1450VP SEM operated at 15 keV.
Sediment organic C determination
Total organic carbon concentrations were calculated from the difference between coulometric determination (UIC 5012 Coulometer) of total carbon (TC) and total inorganic carbon (TIC) content of dry homogenized sediments. TC was calculated from CO2 released during sample combustion, and TIC was calculated from CO2 released during heated sample reaction with 1.5 M H3PO4. Accuracy of TC and TIC determinations was assessed with anhydrous CaCO3 powder, with a mean recovery of 100.4±0.8% (1 s.d., n=15). The limit of detection (3 s.d. of blanks) was <10 μg C, equivalent to <0.03 wt% total organic carbon.
How to cite this article: Homoky, W. B. et al. Distinct iron isotopic signatures and supply from marine sediment dissolution. Nat. Commun. 4:2143 doi: 10.1038/ncomms3143 (2013).
We thank the captain and crew of the RRS Discovery and UK GEOTRACES expedition D357. We are grateful to Y.-T. Hsieh and G.M. Henderson (University of Oxford) for supporting the collection of samples, and E.M.S. Woodward (Plymouth Marine Laboratory) and S. Reynolds (CSIRO Marine and Atmospheric Research) for shipboard analysis of nitrate and bottom water oxygen. J.E. Thompson (University of Southampton) provided valuable assistance leaching and digesting sediment samples. A.J. Milton (University of Southampton) and A.D. Rosenberg (University of South Carolina) provided essential technical support of analyses by ICP-MS and MC ICP-MS, respectively. This work was supported by the UK Natural Environment Research Council (NE/F017197/1 and NE/H004394/1) and the US National Science Foundation (OCE-1131387).
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