In this study, we investigated Ni2+, Zn2+, and Co2+ mineralogical incorporation and its effect on green rust transformation to magnetite. Mineral transformation experiments were conducted by heating green rust suspensions at 85 °C in the presence of Ni2+, Zn2+, or Co2+ under strict anoxic conditions. Transmission electron microscopy and powder X-ray diffraction showed the conversion of hexagonal green rust platelets to fine grained cubic magnetite crystals. The addition of Ni2+, Zn2+, and Co2+ resulted in faster rates of mineral transformation. The conversion of green rust to magnetite was concurrent to significant increases in metal uptake, demonstrating a strong affinity for metal sorption/co-precipitation by magnetite. Dissolution ratio curves showed that Ni2+, Zn2+, and Co2+ cations were incorporated into the mineral structure during magnetite crystal growth. The results indicate that the transformation of green rust to magnetite is accelerated by metal impurities, and that magnetite is a highly effective scavenger of trace metals during mineral transformation. The implications for using diagenetic magnetite from green rust precursors as paleo-proxies of Precambrian ocean chemistry are discussed.
Green rust (GR) minerals are a group of Fe2+/Fe3+layered double hydroxides (LDH) that are known to remove metal cations from solution. The GR crystal structure is composed of brucite-like octahedral sheets that envelop an interlayer of interchangeable anions (e.g. SO42−, CO32−, Cl−). The crystal edges contain reactive octahedral sites that are involved in metal binding  and divalent metal ions such as Ni2+ and Zn2+ are known to integrate into these flexibly charged surface sites [2,3,4]. Because GR minerals are commonly found in iron-rich sediments and anoxic waters [5,6,7] metal sorption by GR particles can play a significant role in contaminant sequestration and trace nutrient cycling [6,7,8,9,10,11,12].
Recently, green rust has been proposed as a mineral precursor of mineral assemblages preserved in Precambrian iron formations [13,14,15]. Green rust readily forms in Archean seawater-analogue solutions, and its precipitation in early oceans is thought to have been a major iron sink. GR has also been observed to precipitate in redox transition zones at Archean ocean analogue sites such as Lake Matano (Indonesia) and Arvadi Spring (Switzerland) [6, 7]. At Lake Matano, GR particles form near the iron redoxcline and persist through the water column at depth . At Arvadi Spring, GR accumulates in sediments as flocs that cover the entire sediment surface . Importantly, GR in these ferruginous environments have been found to sorb metal cations and control trace nutrient availability.
Under O2-free conditions, green rust can spontaneously convert to the more stable Fe2+/Fe3+iron oxide phase magnetite (Fe3O4) [16, 17]. The inverse spinel structure of magnetite is comprised of octahedral sites that are occupied by Fe2+ and Fe3+, and tetrahedral sites that only contain Fe3+. Because the magnetite structure has two times as much Fe3+, it has a lower Fe2+/Fe3+ratio compared to GR. The ideal chemical formula for GR sulfate is Fe42+Fe23+(OH)12SO4·8H2O  such that the Fe2+/Fe3+ ratio is 2, while the Fe2+/Fe3+ ratio for magnetite is 0.5. The anoxic conversion of GR to magnetite involves Fe2+ oxidation by water, where electrons transfer to aqueous H+ ions to produce H2 gas. The kinetics of GR transformation to magnetite is known to dependent on pH, Eh, and temperature . However, little effort has been directed into elucidating the effect of trace metals on anoxic GR transformation even though metal sorption is known to modify GR surface charge and mineral reactivity [2, 3, 20,21,22,23,24]. So far, the effect of Ni2+, Zn2+, and Co2+ sorption on GR transformation to magnetite has not yet been studied.
Here we investigated Ni2+, Zn2+, and Co2+ mineralogical incorporation and its effect on GR conversion to magnetite. The objectives were: (1) to examine the sorption of Ni2+, Zn2+, and Co2+ metal ions during GR transformation to magnetite; (2) to determine the effect of trace metal incorporation on magnetite crystallization; and (3) to characterize the solid-phase distribution of metal cations in the magnetite transformation products. The work presented in this study provide new insights into metal sorption by magnetite during GR transformation, and the results have important implications for early Earth studies that use of magnetite as a paleo-proxy of Precambrian ocean chemistry.
Materials and methods
Green rust sulfate (GR-SO4) was synthesized following the procedure described by Géhin et al. . Briefly, a solution containing 150 mM FeSO4·7H2O and 25 mM Fe2(SO4)3 was prepared using deoxygenated ultra-purified water (milli-Q) and purged with N2 gas for 30 min in a sealed 125 mL reactor vial. A solution of 3 M NaOH was then injected into the reactor via a N2-purged needle and syringe and the mixture was gently shaken. A dark green precipitate formed in the reactor and powder X-ray diffraction analysis confirmed the precipitate was GR-SO4. The Fe concentration of this GR stock suspension was 200 mM and final pH was 6.8. The GR was stable at this pH and no transformation products were detected in the GR stock suspension during storage.
Mineral transformation experiment
GR transformation experiments were conducted by heating GR suspensions at 85 °C under strict anoxic conditions. The temperature of 85 °C was selected to simulate the effects of GR burial and early diagenesis. Experiments were performed with GR suspensions in sealed serum bottles purged with N2 gas. GR suspensions were diluted with deoxygenated water to a final Fe concentration of 20 mM and the sealed serum bottles were then placed in an 85 °C water bath. At periodic intervals, the headspace gas and mineral suspension were sampled with needle and syringe. To remove O2, the needle and syringe were purged with N2 gas multiple times prior to sampling. The concentration of H2 in headspace samples was measured by gas chromatography (GC) using a Supelco GC column connected to a thermal conductivity detector (Model 310, SRI Instruments). GC was also used to analyze O2 to ensure that there was no atmospheric contamination. The pH was measured using a handheld HANNA pH probe in an anaerobic glove box.
To monitor mineral transformation, aliquots from the mineral suspension were collected at periodic intervals and the solids were analyzed using powder X-ray diffraction (XRD) and transmission electron microscopy (TEM). Samples were taken using N2-purged syringes and transferred to seal vials filled with nitrogen gas. For XRD analysis, the sample was centrifuged and the supernatant was removed. The solids were then dried with acetone under nitrogen flow. After adding a drop of glycerol to prevent oxidation, the solids were taken out of the vials using a spatula and transferred onto a glass plate for XRD analysis with a Rigaku MiniFlex 6G XRD equipped with a Co anode (λ = 1.790 Å). The X-ray source operated at 40 kV and 30 mA, scanning from 2 theta values of 1–90 degrees, at a scan speed of 1 degree per minute. For TEM analysis, 5 μL of sample from the vial was taken and the sample was taken deposited on a copper grid coated with carbon (Electron Microscopy Sciences CF-400-Cu) in an anaerobic glovebox (97% nitrogen, 3% hydrogen atmosphere). Excess solution was wicked away using filter paper and samples left to dry on the grid for several minutes. Grids were then transferred to a PELCO TEM Grid Vacuum Desiccator (PELCO Product # 16178) that was then pumped down using a vacuum to prevent sample oxidation. Images were captured using a Philip 420 Electron Microscope at 80 kV and analyzed using ImageJ.
Metal incorporation experiment
Trace metal incorporation during the transformation of GR to magnetite was examined by adding a known amount of Ni, Zn or Co to GR suspensions prior to heating at 85 °C. Stock solutions of the metal ions were prepared by diluting 1000 ppm atomic absorption standards with milli-Q H2O and then titrating the solution with NaOH to a pH of 6.5. The metal solutions were deoxygenated by purging with N2 gas. Metal incorporation experiments were performed by adding either Ni, Zn or Co to anoxic GR suspensions ([Fe] = 20 mM) using N2-purged syringes. The final metal concentration (Ni, Zn or Co) was 1 ppm, corresponding to molar concentrations of 17 µM of Ni, 15 µM of Zn, and 17 µM of Co. These metal concentrations were selected because of their environmental relevance. The sealed serum bottles were gently shaken at room temperature for 2 h. One set of reactors were then transferred to an 85 °C water bath and heated to induce mineral transformation for up to 24 h. Another set of reactors were kept at room temperature as controls. Throughout the first 2 h and during the 85 °C heating period, aliquots of the mineral suspension were collected for analysis. Mineral transformation was tracked using XRD measurements and the dissolved metal concentrations were analyzed using inductively coupled plasma optical emission spectroscopy (ICP-OES). XRD was performed using the methods described above. To determine the dissolved metal concentrations, samples were filtered using 0.2 µm nylon filters into test tubes containing 2% HNO3. The metal concentrations in the acidified filtrates were analyzed using an ICPAP-7400 ICP-OES Duo. The concentrations of Ni, Zn, Co, and Fe were measured at 231.6 nm, 213.9 nm, 228.6 nm, and 261.2 nm wavelengths, respectively.
At the end of each transformation experiment, an acid dissolution assay was performed to examine the distribution of the incorporated metals. The magnetite product formed during heating was collected by centrifugation (2000 rpm, 5 min), and dried with flowing N2 gas for 30 min. The solids were then mixed with 4 M HCl to dissolve the magnetite product and aliquots were sampled at periodic intervals to monitor mineral dissolution and metal release. Complete dissolution of the solids occurred within 1 h of reaction with the acid. Samples were filtered (0.2 µm) and dissolved metal concentrations (Fe, Ni, Zn, Co) were measured using ICP-OES.
Heating GR suspensions at 85 °C under anoxic conditions resulted in the production of H2 gas (Additional file 1: Fig. S1),, a decrease in mineral volume, and the precipitation of a dark magnetic product (Additional file 1: Fig. S2). The solution pH dropped slowly and continuously from pH 6.8 to 6.1 over the 24 h experiment (Additional file 1: Fig. S3). Transmission electron micrographs of the parent GR material showed hexagonal platelets approximately 500 nm in diameter (Fig. 1a), and transformation of this GR material resulted in the formation of electron dense cubic crystals 20–30 nm in size (Fig. 1b). XRD analysis of the transformation products indicate that GR was converted to magnetite (Fig. 1c). The starting material displayed XRD peaks at 9.3° and 18.7° 2-theta angles, corresponding to d-spacings of 11.05 Å and 5.51 Å of the layered double hydroxide GR structure. After heating of the GR suspensions for 30 min, a single interlayer GR reflection 13.67° 2-theta corresponding to a d-spacing of 7.52 Å was observed. The appearance of the single interlayer GR reflection and the disappearance of the original interlayers spacings indicate contraction of the hydroxide sheets caused by the expulsion of interlayer SO42− oxyanions. This modification of the GR structure was concurrent with the appearance of 2-theta peaks at 41.20°, 34.92 o, 50.24 o, 67.03 o and 73.85 o corresponding to the d-spacings 2.54 Å, 2.98 Å, 2.11 Å, 1.62 Å, 1.49 Å, respectively, indicating the formation of magnetite. As the reaction progressed, the XRD peak intensities of magnetite increased and those of GR decreased. Both TEM and XRD analyses showed a mixture of GR and magnetite at the end of the 24 h experiment, indicating the presence of residual GR and incomplete mineral transformation. Control experiments conducted at room temperature showed no H2 production or change in pH, and the GR remained stable with no mineral transformation occurring for over 1 year.
The addition of metal cations accelerated the transformation of GR to magnetite (Fig. 2). When 1 ppm of either Ni2+ and Zn2+ was added to the GR suspension, complete transformation to magnetite was observed by 0.5 h of heating at 85 °C, while the addition of 1 ppm Co2+ resulted in complete GR transformation in less than 2 h. Residual GR was not detectable by XRD in any of the metal-mineral systems at the end of the 24 h experiments.
Chemical analyses of the aqueous solutions showed that the conversion of GR to magnetite resulted in the rapid removal of dissolved Ni2+, Zn2+, and Co2+ (Fig. 3), indicating that the metal cations were sorbed/co-precipitated with magnetite during mineral transformation. In the Ni2+ experiment, pre-equilibration of the metal solution with GR at room temperature led to sorption of approximately 9% of total Ni2+(aq) (Fig. 3a). Upon heating, Ni2+ was quickly partitioned to the solid phase with over 85% of Ni2+(aq) removed after 4 h of reaction. Replicate experiments exhibited excellent agreement between independent experimental runs (Additional file 1: Fig. S4). A longer experiment conducted up to 24 h showed a small amount (< 10%) of Ni re-released back into the aqueous solution (Additional file 1: Fig. S5). The room temperature control experiment showed slow continuous Ni2+(aq) sorption on GR with approximately 20% of Ni2+(aq) removed after 4 h and 28% removed after 24 h. In the Zn2+ experiment, high affinity sorption of Zn2+ into the solid phase was observed (Fig. 3b). Approximately 40% of the Zn2+(aq) was sorbed to GR in the pre-equilibration period. The conversion of GR to magnetite resulted in complete Zn2+(aq) removal at the first sampling time point (30 min), followed by low levels Zn2+ release back to solution. After 4 h, 87% of the Zn2+(aq) was removed at 85 °C heating compared to 52% at room temperature. In the Co2+ experiment, lower affinity sorption of Co2+ onto the solid phase was observed. Pre-equilibration of the Co2+ solution with GR at room temperature removed 10% of the Co2+(aq). Heating at 85 °C resulted in 50% of Co2+(aq) removal at 30 min, with no additional Co2+ removal detected at the following time points. Similar to the other metals, slow continuous Co2+ removal by GR was observed in the room temperature control experiments with approximately 18% of Co2+ sorption after 4 h. Finally, decreases in solution pH were observed during GR conversion to magnetite (Additional file 1: Fig. S6), and the changes in pH (6.8 to 6.2) were nearly identical to the metal-free control experiment (Additional file 1: Fig. S3).
Dissolution of the magnetite product with HCl yielded dissolution ratio curves that revealed the distribution of metal cations within the magnetite structure (Fig. 4). The dissolution ratio curves of Ni to Fe and Zn to Fe showed concave trends, where Fe was preferentially released over the metal cations when magnetite was dissolved. These data indicated that the metal cations were predominately integrated into the interior of the magnetite lattice. Conversely, the dissolution ratio curve of Co to Fe yielded a straight line with a slope close to 1. This indicated that Co was uniformly distributed in the magnetite structure. None of the metal ions exhibited a convex dissolution trend, excluding surface adsorption as a major mechanism.
The primary finding of the work presented here is that the transformation of GR to magnetite is markedly accelerated in the presence of metal impurities. This suggests that the interaction of trace metal sorbates with GR goes beyond simple surface complexation reactions and involves reactions that destabilize the GR structure. We propose that the three metal cations (Ni2+, Zn2+, and Co2+) replace structural Fe2+ cations at GR crystal edge sites and/or in the near-surface lattice, consistent with the results of Elzinga . The ability of these metals to replace Fe2+ can be attributed to their identical valence and similar ionic radii facilitating isomorphous substitution. Exchange may be promoted by the higher hydrolysis constants of the three metals relative to Fe2+ (Zn2+ > Ni2+ > Co2+ > Fe2+), as more hydrolyzable cations are more readily adsorbed and coprecipitated . Substitution may further be enhanced by GR dissolution-reprecipitation reactions driven by solubility differences between the added metals and Fe2+, or by Fe2+-catalyzed GR recrystallization. The resultant substitution of metals into the GR lattice at and near particle edges is a plausible explanation for the observed decrease in GR stability. The incorporation of metal impurities is expected to weaken the GR structure, making the mineral less stable and more susceptible to transformation relative to the pure phase. This explanation also agrees with previous observations of decreased GR mineral stability and increased susceptibility towards mineral transformation due to divalent cation sorption [3, 24, 26, 27].
The XRD results presented in Fig. 2 suggest that GR is rapidly transformed to magnetite, whereas the metal sorption kinetics curves in Fig. 3 exhibit longer term dynamics. Because XRD can only identify crystalline phases, poorly crystalline materials such as degrading GR during the early stages of magnetite nucleation may have evaded detection . It is therefore conceivable that the metal sorption kinetics were controlled by GR dissolution and concurrent magnetite neoformation that were ongoing even after the disappearance of the GR peaks from the diffractograms.
The conversion of GR to magnetite was marked by a significant increase in Ni2+ Zn2+ and Co2+ cation uptake from solution, demonstrating a stronger affinity for metal sorption/co-precipitation of the magnetite product compared to the GR precursor. Increased metal sorption can be attributed to changes in mineral surface charge and surface area during transformation. The pHzpc of magnetite is 6–6.8  compared to the pHzpc of GR of 8.3 . In the pH range of the experiment (pH 6.8 to 6.1), magnetite is expected to exhibit a net negative surface charge which would strongly favor cation adsorption. Furthermore, the particle size of the magnetite product was considerably smaller than the GR precursor resulting in higher reactive surface area (Fig. 1). The rapid nucleation of magnetite would also promote small crystal formation leading to high surface area in the initial stages of magnetite precipitation.
The adsorption of metal cations to magnetite surfaces during crystal growth resulted in structural incorporation of metals into the mineral lattice (Fig. 4). The congruency plots for Ni and Zn showed preferential accumulation of the metal cations in the interior of the magnetite crystals. This is likely due to a combination of GR dissolution and magnetite crystal growth processes. The removal of Ni2+(aq) and Zn2+(aq) by GR during the pre-equilibration period was driven by sorption reactions at the edges of GR particles where the lattice is disrupted, and not along the chemically stable basal planes [4, 31]. Because of their chemical reactivity, the edge sites are also expected to be the location where the oxidation reactions transforming GR to magnetite take place . The early-stage magnetite crystals therefore likely incorporated the Ni2+ and Zn2+ that had accumulated at the GR edges during pre-equilibration, resulting in elevated impurity contents. Furthermore, there were higher levels of aqueous Ni2+ and Zn2+ available for incorporation in the early stages of magnetite crystallization compared to the later stages (Fig. 2). This indicates that the nuclei of the early-stage magnetite crystals sequestered high levels of aqueous metal cations into the core of the mineral during neoformation, leaving behind lower concentrations of dissolved Ni2+ and Zn2+ at the later-stages of crystal growth.
The even distribution of Co2+ suggests a different mechanism where cobalt incorporation is limited not by its concentration but by some other factor that scales with the rate of magnetite crystal growth. One possibility is that oxidation of Co2+ to Co3+ occurred during magnetite precipitation and cobalt incorporation, and that concurrent Co2+ and Fe2+ oxidation resulted in the uniform incorporation of cobalt as Co3+ into the magnetite lattice. The potential for Co2+ oxidation to Co3+ during magnetite formation has been previously reported [33, 34]. Co2+ oxidation and the incorporation of Co3+ may be linked to slower kinetics of GR dissolution in the cobalt experiment (Fig. 2C). Additional studies addressing the speciation of the incorporated metals in the magnetite structure are warranted to further elucidate the mechanism of metal integration.
The results of this study indicate that Ni2+, Zn2+ and Co2+ sorption is coupled to GR transformation to magnetite. Because GR is a precursor to magnetite found in sedimentary rocks [13,14,15, 35] our findings have important implications for understanding the trace metal composition of iron oxides preserved in the geologic record. Field studies have shown that GR is one of the dominant Fe minerals that deposit in anoxic sediments at Archean analogue sites [6, 7]. Our experiments indicate that increases in temperature during sediment diagenesis can trigger GR transformation to magnetite. The mineral conversion process, which likely occurs during early diagenesis, is a key step in metal transfer to magnetite crystals. This is a significant insight because trace metal composition of ancient magnetite-containing rocks has been used to infer the aqueous metal concentrations of Archean oceans [36,37,38,39]. If iron formations are to be used as chemical archives of paleo-seawater, then it is crucial to understand the relative roles of GR and magnetite in metal sorption, as well as the geochemical conditions that control metal transfer to the mineral phase. Our results demonstrate that the reactivity of GR differs from that of magnetite, and that magnetite is a more effective scavenger of metals, including Ni2+ a metal which is thought to be an essential micronutrient for methanogenesis. Furthermore, mineral transformation reactions that occurs after burial imply that the metal impurities found in magnetite reflect conditions during diagenesis and sediment pore water composition rather than overlying water column chemistry. Based on these findings, caution should be exercised when using diagenetic magnetite as a paleo-proxy for nutrient availability in Precambrian oceans.
Availability of data and materials
The datasets used for this manuscript are displayed in the figures in the manuscript and the additional file. The data in tabulated form are available upon request.
Usman M, Byrne JM, Chaudhary A et al (2018) Magnetite and green rust: synthesis, properties, and environmental applications of mixed-valent iron minerals. Chem Rev 118:3251–3304. https://doi.org/10.1021/acs.chemrev.7b00224
Chaves LHG, Curry JE, Stone DA, Chorover J (2007) Fate of nickel ion in (II-III) hydroxysulphate green rust synthesized by precipitation and coprecipitation. Rev Bras Cienc Solo 31:813–818. https://doi.org/10.1590/S0100-06832007000400021
Wang X, Peng J, Liang X et al (2019) Effects of Mn2+, Ni2+, and Cu2+ on the Formation and Transformation of Hydrosulfate Green Rust: Reaction Processes and Underlying Mechanisms. ACS Earth Space Chem 3:519–530. https://doi.org/10.1021/acsearthspacechem.8b00187
Elzinga EJ (2021) Mechanistic study of Ni(II) sorption by green rust sulfate. Environ Sci Technol 55:10411–10421. https://doi.org/10.1021/acs.est.1c01442
Feder F, Trolard F, Klingelhöfer G, Bourrié G (2005) In situ Mössbauer spectroscopy: evidence for green rust (fougerite) in a gleysol and its mineralogical transformations with time and depth. Geochim Cosmochim Acta 69:4463–4483. https://doi.org/10.1016/j.gca.2005.03.042
Zegeye A, Bonneville S, Benning LG et al (2012) Green rust formation controls nutrient availability in a ferruginous water column. Geology 40:599–602. https://doi.org/10.1130/G32959.1
Koeksoy E, Sundman A, Byrne JM et al (2019) Formation of green rust and elemental sulfur in an analogue for oxygenated ferro-euxinic transition zones of Precambrian oceans. Geology 47:211–214. https://doi.org/10.1130/G45501.1
Génin J-MR, Refait P, Bourrié G et al (2001) Structure and stability of the Fe(II)–Fe(III) green rust “fougerite” mineral and its potential for reducing pollutants in soil solutions. Appl Geochem 16:559–570. https://doi.org/10.1016/S0883-2927(00)00043-3
O’Loughlin EJ, Kelly SD, Kemner KM et al (2003) Reduction of AgI, AuIII, CuII, and Hg II by FeII/FeIII hydroxysulfate green rust. Chemosphere 53:437–446. https://doi.org/10.1016/S0045-6535(03)00545-9
Johnson CA, Freyer G, Fabisch M et al (2014) Observations and assessment of iron oxide and green rust nanoparticles in metal-polluted mine drainage within a steep redox gradient. Environ Chem 11:377–391. https://doi.org/10.1071/EN13184
Roberts AP, Almeida TP, Church NS et al (2017) Resolving the origin of pseudo-single domain magnetic behavior. J Geophys Res Solid Earth 122:9534–9558. https://doi.org/10.1002/2017JB014860
Perez JPH, Freeman HM, Schuessler JA, Benning LG (2019) The interfacial reactivity of arsenic species with green rust sulfate (GRSO4). Sci Total Environ 648:1161–1170. https://doi.org/10.1016/j.scitotenv.2018.08.163
Halevy I, Alesker M, Schuster EM et al (2017) A key role for green rust in the Precambrian oceans and the genesis of iron formations. Nat Geosci 10:135–139. https://doi.org/10.1038/ngeo2878
Dodd MS, Wang H, Li C et al (2022) Abiotic anoxic iron oxidation, formation of Archean banded iron formations, and the oxidation of early earth. Earth Planet Sci Lett. https://doi.org/10.1016/j.epsl.2022.117469
Sun L, Lechte M, Shi X et al (2022) Hexagonal magnetite in Algoma-type banded iron formations of the ca. 2.52 Ga Baizhiyan formation, North China: evidence for a green rust precursor? Am Miner 107:970–984. https://doi.org/10.2138/am-2022-7981
Tamaura Y, Yoshida T, Katsura T (1984) The synthesis of green rust II(FeIII1–FeII2) and its spontaneous transformation into Fe3O4. Bull Chem Soc Jpn 57:2411–2416. https://doi.org/10.1246/bcsj.57.2411
Sumoondur A, Shaw S, Ahmed I, Benning LG (2008) Green rust as a precursor for magnetite: an in situ synchrotron based study. Mineral Mag 72:201–204. https://doi.org/10.1180/minmag.2008.072.1.201
Simon L, François M, Refait P et al (2003) Structure of the Fe(II-III) layered double hydroxysulphate green rust two from rietveld analysis. Solid State Sci 5:327–334. https://doi.org/10.1016/S1293-2558(02)00019-5
Inoue K, Kwon SK, Kimijima KNI et al (2007) Analysis of iron oxyhydroxides and oxides converted from green rust in aqueous solution. ISIJ Int 47:453–457. https://doi.org/10.2355/isijinternational.47.453
Refait P, Drissi H, Marie Y, Genin J-MR (1994) The substitution of Fe 2+ ions by Ni 2+ ions in green rust one compounds. Hyperfine Interact. https://doi.org/10.1007/BF02069144
Choi J, Batchelor B, Won C, Chung J (2012) Nitrate reduction by green rusts modified with trace metals. Chemosphere 86:860–865. https://doi.org/10.1016/j.chemosphere.2011.11.035
van Genuchten CM, Behrends T, Dideriksen K (2019) Emerging investigator series: Interdependency of green rust transformation and the partitioning and binding mode of arsenic. Environ Sci Process Impacts 21:1459–1476. https://doi.org/10.1039/C9EM00267G
Thomas AN, Eiche E, Göttlicher J et al (2020) Effects of metal cation substitution on hexavalent chromium reduction by green rust. Geochem Trans. https://doi.org/10.1186/s12932-020-00066-8
Refait P, Duboscq J, Aggoun K et al (2021) Influence of Mg2+ ions on the formation of green rust compounds in simulated marine environments. Corros Mater Degrad 2:46–60. https://doi.org/10.3390/cmd2010003
Géhin A, Ruby C, Abdelmoula M et al (2002) Synthesis of Fe(II-III) hydroxysulphate green rust by coprecipitation. Solid State Sci 4:61–66. https://doi.org/10.1016/S1293-2558(01)01219-5
Tamaura Y (1986) Ni(II)-bearing green rust II and its spontaneous transformation into Ni(II)-bearing ferrites. Bull Chem Soc Jpn 59:1829–1832. https://doi.org/10.1246/bcsj.59.1829
Inoue K, Shinoda K, Suzuki S, Waseda Y (2008) Characteristic behavior of nickel ions during transformation of green rust to ferric oxyhydroxides in aqueous solution. Mater Trans 49:466–470. https://doi.org/10.2320/matertrans.MBW200710
Montes-Hernandez G, Findling N, Renard F (2021) Direct and indirect nucleation of magnetite nanoparticles from solution revealed by time-resolved raman spectroscopy. Cryst Growth Des 21:3500–3510. https://doi.org/10.1021/acs.cgd.1c00282
Bobik M, Korus I, Dudek L (2017) The effect of magnetite nanoparticles synthesis conditions on their ability to separate heavy metal ions. Archiv Environ Protect 43:3–9. https://doi.org/10.1515/aep-2017-0017
Guilbaud R, White ML, Poulton SW (2013) Surface charge and growth of sulphate and carbonate green rust in aqueous media. Geochim Cosmochim Acta 108:141–153. https://doi.org/10.1016/j.gca.2013.01.017
Perez JPH, Freeman HM, Brown AP et al (2020) Direct visualization of arsenic binding on green rust sulfate. Environ Sci Technol 54:3297–3305. https://doi.org/10.1021/acs.est.9b07092
O’Loughlin EJ, Kelly SD, Cook RE et al (2003) Reduction of uranium(VI) by mixed iron(II)/iron(III) hydroxide (green rust): formation of UO2 nanoparticles. Environ Sci Technol 37:721–727. https://doi.org/10.1021/es0208409
Coker VS, Pearce CI, Pattrick RAD et al (2008) Probing the site occupancies of Co-, Ni-, and Mn-substituted biogenic magnetite using XAS and XMCD. Am Miner 93:1119–1132. https://doi.org/10.2138/am.2008.2681
Rutirawut T, Limphirat W, Sinsarp A et al (2015) Composition and oxidation state of cobalt and nickel-iron oxide colloidal nanoparticles in liquid phase. Adv Mat Res 1103:21–27. https://doi.org/10.4028/www.scientific.net/amr.1103.21
Li YL, Konhauser KO, Zhai M (2017) The formation of magnetite in the early Archean oceans. Earth Planet Sci Lett 466:103–114. https://doi.org/10.1016/j.epsl.2017.03.013
Konhauser KO, Pecoits E, Lalonde S, v, et al (2009) Oceanic nickel depletion and a methanogen famine before the great oxidation event. Nature 458:750–753. https://doi.org/10.1038/nature07858
Mloszewska AM, Pecoits E, Cates NL et al (2012) The composition of Earth’s oldest iron formations: The Nuvvuagittuq Supracrustal Belt (Québec, Canada). Earth Planet Sci Lett 317–318:331–342. https://doi.org/10.1016/j.epsl.2011.11.020
Robbins LJ, Lalonde S, v., Planavsky NJ, et al (2016) Trace elements at the intersection of marine biological and geochemical evolution. Earth Sci Rev 163:323–348. https://doi.org/10.1016/j.earscirev.2016.10.013
Konhauser KO, Planavsky NJ, Hardisty DS et al (2017) Iron formations: a global record of neoarchaean to palaeoproterozoic environmental history. Earth Sci Rev 172:140–177. https://doi.org/10.1016/j.earscirev.2017.06.012
We thank Kenneth McGuinness for his assistance with transmission electron microscopy and Winnie Liu for helpful discussions on green rust synthesis.
This work was supported by NASA Astrobiology Grant 80NSSC18M0093.
Ethics approval and consent to participate
The authors declare that they have no competing interests.
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Additional file 1: Figure S1.
Production of H2 gas. GR suspensions were heated at 85oC under anoxic conditions and headspace was analyzed using gas chromatography. Figure S2. Formation of a magnetic product. GR samples were heated at 85oC for 24 hours. The starting GR material is shown on the right and the magnetic product is shown on the left. Figure S3. Change in solution pH during GR transformation. Open symbols represent the room temperature control experiment and the closed symbol represent GR heated at 85oC. Figure S4. Replicate experiments of Ni incorporation during GR transformation to magnetite. Open symbols represent the room temperature control experiment, and the closed symbols represent 3 independent experiments of GR heated at 85oC in presence of 1 ppm Ni. Figure S5. 24 hour experiment of Ni incorporation during GR transformation to magnetite. Open symbols represent the room temperature control experiment and the closed symbols represent GR heated at 85oC. Figure S6. Changes in solution pH during GR transformation in the metal amended experiments. Open symbols represent the room temperature control experiment and the closed symbols represent GR samples heated at 85oC containing A) nickel, B) zinc, and C) cobalt.
Rights and permissions
Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/. The Creative Commons Public Domain Dedication waiver (http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated in a credit line to the data.
About this article
Cite this article
Farr, O., Elzinga, E.J. & Yee, N. Effect of Ni2+, Zn2+, and Co2+ on green rust transformation to magnetite. Geochem Trans 23, 3 (2022). https://doi.org/10.1186/s12932-022-00080-y
- Hydrosulfate green rust
- Layered double hydroxides
- Banded iron formations