Journal topic
Biogeosciences, 15, 4905–4922, 2018
https://doi.org/10.5194/bg-15-4905-2018
Biogeosciences, 15, 4905–4922, 2018
https://doi.org/10.5194/bg-15-4905-2018

Research article 20 Aug 2018

Research article | 20 Aug 2018

# A systematic look at chromium isotopes in modern shells – implications for paleo-environmental reconstructions

A systematic look at chromium isotopes in modern shells – implications for paleo-environmental reconstructions
Robert Frei1, Cora Paulukat1,2, Sylvie Bruggmann1, and Robert M. Klaebe1 Robert Frei et al.
• 1Department of Geoscience and Natural Resource Management, University of Copenhagen, Øster Voldgade 10, 1350 Copenhagen K, Denmark
• 2ALS Scandinavia AB, Aurorum 10, 977 75 Luleå, Sweden

Correspondence: Robert Frei (robertf@ign.ku.dk)

Abstract

The chromium isotope system (53Cr 52Cr, expressed as δ53Cr relative to NIST SRM 979) in marine biogenic and non-biogenic carbonates is currently being evaluated as a proxy for the redox state of the ocean. Previous work has concentrated on using corals and foraminifera for this purpose, but investigations focusing on the behavior of Cr in bivalves as potential archives are lacking. Due to their often good preservation, fossil marine biogenic carbonates have the potential to serve as useful archives for the reconstruction of past ocean redox fluctuations and eventually link those to climatic changes throughout Earth's history. Here, we present an evaluation of the Cr isotope system in shells of some modern bivalves. Shell species from Lucidinadae, Cardiidae, Glycimerididae and Pectenidae, collected systematically from one Mediterranean location (Playa Poniente, Benidorm, Spain) over a 3-year period reveal δ53Cr values ranging from 0.15 ‰ to 0.65 ‰, values that are systematically below the local seawater δ53Cr value of 0.83±0.05 ‰. This attests to a significant reduction of dissolved seawater chromium in the process leading to calcification and thus for control of Cr isotope fractionation during biological routes. A similar, constant offset in δ53Cr values relative to surface seawater is observed in shells from Mytilius edulis from an arctic location (Godhavn, Disko Bay, Greenland). Chromium concentrations in the studied shells are significantly controlled by organic matter and typically range from 0.020 to 0.100 ppm, with some higher concentrations of up to 0.163 ppm recorded in Pectenidae. We also observe subtle, species-dependent differences in average Cr isotope signatures in the samples from Playa Poniente, particularly of Lucidinadae and Cardiidae, with considerably depressed and elevated δ53Cr values, respectively, relative to the other species investigated. Intra-species heterogeneities, both in Cr concentrations and δ53Cr values, are favorably seen to result from vital effects during shell calcification rather than from heterogeneous seawater composition. This is because we observe that the surface seawater composition in the particular Playa Poniente location remained constant during the month of July of the 3 years we collected bivalve samples. Intra-shell heterogeneities – associated with growth zones reflecting one to several years of growth, both in δ53Cr and Cr concentrations – are observed in a sample of Placuna placenta and Mimachlamys townsendi. We suspect that these variations are, at least partially, related to seasonal changes in δ53Cr of surface seawaters. Recognizing the importance of organic substances in the bivalve shells, we propose a model whereby reduction of Cr(VI) originally contained in the seawater as chromate ion and transported to the calcifying space, to Cr(III), is effectively adsorbed onto organic macromolecules which eventually get included in the growing shell carbonates. This study, with its definition of statistically sound offsets in δ53Cr values of certain bivalve species from ambient seawater, forms a base for future investigations aimed at using fossil shells as archives for the reconstruction of paleo-seawater redox fluctuations.

1 Introduction

Redox processes on land lead to mobilization of Cr from weathering rocks and soils into the runoff. It is now known that oxidation of silicate-hosted and oxide-mineral-hosted Cr(III), potentially with the catalytic help of MnO2, to Cr(VI) is accompanied by an isotopic fractionation rendering the mobilized Cr(VI) isotopically heavier (Ellis et al., 2002; Zink et al., 2010; Døssing et al., 2011). Recently, an alternative, redox-independent pathway of Cr mobilization, through ligand-promoted dissolution of Cr-containing solids, was advocated by Saad et al. (2017). This mobilization path is based on the ability of organic acids and siderophores to efficiently bind Cr(III) whereby respective ligand formation is accompanied by isotope fractionation effects, leading to Cr(III) being enriched in 53Cr very much like in redox-dependent mobilization paths.

The fate of Cr transported to the oceans, its transfer and/or removal to marine sediments and its cycling through marine organisms, is largely unexplored and complex. Much research focus today is on the understanding of the redox cycling of Cr in the ocean system, and on investigating marine sediments and marine organisms as potential archives for recording past redox conditions of the ocean–atmosphere system through geological time (Frei et al., 2009, 2011, 2013, 2016; Bonnand et al., 2013; Planavsky et al., 2014; Holmden et al., 2016; D'Arcy et al., 2017; Rodler et al., 2016a, b; Gilleaudeau et al., 2016). It is conceivable that the Cr isotope composition of seawater and marine chemical sediments reflect a complex signal of oxidation/reduction processes operating within the oceans (Scheiderich et al., 2015; Paulukat et al., 2016), and it is therefore clear that one must first understand the individual processes and mechanisms that govern the transfer of dissolved Cr in seawater into the respective potential archives. Recent studies (Rodler et al., 2015; Pereira et al., 2015; Wang et al., 2016) have paved the way, but further systematic investigations in both natural and laboratory-controlled settings are required.

Available results from inorganic calcite precipitation experiments revealed that the incorporation of Cr from a solution into CaCO3 is facilitated as a chromate anion (${\mathrm{CrO}}_{\mathrm{4}}^{\mathrm{2}-}$), which replaces a carbonate anion (${\mathrm{CO}}_{\mathrm{3}}^{\mathrm{2}-}$) in the calcite lattice (Tang et al., 2007). This process of inorganic calcification tends to preferentially incorporate heavy 53Cr isotopes into the mineral, yielding the δ53Cr of calcite that is up to ∼0.3 ‰ more positive compared to the fluid; unless the latter is a Cr-poor solution (such as seawater) in which case the isotope fractionation between inorganic calcite and the fluid is negligible (Rodler et al., 2015).

In contrast, results from biologically produced CaCO3 minerals, such as foraminiferal calcite (Wang et al., 2016) and/or coral aragonite (Pereira et al., 2015) confirmed that these marine organisms produce CaCO3 skeletons that are systematically negatively fractionated, up to ∼1 ‰, compared to ambient seawater. Similarly, data by Holmden et al. (2016) from the modern Caribbean Sea show that the δ53Cr of bulk carbonate sediments is about 0.46±0.14 ‰ lower relative to local seawater. These results therefore oppose those from inorganic calcite precipitation experiments (cf. Rodler et al. 2015).

Furthermore, due to a local redox cycling and biological uptake of Cr in the oceans (Semeniuk et al., 2016), the Cr isotope signature of present-day seawater is not globally homogeneous (Scheiderich et al., 2015; Paulukat et al., 2016). This additionally complicates the application of δ53Cr measurements in marine carbonate archives with respect to deducing information regarding global ocean redox, and implications thereof for climatic changes on Earth through time. Considering the abovementioned issues and limitations, the full potential of Cr isotopes for paleo-redox studies can only be realized with more detailed calibration work done on modern seawater-carbonate systems from different oceanographic settings and locations, where δ53Cr data can be collected simultaneously from (i) local ocean waters and (ii) precipitated inorganic/biogenic carbonates.

Figure 1Map with locations where bivalve and seawater samples were collected.

This contribution is a follow-up of a recent study by Farkaš et al. (2018) who for the first time present a comprehensive Cr isotope investigation of a coupled seawater-carbonate system from one of the world's largest carbonate-producing shelf ecosystems, the Great Barrier Reef (Lady Elliot Island, Australia). These authors present δ53Cr data from local seawaters and selected recent biogenic carbonates (i.e., gastropods, cephalopods, corals and calcifying algae), complemented by additional δ53Cr analyses of marine skeletal carbonates (i.e., bivalves, gastropods and cephalopods) collected from main oceanic water bodies including the North Atlantic and South Atlantic Ocean, North Pacific and South Pacific Ocean and the Mediterranean Sea. Our study goes a step further in that we compare Cr isotope signatures of certain bivalve species from one location in the Mediterranean Sea collected over a period of 3 years with simultaneous collection of surface seawater from that location. This allows us to elaborate on inter- and intra-species Cr isotope variations, with the ultimate aim to eventually deduce systematic fractionation trends or offsets relative to ambient seawater compositions, that could later be used for reconstructing the redox state of past ocean waters.

Figure 2Photographs of representative bivalve species studied herein. (1)–(8) from Playa Poniente, (9) from Kakinada Bay, (10) from Hawke's Bay, and (11) from Godhavn (Qeqertarsuaq). Black scale bar correspond to 1 cm. (1) Cardiidae (unknown species); (2) Pecten jacobaeus; (3) Challista chione; (4) Glycymeris glycymeris; (5) Chamelea striulata; (6) Loripes lucinalis; (7) Venus verrucosa; (8) Arca navicularis; (9) Placuna placenta (windowpane oyster, Capiz; with growth profile samples indicated); (10) Mimachlamys townsendi (with growth profile samples indicated) and (11) Mytilus edulis.

2 Study sites and samples

Bivalve shells (from families Cardiidae, Veneridae, Glycymerididae, Pectinidae and Lucinidae) and ambient surface seawater samples were collected during the first 2 weeks of July in the three successive years from 2015–2017, at the Mediterranean Playa Poniente beach, Benidorm, Spain (38324.20${}^{\prime \prime }$ N, 0857.30${}^{\prime \prime }$ W; Fig. 1). In addition, in situ growing, alive Mytilus edulis species and seawater samples were collected by researchers from the Center for Permafrost (CENPERM), University of Copenhagen, at a rocky coast section near arctic Godhavn (Qeqertarsuaq), Disko Island, Greenland (691444.14${}^{\prime \prime }$ N, 533138.34${}^{\prime \prime }$ W; Fig. 1) during fieldwork in June 2016. Respective seawater analyses from the same locations, except the 2017 Playa Poniente sample, were performed earlier and published in Paulukat et al. (2016). Two additional bivalve shells (Placuna Placenta; Mimachlamys townsendi) from Kakinada Bay, Andhra Pradesh, India (165530.85${}^{\prime \prime }$ N, 821543.36${}^{\prime \prime }$ E; Fig. 1) and from Hawke's Bay Beach, Karachi, Pakistan (245136.46${}^{\prime \prime }$ N, 665136.66${}^{\prime \prime }$ E; Fig. 1), respectively, were used to investigate intra-shell Cr isotope and Cr concentration ([Cr]) variations. These specimen were cut along a growth transect into subsamples and analyzed individually. Pictures of representative shell species (with the subsample growth transects of the two specimens studied for intra-shell variations) studied herein are depicted in Fig. 2.

Bivalve species studied from Playa Poniente all live in sand in an intertidal setting to about 20 m of depth. While exact ages of the species studied are not known – based on the relatively small sizes and number of annual growth zones in Glycymeris (Beaver et al., 2017; Yamaoka et al., 2016) and Callista chione (Moura et al., 2009) – we estimate the age range of the majority of shells sampled to be between ∼2 and 5 years. Mytilus edulis lives in the intertidal and sublittoral (up to 5 m of depth) on a wide range of habitats from rocky shores to estuaries. Our samples were collected from a rocky coast intertidal environment near Godhavn. Growth rates in Mytilus edulis are highly variable and dependent on location and environmental conditions. Typically, under optimal conditions, Mytilus edulis can grow up to 60–80 mm in length within 2 years (Seed and Suchanek, 1992). Placuna placenta (windowpane oyster, Capiz) species from Kakinada Bay were purchased from a fisherman who hand-picked them at low tide in a water depth of ∼1 m. Windowpane oysters from this location have been reported to attain an average length of 122 mm in 1 year and 157 mm in 2 years (Murthy et al., 1979). The Placuna placenta sample studied herein, measuring ∼10 cm from the apex to the rim (Fig. 2), therefore represents about a 1-year growth period. The Pectenidae species, determined as Mimachlamys townsendi, from Hawke's Bay was collected on the sandy beach in 1969 by the lead author himself. There is an extensive variation in growth rates and attained ages of Pectinidae. Commonly, Mimachlamys has a lifetime of up to 6 years and in this time reaches sizes between 6 and 10 cm. Our specimen of Mimachlamys townsendi with ∼8 cm in length therefore represents a fully grown-up shell and our transect (Fig. 2) is representative of several years of growth. These scallops usually live intertidally in shallow water of up to 10 m of depth. Some biological and ecological characteristics of scallops can be found in Minchin (2003).

3 Analytical details

## 3.1 Sample preparation and dissolution

Seawater samples were collected into pre-cleaned plastic bottles, filtered through 0.45 µm nylon membrane filters using a vacuum pump and then acidified and spiked with a 50Cr-54Cr double spike within 1 week from collection.

In order to recover enough Cr for isotopic analyses (> 50 ng Cr are usually required for a precise mass spectrometric analysis), shell samples (single shell pieces, transect pieces) weighing between 1.5 and 3 g were required. In cases where individual shell specimens weighed less than this amount, multiple shells from the same species (up to seven individual shells in the case of Chamelea striatula and Loripes lucinalis) were combined. Samples were first physically brushed and washed in Milli-Q water (MQ, resistivity 18 MΩ), and then immersed in 2 % hydrogen peroxide (H2O2) for 10 min. They were briefly leached in 0.5N HCl and finally thoroughly washed in MQ water. Ten Mytilus edulis shells (five dorsal and five ventral shells) were combined and powdered in an agate mortar to be used as a so-called “mixed” sample. With the exception of the Mytilus edulis samples from Godhavn which were dissolved directly in aqua regia after removal of the mussel tissue, pre-cleaned shells (also including the three samples of Mytilus edulis for comparative purposes) were weighed into chemical porcelain crucibles (CoorsTek, 15 mL capacity) and ashed in a furnace at 750 C for 5 h prior to dissolution in 6N HCl. The aim with this incineration was to achieve a total dissolution of the respective shells, including the organic material known to have chromium associated with it.

## 3.2 Ion chromatographic separation of chromium

Methods used in this study for the purification and isotope analysis of Cr in seawater samples and biogenic carbonates follow those described in Paulukat et al. (2016) and Pereira et al. (2015), with small modifications. Briefly, filtered and spiked seawater samples were transferred into 1 L Savillex teflon beakers, evaporated, redissolved in 50 mL of aqua regia, and evaporated again. Respective spiking (aiming at a 50Cr 52Cr ratio in the sample-spike mixture of between 0.15 and 0.75) of biogenic carbonates was done during the attack with aqua regia or during the 6 N HCl attack of incinerated samples. Spiking prior to ion chromatographic separation procedures enables correction of any mass-depended Cr isotope fractionation effects that could occur during the chemical purification and/or mass spectrometric analysis of the samples. The acid-digested and dried down samples (i.e., filtered seawaters and pre-cleaned carbonates) were then processed through a two-step Cr purification chromatography, using a combination of anionic and cationic exchange columns. The first step used a pass-over column (Spex) loaded with 2 mL anion exchange resin. The spiked and dried samples were redissolved in ca. 40 mL of 0.1 N HCl together with 0.5 mL of a freshly prepared 1N ammonium persulfate ((NH4)2S2O8; Sigma-Aldrich, BioXtra, ≥98 %, lot#MKBR5789V) solution, which acts as an oxidizing agent. The sample solutions, contained in 60 mL Savillex Teflon vials, were placed in a microwave oven and heated with closed lids for 50 min using a low-energy thawing program to ensure full oxidation of Cr(III) to Cr(IV). After the samples cooled to room temperature, they were passed through anion exchange columns loaded with 2 mL of pre-cleaned Dowex AG 1×8 anion resin (100–200 mesh). The matrix was washed out with 10 mL of 0.2 N HCl, then with 2 mL of 2 N HCl and finally with 5 mL of MQ H2O, before Cr was collected through reduction with 6 mL 2 N HNO3 doped with a few drops of 5 % H2O2. The so-stripped Cr-bearing solution was then dried down at 130 C.

The second step used a pass-over column (BioRad Econo) loaded with cation exchange resin. For this, the Cr-bearing samples from the anion columns were redissolved in 100 µL of concentrated HCl and diluted with 2.3 mL ultrapure MQ water. This solution was added to the extraction columns loaded with 2 mL of pre-cleaned Dowex AG50W-X8 cation resin (200–400 mesh). The extraction procedure principally adhered to that published by Bonnand et al. (2011) and Trinquier et al. (2008) with only small modifications. The final Cr-bearing liquid cut was dried down at 130 C, ready to be loaded for Cr isotopic analysis on the thermal ionization mass spectrometer.

Total procedure Cr blanks, including incineration, dissolution and ion chromatography procedures remained below 4 ng of Cr. In the worst case scenario, using the sample with the lowest [Cr] in our study (sample Pec-B; [Cr] = 0.021, sample weight = 2.8 g), such blank contribution (assuming the blank Cr composition is of an igneous Earth inventory one) would induce a change in the δ53Cr signature of 0.04 ‰. This is below our current level of analytical precision achieved on the samples studied herein, and below the external reproducibility of between ±0.05 ‰ and 0.08 ‰ for double-spiked NIST SRM 979 (see below) under similar measuring conditions. We therefore did not perform a blank correction of our measured sample Cr isotope signatures.

Figure 3Plot depicting average δ53Cr values from multiple filament runs with 200 nanogram loads of NIST SRM 979 measured on the PHOENIX thermal ionization mass spectrometer at 53Cr beam intensities of 350 mV and 1 V, respectively. The yellow colored range indicates the ±0.08 ‰ external reproducibility of the 10 filaments loads ran at 350 mV 53Cr beam intensities, which correspond to typical beam intensities obtained from our samples.

## 3.3 Mass spectrometric analyses of Cr

The Cr isotope measurements were performed on an IsotopX Ltd PHOENIX thermal ionization mass spectrometer (TIMS) equipped with eight Faraday collectors that allow simultaneous collection of the four chromium beams (50Cr+, 52Cr+, 53Cr+, 54Cr+) together with interfering 49Ti+, 51V+ and 56Fe+ masses.

Table 1Chromium isotope compositions and chromium concentrations of surface seawaters.

The separated Cr residues were loaded onto outgassed Re-filaments using a loading solution consisting of 1 µL of 0.5 N H3PO4, 2.5 µL silicic acid (Gerstenberger and Haase, 1997) and 0.5 µL of 0.5 N H3BO3. The samples were analyzed at temperatures between 1050 and 1250 C and 52Cr beam intensities of between 0.35 and 1 V. One run consisted of 120 cycles and where possible every sample was run at least twice. The final δ53Cr values of the samples were determined as the average of the repeated analysis and are reported in per mil (‰) with ± standard deviation (2σ) relative to the international standard reference material NIST SRM 979 as

$\begin{array}{ll}& \mathit{\delta }{}^{\mathrm{53}}\mathrm{Cr}\left(\mathrm{‰}\right)\phantom{\rule{0.125em}{0ex}}=\phantom{\rule{0.125em}{0ex}}\left[{\left({}^{\mathrm{53}}\mathrm{Cr}\phantom{\rule{0.125em}{0ex}}/\phantom{\rule{0.125em}{0ex}}{}^{\mathrm{52}}\mathrm{Cr}\right)}_{\mathrm{SAMPLE}}/\right\\ & \phantom{\rule{1em}{0ex}}{\left({}^{\mathrm{53}}\mathrm{Cr}\phantom{\rule{0.125em}{0ex}}/\phantom{\rule{0.125em}{0ex}}{}^{\mathrm{52}}\mathrm{Cr}\right)}_{\mathrm{NIST}\phantom{\rule{0.125em}{0ex}}\mathrm{SRM}\mathrm{979}}-\mathrm{1}]×\mathrm{1000}.\end{array}$

The within-run two standard errors of the measurements reported in this study were consistently ≤0.1 ‰. The external reproducibility was determined using average δ53Cr values of double-spiked NIST SRM 979 measured under the same conditions as the samples on the PHOENIX. Figure 3 depicts the averages of 10 runs each from the same filament loaded with 200 ng of double-spiked NIST SRM 979 at beam intensities of 0.35 V and of 1 V. The external reproducibility of the standard under these conditions was ±0.08 ‰ and 0.05 ‰ (2σ), respectively, at the above mentioned 53Cr beam intensities (Fig. 3). The average composition of the 0.35 V and 1 V multiple NIST SRM 979 runs analyzed during the course of this study shows an average offset of $+\mathrm{0.04}±\mathrm{0.03}$ ‰ (2σ; n=11; Fig. 3) on our machine compared to the 0 ‰ certified value of this standards. This offset stems from the original calibration of our double spike relative to the NIST 3112a Cr standard, and the observed offset of 0.04 ‰ was deducted from the raw δ53Cr results to account for this small discrepancy.

Table 2Chromium isotope compositions and chromium concentrations of bivalves.

DCr= ([Cr]CaCO3 [Cr]seawater). ΔCr= offset from respective surface seawater.

4 Results

## 4.1 Surface seawater – chromium isotope compositions and chromium concentrations

Table 1 lists the Cr isotope compositions and Cr concentrations of surface seawater samples relevant to this study. Waters collected during 4 subsequent years in July from Playa Poniente yield surprisingly homogeneous Cr isotope compositions and dissolved [Cr] that range from δ53Cr = 0.81–0.85 ‰, and from 222–280 ng kg−1, respectively. These are comparable with surface seawater data (δ53Cr = 0.81–0.96 ‰, [Cr] = 239–306 ng kg−1) collected from Playa Albir, a beach situated ca. 9.5 km to the east-northeast of Playa Poniente (Fig. 1) in the years 2013 through 2015 (data published by Paulukat et al., 2016).

Figure 4Plot showing the chromium concentrations ([Cr]; blue filled symbols) and chromium isotope compositions (δ53Cr; red filled symbols) of various incinerated bivalve species analyzed from Playa Poniente. (1) Callista Chione; (2) Cardiidae (species unknown); (3) Chamelea gallina; (4) Chamelea striatula; (5) Glycymeris glycymeris; (6) Loripes lucinalis; (7) Pecten jacobaeus and (8) Venus verrucosa. Dashed red lines mark the average values of inter-species analyses, the red area ranges the two standard deviation errors of these analyses. The light gray horizontal bar depicts the Igneous Earth inventory composition (Schoenberg et al., 2009) and the blue horizontal bar the local surface seawater composition measured from this location. One sample of Loripes lucinalis (marked with a light red and a light blue filled symbol) has been dissolved in aqua regia without previous incineration. For details see text.

## 4.2 Shells – chromium isotope compositions and chromium concentrations

Cr isotope compositions and [Cr] of a variety of bivalve species from Playa Poniente (an undefined species of Cardiidae, Callista chione, Chamelea gallina, Chamelea striulata, an undefined species of Glycymeris, Loripes lucinalis, Pecten jacobaeus, Venus verrucosa, Venus nux and Arca Navicularis), of Mytilus edulis species from Godhavn, of subsamples from a windowpane oyster (Placuna placenta) from Kakinada Bay and of a specimen of Mimachlamys townsendi (Pectenidae) from Hawke's Bay Beach are listed in Table 2. Respective data are plotted in Figs. 4–7, together with the ranges of local surface seawaters and the range of igneous Earth reservoirs as defined by Schoenberg et al. (2008). There is no obvious correlation between δ53Cr and [Cr] data (r2= 0.18, diagram not shown) of the samples analyzed herein.

Figure 5Plot showing the chromium concentrations ([Cr]; blue filled symbols) and chromium isotope compositions (δ53Cr; red filled symbols) of various Mytilus edulis shells and of a shell mixture from Godhavn, Disko Bay, Greenland. The darker red and darker blue filled symbol mark analyses on incinerated shells, whereas the lighter colored respective symbols depict analyses from solely aqua-regia-dissolved shells. The light gray horizontal bar depicts the igneous Earth inventory composition (Schoenberg et al., 2009), and the blue horizontal bar the local surface seawater composition measured from this location (Paulukat et al., 2016). For details see text.

Bivalves collected from Playa Poniente generally show low and scattered Cr concentrations ranging from 0.027 to 0.163 ppm, with the largest variations recorded in Glycymeris, and the systematically highest concentrations measured in species of Pecten jacobaeus (Fig. 4; Table 2). Isotopically, the assembly of shell data from Playa Poniente point to a rather restricted compositional band with δ53Cr data ranging from 0.157 ‰ to 0.636 ‰, significantly lower than the local surface seawater average over four consecutive years of δ53Cr =0.83±0.05 ‰ (Fig. 4). On closer inspection, however, we note some distinctive Cr isotope ranges defined by the different bivalve species analyzed. So, for example, samples from Cardiidae exhibit the highest (δ53Cr =0.60±0.13 ‰), while samples from Loripes lucinalis show the lowest Cr isotope compositions (δ53Cr =0.21±0.10 ‰; Table 2, Fig. 4). One subsample of Loripes lucinalis (sample PP15-D unashed; Table 2) was dissolved in aqua regia without prior incineration. This specific sample yielded a distinctively lower Cr concentration ([Cr] = 0.027 ppm) compared to all other Loripes lucinalis samples, but at the same time a δ53Cr value which statistically cannot be distinguished from the other Loripes lucinalis samples (Fig. 4). While this, as expected, points to the fact that a significant fraction (in fact roughly 50 % in the case of Loripes lucinalis) of the total Cr budget in biogenic carbonates is associated with organic material, and not with carbonate itself, it also points to the likelihood that there is not much difference in the Cr isotope composition of these two potential Cr host materials. This result is substantiated and supported by our study of Mytilus edulis from artic Godhavn (see below). Last but not least, we do not see any statistically significant and systematic differences in Cr isotope compositions and Cr concentrations between bivalve species collected during the consecutive sampling years. This conforms to the rather homogeneous surface seawater compositions analyzed from Playa Poniente and the neighboring location Playa Albir during the entire sampling period (Table 1).

Figure 6Plot showing the chromium concentrations ([Cr]; blue filled symbols) and chromium isotope compositions (δ53Cr; red filled symbols) of samples along a growth transect of a Placuna placenta sample (depicted in Fig. 2) from Kakinada Bay. Sample Cap-A is characterized by an elevated [Cr] which is potentially due to an elevated organic content in the initial growth zone comprising the apex of the shell. The sinusoidal distribution of δ53Cr values along the transect potentially reflects seasonal changes in ambient surface seawater. For details refer to the text.

Results of entirely aqua regia dissolved half shells of Mytilus edulis from Godhavn in the Disko Bay, Greenland, are plotted in a similar combined δ53Cr – [Cr] diagram as the shells from Mediterranean Playa Poniente in Fig. 5. These analyses are complemented by a bulk analysis of powdered multiple Mytilus edulis specimens from the same location. In addition, two specimens (in each case the dorsal or ventral shell counterparts of the respective Mytilus edulis specimen dissolved by aqua regia, i.e., samples God-4 and God-5; Table 2) were ashed before final dissolution, in order to evaluate the importance of Cr associated with organic material in these shells compared to the total Cr budget. This was also done with an aliquot of the powdered Mytilus edulis mix. All data define an average δ53Cr value of 0.11±0.05 ‰ (n=10; 2σ), significantly lower than the local surface seawater of 0.73±0.05 ‰ (Paulukat et al., 2016; Fig. 5). [Cr] for aqua-regia-dissolved specimens are a bit more variable, defining an average of [Cr] =0.039±0.009 ppm (n=7, 2σ). Again, the incinerated aliquots, while isotopically indistinguishable from the unashed samples, yielded about twice as high a [Cr] ([Cr] =0.068±0.004 ppm; n=3, 2σ). As mentioned above, this indicates that organic material, effectively attacked by incineration, is a major and significant host of Cr in these bivalves, besides the biogenic carbonate. Again, as already emphasized by the results of Loripes lucinalis from Playa Poniente, the two Cr host materials seem not to be isotopically distinguishable. While, with the exception of Loripes lucinalis, the negative offset (ΔCr) of different bivalve species from local surface seawater at Playa Poniente is between ∼0.4 ‰ and ∼0.2 ‰, the respective ΔCr value for Mytilus edulis from Godhavn is higher, ∼0.7 ‰, and comparable to ΔCr ∼0.6 ‰ defined by Loripes lucinalis from Playa Poniente (see details below).

Figure 7Plot showing the chromium concentrations ([Cr]; blue filled symbols) and chromium isotope compositions (δ53Cr; red filled symbols) of samples along a growth transect in a Mimachlamys townsendi specimen from Hawke's Bay. Sample Pec-H is characterized by an elevated [Cr] which is potentially due to an elevated organic content in the initial growth zone comprising the apex or hinge of the shell (cf. Fig. 2). For details refer to the text.

Results from two profiles along respective major growth transects of a specimen of Placuna placenta from Kakinada Bay, Andhra Pradesh, India and a species of Pectinidae (Mimachlamys townsendi) from Hawke's Bay, Karachi, Pakistan, are plotted in Fig. 6 (Placuna placenta) and Fig. 7 (Mimachlamys townsendi).

[Cr] along the Placuna placenta growth profile vary from 0.03 to 0.25 ppm, but this variation is much smaller if the first sample (Cap-A) is excluded. Sample Cap-A incorporates the beak of the shell and a first growth zone which is visually characterized by a more brown (organic-rich) color (Fig. 3). Intra-species variations in δ53Cr and [Cr] of Mimachlamys townsendi from Hawke's Bay are depicted in Fig. 7. The average δ53Cr value of all 8 profile samples is 0.07±0.11 ‰ (2σ) and statistically indistinguishable from that of Placuna placenta (average δ53Cr =0.05±0.19 ‰; n=7, 2σ). With the exception, like in Placuna placenta, of the sample closest to the apex/hinge of the shell (sample Pec-H; Fig. 7), which yielded by far the highest [Cr] in the profile, the [Cr] of the remaining profile samples are ∼0.04 ppm. In the specimens studied, the δ53Cr values along the profile are statistically indistinguishable from each other.

5 Discussion

## 5.2 Surface seawater

The Playa Poniente seawater data are compatible with data from other Mediterranean surface seawaters, which distinguish in [Cr] vs. δ53Cr space from Baltic Sea seawater, but are compatible with the trend of an inverse logarithmic relationship between δ53Cr and [Cr] defined by Scheiderich et al. (2015) and substantiated later by Paulukat et al. (2016) of worldwide Atlantic and Pacific ocean waters. Three separate analyses of seawater from Disko Island, published by Paulukat et al. (2016), are characterized by slightly lower [Cr] and δ53Cr values compared to the Mediterranean waters, but are similar to other waters from the North Atlantic (cf. Fig. 2 in Paulukat et al., 2016). Our data therefore support the hypothesis put forward by Scheiderich et al. (2015) that the observed Cr isotope signature in worldwide seawater likely arises from fractionation during the reduction of Cr(VI) in surface waters, scavenging of isotopically light Cr(III) to deeper water and sediment, and subsequent release of this seawater-derived Cr(III) back into seawater, either as organic complexes with Cr(III) or after oxidation to Cr(VI).

## 5.3 Shell transects

Placuna Placenta from Kakinada Bay: although some fluctuations in [Cr] and δ53Cr values beyond the statistical errors across the beak-margin profile of the studied Placuna placenta specimens exist (which we may attribute to local, seasonal, changes in seawater composition during growth and/or to changing reductive efficiencies during the calcification process), the studied specimen pretty much averages such environmental and biogenic changes out over its entire growth period estimated to be about 2 years. Here, we attribute the exceptionally high Cr concentration in the beak sample (CAP A) to increased, organic-rich components which seem to act as efficient Cr hosts, basically confirming our experiments on Mytilus edulis from Godhavn (Fig. 5). Chromium concentrations in this oyster from the Indian Ocean are comparable with those of the Mediterranean shells studied from Playa Poniente (Table 2, Fig. 4). In contrast, δ53Cr values of Placuna placenta are lower than those recorded in the Mediterranean bivalves and show values that are just about statistically distinguishable from the igneous Earth inventory value of $-\mathrm{0.12}±\mathrm{0.11}$ ‰ defined by Schoenberg et al. (2008). Lack of a respective surface seawater sample from Kakinada Bay itself does not allow for a concrete definition of the ΔCr value – the nearest surface seawater sample from which we have a Cr isotope composition available is from the Bay of Bengal with δ53Cr =0.55±0.08 ‰ (Paulukat et al., 2015). If we assume that the local surface seawater in Kakinada Bay has a similar Cr isotope composition, then ΔCr would be ∼0.5 ‰, an offset which is similar to that of Loripes lucinalis from Playa Poniente, but higher than most other species from this Mediterranean location.

Mimachlamys townsendi from Hawke's Bay: if Hawke's Bay surface seawater has a δ53Cr similar to that of the Bengal Bay (Paulukat et al., 2015; and assuming it has remained about the same since the collection of the Mimachlamys townsendi sample), then Mimachlamys townsendi exhibits the same ΔCR value (∼0.5 ‰) as Placuna placenta from Kakinada Bay. If calcification processes in Mimachlamys townsendi remained constant in terms of biogenic reduction of Cr(VI) to isotopically lighter Cr(III) over the several years of growth of the specimen studied, then this would signify a more or less constant δ53Cr of surface water in this location.

## 5.4 Individual shells – chromium distribution coefficients (DCr) between bivalve shell carbonates and seawater

Our sample sets from Playa Poniente and from Godhavn, which contain both surface seawater and bivalve shell data, allow for a direct calculation of the distribution coefficients (DCr) describing the partitioning of chromium between biogenic CaCO3 and seawater at the respective study sites. The DCr is calculated as

$\begin{array}{}\text{(1)}& {D}_{\mathrm{Cr}}=\left(\left[\mathrm{Cr}{\right]}_{{\mathrm{CaCO}}_{\mathrm{3}}}/\left[\mathrm{Cr}{\right]}_{\mathrm{seawater}}\right),\end{array}$

where [Cr]${}_{{\mathrm{CaCO}}_{\mathrm{3}}}$ represents the measured total concentration of chromium in the bivalve shell (CaCO3 and organic matter hosted) and [Cr]seawater the measured dissolved chromium concentration of the surface seawater at the respective location (e.g., 0.000300, 0.000176 and 0.000254 ppm, respectively, for Hawke's Bay/Kakinada Bay, Godhavn and Playa Poniente).

The calculated DCr values for biogenic carbonates are listed in Table 2. Our data span a wide range with values from 70 to 1297, but the upper data limit is characterized by a few exceptionally high DCr values, for example, that of sample Cap A (DCr=1297) and Pec H (DCr=820) from the respective hinges of the Placuna placenta species from Kakinada Bay and the Mimachlamys townsendi specimen from Hawke's Bay which probably are characterized by elevated organic matter. By far most samples have a more restricted DCr range with values between 70 and 640. The DCr range presented herein for bivalves is much more narrow compared to data from the study of Farkaš et al. (2018) in which those authors present DCr values spanning more than 3 orders of magnitude (from 79 up to 10 895) in marine biogenic carbonates from Lady Elliot Island and other worldwide locations. However, as Farkaš et al. (2018) note, skeletal carbonates (i.e., corals, mollusks) in their study tend to have systematically lower values (from ∼80 to ∼780) than microbial carbonates (i.e., calcifying algae) that yielded much higher DCr of ∼1000 and 2356. The range of DCr values for corals and mollusks in the study of Farkaš et al. (2018) otherwise compares well with the range of DCr values for bivalve shells in our study, and are within the range of DCr calculated for foraminifera that vary from ∼300 to 4000 (Wang et al., 2016) and with DCr values for corals in the range of 135 to 253 calculated from data in Pereira et al. (2015). Such high DCr values observed in biogenic carbonates produced by different marine organisms point to a strong biological control over the incorporation of Cr from seawater into CaCO3 skeletons, where it could be incorporated either as Cr(III) and/or Cr(VI) depending on species-specific redox cycling of Cr (cf. Wang et al., 2016; Semeniuk et al., 2016) and/or, as recently suggested, directly assimilated as organic ligand-bound Cr during biological uptake (Saad et al., 2017). It is too premature to compare the biogenic distribution coefficients with abiogenic values, simply because there is a lack of suitable modern seawater–carbonate pairs from which such values could be calculated. To our knowledge, the only suitable pair that allows for an estimation of a seawater–carbonate sediment distribution coefficient is that published by Holmden et al. (2016) for Jamaica. Using their average [Cr] of 140 ng kg−1 for Jamaican surface seawater and 9 ppm for Jamaican carbonate sediment (their Table 3), we calculate a DCr value of ∼64 000. This value is significantly higher than DCr values from biogenic carbonates calculated in this study and from data in Farkaš et al. (2018), and possibly point to the potential discrimination of Cr against incorporation into marine calcifying skeletons.

## 5.5 Evidence for isotopically fractioned Cr in bivalve shell carbonates

Our study confirms the outcome of previous investigations (Wang et al., 2016; Pereira et al., 2015; Farkaš et al., 2018) showing that marine (skeletal and non-skeletal) biogenic carbonates are characterized by isotopically variably fractionated, but systematically 53Cr enriched Cr compositions that have δ53Cr values above the Earth's igneous inventory value of 0.12±0.11 ‰. From data which allow direct comparison with ambient seawater compositions, including those presented in this study, it can also be deduced that the biogenic carbonates so far analyzed all have Cr isotope compositions which are depleted in 53Cr relative to respective seawater values, implying redox cycling, in particular reductive processes, to take place somewhere during the uptake and calcification processes.

In order to explain the isotopically light Cr incorporated in coral skeletal carbonate, Pereira et al. (2015) propose a mechanism whereby initial photoreduction of isotopically heavy Cr(VI) in the surface seawater to isotopically lighter Cr(III) in the endodermal layer of corals must be followed by efficient and effective reoxidation of reduced Cr species to favor subsequent chromate (${\mathrm{CrO}}_{\mathrm{4}}^{\mathrm{2}-}$) substitution during the calcifying processes ultimately leading to the coral skeleton.

## 5.6 Biomineralization/calcification and incorporation of chromium into shells

A central question is that regarding the mechanisms on how dissolved chromium from the seawater behaves during biomineralization and calcification processes, and ultimately how it is incorporated into marine biogenic carbonates. It becomes evident from recent studies (Wang et al., 2016; Pereira et al., 2015; Farkaš et al., 2018) that redox mediated processes play a role during calcification because marine biogenic carbonates measured so far are all characterized by significantly 53Cr depleted (i.e., isotopically lighter) signatures relative to ambient seawaters. Reduction processes of dissolved Cr(VI) complexes to Cr(III) species in ocean water have been used by Scheiderich et al. (2015) and Paulukat et al. (2016) to explain the δ53Cr variations in the world's oceans. Scavenging of isotopically light Cr(III) to deeper water and sediment, potentially by phytoplankton (Semeniuk et al., 2016), and subsequent release of this seawater-derived Cr(III) back into seawater, either as organic complexes with Cr(III) or after oxidation to Cr(VI), are advocated as potential processes to explain the δ53Cr vs. [Cr] fractionation trend in seawater.

It is unclear whether Cr can be directly incorporated into the carbonate structures as Cr(VI) forming part of CrO${}_{\mathrm{4}}^{\mathrm{2}-}$ compounds or whether reduced species of Cr(III) can be assimilated/adsorbed or structurally bound into skeletal carbonates or associate with a multitude of known organic matrices contained within and along cleave/grain boundaries of calcifying layer carbonates. In one way or the other, models that address the mechanisms of Cr uptake during calcification processes need to involve the fact that bulk marine biogenic carbonates are isotopically lighter than ambient seawater in which they are formed. Pereira et al. (2015) proposed a model for skeletal carbonates of corals whereby initial photoreduction of isotopically heavy Cr(VI) to isotopically lighter Cr(III) in the endodermal layer of corals must be followed by efficient and effective reoxidation of reduced Cr species to favor subsequent chromate (${\mathrm{CrO}}_{\mathrm{4}}^{\mathrm{2}-}$) substitution during the calcifying processes ultimately leading to the formation of the coral skeleton.

A vast number of studies dedicated to biomineralization processes of marine biogenic carbonate producers have recognized the importance of organic network matrices (Griesshaber et al., 2013), and of organic macromolecules in particular (e.g., Suzuki et al., 2011; Okumura et al., 2013), in the organic–inorganic interaction in biomineralization of, particularly, molluscan shells. Major components of the shell are calcium carbonate, which ordinarily exists as a crystalline polymorph, either calcite or aragonite. The type of polymorph, crystal orientation, morphology and texture of the crystals are regulated in the shell. Studies have shown that shells are not composed of purely inorganic carbonate crystals but contain small amounts of organic substances to regulate the structure and property of these crystals (e.g., Falini et al., 1996; Belcher et al., 1996; Okumura et al., 2013). Suzuki et al. (2011) visualized intracrystalline spherular structures in shell carbonates containing carbon from organic macromolecules. The size of the spherules identified by these authors roughly corresponded to that of soluble organic macromolecules that these authors extracted from the nacreous layer (innermost layer of the shell of a mollusk secreted by the mantle epithelium layer). Their function for the crystal formation of molluscan shells remains unclear though. A comprehensive review on the presence and role of organic matrices for the growth of mollusk shells is contained in Suzuki and Nagasawa (2013).

Figure 8Schematic representation of a simplified model for the transfer of chromium from an extrapallial fluid within an interlamellar space into shell carbonate nuclides (modified from Suzuki and Nagasawa, 2013). The insoluble frameworks consist of chitin (black and long rectangles) that make a scaffold to supply the space for precipitation of calcium carbonate crystals. (a) The interlamellar space is filled with a supersaturated extrapallial fluid with respect to ${\mathrm{CO}}_{\mathrm{3}}^{\mathrm{2}-}$ and Ca2+. Cr(VI) likely occurs as dissolved compounds in the fluid and is eventually reduced to isotopically lighter Cr(III) by dissolved organic macromolecules (gray circles) onto which it is efficiently adsorbed. Insoluble matrix proteins (gray discs) have the hydrophobic region for organic macromolecules (protein) – chitin interaction and the hydrophilic – acidic region for the calcium carbonate binding ability to mediate the connection between the organic scaffolds. (b) The soluble matrix proteins that have a hydrophyllic region for calcium carbonate binding adhere to the chitinous layers and probably regulate nucleation, crystal polymorph and crystal orientation of inorganic calcium carbonate crystals (gray rectangles). (c) As the crystals grow, insoluble matrix proteins are used for organic framework formation as intercrystalline organic matrices and soluble matrix proteins, including adsorbed Cr(III), are eventually included in the calcium carbonate crystals as intracrystalline organic matrices. Cr(VI) potentially present as chromate (${\mathrm{CrO}}_{\mathrm{4}}^{\mathrm{2}-}$) ions likely also substitute for carbonate (${\mathrm{CO}}_{\mathrm{3}}^{\mathrm{2}-}$) ions directly in the calcium carbonate lattice (Tang et al., 2009).

We would like to focus our attention on the potential role of organic matrices as hosts for Cr in mollusk shells. A hint that organics may play a defining role stems from our few results which compare [Cr] in incinerated shell material to corresponding [Cr] in aliquots which were attacked with aqua regia to preferentially attack the carbonate. While it is clear from our study of Mytilus edulis from Godhavn with an apparent organic-rich periostracum that this outermost shell layer itself may contain elevated [Cr], based on a similar result (cf. Fig. 3, Table 2) performed on Loripes lucinalis from Playa Poniente where the actual periostracum has been mechanically removed by tidal abrasion in the beach sand, we suspect that organics contained in the nacreous layer are equally important as potential Cr hosts. In all cases (see above and Table 2) we note significantly higher [Cr] in the ashed samples, which we see as a consequence of effective release of organic-material-bound Cr (otherwise only weakly attached, or even not attacked at all, by the hydrochloric acid) during burning of the organic material. So, for example, Suzuki et al. (2007) hydrolyzed the insoluble organic matrices from the prismatic layer in the mollusk shell with 6 M HCl. These authors detected D-glucosamine hydrochloride, known as a degradation product of chitin, using nuclear magnetic resonance spectroscopy measurements. In the nacreous layer of mollusk shells, chitin serves as the major component of the organic framework, building up the compartment structure and controlling the morphology of calcium carbonate crystals (Falini and Fermani, 2004).

## 5.7 A model explaining the occurrence of Cr in molluscan shells

Adopting the schematic framework that includes the representation of the localization and function of organic matrices with respect to calcium carbonate crystals in the nacreous layer of mollusks we would like to propose a model that explains the transfer of Cr from the water into the calcifying space and the incorporation of Cr into shell carbonates (Fig. 8). During adult shell formation, the periostracum, which is not mineralized and covers the external surface of the shell, is formed first, and the calcified layer subsequently forms on the periostracum (e.g., Checa, 2000). The shell is in contact with the mantle, which supplies the periostracum and calcified layers with inorganic ions and organic matrices through the extrapallial fluid (for a review, see Marin et al., 2012). This fluid also contains organic molecules. As the fluid is supersaturated with respect to calcium carbonate, these macromolecules – in particular acidic proteins and GAGs (group specific antigen) – are supposed to transiently maintain calcium in solution, by inhibiting the precipitation of calcium carbonate, and by allowing it to precipitate where needed (Marin et al., 2012). The manner in which the inorganic precursors of calcification are driven to the site of mineralization is still speculative. Figure 8 schematically shows the growth front in an interlamellar space of the nacreous layer, confined by chitinous membranes, as proposed by Suzuki and Nagasawa (2013). We emphasize that under neutral to basic pH, as inferred for an extrapallial fluid, Cr is present either as dissolved Cr(VI) compound, as Cr(III) species adsorbed onto organic macromolecules and/or as dissolved organic substances. The fact that δ53Cr measured in bivalve shells is systematically lower than ambient seawater implies that reduction of dissolved Cr(VI) in seawater, transferred to the calcifying space, is likely promoted by the organic macromolecules, which are densely localized on the surface of the interlamellar membranes (Suzuki and Nagasawa, 2013; Suzuki et al., 2011). So-formed isotopically light Cr(III) species, effectively adsorbed onto organic macromolecules, adhere to the chitinous membranes where they are incorporated inside growing carbonate crystals filling the space, whereas other organic molecules cover the surface of these crystals. Some Cr might also be directly incorporated into the carbonate lattices during growth, where chromate ions may coprecipitate with calcite (Tang et al., 2007). In such a scenario, the measured bulk δ53Cr values of mollusk shells would reflect a mixture of both Cr(VI) and Cr(III) characteristic of the ambient seawater and an isotopically lighter, Cr(III) fraction ultimately associated with the organic molecules in the shells. The exact δ53Cr value would depend on the extent of reduction and specific metabolism. A small extent of reduction would lead to low δ53Cr values while quantitative reduction of dissolved Cr(VI) would lead to similar to seawater values.

## 5.8 Inter- and intra-species shell variations

While from the studies conducted earlier (e.g., Pereira et al., 2015; Wang et al., 2016) and from this study it is now evident that marine biogenic carbonates are characterized by δ53Cr values that are less fractionated compared to ambient seawater, it remains unclear whether these isotopic offsets are species dependent. Wang et al. (2016) observed large δ53Cr variations between foraminifera species within and among samples. As advocated by these authors, the variation in δ53Cr among different samples of the same species could be explained by heterogeneous seawater δ53Cr. However, Wang et al. (2016) also found that foraminifera species with similar depth habitats from the same core-top sample also yielded different δ53Cr values. Species-dependent δ53Cr variations are furthermore complicated by the observation that species with shallower water depth habitats yielded consistently lower δ53Cr than species preferring deeper water environments, which is opposite to the general patterns expected in seawater δ53Cr (Bonnand et al., 2013; Scheiderich et al., 2015). These observations hint at the possibility that species-dependent biological (metabolic) processes may play a major role in controlling Cr isotope fractionation during biomineralization/calcification processes of marine biogenic carbonate producers in general, not only in foraminiferal calcification. Our data herein contribute to a more systematic assessment of the above: the systematic sampling of some bivalve species from the same location over several years, together with respective ambient surface seawaters, reveals that subtle inter-species differences in average bulk δ53Cr signatures exist amongst different species. Although five species (Calista chione, an unidentified species of Cardiidae, Chamelea striulata, Glycymeris glycymeris, and Pecten jacobaeus) at the 2σ level cannot be statistically distinguished by their average δ53Cr values (Fig. 3), Loripes luncinalis is an exception and yielded, on average, lower δ53Cr values than the other species. Thus, while we observe subtle differences in the average δ53Cr signatures of individual bivalve species from Playa Poniente, intra-species variations, as observed by Wang et al. (2016) for certain foraminifera, are statistically not discernable. The exception to this are two samples of Arca Navicularis, sampled simultaneously in 2015, which both show distinctly different δ53Cr signatures of 0.570 and 0.166 ‰, and also significantly different [Cr] of 0.052 and 0.166 ppm, respectively. We are unable, at this point, to explain these discrepancies observed in Arca Navicularis. Last but not least, while [Cr] in the samples studied scatter considerably between ∼0.03 and 0.10 ppm and do not correlate with bivalve species, there is an exception to this which is reflected by the data of Pecten jacobaeus. The three samples of this species all revealed elevated [Cr] in the range of 0.127 to 0.163 ppm (Table 2, Fig. 3). Whether or not the intensity of pigmentation (Pecten jacobaeus shows a red pigmentation that increases from the hinge to the margin of the shell; Fig. 2) is not clear, but it could partially explain the increased [Cr] scatter in the analyses from Glycymeris glycymeris (cf. Fig. 2, Table 2) which exhibits similar variations in pigmentation amongst individual samples. Importantly, however, is the fact that the increased scatter of [Cr] does not seem to translate into an increased scatter of bulk δ53Cr values of the bivalve shells studies, nor does [Cr] seem to correlate with δ53Cr in any of the species studied either. If, as emphasized in our preferred scenario, [Cr] in the bivalve shell is significantly associated with organic matter, it implies that intralamellar reductive processes eventually lead to adsorption of isotopically light Cr(III) onto organic macromolecules. The production rate of these macromolecules are likely metabolically controlled/buffered prior to their encapsulation into the shell carbonates. This is maybe best exemplified by the Mytilus edulis sample suite from Godhavn. This suite of samples reveals limited intra-species variations both in δ53Cr and [Cr] among the six half shells analyzed, which we take as an indication for an effective and stabilizing biological control, potentially via organic macromolecule production, of biomineralization processes in general, and of Cr incorporation into the shell carbonates.

Figure 9Bar graph showing the conservative offset ranges (ΔCr) of δ53Cr values of bivalve species from ambient seawater. The larger range of Placuna placenta is due to within-shell heterogeneities probably resulting from seasonal surface seawater fluctuations which are smoothed out by the bulk shell analyses of the other species (see text for details).

Our study may eventually also contribute to the understanding of the environmental stability over relevant growth periods (several years) around the calcifying space of bivalves. However, such investigations are dependent on the knowledge of the seawater Cr isotope composition during the respective growth periods (in our case during growth of the Placuna placenta from Kakinada Bay and the Mimachlamys townsendi sample form Hawke's Bay Beach, which we do not have at hand. It is strongly perceivable that surface seawater conditions at a specific location are not, and have not been , constant, and this has been shown for the δ53Cr values of surface water from the Baltic Sea by Paulukat et al. (2016). These authors correlated seasonal fluctuations in δ53Cr with algae bloom periods, and thus with the seasonal presence of strong Cr(VI) reducers capable of considerably depleting the [Cr] in the surface waters by reductive adsorption mechanisms. Seasonal fluctuations could explain the sinusoidal δ53Cr growth pattern in the studied Placuna placenta shell (Fig. 6) whose size roughly implies a ∼1-year growth period. Likewise, small fluctuations in Mimachlamys townsendi of δ53Cr signatures over the entire growth period of the specimen studied could reflect seasonal changes in the ambient surface seawater during this several years long growth period. However, we want to emphasize that these intra-shell δ53Cr fluctuations, in the order of ±0.15 ‰, compare well with inter-species fluctuations of the same order observed in all the Playa Poniente bivalve species. This makes the average δ53Cr signature of a bivalve shell still a valuable parameter which, given that the isotopic offset from ambient seawater is known, potentially can be used for recording the seawater Cr isotope signature prevailing at the habitat location of the respective bivalve.

## 5.9 A first attempt to define average δ53Cr offsets of specific bivalves from ambient seawater

Our data set allows for a preliminary definition of Cr isotope offsets between certain bivalve species and ambient seawater, which potentially could be used in paleo-seawater reconstructions using suitable fossil aliquots. Instead of using average δ53Cr values defined by our sample suites, and average seawater δ53Cr values, we prefer to define such offsets (ΔCr) conservatively, using bandwidths (rather than comparing average values) that take analytical uncertainty into consideration (i.e., minimum ΔCr values defined by difference between (δ53Cr + 2σ)sample and (δ53Cr  2σ)seawater; maximum ΔCr values defined by difference between (δ53Cr  2σ)sample and (δ53Cr + 2σ)seawater). These ranges are listed in Table 3 and plotted in Fig. 9 for all species where we have multiple analyses and ambient seawater values. The ΔCr offset range of Placuna placenta is not strictly comparable to the other values as it includes growth segment analyses covering the growth period of the entire shell. These introduce enhanced scatter that is most likely due to seasonal changes in seawater, a factor which is smoothed out by the analyses of entire shells as is the case for the other species. This explains the rather large ΔCr range calculated for Placuna placenta.

Although preliminary (additional data need to be collected to more precisely define species-dependent ranges), our data allow for a first order estimation on the use of the ΔCr seawater offset ranges defined herein to ultimately reconstruct the local surface seawater redox state. On average, δ53Cr values of ambient seawater can be reconstructed to $\sim ±\mathrm{0.3}$ ‰. At first sight, this seems to be rather imprecise, but considering that surface seawaters today exhibit δ53Cr variations between +0.13 ‰ and +1.24 ‰ (Paulukat et al., 2016), this uncertainty nevertheless allows for placing reconstructed seawater compositions into a meaningful redox framework. The usefulness of this tool for the reconstruction of paleo-seawater compositional changes awaits the assessment, testing and acquisition of Cr isotope composition of fossil calcifiers that can be compared to data from modern respective species.

6 Conclusions

We have conducted bulk δ53Cr and [Cr] analyses of a set of common bivalve species from two locations, one at Playa Poniente on the Mediterranean Sea, and one from Disko Bay in the arctic North Atlantic, from where we also measured the ambient seawater. Collection of the same species during a specific period in July over several years, and of multiple samples from some of the species, allowed us to monitor the stability of Cr isotope signatures in each of the species, and to define long-term δ53Cr offsets from ambient seawater. The outcome of our study can be summarized as follows:

1. The local surface seawater Cr isotope composition and [Cr] at Playa Poniente at times of sample collection over a 3-year period is surprisingly homogenous, with δ53Cr =0.83±0.05 ‰, and with [Cr] =254±54 ng kg−1.

2. Offsets (ΔCr) from different bivalve species from this value show subtle differences, with typical values of ∼0.3 ‰ to 0.4 ‰ lower than ambient seawater. Of all the species investigated, Loripes lucinalis exhibits the largest ΔCr of ∼0.6 ‰. The systematically lighter Cr isotope compositions of all bivalves studies herein relative to ambient seawater confirms earlier studies by Pereira et al. (2015) on corals, by Wang et al. (2016) on foraminifera and by Farkaš et al. (2018) for various marine calcifiers from a location in the Great Barrier Reef.

3. Recognizing the importance of organics in the shell structures of bivalves, and considering our results from incinerated vs. solely 6N HCl dissolved bivalve shells systematically showing recovery of higher [Cr] in ashed samples, we propose a model whereby reduction of Cr(VI) originally contained in the seawater and transported to the calcifying space, to Cr(III), and its effective adsorption onto organic macromolecules that adhere to chitinous interlamellar coatings, plays a central role. In such a scenario, organic-matter-bound, isotopically light Cr forms preferable loci for the nucleation of carbonates, and it is eventually included into the growing shell carbonates, possible together with dissolved chromate that may substitute for ${\mathrm{CO}}_{\mathrm{3}}^{\mathrm{2}-}$ directly in the carbonate lattice.

4. Inter-species Cr isotope variations, tested on a suite of contemporaneously sampled alive Mytilus edulis samples from Godthavn (Disko Bay), are small (in the range of δ53Cr $=±\mathrm{0.05}$ ‰) and independent of [Cr]. Although not knowing the exact host of Cr in these shells (periostracum, organic macromolecules, chitinous interlamellar membranes etc.), the homogenous Cr isotope composition measured in this suite of samples renders Mytilus edulis a potential archive for the reconstruction of the redox state of ambient local seawater. This needs to be verified by studies of this species from other locations before attempts to use fossil aliquots for the reconstruction of paleo-seawater redox fluctuations.

5. Intra-shell variations in δ53Cr and [Cr] over respective entire growth periods was investigated in two examples, a sample of Placuna placenta (windowpane oyster, Capiz) and a sample of Mimachlamys townsendi (Pecinidae) from Kakinada Bay (Bay of Bengal) and from Hawke's Bay Beach (Karachi, Pakistan). We observe subtle fluctuation of both parameters of the growth period of ∼1 years and several years, respectively, which are in the order of 0.1 to 0.2 ‰. These fluctuations may arise from either seasonal changes in ambient seawater compositions and/or from metabolic instabilities in the calcifying space affecting reduction of Cr(VI) and production of organic macromolecules.

6. Our study can be used as a base for more detailed future investigations of marine biogenic carbonates, including fossil marine calcifiers, aimed at the reconstruction of paleo-seawater redox state fluctuations, and eventually to correlate these with climate change aspects in certain periods of Earth's history.

Data availability
Data availability.

All complete data sets are contained in the two tables.

Author contributions
Author contributions.

RF initiated the study and collected the samples; RF and CP processed the samples through the chemistry and performed the mass spectrometric analyses, and hosted continuous discussions through the lengthy project period amongst all co-authors (RF, CP, SB and RK), which led to substantial improvement, enhanced understanding, important modifications and adaptations of the original research ideas. RF prepared the manuscript with contributions from all co-authors.

Competing interests
Competing interests.

The authors declare that they have no conflict of interest.

Acknowledgements
Acknowledgements.

We would like to thank Toby Leeper for always maintaining the mass spectrometers in perfect running condition and Toni Larsen for lab assistance. Financial support through the Danish Agency for Science, Technology and Innovation grant number 11-103378 to RF is highly appreciated. Bo Elberling is thanked for providing us with samples from arctic Godhavn. We thank two anonymous reviewers and associate journal editor Aninda Mazumdar for their constructive comments that helped improve the initially submitted manuscript.

Edited by: Aninda Mazumdar
Reviewed by: two anonymous referees

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