Abstract
A refined method for the isolation, purification, and high precision measurement of Ru isotope compositions in natural samples by negative thermal ionization mass spectrometry (N-TIMS) is reported. After chemical purification of Ru using ion exchange chromatography and microdistillation techniques, the Ru isotopic composition is measured as RuO3− via N-TIMS. Data are corrected for oxide interferences using the simultaneously measured oxygen isotope composition, and subsequently for mass fractionation using an exponential law. Repeat analyses of an Alfa Aesar Ru standard solution demonstrate external reproducibility of 100Ru/101Ru to ±6.4 ppm (2SD). This level of precision is more than two times better than prior techniques. Repeat analyses of gravimetrically prepared mixtures of a natural Alfa Aesar Ru standard and a 100Ru enriched spike show that isotopic differences of ≥13 ppm can be resolved by single measurements of a material using this method. Repeat analyses of diverse terrestrial materials (chromitites and Os-Ir-Ru alloys) are characterized by compositions that are identical to the Alfa Aesar standard, and the external reproducibility for these materials is also identical to that of the chemically pure standard, demonstrating that chemical separation/purification methods introduce no bias to the analysis. These materials likely define the Ru isotopic composition of the Earth’s mantle.
Keywords: Ruthenium isotope, 100Ru, Thermal ionization mass spectrometry, N-TIMS
1. Introduction
Mass-independent nucleosynthetic isotopic anomalies have been observed in Ru present in whole rock meteorites and their components [1–7]. The nature and magnitude of the anomalies have been used to investigate the stellar origins of matter in our solar system, as well as nebular mixing processes. Ruthenium isotopes (96Ru = 5.52%; 98Ru = 1.87%; 99Ru = 12.8%; 100Ru = 12.6%; 101Ru = 17.1%; 102Ru = 31.6%; 104Ru = 18.6%) are well suited for this task. This is because of the diverse nucleosynthetic processes by which Ru isotopes were made (p-, s-, r-process; [33]), and the high condensation temperature of Ru (Tc = 1565 K, where Tc is the temperature at which 50% of the element is condensed; [8]). Additionally, there are two short-lived chronometers associated with the Ru isotope system, 98Tc-98Ru and 99Tc-99Ru (t1/2 = 4.2–10 Ma and t1/2 = 0.21 Ma, respectively; [9]). Conclusive evidence for either chronometer, however, is yet to be identified. Further, given the variations in Ru isotopic compositions among early solar system materials, Ru isotopes show great promise for providing genetic fingerprints of diverse, late-stage accretionary additions to the Earth and Moon [10, 11]. This is possible because the Ru present in, for example, lunar impact melt rocks produced by basin-forming events, is primarily derived from the impactor (e.g., [12]).
High precision isotopic analytical capability is required to fully pursue these cosmochemical and geochemical objectives. Ruthenium isotopes have previously been measured using either thermal ionization mass spectrometry (TIMS; [6, 13]) or multiple-collector inductively coupled plasma mass spectrometry (MC-ICP-MS; e.g., [7, 14]). The current state-of-the-art for 100Ru/101Ru is ±31 ppm using TIMS [6] and ±13 ppm using (MC-ICP-MS [7]), where uncertainties are 2SD, defined by repeat analyses of laboratory standards. Here, we present refined chemical and mass spectrometric procedures to precisely measure Ru isotopic compositions in natural samples. The new method offers a better than twofold improvement in precision for some Ru ratios, compared to the existing techniques.
2. Methods
2.1. Samples
The in house laboratory standard used in this study was a Ru Alfa Aesar Specpure® plasma standard solution (1000 μg/ml, RuCl3 in 20% HCl). In order to confirm that our chemical isolation/purification and measurement procedures did not impart systematic biases, as well as to define the Ru isotopic composition of modern terrestrial mantle, chromitites from the 492 Ma Shetland ophiolite complex [15] and Os-Ir-Ru alloy grains from the 162 Ma Josephine ophiolite complex [16] were analyzed (EA1). In order to test the procedures for cosmochemical materials, and to enable comparisons of data with data from prior studies, the group IVB iron meteorite Hoba was also analyzed (EA1). Each sample type has a chemically distinct matrix, thus making this suite well suited to testing the robustness of our chemical separation and mass spectrometric protocols.
2.2. Sample preparation
Chromitites (C1, C2, C3) were cut into 2–3 g pieces using a MK Diamond Products (Inc.) water-cooled tile saw with a 25.4 cm diameter diamond blade. The pieces were abraded using silicon car-bide sandpaper, in order to remove visible saw marks, rinsed with distilled water, and then fragmented into 0.1–0.5 g chips using a hammer wrapped in plastic film. The fragments were then carefully ground to a fine (~10 μm) powder using an agate mortar and pestle dedicated to chromitites and other terrestrial rocks with high Ru abundances. Between samples, the mortar and pestle were mechanically cleaned by grinding multiple aliquots of silica grains, using new aliquots of silica grains each time. The mortar and pestle were then cleaned in dilute aqua regia overnight at ~40 °C, followed by a few hours in Milli-Q (water deionized to a resistivity of 18.2 MΩcm) at the same temperature. The Os-Ir-Ru alloy grains analyzed here are a small subset of the grains studied in [16]. No sample preparation prior to digestion was required. Approximately 10 g of the meteorite Hoba was obtained from the Smithsonian Institution National Museum of Natural History (USNM 6506). The sample was cut into a 0.7 g piece using a distilled water-cooled Leco “Vari-cut” saw with a 12.7 cm diamond wafering blade. The blade was cleaned with carborundum before cutting the sample (as detailed in [17]). Pieces with or near fusion crust and rust patches were avoided. The cut sample was abraded using silicon carbide sandpaper, and then sonicated in Milli-Q water three times for 10 min at a time, using fresh Milli-Q water each stage. This was done to remove any adhering material from the sample.
2.3. Sample digestion
The Carius tube digestion technique employed to digest chromitites and Os-Ir-Ru alloys is based on the method adapted by [18]. Between 0.9 and 1.2 g of a powdered chromitite sample, or a single Os-Ir-Ru alloy grain (0.05–0.1 g), 3 ml of quartz-distilled concentrated hydrochloric acid (HCl) and 6 ml of quartz-distilled concentrated nitric acid (HNO3) were placed in a chilled, thick-walled Pyrex® Carius tube. The distilled acids were made from either Sigma Aldrich® ACS grade or BDH Aristar® ACS grade commercial acids. The Carius tube was sealed promptly after addition of the acids in order to avoid possible loss of volatile RuO4 (boiling point (BP) = 40 °C; [19]), which is produced on the addition of an oxidizing agent to a sample. Digestions of the samples were performed at 240 °C for 4–5 days. Although not critical here, complete dissolution of the sample was typically not achieved. After digestion, the Carius tube was chilled in an ice bath, opened, and the acid phase was transferred to a 60 ml Savillex Teflon® beaker containing ~20 ml of quartz-distilled 6 M HCl. The mixed solution was gently dried down to ~2 ml using an ultraviolet heat lamp. The solution from the Carius tube was mixed with the 6 M HCl to promote the reduction of the volatile RuO4 to a non-volatile form, thus reducing its loss during evaporation. The gentle and incomplete dry down at this stage also limited the loss of RuO4. Approximately 5 ml of 6 M quartz-distilled HCl was added to the beaker to continue converting the Ru in solution to a chloride form. This solution was gently evaporated down to ~1 ml of residual solution. This step was repeated once.
At this point, Os-Ir-Ru alloy samples were dried down to ~0.2 ml and transferred to the cap of a 5 ml conical bottom Savillex Teflon® beaker for microdistillation, as described below. The Ru present in the chromitite samples, however, required further purification before microdistillation, and this was achieved by separating the Ru from the matrix via ion exchange chromatography. In preparation for this, the remaining ~1 ml of solution was evaporated down to a slurry using the heat lamp, after which 5 ml of 0.15 M quartz-distilled HCl was added. This solution was again evaporated to slurry, subsequently taken up in 10 ml of 0.15 M quartz-distilled HCl, and left to dissolve at room temperature. The sample was then transferred to a 10 ml centrifuge tube and centrifuged for 10 minutes at 7000 rpm. The supernatant was then removed for ion exchange chromatography.
The sanded and sonicated meteorite piece was added to 30 ml of 9 M quartz-distilled HCl in a 60 ml Savillex Teflon® beaker and left capped at 130 °C on a hotplate for 12 h to digest. Following this, another 20 ml of 9 M quartz-distilled HCl was added to the beaker. The beaker was sonicated for 10 min, and then returned to the hot-plate and left at 150 °C for 24 h. After this treatment, the sample was completely dissolved. The sample was then gently evaporated to slurry, after which 5 ml of 0.15 M HCl was added, and the solution again slowly evaporated to slurry. The slurry was taken up in 5 ml of 0.15 M quartz-distilled HCl and left to dissolve at room temperature. The sample was transferred to a 10 ml centrifuge tube and centrifuged for 10 min at 7000 rpm. Finally, the supernatant was removed for ion exchange chromatography.
2.4. Ion exchange chromatography
Ruthenium has commonly been isolated using one- or two-stage ion exchange chromatographic procedures and then further purified using microdistillation [6, 7, 20]. Consistently achieving high recovery and high purity Ru with these techniques has been problematic. This is mainly due to the tendency of Ru to exist in multiple oxidation states (0 to +8; [21]), many of which exhibit different redox potentials and cation/anion exchange behaviors. This can lead to loss of Ru during chemical purification, as well as variable efficiency of chromatographic separations and microdistillation.
In this study, a two-step ion exchange chromatographic procedure was initially adapted from previous studies (e.g., [6, 20]), in order to isolate Ru from the large amount (~1 g) of sample matrix used for chromitite and meteorite analyses. This method works by removing the majority of chromium (chromitites) or iron (iron meteorites) from the Ru and other highly siderophile elements (HSE: Re, Os, Ir, Pt, Rh, Pd, Au), in a primary (1°) cation column using an HCl-based chemistry. Ruthenium is separated from the other HSE using a secondary (2°) anion column, and an HCl-HNO3 based chemistry (Table 1). The yields, however, from the 2° column were only ~50%. This is likely a result of on-column reduction and retention of Ru-complexes in different oxidation states during the elution protocol, in addition to the loss of some RuO4 during evaporation of the Ru-Re fraction (HNO3). Subsequently, for those samples requiring column chromatography, better Ru yields were achieved by proceeding directly from the 1° column chemistry to a microdistillation.
Table 1.
Acid | Volume (ml) | Step |
---|---|---|
1° cation column: 2–4 Biorad columns filled with 10 ml of pre-cleaned AG50WX8 (200–400 mesh) | ||
Milli-Q water | 20 | Resin cleaning |
6M HCl | 10 + 10 + 10 + 10 | Resin cleaning |
Milli-Q water | 20 | Resin cleaning |
0.15 M HCl | 10 | Backwash |
0.15 M HCl | 10 | Equilibration |
0.15 M HCl | 2.5 | Load |
0.15 M HCl | 1 + 1 +1 + 5 | Rinse HSE |
6 M HCl | 1 + 1 + 1 + 27 | Rinse matrix |
6 M HCl | 10 + 10 + 10 + 10 + 10 + 10 | Resin cleaning |
Milli-Q water | 20 | Resin cleaning |
2° anion column: 1 Biorad column filled with 3.8 ml of pre-cleaned AG1X8 (200–400 mesh) | ||
Milli-Q water | 10 | Resin cleaning |
Concentrated HNO3 | 10 + 10 | Resin cleaning |
Milli-Q water | 5 | Resin cleaning |
Concentrated HCl | 10 | Resin cleaning |
Milli-Q water | 5 | Resin cleaning |
1 M HCl | 3 | Backwash |
1 M HCl | 4 | Equilibration |
1 M HCl | 1 | Load |
0.5 M HCl | 2 | Matrix, Mo |
0.8 M HNO3 | 0.5 | Matrix, Mo |
0.8 M HNO3 | 5 | Zn, Cd, Mo |
8 M HNO3 | 10 | Ru, Re |
Concentrated HNO3 | 4 | Ru, Re |
Concentrated HNO3 | 10 | Pt, Ir |
11 M HCl | 2 | Pt, Ir, Ag |
11 M HCl | 8 | Pd |
Concentrated HNO3 | 5 | Pd |
In detail, the 1° column cation exchange chromatography used ~10 ml of pre-cleaned Eichrom AG50WX8 200–400 mesh cation exchange resin equilibrated in Milli-Q water (see EA2 for pre-cleaning steps and Table 1 for elution protocol). This resin was transferred to a Biorad column (1.5 cm × 12 cm) as a slurry, then further cleaned using 4× 10 ml 6 M HCl (quartz distilled). The columns were then equilibrated using 10 ml 0.15 M HCl. Each sample was split into two to four 2.5 ml aliquots, and each aliquant (2.5 ml0.15 M HCl) was loaded onto a separate column, such that each column was used to process ~250 mg of sample. The HSE are not retained on the cation exchange column in low molarity HCl, in contrast to the major elements (e.g., Cr+3, Fe+2, Fe+3; [22]). Thus, the HSE were directly collected in 8 ml of 0.15 M HCl after loading. The matrix, which largely remains on the column after HSE elution, was subsequently eluted using 30 ml 6 M HCl. Recovery of HSE per column was >90%. The total procedural blank for Carius tube digestion and 1° column chemistry was 110 ± 63 pg (n = 4). The total procedural blank for digestion in Savillex Teflon® beakers and 1° column chemistry was 6.1 pg (n = 1). These blanks are ≪1% of the total Ru measured for each sample here, and are inconsequential for the measurements reported.
The 2° column utilized anion exchange chromatography to separate Ru from the other HSE. It is based on methods described in[20]. Approximately 3.8 ml of pre-cleaned Eichrom AG1X8 anion exchange resin (200–400 mesh; see EA2 for pre-cleaning procedure and Table 1 for elution protocol) equilibrated in Milli-Q water was transferred to a Biorad column (0.8 cm × 4 cm) as a slurry and further cleaned using 20 ml concentrated HNO3, 10 ml Milli-Q water, 10 ml concentrated HCl, and finally 10 ml of Milli-Q water. The resin was then washed using 3 ml of 1 M HCl, and equilibrated using 4 ml of 1 M HCl prior to sample loading. One sample was processed per anion column. Samples were loaded onto the anion resin in 1 ml of 1 M HCl. Matrix elements (and Mo) were rinsed from the resin using 2 ml of 0.5 M HCl and 0.5 ml of 0.8 M HNO3. Zinc, Cd, and traces of Mo were then eluted using 5 ml of 0.8 M HNO3. Rhenium and Ru were then eluted together using 10 ml of 8 M HNO3 and 4 ml concentrated (14 M) HNO3. Recovery of Ru for this column was ~50%. The total procedural blank for digestion and 2° column chemistry was 28 ± 21 pg (n = 7). This blank is ≪1% of the total Ru measured for each sample here inconsequential for the measurements reported here.
2.5. Microdistillations
Following ion exchange chromatography, Ru was purified by microdistillation. This technique was originally developed to purify Os [23, 24], however, given the similarity in volatility of high valence RuO4 (BP = 40 °C; [19]) and OsO4 (BP = 129.7 °C; [19]), this technique can also be used to purify Ru and remove organics which may be present following column chromatography [25]. Here, microdistillations were conducted in 5 ml conical bottom Savillex Teflon® vessels, where the sample and oxidant were placed on the cap and a reductant held in the tip of the beaker. Initially, the distillation vessel was placed in a steel block with a stainless steel jacket placed around the body of the beaker. This left the tip of the beaker exposed to the atmosphere to promote warming and oxidation of Ru in the lower part of the vessel, while keeping the top part of the beaker cool to promote reduction of RuO4. This design, however, was not found to improve recovery yields and was abandoned.
A significant issue in the microdistillation of Ru is achieving consistently high yields. Efficient distillation of Ru requires a strong oxidant to oxidize the Ru, and a strong reductant to reduce the captured Ru in the trap solution. In an effort to improve the recovery of purified Ru, a number of different oxidants and reductants, distillation temperatures, and distillation reaction times were tried. Oxidizing reagents tested for microdistillations included acidified ceric sulfate and acidified (sulfuric acid) dichromic acid (H2Cr2O7), and reducing (trapping) reagents included concentrated double quartz distilled hydrobromic acid (HBr), 6 M HCl-ethanol (50:50), and 6 M HCl. Different combinations of the reagents listed above were tested at temperatures ranging from ca. 25 °C to 120 °C for periods between 2 h and 48 h.
The 6 M HCl-ethanol mixture for trapping and reducing Ru resulted in very low recovery yields (<5%), regardless of the oxidant and temperature used. Ceric sulfate also produced poor recovery yields for Ru (<5%) regardless of the trapping/reductant solution and temperature. Acidified H2Cr2O7 generally resulted in a higher recovery for Ru (20–90%) that was highly dependent on the trapping/reductant solution used, as well as the reaction time and temperature. It was found that recovery of Ru was low when the oxidation step was carried out at >100 °C. Concentrated HBr as the trapping solution, in combination with H2Cr2O7 as the oxidant resulted in highly variable yields (20–80%). The use of 55 μl of H2Cr2O7 as the oxidant and 10 μl of 6 M HCl as the trapping agent consistently produced the highest Ru recovery (50–90%) when distillation was performed at 55 °C for 12 h, and repeated for another 12 h after the addition of an additional 20 μl of H2Cr2O7 and replenishment of the 6 M HCl trapping agent. The blank for this microdistillation was 570 ± 160 pg (n = 4). This blank is ≪1% of the total Ru measured for each sample here and inconsequential for the measurements reported. The cause of persistent variability in yields from microdistillation remains unclear, but yields appear to be improved if little matrix remains after the 1° column, and if the sample has been gently and not completely dried down at any stage of the purification chemistry. Importantly, the variability in Ru yield that is observed in this study (20–90%) does not have a significant effect on the isotopic composition measured. Samples which had yields of ~20% generated the same 100Ru/101Ru as the same sample with ~90% yields, within the analytical error.
Chromium contamination in the distilled Ru occasionally occurred during the early stages of development of this method, likely due to splashing of H2Cr2O7 during distillation. The presence of minor Cr-contamination led to a substantial reduction of the RuO3− signal during N-TIMS analysis. Avoidance of Cr-contamination was achieved by slowly heating-up the microdistillation vessel in steps of 10 °C from room temperature. Traces of Os can co-distil with the Ru; however, this contamination of the Ru can be kept to negligible amounts by distilling at ≤55 °C.
Following microdistillation, the purified Ru was ready for loading onto filaments for N-TIMS analysis. Upon completion of the Ru purification, a small aliquot (0.1%) was removed for analysis using an ICP-MS to assess elemental purity and determine the chemical yield of each sample. All samples processed for this study were found to be of high purity with no contamination by potentially interfering elements, such as Zr, Mo, Rh, and Pd.
3. Mass spectrometry
3.1. Instrumentation
A Thermo-Fisher Triton Plus TIMS in negative ionization mode was used to make Ru isotope measurements. The analysis of negatively charged molecular species of Ru was refined here from methods reported by [6]. The N-TIMS method has been shown to be a highly sensitive and accurate technique in the analysis of ions with high electron affinities [26]. The instrument was equipped with nine Faraday cups, seven of which were used to measure the seven stable Ru isotopes as trioxides (RuO3−) using a single static line measurement method (Fig. 1). High purity oxygen was bled into the source chamber using a variable leak valve to promote formation of RuO3−. The oxygen pressure (ranging from 6.50 × 10−7 to 9.60 × 10−7 mbar, depending on the baseline pressure) was allowed to settle at the beginning of the measurement campaign and was left unchanged throughout the session. During development of this method, it was found that within and between run oxygen isotope variations can significantly affect analytical precision. Use of an amplifier equipped with a 1012 Ω resistor (connected to the H4 Faraday cup) was employed to measure in-run oxygen isotope compositions by quantifying the 104Ru18O16O2− species. Possible interferences from ZrO3−, MoO3−, BaO−, and PdO3− were monitored at masses 138 (95ZrO3), 143 (95MoO3), 153 (137BaO), and 156 (108PdO3), using the secondary electron multiplier at the beginning and end of each run. Corrections were neither needed nor applied for these elements.
3.2. Filament preparation and sample loading
Platinum and Re single filaments as well as Ta-Pt and Pt-Pt double filament assemblies were tested. Single Pt filaments generated the most stable and sensitive RuO3− signal over the longest periods of time (8–13 h). Prior to loading, the Pt filaments were outgassed in air at 2.2 A for 7–10 min and left for 12–24 h before loading. Different brands of Pt ribbon were tested (EA3), however, all produced similar RuO3− signals and levels of precision.
Because of the range of oxidation states of Ru and the markedly different volatilities of these valences, careful attention was paid in maintaining a constant, low valence state during loading. If this is not done, Ru can be present on the filament in both high and low valence states which can lead to different rates of evaporation during warming of the filament (also documented by[13]). This results in unstable and short-lived RuO3− signals, as well as complexly fractionated analyses. Different loading solutions (6 M HCl, 6 M HNO3, concentrated HBr, dilute HBr, Mill-Q) and loading techniques were tried in order to promote a reduced Ru valence state during loading. It was found that gently drying the solution down and then taking it up in concentrated HBr prior to loading on the filament produced the most stable RuO3− signals.
Samples containing ~1000 ng Ru were loaded onto the center of a Pt filament. To dry down the Ru solution, the filament was resistively heated by maintaining a current of 0.6 A. Loading in small volumes reduced the probability of the sample spreading on the filament, which can lead to the formation of multiple chemical reservoirs on the filament and signal instability. After the sample solution dried, the current to the filament was gradually increased over a period of ~5 s until it glowed to dull red for ~1 s. This step promoted reduction of the sample on the filament. After glowing the filament, the sample is characterized by a subtle navy colored sheen.
For N-TIMS, samples must typically also be loaded with an activator solution bearing an electron emitter (e.g., [27]). The activator supplies the electrons necessary to form the negatively charged ionic species required. Different electron activators were tried here including silica gel, Ba(NO3)2, Ba(NO3)2-NaOH-Ba(OH)2, or NaOH-Ba(OH)2. The most stable, long-lasting signals were obtained by using 0.8–2 μl of NaOH-Ba(OH)2 (super saturated solution), which was painted across the sample (post glowing) with a micro-pipetter tip, while resistively heating the filament using a current of 0.2 A. The activator solution was left to dry at this current, after which the filament was resistively heated to the point that the activator melted across the sample. The Ru loading blank was ≤1 pg and is negligible for the measurements reported here. Filaments were then immediately put into the mass spectrometer.
3.3. Data acquisition protocol
All standards and samples were heated in the mass spectrometer using the same protocol. As documented in earlier studies [6, 13, 28], a temperature maximum was observed, above which the RuO3− signal began to decrease, despite continued heating. Volkening et al. [28] suggested that the drop in signal occurs because the increasing number of RuO3− ions formed as a result of the higher reaction rate cannot compensate for the loss of the ions that instantaneously decompose at the higher temperatures. As was also observed by [6], we found that the temperature maximum could not be precisely defined. It appeared to be dependent on the thickness of the filament ribbon and the quality of the load. To avoid the sharp decrease in signal after reaching the temperature threshold, the filament was heated slowly to promote exponential growth of the RuO3− signal, and the heating rate gradually tapered off to achieve a stable signal (102RuO3− ~0.7 to 1.2 V) at a low and constant heating rate (0.1 Ma/min) during a 13 h measurement period. The RuO3− signal generally fell to 0.5–1.0 V during a run (8–13 h). The temperatures of the filament during data collection ranged from 830 °C to 1000 °C, but typically remained between 850 °C and 930 °C, as recorded by a pyrometer.
All measurements were performed using a single line, static acquisition scheme, where the mass 148 beam, corresponding to 100Ru16O3−, was directed into the axial Faraday cup (Fig. 1). The original measurement method using only 1011 Ω resistors proceeded as follows: Between 1000 and 1800 ratios were collected with 16.777 s integration times, one integration, 4 s idle times, in blocks of 20 ratios. Between each block, 30 s baseline measurements by beam deflection with a 10 s pre-baseline wait time were made. Inter-amplifier biases were canceled by electronically rotating the amplifiers at the beginning of each block, using the virtual amplifier capability of the Triton. Every 3 blocks, the 148 peak was centered and refocused using the automated peak centering and focus capability of the Triton.
Upon installation of a 1012 Ω resistor, in-run oxygen isotope compositions were monitored by measuring the 104Ru18O16O2− species in the H4 Faraday cup. The 1012 Ω resistor is used to increase the signal to noise ratio measured by the amplifier, when the effective signal strength of the ion beam is between ~1 and 20 mV (e.g.,[29]), a typical intensity of the 104Ru18O16O2− signal. Two measurement methods tested after the installation of the 1012 Ω resistor were characterized either by using 2 integrations (termed long integration method), or 1 integration (termed short integration method). The long integration method is as follows: Between 100–250 ratios were collected with 67.1 s integration times, two integrations, 15 s idle times, in blocks of 25. Inter-amplifier biases were canceled by rotating the amplifiers. The 1012 Ω resistor amplifier connected to H4 was excluded from the rotation scheme. The 148 peak was centered and the beam focused using the automated peak centering and focus capability of the Triton at the beginning of each block. Twenty minute baseline measurements were made every five blocks for each Faraday cup/amplifier pair by beam deflection, with a 30 s pre-baseline wait time. Longer idle times, pre-baseline wait times, and baseline measurement times were used to accommodate the longer settling time required with usage of the 1012 Ω resistor. For the short integration method, the number of integrations was reduced to one, the number of ratios increased to 500, ratios were measured in blocks of 10, and baseline measurements occurring every 10 bocks. All the other parameters were kept constant.
To describe measurement results for 100Ru/101Ru, the ratio for which the best precision is obtained, we use the μ100Ru notation, which corresponds to the deviation of the 100Ru/101Ru of a sample, relative to average isotope ratio calculated for the repeat analysis of the Alfa Aesar standard for that analytical campaign, in parts per million:
3.4. Mass fractionation correction
Instrumental fractionation is the major limiting factor in the accurate determination of isotopic ratios by mass spectrometry. For thermal ionization sources, it is largely influenced by preferential evaporation of light isotopes relative to heavier isotopes. The effect of this mass-dependent fractionation can be corrected for a given isotope ratio by normalizing to a second ratio of two stable and non-radiogenic isotopes using the exponential law [30]:
where corresponds to the mass fractionation corrected ratio, is the measured (oxygen corrected) ratio, is the atomic mass ratio of the Ru isotope species, and β is the fractionation factor such that:
where is the measured (oxygen corrected) ratio, is the normalizing ratio (100Ru/101Ru = 0.745075; [6]) and is the atomic mass ratio of the Ru isotope species.
Mass fractionation using the molecular species, instead of the common isotopic species, was tested. Both correction schemes produced very similar ratios (identical within <2 ppm), but it was found that correction using the isotopic species consistently produced a slightly lower external reproducibility for all Ru isotopes measured, and thus, the isotopic species were used during mass fractionation correction for all data reported here.
Ruthenium comprises seven stable isotopes (96Ru, 98Ru, 99Ru, 100Ru, 101Ru, 102Ru, 104Ru) which provide multiple options for mass fractionation correction. Traditionally 100Ru/101Ru = 0.745075 has been used [6, 7] and this ratio is applied here. After mass fractionation correction relative to 99Ru/101Ru, internal precision of 2.5–4.5 ppm (2SE) on 100Ru/101Ru is typically reached by the end of a measurement cycle, consistent with errors predicted by theoretical ion-counting statistics.
3.5. Oxide interferences
The ionization of Ru as RuO3− mainly results in the production of Ru16O3−, but also, in smaller abundances other oxygen species including Ru16O217O−, Ru16O17O2−, Ru16O18O2−, Ru16O, 17O, 18O−, Ru17O3−, and Ru17O218O−. These species result in isobaric interferences on the major Ru isotopes measured that must be corrected for. Additional species (Ru17O18O2 and Ru18O3) are also formed; however, they are in such low abundance that they do not generate significant interferences. The measured intensity at mass x (xI) is derived from the combination of the signal due to the x−48Ru16O3 trioxide, and signals derived from other isobaric Ru trioxides. These oxide interferences must be corrected for in order to obtain precise data. The oxide correction equations developed for Ru and Os isotope measurement by N-TIMS were applied here (e.g., [27, 31]). Three different reduction protocols were tried and these will be discussed in turn:
Nier correction scheme: Where oxide interference corrections are estimated by assuming that Ru is associated with oxygen with an ambient isotopic composition (Nier correction; 17O/16O = 0.0003749 and 18O/16O = 0.0020439; [32]). This reduction protocol does not take into account within-run or between-run oxygen isotope variations. The highest external precision obtained here using this reduction scheme, was μ100Ru ±7.7, where n = 48 (2SD; Table 2, Fig. 2a).
Single measured oxygen value correction scheme: This reduction protocol employs two iterations to enable the measurement of the within-run oxygen isotope compositions as an average single value for the measurement. First, oxide interference corrections are estimated by assuming that Ru is associated with oxygen with an ambient isotopic composition (Nier correction). After correcting the oxygen isotope interferences on the RuO3 species, we calculated an average 18O/16O composition from the 104Ru16O218O species for that measurement. The corresponding 17O/16O composition has traditionally been determined by using the terrestrial fractionation line slope (17O/16O vs. 18O/16O = 0.095, or δ 17O/16O vs. δ 18O/16O = 0.52). However, we found that using an iteratively derived slope of 17O/16O vs. 18O/16O = 0.47 (μ100Ru ±6.4; 2SD) generated far higher precision than if 17O/16O vs. 18O/16O = 0.0954 (μ100Ru >30; 2SD) was used. This is either because there is interference on the 104Ru16O218O peak used to calculate 18O/16O or because the fractionation of 17O/16O and 18O/16O during analysis does not follow the terrestrial fractionation trend. Careful monitoring of the 104Ru16O218O peak indicated that there were no interferences on the 104Ru16O218O peak. However, evidence for “non-mass-dependent” fractionation of the 17O/16O and 18O/16O ratios was found when measuring 104Ru16O217O and 104Ru16O218O of a 104Ru enriched spike solution (EA4). For the analyses of the spike, in situ measurement of 17O/16O and 18O/16O was achieved by monitoring the 104Ru16O217O species and 104Ru16O218O. We found that the 17O/16O vs. 18O/16O slope varied between runs (0.08 to 0.28; EA4). The deviation of the measured 17O/16O vs. 18O/16O slope from the terrestrial fractionation line is potentially a result of mixing of isotopically distinct reservoirs of oxygen from the tank and the filament. To obtain more accurate and precise oxide corrections, the 17O/16O ratio should be measured in situ along with the 18O/16O species. However, this was not viable for our instrument during typical analyses, given the very small signal intensities associated with 96Ru16O217O (<1 mV). Thus, for the measurements where oxygen was measured in situ, the corresponding 17O/16O was calculated using an iteratively derived slope of 17O/16O vs. 18O/16O = 0.47. This oxygen isotope composition was then used in a second iteration after the first iteration Nier correction to correct for oxygen isotope interferences on the RuO3 species. This reduction scheme is referred to as using a single measured oxygen isotope composition to correct for oxide interferences on the RuO3 species. It demonstrates an external reproducibility of μ100Ru ±6.4 (2SD), where n = 17.
Line-by-line oxygen correction scheme: This reduction scheme similarly employs two iterations. It was designed to monitor the evolution of the oxygen isotope composition during each line. As with (b), the first iteration involved correcting for the oxide interferences by assuming that Ru is associated with oxygen with an ambient isotopic composition (Nier correction). The second iteration involves calculating an average 18O/16O composition from the 104Ru16O218O species for each line. We then took the oxygen isotope composition associated with that line to correct for oxide interferences on the corresponding RuO3 species measured in the same line. A slope of 0.47 was used to calculate 17O/16O, as described above. This reduction scheme is referred to as using a line-by-line measured oxygen isotope composition to correct for oxide interferences on the RuO species. It demonstrates a precision μ100Ru ±6.4 (2SD; Table 3, Fig. 2b), where n = 17.
Table 2.
96/101Ru | 2SE | 98/101Ru | 2SE | 100/101Ru | 2SE | 102/101Ru | 2SE | 104/101Ru | 2SE | |
---|---|---|---|---|---|---|---|---|---|---|
Ru std 01 | 0.321861 | 0.000004 | 0.108969 | 0.000002 | 0.737112 | 0.000003 | 1.853136 | 0.000010 | 1.097470 | 0.000011 |
Ru std 02 | 0.321857 | 0.000004 | 0.108969 | 0.000002 | 0.737114 | 0.000003 | 1.853161 | 0.000010 | 1.097477 | 0.000010 |
Ru std 03 | 0.321832 | 0.000004 | 0.108956 | 0.000002 | 0.737114 | 0.000003 | 1.853160 | 0.000010 | 1.097425 | 0.000011 |
Ru std 04 | 0.321843 | 0.000004 | 0.108968 | 0.000002 | 0.737110 | 0.000003 | 1.853144 | 0.000009 | 1.097446 | 0.000010 |
Ru std 05 | 0.321858 | 0.000007 | 0.108975 | 0.000004 | 0.737111 | 0.000005 | 1.853169 | 0.000016 | 1.097473 | 0.000017 |
Ru std 06 | 0.321844 | 0.000005 | 0.108975 | 0.000003 | 0.737112 | 0.000004 | 1.853140 | 0.000012 | 1.097445 | 0.000014 |
Ru std 07 | 0.321863 | 0.000004 | 0.108977 | 0.000002 | 0.737115 | 0.000003 | 1.853121 | 0.000010 | 1.097444 | 0.000011 |
Ru std 08 | 0.321847 | 0.000003 | 0.108972 | 0.000002 | 0.737109 | 0.000003 | 1.853132 | 0.000008 | 1.097432 | 0.000009 |
Ru std 09 | 0.321837 | 0.000005 | 0.108966 | 0.000003 | 0.737114 | 0.000004 | 1.853143 | 0.000011 | 1.097453 | 0.000012 |
Ru std 10 | 0.321870 | 0.000003 | 0.108967 | 0.000002 | 0.737116 | 0.000003 | 1.853166 | 0.000008 | 1.097513 | 0.000009 |
Ru std 11 | 0.321848 | 0.000004 | 0.108944 | 0.000002 | 0.737114 | 0.000003 | 1.853242 | 0.000010 | 1.097536 | 0.000011 |
Ru std 12 | 0.321871 | 0.000005 | 0.108965 | 0.000002 | 0.737111 | 0.000004 | 1.853214 | 0.000011 | 1.097563 | 0.000012 |
Ru std 13 | 0.321870 | 0.000008 | 0.108966 | 0.000004 | 0.737112 | 0.000006 | 1.853166 | 0.000018 | 1.097518 | 0.000019 |
Ru std 14 | 0.321857 | 0.000006 | 0.108973 | 0.000003 | 0.737113 | 0.000005 | 1.853175 | 0.000014 | 1.097532 | 0.000015 |
Ru std 15 | 0.321857 | 0.000006 | 0.108954 | 0.000003 | 0.737114 | 0.000004 | 1.853209 | 0.000013 | 1.097535 | 0.000014 |
Ru std 16 | 0.321855 | 0.000005 | 0.108958 | 0.000003 | 0.737109 | 0.000004 | 1.853193 | 0.000011 | 1.097499 | 0.000012 |
Ru std 17 | 0.321857 | 0.000002 | 0.108961 | 0.000001 | 0.737110 | 0.000002 | 1.853200 | 0.000006 | 1.097518 | 0.000007 |
Ru std 18 | 0.321874 | 0.000007 | 0.108967 | 0.000004 | 0.737109 | 0.000005 | 1.853173 | 0.000016 | 1.097472 | 0.000017 |
Ru std 19 | 0.321872 | 0.000007 | 0.108963 | 0.000004 | 0.737111 | 0.000005 | 1.853177 | 0.000015 | 1.097492 | 0.000017 |
Ru std 20 | 0.321846 | 0.000007 | 0.108965 | 0.000004 | 0.737116 | 0.000006 | 1.853209 | 0.000016 | 1.097553 | 0.000018 |
Ru std 21 | 0.321856 | 0.000004 | 0.108955 | 0.000002 | 0.737117 | 0.000003 | 1.853175 | 0.000009 | 1.097491 | 0.000010 |
Ru std 22 | 0.321846 | 0.000003 | 0.108951 | 0.000002 | 0.737116 | 0.000003 | 1.853223 | 0.000008 | 1.097518 | 0.000009 |
Ru std 23 | 0.321860 | 0.000005 | 0.108958 | 0.000003 | 0.737116 | 0.000004 | 1.853197 | 0.000012 | 1.097513 | 0.000013 |
Ru std 24 | 0.321853 | 0.000004 | 0.108962 | 0.000002 | 0.737115 | 0.000003 | 1.853188 | 0.000009 | 1.097501 | 0.000010 |
Ru std 25 | 0.321863 | 0.000004 | 0.108967 | 0.000002 | 0.737118 | 0.000003 | 1.853167 | 0.000008 | 1.097501 | 0.000009 |
Ru std 26 | 0.321855 | 0.000004 | 0.108961 | 0.000002 | 0.737118 | 0.000004 | 1.853212 | 0.000011 | 1.097540 | 0.000011 |
Ru std 27 | 0.321859 | 0.000005 | 0.108960 | 0.000002 | 0.737110 | 0.000004 | 1.853190 | 0.000011 | 1.097520 | 0.000012 |
Ru std 28 | 0.321871 | 0.000005 | 0.108968 | 0.000003 | 0.737112 | 0.000004 | 1.853165 | 0.000012 | 1.097495 | 0.000013 |
Ru std 29 | 0.321867 | 0.000003 | 0.108964 | 0.000002 | 0.737117 | 0.000003 | 1.853176 | 0.000008 | 1.097508 | 0.000009 |
Ru std 30 | 0.321855 | 0.000004 | 0.108959 | 0.000002 | 0.737114 | 0.000003 | 1.853198 | 0.000010 | 1.097497 | 0.000011 |
Ru std 31 | 0.321857 | 0.000005 | 0.108956 | 0.000002 | 0.737111 | 0.000004 | 1.853195 | 0.000011 | 1.097516 | 0.000012 |
Ru std 32 | 0.321869 | 0.000004 | 0.108970 | 0.000002 | 0.737111 | 0.000004 | 1.853139 | 0.000011 | 1.097484 | 0.000011 |
Ru std 33 | 0.321860 | 0.000005 | 0.108963 | 0.000003 | 0.737113 | 0.000004 | 1.853177 | 0.000012 | 1.097506 | 0.000013 |
Ru std 34 | 0.321861 | 0.000004 | 0.108969 | 0.000002 | 0.737116 | 0.000003 | 1.853152 | 0.000010 | 1.097464 | 0.000011 |
Ru std 35 | 0.321864 | 0.000003 | 0.108972 | 0.000001 | 0.737112 | 0.000002 | 1.853137 | 0.000007 | 1.097467 | 0.000007 |
Ru std 36 | 0.321864 | 0.000004 | 0.108979 | 0.000002 | 0.737115 | 0.000003 | 1.853128 | 0.000009 | 1.097470 | 0.000010 |
Ru std 37 | 0.321871 | 0.000004 | 0.108975 | 0.000002 | 0.737115 | 0.000003 | 1.853128 | 0.000009 | 1.097482 | 0.000010 |
Ru std 38 | 0.321865 | 0.000005 | 0.108968 | 0.000003 | 0.737116 | 0.000004 | 1.853157 | 0.000013 | 1.097475 | 0.000013 |
Ru std 39 | 0.321862 | 0.000004 | 0.108971 | 0.000002 | 0.737109 | 0.000003 | 1.853152 | 0.000010 | 1.097506 | 0.000011 |
Ru std 40 | 0.321853 | 0.000005 | 0.108958 | 0.000003 | 0.737109 | 0.000004 | 1.853193 | 0.000012 | 1.097515 | 0.000013 |
Ru std 41 | 0.321862 | 0.000003 | 0.108963 | 0.000001 | 0.737113 | 0.000002 | 1.853159 | 0.000007 | 1.097485 | 0.000008 |
Ru std 42 | 0.321866 | 0.000004 | 0.108966 | 0.000002 | 0.737114 | 0.000003 | 1.853145 | 0.000011 | 1.097480 | 0.000012 |
Ru std 43 | 0.321842 | 0.000004 | 0.108952 | 0.000002 | 0.737117 | 0.000003 | 1.853221 | 0.000010 | 1.097502 | 0.000011 |
Ru std 44 | 0.321848 | 0.000003 | 0.108957 | 0.000001 | 0.737116 | 0.000002 | 1.853212 | 0.000007 | 1.097508 | 0.000007 |
Ru std 45 | 0.321856 | 0.000006 | 0.108967 | 0.000003 | 0.737106 | 0.000005 | 1.853139 | 0.000014 | 1.097468 | 0.000015 |
Ru std 46 | 0.321859 | 0.000005 | 0.108972 | 0.000003 | 0.737112 | 0.000004 | 1.853146 | 0.000012 | 1.097477 | 0.000013 |
Ru std 47 | 0.321848 | 0.000004 | 0.108958 | 0.000002 | 0.737117 | 0.000003 | 1.853188 | 0.000009 | 1.097487 | 0.000010 |
Ru std 48 | 0.321846 | 0.000004 | 0.108956 | 0.000002 | 0.737115 | 0.000004 | 1.853205 | 0.000011 | 1.097497 | 0.000012 |
Mean | 0.321857 | 0.000005 | 0.108964 | 0.000002 | 0.737113 | 0.000004 | 1.853173 | 0.000011 | 1.097493 | 0.000012 |
±2σ (ppm) | 60.5 | 136.9 | 7.7 | 32.0 | 55.4 |
Table 3.
96/101Ru | 2SE | 98/101Ru | 2SE | 100/101Ru | 2SE | 102/101Ru | 2SE | 104/101Ru | 2SE | |
---|---|---|---|---|---|---|---|---|---|---|
Corrected using an assumed oxygen isotope composition [32] | ||||||||||
Ru std 01 | 0.321799 | 0.000003 | 0.108933 | 0.000002 | 0.737143 | 0.000002 | 1.853247 | 0.000007 | 1.097404 | 0.000007 |
Ru std 02 | 0.321827 | 0.000004 | 0.108947 | 0.000002 | 0.737146 | 0.000003 | 1.853231 | 0.000010 | 1.097448 | 0.000011 |
Ru std 03 | 0.321815 | 0.000005 | 0.108945 | 0.000002 | 0.737147 | 0.000003 | 1.853230 | 0.000011 | 1.097450 | 0.000012 |
Ru std 04 | 0.321800 | 0.000004 | 0.108937 | 0.000002 | 0.737148 | 0.000003 | 1.853259 | 0.000011 | 1.097440 | 0.000012 |
Ru std 05 | 0.321818 | 0.000003 | 0.108941 | 0.000001 | 0.737141 | 0.000002 | 1.853234 | 0.000007 | 1.097435 | 0.000007 |
Ru std 06 | 0.321801 | 0.000003 | 0.108945 | 0.000002 | 0.737149 | 0.000003 | 1.853215 | 0.000009 | 1.097398 | 0.000009 |
Ru std 07 | 0.321826 | 0.000004 | 0.108945 | 0.000002 | 0.737148 | 0.000003 | 1.853221 | 0.000010 | 1.097445 | 0.000011 |
Ru std 08 | 0.321813 | 0.000006 | 0.108936 | 0.000003 | 0.737149 | 0.000005 | 1.853250 | 0.000014 | 1.097441 | 0.000016 |
Ru std 09 | 0.321797 | 0.000007 | 0.108923 | 0.000004 | 0.737145 | 0.000005 | 1.853325 | 0.000016 | 1.097462 | 0.000017 |
Ru std 10 | 0.321804 | 0.000005 | 0.108931 | 0.000003 | 0.737145 | 0.000004 | 1.853282 | 0.000013 | 1.097453 | 0.000014 |
Ru std 11 | 0.321790 | 0.000004 | 0.108919 | 0.000002 | 0.737149 | 0.000003 | 1.853306 | 0.000010 | 1.097454 | 0.000010 |
Ru std 12 | 0.321823 | 0.000007 | 0.108938 | 0.000004 | 0.737151 | 0.000005 | 1.853277 | 0.000018 | 1.097508 | 0.000020 |
Ru std 13 | 0.321812 | 0.000005 | 0.108935 | 0.000002 | 0.737151 | 0.000004 | 1.853287 | 0.000011 | 1.097501 | 0.000012 |
Ru std 14 | 0.321802 | 0.000005 | 0.108934 | 0.000003 | 0.737150 | 0.000004 | 1.853284 | 0.000011 | 1.097466 | 0.000012 |
Ru std 15 | 0.321817 | 0.000003 | 0.108941 | 0.000002 | 0.737144 | 0.000003 | 1.853255 | 0.000009 | 1.097463 | 0.000008 |
Ru std 16 | 0.321819 | 0.000003 | 0.108934 | 0.000002 | 0.737147 | 0.000002 | 1.853309 | 0.000008 | 1.097507 | 0.000008 |
Ru std 17 | 0.321813 | 0.000003 | 0.108939 | 0.000002 | 0.737142 | 0.000003 | 1.853267 | 0.000009 | 1.097477 | 0.000009 |
Mean | 0.321810 | 0.108937 | 0.737147 | 1.853263 | 1.097456 | |||||
±2σ (ppm) | 67.7 | 138.0 | 8.2 | 35.1 | 56.2 | |||||
Corrected using a line-by-line measured oxygen isotope composition | ||||||||||
Ru std 01 | 0.321777 | 0.000003 | 0.108915 | 0.000001 | 0.737142 | 0.000002 | 1.853326 | 0.000007 | 1.097448 | 0.000008 |
Ru std 02 | 0.321794 | 0.000004 | 0.108922 | 0.000002 | 0.737144 | 0.000003 | 1.853349 | 0.000010 | 1.097515 | 0.000011 |
Ru std 03 | 0.321784 | 0.000005 | 0.108921 | 0.000002 | 0.737145 | 0.000003 | 1.853343 | 0.000011 | 1.097511 | 0.000012 |
Ru std 04 | 0.321727 | 0.000005 | 0.108882 | 0.000003 | 0.737144 | 0.000003 | 1.853521 | 0.000012 | 1.097590 | 0.000013 |
Ru std 05 | 0.321778 | 0.000003 | 0.108910 | 0.000001 | 0.737139 | 0.000002 | 1.853375 | 0.000007 | 1.097515 | 0.000007 |
Ru std 06 | 0.321724 | 0.000004 | 0.108885 | 0.000002 | 0.737144 | 0.000003 | 1.853495 | 0.000010 | 1.097557 | 0.000010 |
Ru std 07 | 0.321762 | 0.000004 | 0.108897 | 0.000002 | 0.737144 | 0.000003 | 1.853448 | 0.000010 | 1.097574 | 0.000011 |
Ru std 08 | 0.321748 | 0.000008 | 0.108886 | 0.000005 | 0.737145 | 0.000005 | 1.853484 | 0.000021 | 1.097573 | 0.000019 |
Ru std 09 | 0.321790 | 0.000006 | 0.108918 | 0.000003 | 0.737145 | 0.000004 | 1.853346 | 0.000017 | 1.097475 | 0.000017 |
Ru std 10 | 0.321780 | 0.000004 | 0.108913 | 0.000002 | 0.737144 | 0.000002 | 1.853371 | 0.000009 | 1.097502 | 0.000009 |
Ru std 11 | 0.321755 | 0.000004 | 0.108893 | 0.000002 | 0.737147 | 0.000003 | 1.853436 | 0.000010 | 1.097527 | 0.000011 |
Ru std 12 | 0.321734 | 0.000008 | 0.108867 | 0.000004 | 0.737145 | 0.000005 | 1.853610 | 0.000021 | 1.097694 | 0.000022 |
Ru std 13 | 0.321715 | 0.000005 | 0.108859 | 0.000003 | 0.737145 | 0.000004 | 1.853650 | 0.000013 | 1.097708 | 0.000013 |
Ru std 14 | 0.321707 | 0.000006 | 0.108859 | 0.000003 | 0.737144 | 0.000004 | 1.853629 | 0.000016 | 1.097658 | 0.000014 |
Ru std 15 | 0.321764 | 0.000003 | 0.108901 | 0.000002 | 0.737140 | 0.000003 | 1.853449 | 0.000008 | 1.097572 | 0.000009 |
Ru std 16 | 0.321743 | 0.000003 | 0.108875 | 0.000002 | 0.737142 | 0.000002 | 1.853585 | 0.000009 | 1.097664 | 0.000009 |
Ru std 17 | 0.321745 | 0.000003 | 0.108888 | 0.000002 | 0.737138 | 0.000003 | 1.853517 | 0.000009 | 1.097618 | 0.000009 |
Mean | 0.321755 | 0.108894 | 0.737143 | 1.853467 | 1.097571 | |||||
±2σ (ppm) | 168.4 | 386.9 | 6.4 | 115.6 | 139.5 |
Although the different correction schemes tried here produce similar levels of precision, the highest precision was achieved by using either the line-by-line measured oxygen isotope composition or the single measured oxygen isotope composition to correct for oxide interferences on the RuO3 species. We consider the line-byline reduction protocol to be preferable because this method can better monitor in-run changes in the oxygen isotope composition. For each reduction scheme, small residual internal correlations between Ru isotopes persist for most isotope ratios. These likely reflect small uncorrected variations in the isotopic composition of oxygen during the course of a run. The measured oxygen isotope composition is likely a combination of the oxygen being bled into the source can, and that provided by the activator (NaOH-Ba[OH]2). Notably, it was found that maintaining a stable oxygen pressure during an analysis and a measurement campaign, in addition to careful application of the same volume of activator to each filament, was essential to reducing the variation in oxygen composition within and between runs.
The precision achieved on the remaining Ru isotopes is significantly worse (>50 ppm) using the measured oxygen composition scheme (b) or (c), compared to (a), although the line-by-line correction scheme produces slightly (<5 ppm) more precise data than the single value correction scheme. For the line-by-line correction scheme, internal weak correlations between Ru isotope ratios and the oxygen isotope composition (18O/16O) persist. For example, a weak positive correlation was occasionally observed for 102Ru vs. 18O/16O (r2 = 0.07) and 104Ru vs. 18O/16O (r2 = 0.13), coupled with a weak negative correlation for 96Ru vs. 18O/16O (r2 = 0.0.05), 98Ru vs. 18O/16O (r2 = 0.11), and 100Ru vs. 18O/16O (r2 = 0.00.06). This correlation varies in both direction and strength depending on the Ru isotope ratio used. The strength and direction of these correlations also vary between runs, but they are of consistently weak nature. For the single value correction scheme, however, between-run Ru isotope ratios strongly correlate with the oxygen isotope composition (18O/16O) calculated from the oxide corrected 104Ru16O218O species. For example, positive correlations persist for 102Ru vs. 18O/16O (r2 = 0.91), 104Ru vs. 18O/16O (r2 = 0.87), 100Ru vs. 18O/16O (r2 = 0.0082), and negative correlations persist for 96Ru vs. 18O/16O (r2 = 0.86) and 98Ru vs. 18O/16O (r2 = 0.88).
These correlations confirm in both correction schemes that the changing oxygen isotope composition observed within and between runs can directly and adversely affect the reported Ru isotope composition. The persistence of xRu vs. 18O/16O correlations indicates that there is an additional effect in the oxygen isotope correction scheme that is currently not adequately accounted for in the measurement and/or reduction protocols. Although not desired, this is not relevant to the aim of this work, which was to measure 100Ru/101Ru to <10 ppm (2SD). When the other Ru isotope species are required these ratios can be corrected with the Nier correction scheme. The Nier method generated external reproducibility for short-term measurement campaigns (1 month) of μ96Ru = 67, μ98Ru = 138, μ100Ru = 8.2, μ102Ru = 35, μ104Ru = 56 (2SD; Table 3) and is similar to the long-term precision (8 months) μ96Ru = 61, μ98Ru = 137, μ100Ru = 7.7, μ102Ru = 32, μ104Ru = 55 (2SD; Table 3, Fig. 2b). These precisions are higher than the precisions reported by [6] of μ96Ru = 119, μ98Ru = 198, μ100Ru = 31, μ102Ru = 64, μ104Ru = 58, and are comparable to those obtained using MC-ICPMS (μ96Ru = 45, μ98Ru = 52, μ100Ru = 13, μ102Ru = 15, μ104Ru = 31;[7]), but for μ100Ru which is significantly higher in precision.
3.6. Measurement method integration times
As stated in Section 3.3, two measurement methods were tried during this study. The initial method (long integration method) involved setting the number of integrations to two and the number of ratios to 250. The second method involved shortening the integration time (short integration method) by changing the number of integrations to one, increasing the number of ratios to 500, ratios were measured in blocks of 10, and baseline measurements occurring every 10 bocks. All of the other parameters were kept constant. The different measurement methods varied the length of time of ion current integration on the Faraday cups.
It was found that the long integration method did not provide sufficient precision to precisely measure the oxygen isotope composition during a run. This was evidenced by the resulting lower level of precision on μ100Ru ±10 (2SD; n = 19), when using a line-by-line measured oxygen isotopic composition to correct data collected using the long integration, than if an assumed oxygen composition was used (e.g., [32]).
Subsequently, the short integration method was tried and a higher level of precision was reached on μ100Ru ±6.4 (n = 17; 2SD) using this method than reached using the long integration times. As the rate of change of the oxygen isotope composition during Ru isotope analysis is rapid, shorter integration times enable more precise oxygen isotope measurement and thus a more precise oxide interference correction.
4. Results and discussion
4.1. Precision of the Ru isotope measurements
The precision of our 100Ru/101Ru analysis was monitored by measuring two gravimetrically prepared mixtures (Mix A and Mix B) of Ru standard and 100Ru-enriched spike. The gravi-metric predictions of these mixes are μ100RuA = +14.9 ppm and μ100RuB = +29.3 ppm. The spike-standard mixes were processed in the same manner as the Os-Ir-Ru alloys. Separate aliquots of each mix (A and B) were microdistilled once (A1–A2; B1–B3) and measured using different methods as described below.
During testing of the long integration measurement method, a number of spike standard mixes and terrestrial materials were measured (Fig. 3a, EA5). These data were reduced using either an assumed or measured (line-by-line) oxygen composition for the oxide corrections and the isotopic species for mass fractionation correction. For the assumed oxygen composition measurements, repeated measurements of the mixes yielded μ100Ru = 14.5 ± 3.9 (2SD; Mix A) and μ100Ru = 27.3 ± 3.2 (2SD; Mix B), which are in excellent agreement with the gravimetric calculation. These data indicate that this measurement scheme and data reduction protocol generate precise data and can resolve differences of <10 ppm.
During the testing of the short integration measurement method, the spike-standard mixes were again measured to confirm precision of the measurement and reduction protocols (Fig. 3b, EA5). These data were reduced using a line-by-line measured oxygen composition for the oxide corrections and the isotopic species for mass fractionation correction. Repeated measurements of the mixes yielded μ100Ru = 10.7 ± 6.4 (2SD; Mix A) and μ100Ru = 27.3 ± 3.9 (2SD; Mix B), which are in excellent agreement with the gravimetric calculation. These data indicate that this measurement scheme and data reduction protocols generate precise data and can resolve differences of ≥ 13 ppm.
4.2. Ruthenium isotope measurement of natural samples
The analyses of Ru separated from chromitites from the 492 Ma Shetland ophiolite complex [15], Os-Ir-Ru alloy grains from the 162 Ma Josephine ophiolite complex [16], and the iron meteorite Hoba (IVB), using separate dissolutions and different purification protocols, allowed for the thorough assessment of our methods when applied to natural samples (Table 4, Fig. 4). These data were collected when using the long integration measurement method and thus were corrected using an assumed oxygen isotope composition [32], and mass fractionation corrected using 99Ru/101Ru = 0.745075. Repeat analyses of Ru fractions from the chromitites processed through 1° and 2° columns, and microdistillation show good agreement with the Ru standard solution. There is a slight positive offset for μ100Ru (μ100Ru +4.73, 2SD), thus one of these samples (C3_02) was reanalyzed using the simplified chemistry (1° column and microdistillation) and showed no statistically significant offset from the Alfa Aesar standard (μ100Ru +0.85, 2SD). This may suggest that the second stage chemistry may add a small bias (<5 ppm) which is at the limit of our analytical precision. Consequently, the simplified chemistry is the preferred method to process samples. The Os-Ir-Ru alloys processed through microdistillation show excellent reproducibility (μ100Ru +0.08 ± 7.6; 2SD) comparable to what is observed for the Ru Alfa Aesar standard solution, with no statistically significant deviation from the terrestrial standard. Analysis of the iron meteorite Hoba, which was passed through 1° and 2° columns, and microdistillation, is in good agreement with published data, but is more precise.
Table 4.
96/101Ru | 2SE | 98/101Ru | 2SE | 100/101Ru | 2SE | 102/101Ru | 2SE | 104/101Ru | 2SE | |
---|---|---|---|---|---|---|---|---|---|---|
Os-Ir-Ru alloys processed through microdistillation | ||||||||||
M3_6 | 0.321847 | 0.000005 | 0.108959 | 0.000003 | 0.737097 | 0.000004 | 1.853133 | 0.000012 | 1.097506 | 0.000013 |
μ (ppm) | 36.4 | −24.0 | 7.4 | 10.3 | 53.3 | |||||
M8_02 | 0.321855 | 0.000006 | 0.108958 | 0.000003 | 0.737089 | 0.000005 | 1.853122 | 0.000013 | 1.097461 | 0.000014 |
μ (ppm) | 60.4 | −32.1 | −4.5 | 4.0 | 12.2 | |||||
L5_3a | 0.321857 | 0.000005 | 0.108965 | 0.000003 | 0.737094 | 0.000004 | 1.853077 | 0.000012 | 1.097434 | 0.000013 |
L5_3b | 0.321840 | 0.000005 | 0.108946 | 0.000003 | 0.737089 | 0.000004 | 1.853170 | 0.000012 | 1.097495 | 0.000013 |
L5_3c | 0.321840 | 0.000006 | 0.108962 | 0.000004 | 0.737088 | 0.000005 | 1.853113 | 0.000015 | 1.097472 | 0.000016 |
L5_3d | 0.321839 | 0.000003 | 0.108961 | 0.000002 | 0.737093 | 0.000003 | 1.853079 | 0.000009 | 1.097412 | 0.000009 |
L5_3e | 0.321847 | 0.000007 | 0.108965 | 0.000004 | 0.737094 | 0.000006 | 1.853162 | 0.000017 | 1.097492 | 0.000019 |
Mean | 0.321845 | 0.000005 | 0.108960 | 0.000003 | 0.737092 | 0.000004 | 1.853120 | 0.000013 | 1.097461 | 0.000014 |
μ (ppm) | 29.4 | −16.2 | −0.5 | 3.3 | 12.5 | |||||
±2σ (ppm) | 45.5 | 142.5 | 7.56 | 47.7 | 66.5 | |||||
Chromitites processed through 1° + 2° columns & microdistillation | ||||||||||
C1 | 0.321845 | 0.000005 | 0.108950 | 0.000002 | 0.737116 | 0.000004 | 1.853221 | 0.000012 | 1.09750 | 0.000013 |
C2 | 0.321864 | 0.000006 | 0.108970 | 0.000003 | 0.737116 | 0.000005 | 1.853184 | 0.000014 | 1.097483 | 0.000015 |
C3a | 0.321837 | 0.000005 | 0.108956 | 0.000002 | 0.737116 | 0.000004 | 1.853215 | 0.000013 | 1.097482 | 0.000014 |
C3b | 0.321848 | 0.000004 | 0.108966 | 0.000002 | 0.737117 | 0.000003 | 1.853187 | 0.000010 | 1.097480 | 0.000011 |
C3c | 0.321847 | 0.000004 | 0.108961 | 0.000002 | 0.737118 | 0.000003 | 1.853200 | 0.000009 | 1.097489 | 0.000010 |
Mean | 0.321848 | 0.000005 | 0.108960 | 0.000002 | 0.737117 | 0.000004 | 1.853201 | 0.000012 | 1.097487 | 0.000013 |
Mean (ppm) | −28.9 | −44.6 | 4.6 | 19.6 | −0.1 | |||||
±2σ (ppm) | 61.7 | 145.0 | 1.7 | 17.7 | 15.0 | |||||
Chromitites processed through 1° column & microdistillation | ||||||||||
C3_02a | 0.321836 | 0.000005 | 0.108955 | 0.000002 | 0.737135 | 0.000004 | 1.853189 | 0.000011 | 1.097427 | 0.000012 |
C3_02b | 0.321829 | 0.000006 | 0.108965 | 0.000003 | 0.737136 | 0.000005 | 1.853196 | 0.000015 | 1.097450 | 0.000014 |
C3_02c | 0.321832 | 0.000003 | 0.108956 | 0.000001 | 0.737135 | 0.000002 | 1.853196 | 0.000007 | 1.097455 | 0.000007 |
C3_02d | 0.321840 | 0.000005 | 0.108960 | 0.000003 | 0.737137 | 0.000004 | 1.853205 | 0.000010 | 1.097475 | 0.000013 |
Mean | 0.321834 | 0.000005 | 0.108959 | 0.000002 | 0.737135 | 0.000004 | 1.853197 | 0.000011 | 1.097452 | 0.000012 |
μ (ppm) | 25.0 | 31.6 | −0.9 | 4.2 | 13.4 | |||||
±2σ (ppm) | 30.3 | 84.9 | 2.6 | 7.3 | 35.7 | |||||
Iron meteorite processed through 1° + 2° columns & microdistillation | ||||||||||
Hoba a | 0.321883 | 0.000008 | 0.108985 | 0.000004 | 0.737033 | 0.000006 | 1.853117 | 0.000018 | 1.097542 | 0.000019 |
Hoba b | 0.321873 | 0.000008 | 0.108977 | 0.000005 | 0.737029 | 0.000007 | 1.853074 | 0.000020 | 1.097534 | 0.000022 |
Mean | 0.321878 | 0.000008 | 0.108981 | 0.000005 | 0.737031 | 0.000006 | 1.853096 | 0.000019 | 1.097538 | 0.000021 |
μ (ppm) | 117.2 | 268.3 | −116.9 | −64.8 | 34.2 | |||||
±2σ (ppm) | 45.4 | 99.2 | 7.5 | 32.1 | 10.1 | |||||
Lit. mean (ppm)a | 57 | 43.5 | −98.0 | −27.5 | 24.5 | |||||
±2σ (ppm) | 119 | 118 | 31 | 64 | 58 |
Data from [6].
Data for the geological samples were not collected using the preferred analytical method which enables in situ oxygen isotope measurement and oxide interference correction. The excellent agreement between the spike-standard data measured using both measurement methods, however, indicates that both measurement protocols produce very precise data. Thus, the measurements of the natural samples are taken as evidence that our methods of chemical isolation/purification and measurement of Ru do not impart biases. The Ru isotope compositions determined here for chromitites from the 492 Ma Shetland ophiolite complex and Os-Ir-Ru alloy grains from the 162 Ma Josephine ophiolite complex are interpreted to be representative of the Earth’s mantle.
5. Conclusions
We have refined the chemical isolation methods and measurement of Ru by N-TIMS using a Thermo-Fisher Triton Plus mass spectrometer. Repeat analyses of an Alfa Aesar Ru standard solution demonstrate external reproducibility within ±6.4 ppm (2SD) for 100Ru/101Ru using a line-by-line measured oxygen isotope composition to correct for oxide interferences on the RuO3 species and the isotopic species for mass fractionation correction. Repeat analysis of gravimetrically prepared mixtures of a natural Alfa Aesar Ru standard and a 100Ru enriched spike show that differences of ≥13 ppm can be resolved using this measurement method. Repeat analysis of separate dissolutions of iron meteorites, modern day chromitites, and Os-Ir-Ru alloys demonstrate that the chemical isolation procedures applied do not shift the Ru isotope composition.
Acknowledgements
This work has been supported by the NASA grants NNX13AF83G and NNA14AB07A, and NSF-CSEDI grants EAR1160728 and EAR1265169. These sources of funding are gratefully acknowledged. We would like to thank editor P. Barran and external reviewer F. Corfu for providing thorough and helpful reviews of the original manuscript; I.S. Puchtel for discussions and assistance in the chemistry labs; R.D. Ash for assistance with MC-ICP-MS instruments; and B. O’Driscoll for providing the Shetland ophiolite samples.
Appendix A.
EA1.
Sample | Rock type | Ru(μgg−1)a | Digestion | Isolation/purificationb | Chemical yields (%)c |
---|---|---|---|---|---|
C1 | Chromitite | 16.68 | Carius tube | 1°, 2°, MD | ~20 |
C2 | Chromitite | 5.908 | Carius tube | 1°, 2°, MD | ~20 |
C3_01 | Chromitite | 20.06 | Carius tube | 1°, 2°, MD | ~20 |
C3_02 | Chromitite | 20.06 | Carius tube | 1°, MD | ~20 |
L5-3 | Os-Ir-Ru alloy | 5.67 wt% | Carius tube | MD | N/A |
M3-6 | Os-Ir-Ru alloy | 14.10 wt% | Carius tube | MD | N/A |
M8-2 | Os-Ir-Ru alloy | 14.66 wt% | Carius tube | MD | N/A |
Hoba | IVB iron | 29.15 | Teflon® beaker | 1°, 2°, MD | ~20 |
SS-Ad | - | - | Carius tube | MD | N/A |
SS-Bd | - | - | Carius tube | MD | N/A |
1° refers to primary cation column; 2° refers to secondary anion column, MD refers to microdistillation.
Chemical yields from alloy chemistry and spike-standard mix chemistry are unknown due to the unknown quantity of the sample initially digested.
SS-A refers to spike standard mix A; SS-B refers to spike standard mix B.
EA2.
(1) Fill Teflon resin bottle with Biorad resin mixed with Milli-Q water. |
(2) Shake mixture and let resin settle for 15 min |
(3) Decant water |
(4) Fill with Milli-Q water and shake thoroughly; let resin settle and decant water |
(5) Repeat twice more with Milli-Q water |
(6) Repeat with 1 M Hydrochloric acid (quartz distilled) |
(7) Repeat with 6 M Hydrochloric acid (quartz distilled) |
(8) Repeat with 6 M Hydrochloric acid (quartz distilled) |
(9) Repeat with 1 M Hydrochloric acid (quartz distilled) |
(10) Repeat 3 times with Milli-Q water |
(11) Repeat with 1 M Nitric acid (quartz distilled) |
(12) Repeat with 6 M Nitric acid (quartz distilled) |
(13) Repeat with 6 M Nitric acid (quartz distilled) |
(14) Repeat with 1 M Nitric acid (quartz distilled) |
(15) Repeat 3 times with Milli-Q water |
EA3.
Brand | Purity | Size |
---|---|---|
ESPI metals | 5N | 0.001” T × 0.020” W |
Materion | 99.99% | 0.001” T × 0.020” W |
Pressed Pt ribbon | 99.999% | 0.005” W |
EA5.
96/101Ru | 2SE | 98/101Ru | 2SE | 100/101Ru | 2SE | 102/101Ru | 2SE | 104/101Ru | 2SE | |
---|---|---|---|---|---|---|---|---|---|---|
Corrected using an assumed oxygen isotope composition [32] | ||||||||||
SS B1 | 0.32183 | 0.000003 | 0.108954 | 0.000002 | 0.737156 | 0.000003 | 1.853217 | 0.000008 | 1.097482 | 0.000009 |
SS B2a | 0.321838 | 0.000004 | 0.10896 | 0.000002 | 0.737155 | 0.000003 | 1.853152 | 0.000009 | 1.097416 | 0.00001 |
SS B2b | 0.321824 | 0.000004 | 0.108955 | 0.000002 | 0.737158 | 0.000003 | 1.853212 | 0.000009 | 1.097449 | 0.00001 |
SS B2c | 0.321833 | 0.000009 | 0.108962 | 0.000005 | 0.737155 | 0.000005 | 1.853209 | 0.000021 | 1.09748 | 0.000025 |
SS B3 | 0.321816 | 0.000003 | 0.108949 | 0.000002 | 0.737157 | 0.000002 | 1.853216 | 0.000008 | 1.097445 | 0.000007 |
Mean | 0.321828 | 0.000005 | 0.108956 | 0.000002 | 0.737156 | 0.000003 | 1.853201 | 0.000011 | 1.097454 | 0.000012 |
μ (ppm) | 6.9 | 5.9 | 27.3 | 6.5 | 15.7 | |||||
±2σ (ppm) | 54.2 | 93.0 | 3.2 | 29.8 | 50.3 | |||||
SS A1a | 0.321821 | 0.000006 | 0.108951 | 0.000003 | 0.737146 | 0.000005 | 1.853225 | 0.000011 | 1.09746 | 0.000014 |
SS A1b | 0.321836 | 0.000004 | 0.10896 | 0.000002 | 0.737149 | 0.000002 | 1.853216 | 0.000008 | 1.097461 | 0.00001 |
SS A1c | 0.321826 | 0.000004 | 0.108952 | 0.000002 | 0.737145 | 0.000003 | 1.853201 | 0.00001 | 1.09744 | 0.000012 |
SS A1d | 0.321823 | 0.000003 | 0.108959 | 0.000002 | 0.737149 | 0.000003 | 1.853208 | 0.000009 | 1.097469 | 0.000009 |
SS A1e | 0.321843 | 0.000007 | 0.108968 | 0.000003 | 0.737147 | 0.000006 | 1.853138 | 0.000016 | 1.097425 | 0.000017 |
SS A1f | 0.321829 | 0.000004 | 0.108954 | 0.000003 | 0.737146 | 0.000004 | 1.853215 | 0.00001 | 1.097458 | 0.00001 |
A2 | 0.321822 | 0.000003 | 0.108944 | 0.000002 | 0.737147 | 0.000003 | 1.853249 | 0.000008 | 1.09748 | 0.000009 |
Mean | 0.321829 | 0.000005 | 0.108955 | 0.000002 | 0.737147 | 0.000004 | 1.853208 | 0.00001 | 1.097456 | 0.000012 |
μ (ppm) | 7.23 | −2.0 | 14.5 | 10.1 | 17.4 | |||||
±2σ (ppm) | 51.0 | 141.8 | 3.9 | 36.9 | 33.0 | |||||
Corrected using a line-by-line measured oxygen isotope composition | ||||||||||
SSB2d | 0.321771 | 0.000003 | 0.108914 | 0.000001 | 0.737165 | 0.000002 | 1.85341 | 0.000008 | 1.097524 | 0.000008 |
SSB2e | 0.321795 | 0.000003 | 0.108932 | 0.000002 | 0.737162 | 0.000003 | 1.853323 | 0.000007 | 1.097493 | 0.000008 |
SSB2f | 0.321763 | 0.000003 | 0.108911 | 0.000001 | 0.737162 | 0.000002 | 1.853388 | 0.000007 | 1.097481 | 0.000008 |
SSB2f (repeat) | 0.321716 | 0.000009 | 0.108881 | 0.000005 | 0.737165 | 0.000005 | 1.853563 | 0.000024 | 1.097612 | 0.00002 |
Mean | 0.321771 | 0.000003 | 0.108914 | 0.000001 | 0.737165 | 0.000002 | 1.85341 | 0.000008 | 1.097524 | 0.000008 |
μ (ppm) | 21 | 146.1 | 27.3 | −24.7 | −39.2 | |||||
±2σ (ppm) | 206.2 | 389 | 3.9 | 109.4 | 108.3 | |||||
A2 | 0.321792 | 0.000002 | 0.108919 | 0.000001 | 0.737151 | 0.000002 | 1.853333 | 0.000006 | 1.097486 | 0.000007 |
μ (ppm) | 117.2 | 237.5 | 10.7 | −72.2 | −76.8 |
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