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THE PROGRESS OF 14C-AMS ANALYSIS FOR ULTRA-SMALL SAMPLES AT XI’AN AMS CENTER

Published online by Cambridge University Press:  15 August 2023

Hua Du*
Affiliation:
State Key Laboratory of Loess and Quaternary Geology, Institute of Earth Environment, Chinese Academy of Sciences, Xi’an 710061, China Shaanxi Key Laboratory of Accelerator Mass Spectrometry Technology and Application, Xi’an AMS Center, Xi’an 710061, China
Yunchong Fu*
Affiliation:
State Key Laboratory of Loess and Quaternary Geology, Institute of Earth Environment, Chinese Academy of Sciences, Xi’an 710061, China Shaanxi Key Laboratory of Accelerator Mass Spectrometry Technology and Application, Xi’an AMS Center, Xi’an 710061, China Institute of Global Environmental Change, Xi’an Jiaotong University, Xi’an 710049, China
Peng Cheng
Affiliation:
State Key Laboratory of Loess and Quaternary Geology, Institute of Earth Environment, Chinese Academy of Sciences, Xi’an 710061, China Shaanxi Key Laboratory of Accelerator Mass Spectrometry Technology and Application, Xi’an AMS Center, Xi’an 710061, China Institute of Global Environmental Change, Xi’an Jiaotong University, Xi’an 710049, China
Haiyan Zhao
Affiliation:
Shaanxi Key Laboratory of Accelerator Mass Spectrometry Technology and Application, Xi’an AMS Center, Xi’an 710061, China Xi’an Institute for Innovative Earth Environment Research, Xi’an 710061, China
Yaoyao Hou
Affiliation:
State Key Laboratory of Loess and Quaternary Geology, Institute of Earth Environment, Chinese Academy of Sciences, Xi’an 710061, China Shaanxi Key Laboratory of Accelerator Mass Spectrometry Technology and Application, Xi’an AMS Center, Xi’an 710061, China
Xiaohu Xiong
Affiliation:
State Key Laboratory of Loess and Quaternary Geology, Institute of Earth Environment, Chinese Academy of Sciences, Xi’an 710061, China Shaanxi Key Laboratory of Accelerator Mass Spectrometry Technology and Application, Xi’an AMS Center, Xi’an 710061, China
Huachun Gu
Affiliation:
Shaanxi Key Laboratory of Accelerator Mass Spectrometry Technology and Application, Xi’an AMS Center, Xi’an 710061, China Xi’an Institute for Innovative Earth Environment Research, Xi’an 710061, China
Ling Yang
Affiliation:
State Key Laboratory of Loess and Quaternary Geology, Institute of Earth Environment, Chinese Academy of Sciences, Xi’an 710061, China Shaanxi Key Laboratory of Accelerator Mass Spectrometry Technology and Application, Xi’an AMS Center, Xi’an 710061, China
*
*Corresponding authors. Emails: [email protected] and [email protected]
*Corresponding authors. Emails: [email protected] and [email protected]
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Abstract

As there exists a growing demand for chronological research and tracer applications using radiocarbon (14C) analyses of samples smaller than 100 μg C, a compact micro-specific hydrogen graphitization method has been developed at the Xi’an Accelerator Mass Spectrometry (AMS) Center. This article describes the performance of the system and the mass of carbon background produced during ultra-small sample preparation. Furthermore, we discuss the results of contamination corrections and perform 14C analyses on small samples with known age or reference values. The results reveal that our 14C analysis of ultra-small samples of 10–100 μg C can obtain accurate and reliable results, and the micro-scale 14C-AMS analysis technique meets our research objectives for dating and tracer applications.

Type
Conference Paper
Copyright
© The Author(s), 2023. Published by Cambridge University Press on behalf of University of Arizona

INTRODUCTION

In recent years, there has been an increase in demand for radiocarbon (14C) analyses of samples with less than 100 micrograms of carbon (μg C) with continuous improvement of single-molecule separation technologies and the expansion of new 14C applications. These currently include the use of anthropogenic signals from nuclear testing (14C bomb peak) (Cook et al. Reference Cook, Dunbar, Black and Xu2006; Buchholz and Spalding Reference Buchholz and Spalding2010; Saitoh et al. Reference Saitoh2019), compound-specific radiocarbon analysis (CSRA), for environmental (Eglinton et al. Reference Eglinton, Aluwihare, Bauer, Druffel and McNichol1996; Zhao et al. Reference Zhao, Meng, Zhang and Tao2014; Druffel et al. Reference Druffel, Zhang, Xu, Ziolkowski, Southon, Santos and Trumbore2010; Feng et al. Reference Feng, Vonk, Griffin, Zimov, Montluçon, Wacker and Eglinton2017; Zhang et al. Reference Zhang, Huang and Xie2021) and archaeological samples (Berstan et al. Reference Berstan, Stott, Minnitt, Ramsey, Hedges and Evershed2008; Devièse et al. 2018; Casanova et al. Reference Casanova, Knowles, Bayliss, Dunne, Barański and Denaire2020; Spindler Reference Spindler, Comeskey, Chabai, Uthmeier, Buckley, Devièse and Higham2021); in-situ 14C measurements (Lifton et al. Reference Lifton, Jull and Quade2001; Miller et al. Reference Miller, Briner, Lifton and Finkel2006; Pigati et al. Reference Pigati, Lifton and Jull2010; Lupkera et al. Reference Lupkera, Hippeb, Wackerb, Steinemannb, Tikhomirovb, Madene, Haghipoura and Synal2019; Hippe et al. Reference Hippe, Kober, Baur, Ruff, Wacker and Wieler2009, Reference Hippe, Jansen and Skov2021); and biomedical applications (Salehpour et al. Reference Salehpour, Håkansson and Possnert2013; Spalding et al. Reference Spalding, Arner, Westermark, Bernard, Buchholz and Bergmann2008, Reference Spalding, Bergmann, Alkass, Bernard, Salehpour, Huttner, Bostro and Westerlund2013), all these employ micro-scale 14C-AMS analyses. This increasing demand for ultra-small samples has prompted the development of specialized graphitization techniques and other approaches. Micro-scale 14C-AMS analysis will pave the way for challenging analysis relevant to chronological research and tracer applications.

Since the late 1990s, several AMS laboratories have developed techniques and used them for micro-scale 14C analysis. For example, the Keck Carbon Cycle Accelerator Mass Spectrometry laboratory at the University of California, Irvine (KCCAMS/UCI) has developed sample preparation, measurement setup, data analysis, and background corrections for ultra-small mass 14C-AMS (1000–2 μg C) (Santos et al. Reference Santos, Moore, Southon, Griffin, Hinger and Zhang2007a, Reference Santos, Southon, Griffin, Beaupre and Druffel2007b, Reference Santos, Southon, Drenzek, Ziolkowski, Druffel, Xu, Zhang, Trumbore, Eglinton and Hughen2010; Xu et al. Reference Xu, Gao and Salamanca2013; Walker and Xu Reference Walker and Xu2019). In routine 14C analysis at the National Ocean Sciences Accelerator Mass Spectrometry (NOSAMS) laboratory, a minimum sample mass of 25 µg C has been achieved, and ultra-small graphitization reactors have been developed (Pearson et al. Reference Pearson, McNichol, Schneider, Von Reden and Zhang1998; Walter et al. Reference Walter, Gagnon, Roberts, McNichol, Gaylord and Klein2015). By 2004, the Australian Nuclear Science and Technology Research Organization (ANSTO) laboratory routinely analyzed 14C samples less than 100 μg C, using a 2.5 mL micro-specific hydrogen graphitization reactor for samples with 10–200 µg C. Subsequently, they developed a novel miniaturized laser-heated “microfurnace” aimed at preparing ultra-small mass (∼5 µg C) graphite samples from carbon dioxide (CO2) (Hua et al. Reference Hua, Zoppi, Williams and Smith2004; Smith et al. Reference Smith, Hua, Williams and Thorpe2006, Reference Smith, Hua, Williams, Levchenko and Yang2010; Yang and Smith Reference Yang and Smith2017). Scientists at Tokyo University have developed the most optimal conditions for ultra-small 14C samples (5–400 μg C) measurements by improving the pretreatment method to reduce modern and 14C-dead carbon contamination and optimizing the graphite position in the target holders to maximize beam intensity (Yokoyama et al. Reference Yokoyama, Koizumi, Matsuzaki, Miyairi and Ohkouchi2010; Yamane et al. Reference Yamane, Yokoyama, Hirabayashi, Miyairi, Ohkouchi and Aze2019). At the Vienna Environmental Research Accelerator (VERA) laboratory, AMS measurement performance on micrograms of graphite has also been explored (Liebl et al. Reference Liebl, Steier, Golser, Kutschera, Mair, Priller, Vonderhaid and Wild2013; Steier et al. Reference Steier, Liebl, Kutschera, Wild and Golser2017). Moreover, several laboratories have measured small 14CO2 gas samples using EA-AMS online coupling technology (Ruff et al. Reference Ruff, Wacker, Gäggeler, Suter, Synal and Szidat2007, Reference Ruff, Szidat, Gäggeler, Suter, Synal and Wacker2010; Uhl et al. Reference Uhl, Luppold, Rottenbach, Scharf, Kritzler and Kretschmer2007; Fahrni et al. Reference Fahrni, Wacker, Synal and Szidat2013; Welte et al. Reference Welte, Hendriks, Wacker, Haghipour, Eglinton, Günther and Synal2018; Melchert et al. Reference Melchert, Stolz, Dewald, Gierga, Wischhöfer and Rethemeyer2019).

Small-mass radiocarbon samples (>25 μg C) are now routinely analyzed at the Xi’an AMS facility (Fu et al. Reference Fu, Zhou, Du, Cheng, Zhao, Liu, Lu and Zhao2015). However, ultra-small samples require further development, with a dedicated graphitization reactor and systematic study of reproducibility and background for 14C analysis. The Xi’an AMS Center has installed new micro hydrogen graphitization reactors that were made at ANSTO. The goals of our study are: (1) to report on the performance of micro-specific graphitization reactors and 14C-AMS measurements of small to ultra-small samples, (2) to evaluate and correct the carbon contamination during sample preparation and analysis, (3) to assess the reproducibility and accuracy of our micro-scale 14C-AMS analysis, (4) to perform a case study about the chronological application on 14C-AMS analysis of small foraminiferal samples.

SAMPLE PREPARATION AND AMS MEASUREMENTS

The Micro-Specific Graphitization Reactor

The micro-specific graphitization reactors are based on the micro conventional furnace (MCF) design at ANSTO (Yang et al. Reference Yang, Smith and Hua2013; Yang and Smith Reference Yang and Smith2017). The MCF is a cost-effective solution for producing graphite from carbon dioxide sample gas and is connected to a vacuum line for the synthesis of graphitic carbon in 1.2 mL fixed reaction tubes using hydrogen reduction. Reducing the internal volume of reactors is an effective approach for graphitizing smaller samples while minimizing isotopic fractionation (Pearson et al. Reference Pearson, McNichol, Schneider, Von Reden and Zhang1998; Santos et al. 2007; Yokoyama et al. Reference Yokoyama, Koizumi, Matsuzaki, Miyairi and Ohkouchi2010). Our device comprises two small-volume graphitization reactors connected by quartz manifolds and stainless steel cold fingers suitable to trap water vapor during the reaction. Samples with 10–300 μg C can be synthesized in a tube furnace at 600°C, adding reduced iron powder and ultrapure hydrogen (H2), these reactors can also produce a few micrograms of graphite (<10 μg C).

The performance of the micro-specific graphitization reactors was assessed by analyzing ultra-small standard samples, including the National Institute of Standards and Technology (NIST) standard oxalic acid II (OxII; SRM 4990C) as well as secondary standards - International Atomic Energy Agency (IAEA) 14C reference materials (IAEA-C2, IAEA-C3, IAEA-C6, IAEA-C7) and background samples (calcite, Sigma Aldrich graphite, 99.99% pure, -100 mesh, anthracite, CO2 background gas). Many smaller CO2 standard gases were obtained by combustion or hydrolyzed of large quantities of the standard materials with 85% orthophosphoric acid (H3PO4) and subsampled to equal 5–150 µg C for graphite synthesis on the ultra-small reactors.

Performance of Micro-Specific Graphitization Reactors

We analyzed the effects of different catalysts and reducing agents involved in the graphitization of microgram carbon samples based on Scanning electron microscope (SEM) images and AMS measurements to determine appropriate conditions for the synthesis of ultra-small mass graphite.

Efficiency of Graphitization with Different Fe Catalysts

Hydrogen-catalyzed reduction reactions were conducted using four Fe catalysts: (1) Sigma FeO: Fe2O3 powder (Sigma Aldrich, ≥99.995% pure), (2) Acros FeO: Fe2O3 powder (Acros organics, 99.999% pure, -100 mesh), (3) Sigma Fe: Fe powder (Sigma Aldrich, 97% pure, -325 mesh), and (4) nano FeO: Fe2O3 powder. These Fe catalysts were processed by first reducing Fe or Fe2O3 in H2 at 600°C before graphitization. Subsequently, AMS measurement and micro-scale morphological analyses were conducted to determine optimal reagents. This section aims to establish the optimal reagents and suitable mass of carbon for micro-specific graphitization reactors by synthesizing and analyzing graphite samples with different carbon masses.

First, we examined the graphitization reaction curves of CO2 gas samples with various carbon masses using the four different Fe catalysts described above. The reaction curves for the first three Fe catalysts are shown in Figure 1 as residual gas pressure during graphitization. Nano-FeO is not shown due to low yields (20–30%). Sample masses in Figure 1 range from 34 -5.82 μg C. “0” on the time-scale in Figure 1 denotes the moment when the graphitization reaction tube was pushed into the 600 °C furnace, indicating the warming up period before the graphitization reaction, during which the gas pressure first rises rapidly due to the temperature increase. All of the curves reach a peak within one minute. From this point, the pressure of all the gases begins to drop, which means the true beginning of all graphitization reactions, two types of curves are observed: (1) a rapid graphitization that is completed within 15 minutes (Acros FeO and Sigma FeO); and (2) a relatively slow graphitization that is completed within 45 minutes (Sigma Fe). The reaction time also depends on the sample mass. A sample with 5 μg C can be processed in five minutes. We conclude that Acros FeO and Sigma FeO have the highest efficiency with nearly 100% reaction yields.

Figure 1 Graphitization reaction curves for a variety of CO2 gases with varying carbon size catalyzed by various Fe reagents. The solid line for Acros FeO, the dashed line for Sigma FeO, and the dotted line for Sigma Fe are used to depict the three Fe catalysts, and the carbon size is decreased sequentially from top to bottom.

SEM Morphological Analysis of Different Fe Catalysts

Sigma Fe catalyst is used routinely at the Xi’an lab for graphitization in standard 14C analyse. However, for ultra-small samples, FeO catalysts appear to perform better. SEM analysis of graphites produced in our experiments was performed on the Fe catalysts and Fe-C mixtures using a Zeiss EVO18 multipurpose SEM analysis system. The results are shown in Figure 2 with 2-μm resolution. Graphite for these tests was synthesized from the IAEA-C2 reference standard with carbon mass above and below 20 micrograms. Another graphite with a similar C mass was synthesized and measured by AMS to measure 12C3+ currents and fraction modern C (F14C) values. SEM images of several activated Fe powders revealed that most exhibit relatively smooth surfaces with both types of FeO. These showed a relatively large surface area, as compared to Sigma Fe which may explain the relatively slow reaction time of the latter.

Figure 2 The SEM images of iron powder before and after graphitization.

A black graphite-coated iron powder is produced during the graphitizations and this form contributes to strong and reliable ion currents for AMS analysis along with accurate and precise F14C values (Kim et al. Reference Kim, Kelly and Clifford2008). Although the mass of carbon is small, a visible amount of graphite was observed on the surface of Fe powder in the SEM images (Figure 2), no apparent difference exists between the images of different carbon masses, however, 12C3+ beam current and F14C values (reference value: 0.4114 ± 0.0003) of the IAEA-C2 reference standard targets measured by AMS were significantly different. All the targets >20 µg C had relatively high 12C3+ currents and F14C values close to their reference values, whereas all the targets < 20 µg C produced relatively low 12C3+ currents and F14C values, further from their reference values. Based on the SEM images, Sigma FeO and Acros FeO catalysts appear to be better than Sigma Fe (based on surface area), and they outperformed Sigma Fe, based on reaction rate analysis, with varying carbon sizes.

The Sigma FeO catalyst was selected as our catalyst of choice since it demonstrated superior reaction rates and consistent F14C values for samples<20 µg C. With this dedicated trace graphitization system, all CO2 gas samples above 5 µg C can be synthesized, and the optimal amount of carbon for the analyzed samples lies within the range of 10–200 µg C.

AMS Measurements

All samples were analyzed using the 3 MV multi-nuclide Accelerator Mass Spectrometer at the Xi’an AMS Center, Institute of Earth Environment, Chinese Academy of Sciences. Under routine ion source conditions producing∼20 μA 12C from graphite injected into the tandem accelerator, the ion injection energy used was 35 k eV, and a fast 100 Hz cycling frequency was routinely employed in the Fast Sequential Injection (FSI) mode that alternates 12C, 13C and 14C injections. The isotopes: 12, 13, 14C3+ were measured in the high-energy end of the machine with a terminal voltage of 2.5 MV. The best background of 14C/12C was 1.84 × 10–16 with a long-term daily 14C/12C procedural background range for 1 mg C in the range of 9 × 10–16 to 2 × 10–15 (Figure 3; Zhou et al. Reference Zhou, Zhao, Lu, Liu, Wu, Cheng, Zhao and Huang2006, Reference Zhou, Lu, Wu, Zhao, Huang, Li, Cheng and Xin2007, Reference Zhou, Wu, Lange, Lu, Cheng, Xiong, Cruz, Liu, Fu and Zhao2012).

Figure 3 Plot of the average 12C3+ beam current versus the sample sizes. The linear fitting of 12C3+ beam current and the carbon content (%) for three ranges of sample sizes (<20 μg C, 20–100 μg C, and 100–200 μg C) is shown in small figure. The black dots and black line for the range of 100–200 μg C, the blue squares and blue line for the range of 20–100 μg C, the pink triangles and pink line for the range of <20 μg C. (Please see online version for color figures.)

According to the carbon mass of samples, the analyzed graphite samples were divided into wheels of >20 µg C targets and <20 µg C targets, and targets with activated Fe2O3, Fe powder, and Nd powder were inserted into each batch of samples to monitor 14C counting interference. Sample batches consist of a set of small standards with the same size as the unknown samples, analyses of IAEA reference materials and background materials of the same type as unknown samples, as well as OxII standards that are used for quality and consistency control and standards normalization. Measured 14C/12C ratios are reported as F14C. The data were analyzed and performed the correction for isotope fractionation (normalization to δ13C = –25‰ VPDB). Uncertainties of our data are fully propagated for each correction.

AMS RESULTS AND DISCUSSION

Beam Current Investigation

Figure 4 shows the 12C3+ beam currents that we measured on the AMS. The 12C3+ beam current intensity of 1 mg C samples was 20–30 µA and decreased to a few µA or even below 1 µA as the carbon mass of the sample decreased (Figure 4). In general, we fix the C/Fe mass ratio for conventional mg-scale samples to 1:2 (Zn method) or 1:3 (H2 method). To make it easier to load ultra-small mass samples into the holder, we used a constant amount of iron (1 mg Fe or 1.43 mg Fe2O3) regardless of carbon mass. Hence, the C concentration in the targets decreases with carbon mass. This dilution caused the 12C3+ beam current to decrease with decreasing sample mass. We achieved a maximum 12C3+ beam currents of approximately 0.1 µA per µg of carbon. The carbon concentration in conventional 1 mg graphite targets was about 25% (calculated by the C/Fe mass ratio of 1:3), corresponding to an anion beam current of 20–30 µA. For samples of 200 µg C or more, the 12C3+ beam current was stable and above 20 µA, which is consistent with regular 1 mg C targets. For samples of less than 200 µg C, the 12C3+ beam currents decreased sharply with decreasing sample mass (from 20 µA→1 µA or less), which was primarily attributed to dilution of the carbon concentration in the graphite target (from 25%→1%), and 12C3+ beam currents correlated linearly with sample mass. The maximum observed 12C3+ beam current to mass ratio was approximately 0.1 μA/1 μg C. A relatively uniform distribution of 12C3+ beam currents for samples was observed ranging from 20 to 200 µg C, and the distribution was linear for samples with masses between 1 and 20 µA. For ultra-small samples of <20 µg C, 12C3+ beam currents were more dispersed, especially for samples smaller than 10 µg C, where the 12C3+ beam current was below 1 µA and did not correlate well with sample mass.

Figure 4 (a) Fraction modern C values for four 14C-free blanks samples from 0.005 mg C to 0.3 mg C sample size are shown to quantify modern carbon contamination (MCC). The four 14C-free blanks represent the MCC from four different processes for the 14C micro-samples analysis: graphitization (14C-free CO2 gas), surface leaching (carbonates: calcite), combustion and purification (organics: graphite), conventional acid/base/acid washes process (organics: anthracite). (b) ΔF14C values for small and ultra-small OxII samples from 0.003 mg C to 1 mg C measured against 1 mg C normalizing OxII standards are shown to quantify the dead carbon contamination (DCC). Note that uncorrected 14C results from smaller OxII samples are always depleted. The solid lines in both plots represent fixed amounts of carbon contamination from 0.1 to 2 µg C.

By linear fitting of 12C3+ beam current and the C% for three sample sizes range (<20 μg C, 20–100 μg C, and 100–200 μg C), it is found that all of them had a strong linear relationship, especially for the sample sizes of 100–200 μg C, for which the linear relationship is the most significant (R2=0.9894). These linear relationships become weaker as the sample size decreases, it is possible that be related to the uncertainty of analytical results caused by the small sample size, the smaller the sample size, the greater the uncertainty introduced into the analytical results. It could be brought on by uncertainties of various apparatus such as pressure gauge, analytical balance, and others. Therefore, a miniature pressure transducer and a 1.2 mL fixed reaction tube are used to minimize this uncertainty of measurement in our reactor, and the uncertainty introduced by this measurement was considered to be small. It is also possible that by the sample purity, the introduction of contamination can also influence the accuracy of sample mass. While the exogenous contamination introduced during the analysis can be solved by taking multiple measurements of different small standard materials at the same time and applying a suitable correction model.

Quantity of Exogenous Carbon Contamination

Exogenous carbon contamination is generally made up of two major components: (1) modern carbon contamination (MCC) and (2) 14C-dead carbon contamination (DCC), both of which are introduced during sample preparation. The contamination can come from chemical reagents, quartz tubes for loading samples, pretreatment protocols, and poor vacuum, and the uncertainty introduced by this measurement was considered to be small. The proportion of carbon contamination increases as the sample mass decreases, especially for targets with <0.1 mg C, amplifying the effect of contaminations and causing 14C results and δ13C data to significantly deviate from true values. A blank correction has become an indispensable step in the analysis of ultra-small samples due to the increased uncertainties associated with ultra-small samples using AMS.

Several researchers have proposed models for this correction calculation. For instance, Santos et al. (Reference Santos, Moore, Southon, Griffin, Hinger and Zhang2007a) developed formulas to separately correct the contribution of MCC and DCC from unknown samples as small as 0.001 mg C (Santos et al. Reference Santos, Southon, Griffin, Beaupre and Druffel2007b, Reference Santos, Southon, Drenzek, Ziolkowski, Druffel, Xu, Zhang, Trumbore, Eglinton and Hughen2010). By analyzing systematic trends of standard and background normalization results from a similar batch, the MCC content was quantified using smaller 14C-free background samples (3–200 µg C) in the same batch. For this purpose, four background materials were analyzed representing four different chemical pretreatment procedures, including anthracite, calcite, and graphite, and 14C-free CO2 gas (Figure 5a). The trend of the four background F14C values with varying sample sizes are discussed, the solid lines represent the linear effects of several fixed amounts of MCC contamination ranging from 0.1 to 2 µg C, revealing an average MCC of 0.2–1.2 µg. The fraction modern carbon values of the four backgrounds reflect different sources of MCC contamination introduced from conventional 14C-AMS experimental processes (e.g., acid-base-acid pretreatment of organics, combustion and purification, acid-hydrolysis of carbonates, and graphitization). The estimated quantity of our MCC involving different procedural stages are presented in Table 1. The chemical pretreatment process of 14C-AMS samples must be carefully monitored for ultra-small samples. DCC is calculated from ΔF deviation values of the measured fraction modern carbon for small aliquots OxII samples from the primary standard (1 mg C OxII) (Figure 5b). Similarly, several black solid lines represent the effects of several fixed amounts of DC contamination. Our DC contamination is in the range of 0.1–1.5 µg C.

Figure 5 The fitting curves of the reciprocal relationships between our F14C results and sample size for various standards. (a) OxII standards from 0.003 mgC to 1 mgC. All FC results have been corrected for fractionation using δ13C AMS measurements. (b) Four background materials: anthracite, graphite, calcite, and 14C-free CO2 gas.

Table 1 Summary of carbon contamination masses in our 14C-AMS analysis of ultra-small samples.

The MCC of the KCCAMS laboratory was 0.6 ± 0.3 µg C, and DCC was 0.3 ± 0.15 µg C (Santos et al. Reference Santos, Southon, Drenzek, Ziolkowski, Druffel, Xu, Zhang, Trumbore, Eglinton and Hughen2010). The values of the single-stage AMS laboratory at Tokyo University were 0.37 ± 0.13 µg C (MC) and <1.62 µg C (DC) (Masako Yamane et al. Reference Yamane, Yokoyama, Hirabayashi, Miyairi, Ohkouchi and Aze2019). By comparing with data published by other laboratories, it is found that our DC blank contribution was quite significant, this could be attributed to our vacuum system for pumping samples and the chemical reagents used. It is suspected that the use of oil in our vacuum pumps has a negative impact, which, however, needs to be investigated in detail. The 14C content of extraneous carbon in CuO (an oxidation reagent) can vary significantly between batches and suppliers. CuO promotes more contamination than Fe powder (Q. Hua et al. Reference Hua, Zoppi, Williams and Smith2004) because more CuO is used for sample preparation, therefore, having a much higher contamination potential. In the future, oil-free pumps and higher purity reagents will be considered to adopt to minimize these contamination contributions during sample processing at the Xi’an AMS center.

Furthermore, we explore the constant contamination model to precisely quantify the F14C of the contamination (F14Cc) and the mass of the contamination (mc), the F14C measured by AMS (F14Cm) can be expressed as:

(1) $${\rm{F}}_{}^{14}{C_m} = {{{\rm{F}}_{}^{14}{C_s} \times {m_s} + {\rm{F}}_{}^{14}{C_c} \times {m_c}} \over {{m_m}}}$$

Where the F14Cs is the actual F14C of the sample, and mm denotes the total measured C mass, which is the sum of the actual mass of the sample (ms) and mc. From Equation (1) and derivation, we obtain the following equation:

(2) $${\rm{F}}_{}^{14}{C_m} = {\rm{F}}_{}^{14}{C_s} + {m_c} \times {{{\rm{F}}_{}^{14}{C_c} - {\rm{F}}_{}^{14}{C_s}} \over {{m_s}}}$$

The impact of constant contamination is reciprocally related to the sample size, its mass is assumed to be much smaller than that of the sample (mc ${\rm{\;}} \ll $ ms) (Hua et.al. Reference Hua, Zoppi, Williams and Smith2004). Since the values of F14Cs、F14Cc and mc are constant, F14Cm is inversely related to ms, here F14Cs and mc × (F14Cc-F14Cs) can be regarded as the offset and coefficient of the F14Cm and ms relationships, respectively. The reciprocal curves of OxII and four background samples between our F14Cm results (corrected for δ13C fractionation) and sample size are fitted (Figure 6), and the quantity of our mc and F14Cc involved different procedural stages are calculated and presented in Table 1. Based on a two-component mixing model explored in the publication of Hua et.al. (Reference Hua, Zoppi, Williams and Smith2004), the F14C of our several IAEA reference materials are corrected, the corrected results are illustrated in Figure 8 and discussed in the section “Accuracy and Reproducibility.”

Figure 6 The 14C counts rate (CPS, counts per second) and 12C3+ current values of the reagents used in the ultra-small graphite holders. The blue bar chart represented the CPS values of before and after reduced Fe2O3 reagents, the brown curves represent 12C3+ current values of before and after reduced Fe2O3 reagents. The x-axis represents many measurements of targets which were made of Fe and Fe2O3 powder in measured wheels.

Results of F14Cc and mc for the different procedural stages of our 14C-AMS analysis are obtained more precisely based on the mass-balance model with the Fc and mc of the four background standard materials in Table 1. These results include a carbon contamination mass of 0.07 ± 0.01 μg of C with an F14Cc value of 1.33 ± 0.37 introduced from the acid-base-acid chemical pretreatment process for organics, a mass of 0.11 ± 0.02 μg of C with an F14Cc value of 1.39 ± 0.37 introduced from the combustion process, a mass of 0.04 ± 0.008 μg of C with an F14Cc value of 1.36 ± 0.19 introduced from acid-hydrolyzation process for carbonates, and a larger mass of 0.54 ± 0.10 μg of C with an F14Cc value of 0.44 ± 0.09 introduced from graphitization and AMS measurements process. It is concluded that mc of graphitization is the most, and more dead carbon contamination is introduced from this process (F14C $ \ll $ 1).

Iron catalyst is a key participant in the entire graphitization and AMS measurements, the most probable source of dead carbon contamination can be iron catalyst (Cherkinsky et al. Reference Cherkinsky, Prasad and Dvoracek2013). Correction for contamination of dead and modern carbon which could be present in the catalyst or from cross-contamination in the ion source also plays a significant role, it should not be neglected especially in the 14C-AMS analysis of ultra-small samples (<20 μg C). Therefore, our measurement results of small samples are performed using a correction method of 14C counts from iron.

Correction of 14C Counts from Fe Powder

In the measured wheels of ultra-small samples, targets made of Fe powder, Nb powder, and Fe2O3 were also added. Fe powder and Fe2O3 powder were prepared in two ways: (1) pre-activated and (2) post-activated. Pre-activated targets were heated to 600°C for 2 hr. Post-activated targets were reduced with H2 at 600°C. We measured the 14C count rate and 12C3+ beam currents for these targets. The 14C count rate of Fe powder and 12C3+ beam currents of the pre-activated and post-activated targets are shown in Figure 7. The 14C count rate and 12C3+ beam currents have changed before and after activated Fe2O3. Post-activated targets had higher 14C count rates. This implies that atmospheric 14CO2 (of modern origin) could have contaminated the catalyst during the reaction process. Therefore, we introduce a correction for the exogenous carbon contribution during graphitization by subtracting 14C counts from Fe powder alone. The corrected F14C was obtained from the subtraction of 14C counts for all samples measured in the same batch respectively, which also includes various standards measured in the same batch the measured, and further calculations with formulas involved in the conventional 14C-AMS analysis.

Figure 7 (a) F14C results for multiple 14C-AMS measurements of OxII samples between 0.004 mg C and 1 mg C are shown. The uncorrected F14C values are represented by the black hollow triangle and the corrected F14C values by the black solid triangle. The dashed line represents the consensus value of OxII. The horizontal dark gray (light gray) band indicates the 1σ (2σ) uncertainty calculated from all F14C results corresponding to the range of each sample size. (b) F14C results for background samples between 0.003 mg C and 0.2 mg C from multiple 14C-AMS measurements are shown. The uncorrected F14C values are represented by hollow symbols, and the corrected F14C values by colored solid symbols. Different materials have different symbols and colors: anthracite with square and blue), graphite with Rhombus and yellow, calcite with circle and gray, 14C-free CO2 gas with triangle and orange. The dashed line represents several 14C age boundaries corresponding to F14C values respectively, including 10 ka, 30 ka, 40 ka, and 50 ka. All results have been corrected for fractionation using δ13C AMS measurements, also compared the F14C values before and after 14C counts calibrated from Fe powder for all background samples.

After correction, F14C values of the OxII standard and four background materials with various carbon masses are compared with measured values (Figure 7). Figure 7a shows the variation in F14C values of the OxII standard with varying carbon masses, as well as corrected F14C values. All results have been corrected for fractionation using δ13C-AMS measurements (including machine-induced isotopic fractionation). To precisely clarify the reliability of measurements, the results with three ranges of sample size are analyzed alone. F14C results ranging from 0.1 mg C to 1 mg C mostly fall on the line of the reference value and lie within the 1σ error of all results of measurements in this range. The average F14C of 1.3410 ± 0.0051 analyzed the corrected results of sample size with 0.1–1 mg C agrees with the consensus value of F14C =1.3407 ± 0.0005, with a precision of 3.8‰, which is almost no big difference with of the conventional 14C-AMS analysis. For the range of 0.01–0.1 mg C, the F14C values have the larger error and are more scattered, F14C results generally fall within the 2σ error of all results of measurements in this range. The average F14C of 1.3375 ± 0.0186 (n = 30) analyzed the corrected results of sample size with 0.01–0.1 mg C has some deviation from the consensus value of OxII standard, with a precision of 1.39%. For ultra-small samples of <0.01 mg C, improvement range is larger after correction, but the deviation from consensus remains larger. The 14C count correction from Fe powder does not completely solve the correction problem of C contamination for this range, it is implied that preparing samples of <0.1 mg C is very challenging, probably it is necessary to improve the accuracy via strictly controlling the procedural background in the future.

Figure 7b illustrates the variation in F14C values of all background samples with varying carbon masses, and the corrected background F14C results. The F14C values of small background samples increase with decreasing carbon masses. For small samples more than 0.1 mg C, the background 14C ages remain above 40 ka even for 14C–free CO2 gas close to 50 ka after 14C counts correction. Before the correction, the background 14C results for small samples of 0.1–0.02 mg C generally ranged from 30–40 ka, whereas the 14C results of 14C-free CO2 gas samples appeared to be higher, mostly around 40 ka; as carbon mass decreases, the background F14C values gradually increase, with the 14C age of about 30 ka. With correction, extraneous carbon contamination is removed during the graphitization process, resulting in smaller F14C values and higher background 14C ages, specifically for background gas. For ultra-small samples of <0.02 mg C, the background F14C values rapidly increase with decreasing carbon masses, which is generally scattered between 20 ka and 35 ka. After correction, the 14C age was close to 40 ka, emphasizing the importance of 14C count correction from Fe powder, which is required urgently for ultra-small samples, specifically those near background levels of less than 0.02 mg C. Consequently, the good agreement of the measurements of OxII and four background standards with their reference values demonstrates the improvement of contamination correction and a good precision of ultra-mass graphite preparation and AMS measurement for small samples of >0.01 mg C at Xi’an AMS center.

Accuracy and Reproducibility

To assess the accuracy and reproducibility of our micro-scale 14C-AMS analysis, we prepared and measured four reference materials from the International Atomic Energy Agency (IAEA), IAEA-C2 (travertine, 7135a BP), IAEA-C3 (cellulose, modern sample), IAEA-C6 (ANU sucrose, modern sample), and IAEA-C7 (oxalic acid, 5644a BP), covering a range of 0.01–0.1 mg C. The IAEA series can help in evaluating different correction methods and measurement performance of small samples. The corrected F14C values applying three methods for our IAEA reference materials are compared, including (1) the traditional background subtraction: The F14C values of samples are calculated by the direct subtraction of the F14C values of background measured in the same batch; (2) the constant contamination model: Based on a two-component mixing model explored in the publication of Hua et al. Reference Hua, Zoppi, Williams and Smith2004; and (3) our correction of 14C counts from iron. The three corrected F14C results with the same sample sizes are illustrated in Figure 8. The corrected results with method (2) are mostly higher than the other corrected results, and the corrected results with method (1) and method (3) are close to each other. In comparison, the corrected F14C values based on our correction of iron counts are mostly closer to their corresponding consensus values and lie within 1σ uncertainty of all corrected results, which indicates good reproducibility for samples with >0.01 mg of C. Overall, 14C analysis of small IAEA reference standard samples containing different sample types and age ranges below 10 ka BP show that our 14C analysis of ultra-small samples of 10–100 μg C obtained accurate and reproducible results.

Figure 8 F14C corrected values of IAEA standards ranging 10–100 μg C from multiple 14C-AMS measurements. (a) Different symbols show different correction methods: the traditional background subtraction (black solid squares), constant contamination model (red solid circle), and our correction of 14C counts from iron (blue solid triangle). The black dashed lines represent the F14C consensus values of IAEA standards, the black solid lines and the horizontal gray band represent the average and its associated onesigma uncertainty of all corrected results.

Case Study

Chronological Framework for Marine Sediment Based on 14C Analysis of Small Foraminiferal Samples

Marine sediments are important scientific carriers for studying major issues including paleoclimate change, sea level trends, and geochemical cycles. Understanding the above issues require a precise chronological frame for marine sediments. Planktonic foraminifera is frequently used as 14C-AMS dating material for marine sediment. We have a collection of foraminifer samples from the South China Sea that have been classified into the genera G.ruber and G.sacculifer, respectively. We aim to determine a basic chronological sequence for sediment cores from the South China Sea. In practice, there exist few representative and reliable dating materials in sediments, and many harbor exogenous carbon, making the final 14C results unreliable and difficult to interpret. As a result, foraminiferal shells in marine sediments are selected for dating; it is even more crucial to select a single species of foraminifera for accurate dating. Nevertheless, the quality of single species of foraminifera that can be obtained is frequently limited. Therefore, establishing a chronological framework of marine sediment cores requires reliable 14C-AMS analysis of small foraminifer samples, even ultra-small samples.

In the first stage, four high-quality foraminifer samples were selected for analysis, i.e., 110–112 cm (B56F), 180–182 cm (B91F), 370–372 cm (B186F), and 453–455 cm (B228F). Through carbonate hydrolysis pretreatment, each sample was separated into many small samples of CO2 (0.01–0.2 mg C) for graphitization and AMS dating. Meanwhile, we prepared 1 mg C graphite of each foraminifer sample for AMS measurement to study if ultra-small foraminifera samples as low as 0.01 mg C could be precisely dated as 1 mg C samples. As shown in Figure 9, the 14C-AMS outcomes of small foraminifer samples have been corrected for isotopic fractionation with δ13C-AMS values and 14C counts of Fe powder. In contrast with the 14C ages of the 1 mg C sample as the reference values, the 14C ages of the four foraminifer samples were all dispersed around the corresponding reference values and are within the 3σ error range of the reference value, which is comparable with the 14C results of 1 mg C sample. This illustrates that our small foraminifer samples of 10–200 µg C can also yield stable and reliable 14C ages, which can help in the dating of important layers lacking effective C fractions and emphasize the importance of correctly constructing the chronological framework of marine sediment cores.

Figure 9 The 14C age results of four foraminifera samples between 10 µgC and 1 mgC from multiple 14C-AMS measurements. All results have been corrected for isotopic fractionation with on-line δ13C AMS values and 14C counts of Fe powder. The black solid squares were represented 14C age values and, the black hollow triangles were represented 12C3+ beam currents, the gray zones were represented the range of 3σ errors of 14C age of 1 mg C sample, the dotted lines were represented the linear relationship between 12C3+ currents and the sample size.

CONCLUSIONS

Accurate and reproducible 14C analyses in small samples containing 10–300 µg C were accomplished using the developed micro-specific graphitization reactors and the 14C-AMS analysis of ultra-small graphite targets. The following conclusions are obtained:

  1. 1. For samples containing less than 200 µg C, a good linear correlation between 12C3+ beam current and sample mass was observed, which corresponded to the maximum 12C3+ beam current of approximately 0.1A/1μgC in our facility.

  2. 2. The analysis of Modern and 14C-dead carbon contamination revealed that the total MCC for small samples was 0.2–1.2 µg C, whereas the DCC was 0.1–1.5 µg C. Moreover, F14Cc and mc for four background standard materials are obtained more precisely based on the constant contamination model. The results reveal that mc of graphitization and AMS measurements is the most significant, and more dead carbon contamination is introduced from this process (F14C $ \ll $ 1).

  3. 3. The good agreement of the measurements of OxII and four background standards with their reference values demonstrates the improvement of contamination correction and a good precision of ultra-mass graphite preparation and AMS measurement for small samples of >0.01 mg C at Xi’an AMS center, especially for ultra-small 14C-free CO2 gas samples of >0.02 mg C, where the 14C age limitation is approximately 40 ka BP.

  4. 4. 14C analysis of small IAEA reference standard samples containing different sample types and age ranges below 10 ka BP was performed, and small foraminifer samples were analyzed and discussed to establish a chronological sequence for marine sediment. Both analyses showed that our 14C analysis of ultra-small samples of 10–100 μg C obtained accurate and reproducible results.

The developed micro-scale 14C-AMS analysis technique proved useful for research applications requiring high-precision dating and tracer applications, acting as a supplement to the conventional 14C-AMS analysis at the mg C level. Ultra-small samples of <10 μg C will be examined in the future.

ACKNOWLEDGMENTS

We are grateful to Dr. Bin Yang for the installation of the micro-specific graphitization reactor. This work was supported by the Strategic Priority Research Program of the Chinese Academy of Sciences (B) (Grant No. XDB40000000), West Light Foundation of the Chinese Academy of Sciences (Grant No. XAB2022000008), the Natural Science Basic Research Program of Shaanxi (Grant No. 2022000017) and Youth Innovation Promotion Association CAS (Grant No. Y2021108).

Footnotes

Selected Papers from the 24th Radiocarbon and 10th Radiocarbon & Archaeology International Conferences, Zurich, Switzerland, 11–16 Sept. 2022

References

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Figure 0

Figure 1 Graphitization reaction curves for a variety of CO2 gases with varying carbon size catalyzed by various Fe reagents. The solid line for Acros FeO, the dashed line for Sigma FeO, and the dotted line for Sigma Fe are used to depict the three Fe catalysts, and the carbon size is decreased sequentially from top to bottom.

Figure 1

Figure 2 The SEM images of iron powder before and after graphitization.

Figure 2

Figure 3 Plot of the average 12C3+ beam current versus the sample sizes. The linear fitting of 12C3+ beam current and the carbon content (%) for three ranges of sample sizes (<20 μg C, 20–100 μg C, and 100–200 μg C) is shown in small figure. The black dots and black line for the range of 100–200 μg C, the blue squares and blue line for the range of 20–100 μg C, the pink triangles and pink line for the range of <20 μg C. (Please see online version for color figures.)

Figure 3

Figure 4 (a) Fraction modern C values for four 14C-free blanks samples from 0.005 mg C to 0.3 mg C sample size are shown to quantify modern carbon contamination (MCC). The four 14C-free blanks represent the MCC from four different processes for the 14C micro-samples analysis: graphitization (14C-free CO2 gas), surface leaching (carbonates: calcite), combustion and purification (organics: graphite), conventional acid/base/acid washes process (organics: anthracite). (b) ΔF14C values for small and ultra-small OxII samples from 0.003 mg C to 1 mg C measured against 1 mg C normalizing OxII standards are shown to quantify the dead carbon contamination (DCC). Note that uncorrected 14C results from smaller OxII samples are always depleted. The solid lines in both plots represent fixed amounts of carbon contamination from 0.1 to 2 µg C.

Figure 4

Figure 5 The fitting curves of the reciprocal relationships between our F14C results and sample size for various standards. (a) OxII standards from 0.003 mgC to 1 mgC. All FC results have been corrected for fractionation using δ13C AMS measurements. (b) Four background materials: anthracite, graphite, calcite, and 14C-free CO2 gas.

Figure 5

Table 1 Summary of carbon contamination masses in our 14C-AMS analysis of ultra-small samples.

Figure 6

Figure 6 The 14C counts rate (CPS, counts per second) and 12C3+ current values of the reagents used in the ultra-small graphite holders. The blue bar chart represented the CPS values of before and after reduced Fe2O3 reagents, the brown curves represent 12C3+ current values of before and after reduced Fe2O3 reagents. The x-axis represents many measurements of targets which were made of Fe and Fe2O3 powder in measured wheels.

Figure 7

Figure 7 (a) F14C results for multiple 14C-AMS measurements of OxII samples between 0.004 mg C and 1 mg C are shown. The uncorrected F14C values are represented by the black hollow triangle and the corrected F14C values by the black solid triangle. The dashed line represents the consensus value of OxII. The horizontal dark gray (light gray) band indicates the 1σ (2σ) uncertainty calculated from all F14C results corresponding to the range of each sample size. (b) F14C results for background samples between 0.003 mg C and 0.2 mg C from multiple 14C-AMS measurements are shown. The uncorrected F14C values are represented by hollow symbols, and the corrected F14C values by colored solid symbols. Different materials have different symbols and colors: anthracite with square and blue), graphite with Rhombus and yellow, calcite with circle and gray, 14C-free CO2 gas with triangle and orange. The dashed line represents several 14C age boundaries corresponding to F14C values respectively, including 10 ka, 30 ka, 40 ka, and 50 ka. All results have been corrected for fractionation using δ13C AMS measurements, also compared the F14C values before and after 14C counts calibrated from Fe powder for all background samples.

Figure 8

Figure 8 F14C corrected values of IAEA standards ranging 10–100 μg C from multiple 14C-AMS measurements. (a) Different symbols show different correction methods: the traditional background subtraction (black solid squares), constant contamination model (red solid circle), and our correction of 14C counts from iron (blue solid triangle). The black dashed lines represent the F14C consensus values of IAEA standards, the black solid lines and the horizontal gray band represent the average and its associated onesigma uncertainty of all corrected results.

Figure 9

Figure 9 The 14C age results of four foraminifera samples between 10 µgC and 1 mgC from multiple 14C-AMS measurements. All results have been corrected for isotopic fractionation with on-line δ13C AMS values and 14C counts of Fe powder. The black solid squares were represented 14C age values and, the black hollow triangles were represented 12C3+ beam currents, the gray zones were represented the range of 3σ errors of 14C age of 1 mg C sample, the dotted lines were represented the linear relationship between 12C3+ currents and the sample size.