Precise Analysis of Gallium Isotopic Composition by MC-ICP-MS

Sep 4, 2016 - Though an isotope approach could be beneficial for better understanding the biogeochemical cycle of gallium (Ga), an analogue of the ...
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Precise analysis of Gallium isotopic composition by MC-ICP-MS Wei Yuan, Jiubin Chen, Jean-Louis Birck, Zuoying Yin, ShengLiu Yuan, HongMing Cai, Zhongwei Wang, Qiang Huang, and ZhuHong Wang Anal. Chem., Just Accepted Manuscript • DOI: 10.1021/acs.analchem.6b02317 • Publication Date (Web): 04 Sep 2016 Downloaded from http://pubs.acs.org on September 9, 2016

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Table 1. Elution sequence of the two-step separation Eluant

Volume(ml)

Eluted

First column charged with 1.8 ml AG1-X4 resin H2O

10

Cleaning

0.1 M HCl 6 M HCl Sample (6 M HCl) 6 M HCl

10 10 1 10

Cleaning Cleaning + Conditioning Loading Matrix

0.5 M HCl

5

Ga (Fe and Mo)

Second column charged with 1.4 ml Ln-spec resin 0.5 M HCl 0.5 M HCl sample solution 1 M HCl

10 5 6

Conditioning loading + Ga Ga

0.25 M Oxalic acid + 3 M HCl 0.1 M HCl 4 M HCl

20 20 20

Cleaning (Mo, Fe) Cleaning Cleaning (Fe)

2 3

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Table 2. Nu Plasma II ICP-MS Operating Conditions Component

parameter

Stage control Vocuum Capacitor Gas Panel

Back / Forward: 8.83; In / Out: 3.97; Up/Down: 2.93 Lighting: 2330; Running: 2160 Coolant (L/min): 13.0; Aux (L/min): 0.80; Neb (Psi): 27.6; Mix Gas (L/min): 0.00; Mix Gas 2 (L/min): 0.00 Forward (W): 1300 Quad1: 6.3; Quad2: 74.5 HV1: 5999; HV2: 4412; HV3: 3671; HV4: 1700; HV5: 2814; HV6:2408 146Ge2+ (H7); 71Ga (H4); 140Ce2+ (H2); 69Ga (Ax); 137Ba2+ (L1); 68Zn (L2); 135Ba2+ (L3); 67Zn (L4); 66Zn (L5)

RF Power Quads High Voltage Faraday cups setting

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Table 3. Neptune Plus ICP-MS Operating Settings Component

Parameter

Zoom Optics Parameter Center Cup Source lenses

Focus Quad [V] :10.00; Dispersion Quad [V] :0.00 Decelerator [V]:8199.9; Suppressor [V]:9965.0 Extraction [V] :-2000; Focus [V] :-611.0; X-Defl [V] :6.49; Y-Defl [V]:-4.30; Shape [V]:206.00 Rot Quad [V]:18.93; Source Offset [V]:-6.00 Cool gas [L/min]:16.00; Aux Gas [L/min] :0.88; Sample Gas [L/min]:1.065; Add. Gas1 [L/min]:0.00; Add. Gas 2 [L/min]: 0.00; X-Pos [mm]:0.010; Y-Pos [mm] :-3.300; Z-Pos [mm] :-1.850; Peri.Pump [rpm] :5.00; RF Power [W]:1200 71Ga (H4); 70Zn (H3); 69Ga (H2); 137Ba2+ ( H1); 67Zn (RPQ/IC1); 66Zn (L1); 65Cu (L2); 63Cu (L4)

Inlet System

Faraday cups setting 9

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Table 4. Potential species interfering Ga isotope measurement on MC-ICP-MS Species

Mass-69

Mass-71

Monoisotopic species Argides (Hydro)-Oxides

69

71

Elemental species Double-charged species

Ga 40 Ar29Si+, 37Cl16O2+ 51 18 + 52 V O , Cr17O+, 68Zn1H+, 50 Ti 18O1H+, 50V 18O1H+, 50 Cr 18O1H+, 51V17O1H+, 52 Cr16O1H+, 33 36 S S 138Ba2+, 138La2+, 138Ce2+

Ga Ar15N16O 53 Cr18O+, 54Cr17O+, 55Mn16O+, 54 17 + 70 Fe O , Zn1H+, 52Cr18O1H+, 53 Cr17O1H+, 54Cr16O1H+, 54 16 1 + Fe O H 40

142Nd2+, 142Ce2+

12 13

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Table 5. Results of comparison between Nu and Neptune mass spectrometers δ71Ga-SSB (‰)

Sample JB-2 (basalt) BHVO-2 (basalt) Gallium (III) nitrate hydrate GBW(E) 08056 G-2 (Granite) JG-2 (Granite) MAG-1 (Marine mud) GXR-2 (Soil) GXR-3 (Deposit) GBW 07405 (Soil) 15 16 17

δ71Ga-MEEN (‰)

Nu (mean ±2SD)

Neptune (mean ±2SD)

Neptune (mean ±2SD)

0.11 ±0.03 (n=9) 0.08 ±0.02 (n=9 ) 1.83 ±0.04 (n=10) 1.74 ±0.05 (n=21) 0.03 ±0.03 (n=5) 0.02 ±0.03 (n=3) 0.06 ±0.04 (n=5) 0.04 ±0.05 (n=4) 0.03 ±0.05 (n=4) 0.02 ±0.04 (n=5)

0.10 ±0.04 (n=10) 0.07 ±0.03 (n=10) 1.81 ±0.06 (n=6) 1.73 ±0.03 (n=5)

0.11 ±0.02 (n=9) 0.08 ±0.02 (n=10) 1.82 ±0.03 (n=9) 1.72 ±0.02 (n=9)

n, the number of repeated measurements for the same sample including different column procedures (2 or 3). 2SD, 2 times the standard deviation of the population of n repeated measurements.

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Figure 1. Elution curve of Ga seperation from matrix on the AG 1×4 resin (A) and the Ln-spec

19

resin (B). Though most of the major and trace elements were removed in the first step, Ga fraction

20

still contained Fe and Mo, requiring a second purification, which was done on the column charged

21

with Ln-spec resin. The detail procedure was described in the text.

22

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Figure 2. The assessment of the influence of Ba (A), Ce (B), Cu (C), Zn (D), Fe (E) and Mo (F)

24

on Ga isotopic measurements. The δ71Ga data was the average value of 5 replicate analyses, and

25

the error bars represented the 2SD uncertainty of all measurements. The effect of Fe and Mo were

26

investigated on both Nu Plasma II (red dots) and Neptune Plus (blue rhombi) machines.

27

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Figure 3. Reproducibility of Ga isotope ratio (δ71Ga) for long-term measurements of the standard

29

GBW(E) 08056 on the Nu Plasma II (A, red dots) and the Neptune Plus (B, blue rhombi) using

30

SSB correction method, respectively. The dashed lines and solid line represented the external

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long-term standard deviations (2SD) and mean for all tests, respectively. The error bars (2SD)

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were also given for each measurement and were generally better than 0.05‰.

33 34

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Figure 4. Standard addition experiment for validation of the whole purification and isotopic

37

analysis protocol. The experiment was carried out on six mixture solutions of GBW(E) 08056 Ga

38

and NIST 994 Ga. The δ71Ga values measured here (red points with red error bars, n = 5) for the

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two pure standards (0.00 ± 0.05‰ and 1.75 ± 0.06‰) were consistent with the results (0.00 ± 0.04‰

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and 1.74 ± 0.05‰) of long-term measurements. The linear fit attested the accuracy of Ga isotope

41

analysis. The blank dotted lines were the confidence interval of 6 measurements at 95%

42

confidence levels.

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Precise analysis of Gallium isotopic composition by MC-ICP-MS

2

Wei Yuan ab, JiuBin Chen *a, Jean-Louis Birck c, ZuoYing Yin a, ShengLiu Yuan ab,

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HongMing Cai ab, ZhongWei Wang ab, Qiang Huang a and ZhuHong Wang a

4

a

5

Academy of Sciences (IGCAS), Guiyang 550081, China.

6

b

7

c

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75252 Paris, France

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* Corresponding author.

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State Key Laboratory of Environmental Geochemistry, Institute of Geochemistry, Chinese

University of Chinese Academy of Sciences, Beijing 100049, China

Laboratoire de Géochimie et Cosmochimie, Institute de Physique du Globe de Paris (IPGP),

E-mail: [email protected]

Tel.: +86 851 85892669

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ABSTRACT: Though an isotope approach could be beneficial for better

13

understanding the biogeochemical cycle of Gallium (Ga), an analogue of the

14

monoisotopic element aluminum (Al), the geochemistry of Ga isotopes has not been

15

widely elaborated. We developed a two-step method for purifying Ga from geological

16

(biological) samples for precise measurement of Ga isotope ratio using multi-collector

17

inductively coupled plasma mass spectrometry (MC-ICP-MS). Ga was thoroughly

18

separated from other matrix elements using two chromatographic columns loaded

19

with AG 1-X4 and Ln-spec resin, respectively. The separation method was carefully

20

calibrated using both synthetic and natural samples and validated by assessing the

21

extraction yield (99.8 ± 0.8%, 2SD, n = 23) and the reproducibility (2SD uncertainty

22

better than 0.05‰, n = 116) of the measured isotopic ratio (expressed as δ71Ga). The

23

validation of the whole protocol, together with instrumental analysis, was confirmed

24

by the investigation of the matrix effect, the result of a standard addition experiment

25

and the comparison of Ga isotope measurement on two mass spectrometers Nu

26

Plasma II and Neptune Plus. While the measurements using the sample-standard

27

bracketing (SSB) correction method on both instruments resulted in identical δ71Ga

28

values for reference materials, the modified empirical external normalization (MEEN)

29

method gave relatively better precision compared to SSB on Neptune. Our

30

preliminary results showed large variation of δ71Ga (up to 1.83‰) for ten standards,

31

with higher values in industrially produced materials, implying potential application

32

of Ga isotopes.

33 34

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INTRODUCTION

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Discovered by P. E. Lecoq de Boisbaudran in 18751, Gallium (Ga) is a metallic

37

element close to the non-metals in the periodic table and has special physiochemical

38

characteristics and important economic value, thus is of great interest in many

39

research aspects. Over the past decades, significant advancements about Ga

40

geochemistry have been achieved based mainly on the analysis of Ga concentration

41

and species. Generally, Ga exists primarily in trivalent state (Ga3+) and its free

42

elemental form (Ga0) is rarely found in nature1,2. As the third element of the Group

43

IIIA, Ga has chemical properties similar to aluminum (Al), and is frequently used as a

44

geochemical analog of Al3-7. However, unlike Al which is a major element, the trace

45

element Ga sometimes behaves differently and the fractionation between Ga and Al

46

(Ga/Al ratio) was usually used to investigate the transport and behaviors of trace

47

elements in the ocean4,5,8,9, rivers5,10, and during weathering processes10,11. The ratio

48

of B/Ga was also employed in paleoclimate research, for example, to distinguish the

49

terrigenous from marine environment12. Though Ga is involved in many biological

50

processes and is detected in almost all plants and even enriched in some certain

51

species, the exact role of Ga in biological metabolism still remains unclear13.

52

Moreover, the distribution of Ga in the mantle and core of the earth may be an

53

indicator of the material source, physiochemical condition and dynamic processes

54

during differentiation14. Ga is also useful in the cosmochemical studies, for example,

55

the concentration measurement of Ga (with other elements) helps to classify iron

56

meteorites15-19. Though these studies significantly improved our knowledge on the Ga

57

geochemistry, many processes and mechanisms involved in the transportation and

58

transformation of Ga in nature remain unidentified and/or unquantified.

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Economically, Ga is largely used in high-tech applications2,20, including electronics,

60

the missile industry and the power sector21-23. The wide application of Ga in human

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activities would not only lead to a growing demand for Ga, resulting in the urgent

62

exploration of more potential sources beside bauxite or purification and enrichment

63

techniques for low level minerals24-26, but also modify the biogeochemical cycle of Ga 3

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by for example increasing the continental input of Ga to the ocean. Thus, more

65

research is required to better constrain the anthropogenic impact on the

66

biogeochemical cycle of Ga.

67

Since the last decade, the development of multi-collector inductively coupled

68

plasma mass spectrometry (MC-ICP-MS) and the analyte purification techniques have

69

allowed for accurate and precise measurements of isotopic ratios of many metals27-32,

70

which significantly improved our knowledge on different sectors of earth science.

71

Theoretical, experimental and applicable studies have reported large variations of

72

metal stable isotope ratios in a variety of environments, and shown significant

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fractionation of these isotopes induced by many biogeochemical processes, such as,

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adsorption33,34, biological uptake35-38, diffusion39, precipitation40-43 and weathering44.

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A Ga isotope approach could also provide a better understanding of Ga geochemistry.

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Ga has two stable isotopes, 69Ga and 71Ga, with the abundances of 60.1% and 39.9%,

77

respectively19. Previous studies have demonstrated that the species as well as the

78

chemical bond (and lattice) that incorporate Ga could change under different

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geological conditions (pH, temperature, etc.), or be modified in many physiochemical

80

processes6,7,45-47. These changes or processes may fractionate Ga isotopes and thus

81

induce different Ga isotopic signatures in diverse geological (and biological)

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reservoirs. Ga isotopic composition may be also modified by some specific biological

83

processes, for example, the preferential uptake and accumulation of Ga by some

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lichens and mosses than other plants could induce different isotopic effects13. Thus,

85

Ga isotopes may be useful for variable studies of its geochemical behaviors in nature.

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However, apart from several comparative studies on the abundance and distribution of

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Ga isotopes around the middle of last century19,48-52, the geochemistry of Ga isotopes

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has not been widely elaborated up to now, due to probably the lack of an effective and

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reliable method for separating Ga from complex matrices and measuring Ga isotope

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ratio on the new generation mass spectrometers (MC-ICP-MS).

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This work is devoted to a new chromatographic method to purify Ga from

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geological (biological) samples for precise measurement of Ga isotopic composition

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on MC-ICP-MS. The two -stage separation method is based on a series of tests using 4

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various types of elution and even resin, and carefully calibrated by assessing the

95

extraction yield and the reproducibility of the measured isotopic ratio. The whole

96

protocol, together with instrumental analysis is validated by the investigation of the

97

matrix effect, the results of a standard addition experiment and the comparison of Ga

98

isotope measurement on two mass spectrometers (Nu Plasma II and Neptune Plus).

99

EXPERIMENTAL SECTION

100

Materials and Reagents. All materials and reagents including resins, Milli-Q

101

water (18.2 MΩ, Millipore, US), oxalic acid solution (made by oxalic powder) and

102

distilled acids (HCl, HNO3 and HF) were prepared in the clean room (Class 100). The

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anion exchange resin AG1-X4 (200-400 mesh, Bio-rad) and the cation exchange resin

104

Ln-spec (50-100 µm, TrisKem) were used in this study for Ga separation. Both resins

105

were carefully washed with Milli-Q water and the fine floating grains were discarded

106

before loading into the column. All reagent blanks were determined after evaporation

107

of 10 ml solution and were 0.001, 0.001, 0.001, 0.002, 0.002, 0.009, 0.001 and 0.003

108

µg/L for H2O, 0.1 M HCl, 0.5 M HCl, 1M HCl, 4 M HCl, 6 M HCl, 2% HNO3 and “3

109

M HCl + 0.25 M oxalic acid”, respectively, being negligible in comparison to the

110

amounts of Ga in both standards and samples. NIST SRM 994 Ga concentration

111

standard (NIST, US), GBW(E) 08056 industrial synthetic concentrated solution

112

(prepared by Shandong Metallurgical Science Research Institute, China) were used as

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Ga reference materials. The high pure Ga metal standard, NIST SRM 994, was

114

digested by concentrated HNO3 and HCl with heating, then diluted to 1000 ppm by

115

Mill-Q water. Multi-element standard GBW 081531 (National Institute of Metrology,

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China), mono-element Fe standard (GBW(E) 080364, The Department of Water

117

Environment, IWHR, China) and Mo standard (GBW(E) 080218, National Institute of

118

Metrology, China) were employed to model natural samples or for matrix effect tests.

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Cu standard (Alfa Aesar, Germany) was used for mass bias correction in the modified

120

empirical external normalization (MEEN) method. All Teflon labware was cleaned

121

with ultrapure HNO3 and rinsed with Mill-Q water just before their use.

122

Except for GBW(E) 08056 solution, nine reference standards were acid-digested 5

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for the measurements of Ga isotope compositions. Except for the in-house Ga

124

standard solution (GBW(E) 08056), eight reference materials, including JB-2 (basalt),

125

JG-2 (granite), BHVO-2 (basalt), G-2 (granite), GXR-2 (soil), GXR-3 (Hot springs

126

deposit), MAG-1 (marine mud), GBW07405 (soil) and one Gallium (III) nitrate

127

hydrate (Alfa Aesar, Germany) were also prepared and measured for δ71Ga against the

128

international standard NIST 994 Ga. Before analysis, 100 mg of these geological

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materials were digested with first 4 ml concentrated HNO3 and HF (1:1) in Teflon

130

vials (48 h at 140 ℃), then 1 ml concentrated HNO3 and finally 1 ml 6 M HCl,

131

respectively. After dryness, the last residue was dissolved in 1 ml 6 M HCl and ready

132

for the column chemistry. Elemental concentrations were measured on ICP-MS

133

NexlON 300X (PerkinElmer®, US), with the precision better than 5% (2SD) based on

134

repeated analysis of the geostandard SLRS-5.

135

Ga separation protocol. For precise Ga isotope measurement, it was crucial to

136

thoroughly separate Ga from the matrix and other elements in natural samples,

137

especially from Mg, Al, Fe, Ba, Ce, Cr and Zn, because the presence of these elements

138

could generate spectral effects on Ga isotopes in argide form (Mg, Al), hydro form

139

(Zn) (hydro)-oxide form (Cr, Fe) and double-charged species (Ba, Ce) (see below

140

“Matrix effect on Ga isotopic measurement”). For ensure matrix-matched principle on

141

Ga isotopic measurement Mo and Cu, which often present in natural samples, should

142

also be separated from Ga30,53. The protocol was composed of two chromatographic

143

steps: the first step for purifying Ga from most major and minor elements, and the

144

second step for separating Ga from Fe and Mo, respectively. The elution scheme for

145

the whole purification process was summarized in Table 1. Both steps were carried

146

out on a polypropylene column (inner diameter 0.8× 4 cm, length 9 cm, Bio-Rad).

147

For the first step, the column charged with 1.8 ml AG1-X4 resin was first rinsed

148

with 10 ml H2O and 10 ml 0.1 M HCl, then conditioned with 10 ml 6 M HCl, the

149

sample was loaded in 6 M HCl afterwards. After rinsing with 10 ml 6 M HCl, Ga was

150

eluted in 5 ml 0.5 M HCl. Since this Ga elution still contained substantial amounts of

151

Fe and Mo (measured by ICP-MS), a second purification was required.

152

Table 1 6

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The second separation of Ga from Fe and Mo was achieved on the column loaded

154

with 1.4 ml Ln-spec resin. The column was conditioned with 10 ml 0.5 M HCl. The

155

previously obtained 5 ml Ga-contained 0.5 M HCl solution was loaded onto the

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column. Because Mo and Fe were well retained by the Ln-spec resin but not Ga, the

157

liquid passed through the column was immediately collected into Teflon vial. Another

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6 ml 1 M HCl was introduced to elute the rest of Ga still retained in the resin into the

159

same Teflon vial. The 11 ml Ga elution was further evaporated to dryness and the

160

residual was dissolved in 2% HNO3 for isotope and concentration measurements. To

161

reuse the Ln-spec resin, the column was cleaned by 20 ml mixed solution of 0.25 M

162

oxalic acid and 3 M HCl, 20 ml 0.1 M HCl and 20 ml 4 M HCl to strip Fe and Mo.

163

The total procedure blank was 0.3 ng for the whole protocol and 0.2 ng and 0.1 ng for

164

the first and the second steps, respectively, being negligible compared to the mass (at

165

least 200 ng and 80 ng on Nu and Neptune MC-ICP-MS, respectively) needed for a

166

precise isotope analysis.

167

Ga isotope measurement on the Nu MC-ICP-MS. Ga isotope measurement was

168

performed on the Nu Plasma II MC-ICP-MS (Nu Instruments Ltd., UK) at the

169

Institute of Geochemistry, Chinese Academy of Sciences (IGCAS). The Ga standards

170

and samples were measured in 2% HNO3, and the concentration of Ga was fixed to 50

171

µg/L.

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The instrument setting was shown in Table 2. For the cups configuration, mass

173

dispersion was adjusted to allow collection of two Ga isotopes (69Ga and 71Ga), three

174

Zn isotopes (66Zn,67Zn,68Zn) and four double-charged isotopes including 135Ba2+,

175

137

176

was used as sample introduction system and the low-resolution entrance slit was

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chosen throughout the study. The instrumental baseline and peak centering were done

178

before every sample (standard) analysis. Each measurement included 60 integrations

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of 6s in 5 blocks of 12 cycles, followed by a 3-minutes washing with 0.5 M HNO3 to

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lower the Ga signal to insignificant level (< 1 mV). The instrumental sensitivity was

181

about 7 V on 69Ga for a 50 µg/L solution. In this study, the sample-standard bracketing

182

(SSB) method was employed to correct the mass bias for all measurements, because

Ba2+, 140Ce2+ and 146Ge2+ in variable cups. An Aridus II desolvator (CETAC, USA)

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our Nu instrument mostly had a perfect stability, as reported in previous study30,53. Ga

184

isotope results in this study were expressed as δ71Ga, in units of per mil (‰):

185

δ71Ga = [(71Ga/69Ga)sample / (71Ga/69Ga)standard – 1] × 1000

186

here we chose the NIST SRM 994 solid metal Ga as the reference standard, as it was

187

well calibrated (Ga69/71 = 1.50676 ± 0.00039, at 95% confidence interval) and adopted

188

for an ideal international standard purpose54-56.

189

Table 2

(1)

190

Comparison between Nu and Neptune instruments. Ga isotope measurement

191

was also carried out on a Neptune Plus mass spectrometer, another commonly used

192

instrument for comparison. This was done on the Neptune Plus (Thermo Finnigan®,

193

Germany) at the Institute de Physique du Globe de Paris (IPGP), France. The machine

194

setting of Neptune Plus was summarized in Table 3. The desolvator Apex HF (without

195

nitrogen flow) was instead employed as sample inlet system, equipped with a

196

self-aspiring microconcentric PFA nebulizer. The samples (standards) were measured

197

also in 2% HNO3, but the Ga concentration was set to 20 µg/L, because the Neptune

198

Plus had a better sensitivity (8V on 69Ga for a 20 µg/L solution) compared to the Nu

199

Plasma II. Limited by the detector configuration of this particular Neptune Plus, the

200

Faraday cups were set for measuring two Ga isotopes (69Ga,

201

(63Cu,

202

isotope (137Ba2+) (see Table 3).

65

Cu), three Zn isotopes (66Zn,

67

Zn,

70

71

Ga), two Cu isotopes

Zn), and only one double-charged Ba

203

Table 3

204

In addition to the conventional SSB, the modified empirical external normalization

205

(MEEN) method that has been well described and used in previous studies was also

206

employed for the mass bias correction on the Neptune Plus27,30,31,57-59. The general

207

observation from these studies was that, though SSB and MEEN gave similar results

208

for mass bias correction under relatively stable instrumental conditions (the case of

209

our Nu Plasma II), MEEN approach produces better precision when the Neptune

210

instrument was not very stable due to for example the instability of Apex

211

desolvator30,53,54. Two previous studies have reported the usefulness of Ga for

212

correcting mass bias in Cu and Zn isotope analysis60,61 Here, Cu was alternatively 8

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Analytical Chemistry

213

employed for the correction during Ga isotope determination. In this method, the AAS

214

Cu solution provided by IPGP (France)30 was used with the radio of Ga/Cu of 0.5 at

215

Ga concentration of 20 µg/L.

216

Results and discussion

217

The efficiency and reproducibility of Ga separation protocol. Ga was separated

218

from the geological matrix by two ion-exchange chromatography steps: a first

219

pre-concentration using AG 1-X4 resin and a second purification on the special

220

Ln-spec resin. The anion-exchange resin AG1-X4, which was a lower cross-linked

221

(4%) resin, has been successfully used to separate target elements such as Fe, Zn and

222

Hg from natural sample30,31,62. In this study, the resin volume was set to 1.8 ml to give

223

a compromise between a good purification (partially depending on the volume) and

224

the short elution time. The theoretical capacity of AG1-X4 resin was 1 meq/ml, thus

225

with 1.8 ml resin, 41.4 mg Ga3+ could be retained, which allows for separating Ga

226

from a large amount of geological samples, given the average Ga abundance of 17

227

ppm in the Earth Crust1.

228

For precise Ga isotope measurement, the identical matrix should be guaranteed

229

between standard and sample, thus natural samples need to be thoroughly purified,

230

with a particular goal of separating Ga from major (e.g. Fe) and trace elements such as

231

Ba, Ce, Zn, Cu, and Mo (see below discussion on the matrix effect). To establish an

232

appropriate elution scheme, the solution volume Velu needed for eluting the target

233

element can be calculated using the following equation:

234

V = V + M × Kd

235

where V0 is the dead volume of resin, M is the dry mass of resin, and Kd is the

236

partitioning coefficient of Ga in a given solution, defined as63:

237

Kd =

    /       /   

(9)

(10)

238

In hydrochloric acid medium, the partitioning coefficient Kd of Ga3+ between

239

AG1-X4 resin and the solution increase correspondingly64. As Kd was already higher

240

than 5×104 at 6 M HCl, we chose to load samples in this acidity in order to avoid the

241

volatility of concentrated HCl (> 7 M). Theoretically, 50 L of 6 M HCl could be 9

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Page 20 of 40

242

introduced into the column before Ga breakthrough. The Kd of Ga3+ was below 5 at

243

0.5 M HCl, thus Ga could be eluted in about 5 ml 0.5 M HCl. In order to test the

244

above theoretical calculations, a series of experiments were carried out on both

245

synthetic and natural sample solutions and element concentrations were measured for

246

every elution fraction collected 1 ml by 1 ml. The primary elution curves showed that

247

major elements, such as Na, Mg, Ba and Ca, were not retained by the resin at 6 M

248

HCl (Figure 1A). Figure 1A

249 250

However, almost all of Fe and some of Mo went into the 0.5 M Ga fraction (Figure

251

1A), because of the similar partition coefficient for Fe3+ and Mo6+

252

medium, their Kd were of about 104 and 5×102 at 6 M HCl , and both below 5 at 0.5

253

M HCl, respectively. A further separation step is thus needed to separate Ga from Fe

254

(and Mo). We first attempted to use the same resin (AG1-X4) to achieve this

255

separation by changing the concentration or kind of acid, and by adding other

256

reactants. Though the small Kd difference between Fe3+ and Ga3+ signified a

257

possibility to well separate these two elements by modifying the HCl concentration (1

258

M ~ 2 M), our experimental data showed that Fe3+ was promptly and almost

259

simultaneously eluted in Ga3+ solution. Alternatively, we performed the elution using

260

nitric acid and got similar results. Since the Kd of Fe2+ was very different from Ga3+

261

in HCl solution, we then tried to transfer Fe3+ to Fe2+ in column by adding reductants,

262

(ascorbic acid and hydrazine dihydrochloride), but the

263

of Fe3+ was reduced to Fe2+, likely caused by the loss of reducing ability for these

264

reductants in relatively concentrated acid. Finally, we tried to modify the Kd of metals

265

(here Ga, Fe and Mo) to get a good Ga isolation by adding oxalic acid, which

266

generally forms strong metal complexes in HCl elution65, . The tests showed that this

267

addition did change the Kds, but failed to achieve a complete separation, (Fe trailing

268

in Ga elution). Thus, another chromatographic column loaded with different resin

269

should be chosen and employed.

270 271

in the same HCl

results showed that only part

We first chose the column charged with 1.2 ml cation exchange AG 50W-X12 resin (200-400 mesh, Bio-rad) that was widely used

for separating metals in HF 10

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Analytical Chemistry

272

medium66. Though Ga would theoretically beseparated from Fe on this resin in dilute

273

HF, the tests using 1 M or 1.5 M HF for both loading and eluting showed that,

274

although most of Fe3+ was eventually eluted prior to Ga3+, there was still a small Fe3+

275

fraction present in the following Ga eluent.

276

Finally, the Ln-spec resin that was commonly used to separated radium and

277

lanthanides from geological samples67. Given the theoretical capacity of 0.16

278

mmol/ml for this resin, up to 15 mg Ga could be retained with a resin volume of 1.4

279

ml. Interestingly, Ga3+,Fe3+ and Mo6+ displayed quite different Kd on this resin in

280

dilute HCl or HNO3 medium, for example, their Kds were about 0.3 (Ga3+) and 5×103

281

(Fe3+) at 0.5 M HCl, and 0.8 (Ga3+), 5×103 (Fe3+) and 7×102 (Mo6+) at 0.5 M HNO3,

282

respectively. In fact, the specific "phosphoric acid" from the Ln-Spec resin form more

283

stable complexes with Fe (having incomplete “d” electron shell) than Ga (with

284

complete “d” electron donor). Loading in 0.5 M HCl, Fe3+ (and Mo6+) could be

285

retained by the resin but Ga3+ should directly go through. Thus, the last 0.5 M HCl

286

elution containing Ga, Fe and Mo from the first pre-concentration step could be

287

loaded directly on the Ln-spec column without any additional step (e.g. evaporating to

288

dryness and/or changing the acid medium), which allowed for completing the two step

289

separation in a single day. However, the first tests showed that a small fraction of Ga3+

290

still remained in the Ln-spec resin posterior to the loading, requiring another eluent.

291

We chose 6 ml 1 M HCl to elute the remained Ga3+, because at 1 M HCl, the Kd of

292

Ga3+ reached its minimum value of about 0.2, much lower than that of Fe3+ (about

293

103). The concentration measurement showed that Fe and Mo were still retained on

294

the Ln-spec resin and were not found in the 11 ml (5 ml loading 0.5 M HCl plus 6 ml

295

1 M HCl eluent) Ga fraction at all (Figure 1B). Finally, in order to reuse the Ln-spec

296

resin and avoid the possible presence of Fe (and Mo) in Ga fraction65, a mixture of

297

0.25 M oxalic acid and 3 M HCl was used to elute all Mo and most of Fe, the rest of

298

Fe was further removed from the column in 4 M HCl, because the Kd of Fe in this

299

acid medium was the lowest (about 15). A 0.1M HCl solution was inserted before 4 M

300

HCl to clean the possible presence of other elements (such as REEs) (Table 1).

301

Figure 1B 11

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Page 22 of 40

302

In order to check the recovery of Ga, a series of experiments (n = 23) were done

303

using our purification protocol on synthetic solutions (5 ng to 100 µg GBW(E) 08056

304

Ga mixed with other elements such as Fe, Mo, Ba, Na, Zn, etc.). The recoveries of Ga

305

varied from 98.8% to 100.6% with a mean value of 99.8 ± 0.8% (2SD, n=23). Except

306

for some synthetic samples with very low Ga concentration (< 200 ng), Ga isotopic

307

ratios were measured on the Nu Plasma II instrument (see “the measurement of Ga

308

isotopes of reference materials” section) for all elution derived from the above tests.

309

The results showed that δ71Ga varied from 1.69‰ to 1.78‰, averaging 1.74 ± 0.05‰

310

(2SD, n=21).

311

Matrix effect on Ga isotopic measurement. The effect of matrix such as Ga

312

concentration and other species that may interfere Ga isotopic measurement were

313

systematically investigated. The primary experiments on varying Ga concentration

314

from 5 µg/L to 50 µg/L showed that the Ga content should be set to higher than 20

315

µg/L, because a continuous decrease of δ71Ga with Ga concentration down to 5 µg/L

316

was determined, probably due to the instrumental blank effect, as reported in previous

317

work30.

318

Removing the possible spectral interferences derived from elemental isobars, major

319

argides, trace oxides and doubly-charged species was another critical issue for precise

320

Ga isotopic analysis. The potential spectral interferences were summarized in Table 4.

321

According to this table, Ga should be thoroughly separated from elements such as Ba,

322

Ce, Zn, Fe, because they may generate spectral interferences in doubly-charged

323

species (138Ba2+,

324

70

325

138

Ce2+ and

142

Ce2+) or polyatomic forms (54Fe16O1H+,

68

Zn1H+ and

Zn1H+). Table 4

326

Though our two-step method would well purify Ga from other major and trace

327

elements, we still investigated the effect of the possible presence of certain elements

328

such as Ba, Ce, Cu, Zn, Fe and Mo on Ga isotope measurements. This was done by

329

fixing Ga concentration to 50 ppb and by changing the ratios of element/Ga (thus the

330

percentage) in standard solutions. As shown in Figure 2A and Figure 2B, the presence

331

of Ba and Ce induced a significant deviation of δ71Ga from the actual value (around 12

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Analytical Chemistry

332

zero) of the initial Ga standard. This is caused by the doubly-charged interferences of

333

138

334

result in lower and higher δ71Ga values, respectively. Therefore, Ga isotope analysis

335

should be done on solutions absolutely free of Ba and Ce. In the study, the final Ga

336

eluent from the two-column purification contained hardly any Ba and Ce. The effects

337

of the presence of Cu, Zn, Fe and Mo on δ71Ga were also shown in Figure 2C to 2F.

338

Unlike Ba and Ce, no clear influence was found within the measurement uncertainty

339

(0.05‰, see below) for the given element/Ga ratio range, except for Zn that could

340

interfere with Ga isotopes in hydride forms (68ZnH+ and

341

Zn/Ga was higher than 10%. The fact that the abundance of

342

higher than 70Zn (0.62%) might explain the lower δ71Ga values in test solutions with

343

higher Zn/Ga ratio (> 10%), supposing that both Zn isotopes trended to equally form

344

hydrides. In fact, the concentration ratios of Cu/Ga, Zn/Ga, Fe/Ga and Mo/Ga in the

345

last elution of all tests were very small (far below 2%) for both synthetic and sample

346

solutions, implying no significant impact on Ga isotopic measurement. The tests on

347

the Neptune gave similar results to those on Nu instrument (Figure 2E and 2F).

348

Finally, our measurement data showed no argide interferences (e.g.

349

40

350

mV. Though the presence of Mo did not show clear influence on Ga isotopic

351

measurement (Figure 2F), Mo was removed in our protocol in order to guarantee the

352

identical medium in sample to standard solution and avoid unexpected matrix effect.

353

Ba (71.698)2+,

138

Ce (0.251)2+ on

69

Ga and

142

Ce (11.114)2+ on

70

71

Ga, which would

ZnH+) when the ratio of 68

Zn (18.75%) is much

40

Ar29Si+ and

Ar15N16O) on Ga isotopes, as the background Ga level was generally lower than 0.1

Figure 2

354

The validation of Ga isotopic measurement. The standard GBW(E) 08056 was

355

calibrated against the international standard NIST 994 Ga and was measured regularly

356

as in-house standard on the Nu plasma II to control the analysis quality. The Figure

357

3A showed the results of δ71Ga for 116 measurements in one year. All measurements

358

gave an average δ71Ga of 1.74‰ with a long-term external 2SD uncertainty of 0.05‰

359

(Figure 3A). In order to confirm the accuracy and precision of this calibration (Ga

360

isotopic measurement), a standard addition experiment, similar to a previous study68,

361

was carried out by making six mixture solutions of GBW(E) 08056 Ga and NIST 994 13

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Page 24 of 40

362

Ga, with GBW(E) 08056 Ga proportions of 0% (pure NIST 994 Ga solution), 10%,

363

20%, 50%, 80%, and 100% (pure GBW(E)08056 Ga), respectively. The Ga isotope

364

ratio (and concentration) of all mixtures was measured on Nu MC-ICP-MS using the

365

SSB method. The results showed similar δ71Ga values for both pure standards as the

366

long-term measurements, and more important, a linear correlation between δ71Ga and

367

Ga fraction with the correlation coefficient (R2) of 0.997 (Figure 4), attesting the

368

accurate analysis of this in-house standard and that the use of SSB method for mass

369

bias correlation was adequate.

370

Figure 3A, Figure 4

371

Application to the reference materials. Ga was carefully purified from the ten

372

standards using our newly-developed protocol and Ga isotopic composition was

373

measured on either Nu or Neptune ICP-MS or both (Table 5). As seen in Table 5, our

374

shorter-term measurements gave the external 2SD uncertainty of < 0.05‰ for all

375

samples, comparable to the long-term reproducibility (0.05‰, 2SD, n = 116, Figure 3).

376

As a whole, all reference materials displayed a large δ71Ga variation of about 1.83‰,

377

with generally higher values for standards of industrial processes than natural

378

geological materials. Though the exact mechanism enriching heavier Ga isotopes in

379

industrial materials remains unknown, the large difference of δ71Ga between artificial

380

standards and natural materials implies the usefulness of Ga isotopes in studying some

381

aspects of Ga geochemistry, for example for distinguishing natural from

382

anthropogenic sources.

383

Table 5

384

Nu vs. Neptune. For comparison, Ga isotope measurement was carried out on both

385

Nu and Neptune MC-ICP-MS, but with completely different instrumental setting (see

386

Table 2 and Table 3). Concomitant with the best optimization (tuning) of instrument

387

conditions, the Neptune had a better sensitivity (e.g. 8V on 69Ga for 20 µg/L solution)

388

compared to the Nu ICP-MS (about 7 V on

389

Neptune consumed relatively less Ga mass (to give the same signal intensity and

390

results with good precision, see below) and was more adaptable for dilute samples.

391

Regarding the reference control, the cup configuration and the collector design of the

69

Ga for a 50 µg/L solution). Thus the

14

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Analytical Chemistry

392

Nu Plasma II at IGCAS allowed for measuring more isotopes (nine isotopes, Table 2)

393

than the Neptune Plus at IPGP (eight isotopes, Table 3). An especially important point

394

was the ability to measure

395

interferences of

396

complete removal of Ce must be guaranteed, or sample solution must be scanned prior

397

to Ga isotopic analysis on Neptune.

138

Ce2+ and

140

Ce2+ on the Nu Plasma II allowed recognition of the

142

Ce2+ on Ga isotopes (Figure 2B, Table 4). Therefore,

398

Despite the above mentioned difference, 53 measurements of GBW(E) 08056 Ga

399

using the SSB method on the Neptune displayed similar reproducibility (long-term

400

2SD < 0.05‰) as the Nu instrument (Figure 3B, Table 5). Moreover, the analysis of

401

four reference materials (JB-2, BHVO-2, Ga nitrate and GBW(E) 08056) on Neptune

402

using the same SSB correction gave almost identical δ71Ga values to those on Nu

403

(Table 5), implying that Ga isotope ratio can be readily measured on both instruments.

404

The Table 5 also showed that, though measured on the same Neptune ICP-MS at IPGP,

405

for the four references, the MEEN correction method gave relatively better precision

406

(0.02 to 0.03‰) than the SSB method (0.03 to 0.06‰). Figure 3B

407 408

CONCLUSION

409

The new two-step method allows for separating Ga from complex geological matrix,

410

especially from elements such as Ba, Ce, Zn, Cu, and Fe that may interfere with Ga

411

isotope measurement. The separation protocol was thoroughly calibrated and

412

optimized using both synthetic and natural samples, and has been proven to be

413

reproducible and satisfactory for precise Ga isotope ratio determination on

414

MC-ICP-MS. The short-term analysis performed on both Nu and Neptune

415

spectrometers gave identical δ71Ga values for natural materials, and a precision better

416

than 0.05‰, comparable to that (0.05‰, 2SD, n = 116) of the long-term in-house

417

standard calibration. Our preliminary results revealed large variation of δ71Ga (up to

418

1.83‰) in ten natural and industrial reference materials, stimulating further

419

investigation of Ga isotopic composition in natural reservoirs and the relative

420

fractionation mechanisms. The application of isotope approach would provide new 15

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421

insight into the study of the geochemistry cycle of Ga.

422

ACKNOWLEDGMENTS

Page 26 of 40

423

This work was financially supported by the Natural Science Foundation of China

424

(U1301231, 41561134017) and the State Key Laboratory of Environmental

425

Geochemistry, IGCAS (SKLEG2016001). The authors acknowledge the associate

426

editor R. Niessner, reviewer T. Bullen and the anonymous referee who greatly

427

improved the quality of the manuscript. This is IPGP contribution No. XXX.

428 429

Figure captions:

430

Figure 1. Elution curve of Ga separation from matrix on the AG 1×4 resin (A) and the Ln-spec

431

resin (B). Though most of the major and trace elements were removed in the first step, Ga fraction

432

still contained Fe and Mo, requiring a second purification, which was done on the column charged

433

with Ln-spec resin. The detail procedure was described in the text.

434 435

Figure 2. The assessment of the influence of Ba (A), Ce (B), Cu (C), Zn (D), Fe (E) and Mo (F)

436

on Ga isotopic measurements. The δ71Ga data was the average value of 5 replicate analyses, and

437

the error bars represented the 2SD uncertainty of all measurements. The effect of Fe and Mo were

438

investigated on both Nu Plasma II (red dots) and Neptune Plus (blue rhombi) machines.

439 440

Figure 3. Reproducibility of Ga isotope ratio (δ71Ga) for long-term measurements of the standard

441

GBW(E) 08056 on the Nu Plasma II (A, red dots) and the Neptune Plus (B, blue rhombi) using

442

SSB correction method, respectively. The dashed lines and solid line represented the external

443

long-term standard deviations (2SD) and mean for all tests, respectively. The error bars (2SD)

444

were also given for each measurement and were generally better than 0.05‰.

445 446

Figure 4. Standard addition experiment for validation of the whole purification and isotopic

447

analysis protocol. The experiment was carried out on six mixture solutions of GBW(E) 08056 Ga

448

and NIST 994 Ga. The δ71Ga values measured here (red points with red error bars, n = 5) for the

449

two pure standards (0.00 ± 0.05‰ and 1.75 ± 0.06‰) were consistent with the results (0.00 ± 0.04‰ 16

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Analytical Chemistry

450

and 1.74 ± 0.05‰) of long-term measurements. The linear fit attested the accuracy of Ga isotope

451

analysis. The blank dotted lines were the confidence interval of 6 measurements at 95%

452

confidence levels.

453 454

Table captions:

455

Table 1. Elution sequence of the two-step separation Eluant

Volume(ml)

Eluted

First column charged with 1.8 ml AG1-X4 resin H2O 0.1 M HCl 6 M HCl Sample (6 M HCl) 6 M HCl 0.5 M HCl

10 10 10 1 10 5

Cleaning Cleaning Cleaning + Conditioning Loading Matrix Ga (Fe and Mo)

Second column charged with 1.4 ml Ln-spec resin 0.5 M HCl 0.5 M HCl sample solution 1 M HCl

10 5 6

Conditioning loading + Ga Ga

0.25 M Oxalic acid + 3 M HCl 0.1 M HCl 4 M HCl

20 20 20

Cleaning (Mo, Fe) Cleaning Cleaning (Fe)

456 457

17

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Page 28 of 40

458 459

Table 2. Nu Plasma II ICP-MS Operating Conditions Component

parameter

Stage control Vocuum Capacitor Gas Panel

Back / Forward: 8.83; In / Out: 3.97; Up/Down: 2.93 Lighting: 2330; Running: 2160 Coolant (L/min): 13.0; Aux (L/min): 0.80; Neb (Psi): 27.6; Mix Gas (L/min): 0.00; Mix Gas 2 (L/min): 0.00 Forward (W): 1300 Quad1: 6.3; Quad2: 74.5 HV1: 5999; HV2: 4412; HV3: 3671; HV4: 1700; HV5: 2814; HV6:2408 146 Ge2+ (H7); 71Ga (H4); 140Ce2+ (H2); 69Ga (Ax); 137Ba2+ (L1); 68 Zn (L2); 135Ba2+ (L3); 67Zn (L4); 66Zn (L5)

RF Power Quads High Voltage Faraday cups setting

460 461

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Analytical Chemistry

462 463

Table 3. Neptune Plus ICP-MS Operating Settings Component Zoom Optics Parameter Center Cup Source lenses Inlet System

Faraday cups setting

Parameter Focus Quad [V] :10.00; Dispersion Quad [V] :0.00 Decelerator [V]:8199.9; Suppressor [V]:9965.0 Extraction [V] :-2000; Focus [V] :-611.0; X-Defl [V] :6.49; Y-Defl [V]:-4.30; Shape [V]:206.00 Rot Quad [V]:18.93; Source Offset [V]:-6.00 Cool gas [L/min]:16.00; Aux Gas [L/min] :0.88; Sample Gas [L/min]:1.065; Add. Gas1 [L/min]:0.00; Add. Gas 2 [L/min]: 0.00; X-Pos [mm]:0.010; Y-Pos [mm] :-3.300; Z-Pos [mm] :-1.850; Peri.Pump [rpm] :5.00; RF Power [W]:1200 71 Ga (H4); 70Zn (H3); 69Ga (H2); 137Ba2+ ( H1); 67Zn (RPQ/IC1); 66 Zn (L1); 65Cu (L2); 63Cu (L4)

464

19

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465 466

Table 4. Potential species interfering Ga isotope measurement on MC-ICP-MS Species

Mass-69

Mass-71

Monoisotopic species Argides (Hydro)-Oxides

69

71

Elemental species Double-charged species

Ga 40 Ar29Si+, 37Cl16O2+ 51 18 + 52 V O , Cr17O+, 68Zn1H+, 50 Ti 18O1H+, 50V 18O1H+, 50 Cr 18O1H+, 51V17O1H+, 52 Cr16O1H+, 33 36 S S 138 Ba2+, 138La2+, 138Ce2+

Ga Ar15N16O 53 Cr18O+, 54Cr17O+, 55Mn16O+, 54 Fe17O+, 70Zn1H+, 52Cr18O1H+, 53 Cr17O1H+, 54Cr16O1H+, 54 Fe16O1H+ 40

142

Nd2+, 142Ce2+

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Table 5. Results of comparison between Nu and Neptune mass spectrometers δ71Ga-SSB (‰)

Sample JB-2 (basalt) BHVO-2 (basalt) Gallium (III) nitrate hydrate GBW(E) 08056 G-2 (Granite) JG-2 (Granite) MAG-1 (Marine mud) GXR-2 (Soil) GXR-3 (Deposit) GBW 07405 (Soil) 469 470

δ71Ga-MEEN (‰)

Nu (mean ± 2SD)

Neptune (mean ± 2SD)

Neptune (mean ± 2SD)

0.11 ± 0.03 (n=9) 0.08 ± 0.02 (n=9 ) 1.83 ± 0.04 (n=10) 1.74 ± 0.05 (n=21) 0.03 ± 0.03 (n=5) 0.02 ± 0.03 (n=3) 0.06 ± 0.04 (n=5) 0.04 ± 0.05 (n=4) 0.03 ± 0.05 (n=4) 0.02 ± 0.04 (n=5)

0.10 ± 0.04 (n=10) 0.07 ± 0.03 (n=10) 1.81 ± 0.06 (n=6) 1.73 ± 0.03 (n=5)

0.11 ± 0.02 (n=9) 0.08 ± 0.02 (n=10) 1.82 ± 0.03 (n=9) 1.72 ± 0.02 (n=9)

n, the number of repeated measurements for the same sample including different column procedures (2 or 3). 2SD, 2 times the standard deviation of the population of n repeated measurements

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REFERENCES

473 474 475 476 477 478 479 480 481 482 483 484 485 486 487 488 489 490 491 492 493 494 495 496 497 498 499 500 501 502 503 504 505 506 507 508 509 510 511 512 513

(1) Shaw, D. M. Physics and Chemistry of the Earth 1957, 2, 164-211. (2) Moskalyk, R. R. Minerals Engineering 2003, 16, 921-929. (3) Burton, J. D.; Culkin, F.; Riley, J. P. Geochimica et Cosmochimica Acta 1959, 16, 151-180. (4) Orians, K. J.; Bruland, K. W. Nature 1988, 332, 717-719. (5) Shiller, A. M. Geochimica Et Cosmochimica Acta 1988, 52, 1879-1882. (6) Diakonov, II; Pokrovski, G. S.; Benezeth, P.; Schott, J.; Dandurand, J. L.; Escalier, J. Geochimica Et Cosmochimica Acta 1997, 61, 1333-1343. (7) Pokrovsky, O. S.; Pokrovski, G. S.; Schott, J. Journal of Colloid and Interface Science 2004, 279, 314-325. (8) Yamamoto, T.; Otsuka, Y.; Uemura, K. Journal of the Oceanographical Society of Japan 1976, 32, 182-186. (9) Orians, K. J.; Bruland, K. W. Geochimica Et Cosmochimica Acta 1988, 52, 2955-2962. (10) Shiller, A. M.; Frilot, D. M. Geochimica Et Cosmochimica Acta 1996, 60, 1323-1328. (11) Hieronymus, B.; Boulegue, J.; Kotschoubey, B. Chemical Geology 1990, 84, 78-82. (12) Chen, Z. Y.; Chen, Z. L.; Zhang, W. G. Quaternary Research 1997, 47, 181-191. (13) Poledniok, J. Chemosphere 2008, 73, 572-579. (14) McDonough, W. F.; Sun, S. s. Chemical Geology 1995, 120, 223-253. (15) Lovering, J. F.; Nichiporuk, W.; Chodos, A.; Brown, H. Geochimica et Cosmochimica Acta 1957, 11, 263-278. (16) Wasson, J. T. Geochimica et Cosmochimica Acta 1967, 31, 161-180. (17) Wasson, J. T.; Kimbeblin, J. Geochimica et Cosmochimica Acta 1967, 31, 2065-2093. (18) Wasson, J. T.; Schaudy, R. Icarus 1971, 14, 59-70. (19) De Laeter, J. R. Geochimica et Cosmochimica Acta 1972, 36, 735-743. (20) Lovik, A. N.; Restrepo, E.; Muller, D. B. Environmental Science & Technology 2015, 49, 5704-5712. (21) Font, O.; Querol, X.; Juan, R.; Casado, R.; Ruiz, C. R.; Lopez-Soler, A.; Coca, P.; Garcia Pena, F. Journal of Hazardous Materials 2007, 139, 413-423. (22) Gupta, B.; Mudhar, N.; Singh, I. Separation and Purification Technology 2007, 57, 294-303. (23) Chou, W.-L.; Wang, C.-T.; Yang, K.-C.; Huang, Y.-H. Journal of Hazardous Materials 2008, 160, 6-12. (24) Katrak, F.; Agarwal, J. JOM 1981, 33, 33-36. (25) Ibragimov, A.; Budon, S. ENRC Annual Report and Accounts 2010. (26) Gladyshev, S.; Akcil, A.; Abdulvaliev, R.; Tastanov, Y.; Beisembekova, K.; Temirova, S. Hydrometallurgy 2013, 140, 95-101. (27) Marechal, C. N.; Telouk, P.; Albarede, F. Chemical Geology 1999, 156, 251-273. (28) Zhu, X. K.; O'Nions, R. K.; Guo, Y.; Belshaw, N. S.; Rickard, D. Chemical Geology 2000, 163, 139-149. (29) Hintelmann, H.; Foucher, D.; Evans, R. D.; Dillon, P. Geochimica Et Cosmochimica Acta 2003, 67, A147-A147. (30) Chen, J.-B.; Louvat, P.; Gaillardet, J.; Birck, J.-L. Chemical Geology 2009, 259, 120-130. (31) Chen, J.-B; Hintelmann, H.; Dimock, B. Journal of Analytical Atomic Spectrometry 2010, 25, 22

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514 515 516 517 518 519 520 521 522 523 524 525 526 527 528 529 530 531 532 533 534 535 536 537 538 539 540 541 542 543 544 545 546 547 548 549 550 551 552 553 554 555 556 557

1402-1409. (32) Liu, S.-A.; Teng, F.-Z.; Li, S.; Wei, G.-J.; Ma, J.-L.; Li, D. Geochimica Et Cosmochimica Acta 2014, 146, 59-75. (33) Pokrovsky, O. S.; Viers, J.; Freydier, R. Journal of Colloid and Interface Science 2005, 291, 192-200. (34) Juillot, F.; Maréchal, C.; Ponthieu, M.; Cacaly, S.; Morin, G.; Benedetti, M.; Hazemann, J. L.; Proux, O.; Guyot, F. Geochimica et Cosmochimica Acta 2008, 72, 4886-4900. (35) Weiss, D. J.; Mason, T. F. D.; Zhao, F. J.; Kirk, G. J. D.; Coles, B. J.; Horstwood, M. S. A. New Phytologist 2005, 165, 703-710. (36) Gélabert, A.; Pokrovsky, O. S.; Viers, J.; Schott, J.; Boudou, A.; Feurtet-Mazel, A. Geochimica et Cosmochimica Acta 2006, 70, 839-857. (37) Black, J. R.; Yin, Q.-z.; Rustad, J. R.; Casey, W. H. Journal of the American Chemical Society 2007, 129, 8690-8691. (38) Viers, J.; Oliva, P.; Nonell, A.; Gélabert, A.; Sonke, J. E.; Freydier, R.; Gainville, R.; Dupré, B. Chemical Geology 2007, 239, 124-137. (39) Rodushkin, I.; Stenberg, A.; Andrén, H.; Malinovsky, D.; Baxter, D. C. Analytical Chemistry 2004, 76, 2148-2151. (40) Galy, A.; Bar-Matthews, M.; Halicz, L.; O’Nions, R. K. Earth and Planetary Science Letters 2002, 201, 105-115. (41) Immenhauser, A.; Buhl, D.; Richter, D.; Niedermayr, A.; Riechelmann, D.; Dietzel, M.; Schulte, U. Geochimica et Cosmochimica Acta 2010, 74, 4346-4364. (42) Li, W.; Chakraborty, S.; Beard, B. L.; Romanek, C. S.; Johnson, C. M. Earth and Planetary Science Letters 2012, 333–334, 304-316. (43) Saulnier, S.; Rollion-Bard, C.; Vigier, N.; Chaussidon, M. Geochimica et Cosmochimica Acta 2012, 91, 75-91. (44) Bullen, T. D. 2014. (45) Baes, C. F.; Mesmer, R. E. Hydrolysis of cations; Wiley, 1976. (46) Van Gaans, P.; Oonk, H.; Somsen, G. Journal of Solution Chemistry 1990, 19, 831-854. (47) Benézéth, P.; Diakonov, I. I.; Pokrovski, G. S.; Dandurand, J.-L.; Schott, J.; Khodakovsky, I. L. Geochimica et Cosmochimica Acta 1997, 61, 1345-1357. (48) Aston, F. W. Proceedings of the Royal Society of London. Series A, Mathematical and Physical Sciences 1935, 149, 396-405. (49) Sampson, M. B.; Bleakney, W. Physical Review 1936, 50, 456. (50) Inghram, M. G.; Hess Jr, D. C.; Brown, H. S.; Goldberg, E. Physical Review 1948, 74, 343. (51) Hibbs, R., Mass spectrometric measurements of natural isotopic spectra; 1949. (52) Antkiw, S.; Dibeler, V. H. The Journal of Chemical Physics 1953, 21, 1890-1891. (53) Mason, T. F. D.; Weiss, D. J.; Horstwood, M.; Parrish, R. R.; Russell, S. S.; Mullane, E.; Coles, B. J. Journal of Analytical Atomic Spectrometry 2004, 19, 218-226. (54) Yang, L.; Meija, J. Analytical chemistry 2010, 82, 4188-4193. (55) Machlan, L.; Gramlich, J.; Powell, L.; Lambert, G. J. Res. Natl. Bur. Stand. 1986, 91, 323-331. (56) Brand, W. A.; Coplen, T. B.; Vogl, J.; Rosner, M.; Prohaska, T. Pure and Applied Chemistry 2014, 86, 425-467. (57) Woodhead, J. Journal of Analytical Atomic Spectrometry 2002, 17, 1381-1385. (58) Archer, C.; Vance, D. Journal of Analytical Atomic Spectrometry 2004, 19, 656-665. 23

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(59) Vance, D.; Archer, C.; Bermin, J.; Kennaway, G.; Cox, E. J.; Statham, P. J.; Lohan, M. C.; Ellwood, M. J. Geochimica Et Cosmochimica Acta 2006, 70, A666-A666. (60) Hou, Q.; Zhou, L.; Gao, S.; Zhang, T.; Feng, L.; Yang, L. Journal of Analytical Atomic Spectrometry 2016, 31, 280-287. (61) Roehl, R.; Gomez, J.; Woodhouse, L. R. J. Anal. At. Spectrom. 1995, 10, 15-23. (62) Strelow, F. W. E. Talanta 1980, 27, 727-732. (63) Kiriyama, T.; Kuroda, R. Fresenius' Zeitschrift für analytische Chemie 1988, 332, 338-340. (64) Tremillon, B. Mir, Moscow 1967, 33. (65) Strelow, F.; Weinert, C.; Eloff, C. Analytical Chemistry 1972, 44, 2352-2356. (66) Chang, V. T.-C.; Makishima, A.; Belshaw, N. S.; O'Nions, R. K. Journal of Analytical Atomic Spectrometry 2003, 18, 296-301. (67) Horwitz, E.; Bloomquist, C. Journal of Inorganic and Nuclear Chemistry 1975, 37, 425-434. (68) Huang, Q.; Liu, Y. L.; Chen, J. B.; Feng, X. B.; Huang, W. L.; Yuan, S. L.; Cai, H. M.; Fu, X. W. Journal of Analytical Atomic Spectrometry 2015, 30, 957-966.

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The list of table and figure

574 Number

Title

Table 1 Table 2 Table 3 Table 4 Table 5 Figure 1

Elution sequence of the two-step separation Nu Plasma II ICP-MS Operating Conditions Neptune Plus ICP-MS Operating Settings Potential species interfering Ga isotope measurement on MC-ICP-MS Results of comparison between Nu and Neptune mass spectrometers Elution curve of Ga separation from matrix on the AG 1×4 resin (A) and the Ln-spec resin (B) The assessment of the influence of Ba (A), Ce (B), Cu (C), Zn (D), Fe (E) and Mo (F) on Ga isotopic measurements Reproducibility of Ga isotope ratio (δ71Ga) for long-term measurements of the standard GBW(E) 08056 on the Nu Plasma II (A, red dots) and the Neptune Plus (B, blue rhombi) using SSB correction method, respectively Standard addition experiment for validation of the whole purification and isotopic analysis protocol

Figure 2 Figure 3

Figure 4 For TOC only 575 576 577 578

for TOC only:

579

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1

Figure 1. Elution curve of Ga separation from matrix on the AG 1×4 resin (A) and the Ln-spec

2

resin (B). Though most of the major and trace elements were removed in the first step, Ga fraction

3

still contained Fe and Mo, requiring a second purification, which was done on the column charged

4

with Ln-spec resin. The detail procedure was described in the text.

5

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6

Figure 2. The assessment of the influence of Ba (A), Ce (B), Cu (C), Zn (D), Fe (E) and Mo (F)

7

on Ga isotopic measurements. The δ71Ga data was the average value of 5 replicate analyses, and

8

the error bars represented the 2SD uncertainty of all measurements. The effect of Fe and Mo were

9

investigated on both Nu Plasma II (red dots) and Neptune Plus (blue rhombi) machines.

10

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Figure 3. Reproducibility of Ga isotope ratio (δ71Ga) for long-term measurements of the standard

12

GBW(E) 08056 on the Nu Plasma II (A, red dots) and the Neptune Plus (B, blue rhombi) using

13

SSB correction method, respectively. The dashed lines and solid line represented the external

14

long-term standard deviations (2SD) and mean for all tests, respectively. The error bars (2SD)

15

were also given for each measurement and were generally better than 0.05‰.

16 17

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18 19

Figure 4. Standard addition experiment for validation of the whole purification and isotopic

20

analysis protocol. The experiment was carried out on six mixture solutions of GBW(E) 08056 Ga

21

and NIST 994 Ga. The δ71Ga values measured here (red points with red error bars, n = 5) for the

22

two pure standards (0.00 ± 0.05‰ and 1.75 ± 0.06‰) were consistent with the results (0.00 ± 0.04‰

23

and 1.74 ± 0.05‰) of long-term measurements. The linear fit attested the accuracy of Ga isotope

24

analysis. The blank dotted lines were the confidence interval of 6 measurements at 95%

25

confidence levels.

26 27 28

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