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Table 3 Concentrations of major ions (Cl−, NO2−, Br−, NO3−, SO42−, PO43−, F−, acetic acid, formic acid, NH4+, 2A2M (2-amino-2-methyl-1-propanol), and DMA (dimethylamine), from static sampling, air-filter sampling, and swab sampling during sampler-system development up to the launch of the Hayabusa2 spacecraft

From: Environmental assessment in the prelaunch phase of Hayabusa2 for safety declaration of returned samples from the asteroid (162173) Ryugu: background monitoring and risk management during development of the sampler system

Sample code

Profile

Concentration (ng/sample)

Remarks

Anion

Cation

Cl−

NO2−

Br−

NO3−

SO42−

PO43−

F−

Acetic acid

Formic acid

NH4+

2A2M

DMA

Static sampling

 CPS-01

CC1-Py_Schale

1100

9.0

< 3.6

754

156

< 6.5

19

16

10

32

< 9.9

< 4.2

 

 CPS-02

CC2-Py_Schale

181

5.6

< 3.7

136

80

< 6.4

4.0

107

181

< 2.1

< 9.3

< 3.9

 CPS-03

CC3-Py_Schale

269

4.5

< 3.7

287

47

< 6.4

3.8

57

4.2

< 2.1

< 9.3

< 3.9

 CPS-04

CC4-Py_Schale

509

8.5

< 3.7

401

88

< 6.4

11

135

7.6

< 2.1

< 9.3

< 3.9

 CPS-05

CC5-Py_Schale

108

7.1

< 3.7

26

8.8

< 6.4

2.2

27

6.4

< 2.1

< 9.3

< 3.9

 CPS-06

CC6-Py_Schale

110

5.6

< 3.6

29

13

< 6.5

1.5

< 3.7

< 1.9

< 2.1

< 9.9

< 4.2

 CPS-08

CC8-Py_Schale

36

4.0

< 3.7

3.7

6.5

< 6.4

< 0.8

68

4.1

< 2.1

< 9.3

< 3.9

 CPS-09

CC9-Py_Schale

17

< 2.2

< 3.7

< 2.5

5.5

< 6.4

1.9

296

3.7

< 2.1

< 9.3

< 3.9

 CPS-10

CC10-Py_Schale

35

3.1

< 3.7

7.6

20

< 6.4

1.1

107

2.5

< 2.1

< 9.3

< 3.9

 CPS-12

CC12-Py_Schale

17

3.1

< 3.7

9.2

4.4

< 6.4

1.5

64

5.7

< 2.1

< 9.3

< 3.9

 CPS-15

CC15-Py_Schale

< 1.4

3.6

< 3.6

< 2.5

2.2

< 6.5

< 0.8

4.3

5.8

< 2.1

< 9.9

< 4.2

Process blank for experimental background

Air filter sampling

 QFT-01

BLANK-#2

< 80

< 4

< 24

< 80

< 80

20

8

< 80

< 12

180

< 12

< 4

Quartz filter of process blank

 QFT-02

141024-QF-#2

213

< 15

< 27

< 18

630

< 78

129

< 30

< 12

< 15

< 66

< 33

Quartz filter at SFA2

 QFT-03

VAB-12F

188

< 4

< 24

< 80

132

20

48

< 80

< 12

156

< 12

< 4

Quartz filter at VAB-12F

 QFT-04

STA1-CR

156

< 4

< 24

< 80

192

12

160

< 80

< 12

80

< 12

32

Quartz filter at STA1-CR

Swab sampling

 GWT-01

141024-00B

< 12

< 15

< 27

< 18

< 15

< 78

15

< 30

< 12

< 15

< 66

< 33

Glass wool of process blank

 GWT-02

141024-01A-#2

2880

42

< 27

159

216

< 78

276

< 30

< 12

< 15

< 66

< 33

Glass wool at SFA2 payload room

 GWT-03

141024-02A-#2

1170

63

< 27

330

1980

< 78

1290

150

114

< 15

< 66

< 33

Glass wool at SFA2 fairing room elevator

 GWT-04

141024-03A-#2

630

18

< 27

150

540

< 78

12

< 30

< 12

< 15

< 66

< 33

Glass wool at SFA2 fairing room

 GWT-05

141024-04A-#2

23,800

120

< 27

5220

2160

< 78

51

48

36

< 15

< 66

< 33

Glass wool at VAB-12F floor

 GWT-06

141024-05A-#2

23,000

87

< 27

1860

3930

< 78

51

< 30

< 12

< 15

< 66

< 33

Glass wool at VAB-12F support rod

  1. Static concentrations were normalized in units of nanograms per sample (ng/sample) following Takano et al. (2020) using the system of ion chromatography (IC; DX-120 for cations; DX-500 for anions; Dionex Inc.) with Ion Pac CS10 and Ion Pac AS17 columns for cations and anions, respectively (Dionex Inc.). The concentrations of area-based conversions (i.e., ng cm−2) can be obtained by reference to the size scale (Fig. 1). 2A2M and DMA were analyzed in the same way and are shown as the maximum value for the sample