Separation of dissolved trace elements into ...

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800. 1000. 1200. 1400. CPS. 0. 10000. 20000. 30000. 40000. Repeatability. Organic matter. 600. 1000. 1400. 1800. 2200. 2600. 3000. Absorbance. (254 nm.
Separation of dissolved trace elements into bioaccessibility-based fractions using asymmetrical flow field-flow fractionation (AF4) coupled to ICPMS Chad W. Cuss2, Iain Grant-Weaver2, Marc Cassiede1, Mark Donner2, Lina Du2, Meghan Dueck1, Samineh Kamravaei1, Tommy Noernberg2, Lei Pei1, Nilo Sinnatamby2, Miles Dyck2, Paige Lacy1, Bernadette Quemerais1, and William Shotyk2, Departments of 1Medicine and 2Renewable Resources

MATERIALS AND METHODS Asymmetric flow field-flow fractionation (AF4)

UV-Vis detector

Colloids Flow

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Flow 500

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56Fe

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❶ ❷ 100000

Crossflow shut off



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Time (seconds)

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Modified from Paquin et al., (2002) (ref. 1)

Agilent 1260 diode array Postnova AF2000 Multi-flow AF4 system • 300-Da PES membrane to separate the smallest colloids by size • Measure 200 ≤ λ ≤ 640 nm in 1 nm increments • 500-μm Teflon spacer, 0.3–0.67 mL sample loop every 0.40 s • Flow program: Channel: 0.7 mL min-1, Tip: 0.2 mL min-1, • Use λ = 254 nm as proxy Crossflow: 2.1 mL min-1, Focus time: 7–10 min., Elution: 29 for [organic matter] min. + 1 min. linear crossflow decrease to 0 + 20 min.

Ultra-clean conditions with advanced QC • AF4-ICPMS in certified class-1000, metal-free clean lab • Leach AF4, plasticware with double-distilled HNO3 • Glass reservoir, autosampler vials replaced with polypropylene • Daily: 2 size calibrations, 2 SRMs, LODs (accounts for membrane drift) • Full blanks analyzed between all samples to minimize and account for carryover

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56Fe

20000

Peak Retention time (s) Area 1 455 1016444 2 594 2782018 3 874 3437919

% area 14.0 38.4 47.5

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1000000 800000 600000 400000 200000 0 600

Soil solutions Absorbance (254 nm, mAU)

Absorbance (254 nm, mAU)

80 60 40 20 0 600

Organic matter

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Fe

2.0 1.5 1.0 0.5 0.0 600

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63

Cu

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63

Cu

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137

Ba

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2600

Retention time (s)

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50 40 30 20 10 0 3000

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137Ba (CPS)

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4000 3000 2000 1000 0 3000

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0 500

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89Y (CPS)

1000 800 600 400 200 0

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2000 1500 1000 500 0 3000

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Urine 0.1 1 10 100

350 300 250 1000

3000

238U (CPS)

20000

Absorbance (mAU, log scale)

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Time (s)

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A15

A15

SR

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Patient 1

Fe

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2500 2000 1500 1000 500 0 3000 8000 6000 4000 2000 0 3000

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Patient 2 500

Absorbance (mAU, log scale)

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0.1 1 10 100

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56

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Time (s)

Organic matter

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208Pb (CPS)

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Soil 1, 0.01 M CaCl2 extraction

3000

56

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1000

Retention time (s)

Retention time (min.)

Soil 1, Milli-Q water extraction

800

2500

400 600 800 1000 1200 1400

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Wavelength (nm)

12

2000

56Fe (CPS)

200000 150000 100000 50000 0

SR

CPS

run #3

1500

0

800 1000 1200 1400

A15

% area 13.4 38.3 48.3

1400

800

63Cu (CPS)

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2500 2000 1500 1000 500 0

1400

0

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600

A15

Peak Retention time (s) Area 1 456 925195 2 593 2649850 3 868 3337576

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A15

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SR

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Bromophenol blue: 0.69 kDa (8.019 min. 8.024 min.)

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2

SR

run #2

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SR

56Fe

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137

Ba

CPS (baseline corrected)

• ICP-QMS and ICP-SFMS instruments

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0

Counts per second (CPS)

• Quartz duoPUR still for producing ultrapure nitric acid via sub-boiling double-distillation

400

6

Wavelength (nm)

• Contains 14 HEPA-filtered laminar flow air cabinets designed to minimize trace-metal contamination

80 60 40 20 0

55Mn (CPS)

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A15

0 40000

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0.0

DOM (mAU, 254 nm)

500

PSS-4: 20.7 kDa (15.776 min. 16.034 min.)

PSS-3: 10.2 kDa (13.062 min. 13.218 min.)

0.4

20000

% area 13.9 39.3 46.8

10000

0.6

• Metal-free facility constructed using virgin polypropylene

• High-pressure ultraclave for digesting recalcitrant material

3000

❶ Void peak: mainly ionic + unfocussed ❷ DOM peak: organic-associated ❸ Mainly inorganic (e.g. oxyhydroxides) ❹ Large mainly inorganic • Statistical fractogram deconvolution2 to deconvolute overlapping peaks

A15

PSS-2: 3.42 kDa (10.147 min. 10.144 min.)

0.8

30000

log(tR-t0) = 0.556·log(MM) – 1.438 log(tR-t0) = 0.564·log(MM) – 1.461 R2 = 0.99

Peak Retention time (s) Area 1 454 874860 2 591 2482475 3 858 2951998

run #1

SR

PSS1: 0.89 kDa (8.623 min. 8.628 min.)

56Fe

SR

Void peak

0.2

• Three separate rooms with different particle count levels are available for separating tasks with multiple levels of cleanliness (classes 10,000, 1000, and 100)

2500

Surface waters

Separation & Deconvolution2

SR

1.0

Thermo-Fisher iCAP Qc • HNO3 added online to 2% conc. with 5 ppb In tracer • Collision cell in KED mode • Monitor 20 elements simultaneously, all measured every 2 s

A15

Repeatability 40000

Calibration

CPS

Bioaccessibility depends on speciation • Free ions/truly dissolved tend to be the most available • Colloid availability differs with physicochemical conditions • Larger dissolved particles tend to be less accessible • Speciation also impacts transport through soils and uptake by plants • For many elements, measuring speciation at natural concentrations requires ultra-clean, metal-free conditions to minimize the risk of contamination and reduce background levels

2000

Time (seconds)

CPS

‘Truly dissolved’ + free ions

Trace element fractograms

Organic matter

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0 400

Normalized absorbance

Dissolved particles with adsorbed or occluded metals

Quadrupole ICPMS Counts per second

The biotic ligand model

Absorbance (254 nm)

BACKGROUND

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63Cu

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66Zn

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• AF4-ICPMS using the 300-Da membrane provides high-resolution, high-precision separation of dissolved trace elements and organic matter • Statistical fractogram deconvolution2 facilitates resolution into species that have been associated with varying levels of bioaccessibility1 • Next: Relate distribution of trace element species to uptake by fish in controlled toxicity tests, and to transport through soils and uptake by plants • Next: Relate metal species to organics in urine using metabolomics of fractions (GC-MS) • Next: Characterize size fractions using transmission electron microscopy (TEM)

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238U

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WORKS CITED 1P.R.

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66Zn

20000

Retention time (s)

CONCLUSIONS AND NEXT STEPS

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63Cu

Paquin et al., (2002) The biotic ligand model: a historical overview. Comp. Biochem. Phys. C 133:3-35. 2C.W. Cuss and C. Guéguen (2012) Determination of relative molecular weights of fluorescent components in dissolved organic matter using asymmetrical flow fieldflow fractionation and parallel factor analysis. Anal. Chim. Acta 733:98-102.

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238U

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Retention time (s)

ACKNOWLEDGEMENTS