14.1 - L.Leese

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An Agency of the Health and Safety Executive www.hsl.gov.uk An Agency of the Health and Safety Executive

Arsenic speciation in urine using µLC ICP-MS for routine biological monitoring – A two year study

Elizabeth Leese, Jackie Morton and Vikki Carolan

Email – liz.leese@hsl.gsi.gov.uk

ISBM – Wednesday 11th September 2013

An Agency of the Health and Safety Executive

Introduction

• Arsenic & exposure

• Workplace exposure

• µLC-ICP-MS separation technique

• Background Levels study

• 2 year semi-conductor workplace study

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Arsenic

• Found in all rock, soil, water and air.

• Ranked – 20th most abundant element in the earths crust

– 14th in seawater

– 12th human body

• Classified as a group 1 carcinogen by IARC – Cancer of the skin, lung, kidney and bladder.

– Vomiting, abdominal pain, weakness, diarrhoea and muscle cramps.

• Exposure – Inhalation

– Ingestion

– Dermal

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Species of Arsenic

Monomethylarsonite (MMA3+)

Dimethylarsinite (DMA3+)

Arsenite As3+

Arsenate As5+

Dimethylarsinate (DMA5+)

Monomethylarsonate (MMA5+)

Arsenocholine, AC

Trimethylarsonioacetate Arsenobetaine, AB

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Arsenic Exposure

• Environmental & Dietary

– Cigarettes

– Shellfish & Seafood

– Poultry

– Grain e.g. rice

– Red wine / real ale

– Soil and water

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Arsenic Exposure Worldwide

http://www.bgs.ac.uk/arsenic/

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Arsenic Exposure

• Occupational – Semi Conductor Industry

– Glass Production / Recycling

– Wood Preservation / burning preserved wood

– Pesticide manufacture / application

– Power plants burning arsenic rich coal

– Mining, smelting & landfill

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Urinary Arsenic Analysis – Problem 1

• Total Arsenic

– A total element value is not helpful when assessing exposure, because its unable to distinguish dietary arsenic from toxic inorganic arsenic

• Hydride / Extraction techniques

– Difficulty reducing methylated metabolites • Under estimation

– Food & drink containing methylated metabolites

e.g. rice, red wine & seafood • Over estimation

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Arsenic Speciation - µLC-ICP-MS

• Allows separation of individual species

• Species of Interest

– Inorganic - As3+ As5+

– Methylated Metabolites – DMA5+ MMA5+

– Dietary – AB.

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Separation Technique

ICP-MS

Thermo Scientific XSERIES 2

ESI OneFAST

• 6 port switching value

• 1 ml sample loop

• 50x4mm ID Dionex AG7 column

Mobile Phase A – 2 mM Ammonium carbonate

Mobile Phase B – 70 mM Ammonium carbonate

As3+

As5+ MMA

DMA

AB

1 µg/L Standard

As3+

As5+ MMA

DMA

AB

10 µg/L spiked urine

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Urinary Arsenic Analysis – Problem 2

• Lack of unexposed Background Reference Values

• NO UK Guidance Values

• Drinking water

– EU 10 µg/L total arsenic

– US & WHO 10 µg/L inorganic arsenic

• Biological Samples

– US BEI 35 µg/L summation of inorganic &

– German BAT 50 µg/L metabolites NO AB

• Population studies from unexposed individuals

Most studies people are asked to abstain from eating shellfish and seafood.

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Background Levels Study

• 95 urine samples collected from 53 males and 42 females (>18 years old)

• Not occupationally exposed to arsenic

• Questionnaire returned with urine sample

– Gender / Date of birth

– Smoking habits

– Dietary supplement

– Diet of previous 7 days • Fish Shellfish Seaweed

• Rice Mushrooms Poultry

• Red wine Real ale Bran / germ

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Background Levels Results

Health Canada – Human Biomonitoring of Environmental Chemicals in Canada. n= 6400

US NHANES – National Report on Human Exposure to Environmental Chemicals. n=2557

As3+ As5+ MMA DMA AB

HSL n=95

µg/L µmol/mol creatinine

µg/L

µmol/mol creatinine

µg/L

µmol/mol creatinine

µg/L

µmol/mol creatinine

µg/L

µmol/mol creatinine

95th percentile 0.54 0.99 0.23 0.35 2.37 3.08 12.68 16.08 126.7 174.7

Mean 0.18 0.30 0.06 0.09 0.78 1.33 4.10 7.09 28.69 51.30

As3+ As5+ MMA DMA AB

µg/L µg/L µg/L µg/L µg/L

Health Canada 95th percentile

4.5 <LOD 3.0 30 110

US NHANES 95th percentile

<LOD 1.10 2.40 16.0 35.0

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Background Levels Results µmol/mol creatinine As3+ As5+ MMA DMA AB

Seafood n=66

Mean 0.31 0.09 1.61 8.76 72.06

Range <LOD – 2.3 <LOD – 0.63 <LOD – 13.9 0.9 - 104 0.3 - 1090

NO seafood n=29

Mean 0.29 0.08 0.70 3.31 4.06

Range <LOD – 1.1 <LOD – 0.56 0.2 – 1.9 0.6 – 7.5 0.1 – 47.8

Red wine (NO seafood) n=9

Mean 0.29 0.16 0.81 4.0 4.6

Range 0.07 – 0.54 <LOD – 0.56 0.3 – 1.3 1.9 – 7.5 0.7 – 47.8

NO wine or seafood n =20

Mean 0.29 0.05 0.65 3.02 2.44

Range 0.03 – 1.1 <LOD – 0.31 0.2 – 1.9 0.6 – 5.2 0.1 – 9.8

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2 Year Occupational Study

• Semi-conductors

• Pre & Post samples

– Spring

– Autumn

• 91 workers (54 males & 25 females)

• 441 urine samples

– 203 paired pre and post samples

– 35 single samples

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2 Year Occupational Study Results

Semi-conductors

As3+ As5+ MMA DMA AB

n=441 µg/L µmol/mol creatinine

µg/L

µmol/mol creatinine

µg/L

µmol/mol creatinine

µg/L

µmol/mol creatinine

µg/L

µmol/mol creatinine

Mean 0.10 0.12 0.11 0.13 0.58 0.72 3.5 4.2 29.6 37.9

95th percentile 0.31 0.39 0.28 0.45 1.48 1.87 11.4 14.1 111.3 162.8

Unexposed Background

As3+ As5+ MMA DMA AB

n=95 µg/L µmol/mol creatinine

µg/L

µmol/mol creatinine

µg/L

µmol/mol creatinine

µg/L

µmol/mol creatinine

µg/L

µmol/mol creatinine

Mean 0.18 0.30 0.06 0.09 0.78 1.33 4.10 7.09 28.69 51.30

95th percentile 0.54 0.99 0.23 0.35 2.37 3.08 12.68 16.08 126.7 174.7

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Summary

An arsenic speciation method has been used to establish urinary background levels for five arsenic species in a UK population

A two year semi-conductor occupational study showed workers were not exposed.

• Reproducible

• Low LOQs

• Good external quality assurance (GEQAS)

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Thank you