NERL Research Abstract

EPA's National Exposure Research Laboratory
GPRA Goal 2 - Clean and Safe Water

Significant Research Findings

Method for Identifying Arsenic Species in Urine for Use in
Exposure and Epidemiology Studies

Purpose	Humans are exposed to arsenic primarily through drinking water and dietary

ingestion. The most commonly found arsenic species are in six different
chemical forms: arseno-betaine (AsB), arseno-choline (AsC), dimethyl arsenic
acid (DMA), monomethyl arsonic acid (MMA), arsenite (As(III)), and arsenate
(As(V)). The toxicity of exposure is strongly dependent on dose and chemical
form (As(HI) versus AsB) of the arsenic ingested. However, the application of
traditional analytical methods for the quantification of arsenic results in a total
arsenic concentration. Because this methodology does not differentiate
between more toxic forms of arsenic (e.g., inorganic arsenic) and less toxic
forms of arsenic (e.g., AsB or AsC), a total arsenic concentration will cause an
overestimation of the risk from exposure sources containing only less toxic
forms.

Once ingested by humans, arsenic is predominately excreted in urine. The
ability to separate arsenic into its chemical forms from a urinary sample would
provide valuable information regarding the dose and the source of the arsenic
exposure. Because of the lack of methodology to measure the various forms of
arsenic, arsenic speciation was identified in the Office of Research and
Development's Arsenic Research Plan as a high priority. Thus, research was
conducted to develop an analytical approach capable of providing chemical
form-specific information in a urinary sample that could then be utilized in
future epidemiology studies to assess an individual's exposure to arsenic.
Specifically, this analytical methodology provides epidemiologists and risk
assessors with improved capabilities for measuring and associating arsenic
exposures with observed adverse health effects. The goal of this research was
to develop a methodology that provides excellent sensitivity and selectivity,
good matrix (urinary sample) tolerance, and chromatographic resolution in
combination with reasonable analysis time.

Research Ion chromatography (IC) coupled with Inductively Coupled Plasma Mass
Approach Spectrometry (ICP-MS) detection is one of the premier analytical techniques in
arsenic speciation because it combines both the separation strength of IC and

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the parts-per-trillion detection capability of ICP-MS. The two sample
introduction approaches investigated were direct nebulization and hydride
generation. Direct nebulization offers experimental simplicity by allowing a
direct coupling of the IC to the ICP-MS, but requires chromatography to
separate the arsenic species found in the urine sample from the chloride ion also
found in urine. However, if hydride generation is used as the sample
introduction approach, the chromatographic separation of the chloride ion from
the arsenicals is not required. Hydride generation, in effect, eliminates the
chloride ion as a source of interference, and, in doing so, eliminates a source of
false positives via increased detector selectivity. This added selectivity is
achieved at the expense of added instrumental complexity.

Major	The publications listed in this abstract outline an analytical approach for

Findings and speciating arsenic in urine. The major developments from this research are
Significance ,• , . . ,
s	listed below.

(1)	The development of a membrane hydride generation ICP-MS system that
can provide arsenic speciation data in a urine matrix at the low parts-per-trillion
concentration range. This inherent sensitivity allows the complex matrix
associated with urine to be diluted, and thus alleviates the chromatographic
problems associated with the high salt concentrations typical of urine samples.

(2)	The development of a complementary direct nebulization procedure
provides an experimentally simpler approach that could be used by routine
testing or non-research oriented laboratories.

(3)	The development of a photo-oxidation hydride system that provides the
means to detect all arsenicals in the urine sample, including exposure source
information that may indicate individual dietary patterns (e.g., high AsB and
AsC indicates high seafood ingestion). If the photo-oxidation step is omitted
(turning the UV lamp off), then only the more toxic arsenicals are detected,
thereby providing an analysis that more directly reflects the potential for risk.

Publications Wei, X.-Y., Brockhoff-Schwegel, C.A., Creed, J.T. Application of sample pre-oxidation of

arsenite in human urine prior to speciation via on-line photo-oxidation with membrane
hydride generation and ICP-MS detection. Analyst 125: 1215-1220, 2000.

Wei, X.-Y., Brockhoff-Schwegel, C.A., Creed, J.T. A comparison of urinary arsenic speciation
via direct nebulization and on-line photo-oxidation hydride generation with IC
separation and ICP-MS detection. Journal of Analytical Atomic Spectrometry.
Submitted.

Recent literature reports indicate that the ingestion of arsenosugars
(predominately associated with seafood ingestion) can produce metabolites of
the arsenosugars. To date, these metabolites have not been structurally
identified, and their potential toxicity is not known. The identification and
elution characteristics of these metabolites in urine, including MMA(III) and

Future
Research

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DMA(III), is an area needing additional research.

For additional information about identifying arsenic species, contact:
John Creed, Ph.D.

U.S. Environmental Protection Agency
National Exposure Research Laboratory
26 W. Martin Luther King Dr.

Cincinnati, OH 45268-1320
Phone: (513)569-7298
E-mail: creed.jack@epa.gov

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