Given that arsenic is a toxin and selenium is an essential nutrient, their precise quantification is crucial for understanding their geochemical cycles and environmental impacts.
However, ICP-MS analysis of arsenic and selenium is complicated by spectral interferences, especially from rare earth elements (REEs) like dysprosium or gadolinium, which can lead to false positives.
This application note explores the use of triple quadrupole (TQ) ICP-MS to mitigate these interferences and improve the monitoring of trace levels of arsenic and selenium in complex samples.
Download this application note to find out:
- How to achieve precise quantification of arsenic and selenium in challenging environmental matrices
- The advantages of TQ-ICP-MS over single quadrupole (SQ) ICP-MS
- How TQ-ICP-MS enhances accuracy in arsenic and selenium analysis
Accurate determination of arsenic and
selenium in environmental samples
using triple quadrupole ICP-MS
Authors: Marcus Manecki1
,
Simon Lofthouse2
, Philipp Boening3
and Shona McSheehy Ducos1
;
1
Thermo Fisher Scientific, Bremen,
Germany; 2
Thermo Fisher Scientific,
Hemel Hempstead, UK; 3
Institute of
Chemistry and Biology of the Marine
Environment (ICBM), Carl von Ossietzky
University of Oldenburg, Oldenburg,
Germany
Keywords: Arsenic, interference removal,
REE, rock, selenium, soil, sediment
Goal
To demonstrate the accurate determination of arsenic
and selenium in sediments and rocks that contain elevated
levels of rare earth elements using triple quadrupole
ICP-MS.
Introduction
Due to the impact arsenic and selenium can have in the
environment at low levels, as a toxin or essential nutrient
respectively, it is important to be able to quantify them
accurately.
Selenium for example is an essential element that is
necessary for normal thyroid function and due to its
antioxidant properties, is associated with several health
benefits. Diseases associated with selenium deficiency
such as Keshan disease and symptoms of hypothyroidism,
are most commonly found in areas where levels of
selenium in soil are particularly low. Supplementation as a
remedy is common practice and is not isolated to humans.
Understanding where soil selenium deficiencies occur for
example supports the correct supplementation of cattle
grazing in those areas to prevent white muscle disease
(a cattle specific selenium deficiency disease).
2
Arsenic on the other hand, in its inorganic forms
(the most common forms found in ground water and soils)
is classified as carcinogenic. Arsenic can be found at
natural, elevated levels or highly enriched in ground waters
(e.g. in Bangladesh) and in soils from irrigation with arsenic
contaminated ground water. In this case, accurate analysis
of arsenic is key to understanding whether crops, such as
rice grown in these areas could contain an elevated level of
arsenic and be a potential risk for consumption.
In addition to assessing the exposure implications of these
elements, their accurate analysis is vital to understanding
their geochemical cycling processes and impact on the
environment.
Analysis of these two elements by ICP-MS is challenging
due to multiple spectral interferences, and becomes
especially challenging in the presence of high amounts
of rare earth elements (REEs) such as dysprosium,
gadolinium, neodymium, samarium or terbium due to the
formation of doubly charged ions. These doubly charged
REEs lead to false positive results on arsenic and selenium
and as such lead to incorrect conclusions and actions
based on that data.
Triple quadrupole (TQ) ICP-MS offers improved interference
removal for such challenging applications through the
use of selective reaction chemistry to produce higher
mass ions, which can either mass shift analytes into an
interference free region of the mass spectrum or mass
shift interferences away from analytes. This application
note evaluates the efficiency of TQ-ICP-MS measurement
modes and compares them to single quadrupole (SQ)
ICP-MS measurement modes with the Thermo Scientific™
iCAP™ TQ ICP-MS for the quantification of arsenic and
selenium in the presence of REEs. To test the robustness
and the accuracy of the approach, two samples, a deep
sea sediment and a geochemical reference standard, were
analyzed under optimal conditions.
Instrumentation
An iCAP TQ ICP-MS was used to analyse all samples.
The system was configured with a high matrix interface
(Table 1) for improved handling of the high amounts of total
dissolved solids (TDS) encountered in the samples and a
200 µL·min-1 free aspirating, glass, concentric nebulizer due
to the limited volume of digested sample.
Four different measurement modes were evaluated:
SQ-STD – single quadrupole mode with no collision/
reaction cell (CRC) gas.
SQ-H2
– single quadrupole mode with CRC pressurized
with pure hydrogen as a reaction gas. Please note that
hydrogen is not available on the Thermo Scientific™
iCAP™ TQe ICP-MS.
SQ-KED – single quadrupole mode with CRC pressurized
with helium as a collision gas and Kinetic Energy
Discrimination (KED) applied.
TQ-O2
– triple quadrupole mode with CRC pressurized
with oxygen as a reaction gas, Q1 set to analyte mass (M+)
and Q3 set to product ion mass (MO+).
All parameters within each of the measurement modes
were defined automatically by using the autotune
procedures provided in the Thermo Scientific™ Qtegra™
Intelligent Scientific Data Solution (ISDS) Software. The
autotune functionality ensures that plasma and interface
related settings, such as nebulizer flow and extraction lens
voltage are automatically applied across all associated
measurement modes so that the sample is processed in
exactly the same way in the plasma, independent of the
CRC and quadrupole settings. Details about the settings
used for the different modes are shown in Table 1.
3
Table 1. Instrument parameters for all measurement modes
Parameter Value
Nebulizer MicroMist quartz nebulizer 0.2 mL·min-1, free aspirating
Spraychamber Quartz cyclonic spraychamber cooled to 2.7 ˚C
Injector 2.5 mm id, quartz
Interface High Matrix (3.5 mm) insert, Ni cones
RF Power 1,550 W
Nebulizer Gas Flow 1.04 L·min-1
Modes SQ-STD SQ-H2 SQ-KED TQ-O2
Mass shift applied No No No Yes
Mass shift over x mass units - - - 16
Gas Flow - 9.0 mL min-1 4.65 mL min-1 0.35 mL min-1
CR Bias -2 -7.55 -21 V - 7.0 V
Q3 Bias -1 -12 V -18 V -12 V
Scan Settings 0.2 s dwell time per analyte, 10 sweeps
The method development assistant in the Qtegra ISDS
Software, Reaction Finder, automatically selects the
best mode to use for the analyte measurements. In
this evaluation exercise, in which the effectiveness of
different measurement modes for the same analyte was
investigated, replicate analytes were added and the
measurement modes selected manually.
The formation of doubly charged ions and the resulting
interferences in ICP-MS are known issues. There are
several ways to mitigate these interferences on the analyte
signals, including:
• Interference correction equations
• Tuning of the instrument to reduce formation of doubly
charged ions within the plasma
• Mass shift reactions that move the analyte of interest to a
different m/z
Many laboratories prefer to avoid the approach of using
interference correction equations as it is possible that
due to small daily changes in plasma conditions, they
need to be calculated or checked on a daily basis to
verify their accuracy. Mass shift reactions show promise
but have limitations with SQ-ICP-MS due to the complex
mixture of ions in the CRC that can cause other potential
interferences. With TQ-ICP-MS, the pre-selection of the
mass of interest in Q1 enables a more controlled reaction
for the analytes and removes interferences that could still
be problematic in SQ-ICP-MS.
The Reaction Finder tool selects TQ-O2
mode automatically
for 75As and 80Se. To be able to compare different
modes and the results for different isotopes, the same
measurement mode was also selected for 78Se and 82Se.
This mode uses pure O2
in the CRC to create oxide ions of
the arsenic and selenium isotopes. Arsenic was measured
at m/z 91 as 75As16O and the selenium isotopes 78Se, 80Se
and 82Se were measured at m/z 94 as 78Se16O, at m/z 96 as
80Se16O and at m/z 98 as 82Se16O respectively.
Figure 1 demonstrates how Q1 (when set to the analyte
mass), effectively removes the singly charged REEs and
any ions that would eventually interfere with the product
ions, such as 91Zr and 94Mo for 75As and 78Se respectively.
Q2 (the CRC) is filled with O2
and creates the product ions
91[AsO]+ and 94[SeO]+ for 75As and 78Se respectively. In Q3,
any remaining doubly charged REE are rejected and the
product ion is isolated f