Heavy metals are well-known environmental pollutants, owing to their toxicity, longevity in the atmosphere and ability to bioaccumulate in the human body.
Currently, analyzing environmental waters often requires multiple tests to account for differences in element chemistry, interferences and detection ranges.
This application note explores the use of an automated system for multi-element analysis of environmental samples using triple quadrupole ICP-MS, a single technique capable of analyzing all relevant elements from a single sample with minimal preparation.
Download this application note to discover:
- One system for streamlined, comprehensive analysis of environmental samples
- A high-throughput tool for enabling informed decision-making and interventions to mitigate potential risks
- Automated sample preparation, reducing the potential for errors, inconsistencies and variability in results
Multi-element analysis of surface and
waste waters using triple quadrupole
ICP-MS with prepFAST autodilution
Authors: Simon Lofthouse1
, Claudia
Charko2
, Kristof Tirez3
and Johan Annys4
;
1
Thermo Fisher Scientific, Hemel
Hempstead, UK; 2
Thermo Fisher Scientific
Breda, NL; 3
Vito NV, MOL, BE; 4
Flanders
Environment Agency (VMM), Aalst, BE
Keywords: Multi-element analysis,
PrepFAST, surface water, triple quadrupole
ICP-MS, waste water
Goal
To demonstrate routine automated multi-element analysis
of environmental samples using triple quadrupole ICP-MS.
Introduction
The adverse effects of increased concentrations of heavy
metals in the environment and their potential impact
on human, animal and plant health are of key concern.
Consequently, monitoring of the content of these elements
in a variety of environmental matrices (ground and surface
waters, drinking water, waste waters, soils and sediments) is
one of the most frequently performed analyses in the context
of environmental legislation. Some of the most common
guidelines for different regions are summarized in Table 1.
Elemental analysis of environmental waters usually requires
a number of different analyses to cover the different
elements depending on element chemistry, interferences
and linear range. Ideally, a single technique that could
measure all environmentally relevant elements from a single
sample, based on an easy sample preparation procedure
(e.g. dilution or digestion), and with potential for automated
and unattended analysis is desirable.
2
Parameter Value
Nebulizer PFA-ST nebulizer pumped at 40 rpm
Spraychamber Quartz cyclonic spraychamber cooled
at 2.7 ˚C
Injector 2.5 mm i.d., Quartz
Interface High Matrix (3.5 mm) insert, Ni cones
RF power 1,550 W
Nebulizer gas flow 1.00 L·min-1
Interface High Matrix
QCell settings SQ-NA SQ-KED TQ-O2
Gas flow N/A 4.7 mL·min-1 0.42
mL·min-1
CR bias -2.0 V -21 V -7.2 V
Q3 bias -1.0 V -18 V -12 V
Regulation Region Applicable for Comment
EPA method 200.8 USA Drinking waters and waste waters Use of collision cell is only approved for waste
waters
EPA method 6020 B USA Solid waste Use of collision cell technology approved
CEN/TS 17200:2018 Europe Digests and eluates of construction products Aqua regia and nitric acid digests
FprEN 16171:2015 Europe Sludge, treated biowaste and soil Use of collision cell or high resolution
technology approved
EN ISO 17294 Europe Drinking waters, surface waters, ground waters,
waste waters
GB3838-2002
China
Surface waters
GB5749-2006 Drinking waters
IS 10500:2012 India Drinking waters Mentions ICP-OES primarily, methods for bottled
drinking water require ICP-MS for analysis
Table 1. Overview of applicable regulatory guidelines for the analysis of drinking waters and waste waters globally
Following the introduction of triple quadrupole ICP-MS,
the routine removal of all types of spectral interferences is
now possible (including doubly charged ions interfering for
example on arsenic and selenium). Used in combination
with an online dilution system, this kind of instrumentation
can offer the possibility of sensitive and robust, quantitative
analysis for all relevant matrix and trace elements in a wide
variety of environmental sample matrices. Triple quadrupole
ICP-MS systems such as the Thermo Scientific™ iCAP™ TQ
ICP-MS, allow the use of reactive gases following a mass
filtration step in a quadrupole mass filter situated axially in
front of the collision/reaction cell (CRC). Therefore, more
confidence in the results for a number of critical elements
(for example cadmium, mercury, arsenic, selenium,
sulphur or silicon) can be achieved compared to the
single quadrupole ICP-MS instruments present in most
environmental laboratories. In combination with the use of
an automated inline dilution system, such as the Elemental
Scientific prepFAST, the iCAP TQ ICP-MS offers the potential
to determine all relevant matrix and trace elements in a
single analysis.
A feasibility study was carried out in collaboration with the
Flemish reference laboratory for environmental monitoring
(Vito), and Flanders Environment Agency (VMM) on 25 waste
waters and 25 surface waters. The aim of this study was to
evaluate the performance of the iCAP TQ ICP-MS for the
quantitative multi-element determination of 68 elements in
aqueous environmental samples, in accordance with the
performance requirements included in the compendium for
sampling, measurement and analysis of water (Compendium
voor analyse van water, commonly abbreviated as WAC)1
.
The results obtained were verified using a combination of
quality control standards and certified reference materials.
Instrumentation
All measurements were performed using an iCAP TQ
ICP-MS. The instrument was operated using the
Thermo Scientific™ Qtegra™ Intelligent Scientific Data
Solution™ (ISDS) Software and was initially optimized
using the supplied tune solution to optimize the interface
parameters for maximum sensitivity. Modes using reactive
gases were also tuned using the supplied autotune
procedures to determine optimum gas flows and potentials
for the CRC and the analysing quadrupole. Typical
operating conditions are summarized in Table 2.
Table 2. Typical instrumental parameters
3
The calibration of the system was carried out daily using a
mixed multi-elemental standard solution. The concentration
levels for the individual calibration standards were as
shown in Table 3.
Element Standard concentrations
Na 5, 25, 50 mg·L-1
Mg 1, 5, 10 mg·L-1
Si 0.5, 2.5, 5 mg·L-1
P 0.2, 1, 2 mg·L-1
S 2.5, 12.5, 25 mg·L-1
K 0.1, 5, 10 mg·L-1
All other elements 0, 10, 50, 100 µg·L-1
Ca 2, 10, 20 mg·L-1
Table 3. Concentration levels for calibration standards
The digested samples were automatically diluted 5 times
by the prepFAST syringe-driven inline dilution system, by
defining a prescriptive dilution factor 5 in the sample list.
The internal standard (Rh 20 µg·L-1 in 1%HNO3/5% butanol)
was added on-line, again utilizing the prepFAST system.
In order to select the appropriate instrument settings (e.g.
choice of reaction gas and the mass to be transmitted in
each quadrupole (Q1 and Q3)), the Reaction Finder method
development assistant was used. Reaction Finder allows
analytical methods to be set up without prior detailed
knowledge of potential reaction pathways caused by
other components in the sample. It also determines the
applied resolution setting for Q1 automatically (intelligent
Mass Selection (iMS) vs. ≤1 amu). Further optimization of
the method parameters, such as for example the use of
different reactive gases for some analytes (e.g. NH3
for the
analysis of Ti and platinum group elements), can also be
accomplished. For this work, different measurement modes
were selected outside the default Reaction Finder settings
and were automatically applied to scan all elements in each
sample using a single aspiration.
• O2
was used for the analysis of 28Si, 31P, 32S, 75As, 80Se,
111Cd and 202Hg in TQ mode
• Single quadrupole no gas mode was selected for 7
Li, 9Be
and 11B
• All other isotopes measured in single quadrupole KED
mode
The performance characteristics included in this note are
indicative and additional optimization of the multi-element
method is necessary, including the use of multiple internal
standards in addition to Rh (e.g. 6Li, Sc, Ge, Ir).
Sample preparation
All 50 samples (25 waste waters and 25 surface waters
collected at different sites in the Flanders region of Belgium)
were digested in accordance with NBN-EN-ISO 15587-1.
In brief, 6 mL of HCl + 2 mL of HNO3
were added to a
25 mL aliquot of each sample, and digested at 105 ˚C for
2 hours using a hot block digestion system. After cooling,
the samples were diluted to a final volume of 50 mL with
ultra-pure water.
The list of elements to be determined is summarized in
Table 4, which contains the following three subcategories:
• NBN EN ISO 17294: 2016 “Water – Application of mass
spectrometry with inductively coupled plasma – Part 2:
Determination of selected elements including uranium
isotopes”: 63 elements are included in this standard
method
• Monitoring: 33 elements that are currently being
monitored in the context o