3
Postcolumn reagent
Dissolve 0.06 g of PAR in 1.0 L Dionex MetPac PAR
postcolumn diluent.
Stock solution for sample and pH adjustment
1 M Hydrochloric acid
Weigh 909.70 g of deionized water (Type I reagent grade,
18 MΩ∙cm resistance or better) into an eluent bottle. Tare
the bottle and carefully add 90.3 mL of ultrapure reagent
grade hydrochloric acid directly to the bottle.
Standard and sample preparation
Add 1.0 mL of 1 M hydrochloric acid to 499 g of
sample or standard solution. The final concentration of
hydrochloric acid is 2 mM.
Glassware cleanings
Prior to use, high density polyethylene (HDPE) containers
used for samples and standards preparation were rinsed
with DI water and an aliquot of the sample to reduce the
amount of leachable transition metals from the bottle. To
avoid contamination and pH errors when formulating the
eluent and the PAR reagent, use the high purity reagents
offered by Thermo Fisher Scientific.
System operation
System configuration and operation parameters for
this application are outlined in a previously published
document.
3
To ensure efficient 2 mm column operation, 0.125 mm
(0.005 in.) tubing must be used. Lengths of connecting
tubing should be kept as short as possible to minimize
system void volume. Carefully use a razor blade or
plastic tubing cutter so that the ends of the tubing cuts
are straight and smooth. Irregularity on the surface of a
tubing end can result in unwanted dead volume.
Sample preconcentration is used to improve
sensitivity and lower the detection limits. Samples with
transition metal concentrations below 2 µg/L must be
preconcentrated for accurate quantification. The sample
is loaded onto the Dionex IonPac TCC-2 (Trace Cation
Concentrator) with a pressurized reservoir or Dionex DQP
concentrator pump. The Dionex IonPac TCC-2 column
stationary phase is surface-functionalized sulfonated
resin. We used a flow rate of 2 mL/min and times of 5
and 15 minutes to concentrate 10 and 30 mL of sample.
A Dionex RP-1 pump was used to deliver postcolumn
reagent (PAR). Pneumatic delivery is also acceptable and
either of these techniques can be used successfully in
this method. Figure 1 shows the system configuration.
Results and discussion
Trace level analysis of transition metals is limited by the
purity of water and the reagents. PEEK
™
, metal-free flow
paths are a very important factor in the integrity of the
analytical system. Precautions must be taken at every
step of sample and standard preparation to minimize
contamination. All plastic containers and pipettes
must be cleaned with highest purity reagents (soak in
10 mM HCl overnight and rinse thoroughly with water).
Information about the content of leachable transition
metals in these containers should be obtained from
the supplier. The analytical system flow path, including
tubing, pumps, postcolumn reagent, and sample must be
thoroughly cleaned with 50% IPA/H
2
O at start-up.
To perform analysis of trace levels less than 2 µg/L,
samples must be preconcentrated rather than directly
injected. Figure 2 shows the analysis of 30 mL of a
1 µg/L transition metals standard. All peaks are well
separated from the void volume and from each other and
are therefore easily quantified. Figures 3 and 4 show the
analyses of 10 and 30 mL of high quality deionized water.
These samples were concentrated at 2 mL/min for
5 and 15 min respectively. Iron, copper, and zinc are
major contaminants. Trace analysis of real samples
containing these analytes will depend on the levels of
transition metals present in the water blank. The iron
concentration in 30 mL of water is estimated to be
45 ng/L (ppt) based on the iron area count in the
standard (30 mL of 1 µg/L (ppb) of each transition metal).
Figure 1. System configuration for detection of transition metals.
Waste
Loading
Pump
Concentrator
Column
Guard
Column
Pulse
Damper
Pump
Analytical
Column
3-way
Manifold
10 mm Vis Cell
Knitted Reaction Coil
Pump
Valve