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246
Trace Environmental Quantitative Analysis, Second Edition
eluted off of the sorbent with two 500-µL aliquots of pesticides-residue-grade isooctane. The iso-octane eluent was then passed through a second SPE cartridge. This
second cartridge was packed with approximately 0.5 g of anhydrous sodium sulfate.
The volume of eluent that now contained the recovered analyte was adjusted to a final
volume of 1.0 mL using a volumetric flask. Three microliters of this eluent was injected
via autosampler into an Autosystem Gas Chromatograph (PerkinElmer) incorporating
an electron-capture detector. A 30 m × 0.32 mm capillary GC column containing DB-5
(J&W Scientific) was used to separate the organics in the eluent. This instrument is
abbreviated C-GC-ECD to distinguish it from other gas chromatographs in our laboratory. The column was temperature programmed following injection from 200 to
270°C at a rate of 10°C/min. The C-GC-ECD is connected to a 600 Link (PE-Nelson)
interface module. This interface, in turn, is connected to a 386 personal computer. This
PC uses Turbochrom® (PE-Nelson) software for data acquisition, processing, and
control. A method specific for lindane was written, and one peak was identified within
a 3% relative time interval (retention time window). A retention time, t[R], of 1.8 min
was consistently reproduced using autosampler injection.
Calibration
A series of calibration or working standards were prepared from the methanolic stock
solution containing lindane. This stock solution was prepared by carefully weighing
out pure solid lindane on an analytical balance. These standards were injected into the
C-GC-ECD from lowest to highest lindane concentration. The peak at 1.8 min was
identified as a reference peak in the Turbochrom software, and a narrow t[R] window
was defined around the t[R] of the apex of the peak. A calibration curve was constructed
using a least squares regression algorithm in the software. A correlation coefficient of
0.9990 was obtained.
Sample Analysis
The sequence within which the samples were run after calibration was created by using
the Sequence File Editor within Turbochrom. Samples are injected via autosampler
according to the instructions in the Sequence File. After the sequence is completed, a
Summary File is created and the analytical results are reported within this summary
format. In the Summary File, for each sample analyzed, the following is given:
(a) The sample number
(b) The concentration of lindane in ppb for 1.0 mL of eluent, interpolated from the
external standard mode of instrument calibration
(c) The retention time for lindane, t[R], in minutes
(d) The integrated peak area, in microvolts-seconds
The reported concentration is that for each eluent and should be multiplied by the
eluent volume (in this case, 1.0 mL) to obtain the number of nanograms of lindane
found. The number of nanograms found divided by the volume of the aqueous sample
used in RP-SPE gives the reported concentration in ppb for lindane. The reported
concentration should be divided by the volume of the sample to obtain the reported
concentration in ppb for lindane. The reported concentration should also be divided
by the percent recovery, expressed as a decimal, in order to find the true and final
concentration of lindane in the original sample.
© 2006 by Taylor & Francis Group, LLC
Sample Preparation Techniques
247
Method Evaluation
Lindane is efficiently recovered from aqueous matrices with percent recoveries between
75 and 100% using RP-SPE. The biological sample closely approximates an aqueous
matrix.
70. DOES IT MATTER WHICH ELUTION SOLVENT
IS USED IN RP-SPE?
Answers to this can be given as yes and no and a qualifying statement that it might
depend on the polarity of the retained analyte. With a series of analytes that have
similar octanol–water partition coefficients, differences in eluting solvent polarity
may not significantly influence analyte recovery. If breakthrough studies are not
performed, as discussed earlier, one never knows whether low percent recoveries
are due to poor sorption or to inefficient elution or solvent removal using the RP-SPE
technique. This author recently had the opportunity to quantitatively determine trace
concentrations of 2,4,6-trichlorobiphenyl (246TCBP) and 4-hydroxy-2,4,6-trichlorobiphenyl (4HO246TCBP) in biological matrices. Molecules from these two organic
compounds of environmental interest differ in that a hydroxyl group is substituted
for a hydrogen on the phenyl ring para to the second phenyl. These structures are
as follows:
Cl
Cl
Cl
2, 4, 6-trichloro-bipheny1
Cl
Cl
O
H
Cl
4-hydroxy-2, 4, 6-trichloro-bipheny1
We were quite surprised to measure a zero percent recovery when we attempted
to apply our method for OCs to isolate and recover 4HO246TCBP from spiked
water. Our recoveries of 246TCBP using our OC method were very high. Replacing
iso-octane with methanol as the eluting solvent resulted in a significant increase in
percent recoveries for 4HO246TCBP. This surprising finding led us to conduct a
series of systematic RP-SPE recovery studies. An aqueous spiked sample was prepared that contained both PCB congeners, and two elution schemes were used. In
Scheme A, the retained analytes were eluted with methanol followed by a separate,
second elution with iso-octane. Two receivers were used, and their final volumes
were both adjusted to a 1.0-mL total eluent volume. In Scheme B, the retained
© 2006 by Taylor & Francis Group, LLC
248
Trace Environmental Quantitative Analysis, Second Edition
TABLE 3.13
Comparison of Two Sample Preparation Schemes to
Isolate and Recover 2,4,6-Trichlorobiphenyl and 4Hydroxy-2,4,6-Trichlorobiphenyl Using RP-SPE
246TCBP
Scheme A
Elute with
Elute with
Scheme B
Elute with
Elute with
4HO246TCBP
MeOH, mean of 4 SPEs
iso-octane, mean of 4 SPEs
137,026
40,413
218,526
58,259
iso-octane, mean of 4 SPEs
MeOH, mean of 4 SPEs
210,234
24,825
0
194,002
analytes were eluted with iso-octane followed by methanol. The integrated peak
areas (in units of µV-sec) for the 1-mL eluents are represented in Table 3.13. It is
a good assumption that the response factors for both congeners are near one another
because the substitution of a hydroxyl for hydrogen in the phenyl ring contributes
little or nothing to the ECD response. Eluting first with two 500-µL aliquots of methanol
recovers more 4HO246TCBP than 246TCBP, whereas the second elution with isooctane recovers nearly equal amounts of both congeners. Thus, Scheme A reflects
incomplete recovery of the congeners with two 500-µL aliquots of methanol. Eluting
first with two 500-µL aliquots of iso-octane recovered even more 246TCBP than MeOH,
yet recovered no 4HO246TCBP. This observation was consistent with our preliminary
finding, discussed earlier. Upon eluting with MeOH via Scheme B, a relatively small
amount of 246TCBP was recovered, whereas a relatively large amount of
4HO246TCBP was recovered. The percent recoveries for 4GO246TCBP were similar
between Schemes A and B when MeOH was used to elute off the retained analyte.
Another illustration from the author’s experience is the differences in percent
recovery when hexane is used vs. methyl-tert-butyl ether (MTBE) to elute off of a
C18 sorbent. Two different aqueous matrices were spiked with the OPs diazinon and
malathion. In one series of experiments, two 500-µL aliquots of hexane were used
to elute off of the cartridge, followed by two 500-µL aliquots of MTBE eluted off
of the same cartridge. The same experiment was performed on a second aqueous
matrix that was more acidic by virtue of adding potassium dihydrogen phosphate
(KH2PO4). The results are shown in Table 3.14. It is clearly evident that the more
polar MTBE more effectively removes both OPs from the hydrophobic sorbent than
the less polar hexane. This fact has perhaps more to do with the polarity of OPs and
the nature of the sorbent–analyte–solvent triangle, as discussed earlier in this chapter.
71. HOW CAN PCBS BE ISOLATED AND RECOVERED
FROM SERUM, PLASMA, OR ORGAN FOR TRACE
ENVIRO-HEALTH QA?
Scheme 3.1 (shown earlier) is a flowchart that summarizes this author’s attempt to
use RP-SPE as part of a combination of sample prep techniques that isolate and
© 2006 by Taylor & Francis Group, LLC
Sample Preparation Techniques
249
TABLE 3.14
Percent Recoveries for Diazinon and Malathion Using
Hexane and MTBE as Elution Solvents in RP-SPE
Diazinon
Matrix: 10% NaCl (DDl)
1. Elute with hexane, mean of 3 SPEs
%RSD
2. Elute with MTBE, 1 SPE
Matrix: 10% NaCl, 0.2 M
1. Elute with hexane, mean of 3 SPEs
%RSD
2. Elute with MTBE, 1 SPE
Malathion
20
18.3
0
—
20
14
112
0
—
98
recover AR 1248 with nearly 100% recoveries.101 PCBs are easily released from a
serum, plasma, or tissue homogenate via probe sonification (PC), coagulation using
acetonitrile, or other water-miscible organic solvent or salt. The supernatant aqueous
phase is easily separated from the coagulated protein via mini-centrifugation.
RP-SPE serves in this case, similar to the situation when an environmental water
sample is passed through, as an on–off or digital extraction step. The dilute of the
aqueous supernatant serves to decrease the analyte–matrix interaction, as discussed
earlier, which in turn strengthens the analyte–sorbent interaction. In this case, the
combination of PS-RP-SPE with C-GC-ECD as the determinative technique eliminated the need for further cleanup. Such might not be the case if C-GC-MS or
another universal determinative technique is used. Cleanup techniques might then
need to be considered. Listed below are significant outcomes from the author’s
method development study:101
Sample
Recovery as Total PCB (%)
Spiked
Spiked
Spiked
Spiked
Spiked
102
102
115
88.2
77.7
acetonitrile 1
acetonitrile 2
rat liver 1
rat liver 2
rat liver 3
Janák and coworkers102 have discussed a similar approach to the isolation and
recovery of PCBs from whole blood. Details of their approach are outlined via a
flowchart in Scheme 3.8. Referring to Scheme 3.8A, formic acid dissolved in isopropyl alcohol (IPA) was used to coagulate protein from 5 g of whole blood prior
to bath sonication. After passing the supernatant through a conditioned RP-SPE
cartridge, the sorbent is washed with 5% IPA dissolved in water, followed by 10%
methanol in water. The sorbent is then washed again with a series of solutions as
indicated and dried. Referring to Scheme 3.8B, the sorbent is eluted with methylene
chloride (dichloromethane), then evaporated down to 10 µL, and finally reconstituted
with enough heptane to yield ~100 µL. This heptane eluent is transferred to a Pasteur
© 2006 by Taylor & Francis Group, LLC