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RAPID DETECTION OF PESTICIDES IN FRUIT JUICE WITHOUT SAMPLE PREPARATION USING HIGH RESOLUTION CHROMATOGRAPHY AND HIGHLY SENSITIVE TANDEM MS
Jan Andre Rojas Stutz1, Dimple Shah2, Gordon Fujimoto3, Lauren Mullin2, and Jennifer Burgess2 1Waters SA de C.V., Col Acacias, C.P. 03240, Mexico, 2Waters Corporation, Milford, MA 01757, 3Waters Corporation, Beverly, MA 01915
INTRODUCTION
Pesticide residues in fruit juices have always been an important food safety issue, especially taking into account the high consumption of juice by children. Reports of the fungicide carbendazim in orange juice has drawn widespread public attention. Since carbendazim is not licensed for use on citrus fruits in the U.S., the FDA began testing shipments of orange juice from foreign sources.
Due to the low detection levels required by regulatory bodies (many pesticides have a maximum residue limit (MRL) of 10 ng/mL in the US, Japan and Europe) and the complexity of matrices in which the targeted analytes are present, identification and quantification of pesticides at low levels is a must.
Many published methods are capable of analyzing pesticides in fruit juice for regulatory purposes. However, sample preparation is required for these methods to minimize matrix interferences. With advances in LC-MS/MS technologies, namely UPLC separation and ultra-sensitive MS detection, a fast screening
method using a simple ‘dilute-and-shoot’ approach was evaluated for multi-residue analysis of pesticides in orange juice.
METHODS
Three orange juice samples were purchased to assess the
detection and quantification of pesticide residues at trace levels
using the simple dilute and shoot protocol. A multi-residue
MS method for the acquisition of 2 MRM transitions for each of
375 pesticides was created using the QuanpediaTM database.
All the compounds were analyzed under ESI positive mode.
EXPERIMENTAL
UPLC Conditions
Column: ACQUITY BEH C18 2.1 X 100 mm, 1.7 µm
Column temp: 45 °C
Injection volume: 10 µL
Flow rate: 0.45 mL/min
Mobile phase A: 10 mM ammonium acetate (pH 5) in water
Mobile phase B: 10 mM ammonium acetate (pH 5) in methanol
MS Conditions
MS system: Xevo™ TQ-S
Ionization mode: ESI Positive
Capillary voltage: 3 kV
Desolvation temp: 500 °C
Desolvation gas flow: 1050 L/Hr
Source temp.: 150 °C
Orange juice samples
The three orange juice samples were diluted 100 times with
water and filtered with 0.45 µm PTFE membrane syringe filters
prior to analysis. Atrazine d5 and carbendazim d3 were used as
internal standards and were spiked at 50ng/mL into each
sample. A description of the samples is given in Table 2.
For spiked samples, a standard mix of 80 pesticides was
prepared and spiked into the orange juice at various
concentrations ranging from 5 to 200 ng/mL, followed by
100 times dilution with water. Samples were filtered and
injected for LC-MS/MS analysis.
RESULTS AND DISCUSSION
Figure 1 shows an overlay of the MRM chromatograms of the
80 pesticides in OJ1 at 10 ng/mL.
The majority of the pesticides were detected at 5 ppb in orange
juice without any further sample preparation. Figure 2 shows
the total number of pesticides detected at the different
concentrations using the simple dilute and shoot approach.
Figure 1. Total ion chromatograms of 80 pesticides at 10ng/mL in
orange juice.
Table 1. UPLC method for pesticides analysis.
Time (min) Flow Rate
(mL/min)
%A %B Curve
Initial 0.450 98 2 6
0.25 0.450 98 2 6
12.25 0.450 1 99 6
13.00 0.450 1 99 6
13.01 0.450 98 2 6
17.00 0.450 98 2 6
Table 2. Description of the orange juice samples.
Sample
Name
Sample Description
OJ1 No pulp not from concentrate, 100% orange juice
OJ2 No pulp not from concentrate, 100% orange juice
OJ3 With pulp from concentrate orange juice
Out of the 80 pesticides that were spiked, 63 pesticides were
detected at 5 ng/mL, which is half of the MRL of most pesticides.
At 10 ng/mL (MRL), a total of 66 pesticides were detected. All
but one of the 80 pesticides were detected at 200 ng/mL.
Method accuracy and precision were analyzed using recovery
studies of pesticides in three samples (OJ1, OJ2 and OJ3). All
samples were spiked at various concentrations ranging from
5 ng/mL to 320 ng/mL to generate matrix matched calibration
curves. Recoveries were calculated from samples pre-spiked at
10 ng/mL. Results for each matrix were obtained from samples
prepared in triplicate, and each of the triplicate preparations
were analyzed twice (total = 18 injections). Of all the
compounds detected at 10 ng/mL, the average recovery
ranged from 87-115% in orange juice samples. These
recoveries fall within the SANCO regulations1. The RSDs of
intra orange juice recovery samples ranged between 0.9% and
19.5%. The vast majority showed RSDs less than 10% with
only 9 pesticides showing RSDs above 10%.
For those compounds detected at the MRL, the linearity of both
solvent curves and curves in the matrix ranged from 0.991 to
0.999 (data not shown). Figure 3 shows the average recoveries
of the pesticides detected at 10 ng/mL in the three orange
juice samples with error bars indicating standard deviations.
Matrix effects
Developing analytical methods for detection of pesticides in
food is often challenging due to the complexity of matrices. It
is necessary to characterize and desirable to reduce matrix
interferences to ensure accurate quantification of analytes. The
matrix effect was studied for all three samples by comparison
of the slope of calibration curve in solvent and in matrix. An
increase in the gradient of the matrix curve compared to the
solvent curve indicates ion enhancement while a decrease in
the gradient of the matrix curve indicates ion suppression.
A percentage variation between +20% was considered as no
matrix effect as this variation is close to the repeatability
values1. Values between +20% to +50% were considered as a
medium matrix effects, and a strong matrix effect was deemed
to be values above 50% and below –50%2. Figure 4 shows the
level of the matrix effects on the pesticides tested in the three
different brands of orange juice samples.
Figure 4 shows that OJ1 and OJ2 have limited matrix effects
for the majority of the pesticides that were tested in this study.
For sample OJ2, 74% of the 80 pesticides showed less than
20% ion suppression or ion enhancement in matrix as
compared to that in solvent.
For OJ2 only 5% of the pesticides showed a large matrix effect.
In this case quantification of samples against a solvent based
calibration curve can be used to avoid the requirement of
matrix-matched calibration curves.
For OJ3, however, a strong matrix effect was observed. Almost
80% of the pesticides showed significant suppression or
enhancement. These effect may potentially be attributed to the
presence of pulp in this sample. This observation is consistent
with the understanding that more complex matrices require
further sample cleanup.
79
74
70
69
66
63
1
200 ng/mL
100 ng/mL
50 ng/mL
20 ng/mL
10 ng/mL
5 ng/mL
Not detected
Number of pesticides
Conc
entr
atio
nFigure 2. Number of pesticides detected in orange juice.
0.00
20.00
40.00
60.00
80.00
100.00
120.00
140.00
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% Recovery of pesticides from orange juice
0.00
20.00
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80.00
100.00
120.00
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% Recovery of pesticides from orange juice
Figure 3. % Recovery of various pesticides in orange juice samples.
38%
59%
3%
OJ1
74%
21%
5%
OJ2
18%
3%
79%
OJ3
Figure 4. Observed matrix effects for the three orange juice samples.
An example for the requirement of additional cleanup is the
case of the pesticide rotenone. Rotenone was not detected
with dilute and shoot method owing to significant matrix effects
at this retention time. To determine whether sample cleanup
would rectify this, orange juice (OJ1) samples were subjected to
QuEChERS extraction. Figure 5 shows the MRM chromatograms
of rotenone spiked at 80 ng/mL in water and diluted 100 times
along with the chromatograms of OJ1 sample fortified at
10 ng/mL, prepared with QuEChERS and the dilute and shoot
method, respectively. As can be seen clearly, rotenone can
easily be detected following the QuEChERS extraction.
Using the dilute and shoot method, carbendazim was detected
in one of the purchased orange juice samples at low levels. The
incurred carbendazim residue concentration was calculated
using the standard addition method to ensure the accurate
quantification and account for any matrix effects. The calculated
concentration was determined to be 1.5 ppb (ng/mL) of
carbendazim. The identification of carbendazim was also
confirmed using the expected ion ratio, based on a standard.
Figure 6 shows MRM chromatograms of a carbendazim standard
in water, equivalent to 10 ng/mL along with the sample of
orange juice found to contain carbendazim at 1.5 ng/mL.
To assess the robustness of the method a study was
undertaken to monitor the effects of continuous injections of
diluted juices over 44 hours. Figure 7 shows the TrendPlot
graph of the repeatability of 155 injections of orange juice
spiked with carbendazim. No decrease in performance was
observed over the study.
CONCLUSION
The pesticide screening method with 2 MRM
transitions allows for both screening and confirmatory analysis in fruit juice using a simple
dilute and shoot protocol.
An incurred carbendazim residue was quickly and
easily detected and quantified well below the reporting level and confirmed using ion ratios.
The dilute and shoot method was shown provide excellent repeatability for more than 150 injections
of orange juice.
The combination of ultra performance LC with ultra
sensitive tandem mass spectrometer facilitates trace level detection of pesticides well below the
legislative limit.
The use of a multi-residue method with rapid and
simple sample preparation reduces time to result
and improves laboratory efficiency.
References
1. SANCO/10684/2009. Method validation and quality control procedures for pesticide residues analysis in food and feed. Document no. SANCO/3131/2007
2. Carmen F., M.J.Martinez-Bueno, Ana L., A.R. Fernandez-Alba. Pesticide residue analysis of fruit juices by LC-MS/MS direct injection. One year pilot survey.
Figure 5. MRM chromatograms of rotenone (A) spiked at 80 ng/mL in
water and diluted 100 times, (B) pre-spiked at 10 ng/mL in OJ1 and extracted with QuEChERS method and (C) spiked at 10 ng/mL in OJ
and prepared with dilute and shoot method.
A
B
C
A
B
Figure 6. MRM chromatograms of carbendazim (A) at 10 ppb in
water and (B) OJ1 sample with carbendazim residue at 1.5 ng/ML.
Figure 7. Robustness study of dilute and shoot method over
155 injection of orange juice spiked with carbendazim.