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Determination of Pesticide Residues in four Major Spices using UPLC-MS/MS and Optimized QuEChERS Sample Preparation Workflow

Ramesh Babu Natarajan1,2, Joby Thomas Kakkassery2*, Anaswara Raveendran1, Amrutha Ravi1 and Mohit Mohan1

1Quality Evaluation Laboratory, Spices Board, Palarivattom, Kochi, Kerala, India.

2Department of Chemistry, St. Thomas College (autonomous), Thrissur (University of Calicut), Kerala, India.

Corresponding Author E-mail: drjobythomask@gmail.com

DOI : http://dx.doi.org/10.13005/ojc/380325

Article Publishing History
Article Received on : 06-Apr-2022
Article Accepted on :
Article Published : 30 May 2022
Article Metrics
Article Review Details
Reviewed by: Dr. Sri Mursiti
Second Review by: Dr. Nityanand Singh Maurya
Final Approval by: Dr. S.A. Iqbal
ABSTRACT:

A high sensitivity method for analysis of pesticide residues in four spices, viz. cardamom, cumin, ginger and chillies, using specifically optimized ‘quick, easy, cheap, effective, rugged and safe’ (QuEChERS) sample preparation workflow and UPLC-MS/MS, was developed for 53 pesticides commonly used in the cultivation of these spices. Limits of quantification of 0.01 mg/Kg for all pesticides was achieved in the four spice matrices studied. Matrix effects were evaluated in each spice matrix and were found to be uniformly suppressive, with maximum matrix suppression observed in chillies and cumin, followed by cardamom and ginger, necessitating the use of matrix-matched calibration for each spice. The analytical method was validated as per European Union (EU) SANTE/12682/2019 guidelines. The method was then applied to 20 real samples of each spice collected from Indian markets, and regulatory compliance was evaluated against the maximum residue limits established by EU and Codex Alimentarius Commission.

KEYWORDS:

HPL;, Multi-Residue Methods; Mass Spectrometry; Method Validation

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Natarajan R. B, Kakkassery J. T, Raveendran A, Ravi A, Mohan M. Determination of Pesticide Residues in four Major Spices using UPLC-MS/MS and Optimized QuEChERS Sample Preparation Workflow. Orient J Chem 2022;38(3).


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Natarajan R. B, Kakkassery J. T, Raveendran A, Ravi A, Mohan M. Determination of Pesticide Residues in four Major Spices using UPLC-MS/MS and Optimized QuEChERS Sample Preparation Workflow. Orient J Chem 2022;38(3). Available from: https://bit.ly/3GtzQ2F


Introduction

The use of spices and condiments to add flavour, colour and aroma to food has always been an indispensable culinary requirement all over the world. This global demand is reflected in the world spice trade, which amounted to 2.88 billion US dollars in 20191, and is steadily increasing. In view of ubiquitous global culinary usage and the extent of world spice trade, food safety issues in spices becomes important. The presence of pesticide residues is now considered as one of the principal food safety issues and is internationally regulated in trade by means of stringent maximum residue limits (MRLs). Thus, the need for development of a sensitive, efficient and reliable pesticide residue analytical method in spices merits an important consideration.

Chromatographic techniques coupled to tandem mass spectrometry, typically GC-MS/MS and LC-MS/MS, have now become the de-facto tools for analysis of pesticide residues with the high sensitivity required to ensure compliance with current MRL regulations. Spices are generally considered as difficult matrices for high sensitivity pesticide residue analysis due to their complex chemical composition, which leads to a high amount of matrix coextractives that can potentially interfere with chromatographic separation and mass spectrometric detection and quantification2–5.

The quick, easy, cheap, effective, rugged and safe (QuEChERS) sample preparation technique6, pioneered in 2003, has since evolved into a versatile methodology for pesticide residue analysis in a variety of matrices. Originally this method was applied to fruits and vegetables and found considerable success in covering many matrices and classes of pesticides. Since then, several modifications have been introduced into the classical QuEChERS method which has extended its range of applicability and made it more efficient7–9.

An important issue to be considered in developing pesticide residue analysis methods in spices is their diverse nature. The Codex Committee on Spices and Culinary Herbs (CCSCH) classifies spices into 6 classes, viz. dried fruits and berries (e.g., chillies, black pepper), dried roots and rhizomes (e.g., turmeric, ginger), dried seeds (e.g., cumin, fennel), dried floral parts (e.g., mace, saffron), dried bark (e.g., cinnamon, cassia) and dried leaves (e.g., basil, oregano)10. The widely varying chemical characteristics of different classes of spices has placed constraints on the applicability of QuEChERS methodology, mainly due to the high amount of matrix coextractives present in spice extracts2. Thus, the study of matrix effects is an important consideration in high sensitivity residue analysis using chromatography and mass spectrometric techniques. Also, as the chemical nature of the matrix is different in each class of spices, specific optimizations are required before a sample preparation method for high sensitivity residue analysis can be applied to the different classes.

In LC-MS/MS, matrix effect arises in the electrospray ionisation source (ESI) and usually manifests in the form of signal suppression11. This poses hindrance to reliable identification and quantification of analytes at the sensitivity levels demanded by present regulatory requirements for pesticide residues. Accordingly, assessing and addressing matrix effects is an integral part of method development in pesticide residue analysis.

In this study, development and validation of an analytical method for 53 commonly used pesticides in four commercially important and extensively used spices belonging to different classes, viz. chillies (dried fruit, with high pigmentation), cardamom (dried fruit, with low pigmentation), cumin (dried seed) and ginger (dried rhizome), using UPLC-MS/MS, is documented. Chromatographic and mass spectrometric parameters for 53 pesticides were optimized for response, peak shape and separation. For all spices, a common acetonitrile extraction step based on buffered QuEChERS procedure was optimized. For cleanup of the extracts, different combination of QuEChERS reagents were applied to each spice and optimized to obtain best accuracy and precision in each case. Matrix effects posed by each of the spice matrices in UPLC-MS/MS analysis of residues were assessed. Method validation was performed as per European Union SANTE/12682/2019 guidelines12.  The method was then applied to 20 real samples of each spice collected from local markets, and regulatory compliance of these samples were evaluated against the maximum residue limits established by European Union and Codex Alimentarius Commission.

Materials and Methods

Chemicals and reference standards

LC-MS/MS grade Acetonitrile and methanol were obtained from Biosolv, USA. Analytical grade Ammonium formate, formic acid, anhydrous magnesium sulphate (MgSO4), sodium chloride (NaCl), sodium citrate tribasic dihydrate (C6H5Na3O7.2H2O) and sodium citrate dibasic sesquihydrate (C6H5Na2O7.1.5H2O) were obtained from Merck, India.  Graphitized carbon black (GCB), primary secondary amine (PSA) and C-18 end-capped bulk sorbent were purchased from Agilent Technologies, USA. Certified reference materials of 53 pesticides, with purity > 95% for all compounds, were procured from Dr. Ehrenstorfer GmbH (Germany). Individual pesticide standard stock solutions of 1000 mg/L of 30 compounds and the intermediate mixed standard solution at 10 mg/L were prepared in acetonitrile and stored at -20°C until analysis. Working solutions of the mixed standard were prepared daily by appropriate serial dilutions.

Instrumentation

For sample preparation, vortex mixer and centrifuges used were from Remi, India. Low volume concentrator was from PCI, India. Pesticide residue analysis was performed using a Waters Xevo TQS Micro UPLC-MS/MS system, USA. For concentration of the final extracts for reconstitution, a low-volume concentration workstation from PCI Analytics, India was used.

Optimization of instrument conditions

Chromatographic separations in UPLC were performed over a C-18 column (Waters XBridge® BEH 2.5mm, 2.1x100mm). Four combinations of UPLC mobile phases were assessed, viz. acetonitrile – water system with and without buffer, and methanol – water system with and without buffer. The buffer system used was 5 mM ammonium formate / 0.1% formic acid. Gradients were optimized to obtain good separation and peak shapes. The chromatographic conditions and operational parameters of the mass spectrometer are summarized in Table 1. Mass spectrometric analysis was done using electrospray ionization (ESI) and multiple reaction monitoring (MRM) with two transitions per compound. The compound-dependant parameters for the 53 pesticides used in the study are given in Table 2.

Table 1: Optimized chromatography and mass spectrometry method parameters.

Parameters

 

UPLC

 

Column

Waters XBridge® BEH C-18 2.5mm, 2.1x100mm

Mobile Phase

A: Water with 5mM ammonium formate and 0.1% formic acid

B: methanol with 5mM ammonium formate and 0.1% formic acid

Flow 0.5 ml/min

Gradient: Initial A:B 98:2, 5 min A:B 50:50 curve 6, 7 min A:B 40:60 curve 6, 11 min A:b 25:75 curve 6, 14 min A:b 1:99 curve 6, 17 min A:B 98:2 curve 6. Total runtime 21 min.

 

MS/MS

 

Capillary voltage

0.6 kV

Cone voltage

40

Desolvation temp.

600°C

Source gas

1100 L/hr

Cone gas

50 L/hr

Table 2: Optimized retention times (TR) and MS/MS parameters for 53 pesticides.

Pesticide

TR

(min)

Quantifying transition (m/z)

Qualifying transition (m/z)

Collision Energy (V)

Cone Voltage (V)

Acephate

12.62

183.9/142.95

183.9/49

20/18

10

Acetamiprid

5.09

223/126

223/56.1

15/20

30

Amectoctardin

8.53

276.16/244.07

276.16/168.06

24/14

16

Azoxystrobin

8.6

404/329

404/372

30/25

25

Bifenazate

9.55

301.1/198

301.1/170

20/10

25

Boscalid

8.92

342.9/139.9

342.9/307

20/45

25

Buprofezin

12.45

306.1/201

306.1/57.4

25/10

10

Carbaryl

6.88

202.1/145.1

202.1/127.1

25/10

25

Carbofuran

6.48

222.11/165.1

222.11/123

20/10

5

Chlorpyrifos

13.72

349.9/97

349.9/198

16/16

20

Cyantraniliprole

7.13

475.2/286

475.2/444

16/16

20

Cycloxydim

11.95

326/180

326/280

22/16

34

Cyprodinil

9.58

226/93

226/108

35/25

5

Diazinon

10.8

305.1/169

305.1/96.9

35/22

20

Dimethenamid

8.54

276/244

276/168

26/14

17

Emamectin benzoate

14.48

886.6/158

886.6/126

30/35

20

Ethion

13.59

385/199

385/142.9

25/10

30

Fenarimol

9.84

331/81

331/268

30/25

20

Fenbuconazole

10.35

337/70.1

337/125

30/20

15

Fenhexamid

9.68

301.96/55.18

301.96/97.11

35/25

35

Fenpyroximat

14.78

422.2/366.1

422.2/138.1

30/20

5

Flupicolide

8.98

383/172.999

383/109.06

66/20

40

Flutriafol

7.57

302.1/70.2

302.1/123.1

20/25

15

Fluxapyroxad

9.2

382.2/362

382.2/342

20/10

20

Hexaconazole

11.33

314/70.1

314/159

20/25

15

Imidacloprid

4.69

256.1/209.1

256.1/175.1

20/15

25

Iprobenfos

10.37

289/91

289/205

20/10

9

Malathion

9.08

331/127

331/99

20/15

10

Mandipropamid

9.04

411.8/328.1

411.8/125

35/15

35

Mehtiocarb

8.71

226/169

226/121

20/10

25

Metalaxyl

7.61

280.1/220.1

280.1/192.1

20/15

10

Methamidophos

0.6

142/93.9

142/124.9

13/13

15

Methoxyfenozide

9.2

369.2/149.1

369.2/313.23

15/10

15/5

Penthiopyrad

10.93

360.1/177.1

360.1/276

47/21

30

Phenthoate

10.52

321/79.1

321/135

40/20

9

Phosalone

11.42

367.9/181.9

367.9/110.9

42/14

12

Pirimiphos methyl

10.92

306.1/108.1

306.1/164.1

32/22

25

Procloraz

11.02

375.84/307.92

375.84/70.12

24/16

10

Profenofos

12.54

372.9/302.6

372.9/127.9

40/20

25

Pyraclostrobin

11.33

388.1/193.9

388.1/163

25/12

5

Quinalphos

10.37

299/96.9

299/162.9

30/24

15

Quinoxyfen

13.57

308/197

308/161.9

35/30

15

Spinosad A

11.68

732.6/142

732.6/98.1

35/30

35

Spinosad D

12.44

746.52/142

746.52/98.1

35/31

40

Spirodiclofen

14.76

411.14/71.16

411.14/313.1

15/10

35

Spirotetramat

9.65

374/330

374/302

30/15

20

Tebuconazole

10.85

308/70.1

308/125

20/35

10

Thiacloprid

5.54

253/126

253/90.1

35/20

40

Thiodicarb

7.17

355.08/88.1

355.08/108.1

16

17

Thiophanate

7.88

371/151

371/93.1

50/22

28

Triadimefon

9.17

294.1/69.3

294.1/197.2

20/15

25

Triazophos

9.53

314.1/161.9

314.1/118.9

35/18

22

Trifloxystrobin

12.11

409/186

409/145

40/16

10

 

Selection of samples

For study of matrix effects and method validation, organically cultivated spice samples were selected after screening to confirm that they were free from the pesticides under study. For evaluation of real samples, 20 market samples each for cardamom, cumin, ginger and chillies were collected from local markets in Kochi, Kerala, India.

Sample preparation and optimization

Homogenization of the four spices were performed so as to simulate their typical culinary usage. Cardamom and ginger samples were crushed thoroughly using a kitchen blender before analysis. Cumin and chillies were ground to fine powder and sieved through ASTM 20 (850 mm) mesh before analysis.

The optimized extraction step was same for all four spices, in which 2 g of each spice was soaked in 8 ml water for 30 minutes, and then 10 ml acetonitrile was added, followed by 4 g MgSO4, 1 g each of sodium chloride and sodium citrate tribasic dihydrate, and 0.5 g of sodium citrate dibasic sesquihydrate. The mixture was then vortexed for 30 seconds and centrifuged at 5000 rpm for 5 minutes.

Owing to the diverse chemical nature of the four spice matrices under study, the cleanup step had to be optimized separately for each spice matrix. From the extract 2ml was taken for cleanup, and the optimized combination of chemicals, viz. MgSO4, PSA, C18 sorbent and GCB were added into each spice as detailed in Table 3. The mixture was then vortexed for 30 seconds and centrifuged at 10,000 rpm for 5 minutes. From the cleaned extract, 2 ml was evaporated to dryness and reconstituted with 1 ml methanol, filtered through 0.2-micron nylon 6,6 membrane filter, and 10 ml was injected into UPLC-MS/MS.

Method performance evaluation

Method performance was assessed as per European Union SANTE/12682/2019 guideline12 by determining linearity, matrix effect, limits of quantification (LOQ), accuracy and precision. Linearity was assessed based on the correlation coefficient (R2) of calibration curves with five calibration levels from 0.005 to 0.075 mg/L. Accuracy was assessed using recovery experiments with spike levels of 0.01 and 0.05 mg/Kg. Intra-day, intra-laboratory precision (repeatability) was calculated as relative standard deviation (RSDr) at two spike levels of 0.01 and 0.05 mg/Kg for all four spices, with 5 replicates for each matrix (same instrument, same analyst, same day). Inter-day precision (reproducibility) was calculated as the relative standard deviation (RSDR) at two spike levels of 0.01 and 0.05 mg/Kg for each spice matrix, with each fortification level analysed in triplicate on three non-consecutive days (n = 9). LOQ was taken as the minimum concentration that could be quantified with accuracy and precision in compliance with the validation requirements. 

Evaluation of Matrix effects

Matrix-matched calibration curves for 53 pesticides were setup using post-extraction spikes in blank matrix extracts of cardamom, chilli, ginger and cumin at five concentration levels, viz. 0.005, 0.01, 0.025, 0.05, 0.075 mg/L. Solvent-only (methanol) calibration curves at the same concentrations were also prepared for each pesticide. Matrix effect observed for each spice matrix – pesticide combination was then assessed by comparing the slope of the matrix-matched calibration curve with that of the solvent-only calibration curve.

Results and Discussion

Optimization of UPLC-MS/MS Analysis

Of the four combinations of mobile phase studied, methanol-water composition was in general better than acetonitrile-water composition in obtaining good peak shape and resolution. It was also observed that the use of buffers improved the response and peak shapes in general. Thus, methanol-water mobile phase containing ammonium formate / formic acid (5 mM / 0.1%) buffer was finalized as the mobile phase (Table 1). After optimization, the UPLC chromatogram afforded good separation of the analytes under consideration.

In ESI / MRM mode, for each compound analysed, the mass spectrometer selects a parent ion produced from the analyte molecule and then generates daughter ions from this parent ion by collision induced dissociation with nitrogen inside the collision cell, culminating in a highly specific detection process14. Several parameters influence this ionization process, some generic and other specific to each compound being analysed. These parameters were optimized to obtain maximum response for each compound being analysed. The finalized generic mass spectrometric conditions are summarized in Table 1, and the compound specific parameters are shown in Table 2. These parameters were optimized to minimize interference from co-extractives and maximize response for the individual compounds and spice matrices.

Optimization of QuEChERS extraction and cleanup procedure

In the original QuEChERS procedure validated for fruits and vegetables6, the first step involved extraction of samples directly into acetonitrile in presence of 4g MgSO4 and 1g NaCl. However, spices are dry commodities with moisture content in the range of 8-10%, which is much less than the moisture content in fruits and vegetables. So in the present optimization of the extraction process for the four spices, two additional parameters were studied, viz addition of water to the matrix and soaking time. For extraction, the proportion of sample weight (g) to acetonitrile volume (ml) was maintained optimally at 1:5, as it was noted that decreasing the extraction volume below this ratio resulted in inadequate homogenization during the first vortex mixing step, and above this ratio, there was a dilution of analytes in the extract which would detract from the method sensitivity.

It was established initially that without soaking of the matrix, accuracy and precision within acceptable ranges of method validation cannot be obtained for pesticides at trace levels. This is because saturating the dry spice matrices with water improves the penetration of the extraction solvent and facilitates better partitioning of the residues in the matrix to the solvent. Starting with a sample weight of 2 g and 30-minute soaking time, the sample: water ratios (by weight) of 1:2, 1:4, 1:6 and 1:8 were studied. It was seen that at 1:2 ratio, the recoveries of all the compounds were between 32-61%. At 1:4 ratio, the recovery values showed significant increase, to the range of 50-77%, and further increase in the sample: water ratio did not increase the recoveries significantly. These recovery values were obtained without the cleanup step, which was optimized separately.

Increasing the sample weight while keeping the sample: water ratio at 1:4 did not increase recovery significantly but was seen to affect the repeatability. For 2 g sample weight with addition of 8 ml water with soak time of 30 min, overall intra-day repeatability, RSDr (n=5) was between 8.3 – 13.5% for all compounds, but for 5 g sample weight, this was in the range 14 – 19.6%. This is probably because spices contain significant amounts of crude fibre which makes perfect homogenization difficult, and increasing sample weight consequently would decrease the precision. Increasing soak time beyond 30 minutes did not affect recovery or repeatability to any considerable extent. Thus, sample weight of 2 g, with addition of 8 ml water and a soak time of 30 minutes, were found to be optimal for all four spices. The acetonitrile volume used was fixed at 10 ml itself maintaining the sample-solvent ratio at 1:5.

Addition of sodium citrate salts during the extraction step was considered to enhance the recovery of pH sensitive pesticides. Thus, before optimizing the cleanup step, the effect of buffer salts in the extraction efficiency in the four spices was studied. Using the optimized extraction compositions, recovery studies with and without citrate salts showed that for some pesticides, recovery increased considerably in the presence of citrate salts. For diazinon, carbaryl, chlorpyrifos and malathion, recovery values with addition of citrate salts increased by 13, 19, 17 and 24% in cardamom, 17, 18, 14 and 20% in cumin, 18, 25, 13 and 13% in ginger and 15, 12, 10 and 13% in chillies. For fenhexamid, recovery value increased by 19% in chillies. In all other cases, the variation in recovery values was minor, within ±8% for all compounds in all spice matrices. However, it was deemed beneficial to include sodium citrate salts in the extraction step to improve overall method performance.

To optimize the cleanup step, four QuEChERS reagents were considered, viz. MgSO4, PSA, C-18 end capped sorbent and GCB. MgSO4 is used to remove excess water from the extract and thus facilitate recovery of nonpolar residues. PSA contains primary and secondary amino groups that remove acidic interferences from the extracts. GCB acts by reducing pigments from the extracts but are also known to affect recoveries of planar pesticides. C-18 sorbent is used to remove non-polar interferences.

Spices typically have relatively high amounts of non-polar volatile oil content, of varying chemical compositions, in addition to other active chemical compounds. In cardamom the volatile oil content is around 8 – 9%, in ginger 0.7 – 4% and in cumin 2.7 – 4.3%. Chillies have capsaicinoid content, responsible for their pungency, ranging from 2000 – 5000 mg/Kg. The colour in chillies, arising carotenoid content, range from 0.1 – 0.3%, or 1000 – 3000 mg/Kg15, 16. All these factors contribute to matrix co-extractives which can potentially interfere with analytical performance. Also, as soaking spice samples in water was seen to be very important in spices to obtain good recovery and precision, a natural consequence is the increased water content in the extract which has to be addressed to manage the recovery of non-polar pesticides.

In view of these factors, four combinations of cleanup chemicals were studied: (A) 300 mg MgSO4 + 75 mg PSA + 50 mg C18, (B) 300 mg MgSO4 + 75 mg PSA + 50 mg C18 + 20 mg GCB, (C) 300 mg MgSO4 + 75 mg PSA + 75 mg C18 and (D) 300 mg MgSO4 + 75 mg PSA + 75 mg C18 + 20 mg GCB. Each combination (A) to (D) were applied on 5 samples of each of the four spices spiked at 0.01 mg/kg, and recoveries were assessed. Fig. 1 shows the overall recoveries for five representative compounds, viz. imidacloprid, ethion, chlorpyrifos, quinalphos and spirodclofen, obtained for the four cleanup combinations in the four spices studied.

Figure 1: Optimization of cleanup procedures in four spices based on average recovery for spike level 0.01 mg/kg (n=5).

Click here to View figure

In all four spices, cleanup increased recoveries of the studied compounds considerably. Using cleanup combination (C), average recoveries were obtained in the range 83.7 – 97.8 for cardamom. Using cleanup combination (D), average recoveries in the range 98.7 – 102.7% were obtained for cumin. Using cleanup combination (B), average recoveries in the range 87.7 – 106.8% were obtained for ginger, and in the range 93.8 – 104.6% were obtained for chillies. As these recovery values were respectively the highest for each spice and were in accordance with acceptable validation criteria, the respective cleanup combinations were taken as optimal for each spice. Thus, the optimized QuEChERS extraction and cleanup workflow, for the spices cardamom, cumin, ginger and chillies, are summarized in Table 3.

Table 3: Optimized extraction and QuEChERS cleanup scheme for cardamom, cumin, ginger and chillies.

Process

Cardamom

Cumin

Ginger

Chillies

Extraction

 

 

 

 

Sample weight (g)

2

2

2

2

Add water (ml) / soak time (min)

8/30

8/30

8/30

8/30

Add acetonitrile (ml)

10

10

10

10

Add MgSO4 anh. (g)

4

4

4

4

Add NaCl (g)

1

1

1

1

Add Sodium citrate tribasic dihydrate (g)

1

1

1

1

Add sodium citrate dibasic sesquihydrate (g)

1

1

1

1

 

Vortexed 30 sec, centrifuged 5000 rpm 5 min.

Cleanup

 

 

 

 

Volume taken for cleanup (ml)

2

2

2

2

Add PSA (mg)

75

75

75

75

Add C18 sorbent (mg)

75

75

50

50

Add GCB (mg)

0

20

20

20

Add MgSO4 anh (mg)

300

300

300

300

 

Vortexed 30 sec, centrifuged 10000 rpm 5 min.

Concentration and reconstitution

 

 

 

 

Cleaned extract evaporated to dryness (ml)

2

2

2

2

Reconstituted in 1:1 MeOH:H2O (ml)

1

2

2

2

 

Matrix effects

The extent of matrix coextractives obtained using the optimized extraction and cleanup steps was studied gravimetrically. When compared to the matrix load in the extract, the optimized cleanup step reduced the matrix load (mg/ml) to a considerable extent: 53.3% in cardamom, 51% in cumin, 50% in ginger and 56.7% in chillies.  The results are shown in Fig. 2.

Figure 2: Effect of optimized cleanup on matrix co-extractives as determined by gravimetric analysis.

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In LC-MS/MS, matrix effect (ME) arises in the electrospray ionization (ESI) source and usually manifests in the form of signal suppression13. In calibration curves, signal suppression manifests as lower slopes in matrix matched calibration curves as compared to solvent-only calibration curves. Matrix matched calibration curves were set up using extracts obtained from blank samples of cardamom, cumin, ginger and chillies using the optimized extraction method. Table 4 shows the regression equations and correlation coefficients obtained for 53 compounds studied in each of the four spices.

MEs were calculated using the following equation:

ME between 80-120% are considered negligible, or soft ME, and does not require matrix matched calibration for reliable quantitative results. ME between 50-80% (suppression) and 120-150% (enhancement) are considered medium. ME lower than 50% (suppression) and higher than 150% (enhancement) are considered strong17,18.

The ME posed by the spice matrices were uniformly suppressive and ranged from medium to strong. In cardamom, the ME ranged from 25-80%, in cumin between 10-46%, in ginger between 35-89% and in chillies between 11-67%. Thus, the highest suppression was observed in cumin and chillies. Only 4 pesticides showed matrix suppression in the low ranges (ME > 80%), viz. fenhexamid (88%), fenpyroximat (89%) ad flutirafol (87%) in ginger matrix and pyroaclostrobin (80%) in cardamom matrix.  When matrix suppression is low, i.e., ME is between 80 – 100%, results estimated using solvent-only calibration curves will not have large errors. However, with ME < 80%, using solvent-only calibration curves will lead to considerable underestimation of results. As the ME values were > 80% only in 1.8% cases in all the spice – pesticide combinations studied, it was concluded that matrix matched calibration could not be avoided in all four spices so as to obtain reliable results. The matrix effects observed in 53 pesticides analysed in the four spices studied are shown in Fig. 3.

Figure 3: Matrix effects (%) of 53 pesticides investigated in four spices.

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Table 4: Regression equations and correlation coefficient values for pesticides analyzed by LC-MS/MS in solvent (methanol) and in cardamom, cumin, ginger and chillies.

Pesticide

Regression equation, R2 value

Solvent

Cardamom

Cumin

Ginger

Chillies

Acephate

874x – 233, 0.9952

454x – 205, 0.9932

192x – 184, 0.9922

507x – 182, 0.9902

297x – 238, 0.9862

Acetamiprid

19728x + 24531, 0.9952

13218x + 21588, 0.9912

1973x + 19380, 0.9872

13218x + 19134, 0.9862

6116x + 25022, 0.9912

Amectoctardin

22375x – 353, 0.9981

9845x – 311, 0.9921

5146x – 279, 0.9931

14320x – 275, 0.9911

9397x – 360, 0.9891

Azoxystroin

12353x + 1181, 0.9941

7165x + 1040, 0.9881

4200x + 933, 0.9881

7659x + 922, 0.9921

3459x + 1205, 0.9871

Bifenazate

23099x – 593, 0.9896

15476x – 522, 0.9866

7392x – 468, 0.9806

12704x – 463, 0.9876

15476x – 605, 0.9826

Boscalid

3380x – 35, 0.9933

2602x – 31, 0.9843

1048x – 28, 0.9923

1521x – 27, 0.9873

777x – 36, 0.9893

Buprofezin

49527x – 663, 0.9951

33183x – 583, 0.9901

13868x – 524, 0.9901

17335x – 517, 0.9931

17830x – 676, 0.9881

Carbaryl

1728x + 34564, 0.9914

933x + 30416, 0.9924

432x + 27305, 0.9924

1158x + 26960, 0.9924

639x + 35255, 0.9894

Carbofuran

37168x + 1767, 0.9951

21558x + 1555, 0.9891

13009x + 1396, 0.9941

27876x + 1378, 0.9941

12266x + 1803, 0.9871

Chlorpyrifos

1789x + 10878, 0.9819

876x + 9573, 0.9669

787x + 8594, 0.9629

1180x + 8485, 0.9699

751x + 11096, 0.9659

Cyantraniliprole

9938x – 569, 0.9988

3677x – 501, 0.9918

2783x – 450, 0.9908

6361x – 444, 0.9898

1590x – 580, 0.9958

Cycloxydim

8267x – 156, 0.9952

3803x – 137, 0.9882

1653x – 123, 0.9872

4960x – 122, 0.9872

1819x – 159, 0.9912

Cyprodinil

236x + 11621, 0.9077

130x + 10226, 0.9047

52x + 9181, 0.9047

139x + 9064, 0.8987

57x + 11853, 0.9997

Diazinon

21039x – 678, 0.9954

11151x – 597, 0.9884

5049x – 536, 0.9874

10309x – 529, 0.9864

4839x – 692, 0.9924

Dimethenamid

24025x – 365, 0.9979

14895x – 321, 0.9909

6006x – 288, 0.9909

12733x – 285, 0.9939

3844x – 372, 0.9939

Emamectin benzoate

11650x – 770, 0.9953

6291x – 678, 0.9873

3961x – 608, 0.9893

8388x – 601, 0.9873

1980x – 785, 0.9923

Ethion

8300x + 19149, 0.9962

5312x + 16851, 0.9932

3652x + 15127, 0.9912

5561x + 14936, 0.9882

913x + 19532, 0.9882

Fenarimol

856x + 5417, 0.9905

368x + 4767, 0.9865

300x + 4279, 0.9875

531x + 4225, 0.9815

385x + 5525, 0.9835

Fenbuconazole

17476x + 13519, 0.9911

7864x + 11897, 0.9821

5592x + 10680, 0.9831

11534x + 10545, 0.9831

5592x + 13790, 0.9841

Fenhexamid

8489x + 7107, 0.9918

4584x + 6254, 0.9848

2207x + 5615, 0.9858

7471x + 5544, 0.9878

1358x + 7249, 0.9868

Fenpyroximat

10669x + 28873, 0.9993

6722x + 25408, 0.9953

2667x + 22809, 0.9923

9496x + 22521, 0.9963

1280x + 29450, 0.9913

Flupicolide

14041x + 5096, 0.9953

10952x + 4485, 0.9903

3370x + 4026, 0.9923

10530x + 3975, 0.9913

3229x + 5198, 0.9903

Flutriafol

30923x + 23741, 0.9974

19791x + 20892, 0.9904

8040x + 18755, 0.9904

26903x + 18518, 0.9934

7422x + 24215, 0.9944

Fluxapyroxad

18056x + 7566, 0.9939

10111x + 6658, 0.9919

4153x + 5977, 0.9919

13361x + 5901, 0.9919

3070x + 7717, 0.9919

Hexaconazole

23678x – 789, 0.9934

13023x – 694, 0.9924

4262x – 623, 0.9884

17048x – 615, 0.9904

8051x – 805, 0.9884

Imidacloprid

15187x – 266, 0.9964

10175x – 234, 0.9944

3341x – 210, 0.9884

9416x – 207, 0.9884

5467x – 271, 0.9874

Iprobenfos

44698x + 194, 0.9966

24584x + 171, 0.9896

14303x + 153, 0.9896

28607x + 151, 0.9906

13856x + 198, 0.9896

Malathion

14856x + 1308, 0.9839

10102x + 1151, 0.9769

6091x + 1033, 0.9819

9656x + 1020, 0.9779

5348x + 1334, 0.9889

Mandipropamid

9253x + 11353, 0.9902

5644x + 9990, 0.9862

3516x + 8969, 0.9852

5089x + 8855, 0.9842

1481x + 11580, 0.9872

Mehtiocarb

4483x + 33510, 0.9167

2331x + 29489, 0.9087

1435x + 26473, 0.9147

2869x + 26138, 0.9087

1524x + 34180, 0.9847

Metalaxyl

18905x – 810, 0.9960

8318x – 713, 0.993

8318x – 640, 0.991

10209x – 632, 0.9870

6239x – 826, 0.9870

Methamidophos

198x + 14601, 0.9639

133x + 12849, 0.9629

46x + 11535, 0.9569

109x + 11389, 0.9609

73x + 14893, 0.9869

Methoxyfenozide

2731x + 4244, 0.9282

1803x + 3734, 0.9232

546x + 3353, 0.9202

1748x + 3310, 0.9872

1038x + 4329, 0.9822

Penthiopyrad

8586x + 3839, 0.9966

5409x + 3379, 0.9936

1631x + 3033, 0.9886

5238x + 2995, 0.9956

2662x + 3916, 0.9926

Phenthoate

9306x + 76635, 0.9586

5956x + 67439, 0.9576

2419x + 60542, 0.9956

4839x + 59776, 0.9896

2140x + 78168, 0.9566

Phosalone

3230x + 146, 0.9913

2003x + 128, 0.9893

1421x + 115, 0.9833

2519x + 114, 0.9853

807x + 149, 0.9843

Pirimiphos methyl

23530x – 193, 0.9955

13883x – 170, 0.9925

2588x – 152, 0.9905

17412x – 150, 0.9875

6118x – 197, 0.9865

Procloraz

7702x + 6803, 0.9918

4467x + 5987, 0.9878

1848x + 5374, 0.9828

5314x + 5306, 0.9898

1617x + 6939, 0.9888

Profenofos

1226x + 1228, 0.9977

883x + 1081, 0.9907

282x + 970, 0.9947

748x + 958, 0.9887

417x + 1253, 0.9917

Pyraclostrobin

13534x + 45783, 0.9978

10827x + 40289, 0.9938

5684x + 36169, 0.9968

8662x + 35711, 0.9938

2707x + 46699, 0.9908

Quinalphos

13845x – 724, 0.9981

8861x – 637, 0.9951

6369x – 572, 0.9961

9138x – 565, 0.9971

2354x – 738, 0.9921

Quinoxyfen

4550x – 652, 0.9964

1137x – 574, 0.9954

1592x – 515, 0.9924

3367x – 509, 0.9934

2002x – 665, 0.9884

Spinosad A

34698x – 469, 0.9985

12144x – 412, 0.9915

7981x – 370, 0.9935

22207x – 366, 0.9905

14920x – 478, 0.9935

Spinosad D

6640x – 6706, 0.9979

4249x – 5901, 0.9929

1593x – 5298, 0.9899

4382x – 5231, 0.9959

2722x – 6840, 0.9949

Spirodiclofen

3083x + 7175, 0.9915

2035x + 6314, 0.9905

1356x + 5668, 0.9885

2065x + 5597, 0.9855

1079x + 7319, 0.9835

Spirotetramat

10950x + 7564, 0.9973

7008x + 6657, 0.9943

4928x + 5976, 0.9963

7008x + 5900, 0.9953

3723x + 7716, 0.9893

Tebuconazole

6278x + 31018, 0.9982

2888x + 27296, 0.9902

1632x + 24504, 0.9962

4144x + 24194, 0.9932

3390x + 31638, 0.9902

Thiacloprid

45901x – 160, 0.9972

29836x – 141, 0.9942

12393x – 126, 0.9962

36262x – 125, 0.9892

18820x – 163, 0.9952

Thiodicarb

32888x – 3993, 0.9988

14471x – 3514, 0.9918

9538x – 3155, 0.9898

23351x – 3115, 0.9978

7564x – 4073, 0.9928

Thiophanate

26577x + 15966, 0.997

17807x + 14050, 0.993

10897x + 12613, 0.988

11960x + 12454, 0.991

5050x + 16286, 0.992

Triadimefon

11822x + 6412, 0.9933

6502x + 5642, 0.9913

4138x + 5065, 0.9873

7566x + 5001, 0.9873

3783x + 6540, 0.9843

Triazophos

51525x – 378, 0.9961

22671x – 333, 0.9891

12366x – 299, 0.9951

32461x – 295, 0.9981

13396x – 386, 0.9931

Trifloxystrobin

17890x + 36481, 0.9988

13239x + 32103, 0.9918

4830x + 28820, 0.9908

12702x + 28455, 0.9938

5367x + 37211, 0.9978

Method validation

Validation was performed using the optimized sample preparation and instrument parameters as detailed in the respective sections. Good linearity in response was obtained for all 53 compounds with correlation coefficient r2 ≥ 0.99 in solvent and ≥ 0.98 in all four spice matrices, in the calibration range 0.005 to 0.075 mg/L as shown in Table 4. At spiking levels of 0.01 and 0.05 mg/Kg, average recovery values for all compounds obtained were in the range 79 – 114% for cardamom, 83.3 – 102.7% for cumin, 82 – 107.2% for ginger and 90.3-103.6% for chillies. 

Intraday precision RSDr values at the spike levels 0.01 and 0.05 mg/Kg (n=5 per level) were in the ranges 10 – 13.2% in cardamom, 6 – 11.3% in cumin, 9.1 – 16.3% in ginger and 4.1 – 7.8% in chillies. The inter-day precision (RSDR) at the same spike levels (n=9 per level) were in the ranges 13.6-17% in cardamom, 9.1-14% in cumin, 14.3-18.7% in ginger and 6.1-9.3% in chillies. The relatively higher RSD values in cardamom and ginger are likely to be due to the higher crude fibre content in these spices, which would lead to a reduction in homogeneity. All the accuracy and precision values were within the acceptability limits of validation parameters, i.e., 70-120% for accuracy and RSD<20% for precision. An LOQ at 0.01 mg/Kg, which was the lowest level studied which gave acceptable accuracy and precision values, was fixed for 53 compounds in all spice matrices. This LOQ is sufficient to address international regulatory requirements like Codex and European Union maximum residue limits (MRLs)19,20.

Application of the method to of real samples

The 20 market samples of each spice analysed using the optimized method showed the presence of residues of typical analytes, namely acetamiprid (0.01 – 0.04 mg/Kg) and quinalphos (0.01 – 0.03 mg/Kg) in cardamom; imidacloprid (0.01 mg/Kg) and profenofos (0.01–0.04 mg/Kg) in cumin; ethion (0.01 mg/Kg), hexaconazole (0.01 mg/Kg) and profenofos (0.01 – 0.04 mg/Kg) in chillies and metalaxyl (0.01 mg/Kg) in ginger. The incidence of residues was highest in cardamom (51%), followed by chillies (33%), cumin (28%) and ginger (8%). Although all the detected pesticides had concentrations less than the extant maximum residue limits of Codex and EU, the results highlight the need of effective residue management and monitoring plans for agrochemicals in these spices.

Conclusion

An efficient and sensitive QuEChERS-based extraction and cleanup workflow was optimized for pesticide residue analysis of four spices belonging to different classes, viz. cardamom (dried fruit, low colour), cumin (dried seeds), ginger (dried rhizome) and chilli (dried fruit, high colour), for 53 commonly used pesticides in the cultivation of these spices, using UPLC- MS/MS. The method used the same buffered acetonitrile extraction procedure for all spices, and cleanup step was individually optimized for each spice. The method was successfully validated as per EU SANTE/12682/2019 guidelines, and an LOQ of 0.01 mg/Kg could be achieved for all pesticides in all four spices. High values of matrix effects observed in all four spices showed that matrix matched calibration is essential for obtaining reliable results. The optimized method can be effectively used in routine analysis of spices in commercial laboratories for assessing compliance with regulatory requirements. 

Acknowledgement

The authors gratefully acknowledge the use of instrumentation facilities at Quality Evaluation Laboratory (Kochi, Kerala), Spices Board, Ministry of Commerce, Government of India.

Conflict of Interest

The authors declare that there is no conflict of interest.

Funding Sources

There are no funding source.

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