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Assessment and Method Validation of Chlormequat Chloride (CCC) in Food (Fruit, Vegetable & Grain) by Liquid Chromatography Mass Spectrometry By Virendra Vora*, Mukesh Kumar Raikwar and Vikas Bhardvaj January 2012 The authors are Specialists at the Department of Pesticide Residue, Reliable Analytical Laboratories Pvt Ltd, in Bhiwandi, Thane, India *Corresponding Author See also: «Study of Contamination Level of Pesticide Residues in Grapes ( Vitis vinifera) in Maharashtra» Abstract A fast, sensitive and specific method for routine determination of Chlormequat chloride residue from a variety of different food matrices was developed. It requires no cleaning procedure and very easy to extract without any interference in liquid chromatography (electrospray ionization) tandem mass spectrometry with using a stable isotopically labeled internal standard. Mass spectral acquisition was done in selected reaction monitoring mode (MRM), selecting the transitions from both the 35 Cl and the 37 Cl isotope of chlormequat. Recoveries after extraction was determined with radio-labeled chlormequat and averaged over the spiking range (0.010 – 0.050 mg/kg) in four different commodities were within 83-96%, with a coefficient of variation batter than 2%. The method can be applied to grape, juice concentrates, vegetables, fruits and cereal products, with typical limits of detection for chlormequat estimated at 0.001 – 0.002 mg/kg. A survey of different food commodities especially of grape revealed that chlormequat was detectable at very low level and it is also a very stable compound in many of the food samples analyzed, with the highest concentration recorded in grape (0.328 mg/kg, 100% contamination) and okra (1.0 mg/kg) purchased from Maharashtra region. Measurements were also conducted on two LC – MS instruments, also between international and national labs and demonstrate the versatility and robustness of the method and its applicability to instruments. Introduction Chlormequat chloride (IUPAC name 2-chloroethyltrimethyl ammonium chloride) is a highly stable gibberellins biosynthesis inhibitor used as a plant growth regulator in many fruits and vegetables. Chlormequat chloride (CCC) inhibits cell elongation, hence shortening and strengthening stems and producing sturdier plants. It’s main use in agriculture is on cereal crops, such as wheat, barley and oats, to increase resistance to lodging by limiting stem growth and to improve yields. However, it has also been widely used to improve fruit setting, prevent premature fruit drop, increase fruit size and reduce the need for tree pruning in top fruit. Due to the CCC properties with the relatively strongly bound Cl- (Blinn, 1967) suggested that CCC residue could be accumulated in plant organs as well as the products. However, other workers have subsequently reported that CCC is completely metabolised since CCC residues could not be detected in animal tissues (Dekhuijzen et al., 1973; Dekhuijzen et al., 1974). To protect animals and humans from consumption of CCC in food, the European Community has set up the maximum CCC residual limits 0.05 for Fruits and Grains. Several methods have been described for the determination of chlormequat. The first methods developed were nonspecific spectrometric (Moony et al., 1967) and thin-layer chromatographic Page 1 of 6 Assessment and Method Validation of Chlormequat Chloride in Food by Liquid Chromat ... 2/24/2012 http://www.eco-web.com/edi/03336-02.html

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Assessment and Method Validation of Chlormequat Chloride (CCC) in Food (Fruit, Vegetable & Grain) by

Liquid Chromatography Mass Spectrometry

By Virendra Vora*, Mukesh Kumar Raikwar and Vikas Bhardvaj January 2012

The authors are Specialists at the Department of Pesticide Residue, Reliable Analytical Laboratories Pvt Ltd, in Bhiwandi, Thane, India *Corresponding Author   → See also:

«Study of Contamination Level of Pesticide Residues in Grapes (Vitis vinifera) in Maharashtra»

Abstract A fast, sensitive and specific method for routine determination of Chlormequat chloride residue from a variety of different food matrices was developed. It requires no cleaning procedure and very easy to extract without any interference in liquid chromatography (electrospray ionization) tandem mass spectrometry with using a stable isotopically labeled internal standard. Mass spectral acquisition was done in selected reaction monitoring mode (MRM), selecting the transitions from both the 35Cl and the 37Cl isotope of chlormequat. Recoveries after extraction was determined with radio-labeled chlormequat and averaged over the spiking range (0.010 – 0.050 mg/kg) in four different commodities were within 83-96%, with a coefficient of variation batter than 2%. The method can be applied to grape, juice concentrates, vegetables, fruits and cereal products, with typical limits of detection for chlormequat estimated at 0.001 – 0.002 mg/kg. A survey of different food commodities especially of grape revealed that chlormequat was detectable at very low level and it is also a very stable compound in many of the food samples analyzed, with the highest concentration recorded in grape (0.328 mg/kg, 100% contamination) and okra (1.0 mg/kg) purchased from Maharashtra region. Measurements were also conducted on two LC – MS instruments, also between international and national labs and demonstrate the versatility and robustness of the method and its applicability to instruments.

IntroductionChlormequat chloride (IUPAC name 2-chloroethyltrimethyl ammonium chloride) is a highly stable gibberellins biosynthesis inhibitor used as a plant growth regulator in many fruits and vegetables. Chlormequat chloride (CCC) inhibits cell elongation, hence shortening and strengthening stems and producing sturdier plants. It’s main use in agriculture is on cereal crops, such as wheat, barley and oats, to increase resistance to lodging by limiting stem growth and to improve yields. However, it has also been widely used to improve fruit setting, prevent premature fruit drop, increase fruit size and reduce the need for tree pruning in top fruit. Due to the CCC properties with the relatively strongly bound Cl- (Blinn, 1967) suggested that CCC residue could be accumulated in plant organs as well as the products. However, other workers have subsequently reported that CCC is completely metabolised since CCC residues could not be detected in animal tissues (Dekhuijzen et al., 1973; Dekhuijzen et al., 1974). To protect animals and humans from consumption of CCC in food, the European Community has set up the maximum CCC residual limits 0.05 for Fruits and Grains.

Several methods have been described for the determination of chlormequat. The first methods developed were nonspecific spectrometric (Moony et al., 1967) and thin-layer chromatographic

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procedures (Stijve, 1980). Despite extensive cleanup, interferences were present, blank values were too high, and reproducibility was poor. A method that is currently used in many laboratories for chlormequat determination was developed by Greve and Hogendoorn (1996). In their method, chlormequat is extracted from pears with methanol. After cleanup, using ionexchange chromatography and further cleanup over alumina, chlormequat is converted into acetylene by heating in alkaline medium at 215°C. The acetylene is measured in the head space by gas chromatography (GC) with flame ionization detection. Although acceptable recoveries (68 – 92%) and blanks were obtained, the method is still very labor intensive and unsuitable for routine analysis. Direct determination of chlormequat has been described for the analysis of formulations. Capillary electrophoresis was used with mass spectrometric detection (Moyano et. all, 1996). Mass spectrometry (MS) enables detection of chlormequat, which lacks a chromophoric group, and makes capillary electrophoresis or liquid chromatography (LC) promising alternatives to the classical methods for residue analysis outlined above. In fact, very recently, an LC/MS procedure was reported for the determination of chlormequat in Grapes (Banerjee et. all, 2007).

The purpose of the work described in this paper was to develop a common method for chlormequat residue analysis in food, cereals, fruits and vegetables that is more suitable than the Greve/Hogendoorn method for routine analysis. For method development reverse phase was used. The extraction procedure was very easy, reproducible and robust, which require no cleanup procedure. After complete validation, results were compared with international and national labs. The method was validated and implemented for routine analysis (up to 5 ng/ml) on LCMS/MS.

Materials and Methods

Chemicals

Following chemicals were used in the project are methanol & water (J T Backer) as a mobile phase, formic acid as a acidifying agent for extraction solvent, ammonium formate as a buffer for mobile phase. All these reagents were purchased from Merk. PTFE (Polytetrafluoroethylene) filter of 0.22 µm was used to filter the sample. Standard chloramequat chloride and internal standard Chlormequat Chloride C13 were purchased from “Accu std.”

Standard Stock solution of 1 mg/ml (1000 ppm) was prepared by dissolving 10 mg of CCC in Methanol. The standard working range from 10 to 300 ng/ml was prepared by serial dilution with methanol and std stock solutions were stored in the deep freezer at 4 °C when they were not in use.

Food Samples for Analysis

The fruits (Grape & Mango), Grain (Basmati Rice) and vegetable (Okra) from different region of Maharashtra were collected to carry out the project on contamination of CCC. Grapes & Rice were collected in winter season total number were 862 and 5 consequently, Mango (in fruit or juice form) was collected in summer season in 10 number and Okra was collected in 12 number from the market and farmer field in fresh condition and samples were stored at -18°C as a control sample and to check the stability of CCC in sample (after few days and a month).

Sample Preparation and Extraction

Homogenize matrix require for efficient and precise extraction of CCC. To prepare the matrix, sample was plucked (Grapes) or cut into small pieces (Mango, Okra) depending upon the physical structure of sample. Cut or plucked sample was collected in prewashed & dried 1000 ml beaker then sample was ground in a mixer for 10 min, obtained matrix fluid was blended with blender for 10 min at 5000 rpm to homogenize thoroughly. Rice was ground to coarse/fine powder and homogenized mechanically to obtained uniform matrix.

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The determination of chlormequat residues in plant material is difficult owing to the necessary separation of chlormequat from naturally occurring choline. If separation is not quantitative high blank values are found, which may lead to false positive results but due to its stability and polarity in acidic methanol chlormequat get extracted very easily, so that the following simple method was used for the extraction of CCC.

Weigh 10 gm of homogenized matrix in 50 ml plastic centrifuge tube (for recovery, spikes the sample with specified amount of Standard and then vortex for 2 min). Add 20 ml of 0.1 % Formic acid in methanol. Vortex for 5 min, then centrifuge at 10,000 rpm for 10 min. Pass the supernatant through 0.2 µ filter and Collect the supernatant in 2 ml vial for LC/MS.

LC/MS Conditions and Parameters

For sample analysis and method validation highly sensitive Agilent 6460 (Triple Quadruple) Mass spectrometer was used. Standard of CCC and IS were tuned at 1 mg/kg dissolved in methanol and following MRM (Multi reaction mode) and conditions were set for MS.

Compound Name

Precursor Ion

Product Ion Fragmentor Collision

Energy Polarity

CCC 122 58.1 130 35 PositiveCCC 122 62.9 130 35 PositiveCCC 124 58.1 130 35 PositiveCCC 124 65 130 35 Positive

CCC IS 128 58 120 35 PositiveCCC IS 128 69 120 20 PositiveCCC IS 126 58 120 35 PositiveCCC IS 126 67 120 20 Positive

Multi Reaction Mode (MRM)

Jet Stream ESIGas temp 330 °CGas flow 6.0 l/minSheath gas flow 8.0 l/minSheath gas temp 310 °CNeb Pressure 30 psiCapillary Voltage 3500Nozzle Voltage 500

MS Conditions

HPLC Condition: Due to the high polarity of CCC, HILIC Atlantis silica column of Waters was used with bellow mentioned mobile phase proportion. The column particle size of 5 µ, id 4.6 mm and length 150 mm was selected to perform samples in large quantity as well as for better peak shape. Samples were run at the flow rate of 0.5 ml/min.

Mobile Phase

A8:2 Water : methanol with 5 mM Ammonium formate buffer

B9:1  Methanol : Water with 5 mM Ammonium formate buffer

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Result and Discussion

Method Validation

Method validation is a documentary procedure to make sure that obtained result is precise, accurate and consistent. Following procedure was followed for extraction and analysis method validation. Blank 20 extraction solvents were run before the Linearity. Straight base line was seen in chromatogram of all 20 runs which indicated that none ghost peak or interference peaks coming at the same retention time. Linearity was plotted in solvent (Methanol) from 5 to 300 ng/ml (6 points). 0.99 Coefficient variation (CV) was obtained in both the solvent and all matrixes which say that the response is equal to the concentration (No quenching at higher concentration) in the range from 5 ng/ml to 300 ng/ml. For recovery, spiking was done in each food matrix at known three different concentrations (10, 20 and 50 µg/kg) with three replicates. Internal standard was spiked at same concentration in all series to negate the error occur during the extraction.

Fig-1: MRM chromatogram of Standard (10 µg/kg) and IS (25 µg/kg) in Methanol

Fig-2: Chromatogram of spiked IS (@ 25 µg/kg) and CCC (@ 5 µg/kg) in Grape sample

CCC was run through C18 and HILIC column with the same above mobile phase and RSD was calculated for both. HILIC column gave better elution, good peak shape and lowest RSD compare to C18 column. Other mobile phases Water and Acetonitrile: Methanol (60:40) with 0.1 % formic acid was also tried but best elution at 1 ng/ml was obtained only in Methanol: water. Repeatability with < 2% RSD was obtained between 6 points at three different (10, 20 and 50 µg/kg) concentrations. To check reproducibility between instruments and chemists, validation was again performed on API 2000 Bio sciex LC-MS triple quadruple instrument and better than 2% RSD was found.

Pesticide CCCMatrix Grape Mango Okra RiceRt 12.3 min. 12.4 min. 12.5 min 12.4 min

Calibration Range 0.005 – 0.3 (mg/kg)

0.005 – 0.3 (mg/kg)

0.005 – 0.3 (mg/kg)

0.005 – 0.3 (mg/kg)

Regression Equation y=0.0261x y=0.0234x y=0.0236x y=0.0245x

Linearity (R) 0.9993 0.9989 0.9976 0.9989LOD (µg/kg) 0.001 (mg/kg) 0.001 (mg/kg) 0.001 (mg/kg) 0.001 (mg/kg)LOQ (µg/kg) 0.005 (mg/kg) 0.005 (mg/kg) 0.005 (mg/kg) 0.005 (mg/kg)Recovery (in %) 91.70 95.46 89.67 85.73%  RSD 1.27 1.76 0.85 2.0

Table 2 · Validation of Analytical Methods for CCC in Fruits & Vegetables

Samples Mango (µg/kg)Conc. (µg/kg) R1 R2 R3 Mean % Recovery

0.01 0.0094 0.0096 0.0096 0.0095 95.330.02 0.0190 0.0192 0.0188 0.019 95.000.05 0.0480 0.0476 0.0485 0.0480 96.46

 Samples Grape (µg/kg)

Conc. (µg/kg) R1 R2 R3 Mean % Recovery0.01 0.0092 0.0086 0.009 0.0089 89.33

Table 3 · Percentage Recovery of CCC in Food

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0.02 0.0198 0.0182 0.017 0.018 92.500.05 0.047 0.045 0.046 0.046 93.26

 Samples Okra (µg/kg)

Conc. (µg/kg) R1 R2 R3 Mean % Recovery0.01 0.0094 0.0082 0.0086 0.0087 87.330.02 0.019 0.0185 0.018 0.018 92.500.05 0.041 0.046 0.045 0.044 89.20

 Samples Rice (µg/kg)

Conc. (µg/kg) R1 R2 R3 Mean % Recovery0.01 0.0084 0.0081 0.0085 0.0083 83.330.02 0.016 0.016 0.018 0.017 86.000.05 0.043 0.046 0.041 0.043 87.86

Inter Laboratory and International Laboratory Checking

4 Grape samples were sent to the Europe Lab for testing where analysis was performed by another method and same samples were analyzed by the above method. Then the both results were compared to validate the repeatability of method. Deviation in results was not more than ± 2 % in grape samples.

Stability Testing of CCC in Grapes

CCC is lacking in chromophore, is very polar and has low volatility (Baker et al., 1992) and since does not degrade in the animal body (Calsamiglia et al., 1996, Reynolds et al., 2004). Around 29 Grapes samples were re-extracted after a month, which had been stored at -18 °C in deep freezer. Obtained results were matched with the previous results, not more than ± 5 % variation between results was found. This says that CCC is very stable compound and it even does not degrade in food.

Conclusion

Nº Name of Sample

LOD (mg/kg)

Total Samples

Range (mg/kg)

Samples Contamination

% Contamination

EU MRL (mg/kg)

Samples >  MRL

1 Grapes 0.001 862 0.01-0.328 862.00 100.00 0.05 206

2 Mango 0.001 10 Nil ND - 0.05 Nil3 Okra 0.001 12 1.0 1 8.33 0.05 14 Rice 0.001 5 Nil ND - 0.05 Nil

Table 4 · Level of contamination of CCC in Fruits and Vegetables

From extraction and analysis method we can conclude that the method is very easy and simple to perform the analysis on regular basis, large quantity of samples can be analyzed in a day with less men power and cost. Validation of method by comparing data nationally (inter-laboratory checking) and internationally say that method is very precise, robust, reproducible and accurate even extraction method can be used almost for all foods with better than 85 % recovery. Stability testing has proved that CCC is very stable compound in fruits, vegetables and grains.

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0

Acknowledgement

We are very grateful to the Chairman and Managing Director of Reliable Analytical Laboratories Pvt Ltd, Mrs. Renu Kaushal for the essential and financial support. We are also thankful to the colleagues and lab technicians for giving moral support in this project.

References

Blinn, RC (1967), Biochemical behaviour in 2-chloroethyl trimethylammonium chloride in wheat and in rats. J. Agric. Food. Chem,. 15:984-988.

1.

Dekhuijzen HM and Vonk CV (1974), The distribution and degradation of chlormequat in wheat plants. Pest. Biochem. Physiol., 4:346-355.

2.

Dekhuijzen, HM and Bodlaender KBA (1973), Distribution and persistence of chlormequat in potatoes plants, Pestic. Sci., 4:619-627.

3.

 Moony RP & Pasarela NR (1967) Determination of chlorocholine chloride residues in wheat grain, straw and green wheat foliage J. Agric. Food Chem., 15:989-995.

4.

Stijve T (1980), Thin-layer chromatographic determination of chlormequat residues in various substrates, Dtsche. Lebensm-Rundsch 76:234-237.

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Greve PA and Hogendoorn EA (1996), Trace analysis of pesticides by gas chromatography, In; Analytical Methods for Pesticide Residues in Foodstuffs, 6th Ed., General Inspectorate for Health Protection, Ministry of Health, Welfare and Sports, The Netherlands.

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Moyano E, Games DE & Galceran MT (1996), Determination of Quaternary Ammonium Herbicides by Capillary Electrophoresis/Mass Spectrometry, Rapid Commun. Mass Spectrom.10:1379 – 1385

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Banerjee K, Oulkar DP, gupta S, Patil SB, Patil SH, Savant R and Pandurang G (2007), Validation and uncertainty analysis of a multi-residue method for pesticides in grapes using ethyl acetate extraction and liquidchromatography – tandem mass spectrometry. J. Chromatogr. A. 1173:98-109.

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Baker EA, Hayes AL and Butler RC (1992), physicochemical properties of agrochemicals: Their effects on foliar penetration. Pestic. Sci. 34:167-182. .

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Calsamiglia, S,Stern MD and Firkins JL, (1996), Comparison of nitrogen-15 and purine as microbial markers in continuous culture, J. Anim. Sci., 74;1375-1381.

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Reynolds SL, Thomas MR, Hamey PY (2004). Occurrence and risks associated with chlormequat residues in a range of foodstuffs in the UK. Food Addit. Contam. 21(5): 57-471.

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