Analytical and Bio-Analytical Method Development and Validation of Dichlorvos Pesticide Using RP-HPLC Method


Department of Pharmaceutical Chemistry, JSS College of Pharmacy Mysuru, JSS Academy of Higher Education and Research, Sri Shivarathreeshwara Nagara, Mysuru-570015, Karnataka, India

Abstract

Organophosphorus compounds were synthesised in the 1800s. Later they are used as insecticides in the late 1930s and early 1940s. The German scientist Gerhard Schrader is known for the creation of the basic chemical structure of anticholinesterase organophosphate compounds and development of the first commercialised Organophosperous insecticide. Such chemicals are anticholinesterase insecticide commonly used in agriculture and horticulture. To a lesser extent, they are used for domestic use. Due to the absence of bio persistence in organophosphates, most of the western countries opted to substitute organochlorines with organophosphates. Organophosphate pesticides are commonly used around the world, and contamination by these compounds is a serious public health concern in developing countries. Toxicokinetics and toxicodynamics of OP poisoning not only differ with path or level of exposure. But also the agent's chemical composition. Organophosphates are a group of pesticide that was developed in the 1940s in Germany and soon became an effective defence against agricultural pests. Dichlorvos which is a commonly used group of pesticide is a broad-spectrum organophosphate compound having insecticidal activity. Dichlorvos is a cholinesterase inhibitor exhibiting stomach, contact and systemic mode of action. Therefore, an accurate, fast, cost-effective and straightforward RP-HPLC technique for detecting Dichlorvos was developed. The RP-HPLC method is established by using ACN and Millipore water 50:50 v/v as mobile phase, the Flow rate is maintained at 1.5mL/minute. Detection of Dichlorvos was performed by using a PDA detector at 200nm. By this RP-HPLC procedure, RT of Dichlorvos was identified at 2.9 min.

Keywords

PDA detector, RP-HPLC method, Dichlorvos, organophosphate

Introduction

Organophosphorus compounds are synthesised in the 1800s, and later they are used as insecticides in the late 1930s and early 1940s (Costa, 2006). The German scientist Gerhard Schrader is known for the creation of the basic chemical structure of anticholinesterase organophosphate compounds and development of the first commercialised Organophosperous insecticide (Costa, 2006). Such chemicals are anticholinesterase insecticide commonly used in agriculture and horticulture (Kwong, 2002). To a lesser extent, they are used for domestic use. Due to the absence of bio persistence in organophosphates, most of the western countries opted to substitute organochlorines with organophosphates (Rusyniak & Nañagas, 2004). Organophosphate pesticides are commonly used around the world, and contamination by these compounds is a serious public health concern in developing countries (Sukirtha & Usharani, 2013). Toxicokinetics and toxicodynamics of OP poisoning not only differ with path or level of exposure. But also, the agent's chemical composition (Kwong, 2002).

The toxicity mechanism of organophosphates is by suppression of acetylcholinesterase, which results in building up of acetylcholine neurotransmitter and the continues activation of acetylcholine receptors (Blair et al., 1976; Inoue et al., 2007; Jones, Sommerville, & Wootten, 1992). The recommended treatment comprises of reactivating blocked acetylcholinesterase with an oxime antidote and suppressing acetylcholine’s action on the receptor with atropine (Costa, 2006; Rusyniak et al., 2004). A patient who received an appropriate diagnosis recover from acute toxicity. Dichlorvos is the active component of many insecticidal formulations (Blair et al., 1976; Jones et al., 1992).

The toxicity of Dichlorvos was reported by FAO/WHO at a joint meeting on pesticide residues (1965, 1967, 1968 and 1970) and a permissible daily intake of 0.004 mg /kg was suggested (Blair et al., 1976).

High concentration exposure over the short-term also up to 50 days of exposure on monkeys and rat to 0.1-0.5mg. The only effect seen was a depression of cholinesterase. Dichlorvos is a cholinesterase inhibitor exhibiting stomach, contact and systemic mode of action (Sharma, Jadhav, Rao, Saraf, & Chandra, 1990).

Dichlorvos is a broad-spectrum organophosphate compound having insecticidal activity. In the early days, most organophosperous insecticides were also dangerous to mammals, including humans, i.e. they were not selectively toxic to insects. Chromatographic techniques are commonly used for the chemical isolation, detection and quantification of as many pesticides.

The HPLC, GC or TLC methods were used to determine Dichlorvos, which are having some advantages and disadvantages (Cho, Matsuoka, & Kamiya, 1997; Parrilla, Vidal, Galera, & Frenich, 1994). To increase food production, pesticide applications have become vital. India is the world's fifth pesticide consumer. The proposed RP-HPLC method for the detection of Dichlorvos has a short retention time compared to other HPLC methods. Dichlorvos chemical structure is shown in Figure 1.

Materials and Methods

Instrumentation and Chromatographic conditions

For the current study, high- pressure liquid chromatography (HPLC) LC-20AD with PDA detector is used. The separation was attained by using a Phenomenex Luna C18 column (250 mm X 4.60 mm 5µ). The run time was set to 10min. Acetonitrile (ACN) and Millipore water (50:50 v / v) at a flow rate of 1.5 ml/min are used as the mobile phase. The temperature of the column was set at 40°C. The wavelength of detection was set at 200 nm. PHENEX PTFE0.02μm syringe sensor is used for filtration purposes.

Table 1: Optimized Chromatographic conditions

Column

Phenomenex luna C18 column (250 mm X 4.60 mm 5µ)

Wavelength

200nm

Flow rate

1.5ml/min

Detector

PDA

Injection volume

10µl

Mobile phase

ACN and Millipore water 50:50 (v/v)

Retention time

2.9 min

Table 2: System suitability results

Parameters

Acceptance criteria

Results

Tailing factor

NMT 2.0

1.270

Theoretical plates

NLT 2000.0

8652.304

Table 3: Concentration andpeak area for calibration curve

Concentration

Area

10

549627

20

937318

30

1271496

40

1670206

50

2147712

Table 4: Method precision intraday studies

Concentration

Peak area

Concentration

Peak area

Concentration

Peak area

10

545384

30

1237318

50

2170206

10

546254

30

1229528

50

2194037

10

541658

30

1241167

50

2138502

10

536916

30

1206536

50

2097184

10

534522

30

1283667

50

2198853

10

544521

30

1231128

50

2095633

average

541542.5

1238224

2149069

STD deviation

4407.041

23110.79

42044.54

%RSD

0.813794

1.866447

1.956407

Acceptance criteria: The RSD calculated on 8 determinations must be ≤ 2.0%

Table 5: Method precision interday studies

Concentration

Peak area

Concentration

Peak area

Concentration

Peak area

10

535624

30

1218965

50

2193468

10

546985

30

1204563

50

2185524

10

546685

30

1208265

50

2099835

10

539863

30

1218167

50

2122558

10

548467

30

1205837

50

2192538

10

546997

30

1218462

50

2184935

average

544103.5

1212377

2163143

Std deviation

4695.094

6254.223

37448.89

%Rsd

0.862904

0.515865

1.731226

Acceptance criteria: The RSD calculated must be ≤ 2.0%.

Table 6: Accuracy

Level of recovery

Amount of formulation

Amount of Pure drug

The total amount of drug

Peak area

Difference

%

Recovery

Mean

50

20

10

30

36085012

35535385

98.47686

50

20

10

30

36084635

35535008

98.47684

98.47684

50

20

10

30

36081465

35531838

98.47671

100

20

20

40

78090259

77152941

98.7997

100

20

20

40

71885632

70948314

98.6961

98.6961

100

20

20

40

71852784

70915466

98.6955

150

20

30

50

82284526

81013030

98.45476

150

20

30

50

82276485

81004989

98.45461

98.45461

150

20

30

50

82276352

81004856

98.4546

Acceptance criteria: Mean % recovery and individual at each level should be between 102.0% and 98.0%

% Recovery= (Amount of drug recovered/ Amount of drug added)*100

Table 7: LOD and LOQ

Average of SD

101937

102339

102339

LOD

0.046µg/ml

102659

Average of slope

12302

12301

12301

LOQ

0.139µg/ml

12377

Table 8: Robustness

Parameters

Change in units

Acceptance criteria

Results

Wavelength

205 ±3

%RSD ≤ 2

1.329

Flow rate

1ml/min ±0.1

%RSD ≤ 2

1.256

Column temperature

40˚c ±5˚c

%RSD ≤ 2

0.546

Mobile phase ratio

Acetonitrile: orthophosporic acid 0.1% 50:50 (v/v) ±2

%RSD ≤ 2

0.217

Table 9: Ruggedness

Concentration

Trial 1

Trial 2

Mean

SD

%RSD

by changing the analyst

0

0

0

0

0

0

10

542356

5354867

2948612

3402959

0.925648

20

931234

931025

931129.5

147.7853

0.765426

30

1215482

12256718

6736100

7807333

0.896253

40

1610250

16203652

8906951

10319094

0.925625

By changing the instrument

0

0

0

0

0

0

10

539524

545264

542394

4058.793

0.748311

20

935246

945698

940472

7390.68

0.785848

30

12854691

1226524

7040608

8222356

0.862546

40

1621534

1660214

1640874

27350.89

0.965246

Table 10: Calibration data of Dichlorvos

Sl.no

Conc. (µg/ml)

Peak area

1

0

0

2

10

312932

3

20

615335

4

30

907831

5

40

1095066

6

50

1513468

Table 11: Results showing precision for Dichlorvos (within run)

Concentration

Mean peak area

Mean concentration

SD

%CV

10 (LLOQ)

305015.4

9.9026

0.8183

8.2643

20 (LQC)

585185.0

19.962

0.8725

4.3708

30 (MQC)

861875.4

29.897

1.0632

3.5563

40(HQC)

1136209.2

39.748

1.9101

4.8055

Table 12: Results showing precision for Dichlorvos (between run)

Concentration

Mean peak area

Mean concentration

SD

%CV

10 (LLOQ)

307135.8

9.97877

0.7763

7.7795

20 (LQC)

581728.6

19.8809

0.8446

4.2483

30 (MQC)

862136.0

29.9069

1.0649

3.5609

40(HQC)

1134797.2

39.6973

1.8912

4.7640

Table 13: Results showing recovery for Dichlorvos

Standards

Concentration

Analytical Peak Area

Bioanalytical Peak area

% Recovery

LLOQ

10

549627

312932

56.93533978

LQC

20

937318

615335

65.64847789

MQC

30

1271496

907831

71.39865167

HQC

40

1670206

1095066

65.56472675

UQC

50

2147712

1513468

70.46885243

Table 14: Result showing stability for Dichlorvos

Stability

Standards

Concentration µg/mL

Mean recovered concentration µg/mL)

SD

%CV

Bench-top

LQC

20

19.9169

0.5020

2.5205

HQC

40

39.2690

0.7317

1.8633

Freeze and

LQC

20

19.9370

0.2522

1.2650

thaw

HQC

40

39.7585

0.7294

1.8347

Long term

LQC

20

19.9120

0.2621

1.3166

stability

HQC

40

38.3938

0.0700

0.1827

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Figure 1: Chemical structure of Dichlorvos

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Figure 2: Uv spectrum

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Figure 3: Blank chromatogram

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Figure 4: Standard chromatogram of Dichlorvos at 100µg/ml concentration showing RT at 2.9 min

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Figure 5: Sample chromatogram of Dichlorvos at 20µg/ml concentration showing RT at 2.9 min

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Figure 6: Chromatogram of blank serum

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Figure 7: Standard chromatogram of Dichlorvos

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Figure 8: Sample chromatogram of Dichlorvos

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Figure 9: Calibration curve forDichlorvos

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Figure 10: Linearity graph of Dichlorvos

Chemicals and reagents

Dichlorvos standard was procured from Sigma Aldrich, Bengaluru. Action-3, which is a Dichlorvos marketed formulation manufactured by Jayakrishna pesticides private limited., was procured from a local market. All chemicals used were analytical grade purchased from Merck pharmaceuticals. HPLC grade ACN and Millipore water is used as mobile phase. HPLC grade ACN was used as the diluent for preparation of the solutions.

Analytical method development

Selection of wavelength

The λ max of Dichlorvos was determined by using UV-visible spectrophotometer 1800. Uv spectrum for Dichlorvos is shown in Figure 2.

Mobile phase selection and preparation

Dichlorvos being less polar, different mobile phase combinations of various ratios were tried for the selection of mobile phase. The standard Dichlorvos drug was injected with various combination of mobile phase at different ratios and flow rate for the peak optimisation. The procedure was continued until obtaining a sharp peak. The sharp peak was obtained at 50:50(v/v) of ACN and Millipore water.

Preparation of standard stock solution

The standard stock of Dichlorvos was prepared by dissolving 10mg of the standard drug in 10ml of HPLC grade acetonitrile to obtain 1mg/ml concentration. From the stock solution, the standard stock solutions of 10, 20, 30, 40, and 50µg/ml were prepared. All dilutions were made up by using HPLC grade acetonitrile.

Sample preparation

0.131ml of marketed formulation (Action-3) containing 76% of Dichlorvos was diluted to 100ml by using HPLC grade acetonitrile to form 1mg/ml solution. From the above sample solution, pipette out 0.2ml and make-up to 10ml by using HPLC grade acetonitrile to get 20µg/ml solution. The above resolution was passed through 0.20µm syringe filter and injected to RP-HPLC.

Optimization of the method for Dichlorvos

Study of the effect of various parameters in developing method was carried out. Initially, the solubility of Dichlorvos in multiple solvents was tested. Then a suitable column for separation is selected for the proposed method. To achieve a proper separation of eluted compounds in HPLC, the chromatographic conditions were optimised. Initially, different diluent was tested to elute the drug.

Flow rate and mobile phase choice are determined based on peak parameters like tailing factor or asymmetry, run time, resolution. Acetonitrile and Millipore water in ratio 50:50 (v/v) was used as mobile phase at a flow rate of 1.5ml/min. The blank chromatogram was shown in Figure 3.

The standard and sample chromatogram of Dichlorvos at 2.9 min were shown in Figure 4 and Figure 5 respectively. Chromatographic conditions used for the method is shown in Table 1.

Bio-analytical method development

Preparation of standard stock

Accurately weigh 10mg of pure Dichlorvos into 10ml volumetric flask dissolve and make-up the volume by using HPLC grade acetonitrile to get 1mg/ml concentration.

From the above solution prepare 75, 150, 225, 300 and 375µg/ml so that after diluting it with serum and ACN final concentration will be 10, 20, 30, 40 and 50µg/ml.

Optimized extraction procedure

After trying with a different combination of serum and drug volume for protein precipitation method by using acetonitrile, the following method is finalized.

In this procedure, acetonitrile act as a precipitating protein agent. To the Eppendorf tube add 100µl of human serum and 100µl of a drug, Vortex the above mixture in a vortex meter for 20 seconds. To the mixture add acetonitrile and make-up the volume to 1.5ml then centrifuge it at 9500 RPM for 10 minutes at 4˚c. The supernatant is filtered through 0.20µm syringe filter and injected to RP-UFLC. The blank chromatogram was shown in Figure 6. The standard and sample chromatogram of Dichlorvos at 2.9 min were shown in Figure 7 and Figure 8 respectively. Chromatographic conditions used for the method is shown in Table 1.

Results and Discussion

The precise, quick and easy RP-HPLC technique for the identification of Dichlorvos has been developed. The proposed technique was evaluated following the ICH Q2(R1) guidelines. The RT of Dichlorvos was found to be 2.9min from the chromatogram. And the coefficient of correlation was found to be 0.995 for analytical and 0.9934 for bio-analytical method. The quantification limit (LO Q) was found to be 0.139μg / ml, and the detection limit (LOD) was found to be 0.461μg / ml. The inter-day and intra-day precision value (RS D percentage) were identified to be less than two.

Analytical method validation

System suitability

The standard stock of Dichlorvos was injected six times for testing system suitability parameters, The results were shown in Table 2.

Linearity

It is the ability to obtain experimental results equal to the analyte content in the specimen. The calibration curve was attained by using five different concentrations in triplicate 10, 20, 30, 40, and 50µg/ml and the linearity was established by applying linearity expression y=mx+c, and the slope was calculated. The calibration curve for Dichlorvos is shown in Figure 9. The concentration and peak area was established in Table 3.

Precision

The repeatability of the method was validated by using different concentration of the drug 10, 30 and 50 µg/ml. The above solutions were prepared from the stock solution and used to inject in interday and intraday for the evaluation of precision. The concentrations were prepared at three different times in a day for intraday studies. The results for accuracy was shown in Table 4 and Table 5.

Accuracy

It is the closeness of the obtained value to the true value of the sample, to check the accuracy of the method, the formulation was spiked with 50%, 100% and 150% of Dichlorvos standard drug. The results were analysed to find the % recovery of the Dichlorvos. The result for accuracy was given in Table 6.

Limit of detection and limit of quantification

The LOD and LOQ for the HPLC method were determined by using a calibration standard. LOD can be calculated as per the ICH guidelines by using the formula LO D=3.3×N÷S, N is the standard deviation and S is the slope. LOQ can be calculated by the formula LOQ=10×N÷S where N is the standard deviation and S is the slope. The results for LOD and LOQ was shown in Table 7.

Robustness

A method can stay unchanged when small differences in parameters are applied. The robustness of the suggested technique was verified by increasing and decreasing the wavelength, flow rate, column temperature and 30μg / mL concentration were injected. The result of the robustness was shown in Table 8.

Ruggedness

An experimental procedure's ruggedness is its ability to remain unaffected by minor or intentional changes in system parameters. The ruggedness of the proposed procedure is validated by changing analyst and instrument. The result was shown in Table 9.

Bioanalytical method validation

Calibration curve

It consisted of a matrix sample processed without analyte and matrix sample with calibration standards. It is showing good linearity over the range of 10 to 50µg/ml with a coefficient of correlation 0.9934. The calibration curve for Dichlorvos is shown in Figure 10. The concentration and peak area was shown in Table 10.

Specificity/selectivity

An analytical technique can differentiate and quantify the analyte in the presence of other components in the sample. For selectivity blank plasma of two different lots were taken and analysed. Selectivity was assessed by comparing the extracted blank plasma response with extracted LLOQ. At the RT of the drug, No significant interference from the blank plasma was observed.

Sensitivity

This parameter was evaluated by injecting six different aliquots of extracted LLOQ concentration. Percentage deviation from the nominal concentration and percentage CV were calculated. The developed method was found to be sensitive to %CV.

Accuracy and precision

Within run and between run accuracy were performed by five replicates of LLOQ, LQC, MQC and HQC. Between run, accuracy was assessed by analysing sample on different days.

The accuracy and precision for all batches at LLOQ, LQC, MQC and HQC levels were calculated. Mean percentage nominal concentration and CV for all the batches were found to be within the acceptance limit. The results for precision is shown in Table 11 and Table 12.

Recovery

After spiking the extracted QC samples were analysed and percentage recovery at each level was calculated by comparing the peak area of low, medium and high QC levels.

Mean recovery across all the QC levels is found to be 66.0%. Results for recovery is shown in Table 13.

Stock solution stability

Both main stock and spiking stock of Dichlorvos was found to be stable at 2-10°c for 20 days (long term) and 8 hours at room temperature.

Bench top stability

Low and high QC was prepared and kept at the benchtop at room temperature for a minimum of 4 hrs (stability samples).

Then analysed the response is compared with the freshly prepared calibration standard responses. Mean percentage change was calculated

Freeze and thaw stability

The samples were exposed to three freeze-thaw cycles. The peak area response is then compared with standard calibration responses.

Mean percentage change was calculated and verified against acceptance criteria.

Long term stability

The stability of the sample is evaluated by keeping it for an extended period in freeze state and extracted then analysed. The response is compared with a fresh calibration standard response. Results for stability is shown in Table 14.

Conclusion

The developed RP-HPLC approach has been validated in terms of device suitability, linearity, precision, accuracy, LOD and LOQ, robustness and ruggedness in compliance with the ICH guidelines. It was inferred from the above finding that the system developed was reliable, accurate and unique for the detection of Dichlorvos.