Tracing of contamination level of organochlorine pesticides in Bottle gourd (Lagenaria siceraria), Sponge gourd (Luffa aegyptiaca), Brinjal (Solanum melongena), Plum (Prunus domestica), Kiwi (Actinidia deliciosa) and Pineapple (Ananas comosus)

Devendra Kumar

Department of Chemistry, Institute of Basic Sciences, Khandari Campus Dr. Bhimrao Ambedkar University, Agra, U. P, India

Corresponding Author E-mail:devendrakumar131@gmail.com

DOI : http://dx.doi.org/10.12944/CARJ.11.1.17

Article Publishing History

Received: 11 Oct 2022
Accepted: 04 Apr 2023
Published Online: 03 May 2023

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Plagiarism Check: Yes
Reviewed by: Dr. Sedighe Ashtari
Second Review by: Dr. Fatiha Hakimi
Final Approval by: Dr. Andrea Sciarretta

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Abstract:

Fruits and vegetables have nutritional value, but they can also be source of toxic contaminants such as pesticide residues. The aim of this study was to estimate the contamination level of pesticide residues in summer season fruits and vegetables. The constant use of pesticides contaminated fruits and vegetables pose a major risk to community health. An electron capture detector was used in Gas chromatography analysis to monitor 20 organochlorine pesticides including α-chlordane, γ-chlordane,  isomers of benzene hexachloride (α-BHC, β-BHC, γ-BHC, δ-BHC), 4,4-DDT, 4,4-DDE, 4,4-DDD, aldrin, dieldrin, endrin, endrin aldehyde, endrin ketone, heptachlor, heptachlor epoxide, endosulfan-I, endosulfan II, endosulfan sulfate and methoxychlor in six types of fruits and vegetables (bottle gourd, sponge gourd, brinjal, plum, kiwi and pineapple) of summer season. It was found that plum and pineapple were found contaminated with 4,4’-DDD and other fruits and vegetables were found contaminated with more than one pesticides. During the tracing it was noticed that the estimated pesticides concentrations were lower than the (MRL) values but constant eating of infected pesticide fruits and vegetables may produce severe health complications. The findings of the present research showed that the existence of strict rules and observance of pesticide residues in fruits and vegetables is a basic need.

Keywords:

Fruits; GC-ECD; Organochlorine Pesticides; Vegetables

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Kumar D. Tracing of contamination level of organochlorine pesticides in Bottle gourd (Lagenaria siceraria), Sponge gourd (Luffa aegyptiaca), Brinjal (Solanum melongena), Plum (Prunus domestica), Kiwi (Actinidia deliciosa) and Pineapple (Ananas comosus). Curr Agri Res 2023; 11(1). doi : http://dx.doi.org/10.12944/CARJ.11.1.17

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Kumar D. Tracing of contamination level of organochlorine pesticides in Bottle gourd (Lagenaria siceraria), Sponge gourd (Luffa aegyptiaca), Brinjal (Solanum melongena), Plum (Prunus domestica), Kiwi (Actinidia deliciosa) and Pineapple (Ananas comosus). Curr Agri Res 2023; 11(1). Available from: https://bit.ly/3VqFmKF


Introduction

Fruits and vegetables are an important component of our food because of their nutritional significance and have a main role in the diet from the point of view of health and prevention of disease1. The majority of Indians are vegetarian and their average diet constitutes about 150–250 g of fruits and 400g of vegetables in the total meal per day2. As several pesticides are toxic substances to human health and persist in the surrounding for a long time. Therefore, for improved crop production3 and quality, pesticides are constantly used throughout the whole period of growth time and also at the ripening stage4. In a country like India, the use of pesticides has become predictable to sustain and improve current level of crop production by protecting the crop from pests5. However approximately, per year two million tons pesticides was consumed around the world; out of which, 45% of pesticides is used by Europe, and 25% in USA, the rest of the pesticide is consumed in the remaining world. India’s share is just 3.75%. Now a days, India has turned into the second largest producer of pesticides in Asia after China and it ranks 12th worldwide6. As reported by the Agriculture Ministry & Farmers Welfare, Government of India, the utilization of pesticides in different states and union territories was 58720 metric tons pesticides for the duration of 2021-2022. In all the Indian states, Maharashtra, Haryana, Uttar Pradesh and Telangana are the topmost four states contributing to 57.93 % of pesticide intake in India. The 35.10 % of pesticide used by other states and 6.97 % used by union territories7. These pesticides are absorbed by the fruits and vegetables and finally by human beings due to which they may be hazardous8.

Organochlorine pesticides (OCPs) belong to the class of persistent organic pollutants (POPs) with long term residual effect in the environment. These pesticides have many problems including broad spectrum toxicity for both target and non-target species by alter the exact function of insects nervous system leading to disorders such as convulsions and paralysis followed by eventual death9.  However, most of these pesticides have been banned in the developed countries but they are still used in developing countries of Asia via illegal routes. High global demands of Organochlorine pesticides in agricultural practice, in regard to environmental regulations, are due to their easy availability, cost-effectiveness and excellent efficiency in pest control and to increased yield of the crop in agriculture sector10. OCPs, including DDTs, hexachlorocyclohexanes (HCHs), aldrin, dieldrin, endrin, chlordane and heptachlor are still in use via illegal route10.

Organochlorine pesticides are  associated with various human health’s problems, ranging from short-term  impacts including headaches and nausea, to chronic impacts11, including different cancers12,13, birth defects14, infertility15, metabolic disorders16, parkinson17, amyotrophic lateral sclerosis18, Alzheimer19, neurodegenerative disorders20, chronic lymphocytic leukemia (CLL), multiple myeloma and endocrine disruption21. These negative impacts of pesticides on human health have advised to researchers to monitor a variety of pesticides in many food materials. Keeping these points in mind and in continuation of our preceding work22 in this article, 20 organochlorine pesticides monitoring have been reported in selected fruits and vegetables of summer season viz., bottle gourd, sponge gourd, brinjal, plum, kiwi and pineapple.

Materials and Methods

All glassware was carefully cleaned using distilled water and dipped in acetone and then dried in oven at 150oC temperature before use. Distillation of acetonitrile, acetone, n-hexane, ethyl acetate and dichloromethane (DCM) solvents has been carried out before use for the extraction of pesticide residues from fruits and vegetables. Then, Adsorbents such as silica gel and charcoal were activated before use for cleanup. Purified extracts were examined by GLC equipped with 63Ni-Electron Capture Detector from AIRF JNU, New Delhi. The small equipments like mechanical shaker, warring blender and rotary evaporator etc. were also used during extraction. Stock solution of standard was prepared in n-hexane.

Extraction

Liquid-liquid extraction of pesticides from fruits and vegetables has been achieved in the subsequent stages:

Sampling: 250g of all fruit and vegetable samples, i.e. Bottle gourd (Lagenaria siceraria), Sponge gourd (Luffa aegyptiaca), Brinjal (Solanum melongena), Plum (Prunus domestica), Kiwi (Actinidia deliciosa) and Pineapple (Ananas comosus) were collected directly from native market.

Storage of samples: All samples were brought in lab and stored in a refrigerator at 5ºC. These samples were studied within 3 days of collection. Collected samples of fruits and vegetables have been washed for few minutes with water and dried with tissue paper.

Blending of Samples

To establish the exact concentration of pesticides in human beings, only the eatable parts of fruits and vegetables was keep for tracing of pesticide residue. Each fruit and vegetable has been cut into small pieces after drying process. A representative sample 250g of fruit and vegetable was uniformly blended with 25g of dehydrated sodium sulfate in a warring blender to make a thin ultra-fine paste.

Liquid-liquid extraction of Bottle gourd and Sponge gourd

50g homogenize thin paste of each vegetable sample was subjected to shaken with 100 ml acetonitrile with a mechanical shaker for 2h. It was filtered and 50 ml n-hexane and dichloromethane (3:2 v/v) was added to the filtrate and shaken for 3h. Then, separating funnel was permitted at perpendicular position for about 3h to get the two different layers. n- Hexane layer was removed in a conical flask. The extraction process was again repeated in three more times using 50 ml n-hexane and dichloromethane (3:2 v/v) each time. The collected extract was reduced up to dryness at 45oC and then again 10 ml n- hexane was mixed to the dried solution.

Liquid-liquid extraction of Kiwi fruit and Brinjal

 50g homogenize paste of Kiwi/ brinjal was mixed with 100 ml acetonitrile and shaken for 2 h. The obtained extract was filtered then filtrate was exchanged to liquid –liquid extraction. To this, 50 ml n-hexane was mixed and agitated for 3h. Thereafter, to obtain the two dissimilar layers, separating funnel was permitted at vertical location for about 3h. The upper layer (n-hexane) was separated out. The extraction method was redone thrice using 50 ml n-hexane every time. The collected extract solution was reduced to 5ml at 40oC temperature and 10 ml n- hexane was again mixed.

Liquid-liquid extraction of Plum

50g homogenize paste of plum was shaken for 2h on a mechanical shaker using 100 ml acetonitrile. This extract was filtered, and mixed with 50 ml cyclohexane. After that this solution was agitated for 3h. Thereafter, two distinct layers were obtained on hold up separating funnel at straight position for about 3h. The upper layer of cyclohexane was separated out and the whole method was again repeated three times more using 50 ml cyclohexane at every stage. The collected extract was concentrated at 45ºC temperature up to dryness (5 ml) and again mixed in 10 ml n-hexane.

Liquid-liquid extraction of Pineapple

50g homogenize fine paste of pineapple was subjected to shaken with 100 ml acetonitrile for 2 h. The extract was filtered and filtrate was combined with 50 ml acetone and n-hexane (1:4). This solution was shaken for 3h. Thereafter, to obtain the two different layers, separating funnel was allowed to put at straight up position for about 3h. The upper layer (n-hexane) was separated out from the separating funnel. The extraction process was constantly repeated in the ratio 1:4 using acetone and n-hexane (50 ml) three more times. The collected extract was reduced up to dryness (5 ml) at 30ºC and dissolve in 10 ml n-hexane.

Purification

These extracts were subjected for purification by packed-column chromatography over silica gel and activated charcoal in the ratio 5:1 (w/w) or using silica gel. Every extract was first run via column using 50 ml n-hexane for elution. The obtained extracts were then concentrated to reduce up to dryness and again mixed with 10 ml n-hexane and subsequently, exposed to GC-ECD for pesticides analysis.

Results and Discussion

GC-ECD analysis of pesticide standard was carried out to find out (RT) retention time and peak area equivalent to 0.2 µg/µL concentration (Table-1).

Table 1: Peak area and RT value of standard of organochlorine pesticides

Peak No. Name of pesticides RT value Area Area %
1 α- Benzene hexachloride 7.264 4056398 0.3107
2 γ- Benzene hexachloride 10.666 69248549 5.3044
3 β- BHC 12.108 110194348 8.4409
4 δ-BHC 13.553 67783682 5.1922
5 Heptachlor 15.230 63367599 4.8540
6 Aldrin 16.828 87205582 6.6799
7 Heptachlor epoxide 18.093 4789654 0.3669
8 γ- Chlordane 18.655 65779983 5.0387
9 α- Chlordane 19.761 82997615 6.3576
10 Endosulfan I 20.356 115947358 8.8816
11 4,4’-DDE 21.560 122612908 9.3921
12 Dieldrin 22.460 60365744 4.6240
13 Endrin 23.041 74179902 5.6822
14 4,4’-DDD 23.459 60226898 4.6134
15 Endosulfan II 23.731 59156527 4.5314
16 Endrin aldehyde 24.837 82799420 6.3424
17 4,4’-DDT 25.122 70574949 5.4060
18 Endosulfan sulfate 26.861 69382904 5.3147
19 Methoxychlor 27.713 34287889 2.6265
20 Endrin ketone 32.942 525912 0.0403
Total 1305483821 100.00
Figure 1: Gas chromatogram of Standard 

Click here to view Figure

Chromatogram of Bottle gourd (Lagenaria siceraria) (Fig.2) revealed three peaks at Rt values 13.540 16.858 and 27.685 resemble with δ- benzene hexachloride (δ-BHC), aldrin and methoxychlor correspondingly which specified that aforesaid pesticides were exist in the sample of bottle gourd. The chromatogram of Sponge gourd (Luffa aegyptiaca) exhibited numeral  peaks (Fig.3), among them  three peaks at  Rt value 13.554, 23.448 and 26.831were adjacent to the peak of  δ-BHC, 4,4-DDD  and endosulfan sulphate which indicated that existence of these pesticides in the Sponge gourd sample.

Figure 2: Gas chromatogram of Bottle gourd. 

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Figure 3: Gas chromatogram of Sponge gourd

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Gas chromatogram of Brinjal (Solanum melongena) (Fig.4) displayed two peaks at Rt values 23.014 and 23.450 corresponding to the Rt value of endrin and 4,4’-DDD which point out the occurrence of these pesticides in the sample of Brinjal. The chromatogram of Plum (Prunus domestica) (Fig.5) consisted one peaks at the Rt value 23.464  which was resemble with Rt value of 4,4’-DDD, indicated the existence of 4,4’-DDD  pesticide in the sample of Plum. In case of the gas chromatogram of Kiwi fruit (Actinidia deliciosa) (Fig.6) three peaks were  exact nearby with Rt values 13.530 of δ-BHC, 16.853 of aldrin and 23.013 of endrin which showed the presence of these pesticides in the sample of Kiwi fruit. However, Gas chromatogram of Pineapple (Ananas comosus) (Fig.7) showed one peak at Rt value 23.458 which was adjacent to the Rt value of  4,4’-DDD indicated presence of 4,4’-DDD  in the sample of Pineapple. Detected pesticides and their concentration have been given in Table-2.

Figure 4: Gas chromatogram of Brinjal 

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Figure 5: Gas chromatogram of Plum

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Figure 6: Gas chromatogram of Kiwi fruit      

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Figure 7: Gas chromatogram of Pineapple. 

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Table 2: Discovered pesticides and their concentration evaluated through GC-ECD

S. No. Sample Name Pesticide found Rt. value Pesticides concentration (mg/kg)
1 Bottle gourd δ-BHC 13.540 0.0652
Aldrin 16.858 0.0051
Methoxychlor 27.685 0.022
2 Sponge gourd δ-BHC 13.554 0.01419
4,4-DDD 23.448 0.0065
Endosulfan sulphate 26.831 0.0054
3 Brinjal Endrin 23.014 0.01763
4,4’-DDD 23.450 0.01403
4 Plum 4,4’-DDD 23.464 0.00649
5 Kiwi fruit δ-BHC 13.530 0.0044
Aldrin 16.853 0.0110
Endrin 23.013 0.0087
6 Pineapple 4,4’-DDD 23.458 0.00373

 Aldrin is an alicyclic chlorinated hydrocarbon. It was found in the concentration range 0.0110-0.00513 mg/kg in Kiwi fruit and Bottle gourd, δ-BHC was found in the range 0.0652-0.0044 mg/kg in bottle gourd, sponge gourd and kiwi fruit. Endrin was estimated in the range 0.01763-0.0087 mg/kg in brinjal and kiwi fruit. 4,4’-DDD were recorded in the range (0.01403-0.00373 mg/kg in brinjal, plum and pineapple. Methoxychlor was found 0.022 mg/kg and endosulfan sulphate 0.0054 mg/kg in sponge gourd.

Among the different organochlorine pesticide residues found in various vegetables and fruits, δ-BHC was found with the highest concentration 0.0652 mg/kg in bottle gourd followed by methoxychlor 0.022 mg/kg in bottle gourd, endrin 0.01763 mg/kg in brinjal, 4,4’-DDD  0.01403 mg/kg in brinjal, aldrin  0.0110 mg/ kg in kiwi fruit, endosulfan sulphate 0.0054 mg/kg in sponge gourd.

Many researcher23,24 reported the presence of organochlorine pesticides in food commodities in different range. Although the use of these pesticides has been banned or restricted in last few decades. The presence of lower amounts of pesticides were detected in present studies may be attributed due to previous use of organochlorine pesticides.

Conclusion

 In order to minimize health hazard, pesticide residues tracing in food commodities is important and essential. The results of the study have indicated that all fruits and vegetables selected for tracing work were contaminated with pesticides. However, contamination level was below MRL values set by FAO/WHO Codex Alimentarius Commission but regular consumption of pesticide infected fruits and vegetables may create serious health issues.

Acknowledgement

We thanks  Head, Chemistry Department, I.B.S., Dr. B.R. Ambedkar University, Khandari Campus, Agra for providing indispensable facilities during research work and also thankful to AIRF, JNU, New Delhi, India for providing GC analysis for samples. 

References

  1. Kumari B., Madan V. K., Singh J., Singh S., Kathpal T.S. Monitoring of Pesticidal Contamination of Farmgate Vegetables from Hisar.  Environmetal Monitoring Assessment. 2004; 90(1): 65-71.
    CrossRef
  2. Bhanti  M., Taneja A. Monitoring of organochlorine Pesticide Residues in Summer and Winter Vegetables from Agra, India–A Case Study.  Environmetal Monitoring Assessment. 2005; 110(1):  341-346.
    CrossRef
  3. Mutengwe M.T., Chidamba L.,  Korsten L. Monitoring Pesticide Residues in Fruits and Vegetables at Two of the Biggest Fresh Produce Markets in Africa. Journal of Food Protection. 2016; 79(11): 1938–1945.
    CrossRef
  4. Kumari B., Madan V. K., Kathpal T. S. Monitoring of Pesticide Residues in Fruits.  Environmetal Monitoring Assessment. 2006; 123(1): 407-412.
    CrossRef
  5. Bhanti M., Shukla G., Taneja A. Contamination Levels of Organochlorine Pesticides and Farmers’ Knowledge, Perception, Practices in Rural India: A Case Study. Bulletin of Environmental Contamination and Toxicology. 2004; 73(5): 787-793.
    CrossRef
  6. Bose R., De A., Kumar A. Mozumdar S. Targeted Delivery of Pesticides Using  Biodegradable Polymeric Nanoparticles, New Delhi, India, Springer, 2014.
  7. http://ppqs.gov.in/divisions/pesticides-monitoring-documentation (visited on 10/10/2022)
  8. Madan V.K., Kumari B., Singh R.V., Kumar R. Kathpal T.S. Monitoring of Pesticides from Farm Gate Samples of vegetables in Haryana. Pesticide Research Journal. 1996; 8(1): 56-60.
  9. Donald Sparling, Ecotoxicology Essentials Environmental Contaminants and Their Biological Effects on Animals and Plants, Elsevier, Ist Edition, USA, 2016.
  10. Fosu-Mensah, B.Y., Okoffo, E.D., Darko, G., Gordon C., Assessment of Organochlorine Pesticide Residues in Soils and Drinking Water Sources from Cocoa Farms in Ghana. SpringerPlus. 2016; 5: 869-881.
    CrossRef
  11. Shah R. Pesticides and Human Health. In Emerging Contaminants. IntechOpen, London, 2020.
    CrossRef
  12. Bhat A. R., Wani  M. A., Kirmani A.R., Raina T.H.  Pesticides and Brain Cancer Linked in Orchard Farmers of Kashmir. Indian Journal of Medical Paediatric Oncology. 2010; 31(4): 110.
    CrossRef
  13. Kaur N.,  Swain S.K.,  Banerjee B.D., Sharma T. and Krishnalata T.,  Organochlorine pesticide exposure as a risk factor for breast cancer in young Indian women: A case–control study South Asian Journal of Cancer. 2019; 8(4): 212–214.
    CrossRef
  14. Kalra S., Dewan P., Batra P., Sharma T., Tyagi V., Banerjee B.D. Organochlorine pesticide exposure in mothers and neural tube defects in off springs. Reproductive Toxicology2016; 66:56–60.
    CrossRef
  15. Amir S., Tzatzarakis M., Mamoulakis C., Bello J.H., Akber S.A.M.A.S. E. Qani, Vakonaki E., Karavitakis M., Sultan S.,  Tahir F.,  Shah S.T.A., Tsatsakis A. Impact of organochlorine pollutants on semen parameters of infertile men in Pakistan,Environmental Research, 2021;195: 110832-110840.
    CrossRef
  16. Rosenbaum P.F.,  Weinstock R.S., Silverstone A.E., Sjödin  A., Pavuk M. Metabolic syndrome is associated with exposure to organochlorine pesticides in Anniston, AL, United States. Environment  International , 2017; 108: 11–21.
    CrossRef
  17. Narayana S., Liew Z., Bronsteinb J.M., Ritz B. Occupational Pesticide Use and Parkinson’s Disease in the Parkinson Environment Gene (PEG) Study. Environment International. 2017; 107: 266–273.
    CrossRef
  18. Su F.C., Goutman S.A., Chernyak S., Mukherjee B., Callaghan B.C., Batterman S., Feldman E.L., The Role of Environmental Toxins on ALS: A Case-Control Study of Occupational Risk Factors, JAMA Neurology. 2016; 73(7): 803–811.
    CrossRef
  19. Richardson J. R., Roy A., Shalat S. L., Stein R.T.V., Hossain M. M., Buckley B., Gearing M., Levey A.I., German D.C. Elevated Serum Pesticide Levels and  Risk for Alzheimer Disease. Jama Neurology. 2014; 71(3):284-290.
    CrossRef
  20. Beard J.D.,  Hoppin J.A., Richards M.,  Alavanja M.C.R, Blair A., Sandler D.A.,  Kamel F., Pesticide exposure and self-reported incident depression among wives in the Agricultural Health Study. Environmental Research. 2013; 126: 31-42.
    CrossRef
  21. Palma, P., Palma, V.L., Matos, C., Fernandes, R.M., Bohn, A., Soares, A.M.V.M., Barbosa, I.R. Assessment of the Pesticides Atrazine; Endosulfan Sulphate and Chlorpyrifos for Juvenoid-related Endocrine Activity Using Daphnia magna. Chemosphere. 2009; 76: 335-340.
    CrossRef
  22. Kumar D., Yadav D., Neelam. Monitoring of Organochlorine Pesticides Residues in Pumpkin (Cucurbita maxima), Brinjal (Solanum melongena), Cucumber (Cucumis   sativus), Ridge Gourd (Luffa aegyptiaca) and Apple Gourd (Praecitrullus fistulosus) Vegetables by Using QuEChERS Method. Asian Journal of Chemistry. 2019; 31(7): 1565-1568.
    CrossRef
  23. Bempah, C.K. and Donkor A.K. Pesticide residues in fruits at the market level in Accra Metropolis, Ghana, preliminary study.  Environmetal Monitoring Assessment. 2010; 175: 551-561.
    CrossRef
  24. Bempah C.K., Buah-Kwofie A., Denutsui D., Asomaning J. and Tutu A.O. Monitoring of Pesticide Residues in Fruits and Vegetables and Related Health Risk Assessment in Kumasi Metropolis, Ghana. Research Journal of Environmental and Earth Sciences. 2011; 3(6): 761-771.
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