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Research Detail

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Md. Sultan Ahmed*
Division of Entomology, Bangladesh Agricultural Research Institute, Joydebpur, Gazipur-1701, Bangladesh

Md. Arifur Rahman
Division of Entomology, Bangladesh Agricultural Research Institute, Joydebpur, Gazipur-1701, Bangladesh

Mohammad Dalower Hossain Prodhan
Division of Entomology, Bangladesh Agricultural Research Institute, Joydebpur, Gazipur-1701, Bangladesh

Md. Wahiduzzaman Akon
Division of Entomology, Bangladesh Agricultural Research Institute, Joydebpur, Gazipur-1701, Bangladesh

Afroza Begum
Division of Entomology, Bangladesh Agricultural Research Institute, Joydebpur, Gazipur-1701, Bangladesh

The present study was undertaken to detect and quantify the leftover residue of Fenvalerate and Acephate in beans and tomatoes and comparison between the detected residue levels with Maximum Residue Limit (MRL) set by FAO/WHO. Two supervised field trials (one for Fenvalerate and another for Acephate) were carried out sprayed with the field dose of Fenvalerate (1.0ml/L of water) and Acephate (1.0gm/L of water). Samples were collected at 0, 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11, 12, 13, 14 and 15 days after spray. The leftover residue of Fenvalerate was detected up to 14 DAS, of which up to 3 DAS the quantities of residue were above MRL (1 ppm) in both the vegetables (bean, tomato). This insecticide remained 0.601-0.035 ppm residue in beans and 0.443-0.014 ppm in tomatoes which were below MRL at 4 to 14 DAS. The high amount of Acephate was detected for a longer period than Fenvalerate and it was found up to 14 DAS in which MRL values (0.5 ppm) were found above up to 9 DAS with 0.623 ppm in tomato and 0.928 ppm in the bean. Samples of 10, 11, 12, 13 and 14 DAS of Acephate contained residues 0.289-0.032 ppm in bean and 0.465-0.029 ppm in tomato which were below MRL. At 15 DAS, no residue was detected. Therefore, beans and tomatoes can be harvested safely at 4 days after spraying for Fenvalerate and 10 days after spraying for Acephate.

  Insecticides; Residue; Degradation; DAS; MRL; Hyachinth bean; Tomato
  Pesticide analytical laboratory and experimental field of Entomology Division, Bangladesh Agricultural Research Institute, Joydebpur, Gazipur
  00-00-2011
  00-00-2012
  Resource Development and Management
  Waste, Tomato, Hyacinth bean

The detection, identification, and quantification of pesticides in food are becoming the public interest. But very few references are available on the presence of pesticides in vegetables in Bangladesh (Khatoon et al., 2004). Considering these circumstances, the present study was undertaken to assess the amount and degradation rate of the leftover residue of two frequently used insecticides in hyacinth bean and tomato. 

The study was conducted in the pesticide analytical laboratory and experimental field of Entomology Division, Bangladesh Agricultural Research Institute, Joydebpur, Gazipur during 2011-12 seasons. The standard for Fenvalerate and Acephate was obtained from Sigma-Aldrich Laborchemikalien, Gmbh P O Box-100262 D30918, Seelze, Germany via Bangladesh Scientific Pvt. Ltd. Dhaka, Bangladesh. Standards of both insecticides contained 99.6% purity. Marketable sizes of hyacinth bean and tomato were collected from two different supervised field trials at 0, 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11, 12, 13, 14 and 15 days after spray (DAS) which were sprayed with Fenvalerate @1.0 ml/L of water and Acephate @1.0gm/L of water. The formulated products of those were Fenfen 20EC and Asataf 75SP. The purity of formulated insecticides was tested in the laboratory and found to be 100% pure. 

2.1. Extraction and separation Field collected samples (250g) were grounded thoroughly with the meat grinder (Handmixer M-122, Bamix, Switzerland). A sub-sample of 20g was taken into a wide mouth jar then 100 ml of hexane was added to it. Sodium sulphate (Na2SO4) was also added with the sample until the water was removed from the sample. The mixture was then macerated with a high-speed homogenizer (Ultraturax, IKA T18 basic, Germany) for 2 minutes. The homogenized material was then poured into 250 ml conical flask and placed into the shaker (Orbital Shaking Incubator, Rexmed, Sweden) for 12hrs continuous shaking. After shaking, the slurry was filtered through a Buchner funnel with suction. The flask and filter cakes were rinsed with 25 ml of hexane each. The filtrate was then transferred into 250 ml round bottom flask and was dried to 5 ml by evaporation using a rotary vacuum evaporator (Laborota-4001, Heidolph, Germany). The concentrated filtrate was then transferred into 500 ml separatory funnel making 10 ml in volume. Around 20 ml methanol was added with 10 ml filtrate and shaked vigorously for 5 minutes. After shaking, the separatory funnel was set on a stand and kept undisturbed for 5 minutes. Then the clear part of the solution from the bottom of the separatory funnel was collected in a vial which was then centrifuged at 1200 rpm for 5 minutes (Laboratory Centrifuges, Sigma-3K30, Germany). After centrifuge, the supernatant was collected for injection in GC. 

2.2. Detection and Quantification of pesticide residue in samples The concentrated extracts were subjected to analysis by GC-2010 (Shimadzu). For Acephate FTD (Flame Thirm ionized Detector) and for Fenvalerate ECD (Electron Capture Detector) were used. The capillary column used in FTD was ATTM-1, length 30m, Inner Diameter (ID) 0.25mm and film thickness 0.25µm and in case of ECD it was Optima 1 and length, ID and film thickness was same. Nitrogen was used as a carrier and made up gas in ECD and in FTD it was Helium. 

Prior to the injection of the sample extract, standard solutions of different concentrations of both pesticide groups were prepared and injected with the above instrument parameters. The samples were calibrated (retention time, peak area etc.) against three to four pointed calibration curves of a standard solution of the concerned pesticide. Each peak was characterized by its retention time. Sample results were expressed in ppm automatically by the GC software which represented the concentration of the final volume injected. From this value the actual amount of pesticide residue present in the sample was determined by using the following formula:

Residue in the sample (ppm) = Conc. obtained in injected volume (ppm) X Quantity of final volume (L) / Amount of sample taken (kg)

  Asian Australas. J. Biosci. Biotechnol. 2016, 1 (2), 284-290
  
Funding Source:
1.   Budget:  
  

The degradation rate of Acephate was found slower in tomato and hyacinth bean and faster in both the vegetables for Fenvalerate. Therefore, Fenvalerate was likely to be the most suitable insecticide for the vegetables which would be harvested at the shortest period of time having a withholding period of 4 DAS but in the case of Acephate, it was 10 DAS. Acephate has a higher waiting period with 10 DAS which could not ensure the safe use in a short time harvested vegetables. The findings of the study will help farmers, researchers, consumers and stakeholders to undertake activities for safe food production and processing. 

  Journal
  


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