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Ch. Ramamohana Rao et al., IJSIT, 2012, 1(1), 56-68




  QUALITATIVE AND QUANTITATIVE ANALYSIS OF FENVALERATE, AND
 METHYL PARATHION PESTICIDES IN MANGO AND GRAPES COLLECTED
                                            BY HPLC METHOD

                        CH.RAMAMOHANA RAO, L.CYRIL ARUN KUMAR

           Dept of Bio-Technology, AcharyaNagarjuna University, Nagrjunanagar, Guntur,A.P, India.


                                                  ABSTRACT
        A new HPLC method was developed for Analysis of FENVALERATE, AND METHYL PARATHION
PESTICIDES IN MANGO AND GRAPES. The method has maximum recoveryi.e. 99.0-100.0 %. The method was
applied for analysis of FENVALERATE, AND METHYL PARATHION in fruit samples.
Key words:FENVALERATE, METHYL PARATHION, HPLC Method, Pesticide, Recovery, Mango,Grapes.


                                              INTRODUCTION
        After green revolution the use of pesticides increased very rapidly for all crops i.e. food grains,
vegetables, fruits, cotton, tobacco. In Andhra Pradesh, Nuziveedu is famous for Mango exporting and
Hyderabad is famous for exporting of Grapes. In this area formers are using pesticides in huge quantity to
prevent pest. We analyzed few Mangos and Grapes fruit covers identification of Parathion-methyl,
Fenvalerate.

Parathion-methyl:

        Parathion-methyl   (1-6)   “Parathion-methyl", also known as methyl parathion or dimethyl parathion,
was also developed and is marketed for similar uses. It is a distinct compound with diminished toxicity. Some
trade names of parathion-methyl include Bladan M, Metaphos. As a pesticide, parathion is generally applied
by spraying. It is often applied to cotton, rice and fruit trees. The usual concentrations of ready-to-use
solutions are 0.05 to 0.1%. The chemical is banned for use on many food crops. Parathion acts on the
enzyme acetylcholinesterase, but indirectly. After being ingested by the parathion becomes oxidized
by oxidizes to give paraoxon, replacing the double bonded sulfur with oxygen.(2)



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        The phosphate ester is more reactive in organisms than the phosphorothiolate ester, as the
phosphorus atoms become much more electronegative Parathion is a cholinesterase inhibitor. It generally
disrupts the nervous system by inhibiting the acetylcholinesterase. It is absorbed via skin, mucous
membranes, and orally. Absorbed parathion is rapidly metabolized to paraoxon, as described above.
Paraoxon exposure can result in headaches, convulsions, poor vision, vomiting, abdominal pain,
severe diarrhea, unconsciousness, tremor, dyspnea, and finally lung-edema as well as respiratory arrest.
Symptoms of poisoning are known to last for extended periods of time, sometimes months. The most
common and very specific antidote is atropine in doses of up to 100 mg daily. Because atropine may also be
toxic, it is recommended that small frequently repeated doses be used in treatment. If human poisoning is
detected early and the treatment is prompt fatalities are infrequent. Insufficient oxygen will lead to cerebral
hypoxia and    permanent      brain    damage. Peripheral     neuropathy including paralysis is    noticed    as
late sequelae after recovery from acute intoxication. Parathion has been used for committing suicide and
deliberately poisoning other persons. It is known as "Schwiegermuttergift" in Germany. For this reason most
formulations contain a blue dye providing warning.

        Parathion has been used as a chemical weapon, most notably by the Selous Scouts during
the Rhodesian Bush War.(3) Based on animal studies, parathion is considered by the U.S. Environmental
Protection Agency to be a possible human carcinogen.(4) Studies show that parathion is toxic to fetuses, but
does not cause birth defects.(5) It is classified as a UNEP Persistent Organic Pollutant and WHO Toxicity Class,
"Ia, Extremely Hazardous".Parathion is very toxic to bees, fish, birds, and other forms of wildlife.(5) Parathion
can be replaced by many safer and less toxic alternatives.




                                  Figure 8.A:StructureofMethylParathion

Fenvalerate (7-16):
        Fenvalerate is an insecticide. It is a mixture of four optical isomers which have different insecticidal
activities. The 2-S alpha configuration is the most insecticidally active isomer. Fenvalerate consists of about



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23% of this isomer. Fenvalerate is an insecticide of moderate mammalian toxicity. In laboratory animals,
central nervous system toxicity is observed following acute or short-term exposure. Fenvalerate has
applications against a wide range of pests. Residue levels are minimized by low application rates. Fenvalerate
is most toxic to bees and fish. It is found in some emulsifiable concentrates, ULV, wettable powders, slow
release formulations, insecticidal fogs, and granules. It is most commonly used to control insects in food, feed,
and cotton products, and for the control of flies and ticks in barns and stables. Fenvalerate does not affect
plants, but is active for an extended period of time. Fenvalerate may irritate the skin and eyes on contact, and
is also harmful if swallowed.




                                     Figure 8.B: StructureofFenvalerate


                                      MATERIALS AND METHODS
2.1. Instrumentation:
        For quantitative estimation of Fenvalerate, Methyl Parathion in Fruit an isocratic peak HPLC
instrument with chromosil c18, c8 column, (100 mm x 4.6 mm, 5μ) (250 mm x 4.6 mm, 5μ), (150 mm x 4.6
mm, 5μ) was used. Theinstrument is equipped with a LC 20AT pump for solvent delivery and variable
wavelength programmable UV-Visible detector, SPD-10AVP. A 20μL Hamilton syringe was used for injecting
the samples. Data was analyzed by using PEAK software. Techcomp UV 2301UV-Visible spectrophotometer
(Hitach software) was used for spectral studies. Degassing of the mobile phase was done by using a Loba
ultrasonic bath sonicator. A Denverbalance was used for weighing of the materials.

2.2. Chemicals and Solvents:

        The reference standard of Fenvalerate was obtained from Aimco Pesticides Ltd, Mumbai. The
reference standard of Fenvalerate was obtained from Bhaskar Agro Chemicals Limited, Hyderabad.The fruit
samples were collected from the local fruit markets fruit tree forms, Acetonitrile, Methanol, Water used is
HPLC grade are purchased from Merck Specialties Private Limited, Mumbai, India. T.E.A of AR grade
purchased from local market.




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2.3 Sample collection:

        Fruit samples are collected from local market of Vijayawada, directly from fruit tree forms,
Hypermarkets. The samples are collected randomly from different shops, from each shop we are collected
average 6 fruits. In garden frits are collected from different trees randomly and different gardens.

2.4. The Mobile Phase:

        Two different suitable mobile phases are prepared individually for analysis of target Pesticides in
Fruits. The prepared mobile phases are sonicated up to 30 min, and filtered through 0.45 µ nylon filter paper.

2.5. Standard Solution of the Drug:

        For analysis of 1000 ppm stock solutions are prepared with reference standards of Fenvalerate,
Methyl Parathion pesticides with their mobile phases. From the stock solution calibration curves prepared to
estimate target pesticides.

2.6. Extraction of pesticides from fruits covers (17):

        20 g of fruit cover was collected from the sample. .The covers were kept into a cone flask and
thoroughlymixed with dichloromethane (30 ml) and sodium carbonate (15 g). Then the mixture was to
standing 12 hin the well-sealed cone flask. After that the mixture was filtered through filter paper and then
the tundishwas washed with dichloromethane. The filtered liquid phase was contained in an open watch
glass. Whendichloromethane was dried out, methanol (5 ml) wasadded to extract the DDVP. The extraction
was repeated twice with methanol (2 ml). These extractionswere mixed and diluted by methanol to 10 ml
thenfiltered for analysis.

3. Optimization of HPLC methods from Standard Methods:

        During HPLC method optimization, a systematic study on effect of various factors was performed by
varying one parameter at a time and keeping all other conditions constant. Method development consists of
selecting the appropriate wavelength and chromatographic conditions like stationary and mobile phase. The
following studies were conducted for this purpose.

3.1. Detection Wavelength:

        The proper wavelength was needed to determine maximum detector response. The first step was to
run a UV-VIS spectrum (from 190-320 nm) using an HPLC system equipped with the Photo Diode Array
Detector.



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3.2. Choice of Stationary Phase:

        In general, develop all methods with HPLC columns from the same vendor. The preferred brand of
HPLC column should be selected primarily based on the long term stability and lot-to-lot reproducibility.
Preliminary development trials have performed with octadecyl columns form different manufacturers with
different configurations.

3.3. Selection of the Mobile Phase:
        Liquid chromatography method development began with the optimizing mobile phase composition
and column type. The feasibility of several mixtures of solvent such as acetonitrile, water and methanol using
different buffers such as ammonium acetate, ammonium formate, acetic acid and formic acid with variable pH
range 3–6 was tested for complete chromatographic resolution.
        In order to get sharp peak and base line separation of the components, a number of experiments
were carried out by varying the composition of various solvents and its flow rate. Under isocratic conditions,
mixtures of solvents like methanol, water and Acetonitrile with and without different buffers indifferent
combinations were tested as mobile phase on a C18 stationary phase.

3.4. Flow Rate:

        Flow rate of the mobile phase was changed from 0.5 – 1.5 mL/min for optimum separation. A
minimum flow rate as well as minimum run time gives the maximum saving on the usage of solvents.

3.5. HPLC Conditions Optimization for Analysis of Methyl Parathion (18):
        For analysis of Methyl Parathion .in tissue samples, HPLC with UV-detector set at 225 nm was used,
with low sensitivity and specificity. So, HPLC with PDA detector is used to analysis ofMethyl Parathion. In this
study C18 reversed phase CHROMOSIL column was employed at 25C temperature Water and methanol PH
(5.3) as the mobile phase in 65:35 v/v ratio. The isocratic elution under the condition employed allows the
separation of Methyl Parathion, Good separation and peak shape was obtained at flow rate of 1.0 ml/min.




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   S.No                   Condition                                         Parameter
     1                   Mobile Phase                            Water and Methanol 65:35 (v/v)
     2                      Column                          Chromosil, C18 (4.6 mm, 100 mm) column


     3                    Wave length                                         225 nm
     4                     Flow rate                                        1.0 ml/Min
     5               Column temperature                                         25 c
     6                     Run time                                           10 min
     7                  Sample volume                                          20 µL
     8                         PH                                               5.3


                              Table 8.1:Chromatographic conditions of Methyl Parathion


3.5 HPLC Conditions Optimization for Analysis of Fenvalerate (19):

         For analysis of Fenvalerate, in tissue samples, HPLC with UV-detector set at 239 nm was used, with
low sensitivity and specificity. So, HPLC with U.V detector is used to analysis of Fenvalerate, In this study C18
reversed phase GEMINI column was employed at 30c temperature, Acetonitrile: Methanol, KH2PO4 (50:40:10
V/V/V)PH (6.8) as the mobile phase. The isocratic elution under the condition employed allows the separation
of Fenvalerate, Good separation and peak shape was obtained at flow rate of 1.0 ml/min.


          S.No                       Condition                                    Parameter
           1                        Mobile Phase                      Acetonitrile: methanol-potassium
                                                                    dehydrogenate phosphate (50:40:10)
           2                          Column                            GEMINI C18, 250 mm×4.6 µm
           3                        Wave length                                     239 nm
           4                         Flow rate                                    1.0 Ml/Min
           5                  Column temperature                                       30c
           6                         Run time                                         10 min
           7                     Sample volume                                         20 µL
           8                            PH                                              6.8


                                 Table 8.2:Chromatographic conditions of Fenvalerate




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        Figure 8.C:HPLC Chromatogram forMethylParathion




              Figure 8.D:HPLC Chromatogram forFenvalerate




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                                                              RESULTS
1. Calibration curve with standard:

        From the stock solutions different concentrations METHYL PARATHION (0.2ppm-1.2ppm)
FENVALERATE, (0.5ppm-3ppm) of standard pesticide solutions are injected in to HPLC at system suitable
condition what are optimized from standard procedures. the calibration curves are plotted between area of
peak and pesticide concentrations.


                  S.NO                           Standard concentration                     Peak Area
                                                          (ppm)
                    1                                         0.2                             2352
                    2                                         0.4                             4398
                    3                                         0.6                             6347
                    4                                         0.8                             8309
                    5                                         1.0                            10396
                    6                                         1.2                            12539
                    7                                Slope = 10288.57               Intercept = 161.2857




                                           Table8.3:Calibration table for MethylParathion


                               14000

                               12000

                               10000
                   peak area




                                8000

                                6000

                                4000

                                2000

                                   0
                                       0       0.2      0.4         0.6      0.8    1         1.2       1.4
                                                                    concentration



                                           Figure 8.E:Calibration curve Methyl Parathion


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S.NO     % OF           Fixed        Spiked         Total sample   Amount of        % of         % of
       RECOVERY        conc in       conc in       concentration   recovery       recovery      Average
                        ppm1         ppm1                                                     recovery
 1       50%             0.4           0.2                 0.6       0.599          99.83
 2      100%             0.4           0.4                 0.8       0.797          99.62        99.55
 3      150%             0.4           0.6                 1         0.992          99.2


                           Table 8.4:Recovery studies of Methyl Parathion




        S.NO                                 Parameter                        Concentration in ppm
         1                                         L.O.Q                              0.01
         2                                         L.O.D                             0.005


                     Table8.5:L.O.Q and L.O.D studies of Methyl Parathion




       S.NO               Standard concentration (ppm)                          Peak Area

        1                                    0.5                                  1927
        2                                    1.0                                  3496
        3                                    1.5                                  5221
        4                                    2.0                                  6798
        5                                    2.5                                  8506
        6                                    3.0                                  10024
        7                           Slope = 3323.714                    Intercept = -153.2857




                                 Table8.6:Calibration table for Fenvalerate




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                           12000

                           10000

                            8000

               peak area    6000

                            4000

                            2000

                               0
                                    0           0.5         1           1.5       2         2.5        3           3.5
                                                                        concentration



                                               Figure 8.F:Calibration curve Fenvalerate




S.NO     % OF                      Fixed          Spiked         Total sample         Amount of            % of           % of
       RECOVERY                    conc in        conc in        concetration           recovery      recovery           Average
                                   ppm1            ppm1                                                                  recovery
 1       50%                            1             0.5                1.5             1.496          99.73
 2      100%                            1             1                   2               1.97             98.5           99.27
 3      150%                            1             1.5                2.5             2.499             99.6


                                     Table 8.7: Recovery studies of Fenvalerate




        S.NO                                                Parameter                             Concentration in ppm
         1                                                      L.O.Q                                       0.07
         2                                                      L.O.D                                       0.03


                                            Table8.8:L.O.Q and L.O.D studies of Fenvalerate




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  S.NO          Location of Sample       Fruit sample     Concentration of Methyl            Concentration
                    collection                                Parathion µg/Kg             Fenvalerate, µg/Kg
    1                 Garden                Mango                13.64± 0.43                   7.38± 0.34
    2              Local market             Mango                10.65± 0.28                   6.39± 0.67
    3           Ready for exporting         Mango                   NDL                           NDL
    4             Reliance fresh            Mango                8.54± 0.55                    5.35± 0.28
    5                Spancer                Mango                7.63± 0.47                    4.99± 0.83
    6                 Garden                Grape                14.85± 0.34                   9.37± 0.09
    7              Local market             Grape                11.27± 0.50                   8.81± 0.64
    8           Ready for exporting         Grape                   NDL                           NDL
    9             Reliance fresh            Grape                8.63± 0.24                    7.67± 0.45
   10                Spancer                Grape                8.14± 0.12                    6.89± 0.68


                  Table8.9:Concentrations ofMethyl Parathion and Fenvalerate, in fruit cover samples


                                                     DISCUSSION
         Mango and Grapes are famous and very high nourishing fruits for all age people. Especially mangos
are famous in India. In Andhra Pradesh state Grapes are cultivating in around surroundings of Hyderabad.
The mango fruits are highly exporting from the city Nuzeveedu, Krishna district. But the main issue is the
presence of pesticide residues in fruit cover of these two fruits. Due to this problem the price of fruits is
decreasing in international market. And the fruits importing from India also banned in Singapore, Australia,
U.S, U.K. in order to prove this concept we analyzed fruit samples by H.P.L.C technique. The results are given
in Table.8.5.


         For analysis of Methyl Parathion we are developed a HPLC method with UV-detector at 225 nm, with
C18 reversed phase CHROMOSIL column, at 25C temperature, Water and methanol PH (5.3) as the mobile
phase in 65:35 v/v ratio, at flow rate of 1.0 ml/min. The recovery of this developed method is 99.55. We can
estimate the Methyl Parathion at very low level concentrations up to 0.07 ppm, we may detect the of Methyl
Parathion up to 0.03 ppm


         For analysis of Fenvalerate, in fruit samples, we developed a HPLC method with UV-detector at 239
nm, with C18 reversed phase GEMINI column, at 30c temperature and Acetonitrile: Methanol, KH2PO4
(50:40:10 V/V/V)PH (6.8) as the mobile phase, flow rate of 1.0 ml/min. With our method we recovered 99.27
Fenvalerate by standard addition method. L.OQ and L.OD values are 0.07 ppm, 0.03 ppm respectively.


         From above results we conformed that the sample has Methyl Parathion, Fenvalerate, in high


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Ch. Ramamohana Rao et al., IJSIT, 2012, 1(1), 56-68


concentration in samples which are collected directly from fruit forms. In Mangos Methyl Parathion is 13.64
µg/Kg, Fenvalerat is 7.38 µg/Kg, In Grapes Methyl Parathion is 14.85 µg/Kg, Fenvalerat is 9.37 µg/Kg But in
the exporting quality fruits there are no presence of our target pesticides. May be exporters taken care, or
followed any process to remove pesticide residues in fruit cover. In local fruit market we found Methyl
Parathion, Fenvalerate in high concentrations. i.e. Methyl Parathion is 10.65 µg/Kg, Fenvalerat is 6.39 µg/Kg
(In Mango ) Methyl Parathion is 11.27 µg/Kg, Fenvalerat is 9.37 µg/Kg (In Grapes). But in high per markets
we found target pesticids in less amount compare to local markets. In Reliance fresh i.e. Methyl Parathion is
8.54 µg/Kg, Fenvalerat is 5.35 µg/Kg (In Mango), Methyl Parathion is 8.63 µg/Kg, Fenvalerat is 7.67 µg/Kg
(In Grapes ). in Spencer i.e. Methyl Parathion is 7.63 µg/Kg, Fenvalerat is 4.49 µg/Kg(In Grapes), Methyl
Parathion is 8.14 µg/Kg, Fenvalerat is 6.89 µg/Kg (In Grapes).




                                                   REFERENCES


    1.   Fee, D. C, Gard, D. R.; Yang, C. (2005). "Phosphorus Compounds". Kirk-Othmer Encyclopedia of
         Chemical Technology. New York: John Wiley & Sons.
    2.   Metcalf, R. L. (2002). "Insect Control". Ullman’s Encyclopedia of Industrial Chemistry. New York:
         Wiley-VCH Verlag GmbH & Co. KGaA.
    3.   Moorcraft, Paul; McLaughlin, Peter (2008). The Rhodesian War: A Military History. Yorkshire: Pen &
         Sword. p. 106.
    4.   "Parathion". Integrated Risk Information System. U. S. Environmental Protection Agency. 26 January
         2007.
    5.   "Pesticide Information Profiles - Parathion". Extension Toxicology Network. Oregon State University.
         September 1993.
    6.   S. Kegley, B. Hill, S. Orme. "Parathion - Identification, toxicity, use, water pollution potential,
         ecological toxicity and regulatory information". Pesticide Action Network.
    7.   Mani U, Islam F, Prasad AK, et al. Steroidogenic alterations in testes and sera of rats exposed to
         formulated fenvalerate by inhalation. Hum ExpToxicol 2002;21:593 – 7.
    8.   Abd-el-Aziz MI, Sahlab AM, Abd-el-Khalik M. Influence of diazinon and deltamethrin on reproductive
         organs and fertility of male rats.DtschTierarztlWochenschr 1994, 101:230 – 2.
    9.   Hu JY, Wang SL, Zhao RZ, et al. Effects of fenvalerate on reproductive and endocrine systems of male
         rats. Natl J Androl 2002; 8:18 – 21.
    10. Tan LF, Wang SL. Advances in studies of male reproductive toxicity of pesticides. Natl J Androl 2004;
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    11. World Health Organization. WHO laboratory manual for the examination of human semen and


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                      IJSIT (www.ijsit.com), Volume 1, Issue 1, September-October 2012
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    sperm–cervical mucus interaction.4th ed. New York7 Cambridge Univ Press; 1999.
12. Kaneto M, Kishi K. Spermatogenic dysfunction and its evaluation bycomputer-assisted sperm
    analysis in the rat. Ann Rpts Shionogi ResLab 2003, 53:1 – 20.
13. Bian Q, Xu LC, Wang SL, et al. Study on the relation between occupational fenvalerate exposure and
    spermatozoa DNA dam age of pesticide factory workers. Occup Environ Med 2004;61:999 – 1005.
14. Sakkas D, Mariethoz E, Manicardi G. Origin of DNA damage inejaculated human spermatozoa. Rev
    Reprod 1999; 4:31 – 7.
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    spermiogenesis failure. Mol Hum Reprod1998;4:757 – 62.
16. Moore HDM, Akhondi MA. Fertilizing capacity of rat spermatozoa is correlated with decline in
    straight-line velocity measured by continuous computer-aided sperm analysis: epididymal rat
    spermatozoa from the proximal cauda have a greater fertilizing capacity in vitro than those from
    distal cauda or vas deferens. J Androl 1996; 17:50 – 60.
17. Toth GP, Wang SR, McCarthy H, et al. Effects of three male reproductive toxicants on rat
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18. High-performance liquid chromatographic assay of dichlorvos, isocarbophos and methyl parathion
    from plant leaves using chemiluminescence detection Guangming Huang, Jin Ouyang, Willy R.G.
    BaeyensYiping Yang, Chuanjiang Tao, AnalyticaChimicaActa 474 (2002) 21–29
19. Validated High Performance Liquid Chromatographic Method for Analysis of Fenvalerate Pesticide in
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    K.A. Bakar and Eltayeb E.M. Eid, American Journal of Applied Sciences, Volume 7, Issue 12Pages
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QUALITATIVE AND QUANTITATIVE ANALYSIS OF FENVALERATE, AND METHYL PARATHION PESTICIDES IN MANGO AND GRAPES COLLECTED BY HPLC METHOD

  • 1. Ch. Ramamohana Rao et al., IJSIT, 2012, 1(1), 56-68 QUALITATIVE AND QUANTITATIVE ANALYSIS OF FENVALERATE, AND METHYL PARATHION PESTICIDES IN MANGO AND GRAPES COLLECTED BY HPLC METHOD CH.RAMAMOHANA RAO, L.CYRIL ARUN KUMAR Dept of Bio-Technology, AcharyaNagarjuna University, Nagrjunanagar, Guntur,A.P, India. ABSTRACT A new HPLC method was developed for Analysis of FENVALERATE, AND METHYL PARATHION PESTICIDES IN MANGO AND GRAPES. The method has maximum recoveryi.e. 99.0-100.0 %. The method was applied for analysis of FENVALERATE, AND METHYL PARATHION in fruit samples. Key words:FENVALERATE, METHYL PARATHION, HPLC Method, Pesticide, Recovery, Mango,Grapes. INTRODUCTION After green revolution the use of pesticides increased very rapidly for all crops i.e. food grains, vegetables, fruits, cotton, tobacco. In Andhra Pradesh, Nuziveedu is famous for Mango exporting and Hyderabad is famous for exporting of Grapes. In this area formers are using pesticides in huge quantity to prevent pest. We analyzed few Mangos and Grapes fruit covers identification of Parathion-methyl, Fenvalerate. Parathion-methyl: Parathion-methyl (1-6) “Parathion-methyl", also known as methyl parathion or dimethyl parathion, was also developed and is marketed for similar uses. It is a distinct compound with diminished toxicity. Some trade names of parathion-methyl include Bladan M, Metaphos. As a pesticide, parathion is generally applied by spraying. It is often applied to cotton, rice and fruit trees. The usual concentrations of ready-to-use solutions are 0.05 to 0.1%. The chemical is banned for use on many food crops. Parathion acts on the enzyme acetylcholinesterase, but indirectly. After being ingested by the parathion becomes oxidized by oxidizes to give paraoxon, replacing the double bonded sulfur with oxygen.(2) 56 IJSIT (www.ijsit.com), Volume 1, Issue 1, September-October 2012
  • 2. Ch. Ramamohana Rao et al., IJSIT, 2012, 1(1), 56-68 The phosphate ester is more reactive in organisms than the phosphorothiolate ester, as the phosphorus atoms become much more electronegative Parathion is a cholinesterase inhibitor. It generally disrupts the nervous system by inhibiting the acetylcholinesterase. It is absorbed via skin, mucous membranes, and orally. Absorbed parathion is rapidly metabolized to paraoxon, as described above. Paraoxon exposure can result in headaches, convulsions, poor vision, vomiting, abdominal pain, severe diarrhea, unconsciousness, tremor, dyspnea, and finally lung-edema as well as respiratory arrest. Symptoms of poisoning are known to last for extended periods of time, sometimes months. The most common and very specific antidote is atropine in doses of up to 100 mg daily. Because atropine may also be toxic, it is recommended that small frequently repeated doses be used in treatment. If human poisoning is detected early and the treatment is prompt fatalities are infrequent. Insufficient oxygen will lead to cerebral hypoxia and permanent brain damage. Peripheral neuropathy including paralysis is noticed as late sequelae after recovery from acute intoxication. Parathion has been used for committing suicide and deliberately poisoning other persons. It is known as "Schwiegermuttergift" in Germany. For this reason most formulations contain a blue dye providing warning. Parathion has been used as a chemical weapon, most notably by the Selous Scouts during the Rhodesian Bush War.(3) Based on animal studies, parathion is considered by the U.S. Environmental Protection Agency to be a possible human carcinogen.(4) Studies show that parathion is toxic to fetuses, but does not cause birth defects.(5) It is classified as a UNEP Persistent Organic Pollutant and WHO Toxicity Class, "Ia, Extremely Hazardous".Parathion is very toxic to bees, fish, birds, and other forms of wildlife.(5) Parathion can be replaced by many safer and less toxic alternatives. Figure 8.A:StructureofMethylParathion Fenvalerate (7-16): Fenvalerate is an insecticide. It is a mixture of four optical isomers which have different insecticidal activities. The 2-S alpha configuration is the most insecticidally active isomer. Fenvalerate consists of about 57 IJSIT (www.ijsit.com), Volume 1, Issue 1, September-October 2012
  • 3. Ch. Ramamohana Rao et al., IJSIT, 2012, 1(1), 56-68 23% of this isomer. Fenvalerate is an insecticide of moderate mammalian toxicity. In laboratory animals, central nervous system toxicity is observed following acute or short-term exposure. Fenvalerate has applications against a wide range of pests. Residue levels are minimized by low application rates. Fenvalerate is most toxic to bees and fish. It is found in some emulsifiable concentrates, ULV, wettable powders, slow release formulations, insecticidal fogs, and granules. It is most commonly used to control insects in food, feed, and cotton products, and for the control of flies and ticks in barns and stables. Fenvalerate does not affect plants, but is active for an extended period of time. Fenvalerate may irritate the skin and eyes on contact, and is also harmful if swallowed. Figure 8.B: StructureofFenvalerate MATERIALS AND METHODS 2.1. Instrumentation: For quantitative estimation of Fenvalerate, Methyl Parathion in Fruit an isocratic peak HPLC instrument with chromosil c18, c8 column, (100 mm x 4.6 mm, 5μ) (250 mm x 4.6 mm, 5μ), (150 mm x 4.6 mm, 5μ) was used. Theinstrument is equipped with a LC 20AT pump for solvent delivery and variable wavelength programmable UV-Visible detector, SPD-10AVP. A 20μL Hamilton syringe was used for injecting the samples. Data was analyzed by using PEAK software. Techcomp UV 2301UV-Visible spectrophotometer (Hitach software) was used for spectral studies. Degassing of the mobile phase was done by using a Loba ultrasonic bath sonicator. A Denverbalance was used for weighing of the materials. 2.2. Chemicals and Solvents: The reference standard of Fenvalerate was obtained from Aimco Pesticides Ltd, Mumbai. The reference standard of Fenvalerate was obtained from Bhaskar Agro Chemicals Limited, Hyderabad.The fruit samples were collected from the local fruit markets fruit tree forms, Acetonitrile, Methanol, Water used is HPLC grade are purchased from Merck Specialties Private Limited, Mumbai, India. T.E.A of AR grade purchased from local market. 58 IJSIT (www.ijsit.com), Volume 1, Issue 1, September-October 2012
  • 4. Ch. Ramamohana Rao et al., IJSIT, 2012, 1(1), 56-68 2.3 Sample collection: Fruit samples are collected from local market of Vijayawada, directly from fruit tree forms, Hypermarkets. The samples are collected randomly from different shops, from each shop we are collected average 6 fruits. In garden frits are collected from different trees randomly and different gardens. 2.4. The Mobile Phase: Two different suitable mobile phases are prepared individually for analysis of target Pesticides in Fruits. The prepared mobile phases are sonicated up to 30 min, and filtered through 0.45 µ nylon filter paper. 2.5. Standard Solution of the Drug: For analysis of 1000 ppm stock solutions are prepared with reference standards of Fenvalerate, Methyl Parathion pesticides with their mobile phases. From the stock solution calibration curves prepared to estimate target pesticides. 2.6. Extraction of pesticides from fruits covers (17): 20 g of fruit cover was collected from the sample. .The covers were kept into a cone flask and thoroughlymixed with dichloromethane (30 ml) and sodium carbonate (15 g). Then the mixture was to standing 12 hin the well-sealed cone flask. After that the mixture was filtered through filter paper and then the tundishwas washed with dichloromethane. The filtered liquid phase was contained in an open watch glass. Whendichloromethane was dried out, methanol (5 ml) wasadded to extract the DDVP. The extraction was repeated twice with methanol (2 ml). These extractionswere mixed and diluted by methanol to 10 ml thenfiltered for analysis. 3. Optimization of HPLC methods from Standard Methods: During HPLC method optimization, a systematic study on effect of various factors was performed by varying one parameter at a time and keeping all other conditions constant. Method development consists of selecting the appropriate wavelength and chromatographic conditions like stationary and mobile phase. The following studies were conducted for this purpose. 3.1. Detection Wavelength: The proper wavelength was needed to determine maximum detector response. The first step was to run a UV-VIS spectrum (from 190-320 nm) using an HPLC system equipped with the Photo Diode Array Detector. 59 IJSIT (www.ijsit.com), Volume 1, Issue 1, September-October 2012
  • 5. Ch. Ramamohana Rao et al., IJSIT, 2012, 1(1), 56-68 3.2. Choice of Stationary Phase: In general, develop all methods with HPLC columns from the same vendor. The preferred brand of HPLC column should be selected primarily based on the long term stability and lot-to-lot reproducibility. Preliminary development trials have performed with octadecyl columns form different manufacturers with different configurations. 3.3. Selection of the Mobile Phase: Liquid chromatography method development began with the optimizing mobile phase composition and column type. The feasibility of several mixtures of solvent such as acetonitrile, water and methanol using different buffers such as ammonium acetate, ammonium formate, acetic acid and formic acid with variable pH range 3–6 was tested for complete chromatographic resolution. In order to get sharp peak and base line separation of the components, a number of experiments were carried out by varying the composition of various solvents and its flow rate. Under isocratic conditions, mixtures of solvents like methanol, water and Acetonitrile with and without different buffers indifferent combinations were tested as mobile phase on a C18 stationary phase. 3.4. Flow Rate: Flow rate of the mobile phase was changed from 0.5 – 1.5 mL/min for optimum separation. A minimum flow rate as well as minimum run time gives the maximum saving on the usage of solvents. 3.5. HPLC Conditions Optimization for Analysis of Methyl Parathion (18): For analysis of Methyl Parathion .in tissue samples, HPLC with UV-detector set at 225 nm was used, with low sensitivity and specificity. So, HPLC with PDA detector is used to analysis ofMethyl Parathion. In this study C18 reversed phase CHROMOSIL column was employed at 25C temperature Water and methanol PH (5.3) as the mobile phase in 65:35 v/v ratio. The isocratic elution under the condition employed allows the separation of Methyl Parathion, Good separation and peak shape was obtained at flow rate of 1.0 ml/min. 60 IJSIT (www.ijsit.com), Volume 1, Issue 1, September-October 2012
  • 6. Ch. Ramamohana Rao et al., IJSIT, 2012, 1(1), 56-68 S.No Condition Parameter 1 Mobile Phase Water and Methanol 65:35 (v/v) 2 Column Chromosil, C18 (4.6 mm, 100 mm) column 3 Wave length 225 nm 4 Flow rate 1.0 ml/Min 5 Column temperature 25 c 6 Run time 10 min 7 Sample volume 20 µL 8 PH 5.3 Table 8.1:Chromatographic conditions of Methyl Parathion 3.5 HPLC Conditions Optimization for Analysis of Fenvalerate (19): For analysis of Fenvalerate, in tissue samples, HPLC with UV-detector set at 239 nm was used, with low sensitivity and specificity. So, HPLC with U.V detector is used to analysis of Fenvalerate, In this study C18 reversed phase GEMINI column was employed at 30c temperature, Acetonitrile: Methanol, KH2PO4 (50:40:10 V/V/V)PH (6.8) as the mobile phase. The isocratic elution under the condition employed allows the separation of Fenvalerate, Good separation and peak shape was obtained at flow rate of 1.0 ml/min. S.No Condition Parameter 1 Mobile Phase Acetonitrile: methanol-potassium dehydrogenate phosphate (50:40:10) 2 Column GEMINI C18, 250 mm×4.6 µm 3 Wave length 239 nm 4 Flow rate 1.0 Ml/Min 5 Column temperature 30c 6 Run time 10 min 7 Sample volume 20 µL 8 PH 6.8 Table 8.2:Chromatographic conditions of Fenvalerate 61 IJSIT (www.ijsit.com), Volume 1, Issue 1, September-October 2012
  • 7. Ch. Ramamohana Rao et al., IJSIT, 2012, 1(1), 56-68 Figure 8.C:HPLC Chromatogram forMethylParathion Figure 8.D:HPLC Chromatogram forFenvalerate 62 IJSIT (www.ijsit.com), Volume 1, Issue 1, September-October 2012
  • 8. Ch. Ramamohana Rao et al., IJSIT, 2012, 1(1), 56-68 RESULTS 1. Calibration curve with standard: From the stock solutions different concentrations METHYL PARATHION (0.2ppm-1.2ppm) FENVALERATE, (0.5ppm-3ppm) of standard pesticide solutions are injected in to HPLC at system suitable condition what are optimized from standard procedures. the calibration curves are plotted between area of peak and pesticide concentrations. S.NO Standard concentration Peak Area (ppm) 1 0.2 2352 2 0.4 4398 3 0.6 6347 4 0.8 8309 5 1.0 10396 6 1.2 12539 7 Slope = 10288.57 Intercept = 161.2857 Table8.3:Calibration table for MethylParathion 14000 12000 10000 peak area 8000 6000 4000 2000 0 0 0.2 0.4 0.6 0.8 1 1.2 1.4 concentration Figure 8.E:Calibration curve Methyl Parathion 63 IJSIT (www.ijsit.com), Volume 1, Issue 1, September-October 2012
  • 9. Ch. Ramamohana Rao et al., IJSIT, 2012, 1(1), 56-68 S.NO % OF Fixed Spiked Total sample Amount of % of % of RECOVERY conc in conc in concentration recovery recovery Average ppm1 ppm1 recovery 1 50% 0.4 0.2 0.6 0.599 99.83 2 100% 0.4 0.4 0.8 0.797 99.62 99.55 3 150% 0.4 0.6 1 0.992 99.2 Table 8.4:Recovery studies of Methyl Parathion S.NO Parameter Concentration in ppm 1 L.O.Q 0.01 2 L.O.D 0.005 Table8.5:L.O.Q and L.O.D studies of Methyl Parathion S.NO Standard concentration (ppm) Peak Area 1 0.5 1927 2 1.0 3496 3 1.5 5221 4 2.0 6798 5 2.5 8506 6 3.0 10024 7 Slope = 3323.714 Intercept = -153.2857 Table8.6:Calibration table for Fenvalerate 64 IJSIT (www.ijsit.com), Volume 1, Issue 1, September-October 2012
  • 10. Ch. Ramamohana Rao et al., IJSIT, 2012, 1(1), 56-68 12000 10000 8000 peak area 6000 4000 2000 0 0 0.5 1 1.5 2 2.5 3 3.5 concentration Figure 8.F:Calibration curve Fenvalerate S.NO % OF Fixed Spiked Total sample Amount of % of % of RECOVERY conc in conc in concetration recovery recovery Average ppm1 ppm1 recovery 1 50% 1 0.5 1.5 1.496 99.73 2 100% 1 1 2 1.97 98.5 99.27 3 150% 1 1.5 2.5 2.499 99.6 Table 8.7: Recovery studies of Fenvalerate S.NO Parameter Concentration in ppm 1 L.O.Q 0.07 2 L.O.D 0.03 Table8.8:L.O.Q and L.O.D studies of Fenvalerate 65 IJSIT (www.ijsit.com), Volume 1, Issue 1, September-October 2012
  • 11. Ch. Ramamohana Rao et al., IJSIT, 2012, 1(1), 56-68 S.NO Location of Sample Fruit sample Concentration of Methyl Concentration collection Parathion µg/Kg Fenvalerate, µg/Kg 1 Garden Mango 13.64± 0.43 7.38± 0.34 2 Local market Mango 10.65± 0.28 6.39± 0.67 3 Ready for exporting Mango NDL NDL 4 Reliance fresh Mango 8.54± 0.55 5.35± 0.28 5 Spancer Mango 7.63± 0.47 4.99± 0.83 6 Garden Grape 14.85± 0.34 9.37± 0.09 7 Local market Grape 11.27± 0.50 8.81± 0.64 8 Ready for exporting Grape NDL NDL 9 Reliance fresh Grape 8.63± 0.24 7.67± 0.45 10 Spancer Grape 8.14± 0.12 6.89± 0.68 Table8.9:Concentrations ofMethyl Parathion and Fenvalerate, in fruit cover samples DISCUSSION Mango and Grapes are famous and very high nourishing fruits for all age people. Especially mangos are famous in India. In Andhra Pradesh state Grapes are cultivating in around surroundings of Hyderabad. The mango fruits are highly exporting from the city Nuzeveedu, Krishna district. But the main issue is the presence of pesticide residues in fruit cover of these two fruits. Due to this problem the price of fruits is decreasing in international market. And the fruits importing from India also banned in Singapore, Australia, U.S, U.K. in order to prove this concept we analyzed fruit samples by H.P.L.C technique. The results are given in Table.8.5. For analysis of Methyl Parathion we are developed a HPLC method with UV-detector at 225 nm, with C18 reversed phase CHROMOSIL column, at 25C temperature, Water and methanol PH (5.3) as the mobile phase in 65:35 v/v ratio, at flow rate of 1.0 ml/min. The recovery of this developed method is 99.55. We can estimate the Methyl Parathion at very low level concentrations up to 0.07 ppm, we may detect the of Methyl Parathion up to 0.03 ppm For analysis of Fenvalerate, in fruit samples, we developed a HPLC method with UV-detector at 239 nm, with C18 reversed phase GEMINI column, at 30c temperature and Acetonitrile: Methanol, KH2PO4 (50:40:10 V/V/V)PH (6.8) as the mobile phase, flow rate of 1.0 ml/min. With our method we recovered 99.27 Fenvalerate by standard addition method. L.OQ and L.OD values are 0.07 ppm, 0.03 ppm respectively. From above results we conformed that the sample has Methyl Parathion, Fenvalerate, in high 66 IJSIT (www.ijsit.com), Volume 1, Issue 1, September-October 2012
  • 12. Ch. Ramamohana Rao et al., IJSIT, 2012, 1(1), 56-68 concentration in samples which are collected directly from fruit forms. In Mangos Methyl Parathion is 13.64 µg/Kg, Fenvalerat is 7.38 µg/Kg, In Grapes Methyl Parathion is 14.85 µg/Kg, Fenvalerat is 9.37 µg/Kg But in the exporting quality fruits there are no presence of our target pesticides. May be exporters taken care, or followed any process to remove pesticide residues in fruit cover. In local fruit market we found Methyl Parathion, Fenvalerate in high concentrations. i.e. Methyl Parathion is 10.65 µg/Kg, Fenvalerat is 6.39 µg/Kg (In Mango ) Methyl Parathion is 11.27 µg/Kg, Fenvalerat is 9.37 µg/Kg (In Grapes). But in high per markets we found target pesticids in less amount compare to local markets. In Reliance fresh i.e. Methyl Parathion is 8.54 µg/Kg, Fenvalerat is 5.35 µg/Kg (In Mango), Methyl Parathion is 8.63 µg/Kg, Fenvalerat is 7.67 µg/Kg (In Grapes ). in Spencer i.e. Methyl Parathion is 7.63 µg/Kg, Fenvalerat is 4.49 µg/Kg(In Grapes), Methyl Parathion is 8.14 µg/Kg, Fenvalerat is 6.89 µg/Kg (In Grapes). REFERENCES 1. Fee, D. C, Gard, D. R.; Yang, C. (2005). "Phosphorus Compounds". Kirk-Othmer Encyclopedia of Chemical Technology. New York: John Wiley & Sons. 2. Metcalf, R. L. (2002). "Insect Control". Ullman’s Encyclopedia of Industrial Chemistry. New York: Wiley-VCH Verlag GmbH & Co. KGaA. 3. Moorcraft, Paul; McLaughlin, Peter (2008). The Rhodesian War: A Military History. Yorkshire: Pen & Sword. p. 106. 4. "Parathion". Integrated Risk Information System. U. S. Environmental Protection Agency. 26 January 2007. 5. "Pesticide Information Profiles - Parathion". Extension Toxicology Network. Oregon State University. September 1993. 6. S. Kegley, B. Hill, S. Orme. "Parathion - Identification, toxicity, use, water pollution potential, ecological toxicity and regulatory information". Pesticide Action Network. 7. Mani U, Islam F, Prasad AK, et al. Steroidogenic alterations in testes and sera of rats exposed to formulated fenvalerate by inhalation. Hum ExpToxicol 2002;21:593 – 7. 8. Abd-el-Aziz MI, Sahlab AM, Abd-el-Khalik M. Influence of diazinon and deltamethrin on reproductive organs and fertility of male rats.DtschTierarztlWochenschr 1994, 101:230 – 2. 9. Hu JY, Wang SL, Zhao RZ, et al. Effects of fenvalerate on reproductive and endocrine systems of male rats. Natl J Androl 2002; 8:18 – 21. 10. Tan LF, Wang SL. Advances in studies of male reproductive toxicity of pesticides. Natl J Androl 2004; 7:533 – 7. 11. World Health Organization. WHO laboratory manual for the examination of human semen and 67 IJSIT (www.ijsit.com), Volume 1, Issue 1, September-October 2012
  • 13. Ch. Ramamohana Rao et al., IJSIT, 2012, 1(1), 56-68 sperm–cervical mucus interaction.4th ed. New York7 Cambridge Univ Press; 1999. 12. Kaneto M, Kishi K. Spermatogenic dysfunction and its evaluation bycomputer-assisted sperm analysis in the rat. Ann Rpts Shionogi ResLab 2003, 53:1 – 20. 13. Bian Q, Xu LC, Wang SL, et al. Study on the relation between occupational fenvalerate exposure and spermatozoa DNA dam age of pesticide factory workers. Occup Environ Med 2004;61:999 – 1005. 14. Sakkas D, Mariethoz E, Manicardi G. Origin of DNA damage inejaculated human spermatozoa. Rev Reprod 1999; 4:31 – 7. 15. Tesarik J, Greco E, Cohen-Bacrie P. Germ cell apoptosis in men with complete and incomplete spermiogenesis failure. Mol Hum Reprod1998;4:757 – 62. 16. Moore HDM, Akhondi MA. Fertilizing capacity of rat spermatozoa is correlated with decline in straight-line velocity measured by continuous computer-aided sperm analysis: epididymal rat spermatozoa from the proximal cauda have a greater fertilizing capacity in vitro than those from distal cauda or vas deferens. J Androl 1996; 17:50 – 60. 17. Toth GP, Wang SR, McCarthy H, et al. Effects of three male reproductive toxicants on rat caudaepididymal sperm motion. ReprodToxicol 1992; 6:507 – 15. 18. High-performance liquid chromatographic assay of dichlorvos, isocarbophos and methyl parathion from plant leaves using chemiluminescence detection Guangming Huang, Jin Ouyang, Willy R.G. BaeyensYiping Yang, Chuanjiang Tao, AnalyticaChimicaActa 474 (2002) 21–29 19. Validated High Performance Liquid Chromatographic Method for Analysis of Fenvalerate Pesticide in Chilies by QuEChERS Extraction Cleanup and High Liquid Chromatography, Ahmed A. Altorshani, Nor K.A. Bakar and Eltayeb E.M. Eid, American Journal of Applied Sciences, Volume 7, Issue 12Pages 1587-1592 68 IJSIT (www.ijsit.com), Volume 1, Issue 1, September-October 2012