malathion resistance in musca domestica (diptera: muscidae) in district sargodha, pakistan

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  • 7/28/2019 Malathion resistance in Musca domestica (Diptera: Muscidae) in district Sargodha, Pakistan

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    Malathion resistance in Musca domestica(Diptera: Muscidae) in district

    Sargodha, Pakistan

    Sajida Naseem1, Hafiz Muhammad Tahir1, Shafaat Yar Khan1, Rabia Yaqoob1, Azhar

    Abbas Khan2, Muhammad Mohsin Ahsan1, Muhammad Arshad1, Arif Muhammad Khan3

    & Zahid Abbas Malik3.

    1. Department of Biological Sciences, University of Sargodha, Pakistan.2. Department of Entomology, University College of Agriculture,

    University of Sargodha, Pakistan.

    3. National Institute for Biotechnology and Genetic Engineering,Faisalabad, Pakistan.

    Corresponding author: [email protected]

    ABSTRACT

    The present study was undertaken to assess the resistance status ofMusca domestica

    against malathion in district Sargodha. We also compared the activities of Esterases,

    Glutathione S-transferases and Monooxygenases in malathion resistant and susceptible

    flies. For the study flies were collected from three different localities i.e., Rehman Pura,

    Sultan Colony and Chak No, 75-A, SB. Flies from all studied populations were found

    resistant to the tested concentrations of malathion. The activities of esterases among

    resistant flies were inhibited in all populations. However, the activities of GST and

    Monooxygenases were significantly higher among resistant flies compared to susceptible

    flies.We concluded from the study that higher level of GST and Monooxygenases in the

    malathion treated flies indicate the involvement of these enzymes in the malathion

    resistance. As the high level of melathion resistance is recorded in the flies from all studied

    populations, so it is recommended that malathion shouldnt be used any more for control ofhouseflies in the area.

    Keywords:Musca domesctica, Esterases, GST and Monooxygenases

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    INTRODUCTION

    Houseflies (Diptera: Muscidae) are one of the major public health pests through the

    world (Cetin et al., 2006). Although various tactics are being used to manage theirpopulation but the use of insecticides is common one. However, due to repetitive sequential

    use of the same insecticides or same mode of action, houseflies has developed resistance to

    the insecticides all over the world (Marcon et al., 2003; Shono and Scott, 2003; White et

    al., 2007). The mechanisms involved for insecticide resistance in insects may include

    increased detoxification or metabolism of the toxicants (Taylor and Feyereisen, 1996; Liu

    and Yue, 2000), decreased target site sensitivity (Soderlund, 2005) and decreased rate of

    cuticular penetration (Plapp, 1976; Oppenoorth, 1984). Increased metabolic detoxification

    is considered one of the important mechanisms for the development of insecticide

    resistance in houseflies (Taylor and Feyereisen, 1996; Scott, 1999; Liu and Yue, 2000;

    Soderlund, 2005). Detoxification enzyme-based resistance is due to enhanced levels or

    modified activities of esetrases, glutathione S- transferases (GST) or monooxygenases

    (Patil et al., 1996; Hemingway, 2000).

    Esterases are mainly involved in detoxification of carbamates, organophosphates

    and to a limited extent in metabolism of pyrethroid (Hemingway and Ranson, 2000). These

    enzymes break the ester bond by using water molecule. Esterases cause insecticide

    resistance in two ways, either by metabolism of very restricted range of insecticides

    containing a common ester bond or by rapid-binding and slow turnover i.e., sequestration

    (Herath et al., 1987).

    Glutathione S-transferases are multifunctional enzymes which catalyze the

    conjugation of reduced glutathione with lipophilic compounds having reactive electrophilic

    centers. The resultant products thus formed are more water soluble and easily excretable

    from the cell (Booth et al., 1961; Boyland and Chasseand, 1969; Habig et al., 1974). These

    enzymes posses a wide range of substrate specificities (Enayati et al., 2005). Glutathione S-

    transferases also protect the tissues from the oxidative damage and oxidative stress (Pickett

    and Lu, 1989; Enayati et al., 2005). Insects GSTs are involved in metabolism of

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    organophophate, organochlorines and pyrethroid groups (Grant and Matsumura., 1989;

    Ranson et al., 1997).

    Monooxygenases act by binding with molecular oxygen and receive electrons fromNADPH and results in formation of water (Berge et al., 1998; Li et al., 2007). These

    enzymes metabolize insecticides through hydroxylation, epoxidation, dehalogenation,

    peroxidation, ester oxidation and nitrogen and thioether oxidation (Wilkinson, 1976; Sono

    et al., 1996). Monooxygenases are mainly involved in the metabolism of pyrethroids and to

    a lesser extent in the detoxification of organophosphates and carbamates (Feyereisen,

    1999).

    The present study was undertaken to assess the resistance status ofM. domectica

    against malathion, to estimate and compare the activities of insecticide detoxifying

    enzymes (i.e., Esterases, Glutathione S-transferases and Monooxygenases) between

    malathion treated and control and fed and unfedM. domestica.

    MATERIALS AND METHODS

    Sampling

    Flies were collected from three different localities of district Sargodha, Punjab,

    Pakistan (i.e., Sultan Colony, Rehman Pura and Chak No. 75-A, SB) by using sweep net.

    Collected flies were released in glass jars (12 cm long and 10 cm wide).

    The mouth of each jar was covered with mesh cloth and brought to the laboratory in the

    Department of Biological Sciences, University of Sargodha. Only the adult flies of almost

    same size were used in the study.

    Residual bioassays

    Residual bioassays at the recommended field dose (2.28 mg/ml), half field dose

    (1.14 mg/ml) and double field dose (4.56 mg/ml) were performed to find out resistant

    population ofMusca domestica. For this purpose sixty flies were randomly selected and

    divided into control and experimental groups (n=30 in each group, 15 males and 15

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    females). Both groups were fed up to the satiation level on mixture of water, thick paste of

    condensed milk and sugar. The experimental group was exposed to malathion impregnated

    filter paper for one hour while control group to the filter paper impregnated in distilled

    water. After one hour of exposure, flies were transferred to clean jars. The mortality was

    recorded after every four hours till 24 hours. Sugar water (10%) was provided to the flies

    throughout the experimental period (Kaufman et al., 2010). The residual bioassays were

    replicated thrice.

    Biochemical estimation of insecticide detoxifying enzymes

    For the biochemical estimation of enzymes resistant flies obtained from bioassay

    experiment were selected and frozen at -20C for 30 minutes in order to make them

    immobilize. Later on their legs, wings and abdomens were removed and the rest of the

    body of each fly was homogenized in 600 l of phosphate buffer (100 mM, PH 7.0)

    containing 0.01% (w/v) of Triton X-100. This crude homogenate was centrifuged at

    13000rpm for five minutes at 4C. The supernatant was collected and used as enzyme

    source for biochemical estimation of non-specific esterases ( esterases), Glutathione-S-

    transferases (GSTs) and Monooxygenases. Confirmed susceptible population was taken as

    control for comparison. Enzymes activities of male and females and fed and unfed flies

    were also compared.

    Estimation of non-specific esterases

    To measure the activity of non-specific esterases method of Asperen (1962) was

    followed. Beta naphthyl acetate was used as substrates. The reaction mixture contained 60

    l homogenate, 60 l substrate solutions (0.1 M) and 1440 l phosphate buffer (100 mM).

    The reference solution of the reaction mixture contained 60 l substrate solution and 1500

    l phosphate buffer. These mixtures were incubated for 30 minutes at 37C. When

    incubation time was over one ml mixture of 1% Fast Blue B salt and 5% sodium dodecyl

    sulphate (SDS) in the ratio 2:5 was added to stop the reaction. After 15 minutes these

    solutions were transferred to 4 ml cuvettes and optical density was recorded at the

    wavelength of 545 nm by using spectrophotometer (UV-1700). Optical density of reference

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    was subtracted from the optical density of solution containing supernatant. The resulting

    optical densities (OD) were compared with standard curves to convert the absorbance to

    product concentrations. The enzyme activities were expressed as n-mol of product

    formed/min/mg of protein.

    Estimation of Glutathione-S-transferases

    The activity of Glutathione S-trasferases towards 1-chloro-2,4-dinitrobenezene

    (CDNB) was estimated according to the method of Habig et al (1974). The reaction mixture

    comprised of 100 l 1.0 mM reduced Glutathione, 50 l 1.0 mM 1-chloro-2, 4-

    dinitrobenzene (CDNB) and 2.5 ml phosphate buffer (100 mM, PH 7.0) and 50 l of

    supernatant. Reference solution for reaction mixture contained 50 l 1.0mM CDNB, 2.5 ml

    phosphate buffer (100 mM, PH 7.0) and 100 l 1.0 mM reduced Glutathione. The

    absorbance was measured at 340 nm after five minutes of the reaction. Absorbance values

    were converted to units of concentration using a molar extinction coefficient () of 9.6 mM

    cm-1 for CDNB-GSH conjugate. The activity was calculated as:

    CDNB-GSH conjugate = AB\S (increase in 5 min) x 2.7 x 1000

    formed in nM /mg protein /min 9.6 x 5 x protein in mg

    Estimation of Monooxygenases

    Vulule et al. (1999) was consulted to determine the activity of monooxygenases.

    Reaction mixture comprised of 100 l of homogenate, 1 ml of 3,3, 5,5- Tetramethyl

    benzidine (TMBZ) solution [TMBZ solution was made by dissolving 0.01 g TMBZ in five

    ml ethanol and 15 ml 0.25 M sodium acetate buffer (PH 5.0)], 500 l of 0.625 M potassium

    phosphate buffer (PPB) atpH 7.0 and 150 l of 3% hydrogen peroxide. Reference solution

    for reaction mixture contained one ml TMBZ, 600 l 0.625 M potassium phosphate buffer

    (PPB) at pH 7.0 and 150 l 3% hydrogen peroxide. After 10 minutes readings were

    recorded at the wavelength of 620 nm. The quantity of monooxygenases was calculated

    using the standard curve of cytochrome c.

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    Statistical analyses

    Kolmogorov-Smirnov test was used to analyze the normal distribution of the data.

    Parametric tests were applied on normally distributed data. For comparison of activities of

    different enzymes in control and insecticide treated groups ofM. domestica, two samples

    T-test was applied. T-test was also used to compare the activities of enzymes in fed and

    unfed flies. All analyses were performed by using Minitab Software (Version 14.1).

    RESULTS

    Flies from all three populations showed resistance against all tested concentrations

    of malathion (Table 1). There was no mortality among the fed females belonging in any of

    the three populations exposed to half field rate (1.14 mg/ml) or field rate (2.28 mg/ml) after

    24 hours. At double field rate (4.56 mg/ml) the mortality was 6.6% in the flies collected

    from the Sultan Colony and Chak No, 75-A, SB and 13.3% in the flies captured from

    Rheman Pura. In the starved females exposed to half field rate and field rate of malathion,

    there was 6.6% mortality. At double field rate the mortality was 20 % in Sultan Colony and

    Rheman Pura, while 13.3% in Chak No, 75-A, SB. No mortality was observed in control

    groups (Table 1).

    Fed male flies from all three localities showed no mortality at half field rate of

    malathion (Table 2). The mortality was 6.6% and 13.3% at field rate and double field rate

    respectively. Among starved males the mortality was 6.6% at half field rate and field rate of

    malathion and 20% at double field rate in Sultan Colony and Rheman Pura. The mortality

    was 13.3% among flies of Chak No, 75-A, SB at double field rate. Again no mortality was

    recorded in control groups (Table 2).

    Estimation Insecticide detoxifying enzymes

    The activity of esterases was inhibited among three populations (both in males

    and females) but significant inhibitory effect was recorded in Rehman Pura population

    (Table 3 and 4). Significantly higher activity of GST was observed in malathion treated

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    males and females of Sultan Colony and Chak No, 75-A, SB compared to control groups.

    The activity was also higher in treated flies of Rehman Pura population but didnt differ

    statistically from control groups. The activity of Monooxygenases was also significantly

    higher in treated flies of all populations compared to control flies.

    The comparison of activity of esterases, GST and Monooxygenases among fed

    and starved malathion treated flies is depicted in the Figures 1-3. Significantly higher

    activity of esterases was recorded in fed flied of Rehman Pura population. In the

    population of Sultan Colony and Chak No, 75-A, SB the difference in activity of

    esterases between fed and unfed flies was statistically non significant (Figure 1). Similarly

    significantly higher activity of Glutathione-S-transferases was recorded in fed flies of

    Sultan Colony and Chak No, 75-A, SB populations (in both males and females) (Figure 2).

    No difference in activity of Monooxygenases was recorded among starved and fed flies

    (Figure 3).

    DISCUSSION

    Results of present study revealed that all three populations were found resistance to

    all tested concentrations of malathion. Resistance in houseflies against malathion has also

    been reported in different parts of the world, like in Malaysia by Bong and Zairi (2010), in

    Philippines by Kano et al. (1977) and in Ankara by Sisli et al. (1983). Tang et al. (1994)

    had also reported malathion resistance in houseflies. However, Ahmed and Khalequzzaman

    (2001) had found the malathion to be less toxic to houseflies in Bangladesh. Sargodha is an

    agriculture area of Pakistan and there is an excessive application of insecticides in the area

    which might have caused cross resistance in the flies. Bong and Zairi (2010) reported that

    resistance in housefly increased with increase in insecticide usage.

    Biochemical and molecular methods help us to detect the possible resistance

    mechanism in insects. Our findings regarding estimation of enzymes revealed that the

    activity of beta esterase was not increased in Malathion treated groups. In Rehman Pura

    population significant decrease in activity of beta esterase was recorded in treated flies

    compared to control group. These results were close to findings of Taskin and Kence

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    (2004), who recorded the low activity of non specific esterases in malathion resistant strain

    of housefly compared to control group. Campbell et al. (1998) recorded 25-50% less

    activity of general esterase activity in organophosphate resistant strains than susceptible

    strain. The reason for this lower activity of esterases is explained by mutant ali-esterase

    hypothesis.

    High activity of GST in malathion treated flies was recorded in the present study.

    These results are somewhat similar to those reported by Franciosa and Berge (1995) who

    found high activity of GSTs in malathion resistant housefly. These results are also similar

    to results reported by Taskin and Kence (2004). High activity of GSTs in OP resistant

    housefly strain has also been reported by Motoyama et al. (1980). Increase in activity of

    monooxygenases was recorded in malathion treated flies of all three populations. Evidence

    for increase in activity of monooxygenases against organophosphates in houseflies has also

    been reported in different areas of the world (Kasai and Scott, 2000).

    In present study we didnt recorded mark differences in the insecticide tolerance

    among fed and starved flies. Although the high activity GSTs was recorded in fed

    malathion treated flies compared to starved malathion treated groups of different

    populations. The reason for this difference in activity of GSTs couldnt be justified in

    present study. In order to get more reliable results further research would be required

    including investigating other possible mechanism of resistance. We concluded from our

    results that resistance in Sultan Colony and Chak No.75-A SB populations against

    malathion may be due to elevated activities of monooxygenases and GSTs. However, in

    Rehman Pura population high activity of monooxygenases correlates with malathion

    resistance. We also concluded, as high level of resistance is recorded in all populations of

    Sargodha so malathion shouldnt be used any more for control of housefly in the area.

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    Table 1: Percent mortality in fed and unfed female flies of different populations exposed

    with

    different malathion concentrations.

    Concentrations

    (mg/ml) of

    Malathion

    %Mortality in fed females after

    24 hours of exposure

    %Mortality in unfed females

    after 24 hours of exposure

    Sultan

    Colony

    Rehman

    Pura

    Chak

    No. 75-

    A, SB

    Sultan

    Colony

    Rehman

    Pura

    Chak

    No. 75-

    A, SB

    0.00 (Control) 0 0 0 0 0 0

    1.14 0 0 0 6.6 6.6 6.6

    2.28 0 0 0 6.6 6.6 6.6

    4.56 6.6 13.3 6.6 20 20 13.3

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    Table 2: Percent mortality in fed and unfed male flies of different populations exposed with

    different malathion concentrations.

    Concentrations

    (mg/ml) of

    Malathion

    %Mortality in fed males after 24

    hours of exposure

    %Mortality in unfed males after

    24 hours of exposure

    Sultan

    Colony

    Rehman

    Pura

    Chak

    No. 75-A, SB

    Sultan

    Colony

    Rehman

    Pura

    Chak

    No. 75-A, SB

    0.00 (Control) 0 0 0 0 0 0

    1.14 0 0 0 6.6 6.6 6.6

    2.28 6.6 6.6 6.6 6.6 6.6 6.6

    4.56 13.3 13.3 13.3 20 20 13.3

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    Table 3: Activity of esterases, Glutathione-S-transferases and Monooxygenases in

    control and malathion treated groups of male houseflies.

    Test populations

    esterases(mM/min/mg of

    protein)

    (MeanS.E)

    Glutathione-S-transferases (nM/mg

    of protein/min)

    (MeanS.E)

    Monooxygenases(g/min/mg of

    protein)

    (MeanS.E)

    Sultan Colony

    Control 83.711 348.4 13025

    Malathion treated 72.96.0 61.37.4 41361

    P-value 0.391 0.028

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    Table 4: Activity of esterases, Glutathione-S-transferases and Monooxygenases in

    control and malathion treated groups of female houseflies.

    Test populations

    esterases(mM/min/mg of

    protein)

    (MeanS.E)

    Glutathione-S-transferases (nM/mg

    of protein/min)

    (MeanS.E)

    Monooxygenases(g/min/mg of

    protein)

    (MeanS.E)

    Sultan Colony

    Control 104.515 28.74.3 15947

    Malathion treated 92.59.1 58.110 362.640

    P-value 0.505 0.034 0.005

    Rehman Pura

    Control 274.618 12.902.3 92.672

    Malathion treated 17319 18.321.6 315.060

    P-value 0.003 0.068 0.008

    Chak No. 75-A,

    SB

    Control 84.37.3 10.953.3 19071

    Malathion treated 60.49.4 23.83.1 47077

    P-value 0.059 0.012 0.018

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    Figure 1. Activity of beta esterase among fed and unfed Malathion treated males (a) andfemales (b).

    (a) Males (b) Females

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    Figure 2. Activity of GST among fed and unfed Malathion treated males (a) and females

    (b).

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    Figure 3. Activity of monooxygenases among fed and unfed Malathion treated males (a)

    and females (b).

    (a) Males (b) Females