Murraya Koeingii a Protector Against Insecticide Wastes Leachates Induced Oxidative Stress in Drosophila Melanogaster Third Instar Larvae

DOI : 10.17577/IJERTV8IS120325
Download Full-Text PDF Cite this Publication

Text Only Version

 

Murraya Koeingii a Protector Against Insecticide Wastes Leachates Induced Oxidative Stress in Drosophila Melanogaster Third Instar Larvae

Babita Saroha1

1 Research Scholar, Department of Biotechnology, University Institute of Engineering and Technology (UIET), Maharshi Dayanand University,

Rohtak (Haryana) India

Veer Bhan3*

Anand Kumar2

2 Assistant Professor,

Department of Chemistry, SGRR (PG) College, Dehradun (Uttarakhand) India

3Assistant professor, Department of Biotechnology, University Institute of Engineering and Technology (UIET), Maharshi Dayanand University, Rohtak (Haryana) India

Abstract:- The current study was assessed to know whether an aqueous extract of the leaves of Murraya Koenigii (Curry leaves) has the ability to protect against insecticide wastes leachates induced oxidative stress in the third instar larvae of Drosophila melanogaster (Oregon K). The study shows that the curry leaves dose dependently protected the biomarkers of tissue damage, oxidative stress and antioxidant enzymes from getting altered in the larvae following treatment with leachates. The results specified that the aqueous curry leaf extract (CuLE) might have protected the larvae from leachates induced oxidative stress through antioxidant mechanism(s).

Keywords: Oxidative stress; Biomarkers; Antioxidant; Leachates; Murraya Koenigii

Abbreviations: CuLE: Curry leaves; ROS: Reactive oxygen species; M.koeingii: Murraya koeingii; SOD: Superoxide dismutase ; CAT: Catalase ; LPO: Lipid peroxidation

  1. INTRODUCTION

    Free radicals or activated oxygen has been connected to environmental stresses in animals and appears to be a common participant in most of the degenerative conditions in eukaryotic cells. Oxidative stress is the redox state resulting from an imbalance between the generation and detoxification of reactive oxygen species (ROS) (Wang and Michaelis, 2010). Under carefully controlled situations, ROS function as important physiological regulators of intracellular signaling pathways (Finkel, 2011). However, the overloaded amount of ROS causes damage to cells by oxidizing cellular biomolecules, including nucleic acids, proteins and lipids (Lobo et al., 2010). Summarizing the earlier conducted large body of studies, on different environmental toxicants i.e. metals, pesticides, solvents, industrial and municipal runoffs, in different model systems revealed increased oxidative stress caused by these xenobiotics (Dorts et al., 2009b; Singh et al., 2009; Bhargav et al., 2008; Siddique et al., 2008; Avci et al., 2005; Pandey et al., 2003; Livingstone et al., 2000). From previous studies it was confirmed that industrial soil

    samples from few industrial sites in Rohtak contained heavy metal concentration (Pb, Zn, Cu, Ni, Cd) that exceed the calculated worldwide mean of unpolluted soil, indicating high level of pollution on the site of industries due to solid wastes dumped (Annu, 2016, 2015; Urmilla, 2015) but in vivo study has not been done yet.

    Antioxidants are substances, when present in small quantities prevent the oxidation of cellular organelles by minimizing the damaging effects of ROS and RNS (Reactive Nitrogen species). Under normal healthy conditions, a balance is maintained between oxidative stress and antioxidant requirements. Antioxidant enzymes like catalase (CAT), superoxide dismutase (SOD), metal sequestering proteins forms the endogenous antioxidant defenses. However under pathological conditions or during radiation injury, stress and pollution etc. the balance is lost and excessive supplementation of antioxidants is necessary. During this study we used a very common plant Murraya Koeingii (Curry leaf) as an antioxidant to ameliorate the effect of leachates on Drosophila larvae. This plant has been reported to have anti-oxidative, cytotoxic, antimicrobial, antibacterial, antiulcer, positive inotropic and cholesterol reducing activities (Rahman MM et al., 2005; Kesari et al., 2005; Shrinivasan et al., 2005). In a study on pharmaceutical wastes leachates it was found that CuLE act as a potent antioxidant to enhance climbing ability affected by oxidative stress (Saroha et al., 2019).

    The present study was designed using Drosophila melanogaster as an animal model. Drosophila melanogaster commonly known as fruit fly, is one of the well-studied model organism, has several advantages over other animal models, as it has shorter life cycle (10-12 days at 25oC), high fecundity (females lay 600 eggs in a life time), easy to handle and fewer number of chromosomes (3 pairs of autosomes and 1 pair of sex chromosomes) with 75% similarity with human disease genes. Using fruit fly, we demonstrate the toxic potential of insecticides industrial

    leachates on third instar larvae of Drosophila and antioxidant property of M. koenigii.

  2. MATERIAL AND METHODS
  1. Collection and Extraction of Murraya koeingii Murraya Koeingii leaves were collected dried and grinded into powder and a known 250 g of dried leaves were extracted with distilled water at 45°C for 3 h filtered through whattman No. 1 filter paper and evaporated to get a crude extract.
  2. Collection of soil and leachate preparation Randomized sampling technique was used for collection of industrial soil and solid wastes for the assessment of toxicity (Houk, 1992). Control soil samples were collected from the institute only. Five random samples were collected and made single. For the preparation of 10% leachates, leachates from soil and the industrial solid wastes at three different pH viz, 7.00 (in MilliQ water, neutral), 4.93 (5.7ml glacial acidic acid + 64.3ml IN NaOH

    + 930ml MilliQ water; low acidic) and 2.88 (5.7ml glacial acetic acid + 994.3ml MilliQ water; highly acidic) Toxicity Characteristics Leachate Procedure (TCLP) [Method-1310; USEPA, 1990] was used. The leachates (prepared at three different pHs) were referred to as N, M and H, respectively.

  3. Biochemical markers study

    Newly emerged larvae (22 ± 2 hr) collected from synchronized egg collections were transferred to food vials containing different concentrations of the leachates prepared from industrial waste and soil at different pHs and CuLE and allowed to grow for 96±2 hr. Study is divided in four groups as mentioned below:

    Group 1 Control (Standard diet)

    Group 2 Leachates treated

    Group 3 Standard diet along with CuLE

    Group 4 Leachates treated along with CuLE concentrations

    1. Effects of CuLE on leachates induced oxidative stress

      For the biochemical study, prepared plant extract were used to ameliorate the effects of industrial leachates on drosophila larvae. Newly hatched larvae were allowed to feed on industrial leachates (0.5%, 1%, 2 %) and plant extract (4 g/l and 6 g/l) till third instar larvae emerges. Third instar larvae were collected and washed and homogenized in PBS pH 7.4 and centrifuged for 10 minute supernatant thus obtained was used to determine, lipid peroxidation (LPO), the activity of antioxidant enzymes (SOD and Catalase).

    2. Measurement of Lipid Peroxidation (Okhawa et al., 1979)

      The amount of LPO was measured by measuring Thiobarbituric acid reactive substances in larvae. Reaction mixture consisted of tissue homogenate, 10% (w/v) sodium dodecyl sulfate, 0.8% thiobarbituric acid, 20% (v/v) acetic acid (pH 3.5). Absorbance was taken at 532 nm and expressed as malondialdehyde equivalents.

    3. Measurement of SOD activity (Marklund 1974)

      It was determined by measuring the inhibition of pyrogallol autoxidation. Reaction mixture consisted of 2 mM pyrogallol, tissue homogenate, 0.1 M tris-HCl buffer (pH 8.2). Absorbance was measured for 3 minutes at 420 nm. Activity was expressed as enzyme units required to inhibit 50% pyrogallol autoxidation.

    4. Measurement of Catalase (Aebi 1974)

Catalase activity was analyzed by quantitating the rate of H2O2 decomposition by the enzyme by adding 1% (v/v) H2O2 to reaction mixture containing tissue homogenate and

0.05 M phosphate buffer (pH 7). Absorbance was observed for 3 minute at 240 nm and expressed as moles of H2O2 decomposed/min/mg protein.

    1. Measurement of Total protein content (Lowry 1951)

      Protein content was measured by Lowry method by taking BSA as standard.

    2. Statistical analysis

The data are represented as Mean±S.E. Statistical differences at P<0.05 between groups were analyzed by Two-way analysis of variance (ANOVA) followed by Dunnetts multiple comparision test using Graphpad prism 8 software.

III. RESULT AND DISCUSSION

The present study aims to establish that aqueous CuLE has the potential to protect D.melanogaster against leachates induced oxidative stress. Industrial solid wastes leachates were found to have contrary effects on the exposed organisms as apparent by deviations in oxidative stress markers. Murraya extract has been characterized to be full of alkaloids, polyphenols, flavonoids and chlorophyll. Plants are used as a source of antioxidant and alternative medicines in various models against oxidative stress (Tachibana et al., 2001; Ningappa et al., 2008; Menezes et al., 2013).

A significant ROS generation and MDA was observed in the exposed larvae P<0.05.

A

A

 

12

10

8

6

4

2

0

Control IN 0.5% IN 1% IN 2% IM 0.5% IM 1% IM 2% IH 0.5% IH 1% IH 2%

Groups

6 B

5

4

3

2

1

0

Control 4G CuLE 6G CuLE IH 1% + 4

G/L CuLE

IH 1% + 6 G/L CuLE

IH 2% + 4 G/L CuLE

IH 2% + 6 G/L CuLE

Figure 1 MDA level. Values are Mean ± S.E A) insecticide leachates B) Plants treated and insecticide leachates exposed

Malondialdehyde (MDA) oxidatively modified molecules is well-thought-out to be a marker of oxidative damage (Ali et al., 2004; Paragasam et al., 2006). Lipids are attacked by ROS by free radical chain reaction mechanism to produce lipid peroxidation products. MDA is the lipid peroxidation product produced mostly in oxidative stress conditions.

A significant increase in MDA level was observed in larvae exposed to leachates (P<0.05 vs. Control) Figure1 (A). When larvae were supplemented with CuLE they showed 40 % to 52% decrease in MDA level in larvae exposed to leachates (Figure 1(B). At low concentrations, of leachates (0.5%) larvae shows nonsignificant effects on MDA level with P>0.05.

0.9 A

Units/min/mg protein

Units/min/mg protein

 

0.8

0.7

0.6

0.5

0.4

0.3

0.2

0.1

0

Groups

0.4

Units/min/mg protein

Units/min/mg protein

 

0.35

0.3

0.25

0.2

0.15

0.1

0.05

0

B

Control 4 g/l CuLE 6 g/l CuLE IH 1% + 4 IH 1% + 6 IH 2% + 4 IH 2% + 6

G/L CuLE

Groups

G/L CuLE

G/L CuLE

G/L CuLE

Figure 2 SOD level values are Mean ± S.E A) insecticide leachates B) Plants treated and industrial leachates exposed

At highest concentration and acidic pH leachates evoke significant (P<0.05) 1.07 and 1.85 fold increase in SOD activity exposed to insecticide leachates Figure 2 (A). When provided CuLE a significant P<0.001 upto 55% decrease in SOD enzyme activity was observed Figure 2 (B).

The major antioxidant enzyme is catalase consisting of heme as the prosthetic group. Molecular oxygen and water

is formed in the presence of NADH which acts as cofactor for enzyme activation from H2O2.. Acidic industrial leachates exposure significantly increased the catalase activity by 1.31 and 1.46 fold in drosophila larvae P<0.001. About 31% decrease in catalase activity was observed in larvae supplemented with CuLE along with insecticide leachates. SOD and CAT are responsible to scavenge superoxide anion and hydrogen peroxide.

70 A

CAT activity

(micomoles

H2O2/min/mg protein

CAT activity

(micomoles

H2O2/min/mg protein

 

60

50

40

30

20

10

0

Groups

45 B

CAT activity

(micomoles H2O2/min/mg protein

CAT activity

(micomoles H2O2/min/mg protein

 

40

35

30

25

20

15

10

5

0

Control 4 G CuLE 6 G CuLE IH 1% + 4 IH 1% + 6 IH 2% + 4 IH 2% + 6

G/LCuLE

Groups

G/LCuLE G/L CuLE G/L CuLE

Figure 3 Catalase activity Values are Mean ± S.E A) insecticide leachates B) plants treated and industrial leachates exposed

A previous study on industrial leachates indicates induction of biochemical stress markers in D. melanogaster against complex mixture (Siddique et al., 2007). Increase in the activities of SOD and CAT in the exposed organisms is an effort to reduce the induced damage. SOD and CAT activities remain unaltered in the groups provided with CuLE and in leachates exposed group they protect from getting altered. The protection may be due to the ability of CuLE to reduce the accumulation of free radicals produced

following industrial leachates. Figure 4 shows total protein content in control, leachates exposed and plant extract treated larvae. Proteins are found in large quantity in biological systems and its can be taken as indicator of toxicity (Davies, 2005). Leachates exposed reveals significant 53% to 55% decline in protein content P<0.05 as compared to control larvae. Change in protein content level in larvae and its inflection by CuLE was recorded.

A

7

6

5

4

3

2

1

0

A

7

6

5

4

3

2

1

0

control IN 0.5 IN 1

IN 2 IM 0.5 IM 1

Groups

IM 2 IH 0.5 IH 1 IH 2

control IN 0.5 IN 1

IN 2 IM 0.5 IM 1

Groups

IM 2 IH 0.5 IH 1 IH 2

9

8

B
7
6
5
4
3
2
1
0
control 4 G 6 G IH 0.5% IH 0.5% IH 1% + IH 1% + IH 2% + IH 2% +
CuLE CuLE +4 G +6 CuLE 4 G/L 6 G/L 4 G/L 6 G/L
CuLE CuLE CuLE CuLE CuLE
Groups

Total protein content (mg/ml

Total protein content (mg/ml

 

Total protein content (mg/ml)

Total protein content (mg/ml)

 

Figure 4: Total protein content, values are Mean ± S.E A) Protein content in Insecticide leachates B) Protein content in plant extract treated and leachates exposed

At highest concentration of CuLE protein content evoke to 56% and in larvae exposed to insecticide leachates. Statistically significance: P<0.001 and P<0.05 shows significant increase compared to groups exposed to leachates. However the aqueous CuLE seem to possess an ability to increase protein content probably by scavenging the reactive oxygen species or by chelating the heavy metal or by both. With increase in concentration of CuLE in food medium the increase in oxidative stress decreased until a point of concentration afterward no such effect was observed may be due to absorption threshold of CuLE, it could be because hiher concentration may not get absorbed completely.

The content of total anti-oxidant activity of M. koenigii leaves was found highest (2691mol of Ascorbic acid/ gm) amongst all green leafy vegetables (The Wealth of India) but there in vivo study in Drosophila has not been done so far. Experiments conducted on animals indicated that Pb is both genotoxic (Shaik et al., 2006) and carcinogenic (Fowler et al., 1994), Ni (Haugen et al., 1994)

and Cd (Elinder and Jarup, 1996) are carcinogenic, Cu generated free radicals when present in free form and produces ROS that causes damage to biomolecules like DNA, protein, and lipid (Galaris and Evangelou, 2002).

We finally hypothesize that the changes in biochemical parameters and physiological parameters are somehow affected by leachates induction. Secondly we observed that

  1. koeingii protect against induced oxidative stress.

    REFERENCES

    1. Aebi H (1974) Catalase in Bergmeyer Hans Ulrich, 5th Edition, Methods of enzymatic analysis, Academic press Incorporated, New York,USA. 273-278.
    2. Ali M, Parvez S, Pandey S, Atif F, Kaur M, Rehman H, Raisuddin S (2004) Fly ash leachate induces oxidative stress in freshwater fish Channa punctata (Bloch). Environ. Int. 30: 933 938.
    3. Annu, Garg A, Urmila (2016) Co-Relation and Variability of Metal in Surface Soil of Rapidly Industrialized Area of Rohtak,

      District. Journal of Chemical and Pharmaceutical Research. 8(5):155-163.

    4. Annu, Urmilla, Garg A (2015) Variation of heavy metal accumulation with physiochemical Properties of industrial soil of Rohtak city, Haryana. International journal of science, engineering and technology. 3(1): 333-340.
    5. Avci A, Kacmaz M, Durak I (2005) Peroxidation in muscle and liver tissues from fish in acontaminated river due to a petroleum refinery industry. Ecotoxicol. Environ. Saf. 60: 101-105.
    6. Bhargav D, Pratap Singh M., Murthy RC, Mathur N, Misra D, Saxena DK, Kar Chowdhuri D (2008) Toxic potential of municipal solid waste leachates in transgenic Drosophila melanogaster (hsp70-lacZ): hsp70 as a marker of cellular damage. Ecotoxicol. Environ. Saf. 69: 233-245.
    7. Chattopadhyay A, Biswas S, Bandyopadhyay D, Sarkar C, Datta AG (2003) Effect of isoproterenol on lipid peroxidation and antioxidant enzymes of myocardial tissue of mice and protection by quinidine. Mol Cell Biochem; 245:43-49.
    8. Davies MJ ( 2005) The oxidative environment and protein damage, Biochem. Biophys. Acta. 1703:93109.
    9. Dorts J, Silvestre F, Tu HT, Tyberghein AE, Phuong NT, Kestemont P (2009) Oxidative stress, protein carbonylation and heat shock proteins in the black tiger shrimp, Penaeus monodon, following exposure to endosulfan and deltamethrin. Environ. Toxicol. Pharmacol. 28: 302-310.
    10. Elinder CG, Jarup L (1996) Cadmium exposure and health risks: recent findings. Ambio. 25(5):370-373.
    11. Finkel T (2011) Signal transduction by reactive oxygen species. J Cell Biol. 194:715.
    12. Fowler BA, Kahng MW, Smith DR (1994) Role of Lead binding Proteins in Renal Cancer. Environ. Health. Perspect 102(suppl. 3):115-116.
    13. Galaris D, Evangelou A (2002) The role of oxidative stress in mechanisms of metal induced carcinogenesis. Oncology Hematology. 93-103.
    14. Haugen A, Maehle L, Mollerup S, Rivedal E, Ryberg D (1994) Nickel-induced alterations in human renal epithelial cells. Environ. Health Perspect. 102(suppl.3):117-118.
    15. Houk VS (1992) The genotoxicity of industrial wastes and effluents. Mutat Res 277:91138.
    16. Kesari AN, Gupta RK, Watal G(2005) Hypoglycemic Effects of Murraya koenigii on Normal and AlloxanDiabetic Rabbits. Journal of Ethanopharmacolgy, 97:247-251.
    17. Livingstone DR., Mitchelmore CL, O’Hara SC, Lemaire P, Sturve J, Forlin L (2000b) Increased potential for NAD(P)H- dependent reactive oxygen species production of hepatic subcellular fractions of fish species with in vivo exposure to containment. Mar. Environ.Res 50:57-60.
    18. Lobo V, Patil A, Phatak A, Chandra N (2010) Free radicals, antioxidants and functional foods: impact on human health.

      Pharmacogn Rev. 4:118126

    19. Lowry OH, Rosenbrough NJ, Farr AA, Randall RJ (1951) Protein measurement with the Folin Phenol reagent. J. Biol. Chem. 193:265275.
    20. Markund S, Markund G (1974) Involvement of the superoxide anion radical in the autoxidation of pyragallol and a convenient assay for superoxide dismutase. Eur J Biochem; 47:469-474.
    21. Menezes Patrício Santos CC de, Salvanodori MS, Mota VG, Costa LM, Almeida AAC de, Oliveira GAL de, Costa JP, Freitas

      de RM, Almeida RN de (2013) Antinociceptive and antioxidant activities of phytol in vivo and in vitro models, Neurosci. J.1. 1 9.

    22. Ningappa MB, Dinesha R, Srinivas L (2008) Antioxidant and free radical scavenging activities of polyphenol-enriched curry leaf (Murraya koenigii L.) extracts, Food Chem. 106:.720728.
    23. Ohkawa H, Ohishi N, Yagi K (1979) Assay for lipid peroxides in animal tissues by thiobarbituric acid reaction. Anal. Biochem. 95:351358.
    24. Pandey S, Parvez S, Sayeed I, Haque R., Bin-Hafeez B, Raisuddin S (2003) Biomarkers of oxidative stress: a comparative study of river Yamuna fish Wallago attu (Bl. & Schn.). Sci. Total Environ. 309:105-115.
    25. Rahman MM, Gray AI (2005) A benzoisofuranone derivative and carbazole alkaloids from Murraya koenigii and their antimicrobial activity. Phytochemistry. 66:1601-1606.
    26. Saroha B, Kumar A and Bhan V (2019). Antioxidant response of Murraya koeingii in moderating locomotive impairment in Drosophila melanogaster following Pharmaceutical wastes leachates. International Journal of Research in Advent Technology. 7(3):1057-1065.
    27. Shaik AP, Sankarv S, Reddy SC, Das PG, Jamil K (2006) Lead- induced genotoxicity in lymphocytes from peripheral blood samples of humans: In vitro studies. Drug Chem. Toxicol. 29:111-124
    28. Shrinivasan K (2005) Plant foods in the management of diabetes mellitus: spices as beneficial antidiabetic food adjuncts. Int. J. Food Sci. Nutr. 56(6): 399-414.
    29. Siddique HR, Gupta SC, Mitra K, Bajpai VK, Mathur N, Murthy RC, Saxena DK, Kar Chowdhuri D (2008) Adverse effect of tannery waste leachates in transgenic Drosophila melanogaster: role of ROS in modulation of Hsp70, oxidative stress and apoptosis. J. Appl. Toxicol. 28: 734748.
    30. Siddique HR, Gupta SC, Mitra K, Murthy RC, Saxena DK

      ,Chowdhuri DK (2007) Induction of biochemical stress markers and apoptosis in transgenic Drosophila melanogaster against complex chemical mixtures: role of reactive oxygen species.Chem.Biol.Interact.169:171188.

    31. Singh MP, Reddy MM, Mathur N, Saxena DK, Chowdhuri DK (2009) Induction of hsp70, hsp60, hsp83 and hsp26 and oxidative stress markers in benzene, toluene and xylene exposed Drosophila melanogaster: Role of ROS generation. Toxicol. Appl. Pharmacol. 235: 226-243.
    32. Tachibana Y, Kikuzaki H, Lajis N.H, Nakatani N (2001) Antioxidative activity of carbazoles from Murraya koenigii leaves, J. Agric. Food Chem. 49: 55895594.
    33. The Wealth of India (1988).A Dictionary of Indian Raw Materials and Industrial Products
    34. U.S. Environmental Protection Agency (USEPA) (1990) Test methods for evaluating solid waste, Toxicity Characteristic Leaching Procedure (TCLP). Method-1310, SW-846,USEPA, Washington, DC.
    35. Urmilla, Annu, Garg A (2016) Determination of heavy metals concentration in road side soil of Rohtak, Haryana, India. International journal of science, engineering and technology 3(1): 341-346.
    36. Wang X and Michaelis EK (2010) Selective neuronal vulnerability to oxidative stress in the brain. Front Aging Neurosci 2:12.

Leave a Reply