submitted for the award of the degree of doctor of...
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THESIS
STUDIES ON THE PESTICIDE CONTAMINATION
IN FOOD COMMODITIES AND THEIR RESIDUAL
TOXICITY; AND TOOLSIN VIVO IN SILICO
SUBMITTED FOR THE AWARD
OF THE DEGREE OF
Doctor of philosophyIn
biosciences
INTEGRAL UNIVERSITY,
LUCKNOW, INDIA
DEPARTMENT OF BIOSCIENCES
By
Ashutosh Kumar SrivastavaM.Sc. (Environmental Science)
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Established Under the Integral University Act 2004 (U.P. Act No.9 of 2004)
Approved by University Grant Commission
Phone No.: +91(0522) 2890812, 2890730, 3296117, 6451039, Fax No.: 0522-2890809
Kursi Road, Lucknow-226026 Uttar Pradesh (INDIA)
To Whomsoever It May Concern
This is to certify that Mr. Ashutosh Kumar Srivastava has carried out the
research work presented in the thesis entitled “Studies on the Pesticide
Contamination in Food Commodities and their Residual Toxicity; In vivo and
In silico tools” for the award of the degree of Doctor of Philosophy (Ph.D.) in
Department of Biosciences, Faculty of Applied Sciences, from Integral University,
Lucknow, India under my supervision. It is also certify that:
(i) the thesis embodies the original work of the candidate and has not been
earlier submitted by him or any other candidate elsewhere for any degree,
(ii) the candidate worked under me for the prescribed period,
(iii) the thesis fulfills the requirements of the norms and standards prescribed
by the Integral University, Lucknow.
______________________
Signature of Supervisor
Dr. Mohtashim Lohani Associate Professor
Department of Biosciences,
Faculty of Applied Sciences
Integral University, Lucknow
Date:
Place: Lucknow
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To Whomsoever It May Concern
This is to certify that the thesis titled “Studies on the Pesticide Contamination in
Food Commodities and their Residual Toxicity; In vivo and In silico tools”
submitted to Department of Biosciences, Faculty of Applied Sciences, Integral
University, Lucknow, Uttar Pradesh-India for the fulfillment of the award of
degree of Doctor of Philosophy (Ph. D) embodies the original research work
carried out by Mr. Ashutosh Kumar Srivastava, CSIR-SRF, Pesticide Toxicology
Division, CSIR-Indian Institute of Toxicology Research, Lucknow, under my
supervision. To the best of our knowledge and belief, the data presented in the
thesis have neither been presented previously nor been under consideration for the
award of any other degree or diploma to the candidates or anybody else.
_______________________________
Signature of Co-supervisor
Dr. L. P. Srivastava
Co-Supervisor
Senior Principal Scientist & Head
Pesticide Toxicology Division
CSIR-Indian Institute of Toxicology
Research, Lucknow, Uttar Pradesh –India
Date:
Place: Lucknow
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DECLARATION
I hereby declare that the thesis titled “Studies on the Pesticide
Contamination in Food Commodities and their Residual Toxicity; In vivo
and In silico Tools” embodies the original work carried out by me under the
supervision of Dr. Mohtashim Lohani, Associate Professor, Department of
Biosciences, Faculty of Applied Sciences, Integral University, Lucknow and
co-supervision of Dr. L. P. Srivastava, Senior Principal Scientist, Pesticide
Toxicology Laboratory, Council of Scientific and Industrial Research- Indian
Institute of Toxicology Research (CSIR-IITR), Lucknow (U.P.), India.
Date: (Ashutosh Kumar Srivastava)
Place:
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CONTENTS
Particulars Page No.
Acknowledgement i-ii
Preface iii-iv
List of Abbreviations and Symbols v-ix
List of Tables x-xii
List of Figures xiii-xv
Chapter 1- Introduction 1-7
Chapter 2- Review of Literature 8-26
Chapter 3- Materials and Methods 27-47
Chapter 4- Results and Discussion 48-68
Tables 69-100
Figures 101-109
Chapter 5- Summary and Conclusion 110-116
Strength 117
References 118-132
List of Publications
133
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i
Acknowledgement
First and foremost I would like to acknowledge the good providence of Almighty God
and His replica around me, i.e., my mentors. I am extremely indebted to God that He has given me
the strength and encouragement to undertake and complete this work and hope that His gracious
blessings will continue to be showered on me in all my endeavors.
A journey is easier when you travel together. Interdependence is certainly more
valuable than independence. This thesis is the result three years of my work whereby I have been
accompanied and supported by many people. It is a pleasant aspect that I got the opportunity
expresses my gratitude to all of them.
My foremost thanks’ goes to my supervisor Dr. Mohtashim Lohani, Associate Professor
of the Biosciences, Faculty of Applied Sciences, Integral University, Lucknow, without his
concern support this dissertation would not being completed. I thank him for his encouragement
throughout the period and his valuable advices for completing of this thesis. I appreciate his vast
knowledge and skills in many areas and thankful for accepting me as his student.
I would like to express my deep sense of gratitude to my Co-supervisor, Dr. L.P.
Srivastava, Senior Principal Scantiest & Head of Pesticide Toxicology Laboratory, CSIR-Indian
Institute of Toxicology Research, Lucknow, Council of Science and Industrial Research under
whose leadership I have conducted all experiment included in this thesis. His expertise,
understanding, knowledge and patience have made me to compile and finalize my Ph D thesis. His
valuable feedback has greatly contributed to this dissertation.
I am thankful to Dr. K.C. Gupta, Director, IITR, Lucknow, for providing me the
necessary Laboratory facilities. I am extremely thankful to the Honorable Vice Chancellor, Prof.
Syed Waseem Akhtar and Registrar, Dr. Irfan Ali Khan, Integral University, Lucknow, for
providing an opportunity to registered myself in such a prestigious University for getting the
highest professional degree i.e., Ph.D.
I thank my RDC members, Prof. T. Usmani (Pro-Vice Chancellor), Dr. Mohd. Rizwan
Baig (Examination Controller) and Dr. Abdul Rehman Khan (Dean, Faculty of Biosciences) for
their helpful suggestions and comments during my progress report presentations.
I also wish to convey my regards to Dr. A. K. Srivastava, Head, Department of
Biosciences, Faculty of Applied Sciences, Integral University, Lucknow, for conducting the
regular presentation of my research work, and suggestions to improve the scientific quality of
entire thesis.
Every special thanks goes out to Dr. R.B. Raizada, Scientist-F (Retd.) & Head of
Pesticide Toxicology Laboratory, Indian Institute of Toxicology Research, Lucknow, Council of
Science and Industrial Research (CSIR). His overly enthusiasm and integral view on research and
his mission for providing “only high quality work and not less” I can’t forget his help and guidance
toward my thesis.
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ii
I would like to convey my sincere thanks to Drs. Ashwani Kumar, P. Kakkar,
K.R.P. Singh, Y. Shukla, A.K. Srivastava, R.C. Murty, V.P. Sharma, A.B Pant, D.C. Purohit,
Dhirendra Singh, S.C., Burman, C. Keshavechndran, D.K. patel, M.K.R Mudiam, Rakesh Kumar,
M.K. Srivastava, Pradeep Kumar and B.P. Chwoudhary CSIR-IITR, Lucknow, for extending
their support, suggestion and encouragements.
I cannot adequately express in words my gratitude to my friends Dr. Abhinav
Srivastava and Dr. Manoj Kumar Pathak for their boosting encouragement, moral support, timely
help during pesticide residue analysis and providing multidirectional support. Sincere advices and
funny moments shared with them are unforgettable.
Few names are there, who were instrumental all through the completion of this
task and otherwise also made my perineal stay in Lucknow, as sweet memories of my life. These
Lieutenants of my army are: Aditya Sarangi, Sachin Tripathi, Upasana Kapoor, Satyajeet Rai,
Abhishekh Singh, Amit Srivastava, Shivpoojan, Ambrish Verma, Moh. Fareed, Ravindra
Chaudhary, Ankur Srivastava, Anoop Verma, Sapna Yadav, Swati Sachdev, Ravi saxena, Amit
Kalada and my sweetest bhaiya, Ajay Srivastava.
The technical support extended by R.P. Singh, S.P., Dhruve, K.P., Singh K.P.,
Gupta, Syamla Das, Pradeep Kumar and Pramod Srivastava is also acknowledged.
Sincere thanks to the officials of RPBD Section, Animal house, Library and
Information Center of CSIR-IITR, Lucknow for their constant support and help during research
endeavour’s.
Though, I am indebted to many people for their great help and support but the
chief contributors are undoubtedly my parents. Today, whatever I am, and tomorrow will be, it
entirely bears the stamps of their love, encouragement, and sacrifices beyond their limits. They are
the unparallel source of inspiration and real role models to me. This is only their blessings, untiring
efforts and sacrifices that today their dreams come true. My vocabulary is not wide enough to put
my sentiments in words to repay them for what they have done to groom me in such a great
fashion.
I would like to put on record that the love, affection and support extended by my
sister Nidhi Srivastava, brother-in-law Mr. Satish Srivastava, wife Deepti Srivastava and my
little nephew Saksham babu cannot be ignored and deeply acknowledged herewith.
Financial support to the study by Council of scientific & Industrial Research (CSIR), New Delhi,
is greatly acknowledged.
Last but not least I wish to offer my heartfelt thanks to all, whose names could not be included,
but will be fondly remembered.
Ashutosh Kumar Srivastava
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Ashutosh K. Srivastava Page iii
PREFACE
“Earth provide enough to satisfy every man’s need, But not for every man’s greed.”
(Mahatma Gandhi)
Application and persistence of manmade chemicals are increasing in our surrounding
environment with increase in population, urbanisation and industrialisation. Pesticides
present the only group of chemicals that are purposely applied to the environment with aim to
suppress plant and animal pests and to protect agricultural and industrial products. However,
the majority of pesticides are not specifically targeting the pest only and during their
application they also affect non-target plants, animals and indirectly humans. Repeated
application leads to loss of biodiversity. Many pesticides are not easily degradable, they
persist in soil, leach to groundwater and surface water and contaminate wide environment.
Depending on their chemical properties they can enter the organism, bioaccumulate in food
chains and consequently influence human health also. Overall, intensive pesticide application
results in several negative effects in the environment that cannot be ignored.
A pioneer warning signal about pesticides pollution was assessed in 1962, by Rachel
Carson, an American courageous woman and scientist, wrote down her nature observation
and pointed out sudden dying of birds caused by indiscriminate spraying of pesticides (DDT).
Her book „Silent Spring‟, became a landmark. It changed the existing view on pesticides and
stimulated public concern on pesticides and their impact on health and the environment.
Silent Spring facilitated the ban of the DDT in 1972 in the United States. Further, more
research has been done and several dangerous and persistent organic pesticides like Dieldrin,
Endosulfan and Lindane have been banned or restricted since that time. The Stockholm
Convention on Persistent Organic Pollutants which was a global treaty entered in force in
May 2004, aimed to eliminate the production and use of twelve priority POPs including
organochlorine pesticides such as aldrin, dieldrin, DDT and metabolites, endrin, heptachlor,
chlordane, mirex and toxaphene. In August 2010, Hexachlorocyclohexane, lindane,
chlordecone and pentachlorobenzene were added.
These obsolete pesticides are characterised by a high persistence in the environment (e.g. half
life for DDT in soil range from 22 to 30 years, Toxaphene up to 14 years, Mirex about 12
years, Dieldrin up to 7 years, Chlordecone up to 30 years), low water solubility and thus
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Ashutosh K. Srivastava Page iv
potential to accumulate in fatty tissue of living organisms including humans and toxicity to
both human and wildlife. Due to intensive releases to the environment in past several
decades, their chemical properties and tendency to long-range trans boundary atmospheric
transport, they are now widely distributed and are found around a globe. Significant levels are
detected in regions where persistent pesticides have never been used such as in polar regions,
in tissues of fishes, birds and bears.
In the present thesis entailed “Studies on the Pesticide Contamination in Food
Commodities and their Residual Toxicity; In vivo and In silico tools” assessment of variable
pesticides in food commodities has been done. Food safety is of great importance to all
involved in the food chain. This dissertation also provides detailed information on the results
of the sampling and analysis programmes for residual traces of pesticides in both imported
and domestic food.
This thesis is carried out at Pesticide Toxicology Laboratory, CSIR-Indian Institute of
Toxicology Research, Lucknow, India and Division of Biosciences, Faculty of Applied
Sciences, Integral University of Lucknow. An overview of the organochlorine (OC),
organophosphate (OP) and synthetic pyrethroids pesticide residues analysis in selected food
commodities like vegetables, fruits, cereals, spices and milk as well as their toxicological
implication has been assessed.
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Key Abbreviations
% Percent
µg Microgram
µg g-1
Micro grams per gram
µM Micro molar
ACF Activated Carbon Fiber
ADI Acceptable Daily Intake
ADI Accepted Daily Intake
AOAC Association of Official Analytical Chemists
B (A) P Benjo pyerine
BDL Below Detection Limit
BM Bone Marrow
BUN Blood Urea Nitrogen
Bw Body weight
C.A Chromosomal Aberrations
CAT Catalase
DCM Dichloromethane
DDD Dichlorodiphenyldichloroethane
DDE Dichlorodiphenyldichloroethylene
DDT Dichlorodiphenyltrichloroethane
DTNB 5,5'-Dithiobis-(2-nitrobenzoic Acid)
ECD Electron Capture Detector
EDTA Ethylenediaminetetraacetic acid
ELISA Enzyme Linked Immuno Sorbent Assay
ELOQ Estimated Limit of Quantification
EPA Environmental Protection Agency
EU European Union
FAO Food and Agriculture Organization
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GAC Granular Activated Carbon
GC-MS Gas Chromatography-Mass Spectrometry
GLC Gas Liquid Chromatography
GOT Glutamic Oxaloacetic Transaminase
GPT Glutamic-PyruvicTtransaminase
GPx Glutathione Peroxidase
GR Glutathione Reductase
GSH Reduced Glutathione
GST Glutathione S-Transferase
H Herbicide
H2O2 Hydrogen peroxide
Hb Hemoglobin
HCH Hexachlorocyclohexane
HCL Hydrochloric acid
HDL High Density Lipoprotein
I.P. Intraperitoneally
IARC Agency for Research on Cancer
IARC International Agency for Research on Cancer
ICP-MS Inductively coupled plasma-mass spectrometry
IDL Instrumental Detection Limit
IITR Indian Institute of Toxicology Research
IQL Instrumental Quantification Limit
KCl Potassium chloride
Kg Kilogram
LOAEL Lowest Observed Adverse Effect Level
LOD Limit of Detection
LOQ Limit of Quantification
LPO Lipid Peroxidation
M Molar
MAC Maximum Allowable Concentration
MCH Mean Corpuscules Hemoglobin Concentration
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MCV Mean Corpuscular Volume
MDA Malondialdehyde
MDL Method Detection Limit
mg Milligram
mg g-1
Miligrams per gram
mg l-1
Miligrams per liter
Min Minute
Mix. Mixture
ml Mililiter
MMS Matrix Match Standard
MNT Micronuclei Test
mol l-1
Moles per liter
MPI Maximum permissible intake
MRL Maximum Residual Limit
N Normality
NA Not Available
NaCl Sodium chloride
ND Not Detected
ng g-1
Nano gram per gram
ng l-1
Nano gram per liter
NIN National Institute of Nutrition
NIST National Institute of Standards and Technology
nm Nano Meter
NNMB National Nutrition Monitoring Bureau
NOAEL No Observed Adverse Effect Level
NPD Nitrogen Phosphorus Detector
O.D. Optical Density
OC Organochlorine
OP Organophosphate
op’ Ortho Para
PAC Powdered Activated Carbon
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PBS Phosphate Buffer Saline
PCB Poly Chlorinated Biphenyls
PFA Prevention of Food Adeltration Act.
pp’ Para Para
ppb parts per billion
ppm parts per million
ppt parts per trillion
PSA Primary Secondary Amine
PTDI Provisional Tolerable Daily Intake
PTWI Provisional Tolerance Weekly Intake
QuEChERS Quick Easy Cheap Effective Rugged and Safe
RBC Red Blood Cell
RDI Recommended Daily Intake
RMSE Root Mean Square Error
ROS Reactive Oxygen Species
rpm Round per minute
RSD Relative Standard Deviation
SD Standard Deviation
SDS Sodium Dodecyl Sulfate
SES Socio Economic Status
SP Synthetic Pyrethriods
TBA Thiobarbituric Acid
TBARS Thiobarbituric Acid Reactive Substances
TBE Tris Borate EDTA
TCA Trichloroacetic Acid
TLC Thin Layer Chromatography
TMDI Theoretical maximum daily intake
USEPA United State Environmental Protection Agency
WBC White Blood Cell
WHO World Health Organization
wt Weight
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α Alpha
β Beta
γ Gamma
δ Delta
μg l-1
Micro grams per liter
Σ Total
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LIST OF TABLES
Table
Page No.
Table 1: Action Based Classification of pesticide 9
Table 2: Physicochemical characteristics of pesticides 12-14
Table 3: Fortification experiment of Organochlorine 69
Pesticides residues from spiked vegetables at different level
(Recovery and repeatability), limit of detection (LOD),
Limit of quantification (LOQ), maximum residues limits (MRL)
And acceptable daily intake (ADI)
Table 4: Fortification experiment of organophosphate pesticides 70 -71
residues from spiked vegetables at different level
(recovery and repeatability), limit of detection (LOD),
limit of quantification (LOQ), maximum residues limits (MRL)
and acceptable daily intake (ADI).
Table 5: Fortification experiment of synthetic pyrethroids residues 72
from spiked vegetables at different level (recovery and repeatability),
limit of detection (LOD), limit of quantification (LOQ),
maximum residues limits (MRL) and acceptable daily intake (ADI).
Table 6: Fortification experiment of herbicides residues from 73
spiked vegetables at different level (recovery and repeatability),
limit of detection (LOD), limit of quantification (LOQ), maximum
residues limits (MRL) and acceptable daily intake (ADI)
Table 7: Fortification experiment of organochlorine pesticides 74
residues from spiked fruit at different level
(recovery and repeatability), limit of detection (LOD),
limit of quantification (LOQ),
maximum residues limits (MRL) and
acceptable daily intake (ADI
Table 8: Fortification experiment of organophosphate pesticides residues 75-76
from spiked fruit at different level (recovery and repeatability),
limit of detection (LOD), limit of quantification (LOQ),
maximum residues limits (MRL) and acceptable daily intake (ADI).
Table 9: Fortification experiment of synthetic pyrethroids residues from 77
spiked fruit at different level (recovery and repeatability), limit of
detection (LOD), limit of quantification (LOQ), maximum residues
limits (MRL) and acceptable daily intake (ADI
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Ashutosh K. Srivastava Page xi
Table 10: Fortification experiment of herbicides residues from spiked 78
fruit at different level (recovery and repeatability), limit of detection
(LOD), limit of quantification (LOQ), maximum residues limits (MRL)
and acceptable daily intake (ADI)
Table 11: Fortification experiment of organochlorine pesticides 79
residues from spiked spices at different level (recovery and
repeatability), limit of detection (LOD), limit of quantification (LOQ),
maximum residues limits (MRL) and acceptable daily intake (ADI)
Table 12: Fortification experiment of organophosphate pesticides 80-81
residues from spiked spices at different level (recovery and repeatability),
limit of detection (LOD), limit of quantification (LOQ),
maximum residues limits (MRL) and acceptable daily intake (ADI)
Table 13: Fortification experiment of synthetic pyrethroids residues 82
from spiked spices at different level (recovery and repeatability),
limit of detection (LOD), limit of quantification (LOQ),
maximum residues limits (MRL) and acceptable daily intake (ADI).
Table 14: Fortification experiment of herbicides residues from 83
spiked spices at different level (recovery and repeatability),
limit of detection (LOD), limit of quantification (LOQ),
maximum residues limits (MRL) and acceptable daily intake (ADI).
Table 15: Fortification experiment of Organochlorine pesticides 84
residues from spiked cereals at different level (recovery and
repeatability), limit of detection (LOD), limit of quantification (LOQ),
maximum residues limits (MRL) and acceptable daily intake (ADI).
Table 16: Fortification experiment of organophosphate pesticides 85-86
residues from spiked cereals at different level (recovery and
repeatability), limit of detection (LOD), limit of quantification (LOQ),
maximum residues limits (MRL) and acceptable daily intake (ADI).
Table 17: Fortification experiment of synthetic pyrethroids residues 87
from spiked cereals at different level (recovery and repeatability),
limit of detection (LOD), limit of quantification (LOQ), maximum
residues limits (MRL) and acceptable daily intake (ADI
Table 18: Fortification experiment of herbicides residues 88
from spiked cereals at different level (recovery and repeatability),
limit of detection (LOD), limit of quantification (LOQ), maximum
residues limits (MRL) and acceptable daily intake (ADI).
Table 19: Level of pesticide residues in vegetables 89
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Table 20: Level of pesticide residues in fruits 90
Table 21: Level of pesticide residues in grain 91
Table 22: Level of pesticide residues in spices 92
Table 23: Level of pesticide residues in milk 93
Table 24: Morbidity, mortality and body weight 94
gain of male rat orally administered individual and
combination of dicofol, malathion, cypermethrin for 90 days
Table 25: Food Consumption of male rat orally 95
administered individual and combination of dicofol,
malathion, cypermethrin for 90 days
Table 26: Neurobehavioral examination (spontaneous Locomotion 96
activity) of male rat orally administered individual and combination
of dicofol, malathion, cypermethrin for 90 days
Table 27: Hematological data of male rat orally administered 97
individual and combination of dicofol, malathion, Cypermethrin
for 90 days
Table 28: Relative organ weighta (g%) of male rat orally 98
administered individual and combination of dicofol, malathion,
cypermethrin for 90 days
Table 29: Serume biochemical data of male rat orally 99
administered individual and combination of dicofol, malathion,
cypermethrin for 90 days
Table 30: Proteins with theoretical binding sites for pesticide. 100
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LIST OF FIGURES
Figure
Page No.
Fig. 1.1 The pattern of pesticide usage in India 1
Fig. 2.1 Consumption of pesticides in India
15
Fig. 2.2 Proposed schematic diagram depicting of 16
Pesticide cycle in the environment
Fig. 2.3 Routes of Pesticide Exposure 17
Fig. 2.4 Source of ROS and other free radicals ROS
and other free radical intermediate are 22
Formed during normal metabolic
Processes in oxygen repairing organisms.
Fig. 2.5 Cell injuries by ROS or free radical-induced stress 23
Fig. 2.6 Biological antioxidant defense systems 24
Fig. 3.1 Map showing sampling site, Lucknow, Uttar Pradesh, India 28
Fig. 3.2 Diagrams of QuEChERS method 29
Fig. 3.3 Vegetables samples collected from Lucknow market
30
Fig. 3.4 Fruit samples collected from Lucknow market 31
Fig. 3.5 Cereals samples collected from Lucknow market
32
Fig. 3.6 Spices samples collected from Lucknow market 33
Fig. 3.7 Milk samples collected from Lucknow market 34
Fig. 3.8 GC-ECD chromatogram of organochlorine and 35
synthetic pyrethroids pesticide
Fig. 3.9 GC-ECD chromatogram of herbicide 35
Fig. 3.10 GC-NPD chromatogram of organophosphates 36
Fig. 3.11 The GC-MS confirmation diagram of dicofol 37
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Fig. 3.12 GC-MS confirmation diagram of malathion 38
Fig. 3.13 GC-MS confirmation diagram of Cypermethrin 38
Fig. 4(1A) Cerebellum of brain of control male rats 101
showing normal structure of purkinji cells,
molecular and granular layers (H & E x 1067)
Fig. 4(1B) Cerebellum of brain of treated male rats 101
(20+16+8mg/kg/b.wt./d) showing degenerative
changes in purkinji cells and loss of granules
in granular layer (H & E x1067)
Fig. 4(2A) Liver of control female rats showing normal 102
hepatocytes around the central vein (H & E x1067).
Fig. 4(2B) Liver of treated female rats (20 mg/kg/d) 102
showing mild focal necrosis of hepatocytes (H & E x 1067)
Fig. 4(3A) Kidney of control male rats showing normal tubule 103
and glomerulus structures (H & E x 1067)
Fig. 4(3B) Kidney of treated male rats (20 mg/kg/d) rats showing 103
degeneration of tubular and glomerulus structures
(H & E x 1067)
Fig. 4.1 Effect of dicofol, malathion, cypermethrin and their mixture in liver
on LPO and antioxidant enzymes of male rats orally exposed for
90 days (*p <0.05)
104
Fig. 4.2 Effect of dicofol, malathion, cypermethrin and 104
their mixture in brain on LPO and antioxidant enzymes
of male rats orally exposed for 90 days (*p <0.05)
Fig. 4.3 Effect of dicofol, malathion, Cypermethrin 105
and their mixture in kidney on LPO and antioxidant enzymes
of male rats orally exposed for 90 days (*p<0.05)
Fig. 4.4 Induction of chromosomal aberration by dicofol, 105
malathion, cypermethrin and their mixture in BM
Fig. 4.5 Effects of dicofol, malathion, cypermethrin and their 106
mixture exposure on chromosomal aberration in bone marrow
Fig. 4.6 Induction of micronuclei by dicofol, malathion, cypermethrin 107
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and their mixture in BM
Fig. 4.7 Induction of micronuclei by dicofol, malathion, Cypermethrin 108
in BM
Fig. 5 Number of samples of each commodity containing pesticide 108
residues out of 250 total analyzed samples
Fig. 5.1 Tri-dimensional view of the docking of pesticide 109