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Int. J. Agri. Agri. R.
Hussain et al.
Page 26
RESEARCH PAPER OPEN ACCESS
Pesticides toxicity assessment in occupational workers in Dir
Lower, Khyber Pakhtunkhwa, Pakistan
Fazal Hussain1*
, Muhammad Hussain2
, Sultan Ahmad1
, Salman Khan1
, Amina Zuberi2
,
Fahim Ullah Khan2
, Zohaib Noor2
, Syed Allauddin Khan2
, Muhammad Sardar3
, Saleem
Ur Rahman1
1
Department of Biotechnology, University of Malakand, Chakdara Dir Lower, Khyber
Pakhtunkhwa, Pakistan
2
Department of Animal Sciences, Quaid-i-Azam University, Islamabad, Pakistan
3
Department of Zoology, Hazara University, Mansehra, Khyber Pakhtunkhwa, Pakistan
Article published on May 12, 2016
Key words: Pesticides; Farmers; Dealers; Biochemical Markers; Blood Profiling.
Abstract
Pesticides are chemical compounds used to control insects and weeds to enhance food and crops productivity.
The present study was aimed to evaluate the effects of pesticides on health status of dealers and farmers in
district Dir Lower, Khyber Pakhtunkhwa, Pakistan. Blood samples were collected from different groups viz:
farmers, dealers (exposed to pesticides), and control (not exposed to pesticides) and the history was recorded on
a questioner. For Blood Profiling and Serum Biomarkers analysis, Sysmex Kx-21 (Japan) and Shiamadzu Double
Beam Spectrophotometer 1700 Pharma (Japan) were used. Upon pesticides exposure the blood cholesterol,
Triglyceride, Serum glutamate pyruvate transaminase, Uric Acid, Total Lipid, Low density lipoprotein, High
density lipoprotein, Mean Corpuscular Hemoglobin Concentration, Platelets and White Blood Cells count were
increased in dealers and farmers as compared to control group. While, Hemoglobin, Red Blood Cells,
hematocrit, Mean Corpuscular Volume, Mean Corpuscular Hemoglobin, Lymphocytes and Neutrophils counts
decreased in farmers and dealers as compared to control. The present findings suggest that pesticides exposure
adversely affect dealers and farmers health status by significantly altering their liver and kidney functions as well
as blood biochemistry and hematology.
* Corresponding Author: Fazal Hussain  fazalhussain70@gmail.com
International Journal of Agronomy and Agricultural Research (IJAAR)
ISSN: 2223-7054 (Print) 2225-3610 (Online)
http://www.innspub.net
Vol. 8, No. 5, p. 26-31, 2016
Int. J. Agri. Agri. R.
Hussain et al.
Page 27
Introduction
Pesticides are widely used to improve food and crop
productivity in order to cope with the rapidly growing
population throughout the World (AL-Shinnawy,
2008). These area heterogeneous group of chemicals
used to control, kill and eradicate weeds, insects,
pests, fungi and rodents (Kamel et al., 2004, Mnif et
al., 2011). They include a variety of compounds like
nematicides, plant growth regulators, molluscicides,
herbicides, rodenticides, fungicides and insecticides
(Aktar et al., 2009). Due to exposure these pesticides
results mortality and morbidity in most of the less
developed countries of the World such as Pakistan,
India and Bangladesh (Saxena, 2010).
The ruthless use of these pesticides has not only
adversely affected domestic animals but, also wild
animals including human beings (Alpalan et al.,
2006). Pesticides exposure disrupts sperm
production which ultimately leads to male sterility
and reduced sperm quantity as well as poor quality
(Falck et al., 1992). The widespread use of the
pesticides for agricultural purposes have caused
multiple ailments and problems of respiratory
system, nervous system, endocrine system,
reproductive system, cardiovascular and immune
system such as blood coagulation, arthrosclerosis,
fluid as well as electrolyte imbalance. They are potent
mutagenic as well as carcinogenic for multiple body
parts but, liver and kidney are among the most
vulnerable organs (Kumar, 2008, Patil et al., 2009).
Its exposure predominantly takes place through eyes,
human skin, ingestion and breathing (Patil et al.,
2009). Exposure in occupational workers including
farmers, gardeners and dealers occurs while handling,
processing, using and spraying of the pesticides
(Wolfe et al., 1967). The current research was
undertaken to evaluate the adverse effects of
insecticides on health status of the farmers and
dealers exposed to these toxic chemicals by analyzing
their hematological and biochemical markers.
Materials and methods
Sampling Area and Population
For the current research, three villages (Asbanr,
Tazagram and Ouch) of district Dir Lower, Khyber
Pakhtunkhwa, Pakistan were selected, where
vegetables like tomato and onions and crops such as
wheat and maize are commonly grown and sprayed
with pesticides to protect them from different
diseases as well as pest and weeds. A total of 200
workers including both farmers and dealers exposed
to pesticides and 200 controls (not exposed to
pesticides) were randomly selected and the informed
consent letter was signed from all the participants
and the history was recorded on questioner.
Blood sampling and analysis
A 5 ml blood sample was taken from the brachial vein
of each of pesticides exposed workers (farmers and
dealers) and control group (unexposed to pesticides)
using sterile syringes. The 3 ml blood sample was
taken in vacutainer tube having heparin for complete
blood profiling via Sysmex KX-21(Japan).For serum
isolation, 2 mLblood was transferred to sterile falcon
tubes containing no anticoagulant and stored at -20
°C for analysis. The serum samples were analyzed for
estimation of various biochemical markers
(Triglycerides, Cholesterol and SGPT etc.) by using
Shiamadzu Double Beam Spectrophotometer 1700
Pharma (Japan).
Statistical Analysis
The results were expressed as mean ± standard
deviation. Data was statistically analyzed by one way
analysis of variance (ANOVA) and the mean values
were compared by using Tukey’s comparison test at
p<0.05. The online available software Graph pad
prism, Demo version 5.0 was used for statistical
analysis.
Results and discussions
Despite the widespread use of pesticides in
Agriculture and livestock improvement. Its role in
diseases development in human beings is still
debatable and not clear. To provide a comprehensive
report regarding the adverse effects of pesticides on
Int. J. Agri. Agri. R.
Hussain et al.
Page 28
vital organs such as liver, kidney and heart of
occupational workers the current research work was
undertaken. The present study was designed to
investigate the toxic effects of pesticides on human
health by analyzing blood hematology and
biochemistry of the occupational workers including
farmers and dealers of Dir Lower, Pakistan.
Biochemical Parameters
The blood biochemical parameters like cholesterol
(Fig.1A.), triglyceride (Fig.2A.), serum glutamate
pyruvate transaminase (SGPT) (Fig.3A.), uric acid
(Fig.4A.), total lipid (Fig. 5A.), low density lipoprotein
(LDL) (Fig.6A.) and high density lipoprotein (HDL)
(Fig.7A.) levels increased upon exposure to pesticides
in both dealers and farmers as compared to control
(not exposed to pesticides), but the effects of
pesticides were more severe in farmers than dealers
which may be due to prolonged exposure time and
unawareness while handlings these toxic compounds
by the farmers. High SGPT and Uric acid levels in the
farmers and dealers than control indicate pesticides
stress and toxicity on Liver and kidney.
These results are in close agreement with the findings
of Salih, (1995), who assessed the toxic effects of
Diazinon and Dimethoate on liver and kidney
functions, and reported elevated concentrations of
Aspartate Aminotransferase (AST), Alkaline
phosphatase (ALP), Alanine Aminotransferase (ALT),
glucose, creatinine and uric acid in the serum of the
exposed rabbits in comparison to control. It is
concluded that pesticides significantly alter liver and
kidney functions and also badly affects various blood
biomarkers. Similarly, Muthuviveganandavel et al.,
(2010) reported that carbendazim fungicide result in
increased levels of uric acid, creatinine, glucose and
cholesterol in rats. Our findings are also in harmony
with the results of Nabi et al., (2014).
Fig. 1A. Blood Cholesterol Level of Control, Dealers
and Farmers.
Fig. 2A. Blood Triglyceride Level of Control, Dealers
and Farmers.
Fig. 3A. Serum glutamate pyruvate transaminase
level of control, dealers and farmers.
Fig. 4A. Blood uric acid level of control, dealers and
farmers.
C
ontrol
D
ealers
farm
ers
0
50
100
150
200
250
Control
Dealers
farmers
a a
b
Concentration(mg/dl)
C
ontrol
D
ealers
Farm
ers
0
2
4
6
8
10
Control
Dealers
Farmers
a
b
ab
Concentration(mg/dl)
C
ontrol
D
ealers
Farm
ers
0
50
100
150
200
250 Farmers
Dealers
Control
a
ab
b
Concentration(U/L)
C
ontrol
D
ealers
Farm
ers
0
50
100
150
200
Control
Dealers
Farmers
a
b
ab
Concentration(mg/dl)
Int. J. Agri. Agri. R.
Hussain et al.
Page 29
Fig. 5A. Blood total lipid level of control, dealers and
farmers.
Fig. 6A. Blood LDL level of control, dealers and
farmers.
Fig. 7A. Blood HDL level of control, dealers and
farmers.
Hematological Parameters
The hematological parameters such as Hemoglobin
(HB) (Fig.1B.), Red Blood Cells (RBC) count (Fig.2B.),
hematocrit (HCT) (Fig.3B.), Mean Corpuscular
Volume (MCV) (Fig.4B.), lymphocytes count
(Fig.5B.), neutrophils count (Fig.6B.) and Mean
Corpuscular Hemoglobin(MCH) (Fig.7B.) of dealers
and farmers decreased upon exposure to pesticides
when compared to control (not exposed to pesticides),
while Mean Corpuscular Hemoglobin Concentration
(MCHC) (Fig.8B.), Platelets count (Fig.9B.) and
White Blood Cells (WBC.) count (Fig.10B.) of dealers
and farmers were increased in comparison to control
group and the adverse effects of pesticides were more
prominent in farmers than dealers. High WBC count
in the exposed workers shows that they are at higher
risk to contract various pathological conditions.
Similar results were also reported by Muralidharan,
(2012), who observed a decline in RBC, Erythrocyte
Sedimentation Rate (ESR), hemoglobin and clotting
time, while platelet and WBC levels were increased in
Cyprinus carpiofish treated with different
concentrations of fenthion. These results indicate that
pesticides exposure significantly alter the blood
biochemical as well as hematological parameters.
Similar findings were also reported by Jasper et al.,
(2012).These results are correlated with the findings
ofNabi et al., (2014),who observed elevatedPlatelets,
Neutrophiland white blood cells count in Tandoor
Occupants.
Fig. 1B. Haemoglobin level of control, Dealers and
farmers.
Fig. 2B. RBC level of control, dealers and farmers.
Fig. 3B. Hematocrit level of control, dealers and
farmers.
C
ontrol
D
ealers
Farm
ers
0
20
40
60
80
Farmers
Dealers
Control
a a
b
Concentration(mg/dl)
C
ontrol
D
ealers
Farm
ers
0
200
400
600
800
Farmers
Dealers
Control
a a
b
Concentration(mg/dl)
C
ontrol
D
ealers
Farm
ers
0
50
100
150
200
Farmers
Dealers
Control
a
a
b
Concentration(mg/dl)
C
ontrol
D
ealers
Farm
ers
0
2
4
6
8
Control
Dealers
Farmers
a
ab
b
Concentration(106
/L)
C
ontrol
D
ealers
Farm
ers
0
20
40
60
Control
Dealers
Farmers
a
b b
Concentration(%)
C
ontrol
D
ealers
Farm
ers
0
5
10
15
20
Control
Dealers
Farmers
a
b
b
Concentration(mg/dl)
Int. J. Agri. Agri. R.
Hussain et al.
Page 30
Fig. 4B. Mean Corpuscular Volume of control,
dealers and farmers.
Fig. 5B. Lymphocytes level ofcontrol, dealers and farmers.
Fig. 6B. Neutrophil level of control, dealers and farmers.
Fig. 7B. Mean Corpuscular Haemoglobin of control,
dealers and farmers.
Fig. 8B. MCHC level of control, dealers and farmers.
Fig. 9B. Platelets level of control, dealers and farmers.
Fig. 10B. WBC level of control, dealers and farmers.
Conclusions
It is concluded from these findings that pesticides
exposure adversely affect dealers and farmers health
status by significantly altering their liver and kidney
functions as well as blood biochemical markers and
blood profiling. Further study is to be needed to
identify more risk factors of pesticides exposure
considering large population.
Acknowledgment
We gratefully acknowledge all those who helped and
cooperate during sampling and in the preparation of
this research manuscript.
References
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Alpalan G, Kanat HD, Dilek B, Altuntas I.
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AL-Shinnawy MSAA. 2008. Effects of Orally Fed
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Concentration(103
/L)
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Hussain et al.
Page 31
Albino Rats. The Egyptian Journal of Hospital
Medicine 33, 559– 568.
Falck F, Ricci A, Wolff MS, Godbold J, Deckers
P. 1992. Supplementation on Biochemical Parameters
in Pesticides Sprayers of Grape Gardens of Western
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Pesticides toxicity assessment in occupational workers in Dir Lower, Khyber Pakhtunkhwa, Pakistan

  • 1. Int. J. Agri. Agri. R. Hussain et al. Page 26 RESEARCH PAPER OPEN ACCESS Pesticides toxicity assessment in occupational workers in Dir Lower, Khyber Pakhtunkhwa, Pakistan Fazal Hussain1* , Muhammad Hussain2 , Sultan Ahmad1 , Salman Khan1 , Amina Zuberi2 , Fahim Ullah Khan2 , Zohaib Noor2 , Syed Allauddin Khan2 , Muhammad Sardar3 , Saleem Ur Rahman1 1 Department of Biotechnology, University of Malakand, Chakdara Dir Lower, Khyber Pakhtunkhwa, Pakistan 2 Department of Animal Sciences, Quaid-i-Azam University, Islamabad, Pakistan 3 Department of Zoology, Hazara University, Mansehra, Khyber Pakhtunkhwa, Pakistan Article published on May 12, 2016 Key words: Pesticides; Farmers; Dealers; Biochemical Markers; Blood Profiling. Abstract Pesticides are chemical compounds used to control insects and weeds to enhance food and crops productivity. The present study was aimed to evaluate the effects of pesticides on health status of dealers and farmers in district Dir Lower, Khyber Pakhtunkhwa, Pakistan. Blood samples were collected from different groups viz: farmers, dealers (exposed to pesticides), and control (not exposed to pesticides) and the history was recorded on a questioner. For Blood Profiling and Serum Biomarkers analysis, Sysmex Kx-21 (Japan) and Shiamadzu Double Beam Spectrophotometer 1700 Pharma (Japan) were used. Upon pesticides exposure the blood cholesterol, Triglyceride, Serum glutamate pyruvate transaminase, Uric Acid, Total Lipid, Low density lipoprotein, High density lipoprotein, Mean Corpuscular Hemoglobin Concentration, Platelets and White Blood Cells count were increased in dealers and farmers as compared to control group. While, Hemoglobin, Red Blood Cells, hematocrit, Mean Corpuscular Volume, Mean Corpuscular Hemoglobin, Lymphocytes and Neutrophils counts decreased in farmers and dealers as compared to control. The present findings suggest that pesticides exposure adversely affect dealers and farmers health status by significantly altering their liver and kidney functions as well as blood biochemistry and hematology. * Corresponding Author: Fazal Hussain  fazalhussain70@gmail.com International Journal of Agronomy and Agricultural Research (IJAAR) ISSN: 2223-7054 (Print) 2225-3610 (Online) http://www.innspub.net Vol. 8, No. 5, p. 26-31, 2016
  • 2. Int. J. Agri. Agri. R. Hussain et al. Page 27 Introduction Pesticides are widely used to improve food and crop productivity in order to cope with the rapidly growing population throughout the World (AL-Shinnawy, 2008). These area heterogeneous group of chemicals used to control, kill and eradicate weeds, insects, pests, fungi and rodents (Kamel et al., 2004, Mnif et al., 2011). They include a variety of compounds like nematicides, plant growth regulators, molluscicides, herbicides, rodenticides, fungicides and insecticides (Aktar et al., 2009). Due to exposure these pesticides results mortality and morbidity in most of the less developed countries of the World such as Pakistan, India and Bangladesh (Saxena, 2010). The ruthless use of these pesticides has not only adversely affected domestic animals but, also wild animals including human beings (Alpalan et al., 2006). Pesticides exposure disrupts sperm production which ultimately leads to male sterility and reduced sperm quantity as well as poor quality (Falck et al., 1992). The widespread use of the pesticides for agricultural purposes have caused multiple ailments and problems of respiratory system, nervous system, endocrine system, reproductive system, cardiovascular and immune system such as blood coagulation, arthrosclerosis, fluid as well as electrolyte imbalance. They are potent mutagenic as well as carcinogenic for multiple body parts but, liver and kidney are among the most vulnerable organs (Kumar, 2008, Patil et al., 2009). Its exposure predominantly takes place through eyes, human skin, ingestion and breathing (Patil et al., 2009). Exposure in occupational workers including farmers, gardeners and dealers occurs while handling, processing, using and spraying of the pesticides (Wolfe et al., 1967). The current research was undertaken to evaluate the adverse effects of insecticides on health status of the farmers and dealers exposed to these toxic chemicals by analyzing their hematological and biochemical markers. Materials and methods Sampling Area and Population For the current research, three villages (Asbanr, Tazagram and Ouch) of district Dir Lower, Khyber Pakhtunkhwa, Pakistan were selected, where vegetables like tomato and onions and crops such as wheat and maize are commonly grown and sprayed with pesticides to protect them from different diseases as well as pest and weeds. A total of 200 workers including both farmers and dealers exposed to pesticides and 200 controls (not exposed to pesticides) were randomly selected and the informed consent letter was signed from all the participants and the history was recorded on questioner. Blood sampling and analysis A 5 ml blood sample was taken from the brachial vein of each of pesticides exposed workers (farmers and dealers) and control group (unexposed to pesticides) using sterile syringes. The 3 ml blood sample was taken in vacutainer tube having heparin for complete blood profiling via Sysmex KX-21(Japan).For serum isolation, 2 mLblood was transferred to sterile falcon tubes containing no anticoagulant and stored at -20 °C for analysis. The serum samples were analyzed for estimation of various biochemical markers (Triglycerides, Cholesterol and SGPT etc.) by using Shiamadzu Double Beam Spectrophotometer 1700 Pharma (Japan). Statistical Analysis The results were expressed as mean ± standard deviation. Data was statistically analyzed by one way analysis of variance (ANOVA) and the mean values were compared by using Tukey’s comparison test at p<0.05. The online available software Graph pad prism, Demo version 5.0 was used for statistical analysis. Results and discussions Despite the widespread use of pesticides in Agriculture and livestock improvement. Its role in diseases development in human beings is still debatable and not clear. To provide a comprehensive report regarding the adverse effects of pesticides on
  • 3. Int. J. Agri. Agri. R. Hussain et al. Page 28 vital organs such as liver, kidney and heart of occupational workers the current research work was undertaken. The present study was designed to investigate the toxic effects of pesticides on human health by analyzing blood hematology and biochemistry of the occupational workers including farmers and dealers of Dir Lower, Pakistan. Biochemical Parameters The blood biochemical parameters like cholesterol (Fig.1A.), triglyceride (Fig.2A.), serum glutamate pyruvate transaminase (SGPT) (Fig.3A.), uric acid (Fig.4A.), total lipid (Fig. 5A.), low density lipoprotein (LDL) (Fig.6A.) and high density lipoprotein (HDL) (Fig.7A.) levels increased upon exposure to pesticides in both dealers and farmers as compared to control (not exposed to pesticides), but the effects of pesticides were more severe in farmers than dealers which may be due to prolonged exposure time and unawareness while handlings these toxic compounds by the farmers. High SGPT and Uric acid levels in the farmers and dealers than control indicate pesticides stress and toxicity on Liver and kidney. These results are in close agreement with the findings of Salih, (1995), who assessed the toxic effects of Diazinon and Dimethoate on liver and kidney functions, and reported elevated concentrations of Aspartate Aminotransferase (AST), Alkaline phosphatase (ALP), Alanine Aminotransferase (ALT), glucose, creatinine and uric acid in the serum of the exposed rabbits in comparison to control. It is concluded that pesticides significantly alter liver and kidney functions and also badly affects various blood biomarkers. Similarly, Muthuviveganandavel et al., (2010) reported that carbendazim fungicide result in increased levels of uric acid, creatinine, glucose and cholesterol in rats. Our findings are also in harmony with the results of Nabi et al., (2014). Fig. 1A. Blood Cholesterol Level of Control, Dealers and Farmers. Fig. 2A. Blood Triglyceride Level of Control, Dealers and Farmers. Fig. 3A. Serum glutamate pyruvate transaminase level of control, dealers and farmers. Fig. 4A. Blood uric acid level of control, dealers and farmers. C ontrol D ealers farm ers 0 50 100 150 200 250 Control Dealers farmers a a b Concentration(mg/dl) C ontrol D ealers Farm ers 0 2 4 6 8 10 Control Dealers Farmers a b ab Concentration(mg/dl) C ontrol D ealers Farm ers 0 50 100 150 200 250 Farmers Dealers Control a ab b Concentration(U/L) C ontrol D ealers Farm ers 0 50 100 150 200 Control Dealers Farmers a b ab Concentration(mg/dl)
  • 4. Int. J. Agri. Agri. R. Hussain et al. Page 29 Fig. 5A. Blood total lipid level of control, dealers and farmers. Fig. 6A. Blood LDL level of control, dealers and farmers. Fig. 7A. Blood HDL level of control, dealers and farmers. Hematological Parameters The hematological parameters such as Hemoglobin (HB) (Fig.1B.), Red Blood Cells (RBC) count (Fig.2B.), hematocrit (HCT) (Fig.3B.), Mean Corpuscular Volume (MCV) (Fig.4B.), lymphocytes count (Fig.5B.), neutrophils count (Fig.6B.) and Mean Corpuscular Hemoglobin(MCH) (Fig.7B.) of dealers and farmers decreased upon exposure to pesticides when compared to control (not exposed to pesticides), while Mean Corpuscular Hemoglobin Concentration (MCHC) (Fig.8B.), Platelets count (Fig.9B.) and White Blood Cells (WBC.) count (Fig.10B.) of dealers and farmers were increased in comparison to control group and the adverse effects of pesticides were more prominent in farmers than dealers. High WBC count in the exposed workers shows that they are at higher risk to contract various pathological conditions. Similar results were also reported by Muralidharan, (2012), who observed a decline in RBC, Erythrocyte Sedimentation Rate (ESR), hemoglobin and clotting time, while platelet and WBC levels were increased in Cyprinus carpiofish treated with different concentrations of fenthion. These results indicate that pesticides exposure significantly alter the blood biochemical as well as hematological parameters. Similar findings were also reported by Jasper et al., (2012).These results are correlated with the findings ofNabi et al., (2014),who observed elevatedPlatelets, Neutrophiland white blood cells count in Tandoor Occupants. Fig. 1B. Haemoglobin level of control, Dealers and farmers. Fig. 2B. RBC level of control, dealers and farmers. Fig. 3B. Hematocrit level of control, dealers and farmers. C ontrol D ealers Farm ers 0 20 40 60 80 Farmers Dealers Control a a b Concentration(mg/dl) C ontrol D ealers Farm ers 0 200 400 600 800 Farmers Dealers Control a a b Concentration(mg/dl) C ontrol D ealers Farm ers 0 50 100 150 200 Farmers Dealers Control a a b Concentration(mg/dl) C ontrol D ealers Farm ers 0 2 4 6 8 Control Dealers Farmers a ab b Concentration(106 /L) C ontrol D ealers Farm ers 0 20 40 60 Control Dealers Farmers a b b Concentration(%) C ontrol D ealers Farm ers 0 5 10 15 20 Control Dealers Farmers a b b Concentration(mg/dl)
  • 5. Int. J. Agri. Agri. R. Hussain et al. Page 30 Fig. 4B. Mean Corpuscular Volume of control, dealers and farmers. Fig. 5B. Lymphocytes level ofcontrol, dealers and farmers. Fig. 6B. Neutrophil level of control, dealers and farmers. Fig. 7B. Mean Corpuscular Haemoglobin of control, dealers and farmers. Fig. 8B. MCHC level of control, dealers and farmers. Fig. 9B. Platelets level of control, dealers and farmers. Fig. 10B. WBC level of control, dealers and farmers. Conclusions It is concluded from these findings that pesticides exposure adversely affect dealers and farmers health status by significantly altering their liver and kidney functions as well as blood biochemical markers and blood profiling. Further study is to be needed to identify more risk factors of pesticides exposure considering large population. Acknowledgment We gratefully acknowledge all those who helped and cooperate during sampling and in the preparation of this research manuscript. References Aktar W, Sengupta D, Chowdhury A. 2009. Impact of pesticides use in agriculture: their benefits and hazards. Interdisciplinary Toxicology 2, 1-12. doi:org/10.2478/v10102-009-0001-7 Alpalan G, Kanat HD, Dilek B, Altuntas I. 2006. Effects of diazinon at different doses on rat liver and pancreas tissues. Pesticide biochemistry and physiology 87, 103-108. AL-Shinnawy MSAA. 2008. Effects of Orally Fed Diazinon on Some Biochemical Parameters of Male C o n tro l D ealers F arm ers 0 10 20 30 40 Control Dealers Farmers a a b Concentration(%) C ontrol D ealers Farm ers 0 50 100 150 Farmers Dealers Control a b ab Volume(fL) C ontrol D ealers farm ers 0 20 40 60 80 Control Dealers Farmers a ab b Concentration(%) C ontrol D ealers Farm ers 0 20 40 60 80 Control Dealers Farmers a b ab Concentration(%) C ontrol D ealers Farm ers 0 10 20 30 40 Control Dealers Farmers a a b Concentration(pg) C ontrol D ealers Farm ers 0 100 200 300 400 500 Control Dealers Farmers a b b Concentration(103 /µL) C on trol D ealers F arm ers 0 2 4 6 8 10 Control Dealers Farmers a a b Concentration(103 /L)
  • 6. Int. J. Agri. Agri. R. Hussain et al. Page 31 Albino Rats. The Egyptian Journal of Hospital Medicine 33, 559– 568. Falck F, Ricci A, Wolff MS, Godbold J, Deckers P. 1992. Supplementation on Biochemical Parameters in Pesticides Sprayers of Grape Gardens of Western Maharashtra (India).Indian Journal of Clinical Biochemistry 27, 134–140. doi:org/10.1007/s12291- 012-0207-x Jasper R, Locatelli GO, Pilati C, Locatelli C. 2012. Evaluation of biochemical, hematological and oxidative parameters in mice exposed to the herbicide glyphosate-Roundup. Interdisciplinary Toxicology 5, 133–140.doi:10.2478/v10102-012-0022-5 Kamel F, Hoppin JA. 2004. Association of pesticide exposure with neurologic dysfunction and disease. Environmental Health Perspectives 112, 950- 958.doi:org/10.1289/ehp.7135 Kumar LP, Panneerselvam N. 2008. Toxic effects of pesticides: A review on cytogenetic biomonitoring studies. Medicine and Biology 15, 46-50. Mnif W, Hassine AIH, Bouaziz A, Bartegi A, Thomas O, Roig B. 2011. Effect of Endocrine Disruptor Pesticides. A Review: International Journal of Environmental Research and Public Health 8, 2265-2303.doi:org/10.3390/ijerph8062265 Muralidharan L. 2012. Haemato-biochemical alterations induced by chronic exposure to fenthionin Cyprinus carpio.Trends in Fisheries Research 1, 19-25. Muthuviveganandavel V, Muthuraman P, Muthu S, Srikumar K. 2008.Toxic effects of carbendazim at low dose levels in male rats. Journal of Toxicological Sciences 33, 25-30. Nabi G, Urooj J, Khan AA, Zamani GY, Wahid M, Rahman SU. 2014. Effects of Occupational Exposure to Wood Smoke in Tandoor Occupants. Journal of Biology and Life Science 5, 37- 47.doi:10.5296/jbls.v5i2.4079 Patil JA, Patil AJ, Sontakke AV, Govindwar SP. 2009. Effect of Vitamin E on liver and kidney function. Journal of Basic Clinical Physiology and Pharmacology 20, 335-55. doi:org/10.1515/JBCPP.2009.20.4.335 Salih EMA. 1995. Toxic Effect of Dimethoate and Diazinon on the Biochemical and Hematological parameters in male rabbits. Jordan Journal of Biological Sciences 3, 77-82. Saxena P, Saxena AK. 2010. Cypermethrin Induced Biochemical Alterations in the Blood of Albino Rats. Jordan Journal of Biological Sciences 3, 111-114. Wolfe HR, Durham WF, Armstrong JF. 1967. Exposure of workers to pesticides. Archives of Environmental Health 14, 622–33.