Int J Med Invest 2014; vol 3; num 4; 127-132
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Original article
Pesticide exposure and thyroid function in adult male sprayers
Farzaneh Farokhi1*, Ali Taravati2
2.
1. Department of Biology, Faculty of Basic Sciences Islamic Azad University, Sari Branch, Sari, Iran
Department of Molecular and Cell Biology, Faculty of Basic Sciences, University of Mazandaran, Babolsar,
IR Iran.
Corresponding author: Farzaneh Farokhi
Email: farzane.farokhi@gmail.com
Abstract: Pesticides are often used indiscriminately in a large amounts causing environmental pollution.
Pesticides cause adverse effects on different body systems, including hematological and endocrine
systems. Animal studies have shown the ability of organophosphorus and organochlorine pesticides to
disturb thyroid function, but evidence of such effects on human remains unclear.
The purpose of this study was to investigate the association between exposure to pesticide and serum
levels of thyroid hormones in pesticide sprayers.
Blood samples were obtained from 40 cases and 20 controls after overnight fasting. Glucose, urea, acid
uric and lipid profile were measured by enzymatic methods. Immunoassay methods were used for
determining of TSH, T3 and T4 levels.
The TSH level in sprayers (2.64±1.50 mIU/l, P=0.007) was significantly increased compared to control
subjects (1.33±0.83 μM). Significant decreased in T3 and insignificant decreased in T4 level of sprayers
were observed.
These results suggest that exposure to organophosphorus and organochlorine pesticides may be
responsible for increasing TSH level and decreasing T3 and T4 serum hormone levels, therefore
supporting the hypothesis that organophosphorus and organochlorine pesticides cause hypothyroidism in
pesticide sprayers. So administration of supplementary nutrients or improving defense system in these
peoples is advised.
Keywords: organochlorine, organophosphate, thyroid hormones, hypothyroidism, pesticide sprayers
1. Introduction
During the past 50 years, pesticides have had an
essential role in the agricultural world. Irrational and
wrong use of pesticide has considerably increased
with increased consumer demand.
Widespread use of pesticides in agriculture causes
environmental pollution and severe health risks such
as acute and chronic human poisoning (1, 2). In
addition to spraying, other way of exposure to
pesticides including formulation and handling
without consideration of safety tips are also
contribute to the emergence of toxic side effects (3).
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There is evidence, indicating that environmental
contact, especially with pesticides, is considered to be
a risk factor for thyroid diseases. It has been reported
that special insecticides, herbicides and fungicides
are endocrine disruptors. Their functions performed
by different mechanisms such as inhibition of iodine
absorption, intervention in thyroid hormone receptor,
binding to transfer proteins, intervention with
iodothyronine deiodinases, increased thyroid
hormones clearance and intervention in expression of
thyroid hormone (4, 5).
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Int J Med Invest 2014; vol 3; num 4; 127-132
In a study conducted to evaluate thyroid function in
the workers of a Danish greenhouse, 32% increase of
thyroid stimulating hormone, TSH, and 5-9%
decrease of T3 and T4 in serum were observed in
spring compared with fall (6).Both lindane and
chlordane are among organochlorine insecticides,
which have been reported to affect the level of
thyroid hormones in humans (7-9). Increase in
chlordane level of breast milk is related to congenital
hypothyroidism (10). Studies on the manufacturers of
organochlorine pesticides, especially lindane and
organophosphorus insecticides, have demonstrated
increase of TSH and decrease of T 3 in these workers
compared with the control ones (11). Malathion,
which is an organochlorine insecticide, affects level
of thyroid hormone in catfish and tadpoles of fresh
waters (12, 13). Maneb/Mancozeb fungicides have a
strong relationship with the probability of thyroid
diseases so that causes hypothyroidism in rabbits
(14). In another study on the workers who were in
severe contact with ethylene bis dithiocarbamate
without any protection, TSH level increased but T 4
level did not show any significant difference from
that of the control people (15).
Some compounds such as polychlorinated biphenyls,
Bisphenol A and dioxin are shown to inhibit or
control cellular absorption of thyroid hormones and
lead to the possible increase in biliary excretion of T3
and T4 and change in the activity of thyroid nuclear
receptor, which changes expression of genes.
Polychlorinated
biphenyl,
triclosan,
pentachlorophenol
and
dioxins
inhibit
sulfotransferase activity, which result in decreased
sulfation and disregulation of peripheral levels of T 3
and T4.
People who are in touch with pesticides, especially
those who spray farmlands and gardens, do not use
sufficient protective instruments or do consider safety
guidelines. Unfortunately, farmers are not aware of
right amount of pesticides and its correct spraying
method; they usually spray their crops experimentally
and without knowing its side effects. The present
study was aim to determine the lipids profile and
thyroid function in a population involved in spraying
in some villages of Mazandaran Province, north of
Iran, and likely effects of pesticides on thyroid gland.
.
2. Material and Methods
The people selected for this study were spraying men,
40 peoples, who were involved in spraying for a long
time. These people had been exposed to some kinds
of organophosphorus and organochlorine pesticides.
An informed consent was obtained from all subjects
before measurements. Among the selected ones, a
group with no experience of chronic diseases,
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alcoholism and diabetes was sampled. 20 age and sex
matched control people were selected, considering
the absence of chronic diseases, alcoholism and
diabetes.
Blood sample of the participants was taken between 6
and 7 am. Fasting blood sugar, urea, creatinine, uric
acid, triglyceride (TG), total cholesterol (TC), HDL
and LDL were measured using kits of Pars Azmoon
Company.
The final diagnosis was done based on the following
definitions:
1- Ideal level for total cholesterol was defined
as<200mg/dl. The moderate risk was between
200 and 239 mg/dl and high risk level was ≤240
mg/dl.
2- For LDL cholesterol, ideal level was below
130mg/dl, the moderate risk was between 130
and 159 mg/dl and high risk level was
determined as≤160 mg/dl.
3- Ideal level for triglyceride was <200 mg/dl, the
moderate risk was between 200 and 399 mg/dl
and high risk level was considered ≤400 mg/dl.
4- HDL level was defined at two levels of ≥35
mg/dl (risk level) and <35 mg/dl (desirable
level).
TSH, T3 and T4 tests were conducted using
radioimmunoassay method (Patan Elm Company).
TSH quantitative measurement kit was designed
based on immune enzymatic reaction on solid phase.
T3 and T4 quantitative measurement kit was designed
based on the measurement of competitive immune
enzymatic reaction on solid phase.
In the current research, the following cases were
considered the criterion for the presence of thyroid
disorders.
A- Clinical hyperthyroidism: T 4>12.4 μg/dl or
T3>2.8 nmol/l and TSH≤0.1 mIU/l
B- Subclinical hyperthyroidism: TSH≤0.5 mIU/l
with normal T3 and T4 levels
C- Clinical hypothyroidism: T4<4.5 μg/dl and
TSH≥10 mIU/l
D- Subclinical hypothyroidism: TSH of between 5
and 10 mIU/l and normal T4
The results were showed in the form of
mean±standard deviation that the values P<0.05 were
considered statistically significant. Statistical
analyses were performed to compare the groups using
t-test analysis in SPSS software version 16.0 (SPSS
Inc. Chicago, IL).
3. Results
In this study, effect of pesticides used in spraying the
farmlands of Mazandaran Province, north of Iran,
which were studied on the function of thyroid gland.
For this purpose, the people lacking any history of
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which were not significantly different. The amount of
diseases were sampled after conducing preliminary
fasting serum lipids (lipid profile) was measured in
investigations.
the control and sprayers, as given in Table 1. The
Mean age of the control and spraying peoples were
levels of total cholesterol were 161.31±25.07 mg/dL
38.46±4.86 and 38.59±10.35 years, respectively,
Table 1: Mean and standard deviation of biochemical characteristics relating to age and lipid profile in the control
and spraying peoples
Age (y)
Cholesterol (mg/dL)
Triglyceride (mg/dL)
HDL (mg/dL)
LDL (mg/dL)
LDL /HDL
Cholesterol /HDL
Sprayers
(n = 40)
38.59 ± 10.35
154.19 ± 38.58
127.77 ± 76.03
41.06 ± 9.21
78.07 ± 21.27
1.99 ± 0.63
3.90 ± 1.13
Controls
(n = 20)
38.46 ± 4.86
161.31 ± 25.07
123.00 ± 57.58
39.77 ± 10.07
96.92 ± 26.16
2.69 ± 1.21
4.38 ± 1.50
P-Value
0.965
0.47
0.823
0.693
0.034
0.017
0.314
HDL, high
-density lipoprotein; LDL, low-density lipoprotein.
Data are presented as mean ± SD
Table 2: Mean and standard deviation resulting from CBC results among the control and spraying peoples
WBC(Cumm)
RBC (mil/Cumm)
Hb (g/dl)
HCT %
MCV fl
MCH (pg)
MCHC %
Sprayers
(n = 40)
6131.25 ± 1462.97
4.80 ± 0.48
13.52 ± 1.31
40.54 ± 3.44
84.98 ± 8.37
28.20 ± 3.37
33.32 ± 1.26
Controls
(n = 20)
6215.38± 1448.47
4.86 ± 0.51
13.57 ± 0.94
41.32 ± 2.26
85.54 ± 7.28
28.50 ± 2.29
34.14 ± 3.21
P-Value
0.862
0.71
0.561
0.461
0.824
0.77
0.388
WBC, white blood cells; RBC, red blood cells; Hb, hemoglobin; Hct, hematocrit; MCV, mean corpuscular volume; MCH, mean corpuscular
hemoglobin; MCHC, mean corpuscular hemoglobin concentration; Plt, platelet.
Table 3: Mean and standard deviation of biochemical parameters of blood among the control and spraying peoples
Fasting blood sugar (mg/dl)
Urea (mg/dL)
Creatinine (mg/dL)
U.A (mg/dL)
U.A/ Creatinine
Sprayers
(n = 40)
Controls
(n = 20)
P-Value
74.26 ± 7.22
35.31 ± 7.37
1.04 ± 0.15
4.90 ± 1.07
4.76 ± 0.94
73.77 ± 5.36
33.54 ± 6.28
1.12 ± 0.10
4.88± 0.82
4.33± 0.61
0.806
0.422
0.047
0.94
0.094
Table 4: Mean and standard deviation of thyroid hormones of blood among the control and spraying peoples
TSH (mIU/l)
T3(nmol/l)
T4(μg/dl)
T129
4/ T3
International
Sprayers
(n = 40)
2.64 ± 1.51
1.12 ± 0.52
9.29 ± 2.12
9.17 ±of
2.98
journal
Medical
Controls
(n = 20)
1.33 ± 0.83
1.55 ± 0.57
10.85 ± 2.82
7.62 ± 2.22
Investigation
P-Value
0.007
0.018
0.091
0.098
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Int J Med Invest 2014; vol 3; num 4; 127-132
in the control people and 154.19±38.58 mg/dL in the
spraying people. Mean level of triglyceride in the
control and spraying people was 123.00±57.58
mg/dL and 127.77±76.03mg/dL, respectively. Based
on the statistical analyses (Table 1), there was no
significant difference between these two study groups
in terms of blood cholesterol and triglyceride levels.
HDL values did not show any significant differences
between the two groups, but LDL in the spraying
group was significantly lower than control group
(P>0.05). However, LDL/HDL ratio in the spraying
population was lower than that in control population
(P=0.017).
In order to investigation of the pesticides destructive
effects on hematological systems complete blood
count (CBC) were analyzed. Complete blood count
was measured in both groups, which no significant
difference were found between two groups. These
data are presented in Table 2. According to this table,
leucocytes and erythrocytes, hemoglobin, hematocrit
and other parameters were not significantly different
between the control and spraying people.
Analysis of the data related to blood sugar and urea
did not show any significant difference between the
control and case groups (Table 3). There was
insignificant increase in ureic acid level among the
case group. On the other hand, the results of serum
creatinine showed significantly decrease (P>0.05) in
the case group compared with the control one.
Low level of creatinine among spraying people can
result from their malnutrition, which causes the
reduction of creatinine production in these people
(16). The results obtained from the study of thyroid
function are shown in Table 4. T 3 hormone levels in
the spraying and control people were 1.12 ±0.52
nmol/1
and
1.55±0.57nmol/1,
respectively.
Considering the results, it can be stated that T 3
hormone level in the spraying people was
significantly less than that in the control group
(P=0.018). In addition, T 4 hormone level in the
spraying people (9.29±2.12 μg/dl) decreased
compared with the control people (10.85±2.82 μg/dl),
which was not significant (P=0.091). TSH level was
2.64±1.50 mIU/l in the spraying people and
1.33±0.83 mIU/l in the control people, which
demonstrated significant increase compared with the
control group (p=0.007). This increase of TSH level
confirms the occurrence of hypothyroidism reported
in many studies.
The results obtained from TSH measurement
revealed that the percentage of spraying people with
TSH level>6mIU/l has been around 7%, which is
relatively higher than that of the control group.
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4. Discussions
Pesticides are widely used all over the world to
increase agricultural yield. Therefore, every person
maybe exposing to these compounds to some extent;
however, farming workers are the group with the
maximum exposure. Although acute effects of
exposure to pesticides have been specified, their role
in chronic diseases has not been well established.
Pesticides have destructive effects on different
organs, and consequently cause hematological and
biochemical changes (17). Effect of some of these
chemical compounds on animals has been well
identified, but there is little information about
humans. Farmers and spraying people are close in
touch with pesticides in different ways, which are
susceptible to endocrine dysfunction (18). Despite
using protective equipment in pesticides involved
industries, it is possible that people are exposed to
particles, liquid or powder of these pesticides at their
workplaces. Most of the studies focused on the effect
of pesticides on acetyl cholinesterase and many
papers have referred to the inhibition of this enzyme
by pesticides. Some documents have demonstrated
that exposure to the environment with pesticides is a
risk factor for thyroid diseases (6, 11).
TSH measurement is the first useful test for
evaluating thyroid function. Other measurements
such as T3 and T4 would complement diagnosing of
thyroid disorders. High sensitive measurement of
TSH along with T3 and T4 estimation in this study
allowed the evaluation of thyroid function in the
spraying groups exposed to pesticides.
Some insecticides, herbicides and fungicides disrupt
endocrine system. Thyroid disruptors affect through
different mechanisms (19). It has been shown that
some thyroid disruptors inhibit thyroperoxidase;
thereby they change ability of follicular cell in
producing T4 and then T3, even at sufficient iodine
concentration. Animal studies have revealed that
amitrol (herbicide), ethylenethiourea (fungicide),
Mancozeb (fungicide), bean isoflavones and
benzophenone
2
inhibit
production
of
thyroperoxidase and prevent thyroglobulin synthesis.
Therefore, T3 and T4 synthesis is reduced (20). Many
chemical compounds have high structural similarity
to thyroxin and T3thereby they disrupt the binding of
thyroid hormones to their receptors or transfer
proteins. This case can in turn result in subclinical
hypothyroidism, which is randomly diagnosed in
adults due to its mild symptoms.
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Int J Med Invest 2014; vol 3; num 4; 127-132
Animal
studies
have
demonstrated
that
organophosphorus
pesticides
change
brain
neurotransmitters, which finally change function of
thyroid gland (21, 22). However, there are few
studies on the relationship between non-persistent
pesticides exposure and thyroid function in humans.
There is no study considering thyroid disorders in
pesticide sprayers of Mazandaran Province, in which
agriculture is common. In northern regions, the effect
of pesticide absorption is higher due to high
temperature and humidity. Nevertheless, due to the
large particle size, it is not possible for pesticide to
reach alveolar space. Therefore, their absorption by
lungs is prevented. In contrast, skin is the important
path of absorption because of lipophilic nature of the
pesticides.
However,
humid
environmental
conditions lead to dilated skin vessels and lack of
protective cover would complicates the problem.
Participant in this study declared that they do not use
suitable covers while spraying in hot seasons due to
humidity.
As can be evident in this study, T 4/T3ratio in the
spraying people was insignificantly more than control
ones. Considering T4/T3ratio, it can be stated that
likely disorder may be peripheral conversion of T 4 to
T3, which occurred in spraying people. Therefore,
changes in the TSH, T3 and T4 levels may result of
stimulation of the thyroid hormone synthesis or
changes in peripheral conversion of T 4. Based on
present study, T4 to T3ratio in the spraying people
was more than that in the control ones, which can be
due to less conversion of T4 to T3. Anyway; the
people studied in this work seemed to be healthy. The
results of this study suggested that exposure to
organophosphorus and organochlorine pesticides,
which are the most widely used pesticides, may
changes serum level of TSH, total T 4 and total T3 in
human in the long-term. In another study conducted
in Mexico, the relationship between urine
concentration of dialkyl phosphate and TSH and
thyroid hormone level was examined among farmers
(21-23). Other studies have demonstrated that
greenhouse workers absorb much of the pesticides
during handling of pesticide. Thus, the rate and
amount of chemical exposure is very important. In
this study, some sprayers had longer work experience
than others. In these people, TSH level was more
than 4.5mIU/l, which indicative of hypothyroidism.
Considering different studies, it can be stated that
inhibition of TSH and TRH synthesis through
negative feedback can be affected by exposure to
pesticides. This issue maybe the possible cause of
high TSH level in the sprayers despite their normal
T4level.
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What is evident is that minimizing of the exposure to
pesticides and considering the safety comment can
minimize the influence of these pesticides.
Animal studies have shown that exposure to
pesticides such as dichlorodiphenyldichloroethane
(DDT), amitrol and thiocarbamate related compounds
resulted in decreased free and total T 3 and T4along
with the increased of TSH level (21, 22, 24-26).
Both lindane and chlordane are organochlorine
insecticides, which have been reported to affect the
level of thyroid hormones in human (7, 8). It has
been showed that increased chlordane level in breast
milk is related to higher level of congenital
hypothyroidism17.Malathion is an organochlorine
insecticide, which influences thyroid hormone level
in freshwater fish and tadpoles (12, 13).
Experiments have shown that maneb/mancozeb
causes hypothyroidism in rabbits (14). Working
people who were exposed to ethylenethiourea
demonstrated low level of total T 4significantly (27).
In other studies on people exposed to ethylene bis
dithiocarbamate without protection, TSH level
increased but T4 levels did not show any significant
difference compared with control group (15).
Paraquat is one of the most widely used herbicides,
which is generally used for controlling the broad
leave grass. There is also a relationship between
paraquat herbicide and hypothyroidism. Analysis of
the people intoxicated with paraquat showed a
measurable source of paraquat in their thyroid glands,
which was higher in women compared with men
(15).
Considering the present study and other studies, there
is growing concern about public health due to long
term exposure to even low level of organophosphorus
and organochlorine compounds. Therefore, providing
of information on the risk of exposure to toxic
chemicals used in agriculture would be helpful in
preventing and developing of complications.
Conclusions:
All kinds of pesticides are used around the world as
insecticide and pesticide against the variety of
agricultural crops in all seasons. Therefore, it is
valuable to perform this study for investigating of the
effect of pesticides on endocrine system and thyroid
function. Based on this study, it is concluded that
pesticide spraying without considering safety issues
could result in hypothyroidism. Finally, it is
suggested that farmers be trained about appropriate
use of pesticides to prevent their side effects. It is
also advised a thorough planning to use food
supplements in order to protect people against
harmful factors of workplaces, despite of intensified
physical protective instrument, suitable cover at the
time of exposure to pesticides.
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Int J Med Invest 2014; vol 3; num 4; 127-132
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