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http://tih.sagepub.com/Toxicology and Industrial Health
http://tih.sagepub.com/content/25/7/479The online version of this article can be found at:
DOI: 10.1177/0748233709345942
2009 25: 479Toxicol Ind HealthRamazan Yilmaz, Recep Sutcu and Sadettin Caliskan
Bumin Dundar, Gokhan Cesur, Selcuk Comlekci, Ahmet Songur, Alparslan Gokcimen, Onder Sahin, Ozlem Ulukut, H.development and IGF-1 levels in female Wistar rats
The effect of the prenatal and post-natal long-term exposure to 50 Hz electric field on growth, pubertal
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The effect of the prenatal and post-natallong-term exposure to 50 Hz electricfield on growth, pubertal developmentand IGF-1 levels in female Wistar rats
Bumin Dundar1, Gokhan Cesur2, Selcuk Comlekci3, Ahmet Songur4,Alparslan Gokcimen5, Onder Sahin6, Ozlem Ulukut3, H Ramazan Yilmaz7,Recep Sutcu8 and Sadettin Calıskan2
AbstractTo investigate prenatal and post-natal effects of extremely low frequency (ELF) electric field (EF) on growth and pub-ertal development, pregnant Wistar rats were randomly distributed among three groups. The pregnant rats of theprenatal group were exposed to 24-hour EF at 50 Hz EF 10 kV/min during pregnancy and their subsequent randomlyselected female pups continued to be exposed until puberty. The post-natal group was unexposed to EF during preg-nancy, but randomly selected female pups from this group were exposed to EF between delivery and puberty at thesame doses and duration as the prenatal group. The third group was a sham-exposed group. The mean birth weightand weight gain of the pups during study period were found significantly reduced in prenatal group than post-nataland sham-exposed groups (p < 0.001). No difference could be found among the three groups for body weight atpuberty (p > 0.05). The mean age at vaginal opening and estrous were significantly higher at prenatal group thanpost-natal and sham-exposed groups (p < 0.001). Serum insulin-like growth hormone-1 (IGF-1) levels were foundsignificantly reduced in prenatal exposure group compared with the other two groups (p < 0.001). There was nodifference for birth weight, weight gain, the mean age at vaginal opening and estrous and IGF-1 levels betweenpost-natal and sham-exposed groups (p > 0.05). There was also no difference for FSH, LH and E2 levels at pubertyamong the three groups (p > 0.05). Histological examination revealed that both the prenatal and post-natal groupshad the evidence of tissue damage on hypothalamus, pituitary gland and ovaries. In conclusion, early beginning ofprenatal exposure of rats to 24 hours 50 Hz EF at 10 kV/m until puberty without magnetic field (MF) resulted ingrowth restriction, delayed puberty and reduced IGF-1 levels in female Wistar rats. These effects probably associ-ated with direct toxic effects of EF on target organs. Post-natal exposure to EF at similar doses and duration seems tobe less harmful on target organs. Post-natal exposure to EF at similar doses and duration seems to be less harmful.
Keywords50 Hz, electric field, extremely low frequency, growth, IGF-1, puberty
1 Department of Pediatric Endocrinology, Suleyman Demirel University, Cunur, Isparta, Turkey2 Department of Physiology Faculty of Medicine, Suleyman Demirel University, Cunur, Isparta, Turkey3 Department of Electronics and Communication Engineering, Suleyman Demirel University, Cunur, Isparta, Turkey4 Department of Anatomy, Kocatepe University, Afyon, Turkey5 Department of Histology and Embriology, Suleyman Demirel University, Cunur, Isparta, Turkey6 Department of Pathology, Kocatepe University, Afyon, Turkey7 Department of Medical Biology, Suleyman Demirel University, Cunur, Isparta, Turkey8 Department of Biochemistry, Suleyman Demirel University, Cunur, Isparta, Turkey
Corresponding author:Bumin Dundar, Department of Pediatric Endocrinology, Faculty of Medicine, Suleyman Demirel University, Cunur 32260, Isparta,Turkey. Email: [email protected]
Toxicology and Industrial Health25(7) 479–487ª The Author(s) 2009Reprints and permission: http://www.sagepub.co.uk/journalsPermission.navDOI: 10.1177/0748233709345942tih.sagepub.com
479
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Introduction
Since the numbers of electromagnetic devices have
increased due to industrial development during last
decades, the intensity and variety of exposure to elec-
tric fields (EF) and/or magnetic fields (MF) of organ-
isms living in land have grown dramatically.
Therefore, their possible biologic effects on human
health have continued to be a controversial issue and
have continued to receive increasing scientific interest.
The electric power frequency chosen was of 50 or
60 Hz. These frequencies can be placed in the band of
extremely low frequency. The effects of extremely
low frequency electromagnetic field (EMF) on biolo-
gical parameters, in vivo and in vitro, have been
reported in many studies, but most of the recent stud-
ies focused on the side effects of MF components
(World Health Organization, 1984; Repacholi and
Greenebaum, 1999). There is a lack of data regarding
the biologic effect of pure EF in the current literature.
Whereas, exposure to extremely low frequency (ELF)
EF without MF is not rare in daily life and some prod-
ucts like the electric charges and power lines may
interact with or produce EF in live cells, which result
in enormous dielectric responses.
Many post-natal biological events are programmed
at the intrauterine life and it is well known that expo-
sure to environmental agents at this period usually may
affect prenatal and post-natal growth, and development
of neurological and reproduction systems of fetus ini-
tially (Barker, 1995; Hales and Barker, 2001).
Although the accepted exposure limit is about 10 kV/
m at power frequencies for EF (World Health Organi-
zation, 1984; ICNIRP, 1998), it should be taken into
consideration that the organism may be more sensitive
to the effect of environmental agents during pregnancy.
For this reason, the effects of prenatal exposure of ELF
EF on prenatal and post-natal growth have been inves-
tigated in several studies (Sikov et al., 1984; Portet and
Cabanes, 1988; Rommereim et al., 1989, 1990).
Although the majority of well-conducted studies have
failed to demonstrate any adverse effects of EF and/
or EMF exposure on growth and development, con-
flicting results have also been reported. On the other
hand, some important peptides like insulin-like growth
hormone-1 (IGF-1) that has an important role on the
growth of dams in prenatal and post-natal life, which
were evaluated in a small part of these studies and
inconsistent results have been obtained about the effect
of EF on IGF-1 levels (Rodriguez et al., 2002; Burch-
ard et al., 2004, 2007)
The reproductive system has been thought of as a
major target of EMF and the effect of EMF on repro-
ductive system of humans and animals have also been
investigated in many studies (Rommereim et al., 1989,
1990; Juutilainen, 2005; Al-Akhras et al., 2006; Khaki
et al., 2006; Cao et al., 2006; Davis et al., 2006). How-
ever, most of these studies generally have addressed
the effects of EMF on reproduction and fertility and its
relation to MF. The possible effects of long-term expo-
sure to ELF EF, especially on pubertal development,
have not been evaluated adequately yet.
This study was designed to investigate the effects
of prenatal and post-natal long-term 24-hour exposure
to 50 Hz ELF EF on prenatal and post-natal growth,
pubertal development, IGF-1 levels, and some endo-
crine glands related to puberty, such as hypothalamus,
pituitary gland and gonads of female Wistar rats.
Materials and methods
Study design
The study was approved by the Institutional Review for
Animal Research Board of Suleyman Demirel Univer-
sity and was conducted in accordance with the institu-
tional guidelines. Twenty-four 5-month-old female
Wistar albino rats were mated with 24 male rats in the
study. Each rat was placed into the cage overnight with
a male rat, and the first 24-hour period following the
mating procedure was designated as day 0 of pregnancy.
Firstly, all pregnant female rats were placed into
one cage and they were randomly distributed among
three groups (n ¼ 8) as prenatal, post-natal and
sham-exposed (control) groups. The pregnant rats of
prenatal group were exposed to 24-hour EF at
50 Hz EF 10 kV/min during pregnancy and their pups
continued to be exposed to EF after delivery. The
post-natal group was unexposed to EF during preg-
nancy, but the pups from this group were exposed to
EF at delivery. The third group was the sham-
exposed group. Pups that were born in the field
remained with their dams through the suckling period.
At 21 days of age, eight female rats from each group
were subsequently randomly selected and isolated.
The female pups from prenatal and post-natal groups
continued to be exposed to 24-hour EF at 50 Hz EF
10 kV/min. Female pups selected from the control
group were sham exposed to EF until puberty. Blood
samples were obtained and rats decapitated when
vaginal opening and estrous were detected.
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All pups were fed with breast milk and standard
food during the first 21 days of their lives. After
weaning, rats in all groups were continually fed with
standard food. All animals were fed ad libitum and
subjected to normal daylight cycles (08.00-20.00) at
normal room temperature (21-22�C). During experi-
ments, all animals were provided with the same feed-
ing and watering process. Groups were kept at the
same environmental conditions (humidity (55-60%),
temperature, light intensity and electromagnetic
fields). In the same room, the sham-exposed and
exposure groups were separated by custom-made
stainless steel shield (Figures 1 and 2).
According to the standards and regulations of Insti-
tute of Electrical and Electronic Engineers (IEEEE)
and World Health Organization (WHO), power fre-
quency exposure limit is 10 kV/m (World Health
Organization, 1984; ICNIRP, 1998). For this reason,
we decided to use about 10 kV/min EF intensity in
power frequency, 50 Hz, pure EF condition in this
study.
All animals had EF exposure for a duration of 24
hours a day. These animals were exposed to EF during
life in the experimental room.
The weight of the rats was measured weekly and
genital examinations were performed twice a day to
determine vaginal opening after 15 days of age. Vagi-
nal smear was taken to evaluate cornified epithelium
after vaginal opening. The day of vaginal opening and
determination of cornified epithelium were recorded
as the time of the onset of the puberty.
At the end of the study, all animals were decapi-
tated under ether anesthesia. Blood samples were
collected from the inferior vena cava and separated
by centrifugation at 3000 rpm for 10 min, and the
serum was stored at �80� C until use. At the end of
the procedure, the rat brains (right hemispheres),
pituitary glands and ovaries (right) were removed
immediately for histological examination.
Electric field application set-up
Exposure system: In this study, a custom-made paral-
lel plate exposure system was used. It was planned,
constructed and tested in the Antennas and Propaga-
tion Laboratory of Department of Electronics and
Communication Engineering at Suleyman Demirel
University. From the basic electromagnetic theory,
the E field lines in a set of parallel plate and field
between them is highly uniform. The plates’ effective
area is 0.5 m2 (0.5 � 1.0 m) and space between the
plates is d(variable 0.1-1.0 m) to avoid changing
value of field between plates at power frequency
range (Comlekci, 2006) This set-up is suitable to
use for small animal studies because the size of a
Figure 1. Schematic view of the electric field application set-up.
Figure 2. The appearance of the electric field applicationset-up.
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6-8-animal cage is about 40 � 50 � 20 cm3 (w � l �h), with 2 mm thickness. A perfect conductor (stain-
less steel) was used in construction of plates because
free surface charges can be homogenous in order to
get uniform fields.
The set-up was schematically illustrated in
Figure 1. The EF strength was calculated according
to the equation E ¼ Vd
where E is electric potential
between the plates, d is the distance, and E is the
EF intensity in volt/meter. The corners were rounded
to get rid of corruptions due to end effect. They were
placed upright on wooden stands and positioned paral-
lel to each other. In order not to disturb the field, leads
were connected to the center of the plates on their outer
sides (Aydin et al., 2006; Okudan et al., 2006).
In the exposure system, a step-up transformer rated
220 Vrms/5000 Vrms and 1000 VA was used. The
plates were spaced at 50 cm in distance. Cages were
adequately sized to ensure free movement of rats and
their pups, hence homogenous shielding of each other.
In addition to weekly cleanups of the plates and cages,
the set-ups were frequently scrutinized for gross soil
and wetness that would disturb the homogeneity of
EF. The attenuation due to routine soiling could be
estimated to cause very small variation in EF. From
the equation above, average EF density, between the
plates, were calculated to be 5000 V/0.5 m ¼10,000 V/m (10 kV/m) in EF group. Multimeter (Max
3000 TRMS Model Chauvin Arnoux, Paris, France)
was used for voltage measurements. Primary voltage
of power transformer, secondary voltage and EF den-
sity were in the range of 219-229 Vrms, 4975-5202
Vrms and 9951-10405 V/m, respectively. Digital
Gauss/Tesla Meter (Unilab, Blackburn, UK) was
used to test the purity of EF from background MFs.
Maximum MF density was about 0.001 mT. In the
experiment room, unwanted high-frequency fields
were tested by using HI-3804 Electromagnetic Field
Survey Meter-Industrial Compliance Meter and its
probe (Holaday Industries, Inc, UK).
Histopathological examination
Hypothalamus and pituitary gland: Specimens were
fixed in 10% neutral buffered formaldehyde solution.
After dehydration procedures, the samples were
blocked in paraffin. Five micrometer thick sections
of hemispheres including the hypothalamus and pitui-
tary were cut by a microtome and stained with
hematoxylin-eosin. Mounted slides were examined
under a light microscope (Nikon Microscope
ECLIPSE E600W, Tokyo, Japan) and photographed
using a digital camera (Microscope Digitale Camera
DP70, Tokyo, Japan). In the evaluation of hypothala-
mus sections, the distribution apoptotic changes
(pycnosis and karyorhexis), edema, cellular disorga-
nization and vacuolization were defined as criteria.
Apoptotic changes reduced in basophilic and acido-
philic cells ratio (normally 1/5) and vascular conges-
tion was defined as criteria in the pituitary gland.
These criteria were scored 0-3 (no, low, moderate and
high, respectively) as semi-quantitatively.
Ovaries: Ovarian tissues were fixated in 10% neu-
tral formaline solution. After performing routine tissue
processing procedures, samples were embedded in par-
affin blocks. For microscopic evaluation, 15 sections
were cut from each block by using systematical rando-
mized sampling method. All sections were stained with
hematoxyline-eosine dye. Stained sections were exam-
ined under Olympus-BX 50 light microscope.
Hormone analysis
Follicle stimulating hormone (FSH), luteinizing hor-
mone (LH) and estradiol (E2) were measured in
Architect System (2002 Abbott, Germany) by chemi-
luminescense method for the quantitative determina-
tion on the human serum. IGF-1 levels were also
analysed using chemiluminescense assay by Immulite
2000 kits (BIODPC, LA, USA).
Statistical analysis
SPSS 11.0 software for Windows was used for statis-
tical analysis of the data. The data were presented as
means + standard error of mean (SEM). Kruscal-
Wallis and Mann-Whitney U tests were performed for
group comparisons. p Values of less than 0.05 were
considered as statistically significant.
Results
The data of the mean body weight at delivery and pub-
erty, weight gain during study period and age at vaginal
opening and estrous of the pups at prenatal, post-natal
and sham-exposed groups are shown in Table 1.
The mean birth weight and weight gain during study
period were found significantly reduced in the prenatal
group compared with the post-natal and the sham-
exposed groups (p < 0.001). There was no difference
for the mean birth weight and weight gain during study
period between the post-natal and sham-exposed
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groups (p > 0.05). Body weights of the three groups at
puberty were not significantly different (p > 0.05).
The mean age at vaginal opening and estrous of
three groups are shown in Table 1. Age at vaginal
opening and estrous were significantly higher in prena-
tal groups than in post-natal and sham-exposed groups
(p < 0.001). Vaginal opening time of the post-natal and
sham-exposed groups were similar (p > 0.05).
Serum FSH, LH and E2 levels of groups at puberty
are presented in Table 2. No significant difference for
these hormonal parameters could be detected (p > 0.05).
Serum IGF-1 levels were shown in Figure 3. IGF-1
levels were found significantly reduced in prenatal
exposure group (p < 0.001). No significant difference
was present in IGF-1 levels of the post-natal and the
sham-exposed groups (p > 0.05).
The results of the histopathological examinations
of the hypothalamus and pituitary glands are summar-
ized in Table 3. Increases in degenerative changes
including apoptotic changes, edema, cellular disorga-
nization, vacuolization, reduce in basophilic and acid-
ophilic cells ratio (normally 1/5) and vascular
congestion were determined in prenatal and post-
natal groups. The degenerative signs for both tissues
were more evident in prenatal group than post-natal
exposure group (Figures 4 and 5).
Normal follicles cannot be seen in cortical region
of ovarian tissue obtained from the prenatal and
post-natal groups. There are some other follicles with
developmental degeneration, connective tissue
increment and fibrosis. Especially the primordial and
primary follicles are absent in both groups.
Table 2. Serum FSH, LH and E2 levels of three groups atpuberty
Prenatal Post-natal Control p
FSH (IU/L) 1.05 + 0.1 1.21 + 0.3 1.44 + 0.6 >0.05LH (IU/L) 0.96 + 0.12 1.11 + 0.2 1.22 + 0.31 >0.05E2 (pg/mL) 21.4 + 0.92 23.8 + 2.1 20.8 + 1.55 >0.05
FSH, follicle stimulating hormone; LH, luteinizing hormone; E2,estradiol.
Table 1. The mean body weight at delivery, weight gain per month during study period and the age at vaginal opening andestrus of the pups at prenatal, post-natal and control groups
Prenatal Post-natal Control p
The mean body weight at delivery (g) 3.07 + 0.07 4.80 + 0.08 5.6 + 0.09 <0.001The mean body weight at vaginal opening (g) 72.3 + 4.3 73.3 + 2.3 70.6 + 6.3 >0.05Weight gain per month during study period (g) 21.20 + 2.6 27.610 + 1.8 32.3 + 2.1 <0.001Age at vaginal opening (day) 93.7 + 3.9 71.7 + 4.79 67.7 + 3.52 <0.001Age at estrous (day) 93.8 + 3.9 81.2 + 4.2 68.6 + 3.1 <0.001
Figure 3. Serum insulin-like growth hormone-1 (IGF-I)levels of the three groups at puberty (9.4 + 2.6, 24.33 +5.3 and 30.2 + 6.5 ng/mL, respectively, p < 0.001).
Table 3. The semiquantitative histopathological scores incontrol, prenatal and post-natal magnetic fields groups’hypothalamus and pituitary
Prenatal Post-natal Control
HypothalamusApoptotic changes 3 1 0Edema 2 2 0Cellular disorganization 2 2 0Vacuolization 2 3 1
Pituitary glandApoptotic changes 3 2 2Reduce in basophilic
and acidophiliccells ratio
2 1 0
Vascular congestion 2 1 1
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Discussion
Although there are a few conflicting results about the
adverse effects of EF and/or EMF on growth and
development, the majority of the previous studies
involved large group size using 60 Hz or 50 Hz EF,
and field strengths from 10 to 150 kV/m reported no
adverse effect on growth and development. Portet and
Cabanes (1988) reported that exposure to 50 Hz
50 kV/m EF did not induce significant effects on
growth and development in 8-week-old male rats
exposed 8 hours per day for 4 weeks or rabbits
exposed 16 hours per day from the last 2 weeks of
gestation to 6 weeks after birth. In their other study,
application of 50 Hz EF on rabbits with a dose of
8 hours per day started 6th day of gestation resulted
in no any body and organ growth retardation (Portet
et al., 1984). In contrast, Rommerein et al. (1990)
observed slightly depressed weight gain of dams dur-
ing gestation and more weight loss during lactation
period in rats exposed to 60 Hz EF in high field
strengths. Although the presence of MF makes this
study different from our study, a recent study per-
formed by Cao et al. (2006) reported slower body
weight increase in offsprings prenatally exposed to
50 Hz, 1.2 mT 8 hours per day EMF than the sham-
exposed group in the first 2 weeks of life. In this
study, lower birth weight, reduced post-natal growth
and delayed puberty with reduced levels of IGF-1,
have been observed in pups of rats exposed to long-
term 24/hour 50 Hz 10 kV/m EF during prenatal and
post-natal period compared with post-natal and sham-
exposed groups. However, our study seems to be in
discordance with the majority of data of previous
studies. It is clear that our inconsistent results might
be associated with the differences in animals in used
Figure 5. The representative photomicrographs pituitary gland sections are subjected to prenatal (A), post-natal (B) andcontrol (C). VC, vascular congestion; black arrow, acidophilic cell; and white arrow, basophilic cell, hematoxylin-eosin(H/E) �200 CI.
Figure 4. The representative photomicrographs of hypothalamus sections are subjected to prenatal (A), post-natal (B)and control (C). Black arrow, vacuolization; white arrow, hematoxylin-eosin (H/E) �200.
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previous studies. On the other hand, we think that
starting off exposure to 50 Hz EF at the first day of
pregnancy and 24 hour/day exposure differentiate our
study from most of the previous studies and might
explain how these adverse effects occurred especially
the in prenatal exposure group. It is well known that
timing and duration of environmental effects are very
important during prenatal period.
In this study, while the adverse effects of ELF EF on
growth and pubertal development of prenatal group
have been clearly detected, these parameters for the
post-natal exposed group were found similar with the
sham-exposed group. Our results seem to be consistent
with the literature reporting the lack of the adverse
effect of EF exposure on post-natal and adult life (Juu-
tilainen, 2005). These data indicate that the side effects
of ELF EF on growth and development are more
important, especially during the early prenatal period.
The absence of post-natal catch-up growth of pups
on the prenatal exposure group in the present study
could bring to mind that intrauterine growth was
affected in early stage of embryogenesis in prenatal
EF exposed group. The genotoxic potential effects of
EF and MF, which have been reported previously, sup-
port our consideration (McCann et al., 1998).
It has been known that IGF-1 has a very important
role on fetal and post-natal growth. The variations in
IGF-1 levels associated with EMF exposure have
been reported in a few previous studies. Rodriguez
et al. (2002) observed increased IGF-1 levels in preg-
nant lactating cows exposed to 16 hours vertical EF of
60 Hz 10 kV/m and a horizontal MF of 30 mT. How-
ever, the study of Burchard et al. (2004) did not con-
firm these results in which IGF-1 levels on pregnant
dairy heifers exposed to 10 kV/M 60 Hz EF could not
been detected significantly different than sham-
exposed groups. Nevertheless, in their recent study,
slight decrease in concentration of IGF-1 of pregnant
dairy heifer was reported with 60 Hz and 30 mT EMF
exposures (Burchard et al., 2007). IGF-1 levels were
found significantly lower in prenatal exposure group
than the post-natal and sham-exposed groups in this
study. It can be thought that the lack of catch-up
growth of prenatal exposure rats might be associated
with low IGF-1 levels. To explain how EF caused
reduced IGF-1 levels is difficult. It may depend on the
toxic effect of EF on target organs. On the other hand,
we think that reduced IGF-1 levels might also be
related to maldigestion and/or malabsorbtion associ-
ated with EF effects. Because there is a close relation-
ship between IGF-1 levels and nutrition as well as
growth hormone levels, and nutritional status is the
most important factor during prenatal and early
post-natal life and body weight losses under restricted
diets are associated with reduction in IGF-1 blood
concentrations (Turan et al., 2007; Leon et al.,
2004). However, we did not measure food consump-
tion in the present study and it seems to be the limita-
tion of our study. To clarify the reason of low IGF-1
levels associated with EF, more studies are needed.
There are conflicting results regarding the effects
of ELF EF without MF on reproduction in the litera-
ture. Rommereim et al. (1987) found a statistically
significant decrease in fertility of female rats exposed
to 60 Hz 100 kV/m EF. Nevertheless, they could not
show similar effects on reproduction of rats with
exposure of 60 Hz 150 kV/m EF in their another
study (Rommereim et al., 1989). A significant reduc-
tion in the fertility of adult male and female Sprague
Dawley rats was found after 90 days of exposure to a
50 Hz, 25 mT EMF (Al-Akhras et al., 2001). Hong
et al. (2003) has also reported adverse effects on
reproduction in male rats at similar doses. However,
another study did not confirm these results at the same
doses (Elbetieha et al., 2002). In a recent study, Al-
Akhras et al. (2006) reported a significant decrease
in sperm count, the weights of seminal vesicles and
testosterone levels in the exposed male rats and sug-
gested that long-term exposure to ELF could have
adverse effects on mammalian fertility and reproduc-
tion. There is a lack of study investigating the effect of
ELF EF on pubertal development. In a previous study,
the vaginal opening time of female rats exposed to
ELF EMF has been reported to be identical with that
of the sham-exposed groups (Chung et al., 2004).
However, delayed puberty was detected in the prena-
tal exposure group compared with post-natal and
sham-exposed groups in the present study. As men-
tioned before, it can be considered that intrauterine
growth retardation and absence of catch-up growth
with low IGF-1 levels might lead to delay in puberty
in prenatal exposure group. The presence of statisti-
cally identical levels of FSH, LH and E2 of three
groups at puberty support this point of view. How-
ever, histological evidence of degenerative findings
in hypothalamus and pituitary gland which were
clearer especially, in pre-natal exposure group and
ovaries indicate that direct toxic effect of ELF EF
on target organs might also contribute to this condi-
tion. We think that degenerative findings on these tis-
sues might be related to the effect of EF on membrane
transport mechanisms and electropermeabilization of
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the cells, which can cause biochemical and physiolo-
gical changes in the cell. Because it has been shown
that application of EF to the cell may cause exceeding
in threshold value of the transmembrane potential and
allowing entrance of molecules that otherwise cannot
cross the membrane and further increase in EF inten-
sity may cause irreversible membrane permeabiliza-
tion and cell death (Mir, 2001; Valic et al., 2003).
All side effects have been seen in lower strength
field in this study compared with other studies. This
finding shows that beginning and duration of exposure
time seems to be the more important factors than the
severity of strength field in prenatal side effects of EF.
In conclusion, exposure to 50 Hz 10 kV/sec EF
from the beginning of prenatal period until puberty
without MF resulted in growth restriction, delayed
puberty and reduced IGF-1 levels in female Wistar
rats. Further studies are needed to explain the effect
of 50 Hz EF on intrauterine and post-natal growth,
pubertal development and relation to growth factors.
Acknowledgement
This study was supported by Suleyman Demirel University
Scientific Research Projects Unit (project number: 1052-
m-05).
References
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