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Age-dependent lower or higher levels of hair mercury in autistic children than in healthy controls

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Abstract

An association between autism and early life exposure to mercury is a hotly debated issue. In this study, 91 autistic Polish children, male and female, 3-4 and 7-9 years old, were compared to 75 age- and sex-matched healthy children with respect to: demographic, perinatal, clinical and developmental measures, parental age, birth order, morphometric measures, vaccination history, and hair mercury content. In demographic and perinatal measures there were no consistent differences between the autistic and control groups. Autistic children had a significantly greater prevalence of adverse reactions after vaccinations and abnormal development than controls. Between 45 and 80% of autistic children experienced developmental regress. Autistic children significantly differed from healthy peers in the concentrations of mercury in hair: younger autistics had lower levels, while older - higher levels than their respective controls. The results suggest that autistic children differ from healthy children in metabolism of mercury, which seems to change with age.
Research paper Acta Neurobiol Exp 2010, 70: 196–208
© 2010 by Polish Neuroscience Society - PTBUN, Nencki Institute of Experimental Biology
INTRODUCTION
Autism spectrum disorders (ASDs) represent a
group of neurodevelopmental disorders typified by
impairments in verbal and non-verbal communication,
social withdrawal and stereotypical behaviors, which
may or may not be associated with cognitive deficits,
self-injurious behaviors and other neurological comor-
bidities. The current world-wide epidemic of ASDs
and other neurodevelopmental disorders, including
attention deficit hyperactivity (ADHD), learning dis-
abilities, and mental retardation constitute the most
disturbing public health problems (Robison et al. 1999,
Merrick et al. 2004, Altarac and Saroha 2007, Shayer
et al. 2007, Hertz–Picciotto and Delwiche 2009). Its
magnitude is best illustrated by a dramatic rise in inci-
dences of ASDs in the past 25 years. In many countries
current ASDs prevalence is about 1 in 100, whereas in
the 1970s and early 1980s it was about 1 in 2500-3000
(Merrick et al. 2004, Baird et al. 2006, Gillberg 2009).
It is estimated that only about 5% of the autistic popu-
lation carries identifiable genetic /chromosomal defects
(Newbury et al. 2009). The increase of ASDs preva-
lence cannot be fully explained by advances in diag-
nostics or sudden genetic shifts. There is a growing
consensus among scientists and clinicians that ASDs
ensue from an interaction between biological vulnera-
bility factors and environmental or iatrogenic insults
(James et al. 2006, Gillberg 2009).
The contemporaneous emergence of the ASDs epi-
demic and the introduction of several new infant vac-
cines in the late 1980s and the 1990s, generated a
suspicion that these events might be linked. One of the
agents suspected in autism etiology is an organomer-
cury compound, thimerosal (THIM; sodium ethyl-
mercurithiosalicylate containing approximately 49%
Age-dependent lower or higher levels of hair mercury
in autistic children than in healthy controls
Maria Dorota Majewska1*, Ewa Urbanowicz3, Paulina Rok-Bujko3, Irena Namysłowska3,
Paweł Mierzejewski2
1Marie Curie Chair, Department of Pharmacology and Physiology of the Nervous System, Institute of Psychiatry
and Neurology, Warsaw; *Email : majewska@ipin.edu.pl; 2Department of Pharmacology and Physiology of the Nervous
System, Institute of Psychiatry and Neurology, Warsaw, Poland; 3Department of Child and Adolescent Psychiatry,
Institute of Psychiatry and Neurology, Warsaw, Poland;
An association between autism and early life exposure to mercury is a hotly debated issue. In this study, 91 autistic Polish
children, male and female, 3-4 and 7-9 years old, were compared to 75 age- and sex-matched healthy children with respect
to: demographic, perinatal, clinical and developmental measures, parental age, birth order, morphometric measures,
vaccination history, and hair mercury content. In demographic and perinatal measures there were no consistent differences
between the autistic and control groups. Autistic children had a significantly greater prevalence of adverse reactions after
vaccinations and abnormal development than controls. Between 45 and 80% of autistic children experienced developmental
regress. Autistic children significantly differed from healthy peers in the concentrations of mercury in hair: younger autistics
had lower levels, while older – higher levels than their respective controls. The results suggest that autistic children differ
from healthy children in metabolism of mercury, which seems to change with age.
Key words: autism, mercury, hair, thimerosal, vaccines, development
Abbreviations: THIM - thimerosal
Correspondence should be addressed to M. D. Majewska,
Email: majewska@ipin.edu.pl
Received 19 January 2010, accepted 1 June 2010
Hair mercury in autistic children 197
of Hg by weight), which has been used as a vaccine
preservative for decades without being comprehen-
sively tested for its safety in developing organisms. A
large body of research and at least two centuries of
human experience show that all forms of mercury are
highly toxic to vertebrates. In the body THIM is
metabolized to ethylmercury and then into inorganic
mercury compounds (Qvarnstrom et al. 2003).
Significant amounts of mercury have been measured
in the blood of infants after inoculations with THIM-
containing vaccines, with premature infants accumu-
lating over 3 times more mercury than the mature
ones (Stajich et al. 2000, Pichichero et al. 2008).
Studies conducted with infant monkeys injected with
THIM-containing vaccines showed that a few days
after vaccinations, concentrations of mercury in the
brain were several times higher than those in blood.
Mercury levels in the brain may remain markedly
increased for many months or years, considering con-
tinuous re-exposure to vaccines (Burbacher et al.
2005). Mid-nanomolar concentrations of mercury,
which are likely to be reached in the infant brain after
inoculation with THIM-containing vaccines, are neu-
rotoxic (Parran et al. 2005, Yel et al. 2005).
The preclinical study of Hornig and coauthors
(2004) documented multiple neurodevelopmental dis-
turbances in mice prone to autoimmune diseases after
exposure to THIM doses analogous to those used in
pediatric vaccines. Our recent study showed that
administration of similar doses of THIM to suckling
rats causes persistent disruption of endogenous opioid
system (Olczak et al. 2009), which resembles opioid
dysfunction in autism (Sandyk and Gillman 1986,
Sandman 1988). Based on numerous analogies of bio-
logical and clinical abnormalities associated with mer-
cury poisoning and autism, the hypothesis emerged
linking this disorder with early life exposure to mercu-
rials (Bernard et al. 2001, Mutter et al. 2005). Some
epidemiological and ecological studies associated
autism and other neurodevelopmental disorders with
THIM present in infant vaccines (Geier and Geier
2003, 2006, Young et al. 2008, Gallagher and Goodman
2008, 2009). Other studies denied such a link (Hviid et
al. 2003, Madsen et al. 2003), but they were criticized
for flawed design and clear conflict of interests (Mutter
et al. 2005, Isaacs 2010).
Measurement of heavy metal content in hair is often
used as a marker of exposure, because it correlates
with past blood levels (Clarkson 1993, Magos and
Clarkson 2008). As a non-invasive procedure, it is
especially useful for testing children. A few studies
compared mercury levels in hair of autistic and healthy
children, reporting divergent results. Holmes and
coauthors (2003) and Adams and colleagues (2008)
demonstrated significantly lower levels of mercury in
first baby haircuts of American children diagnosed
with autism, than in healthy controls, which was inter-
preted as possibly impaired mercury and other toxin
elimination by autistic children. Reduced levels of
heavy metals such as arsenic, cadmium, lead and mer-
cury in hair of autistic children 1-6 years old were also
measured by Kern and others (2007). In contrast,
strikingly higher levels of hair mercury in autistic
Kuwaiti boys (4 to 7 years old) than in healthy controls
were detected by Fido and Al-Saad (2005). Higher
concentrations of this metal were also found in baby
teeth and blood of autistic children than in controls
(Adams et al. 2007, Desoto and Hitlan 2007).
Although several studies point to a link between
autism and mercury exposure (Mutter et al. 2005,
Geier and Geier 2006, Windham et al. 2006, Young et
al. 2008, Palmer et al. 2009), the critical sources of this
metal and its role in autism pathogenesis are a subject
of hot debates, particularly in reference to possible
iatrogenic effects of THIM from vaccines and mercury
from amalgam fillings. Continuing controversy and
public apprehension regarding this issue impelled us to
conduct our own study in Polish children, who con-
tinue to be inoculated with THIM-containing vac-
cines. We were particularly interested in identifying
possible demographic, perinatal and/or vaccination-
related factors, which distinguish autistic from healthy
children. In order to assess them we analyzed several
birth-related measures such as Apgar scores, body
weight, head and chest circumference, Rh conflict, as
well as abnormal development in autistic and healthy
children of both sexes from two age groups (3-4 and
7-9 years old). We also compared their history of vac-
cinations, adverse reactions to them, and levels of
mercury in hair.
METHODS
Study Participants
The study was carried out in accordance with the
Declaration of Helsinki of the World Medical
Association. The protocol was approved by the Ethics
198 M. D. Majewska et al.
Committee for Human Studies at the Institute of
Psychiatry and Neurology. Participation in the study
was voluntary. The parents of participants read and
signed informed consent forms after the study proce-
dures had been fully explained to them.
Autistic and control children of both sexes from two
age groups, 3-4 and 7-9 years old were enrolled into
the study. The subjects were not compensated for their
participation. The autistic participants were recruited
from the children earlier diagnosed with autism in out-
patient clinics in Poland. Healthy control children were
recruited from 6 preschools and 3 primary Warsaw
schools. Recruitment took place from November 2007
to April 2009. All participants were Caucasians, about
40% of autistic children were from Warsaw metropoli-
tan area, others were from different, mostly urban, but
some from rural regions located at distances less than
180 km from Warsaw. The autistic children had to
fulfill DSM IV criteria for autistic disorder, and score
at least 30 points in the CARS scale (see later).
Participants were excluded if they had: a neurological
and psychiatric disorder other than autism and comor-
bid disorders; history of liver, renal or endocrine disor-
der; current infection of respiratory tract or fever state
of any origin; and mental retardation. Mental retarda-
tion or behavioral disorders, including hyperkinetic
disorder in children over 6 years old or significant
symptoms of hyperactivity, impulsiveness or restless-
ness in younger children were exclusion criteria only
for the group of healthy control children, but were
allowed as comorbid condition in the autistic cohort.
Children diagnosed with Asperger’s syndrome were
excluded from the study. Study participants were
divided into two groups. Group I was male and female,
autistic and control children 3-4 years old, and group
II – similar children 7-9 years old.
Clinical evaluation
Each autistic child was once more diagnosed by a
group of three specialists (2 psychologists and one
child psychiatrist), who had over five years experi-
ence in autism diagnosis. The examination consisted
of semi-structured interview with parents and 1 hour
observation of the child’s behavior. Extensive medical
histories of the autistic and control children were
taken. The parents were asked about: detailed history
of pregnancy and labor, mental and motor develop-
ment of the child, any illnesses and traumatic events,
history of vaccinations, the occurrence of vaccine-
associated adverse effects (if present, parents were
asked about their subjective appraisal of observed
symptoms and about results of medical professional
consultations). Additional information about birth
morphometric measures, Apgar scores, vaccinations
and development was taken from Child Health
Notebooks, which every child born in Poland receives
at the hospital and which carries his/her health infor-
mation until the age of 18 years. The parents of autis-
tic children were also questioned about the first
symptoms of autism, which occurred in their child,
and the results of previous diagnostic tests. The clini-
cal evaluation of autistic children was based on a one-
hour observation of their behavior by two expe r ienced
psychologists. The diagnosis of autism was made
according to the Diagnostic and Statistical Manual of
Mental Disorders (DSM–IV) criteria for autism or
pervasive developmental delay (PDD) by a trained
professional. The activity and functioning of an autis-
tic child was also assessed according to Childhood
Autism Rating Scale (CARS) (Schopler et al. 1980)
and the Clinical Global Impression Scale. Children
who scored 30 or more points in CARS were diag-
nosed as autistic.
All control study participants were assessed with
use of the Abbreviated Parent-Teacher Questionnaire
(IOWA-Conners; version for scientific research
(Conners 1969, Rowe and Rowe 1997) in order to
exclude children with symptoms of ADHD (diagnosis
was made according to DSM IV criteria).
Measurement of mercury concentration in hair
Haircut samples of autistic and control study par-
ticipants were obtained from occipital area of head,
from the proximal (up to 3 centimeters from scalp) part
of hair. The blinded analysis of mercury content in hair
by atomic absorption spectrometry was performed at
the Chemical Laboratory of Multi-Elemental Analyses
at Wroclaw University of Technology. A single-pur-
pose atomic absorption spectrometer based on in situ
dry washing followed by gold amalgamation cold
vapor AAS method was used for analysis using an
Advanced Mercury Analyzer (AMA-254, ALTEC,
Czech Republic). This cold vapor AAS method is one
of the most widely used techniques for determination
of trace amounts of total mercury in environmental
materials.
Hair mercury in autistic children 199
Table I
Demographic data on study participants
Demographics Males Females p (t-Student, U-M-W
or χ2)
GROUP I (age 3-4 years) Autistic Control Autistic Control
N 30 19 25 19
Mean age 3.6 ± 0.1 3.5 ± 0.1 3.8 ± 0.1 3.6 ± 0.1
Weight at birth (g) 3441 ± 103 3358 ± 159 3295 ± 73 3281 ± 108
Head circumference at birth (cm) 34.3 ± 0.3 33.7 ± 0.5 34.0 ± 0.3 33.3 ± 0.4
Gestational age at birth (weeks) 38.7 ± 0.3 38.8 ± 0.7 39.2 ± 0.3 39.2 ± 0.4
Apgar score 9.5 ± 0.3 9.3 ± 0.3 9.6 ± 0.4 9.9 ± 0.1
Birth order 1.4 ± 0.1 1.5 ± 0.2 1.6 ± 0.2 1.3 ± 0.1
Mother’s age at birth 28.9 ± 0.6 28.4 ± 0.8 27.3 ± 0.9** 31.4 ± 0.8 p<0.01
Father’s age at birth 30.9 ± 0.7 31.3 ± 0.9 28.9 ± 1.0* 33.2 ± 1.3 p=0.01
GROUP II (age 7-9 years) Autistic Control Autistic Control
N 23 18 13 19
Mean age 8.2 ± 0.1 8.4 ± 0.2 7.9 ± 0,2 8.4 ± 0.1
Weight at birth (g) 3329 ± 183 3486 ± 151 3066 ± 183* 3402 ± 108 p=0.02
Head circumference at birth (cm) 33.9 ± 0.7 34.3 ± 0.5 33.2 ± 0.6 33.7 ± 0.4
Gestational age at birth (weeks) 38.2 ± 0.7 38.8 ± 0.4 38.7 ± 0.6 39.4 ± 0.4
Apgar score 8.7 ± 0.5 9.4 ± 0.2 9.0 ± 0.4 9.6 ± 0.2
Birth order 1.4 ± 0.1 1.7 ± 0.2 2.3 ± 0.8* 1.2 ± 0.1 p=0.03
Mother’s age at birth 27.3 ± 0.7 28.3 ± 1.0 28.5 ± 1.4 27.3 ± 0.9
Father’s age at birth 29.5 ± 0.8 30.0 ± 0.9 30.3 ± 1.3 28.7 ± 0.8
Autistic and control study participants were divided into two age-groups, as indicated. Statistically significant
differences between autistic and control groups are denoted by (*) and (**).
200 M. D. Majewska et al.
Statistics
The STATISTICA software package for Windows
(StatSoft, Tulsa, OK, USA) was used to analyze all d ata.
Student’s t-test was used when means of data from two
groups were compared. U–Mann-Whitney test was
used for comparisons of nonparametric data, McNemar’s
test with χ2 statistics was applied for categorical vari-
ables (‘yes’ or ‘no’). For comparisons of mercury levels
in hair 2-way ANOVA (disease x age) was utilized.
Newman-Keuls test was used for individual post-hoc
comparisons. Results with p-level less than 0.05 were
considered significant. The results are presented as
mean ± standard error of mean (SEM).
RESULTS
Demographics and birth-related measures
Altogether 91 autistic children and 75 age- and sex-
matched healthy control children were enrolled into
the study. The demographic data on participants is
shown in Table I. There were no statistically signifi-
cant age differences at the time of psychiatric exami-
nation and collection of specimens between the autistic
and control groups. Most autistic and control children
did not differ significantly with respect to their birth
weights, except for a slightly lower weights of autistic
girls from group II (p=0.02). Also head circumference
at birth was not significantly different between autistic
and control children, although in group I, both in
males and females, there was a trend for slightly larger
head size in autistics than in controls. This difference
did not reach statistical significance ( p=0.07). Likewise,
Apgar scores were not statistically significantly differ-
ent between autistic and control children, except that
there appeared to be a tendency for slightly lower val-
ues for autistic children from group II. The only statis-
tically significant difference in Apgar scores was
between control males and females, with females hav-
ing higher scores (p=0.04). The autistic and control
groups did not vary significantly with respect to their
Table II
Comparison or clinical features between autistic and control children and between autistic males and
females within each age-group
Clinical Features Males Females p (t-Student , U-M-W
or χ2)
GROUP I (age 3-4 years) Autistic Control Autistic Control
Allergies (%) 50 22.7 38.5 36.8
Number of vaccines till Year 2 24.5 ± 0.9 23.6 ± 0.7 24.6 ± 0.6 24.2 ± 0.6
Maximal number vac. at once 5.0 ± 0.2 4.8 ± 0.1 4.8 ± 0.1 5.1 ± 0.2
Vaccine complications (%) 38.5* 4.5 15.4 5.3 p=0.03
Abnormal development (%) 26.2** 0 32** 0 p<0.01
Regress (%) 80.8 81
Hyperactivity (%) 26.9 34.6
CARS total scores 43.6 ± 1.3 45.5 ± 1.2
DSM IV A 9.2 ± 0.3 9.6 ± 0.2
Autism-vaccine connection (%) 19.2 15.4
Hair mercury in autistic children 201
birth order, except again for the females from group II,
who were of higher order (2.3) than controls (1.2;
p=0.03). Autistic and healthy groups also did not
diverge significantly with respect to parental age at
child’s birth, except for autistic girls from group I, who
had slightly younger parents than the controls (p
0.01).
Clinical parameters
Comparisons of major clinical features of autistic
and control children are shown in Table II. There was
a good correlation between CARS and DSM IV autism
diagnostics (r=0.74). In the younger group of autistic
children CARS and DSM IV scores were not notably
dissimilar between males and females. However, in the
older group of autistic children, the females appeared
to be more impaired, as evidenced by their statistically
significantly higher CARS scores than those in males
(p<0.02). Generally, autistic and control children did
not diverge significantly in the number of vaccinations
received up to the 24th month of life, except for the
autistic girls from the group II, who received fewer
vaccinations (p<0.001) due to more frequent vaccine
adverse events.
Autistic children from combined groups I and II
experienced significantly more vaccine complications
(20.4%) than controls (6.5%). This difference was sta-
tistically significant (χ2=6.75; p=0.009 (Table III). It
was particularly pronounced in the males from group
I, where 38.5% of autistics had adverse reactions to
vaccines, while in the control group only 4.5% mani-
fested such reactions (p=0.03, Table II). Vaccine com-
plications reported by parents of autistic children
included: high fever, prolonged crying, extended hypo-
activity and hypotonicity, loss of contact, loss of facial
mimicry, sleepiness, circling around, loss or ability to
walk, point or talk, developmental regress, emergence
of autistic behaviors. The vaccines most frequently
associated with these adverse reactions, were: DTP,
DTP-polio, DTP-Hib, DTP-polio-Hib, MMR, pneu-
mococcal vaccine. A few adverse vaccination events
reported by parents of control children included: skin
reaction, crying and fever. Autistic patients also
Clinical Features Males Females p (t-Student , U-M-W
or χ2)
GROUP II (age 7-9 years) Autistic Control Autistic Control
Allergies (%) 50 40 33.3 33.3
Number of vaccines till Year 2 22.3 ± 0.7 24.2 ± 0.7 20.2 ± 0.9** 24.2 ± 0.5 p<0.001
Maximal number vac. at once 4.6 ± 0.1 4.8 ± 0.1 4.3 ± 0.1* 4.9 ± 0.1 p=0.03
Vaccine complications (%) 16.7 10 26.7 9.2
Abnormal development (%) 52 11 66.6** 0 p<0.01
Regress (%) 45.8 0 80 0
Hyperactivity (%) 50 40
CARS total scores 38.7 ± 1.2* 44.3 ± 1.8 p=0.02
DSM IV A 10.0 ± 0.3 10.0 ± 0.3
Autism-vaccine connection (%) 12.5 26.7
Autistic and control study participants were divided into two age-groups, as indicated. Statistically significant
differences between autistic and control groups, or between autistic males and females are denoted by (*) and (**).
202 M. D. Majewska et al.
diverged from controls in developmental characteris-
tics, where 40.9% of autistics versus 3.9% of controls
were reported to have abnormal development (χ2=30.6;
p<0.001). Among autistic cohort developmental regress
was noted in about 80%, except for the males from
group II, where it was 46% (Table II). Comorbid
hyperactivity was diagnosed in approximately 30% of
the autistic children from group I, and in 45% of such
children from group II. Among autistic boys the fre-
quency of allergies (reported by parents) also appeared
to be slightly higher than in controls, but the distinc-
tion was not statistically significant.
Hair mercury content
Autistic and control children from both age-groups dif-
fered noticeably in the concentration of mercury in hair
(Fig. 1). In group I, hair mercury levels were lower in
autistic than in control children, but the situation was
opposite in group II, where autistics had higher levels than
controls ( p=0.01). Consequently, there appeared to be
opposing developmental trends between autistic and con-
trol children with respect to change of hair mercury levels.
In autistics these levels increased with advancing age
(from 3-4 to 7-9 years), whereas in controls – decreased.
DISCUSSION
This study compared autistic and healthy control
children of both sexes aged 3-4 and 7-9 years with
respect to perinatal morphometric and clinical mea-
sures, abnormal development, vaccination history and
mercury content in hair. The results point to statisti-
cally significant differences between autistic and con-
trol cohorts in three major categories. Autistic children
had: 1) greater prevalence of abnormal development;
2) more frequent vaccine complications; 3) different
concentrations of mercury in hair (younger autistics
had lower levels, while older – higher levels than their
age-matched controls).
For three out of four experimental (age-sex) com-
parison groups, the demographic and birth morpho-
metric measures of autistic children were not statisti-
cally significantly different from the controls. Only the
Table III
Comparison of combined groups of autistic and control children
Autistic (M+F)
Groups I + II
Controls (M+F)
Groups I + II
p
Vaccine complications (%) 20.4* 6.5 p=0.009
Abnormal development (%) 40.9* 3.9 p<0.001
Caesarian or pathological birth (%) 32 29 NS
Epilepsy (%) 5.5 1.2 NS
Potential Rh conflict (%) 8 12 NS
Genetic load (%) 12 5 NS
Nonparametric measures: Comparison of nonparametric measures between combined groups of autistic and control
children. Information about epilepsy, potential genetic load and potential Rh conflict is based on parental interviews. M
= males, F = females. Statistically significant differences are denoted by (*).
Hair mercury in autistic children 203
autistic girls from group II appeared at birth to be
somewhat more disadvantaged, as they weighed less
and were of a greater birth order than the controls.
Greater impairment of this group was also evidenced
by their higher CARS scores, when compared to autis-
tic boys from the same age-group. Moreover, in group
II, both autistic boys and girls had slightly lower Apgar
scores than controls, but these differences did not
reach statistical significance. Thus in the present
study, obvious perinatal disadvantage did not appear to
be a universal feature distinguishing the autistic from
the control children, although a slight tendency for
greater weakness at birth of some autistic children was
noted. Even though this difference was not statistically
significant for all experimental groups, its clinical sig-
nificance for autism development cannot be entirely
ruled out.
The most intriguing observation of this study is a
significant difference in concentrations of hair mer-
cury between autistic and control children, which was
present in both age-groups, albeit with opposite devel-
opmental trends. In the autistic children, hair mercury
levels were lower at a younger age and increased with
development, whereas in the control children these
levels were higher at a younger age and declined with
development. In humans mercury content in hair is a
biomarker of past exposure (Clarkson 1993, Gosselin
et al. 2006), although hair appears to be a minor route
of elimination of heavy metals from the body (Magos
and Clarkson 2008). Typically hair mercury levels cor-
relate with blood levels, but not necessarily with the
burden to various tissues and the whole body (Nielsen
et al. 1994). Studies with infant monkeys and rats
showed that particularly organomercurials, which eas-
ily penetrate the blood brain-barrier and cell mem-
branes, accumulate in the brain and other vital organs
in much larger amounts than are present in blood, and
they can stay in these organs for months or years
(Burbacher et al. 2005, Olczak et al. 2009). The cor-
relation or ratios of blood and hair mercury levels may
be lessened in persons with inefficient cellular mecha-
nisms of metals’ elimination. Such a pattern was
reported in autistic children (DeSoto and Hitlan
2007).
Our finding of lower concentrations of mercury in
the hair of younger autistic children than in that of the
healthy controls are qualitatively similar to the data of
Holmes and colleagues (2003) and Adams and coau-
thors (2008) concerning first baby hair of American
children. Lower hair levels of heavy metals, including
mercury, in autistic children (1-6 years old) were also
measured by Kern and others (2007). On the other
hand, our results pertaining to older children – demon-
strating higher mercury levels in the hair of autistic
than control children – are comparable to the findings
of Fido and Al-Saad (2005) in Kuwaiti boys (4-7 years
old). It is important to stress, however, that the simi-
larities with the latter study are only qualitative. While
the concentrations of mercury in hair of control
Kuwaiti boys (0,3 μg/g) were of the same order as in
our study participants, the levels measured in autistic
Kuwaiti children were 15 times higher (4,5 μg/g).
These children must have been exposed to an extreme-
ly toxic environment, as they also had greatly increased
levels of lead and uranium in their hair. Opposite
developmental trends of hair mercury levels in autistic
and healthy children may explain why in some studies,
which used children of mixed ages, the difference in
hair mercury levels between these cohorts was statisti-
cally insignificant (Kern et al. 2007, Ip et al. 2004).
DeSoto and Hitlan (2007), who reanalyzed the dataset
of Ip and coworkers (2004) that was originally ana-
lyzed with error (Wong 2007) found a significant cor-
relation of autism diagnosis with higher levels of mer-
cury in blood, but not in hair in Chinese children
approximately 7 years old.
Fig. 1 Different levels of mercury in hair of autistic and
healthy children from age groups I and II. The histogram
shows mean values ± SEM. Statistically significant differ-
ences between autistic and control groups are denoted by
(*), (p=0.01). Crossing lines point to divergent develop-
mental trends of change in hair mercury levels between the
autistic and control groups.
204 M. D. Majewska et al.
We did not scrutinize in detail the sources of mer-
cury exposure in our study participants. It could be
both prenatal and postnatal. Only one child – an autis-
tic girl from the group II had 5 amalgam fillings,
which was highly unusual, as such procedures have
been rarely used in children in Poland during the past
10 years. One of the greatest sources of prenatal mer-
cury exposure, which increases vulnerability to autism,
is the number and the age of maternal amalgam fill-
ings (Drasch et al. 1994), because these fillings for
years release significant amounts of mercury vapor,
which is easily absorbed by the lung tissue into the
body. Also, mercury level in breast milk is inf luenced
by the number, size and age of maternal dental amal-
gams. Over time of amalgam exposure, mercury accu-
mulates in body tissues (Mutter et al. 2007).
Furthermore, dental treatments during pregnancy
(cleaning, polishing, insertion or removal of amalgam
fillings) markedly increase maternal and fetal expo-
sure to mercury.
From our data, there appeared to be no significant
difference in the numbers of amalgam fillings between
mothers of autistic and healthy children. Fifty-five
percent of mothers of healthy children and 58% of
mothers of autistic children did not have any amal-
gams. Others had from 1 to 8, but there was no sig-
nificant difference between these two groups. We have
no data regarding the age and size of maternal amal-
gam fillings, nor dental treatments during pregnancy.
Therefore a possible influence of dental amalgam
exposure during pregnancy and body burden of the
infants at the time of birth cannot be excluded. In the
studies of Holmes and coauthors (2003) and Geier and
coworkers (2009b), dental amalgams during pregnancy
increased the risk for autism or the risk for a high
severity of autism. Nonetheless, it seems rather unlike-
ly that maternal amalgams would significantly inf lu-
ence mercury levels in hair of children 3-9 years old.
The most significant source of mercury exposure in
the studied population is from THIM-containing vac-
cines, the environment, including foodstuffs, and
breast milk for the younger group. In this study, we
have not examined the influence and duration of breast
feeding of amalgam bearing mothers. Even though we
did not scrutinize the diets of autistic and healthy chil-
dren, they were not reported to be markedly different
with respect to potential methylmercury sources,
although some autistic children were on gluten, casein
and sugar free diets as part of their therapy. None of
the children have undergone chelation treatment.
Evaluation of the types of vaccines received by autistic
and control children also did not show significant dif-
ferences, suggesting that both groups were probably
exposed to comparable doses of mercury from vacci-
nations.
Distinct levels of hair mercury in autistic and con-
trol children from the same age groups may result
either from dissimilar environmental exposure or dif-
ferences in efficiency of elimination of this metal.
While the first possibility cannot be entirely ruled out,
the second appears more probable. Since older chil-
dren receive fewer vaccinations than younger, hair
mercury content in 7-9 years old would be expected to
be lower than in the younger group. Such a pattern was
indeed observed in the control, but not in the autistic
children, where it was opposite. Our data seem consis-
tent with the notion that young autistic children might
be poor eliminators of heavy metals hence showing
lower mercury levels in the hair but may retain
greater amounts of mercury in their body tissues,
including the brain (Holmes et al. 2003, Adams et al.
2007, 2008). At adrenarche their toxin elimination
capacity may improve, as reflected by higher levels of
mercury in hair of older autistic children.
Vertebrates have several mechanisms of elimina-
tion and detoxification of heavy metals. They include
a system of sulfur containing molecules, such as
sulfhydryl- aminoacids and peptides – cysteine and
reduced glutathione as well as sulfates (Clarkson
1993, Bernard et al. 2001). Glutathione, synthesized
by all mammalian cells is believed to serve as a pri-
mary heavy metal detoxifying molecule, which is
excreted in bile as glutathione-metal complexes
(Refsvik and Norseth 1975, Ballatori and Clarkson
1985). These sulfur-compounds are synthesized in
various tissues, predominantly in the liver via the
methionine transmethylation and transsulfuration
metabolic pathways (Clarkson 1993, James et al.
2005). The mechanisms of mercury binding by
cysteine and glutathione and its detoxification are
complex, regulated by sex, age, genetic factors, and
diets (milk diet decreases mercury excretion)
(Rowland et al. 1984, Thomas et al. 1986, Clarkson
1993). Other heavy metal detoxifying molecules are
cysteine rich proteins, metallothioneins (Piotrowski
et al. 1974, West et al. 2008), the expression of
which changes during postnatal development reach-
ing adult levels in prepubertal age (Waalkes and
Hair mercury in autistic children 205
Klassen 1984). These factors may explain lower
rates of heavy metals’ excretion by suckling animals
than by adults (Doherty et al. 1977, Ballatori and
Clarkson 1982, Lok 1983), as well as our finding of
apparently improved mercury elimination by older
autistic children, as reflected by higher mercury
levels in their hair.
Several studies reported deficiencies in autistic chil-
dren metabolism of sulfur compounds, lower plasma
concentrations of endogenous metabolites of transm-
ethylation and transsulfuration such as methionine,
S-adenosylmethionine, cysteine and reduced glutathi-
one, but increased levels of oxidized glutathione and
S-adenosylhomocysteine (Alberti et al. 1999, Kidd
2002, James et al. 2006, Geier et al. 2009). Some of
these problems may ensue from the presence of sus-
ceptibility alleles, other may result from toxic effects
of mercurials per se (James et al. 2005, 2006).
Metabolic consequences of such defects include
reduced detoxification of heavy metals, hence their
increased toxicity, impaired methylation and redox
homeostasis, and increased oxidative stress (Kern and
Jones 2004, Zoroglu et al. 2004, James et al. 2006,
Geier et al. 2009a), which adversely influence brain
development and CNS functions.
Lower levels of mercury in hair of young autistic
children may suggest reduced ability to excrete metals,
resulting in high burden of mercury and increased vul-
nerability to its neurotoxic effects. This might ensue
from genetic factors or from certain comorbid patholo-
gies. For example, Prandota (2009) recently proposed
that autism spectrum disorders may be linked to cere-
bral toxoplasmosis, which results in hypercytokinemia
and makes infants more vulnerable to environmental
insults, including mercurials and vaccinations. This
intriguing hypothesis requires experimental verifica-
tion. A direct evidence for greater prenatal and postna-
tal mercury burden in autistic children comes from
research showing higher levels of this metal in baby
teeth of autistic children than in controls (Adams et al.
2007) and from a study documenting increased urinary
excretion of this metal by autistic children after treat-
ment with chelating agent (Bradstreet et al. 2003). Also
augmented concentrations of atypical urinary porphy-
rins (specific for mercury exposure) in autistic children
suggest heavy mercury burden (Woods et al. 2005,
Nataf et al. 2006, Geier et al. 2009a).
In our study participants, the source of mercury expo-
sure is probably mixed. Nonetheless, because THIM-
containing pediatric vaccines are still used in Poland
(although they were abandoned by most developed coun-
tries due to toxicity concerns), and the autistic children
manifested higher incidences of serious adverse reac-
tions to vaccinations, an iatrogenic effect of THIM in
this population is possible. Such effect was documented
in American boys immunized at infancy with THIM-
containing Hep-B vaccines, who were 9 times more
likely to suffer from learning disabilities than those who
did not receive these vaccines (Gallagher and Goodman
2008). Furthermore, vaccination of infant boys with
Hep-B vaccines tripled their risk of developing autism,
when compared to unvaccinated children (Gallagher and
Goodman 2009). The neurotoxic effect of THIM-
containing Hep-B vaccine was recently confirmed in
newborn monkeys, which after receiving its single dose
manifested delayed acquisition of vital neonatal reflexes
(Hewitson et al. 2009). In view of the growing body of
clinical and preclinical evidence of strong toxicity of all
forms of mercury in developing organisms, the removal
of THIM from all vaccines given to children and preg-
nant women is urgently required.
Strengths and limitations
The major strength of this study is its controlled
nature, uniformed selection of study participants from
the country, which still uses THIM in pediatric in vac-
cines, utilization of semistructured parental interview
and child diagnosis conducted by the same team of
experienced professionals, comprehensive inspection of
patients’ medical records, and use of age- and sex- dif-
ferentiated groups. The weaknesses include inability to
assess more accurately the sources of mercury exposure
and non-uniform selection of study participants: con-
trols were from one geographic region, while autistic
patients were from more diverse regions of Poland.
(Nonetheless, only one autistic child was from heavy
industrial region, but his level of hair mercury was not
markedly different from the rest of his age group).
CONCLUSION
Autistic and healthy children differ in prevalence of
abnormal development, frequency of adverse reactions
to vaccinations and concentrations of mercury in hair,
which change with development. The data indirectly
imply vaccinations and mercurials as potential factors
in autism pathogenesis.
206 M. D. Majewska et al.
ACKNOWLEDGEMENTS
We are grateful to the psychologists, M.S. Agnieszka
Lucjanek and M.S. Justyna Szczechowicz-Konciała for
help in diagnosis of autistic children; to Dr Michal
Wroniszewski, Dr Joanna Grochowska and Ms. Ursula
Rusilowicz from the Synapsis Foundation, and Dr
Anna Szymanska from the Navicula Foundation for
aid in recruitment of autistic patients. We thank Dr
Helena Gorecka from the Chemical Laboratory of
Multi-Elemental Analyses at Wroclaw University of
Technology in Poland for mercury analysis in hair.
This publication is a part of ASTER project funded
by the European Commission grant (MEXC-CT 2006-
042371) and by the supplementary grant from the
Ministry of Science and Higher Education of Poland,
both to Prof. Maria Dorota Majewska.
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... For the analysis of Hg level in hair, a total of 25 studies were included , encompassinf various geographic regions. Specifically, there were 7 studies conducted in Europe [70,71,74,76,80,85,88], 5 in North America [73,79,83,86,87], 9 in Asia [65][66][67]72,77,78,81,82,84], and 4 in Africa [68,69,75,89]. The meta-analysis of Hg levels in whole blood comprised 15 studies [78,86,[90][91][92][93][94][95][96][97][98][99][100][101][102][103], with 2 conducted in Europe [85,92], 5 in North America [91,95,96,98,99], 1 in Central America [97], 5 in Asia [77,91,93,100,101], and 2 in Africa [94,102]. ...
... (95% CI: −0.980, 0.115) and p = 0.122. Individual study effect sizes ranged from −47.909 (95% CI: −54.806, −41.012, p = 0.000) in the study by [88] to 1.548 (95% CI: 1.150, 1.945, p = 0.000) in the study by [83]. Relative weights and standard residuals for each study are presented in Figure 3. Relative weights ranged from 0.55% [88] to 4.36% [69], and standard residuals ranged from −12.65 [88] to 8.85 [89]. ...
... Individual study effect sizes ranged from −47.909 (95% CI: −54.806, −41.012, p = 0.000) in the study by [88] to 1.548 (95% CI: 1.150, 1.945, p = 0.000) in the study by [83]. Relative weights and standard residuals for each study are presented in Figure 3. Relative weights ranged from 0.55% [88] to 4.36% [69], and standard residuals ranged from −12.65 [88] to 8.85 [89]. High heterogeneity was observed with I 2 = 97.170%, ...
Article
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Mercury (Hg) is a non-essential trace metal with unique neurochemical properties and harmful effects on the central nervous system. In this study, we present a comprehensive review and meta-analysis of peer-reviewed research encompassing five crucial clinical matrices: hair, whole blood, plasma, red blood cells (RBCs), and urine. We assess the disparities in Hg levels between gender- and age-matched neurotypical children (controls) and children diagnosed with autism spectrum disorder (ASD) (cases). After applying rigorous selection criteria, we incorporated a total of 60 case-control studies into our meta-analysis. These studies comprised 25 investigations of Hg levels in hair (controls/cases: 1134/1361), 15 in whole blood (controls/cases: 1019/1345), 6 in plasma (controls/cases: 224/263), 5 in RBCs (controls/cases: 215/293), and 9 in urine (controls/cases: 399/623). This meta-analysis did not include the data of ASD children who received chelation therapy. Our meta-analysis revealed no statistically significant differences in Hg levels in hair and urine between ASD cases and controls. In whole blood, plasma, and RBCs, Hg levels were significantly higher in ASD cases compared to their neurotypical counterparts. This indicates that ASD children could exhibit reduced detoxification capacity for Hg and impaired mechanisms for Hg excretion from their bodies. This underscores the detrimental role of Hg in ASD and underscores the critical importance of monitoring Hg levels in ASD children, particularly in early childhood. These findings emphasize the pressing need for global initiatives aimed at minimizing Hg exposure, thus highlighting the critical intersection of human–environment interaction and neurodevelopment health.
... Autistic patients seem to have a different toxic metal metabolism than healthy individuals. People with ASD may have lower levels of glutathione, which the body needs to carry out its normal detoxifying processes (James et al., 2004;Majewska et al., 2010;Skalny et al., 2017a). It is essential to highlight that the conjugation of toxic metals with glutathione, which is notably lower in autistic cases, is required for toxic metal detoxification (Fiłon et al., 2020). ...
... (Qin et al., 2018) China Blood 34 38 Hg, Cd, and Pb • Hg, Cd and Pb levels were higher in people with autism than in healthy people. (Majewska et al., 2010) Poland Hair 91 75 Hg • Hg levels were lower in autistic than in control children (3-4 years of age). ...
... Twenty-five studies analyzed Hg in hair samples of ASD persons and their healthy controls. Twelve studies confirmed a positive connection (Al-Ayadhi, 2005;Blaurock-Busch et al., 2011;El-baz et al., 2010;Elsheshtawy et al., 2011;Fido and Al-Saad, 2005;Hodgson et al., 2014;Lakshmi Priya and Geetha, 2011;Mohamed et al., 2015;Nabgha-e-Amen et al., 2020;Tabatadze et al., 2015;Tinkov et al., 2019;Yassa, 2014), six studies showed a negative connection (Holmes et al., 2003;Kern et al., 2007;Majewska et al., 2010;Obrenovich et al., 2011;Skalny et al., 2017aSkalny et al., , 2017c, and no relationships were found in seven studies (Adams et al., 2006;Albizzati et al., 2012;Aljumaili et al., 2022;De Palma et al., 2012;Ip et al., 2004;Jung et al., 2008;Wecker et al., 1985). Hg in the (Shearer et al., 1982) USA Hair NA NA 0.5/1.3 ...
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Background and aim Autism spectrum disorder (ASD) is a neurodevelopmental illness characterized by difficulties in social communication and repetitive behaviors. There have been many previous studies of toxic metals in ASD. Therefore, the priority of this study is to review the relationships between exposure to toxic metals and ASD. Materials & methods This study was based on a comprehensive search of international databases, such as Web of Science, Science Direct, Scopus, PubMed, and Google Scholar, for all works related to the subject under discussion from 1982 to 2022. We further summarize published data linked to this topic and discuss with clarifying evidence that agrees and conflicts with the association between exposure to toxic metals, including mercury (Hg), lead (Pb), cadmium (Cd), arsenic (As), and aluminum (Al) and ASD. Results 40 out of 63 papers met the requirements for meta-analysis. Blood Pb levels (standardized mean difference (SMD) = 0.81; 95 % confidence interval (CI): 0.36–1.25), blood Hg (SMD = 0.90; CI: 0.30–1.49), hair Pb (SMD = 1.47; CI: 0.03–2.92), urine As (SMD = 0.65; CI: 0.22–1.09), and urine Al levels (SMD = 0.85; CI: 0.40–1.29) in autistic individuals were significantly higher than those of healthy control (HC). Whereas, blood As levels (SMD = 1.33; CI: −1.32–3.97), hair As (SMD = 0.55; CI: −0.14–1.24), hair Cd (SMD = 0.60; CI: −0.31–1.51), hair Hg (SMD = 0.41; CI: −0.30–1.12), hair Al (SMD = 0.87; CI: −0.02–1.77), urine Pb (SMD = −0.68; CI: −2.55–1.20), urine Cd (SMD = −0.26; CI: −0.94–0.41), and urine Hg levels (SMD = 0.47; CI: −0.09–1.04) in autistic individuals were significantly lower than those of HC. Conclusion Toxic metal content significantly differed between individuals with ASD and HC in the current meta-analysis. The results assist in clarifying the significance of toxic metals as environmental factors in the development of ASD.
... In another study, the blood of 34 and 35 children with autism was tested, and it was found that the lead and mercury levels in the children with autism were significantly higher than the corresponding levels in the controls. Studies have shown that zinc and manganese levels in hair are negatively correlated with autism in subjects, and the severity of autism symptoms is positively correlated with the presence of certain heavy metals such as lead and mercury [30][31][32]. ...
Article
Autism spectrum disorders (ASD) are a group of lifelong neurodevelopmental disorders characterized by cognitive deficits and impaired social and communicative development that have been rising in prevalence in recent decades. These disorders may be accompanied by disabling health issues and often lead to a substantial economic burden. The causes and mechanisms of ASD have not yet been fully elucidated, although it has been reported that genetic background, epigenetic modification, and environmental risk factors all contribute to the development of ASD. Environmental factors, which include prenatal circumstances or events, all play a very important role in the early development of autism, yet the exact mechanism remains largely undetermined. In this review, we promote a 'rethinking' of autism as a neurodevelopmental disease that originates from early life development. We focus on the impact of the prenatal and maternal risk factors such as maternal diabetes, prenatal chemical exposure, and hormone imbalances during pregnancy on the risk for ASD development in children and offspring, identifying important pathological bases and prevention measures for future decades. Further research focused on understanding the role of the environmental factors in the etiology of ASD will drive forward innovation strategies towards intervention and the prevention of the maternal risk factors for autism.
... A previous study found that the level of Hg in the hair of autistic children differed considerably from that of healthy children of the same age and gender. The younger children with ASD (3-4 years old) had lower Hg values in their hair, while the older ASD children (7-9 years old) had higher Hg concentrations than their corresponding control subjects [72,75], which was similar to our findings. Existing data also indicated that ASD children differed in Hg metabolism from healthy control children [76]. ...
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Existing data demonstrate a significant correlation between autism spectrum disorder (ASD) and the status of biologically essential and toxic trace elements. However, there is still a lack of data on the steady state of trace elements in ASD. We performed a case–control study to explore the association between the risk of ASD and 23 trace elements in plasma. The results showed that children with ASD had considerably decreased lithium (Li), manganese (Mn), selenium (Se), barium (Ba), mercury (Hg), and tin (Sn) levels when compared to their age- and sex-matched controls. Meanwhile, children with ASD had considerably increased plasma chromium (Cr) and vanadium (V) concentrations. We also divided each group into subgroups based on age and gender and created element-related networks for each subgroup. We detected significant element correlations within or between subgroups, as well as changes in correlations that included all elements examined. Finally, more element correlations were observed among males, which may open a new avenue for understanding the complicated process behind the sex ratio of children with ASD. Overall, our data revealed a novel relationship between elements and ASD, which may extend current understanding about ASD.
... Thimerosal, which contains approximately 49% mercury by weight and is composed of ethylmercury (EtHg) and thiosalicylic acid, is metabolized in the body to EtHg and further to inorganic forms of mercury (Qvarnström et al., 2003). Thimerosal is still present in vaccines intended for children and pregnant women in developing countries (Geier and Geier 2006;Majewska et al., 2010;Do´rea 2011). ...
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Background: Thimerosal and aluminum containing vaccines could be a significant etiological factor in the rising prevalence of neurodevelopmental disorders. Maternal stress has dramatic effects on the early programming of the physiology and behavior of newborn. Perinatal selenium supplementation appeared to be essential for the offspring antioxidant system. Objective: Therefore, the objectives of this study is to evaluate the effect of postnatal co-administration of thimerosal and Al(OH)3 on learning ability and memory retention of males offspring exposed to either normal and prenatal restraint stress condition, and to investigate whether maternal selenium supplementation could attenuate the neurotoxicity of the these utilized vaccines' additives. Methods: Dams of Sprague-Dawely rats were divided starting from the 7 th day of gestation into two cohort groups, non-stressed and stressed groups (subjected to restraint stress for 2 hrs daily from gestational day 7 to 20). Dams were orally administrated sodium selenite (200µg/kg/b.w) from GD7 to postnatal day (PND) 21. At postnatal days (PNDs 7, 9, 11 and 15), male offspring were intramuscularly administered thimerosal (12.5 µg/kg/b.w.) and Al(OH)3 (60 µgAl/kg/b.w.) in doses analogous to those used in pediatric vaccines. All male neonates of non-stressed or stressed dams were weaned at postnatal day 21, grouped as control, maternal selenium supplemented, postnatal thimerosal/Al(OH)3 and maternal selenium supplemented + postnatal Thimerosal/Al(OH)3 administrated groups. At PNDs 29-34, behavior assessments for learning and memory retention using Morris water maze test were performed. Brain dopamine level was estimated in different brain regions namely amygdala, prefrontal cortex, cortex and hippocampus as well as whole brain nitric oxide (NO) level were evaluated at PND30. Moreover, estimation of serum cortisol level and histopathological examination of brain cortex and hippocampus were performed. Results: The results revealed that, exposure to prenatal stress mainly induced learning and memory deficit. Postnatal thimerosal/Al(OH)3 impaired both learning and memory retention. These effects were exacerbated under prenatal stress condition and associated with neurochemical and brain histopathological changes. Conclusion: The present study reflected that male offspring exposed to chronic stress either prenatal restraint stress or postnatal thimerosal-Al(OH)3 administration exhibited neurotransmitters changes in brain region-specific manner associated with alterations in the behavioral performance indicating that these neurodisruptive/neurotoxic effects were mediated through different mediators or/and mechanisms. Finally, the removal of thimerosal and Al(OH)3 from vaccines must be approved according to the obtained results and as previously recommended by the American Academy of Pediatrics and the U.S. Public Health.
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This study was carried out on human hair samples that were collected from different areas of Basrah Governorate in the year 2009, (67 people of both genders). In the year 2010 (17 people of both genders. The two groups were divided into seven subgroups according to their age. Hair was analyzed for Na, K, Ca, Mg, , Hg, Pb, Cd ,U, Co Cu, As, Fe, Al and Zn; using ICP/Ms instrumentation at maxxam analytical INC , Canada. The results showed levels of most essential and heavy metals that were tested in the year 2009,and the metals tested in the year 2010 were higher than international levels. A significant difference have been observed P< 0.05 between the same group according to the age criteria. Significant differences were observed in between subgroups of the year 2009 Vs. 2010. The maximum reading of Hg, Pb, U, Cu, Ca, Mg, As and Co was found in subgroup (2), Fe and Zn in subgroups 4, 5 and 6 respectively for 2009. Samples from 2010,showed the maximum reading of Hg, Pb, Cd, Cu, Zn, Ca, and Co found in subgroup(3), whereas Fe, Mg, Al, and As, levels were high levels in subgroups 1,2 and 4. The high level of heavy metals seen in this study, reveals that these areas where samples were collected from are highly contaminated with these toxic and polluted materials. This high level needs intensive care from the government to protect the environment from these toxic and carcinogenic substances.
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The present study was conducted to investigate the differences in cadmium (Cd) and mercury (Hg) concentrations between children with autism spectrum disorder (ASD) and controls. In this systematic review and meta-analysis study, three thousand one hundred forty-five studies were collected from scientific databases including Web of Science, Scopus, PubMed, and Google Scholar from January 2000 to October 2022 and were investigated for eligibility. As a result, 37 studies published in the period from 2003 to 2022 met our inclusion criteria and were considered in the meta-analysis. The heterogeneity assumption was evaluated using the Chi-squared-based Q-test and I-squared (I²) statistics. The pooled estimates were shown in the forest plots with Hedges’ g (95% confidence interval) values. The random effects model demonstrated that there is no significant difference in the blood (Hedges' g: 0.14, 95% CI: 0.45, 0.72, p > 0.05), hair (Hedges' g: 0.12, 95% CI: 0.26, 0.50, p > 0.05), and urinary (Hedges' g: 0.05, 95% CI: 0.86, 0.76, p > 0.05) Cd levels of the case group versus control subjects. Moreover, the pooled findings of studies showed no significant difference in the blood (Hedges' g: 1.69, 95% CI: 0.09, 3.48, p > 0.05), hair (Hedges' g: 3.42, 95% CI: 1.96, 8.80, p > 0.05), and urinary (Hedges' g: 0.49, 95% CI: 1.29 – 0.30, p > 0.05) Hg concentrations. The results demonstrated no significant differences in Hg and Cd concentrations in different biological samples of children with ASD compared to control subjects.
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The European Commission asked EFSA to update its 2009 risk assessment on arsenic in food carrying out a hazard assessment of inorganic arsenic (iAs) and using the revised exposure assessment issued by EFSA in 2021. Epidemiological studies show that the chronic intake of iAs via diet and/or drinking water is associated with increased risk of several adverse outcomes including cancers of the skin, bladder and lung. The CONTAM Panel used the benchmark dose lower confidence limit based on a benchmark response (BMR) of 5% (relative increase of the background incidence after adjustment for confounders, BMDL05) of 0.06 μg iAs/kg bw per day obtained from a study on skin cancer as a Reference Point (RP). Inorganic As is a genotoxic carcinogen with additional epigenetic effects and the CONTAM Panel applied a margin of exposure (MOE) approach for the risk characterisation. In adults, the MOEs are low (range between 2 and 0.4 for mean consumers and between 0.9 and 0.2 at the 95th percentile exposure, respectively) and as such raise a health concern despite the uncertainties.
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Environmental factors have been associated with the etiology of autism spectrum disorder ASD in recent times. The involvement of toxic metals in the generation of reactive oxygen species and their epigenetics effects have been implicated in ASD. This systemic review examines the association of toxic metals with autism in children. A systematic literature search was performed in scientific databases such as PubMed, Google scholar, and Scopus. Case-control studies evaluating toxic metal levels in different tissues of ASD children and comparing them to healthy children (control group) were identified. The Newcastle–Ottawa Scale was used to evaluate the risk of bias of the included studies. Six case–control studies with 425 study subjects met our inclusion criteria. A total of four studies indicated higher levels of As, Pb, Hg, Cd, Al, Sn, Sb, Ba, TI, W, and Zr in whole blood, RBC, in whole blood, RBC, and hair samples of children with autism compared with control suggestive of a greater toxic metal exposure (immediate and long-term). Three studies identified significantly higher concentrations of Cd, Pb and Hg in urine and hair samples of autistic children compared to control suggesting decreased excretion and possible high body burden of these metals. The findings from this review demonstrate that high levels of toxic metals are associated with ASD, therefore, critical care is necessary to reduce body burden of these metals in children with ASD as a major therapeutic strategy.
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Large autism epidemics have recently been reported in the United States and the United Kingdom. Emerging epidemiologic evidence and biologic plausibility suggest an association between autistic spectrum disorders and mercury exposure. This study compares mercury excretion after a three-day treatment w ith a n o ral c helating a gent, m eso-2,3- dimercaptosuccinic acid (DMSA), in children with autistic spectrum disorders and a matched control population. Overall, urinary mercury concentrations were significantly higher in 221 children with autistic spectrum disorders than in 18 normal controls (Relative Increase (RI)=3.15; P < 0.0002). Additionally, vaccinated cases showed a significantly higher urinary mercury concentration than did vaccinated controls (RI=5.94; P < 0.005). Similar urinary mercury concentrations were observed among matched vacci- nated and unvaccinated controls, and no association was found between urinary cadmium or lead concentrations and autistic spectrum disorders. The observed urinary concentrations of mercury could plausibly have resulted from thimerosal in childhood vaccines, although other environmental sources and thimerosal in Rh (D) immune globulin administered to mothers may be contributory. Regardless of the mechanism by which children with autistic spectrum disorders have high urinary mercury concentrations, the DMSA treatment described in this study might be useful to diag- nose their present burden of mercury.
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This study investigated the association between vaccination with the Hepatitis B triple series vaccine prior to 2000 and developmental disability in children aged 1– 9 years (n ¼ 1824), proxied by parental report that their child receives early intervention or special education services (EIS). National Health and Nutrition Examination Survey 1999–2000 data were analyzed and adjusted for survey design by Taylor Linearization using SAS version 9.1 software, with SAS callable SUDAAN version 9.0.1. The odds of receiving EIS were approximately nine times as great for vaccinated boys (n ¼ 46) as for unvaccinated boys (n ¼ 7), after adjustment for confounders. This study found statistically significant evidence to suggest that boys in United States who were vaccinated with the triple series Hepatitis B vaccine, during the time period in which vaccines were manufactured with thimerosal, were more susceptible to developmental disability than were unvaccinated boys. Introduction Mercury (Hg) is a recognized neurodevelopmental toxicant (NRC 2000). Coal-fired power plants are a prime source of Hg emissions that aerosolize, travel through the atmosphere to waterways, are transformed by microorganisms into methyl Hg and consumed by fish, then magnify in the marine food chain (Trasande, Landrigan, and Schecter 2005). Pregnant women's consumption of seafood is the major route of in utero exposure to methyl Hg (Trasande, Landrigan, and Schecter 2005). Studies show an association between prenatal methyl Hg exposure and poor performance on cognitive tests (Grandjean et al. 1997). Researchers found that between 316,588 and 637,233 children each year have cord blood methyl Hg levels45.8 mg L À1 , a level associated with loss of IQ and a calculated corresponding loss of productivity equivalent to 8.7 billion dollars annually (Trasande, Landrigan, and Schecter 2005). Windam et al. (2006) reported an association between ambient air Hg levels and autism prevalence.
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Children with autism were examined to determine amounts of mercury (Hg) in their baby hair and the factors that might affect Hg body burden. US children with autism (n = 78) and matched controls (n = 31) born between 1988 and 1999 were studied. Hg in first-cut baby hair was determined using cold vapor atomic fluorescence spectrometry (CVAFS). Twenty samples were split and also measured with Neutron Activation Analysis (NAA). Logistic regression analysis showed that compared to children with higher levels of mercury (above 0.55 mcg g), children with lower levels of mercury in their hair (below 0.55 mcg g) were 2.5-fold more likely to manifest with autism. Children with autism had similar mercury exposure as controls from maternal seafood and maternal dental amalgams. Children with autism also had 2.5-fold higher incidence of oral antibiotic use during their first 18 months of life. Their mothers were possibly more likely to use oral antibiotics during pregnancy or nursing. The amount of Hg in the baby hair of children with autism showed a significant correlation with the number of maternal dental amalgams. The lower level of Hg in the baby hair of children with autism indicates an altered metabolism of Hg, and may be due to a decreased ability to excrete Hg. This is consistent with usage of higher amounts of oral antibiotics, which are known to inhibit Hg excretion in rats due to alteration of gut flora, and may exert a similar effect in humans. Higher usage of oral antibiotics in infancy may also partially explain the high incidence of chronic gastrointestinal problems seen in individuals with autism.
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During winter 1971-72 massive poisoning occurred throughout rural Iraq due to ingestion of homemade bread prepared from seed wheat treated with a methylmercury(CH3Hg) fungicide. Thousands of children and adults were poisoned and hundreds of deaths occurred (Science181:230,1973). Prenatal and early postnatal exposure were documented(Ped.54:5,1974!AJDC130:1070,1976)and long term followup studies of exposed fetuses and infants are in progress. Using a mouse model to determine potentially significant variables relating to CH3Hg toxicity in the developing mammal, we have observed that compared to adults, suckling mice excrete minimal amounts of their body burdens of mercury. Groups of young mice were exposed to a single non-toxic dose of CH3203Hg(0.4 mg/Kg. per os)at 2,4,6.., or 28 days of age. Whole body counts and urinary and fecal excretion were followed for each exposure group. From birth to 15 days, elimination half-times of mercury ranged from 2500 to 200 days. Between 16 and 18 days an abrupt increase to the adult elimination half-time of 8 days occurred. Decreases in whole body counts were accurately reflected in counts recovered in excreta. Studies are underway to determine whether a similar developmental change in excretion occurs in the exposed human infant. Since elimination half-time has been shown to be directly related to cumulative body burden as a function of duration of exposure, these observations are of importance in estimating exposure risks of human fetuses and infants.
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Recently established reference intervals demonstrate that blood mercury is significantly higher in women than in men. Mercury in blood and hair are both used as biomarkers for human methylmercury exposure and employed in risk assessment without considering possible sex-related differences in toxicokinetics of methylmercury. In an experimental study using male and female mice of three different strains, the validty of mercury in hair, blood and muscle as indicators of methylmercury exposure was evaluated. Significant sex-related differences in the toxicokinetics of methylmercury were observed in the mice and it is concluded that hair and blood levels of mercury are of questionable relevance as indicators of both body burden and target organ concentrations of mercury. However, blood concentrations might be used as an indicator of brain deposition and the correlation improves after corrections due to sex-related differences in toxicokinetics.