Keywords iodine deficiency - pregnancy - hypothyroxinemia - neurocognitive development - endocrine
disruptors
Introduction
Thyroid hormones are especially important for embryonic/fetal and early postnatal
neurocognitive development. Depending on the severity, duration and time of iodine
deficiency in certain stages of life, iodine-deficiency disorders are associated with
physical, neurological and mental deficiencies in humans. Severe iodine deficiency
during pregnancy can have a number of negative impacts on the health of mother and
child, including hypothyroidism, goiter, stillbirths, increased perinatal mortality,
neurological damage and mental disability [1 ]
[2 ].
In addition, exposure to endocrine-disrupting chemicals (EDCs) is increasing worldwide
[3 ]
[4 ]
[5 ]. These endocrine disruptors are substances which are either present in nature or
are produced artificially and released into the environment. The majority of EDCs
specifically interfere with the thyroid metabolism and are therefore known as thyroid-disrupting
chemicals (TDCs) [6 ]
[7 ]
[8 ]. The placenta is especially sensitive to EDCs because of its abundance of hormone
receptors [9 ]. Exposure to these chemicals combined with an inadequate iodine intake can additionally
harm the development, growth, differentiation
and metabolic processes of the embryonic/fetal and neonatal brain [6 ]
[7 ]
[8 ]
[10 ]
[11 ]
[12 ]
[13 ]
[14 ]
[15 ]
[16 ]
[17 ]
[18 ]
[19 ]
[20 ]
[21 ]
[22 ].
Both iodine deficiency and exposure to TDCs have a negative impact on general health
and the socioeconomic system. The estimated annual cost of the seven EDC categories
with the highest causation amounts to 33.1 billion Euros in Europe. The largest share
of these costs relate to the loss of IQ and the increase in neurocognitive disorders
[23 ]
[24 ]
[25 ]
[26 ]
[27 ]. In addition, a growing body of evidence suggests that exposure to TDCs, including
through air pollution, not only affects brain function [13 ]
[28 ]
[29 ]
[30 ]
[31 ] but also has an impact on the outcomes of pregnancy and birth [32 ]
[33 ]
[34 ]
[35 ]
[36 ].
“Endemic goiter” has been synonymous with iodine deficiency for years and the aim
has always been to prevent enlargement and overt dysfunction of the thyroid gland.
However, there has been a paradigm shift in recent decades [37 ], ever since the focus has moved to examining the consequences of mild to moderate
iodine deficiency on the cognitive development of the embryo ([Fig. 1 ]).
Fig. 1
The paradigm shift relating to iodine deficiency (Fig. is based on data from [24 ]).
Epidemiological and experimental studies on mild to moderate iodine deficiency carried
out in the last two decades have shown that embryonic/fetal brain development can
be affected not only in the infants of mothers with overt hypothyroidism but also
those born to mothers with hypothyroxinemia in the early stages of pregnancy [38 ]
[39 ]
[40 ]
[41 ]
[42 ]. Low FT4, also known as hypothyroxinemia, is an indication of individual iodine
deficiency. As FT4, but not FT3, is transported almost exclusively via the placenta
in the first three months of pregnancy, slight changes in fetal brain development
can be observed even if maternal thyroid hormone levels are low but still within reference
ranges. The fetus is able to
produce thyroid hormones from week 12–14 of gestation and is then dependent on iodine
which is transported via the placenta, and no longer on maternal FT4 of which lower
levels cross the placenta to reach the fetus from the 12th week of pregnancy.
Because of methodological issues with the definition, findings may not be homogeneous.
Moreover, too little attention has been paid to isolated maternal hypothyroxinemia
(IMH) because of some uncertainty regarding treatment. But IMH is clearly an indication
of maternal iodine deficiency not reflected by elevated TSH levels, as the iodine-depleted
thyroid gland reacts more sensitively to TSH [43 ]
[44 ]
[45 ].
The pollution of our environment, with EDCs found in the air, the water, food, and
sanitary products, is increasing worldwide and has reached potentially hazardous levels.
Generally speaking, EDCs can affect the normal functioning of the endocrine system
of humans and animals. They especially affect the thyroid hormone system, with negative
impacts on fetal and neonatal brain development, growth, differentiation, and metabolic
processes [6 ]
[7 ].
The aim of a recently published review article was to highlight the importance of
IMH caused by mild iodine deficiency and additional environmental factors such as
EDCs and air pollution on the cognitive and psychosocial development of children and
to identify measures for the prevention and treatment of IMH.
Method
The basis for compiling this opinion was a joint review article published in the international
peer-reviewed journal Nutrients in 2023 [2 ]. We also carried a search of the recent literature, focusing on relevant articles
published between 2022 and September 2024 in PubMed, Medline, Cochrane, Web of Science,
and Google Scholar using the search terms Iodine, Pregnancy, Thyroid Hormone, Thyroid
Diseases, Endocrine Disruptors, Hypothyroxinemia, and Subclinical Hypothyroidism,
which were searched for in combination using the operators AND and OR. The drafted
key statements were voted on by the scientific advisory board of the Iodine Deficiency
Working Group (Arbeitskreis Jodmangel e. V. , AKJ).
Thyroid Function in Pregnancy
Thyroid Function in Pregnancy
In pregnancy, the functions of the maternal thyroid are dynamically adapted to the
thyroid hormone needs of the mother and embryo/fetus ([Fig. 2 ]
a ). Pregnant women need about 50% more iodine because of their increased production
of thyroid hormones, increased renal iodide clearance and the transplacental transfer
of iodine to the fetus [46 ]
[47 ]. The average iodine supplementation recommendation during pregnancy is therefore
250 µg/day [48 ].
Fig. 2
Changes in thyroid physiology during pregnancy (a ) and the relationship between thyroid hormone activity and brain development (b ) (Fig. is based on data from [49 ]
[50 ]). See text for further explanations (based on data from [2 ]).
Median urine iodine concentrations (UIC) are used to assess iodine intake of the general
population in the context of epidemiological studies. According to the criteria of
the WHO, they should be over 100 µg/l, and over 150 µg/l during pregnancy and lactation
[51 ].
We know from recent epidemiological studies that the standard iodine intake is below
the mean of what is required in about 30% of adults, 48% of women of childbearing
age, and 44% of children and adolescents in Germany [52 ]
[53 ]
[54 ]. This is also the case in more than 70% (n = 21) of 29 European countries ([Table 1 ]) [52 ]
[55 ]
[56 ]
[57 ]
[58 ]
[59 ]
[60 ]
[61 ]
[62 ]
[63 ]
[64 ]
[65 ]
[66 ]
[67 ]
[68 ]. A mean UIC figure of > 150 μg/l was only found in a few EU countries with mandatory
universal salt iodization programs such as Bulgaria or Romania (see [Table 1 ]). Studies in other countries have shown that only mandatory universal salt iodization
of more than 25 mg/kg can ensure sufficient iodine intake through nutrition across
all sections of the population including pregnant women who have higher requirements
[51 ]
[69 ]. Young women who are vegan or vegetarian and do not take iodine supplements are
most at risk of low iodine status, iodine deficiency, and insufficient iodine intake.
Table 1
Iodine intake for the general population and for pregnant women in Europe (data from
[2 ]).
Country
General populationa
Pregnant womenb
Median (UIC)
(μg/l)
Date of survey
(N, S)
Population
Iodine intake of the population
Median (UIC)
(μg/l)
Date of survey
(N, S)
Iodine intake
Legal status
(year)e
Abbreviations: SAC = school-age children (normally aged 6–12 years); UIC = urine iodine
concentration; USI = universal salt iodization; N = national representative data;
S = only subnational data; Dates from a
[68 ], b
[55 ], c
[70 ], d
[56 ], e
[62 ], f
[63 ]
[64 ]
Austria
111
2012
(N)
SAC
(7–14)
adequate
87
2009–2011
(S)
inadequate
obligatory
(1999)
Belgium
113
2010/2011
(N)
SAC
(6–12)
adequate
124
2010
(N)
inadequate
voluntary
(2009)
Bulgaria
182
2008
(N)
SAC
(7–11)
adequate
165
2003
(N)
adequate
obligatory
(2001)
Croatia
248
2009
(N)
SAC
(7–11)
adequate
140
2009, 2015 (S)
inadequate
obligatory
(1996)
Denmark
145
2015
(S)
SAC
adequate
101
2012
(S)
inadequate
obligatory
(2000)f
Finland
96
2017
(N)
adults
(25–74)
inadequate
115
2013–2017
(S)f
inadequate
voluntaryf
France
136
2006–2007
(N)
adults
(18–74)
adequate
65
2006–2009
(S)
inadequate
voluntary
Germany
89
2014–2017
(N)
SAC, adolescents (6–12)
inadequate
54
2008–2011
(N)c
inadequate
voluntary
Greece
132
2018
(N)
adults
adequate
127
2008–2015
(S)
inadequate
voluntary
Hungary
228
2005
(S)
SAC
(10–14)
adequate
128
2018
(S)d
inadequate
obligatory
(2013)
Ireland
111
2014–2015
(N)
adolescent girls (14–15)
adequate
107
2008–2010
(S)
inadequate
voluntary
Italy
118
2015–2019
(S)
SAC
adequate
72
2002–2013
(S)
inadequate
obligatory
(2005)
Netherlands
130
2006
(S)
adults
(50–72)
adequate
223
2002–2006
(S)
adequate
voluntary
Poland
112
2009–2011
(S)
SAC
(6–12)
adequate
113
2007–2008
(S)
inadequate
obligatory
(2010)
Portugal
106
2010
(N)
SAC
adequate
85
2005–2007
(N)
inadequate
voluntary
Romania
255
2015–16
(N)
SAC
(6–11)
adequate
206
2016
(S)
adequate
obligatory
(2009)
Spain
173
2011–12
(N)
SAC
adequate
120
2002–2011
(S)
inadequate
voluntary
Sweden
125
2006–07
(N)
SAC
(6–12)
adequate
98
2006–2007; 2010–2012
(S)
inadequate
voluntary
(1936)f
Switzerland
137
2015
(N)
SAC
(6–12)
adequate
136
2015
(N)
inadequate
voluntary
United Kingdom
166
2015–2016
(N)
SAC, adolescents (4–18)
adequate
99
2002–2011
(S)
inadequate
no USI program
As thyroxine-binding globulin (TBG) increases in pregnancy, determination of FT4 is
imprecise as routine measurement of FT4 values is false resulting in figures that
are either too low or too high because measurement methods depend on measuring TBG
values.
In practice, this means that to ensure correct values, the mean normal FT4 range must
be assumed to ensure that pregnant women have an adequate iodine intake. Additional
supplementation with iodide tablets is necessary and is a useful preventive measure
for all women wanting to have children [71 ]
[72 ]
[73 ].
Impact of Mild Iodine Deficiency and Maternal Hypothyroxinemia on Prenatal Brain Development
Impact of Mild Iodine Deficiency and Maternal Hypothyroxinemia on Prenatal Brain Development
A time frame (s. [Fig. 2 ]
b , between the two red dotted lines) has been identified in which a decrease in maternal
thyroid hormones (FT4) has a particularly strong impact on neuronal proliferation
and on the migration and development of the inner ear. Recognizing this early critical
phase can have a direct clinical impact on the assessment of risk and the time frame
for treatment options [74 ]
[75 ]. A lower fT4 transfer to the maternal placenta in this critical developmental stage
probably has the greatest impact on the neurological development of the child [76 ]
[77 ]
[78 ]
[79 ]
[80 ]
[81 ] and also manifests in the form of permanent structural and functional anomalies
[38 ]
[82 ]
[83 ]
[84 ]
[85 ]
[86 ].
IMH ([Table 2 ]) probably occurs much more often than subclinical hypothyroidism, [40 ]
[42 ]
[44 ]
[87 ]
[88 ]
[89 ]
[90 ]. IMH prevalence is assumed to be higher in countries with iodine deficiency [43 ]
[91 ]. Trimester-specific reference ranges for serum TSH and fT4 levels in an euthyroid
pregnant population would have to be established as the gold standard for diagnosis
[92 ]
[93 ]. Unfortunately, reference ranges are currently only available for TSH levels.
Table 2
Definition and prevalence of maternal thyroid disorders (data from [82 ]).
Isolated maternal hypothyroxinemia (1.5–25%)
Serum fT4 concentration in the lower 5th or 10th percentile of the reference range
with normal TSH concentrations
Overt hypothyroidism (0.3–0.5%)
Elevated serum TSH levels together with decreased fT4 concentrations
Subclinical hypothyroidism (2–2.5%)
Elevated serum TSH levels and normal fT4 concentrations
Autoimmune thyroid disease (10–20%)
Presence of TPO and/or TG antibodies in serum with or without changes to TSH and fT4
concentrations
In observational studies on the impairment of cognitive development and behavioral
disorders in the context of mild iodine deficiency, maternal blood samples were usually
taken between the 9th and the 13th week of gestation ([Table 3 ]). The neurological examinations of the offspring were carried out between the ages
of 6 months and 16 years [81 ]. The general study designs varied considerably. The differences relate to the criteria
used to select mother-child pairs, the reference values and ranges used to determine
the different levels of maternal hypothyroidism or hypothyroxinemia, and the different
tests used to evaluate neurological development (s. [Table 3 ]).
Table 3
Observational studies on the negative impact on cognitive development and behavioral
disorders in connection with mild iodine deficiency – characteristics of all studies
included in the systematic evaluation (data from [94 ]) (“sister articles” were combined).
Author, Year [Reference]
Total number of tested participants
Country
Maternal thyroid disorder
Pregnancy week at TFT
Criteria for thyroid function disorder
Age of child at evaluation
Tests used to evaluate neurological development
Abbreviations: Co = continuous; HR = hypothyroxinemia; OH = overt hypothyroidism;
SH = subclinical hypothyroidism; TFT = thyroid function test; TSH = thyroid-stimulating
hormone; WISC = Wechsler Intelligence Scale for Children
Pop et al. 1999 [95 ]
220
Netherlands
HR
12 and 32 weeks
10th percentile for fT4 (< 10.4 pmol/l) and 5th percentile for fT4 (< 9.8 pmol/l)
10 months
Bayley Scales of Infant Development
Pop et al. 2003 [96 ]
125
Netherlands
HR
12, 24 and 32 weeks
fT4 < 10th percentile (12.10 pmol/l)
1–2 years
Bayley Scales of Infant Development
Kasatkina et al. 2006 [81 ]
35
Russia
HR
1st and 3rd trimester
fT4 < 12.0 pmol/l
6, 9 and 12 months
Gnome method, especially the Coefficient of Mental Development
Li et al. 2010 [97 ]
213
China
SH and HR
16 to 20 weeks
SH = TSH > 97.5 percentile (4.21 mU/l), HR = tT4 < 2.5 percentile (101.79 nmol/l)
25–30 months
Bayley Scales of Infant Development
Henrichs et al. 2010 [98 ]
3659
Netherlands
HR and Co TSH
13,3 weeks
HR = fT4 10th percentile (< 11.76 pmol/l) and 5th percentile (< 10.96 pmol/l), Co
TSH = TSH reference range 0.03–2.50 mU/l
18 and 30 months
MacArthur-Bates Communication Development Inventories after 18 months, review of speech
development after 30 months
Suárez-Rodríguez et al. 2012 [80 ]
70
Spain
HR
37 weeks
fT4 < 10th percentile (9.5 pmol/l)
38 months and 5 years
McCarthy Scales of Children’s Abilities
Williams et al. 2012 [99 ]
166
United Kingdom
SH and HR
+ 1 hour after delivery
SH = TSH > 3.0 mU/l,
HR = fT4 ≤ 10th percentile (11.6 pmol/l) or tT4 ≤ 10th percentile (108.4 nmol/l)
5.5 years
McCarthy Scales of Children’s Abilities
Craig et al. 2012 [100 ]
196
USA
HR
2nd trimester
fT4 < 3rd percentile (11.84 pmol/l)
2 years
Bayley Scale of Infant Development III
Ghassabian et al. 2014 [79 ]/Korevaar et al. 2016 [83 ]
3737/5647
Netherlands
HR and SH
13.5/13.2 weeks
HR = fT4 < 5th percentile (10.99 pmol/l),
SH = TSH > 2.50 mU/l
6 years
Snijders-Oomen Non-verbal Intelligence Test, revision (mosaic patterns and categories)
Päkkilä et al. 2015 [101 ]
5295
Finland
HR, SH and OH
Average 10.7 weeks
HR = fT4 < 11.4–11.09 pmol/l depending on the trimester,
SH = TSH > 3.10–3.50 mU/l, depending on the trimester
8 and 16 years
Severe and mild ADHD symptoms and normal behavior; teachers reported on the standard
of the schoolwork of the child; self-report by the adolescent and WISC-reviewed
Grau et al. 2015 [102 ]
455
Spain
HR
1st and 2nd trimester
< 10th percentile (13.7–11.5 pmol/l depending on the trimester)
1 and 6–8 years
Brunet-Lézine Scale and WISC-IV
All studies, with the exception of the one by Grau et al. [102 ] which investigated the effects of low maternal fT4 levels at the end of the first
trimester of pregnancy, report impairment of cognitive and motor development in exposed
children [40 ]
[44 ]
[77 ]
[79 ]
[92 ]
[96 ]
[97 ]
[98 ]
[103 ]
[104 ]. The correlation gradually decreased with advancing pregnancy and disappeared by
late pregnancy
[42 ]
[101 ]
[105 ].
Overall, none of the systematic reviews and meta-analyses showed clear threshold values
for high TSH and/or low fT4 values in the serum of pregnant women which would clearly
indicate an increased risk of neurological developmental disorders in their offspring.
Such threshold values could not be determined because the epidemiological studies
were not designed to show quantitative thresholds (s. [Table 3 ]).
Impact of Endocrine Disruptors (TDCs) on Thyroid Hormone System and the Role of Adequate
Iodine Intake
Impact of Endocrine Disruptors (TDCs) on Thyroid Hormone System and the Role of Adequate
Iodine Intake
TDCs do not just have a direct effect on pregnancy by acting as hormone agonists or
antagonists but also have indirect effects by impairing maternal, placental, and fetal
homeostasis. It is thought that the adverse health effects of TDCs including air pollution
on offspring may be the result of two mechanisms: the first mechanism directly affects
the placenta and therefore passes into the fetal circulation, and/or the second mechanism
has an indirect impact through oxidative stress on the placenta which induces inflammation
and epigenetic changes in the placenta and offspring [13 ]
[106 ]
[107 ]
[108 ]
[109 ]
[110 ]
[111 ].
In view of the many different effects of all EDCs, such as low-dose effects, possible
non-linear dose responses, cumulative effects which are often expected in cases of
combined exposure, and cross-generational effects with different impacts during critical
windows of exposure, it is currently unlikely that it is possible to define safe EDC
contamination levels [26 ]
[84 ]
[112 ]
[113 ]
[114 ]
[115 ].
Iodine deficiency is clearly able to promote adverse effects [116 ]. The urgency of the problem is due to the concurrence of the widely prevalent inadequate
iodine intake and the continuously increasing exposure of humans to TDCs [6 ]
[32 ]
[117 ]
[118 ]
[119 ]. The studies on maternal hypothyroxinemia caused by mild to moderately severe iodine
deficiency carried out to date have not taken additional prenatal exposure to TDCs
into account (s. [Table 4 ], right-hand column).
Table 4
Potential thyroid-disrupting chemicals (TDCs) which target the signaling pathways
of thyroid hormones (data from [2 ]).
Examples of chemicals
Target of TDC activities and outcomes
Changes in neurological development
1 OCPs – are predominantly used in agriculture to protect crops, but they have been
banned or their use has been greatly reduced in recent decades because of their environmental
persistence and neurotoxicity.
2 PCBs – banned compounds used to produce electrical devices such as transformers and
used in hydraulic fluids, heat transfer fluids, lubricants, and plasticizers.
3 Perchlorates, thiocyanate, and nitrate – exposure to these harmful substances occurs
through foodstuffs or from other sources (e.g., thiocyanate in cigarette smoke or
rocket fuels and perchlorate and nitrate in fertilizers).
4 Phthalates – are used to make plastics more flexible. They are also present in some
food packaging, cosmetics, children’s toys, and medical devices.
5 Genistein – a substance which occurs naturally in plants with hormone-like activity
found in soya products such as tofu or soya milk.
6 4NP – is used in the production of antioxidants, lubricant oil additives, detergents
and washing-up liquids, emulsifiers, and solubilizers.
7 BP2 – is no longer approved for use as a UV filter in sun creams in the European
Union. However, it is still contained in plastic materials and many cosmetics to prevent
UV-related degradation.
8 Amitrole – is used as an herbicide.
9 PBDEs – are used in the production of flame retardants in household items such as
upholstery foam and carpets. Although most PBDEs have been banned or are being gradually
phased out, they persist in the environment.
10 Triclosan – may be present in some antimicrobial products and personal care products
such as body washes.
11 Silymarin – a flavonoid compound which is a purified extract of the milk thistle
plant.
12 Erythrosine, also known as Red Dye No. 3 – is an organo-iodine compound. It is a
reddish-pink dye mainly used for food coloring.
13 Hydroxylated PBDEs (OH-BDEs) are abiotic and biotic transformation products of PBDEs
which also occur naturally in marine systems.
14 Bisphenols, especially bisphenol A (BPA) – are used in the production of polycarbonate
plastics and epoxy resins and are contained in many plastic products such as water
bottles, food containers, CDs, DVDs, safety equipment, thermal paper, and medical
devices.
Organochlorine pesticides (OCPs)1
Polychlorinated biphenyl compounds (PCB)2
TSH-receptor signaling and reduced stimulation of thyroid follicular cells [120 ]
Impairs cognitive, motor, and communication development [121 ]
[122 ]
[123 ]
[124 ]
[125 ]
Impairs cognitive and motor development and play activity [126 ]
Lower IQ [120 ]
Development of ADHD-associated behavior [127 ]
Perchlorate3
Thiocyanate3
Nitrate3
Phthalates4
Na+/I symporter (NIS) and inhibition of TH biosynthesis
Impairs cognitive development [128 ]
Pre- and postnatal exposure to tobacco can affect neurocognitive development [129 ]
Gender-specific effects on cognitive, psychomotor and behavioral development [116 ]
[130 ]
[131 ]
Lower nonverbal and verbal IQ scores in offspring [132 ]
[133 ]
Propylthiouracil (PTU)
Methimazole (MMI)
Genistein5
4-nonylphenol (NP)6
Benzophenone-2 (BP2)7
Herbicide (amitrole)8
Inhibition of thyroid peroxidase (TPO) leads to lower TH synthesis and a subsequent reduction in circulating TH concentrations.
Increased risk of periventricular heterotopia [134 ]
TH insufficiency leads to brain malformations and learning impairment [135 ]
Lower cognitive function [136 ]
OH-PCBs2
Polybrominated diphenyl ethers (PBDEs)9
Phthalates4
Genistein5
TH distributor proteins : Displacement of T4 and T3 by the thyroid serum-binding protein transthyretin (TTR)
and/or thyroid-binding globulin (TBG) disturbs TH homeostasis and decreases TH plasma
levels.
Impairs cognitive, behavioral, and motor development [137 ]
[138 ]
[139 ]
[140 ]
[141 ]
Delayed neurological development [142 ]
Polychlorinated biphenyls (PCBs, OH-PCBs)2
Triclosan10
Upregulation of thyroid hormone catabolism through activation of key hepatic receptors leads to decrease of circulating TH levels
[111 ]
[143 ].
Silymarin11
Disorders of cellular transmembrane transporters (MCT8, MCT10 and OATP1C1) inhibit T3 uptake.
Erythrosine12
6-n-propylthiouracil
PCBs2
Modification of deiodinase enzyme activities (DIO2, DIO3) through competitive inhibition of the enzyme or through interaction
with its sulfhydryl cofactor.
OH-PCBs2
OH-BDEs13
Bisphenols14
Binding and transactivation of thyroid hormone receptor (TR) (TRα, TRβ) by some chemicals which bind TRs as antagonists and/or change the transcription;
interactions with these TRs disrupt normal thyroid homeostasis which may possibly
lead to anomalies in brain development [11 ]
[18 ]
[149 ]
[150 ].
There are public health concerns about pregnant women with mild iodine deficiency
who are exposed to perchlorate, thiocyanate, nitrate and other environmental “thyreostatic
substances” [5 ]
[8 ]
[12 ]
[26 ]
[143 ]
[151 ]
[152 ]
[153 ]
[154 ]
[155 ]
[156 ]. A dose-effect model which investigated iodide and perchlorate exposure in foodstuffs
showed that a low iodine intake of 75 μg/day and a daily
perchlorate dose of 4.2 μg/kg would be sufficient to induce hypothyroxinemia, whereas
a higher daily dose of perchlorate of about 34 µg/kg would be required if the iodine
intake was sufficient (approx. 250 µg/day) [157 ]. Iodine deficiency can therefore worsen the effects of exposure to TDC, especially
in pregnancy [5 ]
[8 ]
[12 ]
[17 ]
[18 ]
[26 ].
[Table 4 ] summarizes the well-characterized effects of TDCs on TH metabolism and the infant
brain [116 ]
[120 ]
[121 ]
[122 ]
[123 ]
[124 ]
[125 ]
[126 ]
[127 ]
[128 ]
[129 ]
[130 ]
[131 ]
[132 ]
[133 ]
[134 ]
[135 ]
[136 ]
[137 ]
[138 ]
[139 ]
[140 ]
[141 ]
[142 ]
[144 ]
[145 ]
[146 ]
[147 ]
[148 ]
[149 ]
[150 ]
[158 ]. Air pollution is the main risk factor for the global disease burden, but the negative
effects of exposure to airborne fine particulate matter measuring < 2.5 µm (PM2.5 ) in pregnancy were previously not taken into account [159 ]
[160 ]
[161 ]. The available evidence suggests that intrauterine PM2.5 exposure can change prenatal brain development through oxidative stress and systemic
inflammation and lead to chronic neuroinflammation, microglial activation, and neuronal
micturition disorders [28 ]
[162 ]
[163 ]. It was shown that exposure to fine particulate matter was associated with structural
changes to the cerebral cortex of the child as well as impairment of core executive
functions such as inhibitory control [164 ]
[165 ]
[166 ]
[167 ].
Prevention and Treatment of IMH
Prevention and Treatment of IMH
As studies on the impact of IMH on the cognitive and motor development and the risk
of neuropsychiatric disorders in children have shown a clear connection to early pregnancy,
the key clinical question is whether these complications could be prevented at an
early stage by iodine or levothyroxine substitution [39 ]
[43 ]
[89 ]. Treatment of IMH or subclinical hypothyroidism by administering levothyroxine in
early pregnancy did not have any benefit on the neurological development of children
based on evaluations when they were aged 6 and 9 years. However, levothyroxine supplementation
was initiated, on average, in the 12th week of gestation, which is too late [168 ]
[169 ]. This is why the ATA guidelines do not
recommend supplementation with levothyroxine [92 ]. However, based on new epidemiological data, the ETA guidelines suggest that levothyroxine
supplementation should be carried out in the first trimester of pregnancy rather than
during later stages of pregnancy [93 ]. The results of a recent study showed that early levothyroxine supplementation in
women with TSH values of > 2.5 mU/l and fT4 < 7.5 pg/ml in or before the ninth week
of gestation is safe and improves the course of pregnancy. Whether it also improves
the neurological development of affected offspring has not yet been investigated.
The data supports the recommendation to adopt threshold values for levothyroxine supplementation
and start supplementation as early as possible, ideally before the end of the first
trimester of pregnancy. TSH suppression must be avoided [170 ].
A positive association has been demonstrated between maternal iodine intake starting
even before conception and cognitive functions of her offspring at the age of 6–7
years [171 ], but not if iodine substitution was only initiated in pregnancy [105 ]
[172 ]
[173 ]
[174 ]
[175 ]
[176 ]. Well designed, randomized controlled studies to study the neuropsychological development
of children are currently in progress, which will investigate the impact of daily
supplementation with 150–200 µg iodine in the period prior to preconception, during
pregnancy and during lactation [177 ]
[178 ]
[179 ]
[180 ].
The Krakow Declaration on Iodine, published by the Euthyroid Consortium and other
organizations, raises important points on how iodine deficiency in Europe could be
efficiently eliminated. The demands include
harmonizing universal salt iodization in all European countries,
carrying out regular monitoring and evaluation studies to continuously measure the
benefit and potential damage of iodine enrichment programs, and
necessary social engagement to ensure that programs to prevent iodine deficiency disorders
(IDD) are sustained [181 ]
[182 ].
Conclusions for Clinical Practice
Conclusions for Clinical Practice
Iodine deficiency means that less FT4 and more FT3 is produced; rather than being
elevated, TSH concentrations are decreased. Individual levels of iodine deficiency
can be best determined based on hypothyroxinemia.
In clinical practice when dealing with women who want to have children this means
that improving iodine intake should already start prior to conception. A low FT4 level
is a useful supporting argument.
Some of the numerous endocrine-disrupting chemicals (EDCs) in the environment can
negatively affect thyroid hormone metabolism and may even amplify the effects of iodine
deficiency. These chemicals are also referred to as TDCs. As such TDCs may be below
the detection limits in individuals, FT4 can serve as a marker for adequate iodine
intake, especially in the first three months of pregnancy.
Of course, it is the responsibility of policy makers to persuade industry to reduce
the prevalence of EDCs. But every one of us can also contribute to reducing the extent
of EDCs released into the environment.