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Endocrine-disrupting chemicals and child health

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Endocrine-disrupting chemicals (EDCs) are chemicals which are introduced into the environment by human activities. In many cases it has been proven that EDCs can cause adverse health effects in the human. EDCs are classified by their chemical structure, putative direct or indirect effects on endocrine glands and systems, may accumulate and persist in organisms and in the environment, and/or they may exert clinically observable and measurable effects. Often, EDCs may act in concert and as mixtures. Legislation to ban EDCs and protect especially pregnant women and children at young age are needed and needs to be revised and adjusted to new developments on a regular basis. Putative associations, in spite of sometimes conflicting results, have to be analyzed in in vitro model systems be it in cell biology, in vitro settings or animal studies in more detail. This chapter depicts the mainly positive albeit detrimental epidemiological findings for EDC-caused effects in the fields of growth and metabolism, neurocognitive development and sexual development and reproduction.

Introduction

Endocrine-disrupting chemicals (EDCs) are chemical substances which are introduced into the environment by human activities and actions. It is hypothesized, and in many cases proven, that EDCs can cause adverse health effects for humans through interaction with endocrine systems [1,2]. They are classified by their chemical structure, putative direct or indirect effects on endocrine glands and systems, may accumulate and persist in organisms and in the environment, and/or they may exert clinically observable and if at all possible measurable effects. Unfortunately, for analysis and research of the complex mechanisms of their actions in the human body, only in vitro model systems have so far been available [[3], ∗[4], [5]]. For most of these systems insufficient or even no high-throughput capacity is available- This makes risk evaluation very difficult in many cases. In addition and importantly, in industrial countries, most people are often exposed to a rather wide variety of mixtures of substances at the same time, in various locations and/or in a consecutive order. All substances by themselves and all mixtures and combinations of these might cause variable and diverse effects or may exert additive and/or combined effects. In addition, the clinical importance of epigenetic and importantly transgenerational changes caused by the action of EDCs during vulnerable phases of development is currently unclear [6]. Epidemiological studies have often been criticized because reproducibility of these has not always been possible and is not always guaranteed. In addition, results vary between for example populations and cohorts studied and also depend upon the times when studies have been conducted and under which legislative regulations environmental conditions have been analyzed [5]. Nevertheless, epidemiological studies remain the method of choice for the detection and analysis of suitable model systems and to develop hypotheses for translational and basic research on putative effects of EDCs on human health (see Table 1). To detect putative associations, in spite of sometimes conflicting results, is crucial in the selection of factors that can then be analyzed for example in in vitro model systems be it in cell biology, in vitro settings or animal studies in more detail [7]. This chapter depicts the mainly positive albeit detrimental epidemiological findings for EDC-caused effects in the fields of growth and metabolism, neurocognitive development and sexual development and reproduction in a descriptive and personalized way. As has been pointed out already, that there is a strong need for direct linkage between epidemiological studies and mechanistic research using model systems, especially focusing on the interaction of different EDCs and mixtures thereof and the consequences of prenatal and early life exposure [1,[5], [6], ∗[7]].

Section snippets

Scope of the topic

For the last twenty years, the human genome has been analyzed mainly to discover genetic causes of disease, despite the fact that there is strong evidence that gene variants alone explain relatively little risk both for a population or an individual. In contrast, it is hypothesized that unexplained disease risks are caused by the exposome, representing all external exposures by the environment at large and in addition that genome:exposome interactions are most important for risk assessment.

Definitions

Endocrine disrupting chemicals (EDCs) are chemical substances usually brought into the environment by human activities and actions that can cause adverse health effects through interaction with the endocrine system and metabolism. EDCs mostly stem from industrial activities and are for example used as pesticides, additives to clothing, toys, foods or storage and package materials. They are classified either by their chemical structure, putative direct or indirect effects on endocrine organs and

General considerations

For some of the EDCs mechanistic explanations as to their mode of action have been identified or have at least been suggested: for example, polychlorinated biphenyls (PCBs) show a different degree of halogenation, from one to ten chlorine atoms. With an increasing number of chlorine atoms the environmental persistence of PCB increases. Due to their chemical properties, PCBs were widely used as coolant and dielectric fluid, in capacitors and as joint sealing material in industries around the

Growth

According to the “environmental obesogen hypothesis”, early-life (including in utero) exposure to obesogenic chemicals and in particular to endocrine disrupting chemicals (EDCs) may disturb the mechanisms involved in adipogenesis or energy storage, and thus may increase the susceptibility to overweight and obesity and thus interfere with growth trajectories early in life. Animal models have shown that exposure to several of these chemicals could induce adipogenesis and mechanisms that are

Fetal growth

Fetal growth is regulated by the intricate interaction of maternal, placental, nutritional, endocrine, environmental, genetic and fetal factors. The effects and outcomes that chemicals, widely distributed in the environment, may have on the health status of both the mother and the fetus are still not well defined. However, many complex mixtures of a large array of chemical substances are found in the mothers and placenta. Consequently, exposure to endocrine-disrupting chemicals (EDCs) could

Postnatal growth

One study aimed to identify demographic determinants of serum concentrations of different PCBs and the organochlorine pesticide DDT for pregnant women in Germany as a country, which has banned the use and production of these POPs since 1991. Furthermore, this study tried to analyze the association between maternal serum concentrations at 24th or 36th weeks of gestation and anthropometric data of the newborns, as well as thyroid parameters such as TSH, FT3 and FT4 levels of the child at age 6

Thyroid function

In one study, FT3 serum levels of children at the age of 12 months showed a significant negative association with p,p’-DDE, PCB 153, 156, 170 and 180 [1]. A reverse association between PCBs and FT3 serum levels in maternal blood has also been shown. In contrast, in another cohort PCB levels showed no significant association with maternal thyroid hormone levels. This again is in contrast to yet other findings (Nidens). On the one hand side, bisphenols (BPs), and especially bisphenol A (BPA), are

Reproduction

Endocrine-disrupting chemicals are especially known to interfere with normal reproductive function and hormone signaling. Phthalates, bisphenol A, pesticides, and environmental contaminants such as polychlorinated biphenyls and dioxins are known endocrine-disrupting chemicals that have been shown to negatively affect both male and female reproduction. As has already been pointed out, exposure to these chemicals occurs on a daily basis owing to these compounds being found in plastics, toys,

Pubertal development

Puberty is the process of physical changes between childhood and adulthood during which adolescents reach sexual maturity and become capable of reproduction. It is considered one of the main temporal windows of susceptibility to the influence of endocrine-disrupting chemicals (EDCs). EDCs may act as single chemical agents or as chemical mixtures; they can be pubertal influencers, accelerating and anticipating the processing of maturation of secondary sexual characteristics. Moreover, recent

Sex differentiation

Endocrine-disrupting chemicals (EDCs) are variable and pervasive and may have significant diverse consequences for health, including the reproductive development and expression of sex-/gender–sensitive parameters. Despite a growing number of studies on this issue there is still insufficient data about different EDCs and in particular of EDC mixtures and their effects on reproductive relevant end points that in particular for sex differentiation in the human fetus and postnatally. It is

Neurodevelopment and cognition

A number of environmental epidemiology studies link numerous suspected EDCs, including phthalates and bisphenol A (BPA), to adverse neurodevelopmental outcomes. However, results for some chemicals are quite contradictory and inconsistent and most studies only assessed one chemical at a time. To evaluate the overall impact of prenatal exposure to an EDC mixture on neurodevelopment in school-aged children, and identify chemicals of concern while accounting for co-exposures Swedish researchers

Metabolism and obesity

There is sufficient evidence to unequivocally suggest that some environmental chemicals may be able to interfere with the endocrine regulation of energy metabolism and adipose tissue development. Recent findings demonstrate that such endocrine-disrupting chemicals, termed “obesogens”, can promote adipogenesis and cause weight gain. This includes compounds to which the human population is exposed in daily life through their use in pesticides/herbicides, industrial and household products,

Perspectives and summary

Endocrine disruptors have recently been shown to promote an epigenetic transgenerational phenotype involving a number of disease states (e.g. male infertility, metabolic disease) (see Table 1). The anti-androgenic fungicide vinclozolin for example was found to act transiently at the time of embryonic sex determination to promote in the F1 generation a spermatogenic cell defect and subfertility in male mice. When the animals were allowed to age up to 1 year, a number of disease states developed.

Funding

This work is funded by the European Union by means of the European Social Fund (ESF), by the European Regional Development Fund (ERDF), and by means of the Free State of Saxony within the framework of the excellence initiative. This study was performed within the EU project EDC-MixRisk.

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