Cecilia Berg

The reproductive cycle encompasses processes such as sex organ differentiation and development in the early life stages and maturation of the gametes in the adult organism. During the early life stages, critical developmental programming of the endocrine and reproductive systems occurs, and exposure to chemicals during these critical developmental windows can result in impaired reproductive function later in life. It is therefore important to evaluate long-term consequences of early life stage exposure to endocrine-disrupting chemicals. The African clawed frog Xenopus tropicalis has several characteristics that facilitate studies of developmental and reproductive toxicity. Here I present a X. tropicalis life cycle test protocol including study design, exposure regimes, and endpoints for chemical disruption of sex differentiation, gonadal and Müllerian duct development, the thyroxin-regulated metamorphosis, estrogen synthesis (activity of the CYP19 aromatase enzyme), spermatogenesis, oogenesis, puberty and fertility.

Most amphibians breed in water, including the terrestrial species, and may therefore be exposed to water-borne pharmaceuticals during critical phases of the reproductive cycle, i.e. sex differentiation and gamete maturation. The objectives of this paper were to (i) review available literature regarding adverse effects of hormonally active pharmaceuticals on amphibians, with special reference to environmentally relevant exposure levels and (ii) expand the knowledge on toxicity of progestagens in amphibians by determining effects of norethindrone (NET) and progesterone (P) exposure to 0, 1, 10 or 100 ng l ⁻¹ (nominal) on oogenesis in the test species Xenopus tropicalis . Very little information was found on toxicity of environmentally relevant concentrations of pharmaceuticals on amphibians. Research has shown that environmental concentrations (1.8 ng l ⁻¹ ) of the pharmaceutical oestrogen ethinylestradiol (EE ₂ ) cause developmental reproductive toxicity involving impaired spermatogenesis in frogs. Recently, it was found that the progestagen levonorgestrel (LNG) inhibited oogenesis in frogs by interrupting the formation of vitellogenic oocytes at an environmentally relevant concentration (1.3 ng l ⁻¹ ). Results from the present study revealed that 1 ng NET l ⁻¹ and 10 ng P l ⁻¹ caused reduced proportions of vitellogenic oocytes and increased proportions of previtellogenic oocytes compared with the controls, thereby indicating inhibited vitellogenesis. Hence, the available literature shows that the oestrogen EE ₂ and the progestagens LNG, NET and P impair reproductive functions in amphibians at environmentally relevant exposure concentrations. The progestagens are of particular concern given their prevalence, the range of compounds and that several of them (LNG, NET and P) share the same target (oogenesis) at environmental exposure concentrations, indicating a risk for adverse effects on fertility in exposed wild amphibians.

The selective serotonin reuptake inhibitor (SSRI) fluoxetine (FLU, Prozac®) is commonly prescribed for depression in pregnant women. This results in SSRI exposure of the developing fetus. However, there are knowledge gaps regarding the impact of SSRI exposure during development. Given the role of serotonin in brain development and its cross-talk with sex hormone function, we investigated effects of developmental exposure to pharmacologically relevant concentrations of FLU (3 and 30 nM (measured)) on brain neurotransmitter levels, gonadal differentiation, aromatase activity in brain and gonads, and the thyroid system, using the Xenopus tropicalis model. Tadpoles were chronically exposed (8 weeks) until metamorphosis. At metamorphosis brains were cryosectioned and levels of serotonin, dopamine, norepinephrine, and their metabolites 5-hydroxyindoleacetic acid, 3,4-dihydroxyphenylacetic acid, and homovanillic acid were measured in discrete regions (telencephalon, hypothalamus and the reticular formation) of the cryosections using high-performance liquid chromatography. Exposure to 30 nM FLU increased the concentration of 5-hydroxyindoleacetic acid in hypothalamus compared with controls. FLU exposure did not affect survival, time to metamorphosis, thyroid histology, gonadal sex differentiation, or aromatase activity implying that the effect on the serotonergic neurotransmitter system in the hypothalamus region was specific. The FLU concentration that impacted the serotonin system is lower than the concentration measured in umbilical cord serum, suggesting that the serotonin system of the developing brain is highly sensitive to in utero exposure to FLU. To our knowledge this is the first study showing effects of developmental FLU exposure on brain neurochemistry. Given that SSRIs are present in the aquatic environment the current results warrant further investigation into the neurobehavioral effects of SSRIs in aquatic wildlife.

The developmental programming of the reproductive system is vulnerable to chemical exposure. It is therefore important to evaluate long-term consequences of early life-stage exposure to endocrine disrupting chemicals. The African clawed frog Xenopus tropicalis has several characteristics which facilitates studies of developmental reproductive toxicity. Here, I present a X. tropicalis test protocol, including study design, exposure regime, and endpoints for chemical disruption of sex differentiation, reproductive organ development, the thyroxin-regulated metamorphosis, oestrogen synthesis (activity of the CYP19 aromatase enzyme), and fertility.

The usefulness of Xenopus tropicalis as a model species to investigate endocrine disruption and developmental reproductive toxicity was assessed. In our test system tadpoles were exposed to test substances from shortly after hatching until metamorphosis, including the period of gonadal differentiation. Effects on the sex hormone and thyroid hormone axes were evidenced as skewed sex ratios, malformations of reproductive organs, altered cytochrome (CYP19) (aromatase) activity, and gene expression in gonads and brain, as well as changed thyroid histology and time to metamorphosis. Reproductive toxicity was evaluated at sexual maturity. Male-to-female sex reversal was implied at concentrations as low as 6 pM (1.8 ng/L) ethynylestradiol (EE₂), which is comparable to EE₂ levels observed in the environment. EE₂-exposed males that were not sex reversed had significantly reduced fertility and a reduced amount of spermatozoa in testes compared with control males. This indicates that reproduction in wild frogs might be impaired by estrogenic environmental pollutants. Aromatase activity in brain and testes of adult frogs was not affected by larval EE₂ exposure. Preliminary results indicate that exposure to the environmentally relevant pharmaceutical clotrimazole modulated aromatase activity in brain and gonads during sex differentiation, which warrants further investigation. The susceptibility to estrogen-induced sex reversal of X. tropicalis was comparable to that of other frog species and fish. Similarities between the reproductive effects in X. tropicalis and those reported in fish, birds, and mammals after developmental exposure to estrogens make X. tropicalis promising model for research on endocrine disruption and developmental reproductive toxicity.

The susceptibility of Xenopus (Silurana) tropicalis and Rana temporaria to ethynylestradiol (EE₂), a potent estrogenic pharmaceutical and environmental pollutant, was investigated. Larval EE₂ exposure caused female‐biased sex ratios at concentrations as low as 0.06 nM, which is comparable to levels found in the environment. The susceptibility of the two frog species to EE₂ was comparable, supporting the use of X. tropicalis as a model organism for research on developmental reproductive toxicity of estrogenic pollutants.

Eggshell thinning among wild birds has been an environmental concern for almost half a century. Although the mechanisms for contaminant-induced eggshell thinning are not fully understood, it is generally conceived to originate from exposure of the laying adult female. Here we show that eggshell thinning in the domestic hen is induced by embryonic exposure to the synthetic oestrogen ethynyloestradiol. Previously we reported that exposure of quail embryos to ethynyloestradiol caused histological changes and disrupted localization of carbonic anhydrase in the shell gland in the adult birds, implying a functional disturbance in the shell gland. The objective of this study was to examine whether in ovo exposure to ethynyloestradiol can affect eggshell formation and quality in the domestic hen. When examined at 32 weeks of age, hens exposed to ethynyloestradiol in ovo (20 ng/g egg) produced eggs with thinner eggshells and reduced strength (measured as resistance to deformation) compared with the controls. These changes remained 14 weeks later, confirming a persistent lesion. Ethynyloestradiol also caused a decrease in the number of shell gland capillaries and in the frequency of shell gland capillaries with carbonic anhydrase activity. These data suggested that a disrupted carbonic anhydrase expression was involved in the mechanism for the oestrogen-induced eggshell thinning found in this study. The results support our hypothesis that eggshell thinning in avian wildlife can result from a structural and functional malformation in the shell gland, induced by xeno-oestrogen exposure during embryonic development.