The individual's psychological perception of being male, female, neither, both, or somewhere in between1 is called gender identity. It can match the biological sex (cisgender) or can be different (transgender - TG). A TG man is an individual born as a female but who identifies himself as a man. A TG woman is born as a male but identifies herself as a woman2. It is estimated that, at present, there are 25 million TG people worldwide3, most of them suffering from gender dysphoria, a psychological condition characterized by incongruence between their gender and the one they were assigned at birth4, which can result in social discrimination and difficulties at work and in family, often leading to depression, anxiety, and stress5. For such reasons, TG people often go through gender-affirming hormone therapy (GAHT) and/or gender-affirming surgery. GAHT for TG men is characterized by the administration of testosterone (T) (Table 1), and for TG women, estrogens (E2) plus antiandrogens (Table 2)6.
GAHT usually lasts for the entire life of the individual, acting continuously on the endocrine system7,8. So, it is important to analyze the GAHT's impact on the health of TG people and its potential long-lasting effects. Moreover, TG people are exposed, as the general population, to chemical contaminants -- in particular, the endocrine disrupters (ED) -- that target the endocrine system as the GAHT, resulting in overstimulation9.
ED are a group of chemicals affecting the organisms and/or their progeny by altering different hormonal and metabolic processes, such as the secretion, activation, synthesis, release, and binding of natural hormones. Since ED are widespread in the environment, food and products of everyday use (e.g., plastic bottles and containers, liners of metal food cans, detergents, flame retardants, food, toys, cosmetics and pesticides, etc.) general population is continuously exposed during the whole life10. In addition, even low-dose exposure to EDs can lead to tissue and organ damage, and a common phenomenon associated with ED exposure is the occurrence of sex-specific effects both in laboratory animals and in humans11. As an example, exposure to the food contact material, bisphenol A (BPA), is linked to health risks such as endometriosis and polycystic ovary syndrome in women, as well as reduced fertility, due to its estrogenic effects12. In men, BPA can lower levels and diminish sperm quality13. Additionally, pesticides are associated with a higher risk of breast cancer in women and significant fertility issues in men13. So far, no specific tools are available to study the toxicological effects of environmental contaminants, including ED, in TG people9.
The present study aims to describe methods and parameters selected for the development of two TG animal models: a demasculinizing-feminizing model (dMF) and a defeminizing-masculinizing model (dFM). In particular, the selection of suitable dose levels, time, and way of administration of the hormones on the basis of the current human therapies are assessed14. Moreover, tissue and functional biomarkers that define the models uniquely are identified and characterized. In addition, the efficacy and tolerability of therapy in animals as well as the selection of the most appropriate markers for use in long-term studies, are described in detail together with the techniques used for such purposes.
In order to characterize the models, the following endpoints are analyzed: testosterone (T) serum level (the best biomarker to evaluate the success of GAHT in both models9,15); estradiol (E2) serum level (both models); thyroid stimulating hormone (TSH) and thyroxine (T4) (dMF model); sperm count (dMF model); clitoral dimension (dFM model); histopathological analysis of reproductive organs, liver and thyroid (for both models). In addition, gene expression of the following sex-specific liver cytochrome P450 isoforms (CYP450s, for both models) are also analyzed16,17: CYP2C11 (specifically expressed in the male liver), CYP3A18 (expressed 25 times more in male liver than in female), CYP2C12 (specifically expressed in the female liver), and CYP2C6 (predominantly expressed in female liver, but present at lower levels, also in the male).