Review articleOccurrence and fate of hormone steroids in the environment
Introduction
Steroid hormones are a group of biologically active compounds that are synthesized from cholesterol and have in common a cyclopentan-o-perhydrophenanthrene ring. Natural steroids are secreted by the adrenal cortex, testis, ovary and placenta in human and animal, and include progestogens, glucocorticoids, mineralocorticoids, androgens and estrogens (Raven and Johnson, 1999). Estrogens (estradiol, estrone and estriol) are predominantly female hormones, which are important for maintaining the health of the reproductive tissues, breasts, skin and brain. Progestogens (progesterone) can be thought of as a hormonal balancer, particularly of estrogens. Androgens (testosterone, dehydroepiandrosterone and androstenedione) play an important role in tissue regeneration, especially the skin, bones and muscles. Glucocorticoids (cortisol) are produced by the adrenal glands in response to stressors such as emotional upheaval, exercise, surgery, illness or starvation. All the steroid hormones exert their action by passing through the plasma membrane and binding to intracellular receptors. In addition, there are some synthetic steroids such as ethynylestradiol (EE2) and mestranol (MeEE2) used as contraceptives.
All humans as well as animals can excrete hormone steroids from their bodies, which end up in the environment through sewage discharge and animal waste disposal. Those steroids have been detected in effluents of sewage treatment plants (STPs) and surface water (e.g. Desbrow et al., 1998, Kuch and Ballschmitter, 2001, Ternes et al., 1999a). They may interfere with the normal functioning of endocrine systems, thus affecting reproduction and development in wildlife (Jobling et al., 1998). The steroids of concern for the aquatic environment due to their endocrine disruption potential are mainly estrogens and contraceptives, which include 17β-estradiol (E2), estrone (E1), estriol (E3), 17α-ethynylestradiol (EE2) and mestranol (MeEE2) (Fig. 1).
Vitellogenesis (plasma vitellogenin induction) and feminisation in male fish have been observed in British rivers and are attributed to the presence of these estrogenic compounds Desbrow et al., 1998, Jobling et al., 1998. Concentrations as low as 1 ng/l of E2 led to induction of vitellogenin in male trout Hansen et al., 1998, Purdom et al., 1994. Hormone steroids in the environment may affect not only wildlife and humans but also plants Shore et al., 1995b, Lim et al., 2000. Alfalfa irrigated with sewage effluent, which contained hormone steroids, was observed to have elevated levels of phytoestrogens (Shore et al., 1995b).
In addition to estrogenic steroids, there is also a concern about the use of steroid drugs used as growth promoters in livestock (Schiffer et al., 2001). However, little research has been conducted on the fate of these steroids excreted by animals and their effect on wildlife and human health.
In this brief review, we provide an overview of sources, environmental concentrations in surface and ground water, and summarize the current knowledge on fate and behaviour of these steroid compounds.
Section snippets
Physicochemical properties
Natural estrogens, namely estradiol, estrone and estriol, have solubilities of approximately 13 mg/l. Synthetic estrogenic steroids have much lower solubilities of 4.8 mg/l for EE2 and 0.3 mg/l for mestranol (Lai et al., 2000). All these steroids have very low vapor pressures ranging from 2.3×10−10 to 6.7×10−15 mm Hg (Table 1), indicating low volatility of these compounds. The log Kow values of natural steroids are 2.81 for E3, 3.43 for E1 and 3.94 for E2. Synthetic steroids have higher log Kow
Wastewater
The presence of estrogenic compounds in the environment has become a concern because they may interfere with the reproduction of man, livestock and wildlife. The hormones 17β-estradiol and estrone are naturally excreted by women (2–12 and 3–20 μg/person/day, respectively) and female animals, as well as by men (estrone 5 μg/person/day) (Gower, 1975). Based on the survey and previous measurements of human estrogen excretion, Johnson et al. (2000) estimated the daily excretion of estrogens from
Sorption
The distribution and partitioning of estrogenic steroids in the environment are determined by their physicochemical properties and site-specific environmental conditions. Williams et al. (1999) estimated the likely distribution of the steroid estrogens, E1, E2 and EE2, in three English rivers and predicted that the concentrations of these steroids under average conditions varied between 0.21 and 0.37 ng/l for E2, 0.27 and 0.44 ng/l for E1 and 0.024 and 0.038 ng/l for EE2. Bed sediments were
Summary and recommendations
Hormone steroids excreted by humans and animals enter the environment through the discharge of domestic sewage effluents and disposal of animal waste. These compounds could affect wildlife and human health by disrupting their normal endocrine systems. Hormone steroids have been detected in wastewater effluents and surface water as well as ground water at various levels. The behaviour and fate of these hormone steroids in the environment depend on their physiochemical properties and
Acknowledgements
The authors would like to thank Dr. A. Juhasz and Dr. A. Kumar for their valuable comments.
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