In addition to its persistence, mobility, and widespread contamination of water, atrazine is also a concern because several studies have shown that atrazine is a potent endocrine disruptor active in the ppb (parts per billion) range in fish (
4,
5), amphibians (
6–
12), reptiles, and human cell lines (
5,
13–
15), and at higher doses (ppm) in reptiles (
16–
18), birds (
19), and laboratory rodents (
20–
28). Atrazine seems to be most potent in amphibians, where it is active at levels as low as 0.1 ppb (
6–
10). Although a few studies suggest that atrazine has no effect on amphibians under certain laboratory conditions (
29,
30), in other studies, atrazine reduces testicular volume; reduces germ cell and Sertoli cell numbers (
11); induces hermaphroditism (
6,
8,
10); reduces testosterone (
10); and induces testicular oogenesis (
7–
9,
31). Furthermore, atrazine contamination is associated with demasculinization and feminization of amphibians in agricultural areas where atrazine is used (
32) and directly correlated with atrazine contamination in the wild (
7,
9,
33,
34).
Despite the wealth of data from larvae and newly metamorphosed amphibians, the ultimate impacts of atrazine’s developmental effects on reproductive function and fitness at sexual maturity, which relate more closely to population level effects and amphibian declines, have been unexplored. In the present study, we examined the long-term effects of atrazine exposure on reproductive development and function in an all-male population of African clawed frogs (
Xenopus laevis), generated by crossing ZZ females (sex-reversed genetic males) to ZZ males (
SI Materials and Methods). The advantage of using this population is that 100% of the animals tested were genetic males. As a result, all hermaphrodites and females observed are ensured to be genetic males that have been altered by endocrine disruption. We examined sex ratios, testosterone levels, sexual dimorphism, reproductive behaviors, and fertility in males exposed to 2.5 ppb atrazine throughout the larval period and for up to 3 years after metamorphosis.
Discussion
Previous studies showed that atrazine demasculinizes (chemically castrates) and feminizes exposed amphibian larvae, resulting in hermaphrodites (
8,
10) or males with testicular oocytes (
7,
9) at metamorphosis. Since our initial publications (
7,
9,
10), the effects of atrazine on amphibian development and the significance of these effects to amphibian declines have been a subject of debate (
30,
35,
36). Although some investigators, including Carr et al. (
6), reported statistically significant effects of atrazine on gonadal morphology in
X. laevis (
P < 0.0003 for multiple testes and
P = 0.0042 for hermaphrodites), others, using different experimental conditions and different populations of the same species, suggested that atrazine had no effect (
29). Essential to this debate, however, is (
i) the terminology used to describe gonadal abnormalities; (
ii) the expertise and ability of other researchers to recognize abnormalities; (
iii) the possibility of natural variation in sex differentiation processes between species and even between populations (or strains) within a species (
37); and (
iv) the long-term consequences and significance of the observed abnormalities to amphibian reproductive fitness. Here we describe complete and functional female development in genetic (ZZ) males exposed to atrazine, not the production of hermaphrodites or males with testicular oocytes. Thus, there is no confusion in the present study regarding proper terminology or proper identification. Furthermore, because we used an all genetic (ZZ) male colony and genotyped the atrazine-induced ZZ females, there is no question that atrazine completely sex-reversed genetic (ZZ) males, resulting in reproductively functional females.
The present study thoroughly examines the long-term effects of atrazine on reproductive function in amphibians. Although a single published study attempted to examine long-term reproductive effects of atrazine in amphibians (
38), the authors did not report examinations of morphology. Furthermore, their examination of fertility and breeding of atrazine-exposed males was conducted after animals were injected with reproductive hormones (human chorionic gonadotropin, hCG), effectively providing “hormone replacement therapy” and reversing the effects of atrazine. The present study represents a more thorough examination of the effects of atrazine on sex hormone production, testosterone-dependent development and morphology, male reproductive behavior, and fertility.
Perhaps the most dramatic finding here is that hermaphroditism observed at metamorphosis in animals exposed to atrazine (
6,
10) can ultimately result in complete feminization. The complete feminization of males exposed to atrazine is consistent with two previous studies that showed that atrazine feminizes zebra fish (
Danio rerio) (
5) and
Xenopus laevis (
39) (
Fig. 6) and a more recent study that showed that atrazine exposure feminizes leopard frogs,
Rana pipiens (
40). These previous reports based their findings on shifts in the sex ratio, however; our study showed that atrazine-induced females are indeed genetic males. Furthermore, we showed that feminization is persistent and complete, resulting in reproductively functional females capable of producing viable eggs. Together, the present data and these three similar reports (
5,
39,
40) suggest that sex-reversal by atrazine (complete feminization of genetic males) is not a species-specific effect but rather one that occurs across nonamniote vertebrate classes.
In addition to feminization, individuals exposed to atrazine that appeared male were demasculinized in the present study. The decline in testosterone in atrazine-exposed males, also shown in previous studies (
10), is consistent with the decline in all testosterone-dependent morphologies examined here, including demasculinized/feminized laryngeal morphology and decreased breeding gland size. The decreased testosterone and absence of increased testosterone in atrazine-exposed males in the presence of females is further consistent with the inability of atrazine-exposed males to compete with unexposed males for access to females and consistent with the decline in sperm production and severely impaired fertility observed in atrazine-exposed males. The decreased frequency of tubules containing mature sperm suggests that the previously reported decline in germ cells and nursing cells after only 48 h exposure to atrazine in
X. laevis (
11) persists through adulthood. Likewise, the demasculinized larynges suggest that the smaller laryngeal size observed at metamorphosis in previous studies (
10,
41) results in persistent effects through sexual maturity. The low fertility rate of atrazine-treated males (regardless of sperm content) suggests that even atrazine-exposed males with adequate sperm do not show the copulatory behavior necessary for successful reproduction.
The present results are also consistent with other studies that examined long-term behavioral effects of atrazine in fish (salmon,
Salmo salar) (
4). Salmon exposed to atrazine (≥6 ppb) showed a dose-dependent decrease in androgens. Atrazine-exposure (≥6 ppb) resulted in a significant decline in sperm production (milt), and exposed males lost the ability to respond to the attractant female pheromone. Furthermore, atrazine reduced sperm content in a reptile (caiman,
Caiman latirostris), producing a morphology nearly identical to what we report here (
18). The similarities between these previous findings in fish (
4) and in reptiles (
18) and the present findings in an amphibian suggest that the demasculinizing effects of atrazine are also not species, genera, family, or even order specific but occur across vertebrate classes. Indeed, declining androgens (
22,
26) and decreased sperm production have been shown in laboratory rodents exposed to atrazine as well (
22,
26,
42), albeit at higher doses. Furthermore, atrazine exposure is highly correlated (
P < 0.009) with low sperm count, poor semen quality, and impaired fertility in humans (
43).
Although atrazine reportedly affects vertebrates through a number of mechanisms, the reported mechanism most consistent with the effects observed on amphibian reproduction here is the induction of aromatase, which has been shown in several vertebrate classes (
5,
15,
16). The induction of aromatase is consistent with the natural sex differentiation process in
X. laevis, in which the sex-determining gene, DM-W, is a transcription factor (
44) that induces aromatase expression in the developing undifferentiated gonad of genetic (ZW) females (
44). Transcription and subsequent translation of aromatase leads to estrogen production, which in turn directs differentiation of the ovary from the undifferentiated gonad. Just as exogenous estrogen results in the differentiation of ovaries in exposed genetic (ZZ) male
X. laevis (
45), induction of aromatase and subsequent estrogen production likely explain the complete feminization of genetic male
X. laevis by atrazine. Although ideally one needs to show that atrazine induces aromatase in genetic males before the transformation into females to support this hypothesis, it is not clear how such a study can be conducted here. Animals euthanized to measure aromatase expression do not have the opportunity to develop further, and thus it cannot be shown that the individuals that expressed aromatase were destined to become females. Furthermore, why only some males (10% in the present population) are completely feminized, whereas their siblings are merely demasculinized, remains to be explored.
Regardless of the mechanism, the impacts of atrazine on amphibians and on wildlife in general are potentially devastating. The negative impacts on wild amphibians is especially concerning given that the dose examined here (2.5 ppb) is in the range that animals experience year-round in areas where atrazine is used (
1,
32,
46), well within levels found in rainfall (
47), in which levels can exceed 100 ppb in the midwestern United States (
48), and below the current US Environmental Protection Agency drinking water standard of 3 ppb (
49). Furthermore, recent studies have shown that frog skin absorbs atrazine at much higher rates than the skin of mammals (
50), and even semiterrestrial frog species take up significant amounts of atrazine (
51). Thus, the exposure level examined in the present study is relevant even to semiterrestrial amphibians.
Although many studies have focused on death from disease and its role in global amphibian declines and sudden enigmatic disappearances of populations, virtually no attention has been paid to the slow gradual loss of amphibian populations due to failed recruitment (
52). The present study suggests several ways that exposure to endocrine disruptors such as atrazine may lead to population level effects in the wild and contribute to amphibian declines. Certainly, the inability to compete for females and the significant decline in fertility in exposed males, as reported in the present study, will have a direct impact on exposed populations. Furthermore, sex-reversed males (ZZ females) are only capable of producing genetic male (ZZ) offspring, so the sex ratio in exposed populations would be skewed both by the production of atrazine-induced ZZ females as well as by the fact that ZZ females can only produce ZZ (genetically male) offspring. In fact, mathematical models suggest that this very mechanism (the production of sex-reversed all male-producing animals) could drive populations to extinction (
53). Additionally, it is not known whether the increased susceptibility in the ZZ females is heritable or whether the “resistance” apparently present in atrazine-exposed males that do not become females is heritable. In either case, clearly, selection for resistance or susceptibility will affect population genetics and perhaps even cause bottlenecking and loss of genetic diversity. Atrazine likely affects amphibian populations through any combination of these effects and, as such, is a likely contributor to global amphibian declines. It seems that the concerns of Sanderson et al. [“A logical concern would be that exposure of wildlife and humans to triazine herbicides, which are produced and used in large quantities, and are ubiquitous environmental contaminants, may similarly contribute to estrogen-mediated toxicities and inappropriate sexual differentiation.” (
15)] may be borne out.