In the present study, the toxicological effects of GTE in mice and rats included increased activity; decreased body weight gain; and histopathological lesions in the liver, nose, spleen, lymph nodes, and thymus. F344 rats also had decreased thymus weights. In addition, B6C3F1 mice showed increased mortality and increased liver-to-body weight ratios. The changes in the liver and nose were considered primary toxic effects of GTE, while the changes in other organs were considered to be secondary to high-dose, stress-related effects.
Decreased body weight gain after green tea consumption has previously been demonstrated in both animals and humans (
Dulloo et al. 1999;
Kao, Hiipakka, and Liao 2000;
Monteiro et al. 2008;
C. H. Wu et al. 2003). In our study, male rats were more severely affected, which is consistent with previous studies (
Raederstorff et al. 2003;
Takami et al. 2008;
S. N. Williams, Pickwell, and Quattrochi 2003;
Yoshino et al. 1994). The mechanism behind this weight reduction is unknown and may include such factors as changes in food consumption, inhibition of intestinal lipid absorption (
Ikeda et al. 2005,
1992;
Takami et al. 2008;
T. T. Yang and Koo 2000;
Yokozawa, Nakagawa, and Kitani 2002), an increase in the expenditure of energy (
Dulloo et al. 1999), and stimulation of lipid oxidation (
Dulloo et al. 1999;
Murase et al. 2002). Recently, a new mechanism was proposed, suggesting that GTE causes an increase in aromatase expression (
Monteiro et al. 2008).
Hepatic toxicity, observed in both rats and mice in this study, was one of the most significant effects. In mice, significant hepatic toxicity, including necrosis, was observed in the majority of the high-dose males and females. The hepatic toxicity was likely responsible for the early deaths observed in this group as well as accompanying morbidity and ruffled fur. In rats, hepatic toxicity was observed in a limited number of high-dose female rats. There are conflicting reports on the effects of green tea or its ingredients on the liver
in vivo and
in vitro. Several studies reported a protective effect of green tea on the liver in mice and rats, mainly by its proposed antioxidant effects (J. H.
Chen et al. 2004;
Dobrzynska et al. 2004;
Fiorini et al. 2005;
Zhang et al. 2006). Other studies reported an antineoplastic effect in the liver by inducing apoptosis of neoplastic cells in hepatocellular carcinomas (
Nishikawa et al. 2006). Though some studies failed to show any adverse hepatic effects following administration of green tea to mice, rats, and dogs (
Bun et al. 2006;
Isbrucker et al. 2006;
Liao et al. 1995), there are many reports of green tea–induced hepatic toxicity, both
in vitro and
in vivo.
Goodin and Rosengren (2003) reported severe hepatic necrosis, resulting in death, in female Swiss-Webster mice administered EGCG. The results of this study are consistent with their previous report of mild hepatotoxicity induced in C57B1/6 female mice (
Goodin et al. 2002). Polyphenon E, a decaffeinated green tea catechin mixture containing about 50% EGCG, was also found to cause hepatic necrosis in Swiss-Webster mice (
Chang et al. 2003). Green tea polyphenols and EGCG also caused hepatic necrosis in rats (
Johnson et al. 1999;
McCormick et al. 1999).
As mentioned above, the etiology of the hepatotoxicity is still unknown. However, it was suggested that the components responsible for the hepatotoxicity are the catechins and their gallic acid esters, predominantly EGCG (
Mazzanti et al. 2009). It was proposed that the hepatotoxicity was due to oxidative stress, induced in the liver by EGCG or its metabolites.
In the present study, a slight tendency toward increased susceptibility of females to hepatotoxicity was noted. In rats, findings in the liver were seen only in females; and in mice, the females, but not males, exhibited clinical abnormalities before dying. Sex-dependent effects of EGCG-mediated hepatic toxicity were demonstrated in Balb/c mice, where females were much more susceptible to the toxic effects (
Goodin, Bray, and Rosengren 2006). In addition, sex-specific differences in cytochrome P450 (CYP450) isoform modulation following administration of EGCG and epigallocatechin gallate to Swiss Webster mice were shown (
Goodin, Bray, and Rosengren 2006). Interestingly, increased female susceptibility to green tea–induced hepatotoxicity was also suggested in humans, possibly because of different genetic factors (
Mazzanti et al. 2009).
The most sensitive organ for detecting GTE toxicity was the nose, both in rats and in mice. This is the first time that nasal toxicity has been observed following green tea administration. It is reasonable to believe that the lesions in the olfactory system were at least in part responsible for the decreased body weight gain observed. Such lesions lead to changes in the animals’ ability to smell, and consequently to taste, culminating in decreased ability to acquire food (
Lock and Harpur 1992). In line with this assumption, the nasal lesions were generally more severe in the male rats, correlating to the more pronounced decreased body weight gain.
Nasal toxicity is more common following inhalation studies; however, noninhalation routes of administration can also lead to nasal lesions by exposure through the bloodstream to the tested compound or its metabolites (
Sells et al. 2007). In addition, the nasal epithelium itself is recognized as a major metabolizing organ, demonstrating significant enzymatic activity (
Bogdanffy 1990;
Dahl and Hadley 1991;
Reed 1993). For example, very active cytochrome P450 enzymes are present in the nasal epithelium, as well as glutathione S-transferase, carboxylesterases, aldehyde and formaldehyde dehydrogenase, and flavin monoxygenases (
Lock and Harpur 1992). Metabolic activity could explain the distribution of lesions in the nasal cavity (
Sells et al. 2007). In our study, the olfactory epithelium was affected more severely than the respiratory epithelium, which corresponds to the levels of enzymatic activity in these epithelial types, the olfactory epithelium having the higher levels (
Walsh and Courtney 1998). The concentration of CYP450 in the respiratory mucosa is only 25% of that in the olfactory mucosa (
Thornton-Manning and Dahl 1997).
The ability of green tea compounds to alter the activity of CYP450 has been demonstrated in various organs, either in human cell lines or in animals. Among the CYP450s that were found to be altered are CYP1A1, CYP1A2, CYP3A4, and CYP4A1 (
Allen et al. 2001;
Anger, Petre, and Crankshaw 2005;
Bu-Abbas et al. 1994;
L. Chen et al. 1996;
Maliakal, Coville, and Wanwimolruk 2001;
Nishikawa et al. 2004;
Obermeier, White, and Yang 1995;
Sohn et al. 1994;
Whitlock 1999;
S. N. Williams et al. 2000;
S. P. Yang and Raner 2005). However, other reports showed little or no effect of green tea on CYP450 activity (
Chow et al. 2006;
Donovan et al. 2004), and some of the CYP450 altered effects might be attributed to the caffeine component of the tea extracts, a potent inducer of CYP1A2 (
Ayalogu et al. 1995;
Goasduff et al. 1996). The fact that both the liver and the nasal cavity, two organs rich in metabolic activity, were the major target tissues in this study leads us to believe that metabolism and activation of GTE by CYP450 were, at least in part, responsible for the adverse effects observed. This issue will be of great interest for future studies.
Some of the findings in this study were considered to be secondary effects rather than a direct consequence of GTE toxicity. The increased activity of the rats during the first weeks of the study can be attributed to stimulation by caffeine. The decrease in thymus weight correlated with the atrophy seen in that organ, which was attributed to nonspecific stress related to high dose exposure, as were the microscopic lesions in the spleen and lymph nodes (
Pearse 2006).
Human exposure to GTE by habitual consumption of green tea would be very unlikely to reach the toxic concentrations of GTE as observed in our study, since it is estimated that 10 cups of green tea are equivalent to only 2.5 grams of GTE (
Fujiki et al. 2002). In addition, the recommended dose of GTE tablets, some of them sold as dietary supplements, is about 1,000 mg/d (Puritan’s Pride, Oakdale, NY). The high dose of 1,000 mg/kg/d in our studies would therefore be equivalent to about 60 to 70 times higher. However, abuse of these supplements may expose humans to much higher concentrations, and indeed, it is interesting to note that the most pronounced effect of GTE exposure in rodents was hepatotoxicity, similar to the effect observed in humans consuming such tablets. Nevertheless, nasal toxicity, which was a pronounced effect observed in our study, was never reported before in humans after exposure to GTE. This difference may stem either from lower levels of exposure in humans, or from the known differences in the amount and expression pattern of the different CYP450 in the oral mucosa between humans and rodents (
Ling et al. 2004). Indeed, a comprehensive study had shown that none of several chemicals known to elicit rodent nasal cytotoxicity was associated with a similar toxicity in humans (
Jeffrey, Iatropoulos, and Williams 2006).
A limitation of our study is the use of GTE, which is composed of several potentially toxic compounds, and additionally each component in the mixture may have a modifying effect on the other components. Therefore, it is difficult to define which of the GTE constituents is responsible for the toxic effects observed in our study. The picture is even more complex considering the different metabolites that may be formed from each compound, a fact that further complicates the relevance of our findings to humans.
In summary, GTE administered by gavage to mice and rats resulted in direct treatment-related effects in the liver similar to those seen in previous studies in humans and rodents. In addition, this is the first report of toxic effects of green tea in the nose. Secondary effects, attributed to stress, were observed in the spleen, lymph nodes, and thymus. Furthermore, body weight gain was decreased. The no adverse effect level (NOAEL) for the liver in both species was 500 mg/kg. In the nose of rats, the NOAEL in males was 62.5 mg/kg, and in the female no NOAEL was found. No NOAEL was found in the nose of male or female mice. The obvious increased susceptibility of the nose and the liver, both organs rich in active metabolic enzymes, suggests a role for GTE metabolites in the observed toxicity.