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Nadia Maffei Research Fellow (A.L.M.), Jean Hailes Centre (S.R.D.), Clayton; Baker Institute Menopause Clinic (G.W.), Prahran; Victoria, Australia 3168
Address correspondence and requests for reprints to: Alice L. Murkies, M.D., Nadia Maffei Research Fellow, Jean Hailes Centre for Women, 291 Clayton Road, Clayton, Australia 3168.
| Abstract |
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| Introduction |
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Following publication of the Allen Doisy bioassay for estrogens in 1923 (4), plant extracts were first reported to exhibit estrogenic activity in 1926 (5). By 1975, several hundred plants had been found to exhibit estrogenic activity on bioassay or to contain estrogenically active compounds (6). Phytoestrogens assumed biological and economic importance in the 1940s, with the outbreak of infertility in sheep grazing on pastures rich in subterranean clover in Western Australia, later known as "Clover Disease" (7).
Phytoestrogens were identified in the urine of nonhuman primates in 1979, (8) and in humans in 1982 (9, 10). Epidemiological studies suggest that consumption of a phytoestrogen-rich diet, as seen in traditional Asiatic societies, is associated with a lower risk of the so-called "Western" diseases such as breast and prostate cancer and cardiovascular disease (11).
Estrogenic activity has been reported amongst compounds produced by animals, plants, and microorganisms, as well as in industrially manufactured chemicals and their breakdown products (12). Pesticides and insecticides, including DDT, also contain estrogen-like compounds and are now classified as xenoestrogens (13). Little is known of the long-term effects of xenoestrogens, however there is substantial concern regarding their potentially deleterious effects. Further discussion of xenoestrogens is beyond the scope of this review.
| Classification and Metabolism of the Major Phytoestrogens |
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In humans, after consumption of plant lignans and
isoflavones, complex enzymatic metabolic conversions occur in the
gastrointestinal tract, resulting in the formation of heterocyclic
phenols with a close similarity in structure to estrogens (10) (Fig. 2
). Absorbed phytoestrogen metabolites
undergo enterohepatic circulation and may be excreted in the bile (16)
deconjugated by intestinal flora, reabsorbed, reconjugated by the
liver, and excreted in the urine (17). Lignans and isoflavones can be
measured in urine, plasma, faeces, semen, bile, saliva, and breast milk
(18). Concentrations of the different phytoestrogen metabolites vary
widely between individuals even when a controlled quantity of
an isoflavone or lignan supplement is administered. As dietary
phytoestrogen metabolism is predominantly determined by the
gastrointestinal flora, antibiotic use, or bowel disease and gender
will modify metabolism (10, 19, 20, 21).
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| Food Sources |
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Second generation soy foods are made by adding soy ingredients to a wide variety of manufactured foods, hence the isoflavone content is diminished, for example tofu yoghurt and soy noodle (33, 34, 35). Soy sauce contains few isoflavones.
Lignans are found widely in cereals, fruit, and vegetables. They occur
in high concentration in flaxseed also known as linseed (15, 30, 36)
and in lesser concentration in whole grain cereals, vegetables, fruit
and seeds (1) Table 1
. Estimation of the
concentration of lignans in foods has been limited by assay technique
(36).
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Resorcylic acid lactones, including zearalenone and zearalenol, are mycotoxins, and are produced by Fusarium species of mold growing on crops stored in damp conditions. These compounds are most concentrated in the seed hull which is commonly removed in preparation of foodstuffs (1).
| Phytoestrogen levels in various populations |
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Macrobiotics and other vegetarians such as Seventh Day Adventists have the highest excretion values of lignans (38). Asian populations, such as those in Japan, Taiwan and Korea, are estimated to consume 20150 mg/day of isoflavones, with a mean of about 40 mg from tofu and miso (38).
| Potency and biological effects |
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Estrogenic and antiestrogenic activity
Phytoestrogens are of biological interest because they exhibit both in vitro and in vivo weak estrogenic and antiestrogenic actions (1).
The estrogenic effect of phytoestrogens was first observed as reproductive disturbances in sheep (7). Isoflavones stimulate uterine hypertrophy in laboratory animals exhibiting estrogenic action (1, 40). When administered with estradiol, genistein functions as an antiestrogen, decreasing uterine estradiol uptake in animal models (32). Isoflavones exhibit anticarcinogenic activity in vivo. Laboratory animals fed soy-fortified diets, have predominantly less breast tumor proliferation after stimulation with direct acting [N-methyl-N'-nitrosourea (NMU)] and indirect acting [dimethylbenz[a]anthracene (DMBA)] tumor-inducing agents (32).
Genistein has been the phytoestrogen of greatest interest at present and, in vitro, has been shown to exert both proliferative (estrogenic) and antiproliferative (antiestrogenic) effects in human cell lines (41, 42). In the human estrogen receptor (ER)-positive MCF-7 breast cancer cell line, these effects are biphasic and concentration dependent, with stimulation of cell growth occurring at low concentrations of genistein [10-510-8 M] and inhibition at higher concentrations [10-410-5 M](41). At low concentrations genistein competes with estradiol for binding to the ER with a 50% inhibition concentration of 5 x 10-7 M and stimulates the expression of pS2 mRNA, a specific marker of ER-mediated estrogen like activity(41). Sathyamoorthy (42)and others have shown a similar stimulatory effect with daidzein, equol, and enterolactone at 10-6 M concentrations.
The antiproliferative effects of genistein described above occurred in both ER-positive and ER-negative cell lines and thus appear not to be mediated by the ER (41). It has been proposed that genistein, and perhaps other phytoestrogens, inhibit tumor cell growth by interfering with the tyrosine kinase activity of activated growth factor receptors and cytoplasmic tyrosine kinases, which are essential for the transduction of mitogenic signals. Akiyama and others (43) reported that genistein inhibits epidermal growth factor-receptor (EGF-R) tyrosine autophosphorylation, whereas Peterson and Barnes (44) were unable to demonstrate this effect and concluded that the isoflavones exert their inhibitory effects either downstream from EGF-R tyrosine autophosphorylation or by some other mechanism (44).
Extrapolation of cell culture studies to humans is questionable, especially in terms of tumor growth inhibition. A high soy diet results in an approximate plasma level of 0.54 mmol/l of genistein (45, 46), whereas the studies describing an antiproliferative effect indicate a minimum cell culture concentration of 10100 mmol/l of genistein (39, 32).
Other reported biologic properties
Isoflavones exhibit additional anticarcinogenic activity in vitro and have been reported to inhibit angiogenesis (47) and cell cycle progression (48). Other effects include aromatase enzyme inhibition (49, 50), stimulation of sex hormone binding globulin (SHBG) synthesis (51, 52), antioxidant properties (53), and digitalis-like activity (54).
| Effects in humans |
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A cyclic pattern of lignan excretion has been observed during the menstrual cycle in humans and in Vervet monkeys (8). It is probable that the precursors of these lignans are of dietary origin, however there is also a hormonal influence on the metabolism and absorption of these compounds (55). Dietary intervention with 60 g soy protein daily has been reported to increase follicular phase length (56). This effect was associated with suppression of the midcycle surges of FSH and LH (56). Twelve ounces of soy milk three times daily decreases serum 17 beta-estradiol and luteal phase serum progesterone in 2229-yr-old females (57). In contrast, daily 10 g flax seed supplementation increases luteal phase duration, but with no difference in follicular phase length in normally cycling women (58). An increase in SHBG was not observed in these studies (56, 58) in contrast to earlier in vitro reports (11, 51). McMichael-Phillips (59) has reported that 14 days of 60 g soy supplementation increases the proliferation rate of premenopausal breast epithelium.
Postmenopausal women
Japanese women are reported to have a low frequency of hot flushes
compared with postmenopausal western women, in part attributed to their
high phytoestrogen consumption (60). Whether this is valid has been
recently challenged (61). Evidence from several human studies
demonstrates that certain dietary phytoestrogens can produce mild
estrogenic effects in the postmenopausal woman, including estrogen-like
effects on vaginal cytology (62, 63, 64) and reductions in hot flushes
(647) (Table 2
). However, the findings
are inconsistent; four weeks supplementation with textured vegetable
protein produced no effect. There are variations in response within
studies, and there is no clear correlation in response to estrogenic
changes in vaginal cytology and the effect on hot flushes. This
illustrates the difficulty in making objective assessments of hot
flushes due to the natural resolution of flushes over time. The
variations in response may depend on populations studied, soy products
used, and study design, particularly with respect to duration of
exposure, variability in response, and nonresponse in some
postmenopausal women to phytoestrogen supplementation (24).
Phytoestrogen supplementation may benefit some women in alleviating
menopausal symptoms, however it is difficult to make specific
recommendations of formulation and dosage.
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| Disease Relationships |
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There is evidence to support the hypothesis that phytoestrogen consumption contributes to the lower incidence of cardiovascular disease in Asian countries and in vegetarians and that phytoestrogens may be cardioprotective (11).
A study of Rhesus male and female monkeys has shown that isoflavone-intact soy protein supplementation results in a hypocholesterolemic effect when compared with a soy diet depleted of phytoestrogen (P < .004) (68). Both male and female animals receiving the soy diet were observed to have low density lipoprotein (LDL) cholesterol and very low density lipoprotein (VLDL) cholesterol values 3040% lower than controls. High density lipoprotein (HDL) cholesterol ratio increased by 50% in female and 20% in male animals (68).
Another study has investigated the effects of soy protein in male cynomologus macaques. The animals were fed an atherogenic diet and randomized to supplementation with either casein, soy protein with isoflavones intact (soy+), or soy protein with isoflavones extracted (soy-). The soy+ diet had a lower total cholesterol, higher HDL cholesterol, and lower LDL and VLDL cholesterol. Similarly the extent of coronary artery atherosclerosis was negligible in the monkeys fed the soy+ diet compared with the other two groups in whom atheromatous plaque was detected (69). Furthermore the soy+ diet enhanced dilator responses of atherosclerotic coronary arteries to acetylcholine in female rhesus monkeys (69).
Cassidy et al. observed a 9% reduction in total cholesterol in a small study of normolipemic premenopausal women given a 60-g soy protein supplement (56). Consumption of 25-g soy protein enriched bread resulted in a decreased total serum cholesterol and increased HDL cholesterol in hypercholesterolemic men (70). A soybean protein diet in subjects with Type II hyperlipoproteinemia may lower cholesterol on average by 20% (71). A meta-analysis of 38 published controlled clinical trials of soy protein consumption that averaged 47 g per day and serum lipid and lipoprotein concentrations found that consumption of soy protein was associated significantly with mean reductions in total cholesterol (9.3% decrease, 95% CI 0.350.85 mmol/L), LDL cholesterol (12.9% decrease, 95% CI 0.300.82 mmol/L), and triglycerides (10.5% decrease, 95% CI 0.0030.29 mmol/L) (72). The hypocholesterolemic effect appears to be significantly related to pretreatment plasma cholesterol (72). A recent study of normolipemic postmenopausal women supplemented with a 40-mg phytoestrogen pill demonstrated a 22% increase in HDL cholesterol and no significant change in other parameters (73). Dietary soy phytoestrogens may provide cardioprotective benefits via a direct effect on lipids. Other reported properties, such as inhibition of platelet aggregation and antioxidant effects, may also be important (1, 74).
Osteoporosis
Osteoporosis is related to multiple factors including aging, hormone deficiency, and diet. There is a paucity of data regarding the possible role of phytoestrogens in bone metabolism and the incidence of osteoporosis. Dietary soybean prevents significant bone loss in ovarectomized rats (P < 0.001) (75). Ipriflavone (7 isopropoxy-isoflavone), a synthetic flavonoid, inhibits osteoclast recruitment and function, and 600 mg/day has prevented bone loss at the distal radius in osteoporotic postmenopausal women (76). Postmenopausal women randomized to receive casein, soy protein with either 1.39 mg total isoflavones/g protein (ISP), or 2.25 mg total isoflavones/g protein (ISP+) for six months demonstrated increased bone mineral content and density with ISP+ compared with controls (P < 0.005) (77). Postmenopausal women increased bone mineral content when fed 45 g soy enriched bread compared with controls fed wheat kibble bread (P < 0.03) (64). At present there is little published data to support a specific role for phytoestrogens in the prevention of osteoporosis, and further studies of longer duration are needed.
Cancer
The incidence of hormone dependent tumors is lower in Asia and Eastern Europe than western countries (11, 78) and amongst vegetarians (79, 80). Breast, ovarian, prostate, and colon cancer show a negative correlation with cereal and phytoestrogen intake when comparing cancer mortality rates and food availability data between countries (78).
Breast cancer
Japanese immigrants to North America have a higher incidence rate of breast cancer than their counterparts in Japan (81). Breast cancer rates of North American-born Japanese and "early" Japanese immigrants are almost identical to those of caucasian North Americans, whereas "late" immigrants have an incidence rate intermediate between the former groups and that of Japanese residing in Japan (81). Such findings support the role for environmental conditions in the etiology of breast cancer. Japanese women, in their homeland, who have breast cancer have a higher number of in situ tumors with fewer nodal metastases, and those with metastases have less nodal spread, than women with breast cancer in the United States or Britain (82). Hirayama (83) reported a significant graded inverse association in Japanese women between risk of breast cancer and consumption of miso (soybean paste soup). A diet high in soy products conferred a low risk of breast cancer in premenopausal women in Singapore, with no effect observed in postmenopausal women (84).
Baghurst and Rohan (79) investigated the relationship between dietary fiber and breast cancer in a case controlled study and reported a progressive reduction in breast cancer relative risk with each quintile of increasing fiber intake for women. Those in the highest quintile of nonstarch polysaccharide intake had a relative risk of 0.46. Whether this relates to interference with the enterohepatic circulation of both endogenous estrogens and phytoestrogens and hence an overall reduction in total circulating estrogens, to the phytoestrogen content of the dietary fiber, the exclusion of other carcinogenic foods or the concurrent ingestion of other influencing macronutrients is yet to be ascertained. Low urinary lignan values, a measure of low fiber intake, have been reported in breast cancer patients (11).
Protective effects of isoflavones including soy, measured by tumor number, incidence, metastases, and latency (857), are seen in animal models with experimentally induced breast cancer. Prepubertal genistein-treated rats developed fewer mammary gland terminal-end buds, with significantly less cells in the S-phase of the cell cycle, and more lobules than controls at 50-days-old (88).
Breast cell lines saturated with predominantly genistein exhibited receptor stimulation at low concentrations, (423, 89) and dose dependent inhibition at increased concentrations (40, 89, 90, 91).
The epidemiological, animal, and cell-line data suggest that phytoestrogens may play a role in breast cancer. Prepubertal phytoestrogens may cause precocious maturation of breast terminal end buds to more differentiated lobules and subsequent breast cancer protection. In contrast, increased post-pubertal exposure, without breast maturation from significant phytoestrogen ingestion in childhood, or another stimulus for breast maturation such as full-term pregnancy, could potentially increase breast cancer risks via an agonistic estrogenic action.
Prostate cancer
Mills (92) reported that increased consumption of beans, lentils and peas, tomatoes, and dried fruits was associated with significantly decreased prostate cancer risk in 14,000 Seventh Day Adventist men (92). Hirayama (83) showed the protective effects from prostate cancer with consumption of green leafy vegetables, relative risk 0.5 (P < 0.03), but found no association with soybean paste (83). A prospective study of men of Japanese ancestry living in Hawaii has shown a decreased prostate cancer risk in those who consume rice and tofu (93), and a study of Japanese immigrants to North America reported an increase in the incidence rate of prostate cancer with younger age at immigration, supporting the hypothesis that environmental changes, including diet, can impact on cancer risk even in later life (79).
In human prostate cancer cell lines, high concentrations of genistein and biochanin A inhibit the growth of androgen-dependent and independent cells. However fairly high concentrations of genistein were required to achieve this effect (44).
Overall, the epidemiological data suggest that phytoestrogens may play a protective role against the development prostate cancer (51); however, the physiological significance of the inhibitory effects of genistein on prostate cancer cell lines in vitro at this stage is difficult to evaluate.
| Conclusion |
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Cancer data is still in its infancy. Extrapolating from human cell line and animal studies has limitations. More human studies are needed to establish the role of phytoestrogens as estrogen agonists and antagonists and of their actions on tyrosine kinases and other growth factor inhibitors in the cancer population. Although epidemiological and animal data suggest phytoestrogens may play a protective role against both breast and prostate cancer (50), the antiproliferative effects observed in breast and prostate cancer cell lines must be interpreted with caution because of the difficulty in correlating the phytoestrogen exposure to the cells in vitro to in vivo tissue levels in humans. Studies of the inhibitory effects of genistein on the growth of untransformed, normal cells are needed if an increased phytoestrogen dietary intake is to be widely recommended. Furthermore the temporal relationships between dietary phytoestrogen exposure in humans and carcinogenesis needs to be investigated. Data from the animal models described indicate prepubertal exposure may be essential for the breast cancer protective effects to be manifest. Western women, particularly postmenopausal women who have the greatest breast cancer risk, are being encouraged to suddenly increase their phytoestrogen intake without consideration of this potentially significant and possibly adverse temporal effect.
In conclusion, it is naive to try to extract a single component of a total life style from a community such as Japan, where several other significant lifestyle factors are operative, and expect to see a distinct correlation with disease. It may be that phytoestrogen ingestion needs to be life-long and combined with other low-risk dietary constituents and behaviors for the protective effects to be significantly manifest. To date, major dietary studies relating to cancer prevention have been mostly limited to the effects of soy; however, other foods and their interactions also warrant investigation.
| Acknowledgments |
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| Footnotes |
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Received July 1, 1997.
Revised October 24, 1997.
Accepted October 30, 1997.
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