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Original Article NTP-CERHR Expert Panel Report on the Developmental Toxicity of Soy Infant Formula Gail McCarver, 1 Jatinder Bhatia, 2 Christina Chambers, 3 Robert Clarke, 4 Ruth Etzel, 5 Warren Foster, 6 Patricia Hoyer, 7 J. Steven Leeder, 8 Jeffrey M. Peters, 9 Emilie Rissman, 10 Michael Rybak, 11 Claire Sherman, 13 Jorma Toppari, 13 and Katie Turner 14 1 Medical College of Wisconsin, Milwaukee, Wisconsin 2 Medical College of Georgia, Augusta, Georgia 3 University of California San Diego Medical Center, San Diego, California 4 Georgetown University School of Medicine, Washington, District of Columbia 5 George Washington University Washington, District of Columbia 6 McMaster University, Ontario, Canada 7 University of Arizona, Tucson, Arizona 8 Children’s Mercy Hospitals and Clinics, Kansas City, Missouri 9 Pennsylvania State University, University Park, Pennsylvania 10 University of Virginia School of Medicine, Charlottesville, Virginia 11 U.S. Centers for Disease Control and Prevention, Atlanta, Georgia 12 Cerus Corporation/P-val Gal Consulting, Davis, California 13 University of Turku/Turku University, Turku, Finland 14 RTI International, Research Triangle Park, North Carolina Soy infant formula contains soy protein isolates and is fed to infants as a supplement to or replacement for human milk or cow milk. Soy protein isolates contains estrogenic isoflavones (phytoestrogens) that occur naturally in some legumes, especially soybeans. Phytoestrogens are nonsteroidal, estrogenic compounds. In plants, nearly all phytoestrogens are bound to sugar molecules and these phytoestrogen–sugar complexes are not generally considered hormonally active. Phytoestrogens are found in many food products in addition to soy infant formula, especially soy-based foods such as tofu, soy milk, and in some over-the-counter dietary supplements. Soy infant formula was selected for National Toxicology Program (NTP) evaluation because of (1) the availability of large number of developmental toxicity studies in laboratory animals exposed to the isoflavones found in soy infant formula (namely, genistein) or other soy products, as well as few studies on human infants fed soy infant formula, (2) the availability of information on exposures in infants fed soy infant formula, and (3) public concern for effects on infant or child development. On October 2, 2008 (73 FR 57360), the NTP Center for the Evaluation of Risks to Human Reproduction (CERHR) announced its intention to conduct an updated review of soy infant formula to complete a previous evaluation that was initiated in 2005. Both the current and previous evaluations relied on expert panels to assist the NTP in developing its conclusions on the potential developmental effects associated with the use of soy infant formula, presented in the NTP Brief on Soy Infant Formula. The initial expert panel met on March 15 to 17, 2006, to reach conclusions on the potential developmental and reproductive toxicities of soy infant formula and its predominant isoflavone constituent genistein. The expert panel reports were released for public comment on May 5, 2006 (71 FR 28368). On November 8, 2006 (71 FR 65537), CERHR staff released draft NTP Briefs on Genistein and Soy Formula that provided the NTP’s interpretation of the potential for genistein and soy infant formula to cause adverse reproductive and/or developmental effects in exposed humans. However, CERHR did not complete these evaluations, finalize the briefs, or issue NTP Monographs on these substances based on this initial evaluation. Between 2006 and 2009, a substantial number of new publications related to human exposure or reproductive and/or developmental toxicity were published for these substances. Thus, CERHR determined that updated evaluations of genistein and soy infant formula were needed. However, the current evaluation focuses only on soy infant formula and the potential developmental toxicity of its major isoflavone components, e.g. genistein, daidzein (and estrogenic metabolite, equol), and glycitein. This updated evaluation does not include an assessment on the potential reproductive toxicity of genistein following exposures during adulthood as was carried out in the 2006 evaluation. CERHR narrowed the scope of the evaluation because the assessment of reproductive effects of genistein following exposure to adults was not considered relevant to the consideration of soy infant formula use in infants during Published online in Wiley Online Library (wileyonlinelibrary.com) DOI: 10.1002/bdrb.20314 *Correspondence to: Gail McCarver, Medical College of Wisconsin, Milwaukee, Wisconsin. E-mail: [email protected] Received 4 March 2011; Accepted 17 May 2011 Birth Defects Research (Part B) 92:421–468 (2011) & 2011 Wiley Periodicals, Inc.
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NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

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Page 1: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

Original Article

NTP-CERHR Expert Panel Report on theDevelopmental Toxicity of Soy Infant Formula

Gail McCarver,1� Jatinder Bhatia,2 Christina Chambers,3 Robert Clarke,4 Ruth Etzel,5 Warren Foster,6

Patricia Hoyer,7 J. Steven Leeder,8 Jeffrey M. Peters,9 Emilie Rissman,10 Michael Rybak,11 ClaireSherman,13 Jorma Toppari,13 and Katie Turner14

1Medical College of Wisconsin, Milwaukee, Wisconsin2Medical College of Georgia, Augusta, Georgia

3University of California San Diego Medical Center, San Diego, California4Georgetown University School of Medicine, Washington, District of Columbia

5George Washington University Washington, District of Columbia6McMaster University, Ontario, Canada7University of Arizona, Tucson, Arizona

8Children’s Mercy Hospitals and Clinics, Kansas City, Missouri9Pennsylvania State University, University Park, Pennsylvania

10University of Virginia School of Medicine, Charlottesville, Virginia11U.S. Centers for Disease Control and Prevention, Atlanta, Georgia

12Cerus Corporation/P-val Gal Consulting, Davis, California13University of Turku/Turku University, Turku, Finland

14RTI International, Research Triangle Park, North Carolina

Soy infant formula contains soy protein isolates and is fed to infants as a supplement to or replacement for human milkor cow milk. Soy protein isolates contains estrogenic isoflavones (phytoestrogens) that occur naturally in some legumes,especially soybeans. Phytoestrogens are nonsteroidal, estrogenic compounds. In plants, nearly all phytoestrogens arebound to sugar molecules and these phytoestrogen–sugar complexes are not generally considered hormonally active.Phytoestrogens are found in many food products in addition to soy infant formula, especially soy-based foods such astofu, soy milk, and in some over-the-counter dietary supplements. Soy infant formula was selected for NationalToxicology Program (NTP) evaluation because of (1) the availability of large number of developmental toxicity studies inlaboratory animals exposed to the isoflavones found in soy infant formula (namely, genistein) or other soy products, aswell as few studies on human infants fed soy infant formula, (2) the availability of information on exposures in infantsfed soy infant formula, and (3) public concern for effects on infant or child development. On October 2, 2008 (73 FR57360), the NTP Center for the Evaluation of Risks to Human Reproduction (CERHR) announced its intention to conductan updated review of soy infant formula to complete a previous evaluation that was initiated in 2005. Both the currentand previous evaluations relied on expert panels to assist the NTP in developing its conclusions on the potentialdevelopmental effects associated with the use of soy infant formula, presented in the NTP Brief on Soy Infant Formula.The initial expert panel met on March 15 to 17, 2006, to reach conclusions on the potential developmental andreproductive toxicities of soy infant formula and its predominant isoflavone constituent genistein. The expert panelreports were released for public comment on May 5, 2006 (71 FR 28368). On November 8, 2006 (71 FR 65537), CERHRstaff released draft NTP Briefs on Genistein and Soy Formula that provided the NTP’s interpretation of the potential forgenistein and soy infant formula to cause adverse reproductive and/or developmental effects in exposed humans.However, CERHR did not complete these evaluations, finalize the briefs, or issue NTP Monographs on these substancesbased on this initial evaluation. Between 2006 and 2009, a substantial number of new publications related to humanexposure or reproductive and/or developmental toxicity were published for these substances. Thus, CERHR determinedthat updated evaluations of genistein and soy infant formula were needed. However, the current evaluation focuses onlyon soy infant formula and the potential developmental toxicity of its major isoflavone components, e.g. genistein,daidzein (and estrogenic metabolite, equol), and glycitein. This updated evaluation does not include an assessment onthe potential reproductive toxicity of genistein following exposures during adulthood as was carried out in the 2006evaluation. CERHR narrowed the scope of the evaluation because the assessment of reproductive effects of genisteinfollowing exposure to adults was not considered relevant to the consideration of soy infant formula use in infants during

Published online in Wiley Online Library (wileyonlinelibrary.com)DOI: 10.1002/bdrb.20314

*Correspondence to: Gail McCarver, Medical College of Wisconsin,Milwaukee, Wisconsin.E-mail: [email protected] 4 March 2011; Accepted 17 May 2011

Birth Defects Research (Part B) 92:421–468 (2011)& 2011 Wiley Periodicals, Inc.

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the 2006 evaluation. To obtain updated information about soy infant formula for the CERHR evaluation, the PubMed(Medline) database was searched from February 2006 to August 2009 with genistein/genistin, daidzein/daidzin,glycitein/glycitin, equol, soy, and other relevant keywords. References were also identified from the bibliographies ofpublished literature. The updated expert panel report represents the efforts of a 14-member panel of government andnongovernment scientists, and was prepared with assistance from NTP staff. The finalized report, released on January15, 2010 (75 FR 2545), reflects consideration of public comments received on a draft report that was released on October19, 2009, for public comment and discussions that occurred at a public meeting of the expert panel held December 16 to18, 2009 (74 FR 53509). The finalized report presents conclusions on (1) the strength of scientific evidence that soy infantformula or its isoflavone constituents are developmental toxicants based on data from in vitro, animal, or human studies;(2) the extent of exposures in infants fed soy infant formula; (3) the assessment of the scientific evidence that adversedevelopmental health effects may be associated with such exposures; and (4) knowledge gaps that will help establishresearch and testing priorities to reduce uncertainties and increase confidence in future evaluations. The Expert Panelexpressed minimal concern for adverse developmental effects in infants fed soy infant formula. This level of concernrepresents a ‘‘2’’ on the five-level scale of concern used by the NTP that ranges from negligible concern (‘‘1’’) to seriousconcern (‘‘5’’). The Expert Panel Report on Soy Infant Formula was considered extensively by NTP staff in preparing the2010 NTP Brief on Soy Infant Formula, which represents the NTP’s opinion on the potential for exposure to soy infantformula to cause adverse developmental effects in humans. The NTP concurred with the expert panel that there isminimal concern for adverse effects on development in infants who consume soy infant formula. This conclusion wasbased on information about soy infant formula provided in the expert panel report, public comments received during thecourse of the expert panel evaluation, additional scientific information made available since the expert panel meeting,and peer reviewer critiques of the draft NTP Brief by the NTP Board of Scientific Counselors (BSC) on May 10, 2010(Meeting materials are available at http://ntp.niehs.nih.gov/go/9741.). The BSC voted in favor of the minimal concernconclusion with 7 yes votes, 3 no votes, and 0 abstentions. One member thought that the conclusion should be negligibleconcern and two members thought that the level of concern should be higher than minimal concern. The NTP’s responseto the May 10, 2010 review (‘‘peer-review report’’) is available on the NTP website at http://ntp.niehs.nih.gov/go/9741.The monograph includes the NTP Brief on Soy Infant Formula as well as the entire final Expert Panel Report on SoyInfant Formula. Public comments received as part of the NTP’s evaluation of soy infant formula and other backgroundmaterials are available at http://cerhr.niehs.nih.gov/evals/index.html. Reports can be obtained from the web site(http://cerhr.niehs.nih.gov/) or from: Kristina A. Thayer, PhD, NIEHS/NTP K2-04, PO Box 12233, Research TrianglePark, NC 27709. E-mail: [email protected]. Birth Defects Res (Part B) 92:421–468, 2011. r 2011 Wiley Periodicals, Inc.

Key words: endocrine disrupters; nutrition; safety assessment

SUMMARY OF CHEMISTRY, USE,AND HUMAN EXPOSURE

In children and adults, exposures to isoflavones occurthrough consumption of soy foods such as tofu, soy milk,soy flour, textured soy protein, tempeh, and miso (FDA,2000b). Infants can be exposed by consuming soy-basedinfant formula, the breast milk of mothers who consumesoy products, or by the use of soy in weaning or‘‘transition’’ foods. Soy oils or soy sauces contain little-to-no genistein (Setchell, 1998; ILSI, 1999). Soy protein canbe used in baked goods, breakfast cereals, pasta,beverages, toppings, meat, poultry, fish products, anddairy-type products including imitation milk and cheese(Soyfoods Associations of North America, 2009; UnitedSoybean Board, 2009). Soybean derivatives are present in60% of processed foods available from U.K. super-markets (UK-Committee-on-Toxicity, 2003). The percent-age of processed foods containing soybeans in the UnitedStates is not known. Exposure to genistein can also occurthrough soy supplements marketed for the beneficialeffects on health, such as improved cardiovascular healthand treatment of menopausal symptoms (Drugstore.com,2009).

On the basis of the sales of soy products, it appearsthat exposure to soy isoflavones in the United States isincreasing and will continue to increase. The SoyfoodsAssociation of America reported that soy food sales haveincreased from $300 million to over $4 billion between

1992 and 2008, attributing this increase to new soy foodcategories being introduced, soy foods being reposi-tioned in the market place, and new customers selectingsoy for health and philosophical reasons (SoyfoodsAssociations of North America, 2009).

The primary isoflavones detected in soy products,including soybeans and soy formula, are derived fromgenistein, daidzein, and to a smaller extent, glycitein.These isoflavones are often referred to as phytoestrogensbecause of their ability to bind to estrogen receptors(ERs) and display weak estrogenic activity comparedwith estradiol (at least based on in vitro model systems),with a relative estrogenic potency of genistein4daid-zein4glycitein (MAFF, 1998; UK-Committee-on-Toxicity,2003; Choi et al., 2008).

The majority of isoflavones in soy formula andunfermented soy products are conjugated to sugarmolecules to form the glycosides genistin, daidzin, andglycitin (Cassidy, 2006; Nielsen and Williamson, 2007).Glucose groups in glycoside compounds can also beesterified with acetyl or malonyl groups to form acetyl-or malonyl glycosides (UK-Committee-on-Toxicity, 2003)(Fig. 1). The terms genistein, daidzein, and glycitein referspecifically to the unconjugated (aglycone) forms of theisoflavones. Small amounts of genistein and daidzein(3.2–5.8%) are present in soy products in their un-conjugated (aglycone) forms (Chen and Rogan, 2004).As a result of bacterial hydrolysis during fermentation,aglycones represent a larger proportion of the isoflavones

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in fermented soy products such as miso, tempeh, andsoybean paste (ILSI, 1999; UK-Committee-on-Toxicity,2003). Because glycosidic compounds are rapidly decon-jugated in the gut to form the biologically active aglyconecompound, exposure to a particular isoflavone istheoretically the sum of the aglycone and respective

glycoside compound concentrations converted on thebasis of molecular weight (MAFF, 1998; UK-Committee-on-Toxicity, 2003). Unfortunately, there is an inconsistency inthe literature where many studies do not clarify whetherthe presented isoflavone levels were normalized on anaglycone basis. Failure to convert the major glycosides,

Fig. 1. Chemical structures of isoflavones found in soy formula.

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i.e. genistin, daidzin, glycitin, to the appropriate aglyconeequivalents can overestimate isoflavone levels or intake byB1.6-fold. Information in the Expert Panel report isnormalized to aglycone equivalents where feasible.

Isoflavone levels in soybeans can vary as a result ofcrop strain, geographic location, climate, and growingconditions (Setchell et al., 1998; UK-Committee-on-Toxicity, 2003). Heating of soy products can causedecarboxylation, deacetylation, or deglycosylation ofglycosides with decomposition of malonyl compoundsto their respective acetylglycosides (Setchell et al., 1998;UK-Committee-on-Toxicity, 2003). Except for alcoholextraction, processing soybeans does not usually reduceisoflavone content (ILSI, 1999).

Soy formula refers to infant food made using soyprotein isolate and other components such as corn syrup,vegetable oils, and sugar (Drugstore.com, 2009). Decadesago soy formula included soy flour. However, in the1950s and 1960s, cases of altered thyroid function, mostlygoiter, were reported in infants fed soy formula. Thisproblem was eliminated by adding more iodine to theformulas and replacing soy flour with soy protein isolate.Although the early reports of goiter in infants fed soyformula have mostly ceased since manufacturers begansupplementing soy formula with iodine in 1959, there isstill concern that the use of soy formula in infants withcongenital hypothyroidism (CH) may decrease theeffectiveness of thyroid hormone replacement therapy,i.e. L-thyroxin. The soy protein isolate is fortified withL-methionine, L-carnitine, and taurine and other nutrients(FDA, 2000a; Bhatia and Greer, 2008). Soy protein isolateincludes phytates (1.5%), which bind minerals andprotease inhibitors, which have antitrypsin, antichymo-trypsin, and antielastin properties (Bhatia and Greer,2008). Phosphorus, calcium, iron, and zinc are added tosoy formula to compensate for phytate binding ofminerals. Heat applied during the processing of soyprotein removes 80 to 90% of protease inhibitor activity.Aluminum is present in soy formulas because of theaddition of mineral salts.

Many aspects of infant formula use are unknown,including what percent of infants are exclusively fedformula compared with what percent are fed a mixtureof infant formula and breast milk. It is also unknownwhat proportion of formula-fed infants are exclusivelyfed soy formula. A 1998 infant-feeding survey conductedby Ross Products Division indicated that 18% of infantsare fed soy formula during the first year of life (Stromet al., 2001). According to market data and hospitaldischarge records, another estimate was that 25% ofnewborns in the United States are fed soy formula(Badger et al., 2002). A study conducted at YaleUniversity assessed formula changes in 189 breast-fedinfants and 184 formula-fed infants and reported that23% of infants in the study received soy formulasometime during the first 4 months of life (Forsythet al., 1985). Based on recent market data, sales of soyformula in the United States represent B12% of the U.S.infant formula dollar sales (personal communicationwith Robert Rankin, Manager of Regulatory and Techni-cal Affairs at the IFC, October 13, 2009). In the UnitedStates between 1999 and 2009, estimates of total soyinfant formula fed decreased from 22.5 to 12.7%calculated based on total formula sold corrected fordifferences in formula cost, i.e. expressed in equivalent

feeding units (public comment from the InternationalFormula Council (IFC), received December 3, 2009 andpersonal communication with Dr. Haley Curtis Stevens,IFC). When sales are considered as a surrogate measureof actual reported usage, these data provide a lowerindication of usage compared with other frequently citedestimates. The usage and sales of soy formula varygeographically ranging from 2 to 7% of infant formulasales in the United Kingdom, Italy, and France, to 13% inNew Zealand (Agostoni et al., 2006; Turck, 2007), and to31.5% in Israel (Berger-Achituv et al., 2005).

A commonly cited reason for use of soy formula is tofeed infants who are allergic to dairy products or areintolerant of lactose, galactose, or cow-milk protein(Essex, 1996; Tuohy, 2003). In May 2008, the AmericanAcademy of Pediatrics (AAP) released an updated policystatement on the use of soy protein-based formulas(Bhatia and Greer, 2008). The overall conclusion of theAAP was that, although isolated soy protein-basedformulas may be used to provide nutrition for normalgrowth and development in term infants, there are fewindications for their use in place of cow milk-basedformula. The only real indications for use are instanceswhere the family prefers a vegetarian diet or for themanagement of infants with galactosemia or primarylactase deficiency (rare). Soy formula is not currentlyrecommended for preterm infants. Similar conclusionswere reached in 2006 by the European Society forPaediatric Gastroenterology Hepatology and Nutrition(ESPGHAN) Committee on Nutrition (Agostoni et al.,2006).

A number of studies in the United States and abroadhave measured total isoflavone levels in infant formulas(see Table 9 of complete final expert panel reportavailable at http://cerhr.niehs.nih.gov/evals/genistein-soy/soyformula/soyformula.html). For formulas fromthe United States, the range of total isoflavone levelsreported in reconstituted or ‘‘ready-to-feed’’ formulaswas 20.9 to 47 mg/liter formula (Franke et al., 1998;Setchell et al., 1998). When normalized to aglyconeequivalents, genistein is the predominant isoflavonefound in soy formula (B58–67%), followed by daidzein(B29–34%) and glycitein (B5–8%). In contrast to theisoflavone content of soybeans and other soy productssuch as soy supplements or soy protein isolates, theisoflavone content in soy formula is less variable. Therange of total isoflavones content in soy formula samplescollected in the United States and other countries is 10 to47 mg/liter (Table 1) (Setchell et al., 1998; Genovese andLajolo, 2002).

Isoflavone exposure through soy formula intake hasbeen estimated in the United States and other countriesbased on total isoflavone levels measured in soyformulas and assumptions of formula intakes and infantbody weights. In the United States, total isoflavone intakeby infants was estimated at 2.3 to 9.3 mg/kg body weight(bw)/day, depending on age of the infant, the estimatedintake for genistein, expressed in aglycone equivalents,ranges from 1.3 to 6.2 mg/kg bw/day. These intakes areseveral orders of magnitude greater than infants whoconsume breast milk or a cows milk-based formula. Soyformula-fed infants have higher daily intakes of genisteinand other isoflavones compared with other populations(excluding regular consumers of soy supplements)(Table 2). However, differences in strategies used to

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develop the intake estimates and sample representative-ness limit the ability to compare across studies, especiallyfor those based on dietary surveys. In addition, iso-flavone intake seems to be inherently highly variable inadult populations and there is support for the notion thatthis variability cannot solely be attributed to differencesin study methods. Recognizing these caveats, the relativeranking of total isoflavone intake appears to be infantsexclusively fed soy formula4vegans4Japanese consum-ing a traditional diet4vegetarians4soy consumers.

Mean blood-based levels of isoflavones in infants fedsoy formulas are considerably higher than other popula-tions, including vegans and Japanese adults (Table 3).For example, concentrations of total genistein in wholeblood samples from U.S. infants fed soy formula are

1455 ng/ml at the 75th percentile (Cao et al., 2009). Thisvalue is almost five times higher than the maximumgenistein concentration detected in plasma in a smallstudy of Japanese men, n 5 6 (Adlercreutz et al., 1994).The mean level of genistein (757 ng/ml) in the blood ofthe soy formula-fed infants reported by Cao et al. (2009)is almost 20 times higher than the mean level of genisteindetected in a sample of vegetarians and vegans inOxford, England (Peeters et al., 2007). Average bloodlevels of total genistein in the soy formula-fed infants areB160 times higher than the mean levels of total genisteinin omnivorous adults in the United States reported byValentin-Blasini (2003) (757 vs. 4.7 ng/ml). A similarpattern is observed based on urinary concentrations ofisoflavones (Table 4).

Table 2Comparison of Estimated U.S. Intake of Genistein and Total Isoflavones in Infants Fed Soy Formula to Other Populations

Daily intake (mg/kg bw/day)

Population Genistein Total isoflavone Reference

U.S. infants (soy formula) 1.3–6.2 2.3–9.3 Table 9 from unabbreviated final expert panel report(http://cerhr.niehs.nih.gov/evals/genistein-soy/SoyFormulaUpdt/FinalEPReport_508.pdf)

U.S. adults (general) 0.005a–0.056b 0.0097a–0.096b Haytowitz et al. (2009)a; Tseng et al. (2008)b; Kirk et al.(1999)

U.S. vegetarians 0.14 0.21European men Mulligan et al. (2007)

Not soy consumers 0.005 0.009Soy consumers 0.057 0.100

European women Mulligan et al. (2007)Not soy consumers 0.004 0.007Soy consumers 0.062 0.112

Vegans (UK) 1.07 Friar and Walker (1998) as cited in Mortensen et al.(2009)

Japanese 0.077a–0.43b 0.67b Fukutake et al. (1996)a as cited in Fitzpatrick (1998);Arai et al. (2000)b

Table 1Comparison of Isoflavone Content in Infant Soy Formulas from Different Countries

Individual isoflavones, mg/liter formula as fed1

(percent of total)

CountryTotal isoflavones, mg/liter

formula as feda Genistein Daidzein Glycitein Reference

US (n 5 20) 20.9a–47b 12.1a–31.2b 7.1a–13.5b 1.7a–2.4b Franke et al. (1998)a; Setchellet al. (1998)b(57.7–66.3%) (B28.8–34%) (B5–8.3%)

UK (n 5 13) 18a–46.7b 10.4a–31.3b 6.7a–12.5b 0.9a–2.8b UK Ministry of Agriculture,Fisheries, and Food (1998)a;Hoey et al. (2004)b

(58.0–67.1%) (26.8–37%) (5–6.1%)

Australia (n 5 4) 17.2–21.9 – – – Knight et al. (1998)New Zealand 17.1–33 11.2–18 5.9–15 – Irvine et al. (1998)(n 5 5) (55–65.4%) (34.6–45%)Brazil 10–27.4 5.9–16.2 2.4–8.6 1.6–2.4 Genovese and Lajolo (2002)(n 5 7) (59.3–59.8%) (23.9–31.7%) (9–16.3%)

1CERHR converted between mg/kg (or mg/g) and mg/liter because the density of prepared formula is similar to water (specific gravityis 1.03) (personal communication from Mead Johnson Medical Nutrition Affairs). – 5 not specified.

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SUMMARY OF PHARMACOKINETICSAND GENERAL TOXICOLOGY

Pharmacokinetics

Genistein, daidzein, and glycitein exist mainly in theirglycosidic forms in unfermented soy foods. Beforeisoflavone glycosides can be absorbed into the systemiccirculation, they must first be hydrolyzed to theiraglycones, which have greater hydrophobicity and lowermolecular weight. Before systemic availability, mostgenistein and daidzein are conjugated with glucuronicacid by uridine diphosphate (UDP)-glucuronosyltrans-ferases; a smaller amount is conjugated to sulfate bysulfotransferases. Conjugation of isoflavones can alsooccur in liver. The glucuronide and sulfate conjugatesenter the systemic circulation, and the majority ofisoflavone compounds in the circulation are present inconjugated form.

Humans. In humans, a considerable amount ofpharmacokinetic information is available for genisteinand daidzein in adults. Less information is available forequol and very little data have been published onglycitein. Human developmental pharmacokinetic dataare lacking; the available ‘‘pharmacokinetic’’ data inhuman infants are essentially equivalent to biomonitor-ing data. The detection of genistein, daidzein, and equolin serum, urine, amniotic fluid, cord blood, and breastmilk in humans demonstrate fetal exposure and absorp-tion into the systemic circulation of infants. Fullpharmacokinetic data on genistein, daidzein, and/orglycitein among human infants following soy formulafeeding have not been published. Rather, data are limitedto single plasma concentrations, generally after chronicsoy formula feeding, which likely represent steady state(although this is uncertain) and spot urinary concentra-tions (Cruz et al., 1994; Setchell et al., 1997; Irvine et al.,

Table 4Comparison of Urinary levels of Genistein, Daidzein, and Equol in Infants Fed Soy Formula to the General

U.S. Population

Urinary concentration (geometric mean), mg/liter or ng/ml

Population Genistein Daidzein Equol Reference

U.S. infants fed soy formula (n 5 27) 5891 5097 2.3 Cao et al. (2009)U.S. children ages 6–11 years (n 5 721–726) 33.8 88.1 11.5 U.S. CDC (2008)U.S. adults ages 40–59 years (n 5 951) 23.7 52.3 8.39 U.S. CDC (2008)

Table 3Comparison of Blood-Based Levels of Genistein and Daidzein in Infants Fed Soy Formula to Other Populations

Average total isoflavone concentration, nM(ng/ml)

Population Sample Genistein Daidzein Reference

U.S. infants (soy formula, n 5 27) Whole blood(spots)

2801 (757), geometricmean

1007 (256), geometricmean)

Cao et al. (2009)

3296 (891), median 1081 (275), median)5384.5 (1455), 75th

percentile2040 (519), 75th

percentileU.S. infants (soy formula, n 5 7) Plasma 2531 (684) 1160 (295) Setchell et al. (1997)U.S. infants (cow milk formula, n 5 30) Whole blood

(spots)52.5 (14.2), geometric

mean(5.5), geometric mean Cao et al. (2009)

U.S. infants (cow milk formula, n 5 7) Plasma 11.7 (3.16), mean 8.1 (2.06), mean Setchell et al. (1997)U.S. infants (breastfed, n 5 20) Whole blood

(spots)40 (10.8), geometric

mean20.8 (5.3), geometric

meanCao et al. (2009)

U.S. infants (breastfed, n 5 7) Plasma 10.3 (2.77) 5.9 (1.49) Setchell et al. (1997)Omnivorous adults in the United States

(n 5 209)Serum 17.4 (4.7) 15.3 (3.9) Valentin-Blasini et al.

(2003)oLOD–(203), range oLOD–(162), range

Vegetarians, Finland (n 5 14) Plasma 17.1 (4.6) 18.5 (4.7) Adlercreutz et al. (1994)Vegans and vegetarians (Oxford, UK,

n 5 70)Plasma 148 (40) 78.7 (20) Peeters et al. (2007)

Japanese women at delivery (n 5 51a or194b)

Serum 26.6 (7.2)a–116.5 (31.5)b 7.1 (1.8)a–50.2 (12.8)b Todaka et al. (2005)a;Nagata et al. (2006)b

Japanese cord serum at delivery (n 5 51a

or 194b)Serum 71.8 (19.4)a–126.9 (34.3)b 16.9 (4.3)a–38.6 (9.81)b Todaka et al. (2005)a;

Nagata et al. (2006)b

Japanese men (traditional diet, n 5 6) Plasma 90.4 (24)–1204 (325),range

58.3 (15)–924 (235),range

Adlercreutz et al. (1994)

426 MCCARVER ET AL.

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Page 7: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

1998; Hoey et al., 2004; Franke et al., 2006; Halm et al.,2007; Franke et al., 2008a; Halm et al., 2008; Cao et al.,2009). No studies of human infants fed genistein,daidzein, and/or glycitein have been reported. Thus,the human pharmacokinetic data are solely based onstudies conducted in adults.

Relatively, few studies include measurement of glyci-tein and it has not been measured in biomonitoringstudies of the general population conducted by the CDCas part of NHANES (U.S. Centers for Disease Controland Prevention, 2008) or measured in the plasma or urineof soy formula-fed infants (Setchell et al., 1997; Irvineet al., 1998; Franke et al., 2006; Cao et al., 2009). Ifglycitein is measured in humans, it is generally followingintentional dosing of subjects with a soy protein orisoflavone supplement.

Before reaching the systemic circulation, most genis-tein and daidzein is conjugated to glucuronic acid byUDP-glucuronosyltransferases; a much smaller amountis conjugated to sulfate by sulfotransferase enzymes(Joannou et al., 1995; Kurzer and Xu, 1997; UK-Committee-on-Toxicity, 2003). Conjugation of genisteinoccurs in the intestine but also has been reported to occurin liver. Based on in vitro data, the enzymes mostinvolved in glucuronidation are: UGT1A1, 1A8, 1A9,1A10 (Tang et al., 2009), whereas the SULT enzymeslikely responsible for sulfation include SULT1A1 andSULT2A1 (Doerge et al., 2000; Chen et al., 2008).However, interpretation of the in vitro data requiresinformation on tissue-specific expression, particularly forhuman intestine and liver. Moreover, to inform thequestion of disposition of soy formula isoflavones, theontogeny of such tissue-specific expression is needed.Only a limited amount of such data are available (Hines,2008) precluding estimates of developmental differencesamong humans, as well as interspecies differencesamong the young.

The glucuronide and sulfate conjugates can enter thesystemic circulation, and it has been reported that themajority of isoflavone compounds in the circulationare present in conjugated form, thus limiting the bio-availability of the aglycone forms of isoflavones. Instudies in which humans were exposed to genistein orisoflavone aglycones at genistein doses of 1 to 16 mg/kgbw, most of the genistein was present in plasma inconjugated form, while free genistein represented 1 to 3%of total plasma genistein levels in most cases (Setchellet al., 2001; Busby et al., 2002; Bloedon et al., 2002).Conjugated isoflavones undergo enterohepatic circula-tion, and on return to the intestine, they are deconjugatedby bacteria with b-glucuronidase or arylsulfatase activity.The metabolites may be reabsorbed or further metabolizedby gut microflora. Isoflavones can undergo furtherbiotransformation that ultimately leads to the formationof 60-hydroxy-O-desmethylangolensin from genistein andO-desmethylangolensin from daidzein (Joannou et al.,1995; Kurzer and Xu, 1997; UK-Committee-on-Toxicity,2003). The metabolic profile varies among individuals,with some individuals producing little or no O-desmethyl-angolensin or equol, an intermediate metabolite ofdaidzein that is biologically active.

Based on the summary of the studies presentedin Nielsen and Williamson (2007) and Cassidy (2006),pharmacokinetic parameters (cmax, tmax, t1/2, area underthe plasma concentration-time curve [AUC]) are similar

for genistein and daidzein. For genistein, the average tmax

was 5.7 hr (range of 3.5–9.3 hr) and for daidzein, it was6.2 hr (range of 4.0–8.3 hr). These estimates are consistentwith the range of peak values of B6 to 8 hr reported byothers for genistein and daidzein following ingestion ofsoy or isoflavones (Pumford et al. (2002); reviewed inWhitten and Patisaul (2001); UK-Committee-on-Toxicity(2003); Larkin et al. (2008). The maximum concentrations(Cmax) of genistein and daidzein, when normalized toingestion of 1mmol/kg bw, were also similar at 0.49 or0.64 mM or 0.50 or 0.54 mM, respectively. The average half-life of elimination (t1/2) estimates from reviews byNielsen and Williamson (2007) and Cassidy (2006) didnot differ between genistein, 9.5 hr (range 6.1–17 hr), anddaidzein, 7.7 hr (range 4.2–16 hr). These estimates aregenerally similar to those presented in a recent review byLarkin (2008); 3 to 9 hr for daidzein and 8 to 11 hr forgenistein after intake of soy foods or pure isoflavoneglycosides. The AUC values, when normalized toingestion of 1mmol/kg bw, were 11 mmol�hr/liter forgenistein and 18mmol�hr/liter for daidzein. Absorptionhalf-lives for both daidzin and genistin, presumably asglucuronides and sulfates of daidzein and genistein,were reported at B1 to 3 hr following intake of foodscontaining r210 mg of each isoflavone or providingdoses of r2 mg/kg bw/day of each isoflavone (Lu et al.,1995; Lu and Anderson, 1998); reviewed in (Whitten andPatisaul, 2001).

Studies in humans that report the bioavailability andother pharmacokinetic parameters of isoflavones ingestedas glycosides versus aglycones have reported conflictingfindings (reviewed in UK-Committee-on-Toxicity, 2003;Cassidy et al., 2006; Nielsen and Williamson, 2007).Although there is no clear explanation for the conflictingfindings on bioavailability of the aglycone and glucoside,one factor may be the differences in the type of isoflavonepreparations administered to subjects, e.g. soybean extractscontaining mixtures of isoflavones, purified single iso-flavone, ingestion in tablet or liquid form (Cassidy, 2006).In addition, comparing the conclusions on bioavailabilityacross studies is difficult because of the variety of indicesused to assess bioavailability, e.g. relative AUC, cmax, tmax,urinary excretion, and recovery, etc. Prasain and Barnes(2007) discussed the various approaches used to assess thebioavailability of isoflavones. In pharmacology (andtoxicology), the term absolute bioavailability refers to theratio of AUC after oral ingestion to the AUC after systemicadministration, i.e. intravenous injection. This is thefraction of the compound absorbed through nonintrave-nous administration compared with the correspondingintravenous administration of the same drug. Thisapproach may underestimate bioavailability at the tissuelevel if circulating isoflavones in the conjugated form areconverted to aglycones by b-glucuronidases and sulfatasessecreted by cells within target tissues. In the nutritionliterature, bioavailability is often assessed by the percent ofadministered isoflavone that is recovered in the urine.Higher degrees of recovery in urine are interpretedas more bioavailability based on the assumption thatthe isoflavone must have been present in bloodbefore reaching the kidney and ultimately being excretedin urine.

In their review, Nielsen and Williamson (2007) con-cluded that despite the apparently contradictory findings,the data are consistent enough to conclude that (1) at

427NTP-CERHR EXPERT PANEL REPORT

Birth Defects Research (Part B) 92:421–468, 2011

Page 8: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

equivalent doses, the Cmax is higher for genistein anddaidzein following administration as glucosides comparedwith aglycones and (2) the half-life is not significantlydifferent for aglycone and glucoside. In addition, theyconcluded that deglycosylation is required for absorptionbut does not appear to be a rate-limiting step. As notedabove, studies by Setchell et al. (2001) and Rufer et al.(2008) suggest the percent of genistein and daidzeincirculating in the unconjugated forms do not differ basedon administered form. These conclusions support theassumption used by others that because glycosides arequickly deconjugated in the gut to form the activeaglycones, exposure to a particular isoflavone (e.g.genistein) is theoretically the sum of the aglycone andrespective glycoside compound concentrations convertedon the basis of molecular weight (MAFF; Setchell et al.,1998; UK-Committee-on-Toxicity, 2003; Rozman et al.,2006).

No pharmacokinetic studies, defined as measurementof isoflavone concentrations in serial blood or plasmasamples, have been conducted in infants or children.The only data that are interpretable in this context are thedata presented in Setchell et al. (1997) and Cao et al.(2009). These studies reported genistein and daidzeinconcentrations in plasma or blood samples obtained atunspecified times relative to feeding in infants chroni-cally fed soy formula. Usual feeding behavior wasreported to result in mean genistein concentrations of684 and 757 ng/ml, and mean daidzein concentrations of295 and 256 ng/ml by Setchell et al. (1997) and Cao et al.(2009), respectively. Data obtained by Cao et al. (2009)indicated that total genistein concentrations in wholeblood ranged from approximately 13.5 to 3562.9 ng/ml(range data obtained from personal communication withDr. Cao, December 2009). Assuming that the infants wereconsuming soy formula for more than 2 to 3 days, thesevalues approximate a steady-state condition, and thereported concentrations provide a context in whichanimal data can be prioritized and interpreted.

Limited data suggest low levels of equol are detectedin both whole blood and urine of infants, regardless oftype of feeding (Setchell et al., 1997, 1998; Hoey et al.,2004; Cao et al., 2009). Setchell et al. (1997, 1998) detectedequol in all cow-milk formula-fed infants, four of sevensoy formula-fed infants, and one of seven breast-fedinfants. In contrast, Cao et al. (2009) did not detectequol in the blood of any infant, but reported detectionof equol in urine among infants fed cow milk formula(22%) compared with those fed soy formula (5%) orbreast-fed infants (2%). Also, given that equol is presentin breast milk and cow milk (King et al., 1998; Setchellet al., 1998), it does not appear that soy-based formula isassociated with increased exposure to equol relative tocow milk-based formula or breast milk. Collectively,these data indicate that relatively low exposures toequol can be detected not only in infants fed soy formulabut also in infants fed cow milk-based formula andbreast milk. Thus, this level of equol exposure in humaninfants is markedly lower than that reported in animalsfed soy-based diets or daidzein. These data from humaninfants provide a context for interpreting the animaldata presented in the section ‘‘Summary of Develop-mental Toxicity of Soy Infant Formula, IndividualIsoflavones Found in Soy Infant Formula, or Other SoyTreatments.’’

Experimental animals. Genistein is absorbed inrats and mice following oral or subcutaneous (sc)exposure. According to data in Table 5, maximumgenistein levels in blood are obtained within 2 hr ofexposure. A mass-balance study of rats orally treated bygavage with 14C-genistein 4 mg/kg bw reported Vd at1.27 to 1.47 L (Coldham and Sauer, 2000). The ExpertPanel noted that the reported Vd suggests that most ofthe circulating radioactivity was not genistein but theglucuronide. Plasma protein binding ranged from B80 to90%. Radioactivity was distributed throughout the body,with levels in reproductive organs (vagina, uterus, ovary,and prostate) higher than levels in other organs (brain,fat, thymus, spleen, skeletal muscle, and bone). Somestudies demonstrated higher levels of genistein aglyconeversus conjugates within tissues compared with blood,raising the possibility of accumulation or hydrolysis ofaglycones within tissues (Fritz et al., 1998; Chang et al.,2000; Doerge et al., 2000). The Expert Panel noted thatdifferences between free genistein levels in blood andtissues are probably due to differences in how theaglycone and glucuronide compounds partition betweenfat in blood and tissues.

There are two high-quality studies that togetheraddress the impact of route of administration in youngmice (Doerge et al., 2002; Jefferson et al., 2009a,b). Basedon these reports, the dose-adjusted AUC after oralgenistin in CD-1 mice is about half that of the scgenistein. Although there is some inconsistency in theCmax data, both values are relevant to humans as they arewithin the range of blood and plasma concentrationsreported in human infants.

Studies in adult rats and mice fed soy-containing feedreported that blood total equol levels were 2 to 10 timeshigher than blood total genistein and daidzein levels(Brown and Setchell, 2001; Lund et al., 2001; Weber et al.2001). In most cases, total equol levels were lower than orwithin the same order of magnitude as genistein anddaidzein levels in fetuses or pups of rat dams fed soy-based diets (Brown and Setchell, 2001; Weber et al., 2001).The half-life for genistein and its metabolites followingingestion of soy products by rats was reported at 8.8 hr.No data were found for half-life of daidzein and itsmetabolites following ingestion through soy foods.Urinary levels of total genistein and daidzein werereported to be B25% of total equol levels in mice andB50% of total equol levels in rats.

Studies demonstrated placental transfer of genistein tothe rat fetus (Fritz et al., 1998; Doerge et al., 2001; Soucyet al., 2006) and lactational transfer to the rat pupfollowing dietary administration of genistein to the dam(Chang et al., 2000). A study examining placental transferreported higher concentrations of aglycone in fetusescompared with dams, leading the authors to concludethat placental transfer probably involves the aglycone;the finding was said to be consistent with limitedconjugation ability of the fetal rat (Doerge et al., 2001).One study reported that the percentage of free genisteinin milk from the pup stomach (78–97%) was higher thanin milk from the dams’ nipples (57%), suggesting thatgenistein conjugates may be hydrolyzed in the pupstomach (Fritz et al., 1998).

Studies in rats demonstrated the distribution of iso-flavones and metabolites to fetuses during pregnancy orpups during lactation following ingestion of soy-containing

428 MCCARVER ET AL.

Birth Defects Research (Part B) 92:421–468, 2011

Page 9: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

Tab

le5

Blo

od

Gen

iste

inL

evel

sin

Ro

den

tsF

edP

hy

toes

tro

gen

-Fre

eD

iets

and

Do

sed

wit

hG

enis

tein

Ser

um

gen

iste

in,

nM

(ng

/m

lo

rmg

/li

ter)

Sp

ecie

san

dst

rain

Ag

ean

dn

um

ber

of

anim

als

Ro

ute

,d

ura

tio

no

fex

po

sure

Do

seT

ota

lA

gly

con

eP

erce

nt

agly

con

eR

efer

ence

Rat

,S

pra

gu

e-D

awle

yD

ams

and

fetu

ses

on

GD

20o

r21

,n

51

dam

(11–

16fe

tuse

s)/

gro

up

Ora

l(g

avag

e),

sin

gle

trea

tmen

to

fd

amo

nG

D20

or

21,

blo

od

coll

ecte

d2

hr

afte

rd

osi

ng

20m

g/

kg

bw

Dam

s:35

40[9

56

]D

ams:

270

[73

]D

ams:

8%D

oer

ge

etal

.(2

001)

Fet

use

s:27

0[7

3]a

Fet

use

s:80

[22

]aF

etu

ses:

31%

34m

g/

kg

bw

Dam

s:54

80[1

48

0]D

ams:

290

[78

]D

ams:

5%F

etu

ses:

190

[51

]F

etu

ses:

60[1

6]

Fet

use

s:34

%75

mg

/k

gb

wD

ams:

4410

[11

91

]D

ams:

780

[211

]D

ams:

18%

Fet

use

s:22

0[5

9]

Fet

use

s:60

[16

]F

etu

ses:

27%

Rat

,S

pra

gu

e-D

awle

yP

ND

1to

2m

ales

and

fem

ales

,n

52

to3

pu

ps

fro

m2

dif

fere

nt

litt

erp

oo

ls

Ora

l(d

iet)

,p

up

sex

po

sed

ind

irec

tly

du

rin

gg

esta

tio

nan

dla

ctat

ion

500

pp

m(B

50m

g/

kg

bw

/d

ay)

tod

ams

1767

307

[48

]47

[13

]53

[27

%b

yC

ER

HR

calc

ula

tio

n]

Do

erg

eet

al.

(200

1)

Rat

,S

pra

gu

e-D

awle

yD

ams

and

PN

D7

and

21p

up

s,n

um

ber

exam

ined

no

tre

po

rted

Ora

l(d

iet)

,d

ams

exp

ose

dd

uri

ng

ges

tati

on

and

lact

atio

n

0D

ams:

6[2

]aD

ams:

6[2

]aD

ams:

100%

Fri

tzet

al.

(199

8)P

ND

7:9

[2]

PN

D7:

9[2

]P

ND

7:10

0%P

ND

21:

6[2

]aP

ND

21:

6[2

]aP

ND

21:

100%

25p

pm

(B2.

2m

g/

kg

bw

/d

ay)

Dam

s:40

[11

]D

ams:

9[2

]D

ams:

23%

PN

D7:

86[2

3]

PN

D7:

16[4

]P

ND

7:19

%P

ND

21:

54[1

5]

PN

D21

:18

[5]

PN

D21

:33

%25

0p

pm

(B22

mg

/k

gb

w/

day

)D

ams:

418

[11

3]

Dam

s:7

[2]

Dam

s:1.

7%P

ND

7:72

6[1

96

]P

ND

7:10

3[2

8]

PN

D7:

14%

PN

D21

:18

10[4

89

]P

ND

21:

120

[32

]P

ND

21:

6.6%

Rat

,S

pra

gu

e-D

awle

yP

ND

21/

PN

D14

0o

ffsp

rin

g,

mal

esan

dfe

mal

es(n

55–

6/g

rou

p)

Ora

l(d

iet)

,d

ams

exp

ose

dd

uri

ng

ges

tati

on

and

lact

atio

n,o

ffsp

rin

gre

ceiv

edd

am’s

die

tat

wea

nin

g

0o

10/o

10[o

3]

–1

to5%

all

do

seg

rou

ps,

bo

thag

esC

han

get

al.

(200

0)5

pp

m[B

0.4

–0.5

mg

/k

gb

w/d

ay]

PN

D21

:–

22[6

](m

ale)

20[5

](f

emal

e)P

ND

140:

–60

[16

](m

ale)

100

[27

](f

emal

e)10

0p

pm

[B8

–1

0m

g/

kg

bw

/day

]P

ND

21:

270

[73

](m

ale)

520

[14

0]

(fem

ale)

PN

D14

0:59

0[1

59

](m

ale)

940

[25

4]

(fem

ale)

500

pp

m[B

40

–50

mg

/k

gb

w/d

ay]

PN

D21

:–

2090

[56

4]

(mal

e)18

70[5

05

](f

emal

e)P

ND

140:

–60

00[1

62

0](m

ale)

7940

[21

44]

(fem

ale)

429NTP-CERHR EXPERT PANEL REPORT

Birth Defects Research (Part B) 92:421–468, 2011

Page 10: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

Tab

le5

Co

nti

nu

ed

Ser

um

gen

iste

in,

nM

(ng

/m

lo

rmg

/li

ter)

Sp

ecie

san

dst

rain

Ag

ean

dn

um

ber

of

anim

als

Ro

ute

,d

ura

tio

no

fex

po

sure

Do

seT

ota

lA

gly

con

eP

erce

nt

agly

con

eR

efer

ence

Rat

,S

pra

gu

e-D

awle

yP

ND

91,

fem

ale,

n5

4O

ral

(die

t),

21d

ays

star

tin

gat

PN

D70

750

pp

m22

00[5

84

]40

0[1

08

]18

.2%

San

tell

etal

.(1

997)

Rat

,S

pra

gu

e-D

awle

yP

ND

70,

mal

e,n

58/

gro

up

Ora

l(d

iet)

,d

ams

exp

ose

dd

uri

ng

ges

tati

on

and

lact

atio

n,

and

then

dir

ectl

yu

nti

lP

ND

70

0p

pm

18[5

]a0

0%F

ritz

etal

.(2

002)

25p

pm

(B2.

2m

g/

kg

bw

/d

ay)

167

[14

]6

[2]a

3.6%

250

pp

m(B

22m

g/

kg

bw

/d

ay)

1908

[51

5]

20[5

]1.

0%

Rat

,S

pra

gu

e-D

awle

yP

ND

70,

mal

e,n

58/

gro

up

Ora

l(d

iet)

on

PN

D57

–65

and

gav

age

on

PN

D66

–70

028

[8]a

6[2

]a21

.4%

Fri

tzet

al.

(200

2)25

0p

pm

die

t;22

mg

/k

gb

w/

day

gav

ageb

1785

[48

2]

32[7

]1.

8%

1000

pp

md

iet;

88m

g/

kg

bw

/d

ayg

avag

eb96

40[2

60

2]41

[11

]0.

43%

Rat

,S

pra

gu

e-D

awle

yA

du

lt,

fem

ale

dam

s,n

54/

gro

up

Ora

l(d

iet)

on

GD

7–P

ND

2125

0p

pm

2100

[56

7]

30[8

]1.

4%H

old

eret

al.

(199

9)

PN

D63

,fe

mal

eo

ffsp

rin

g,

n5

10/

gro

up

Ora

l(d

iet)

,ex

po

sed

ind

irec

tly

du

rin

gg

esta

tio

n(f

rom

PN

D7)

thro

ug

hla

ctat

ion

(PN

D21

)an

dth

end

irec

tly

on

PN

D21

–63

250

pp

m13

10[3

54

]38

[10

]2.

9%12

50p

pm

5300

[14

31]

150

[40

]2.

8%

Rat

,S

pra

gu

e-D

awle

yA

du

lt,

mal

ean

dfe

mal

e,n

510

/g

rou

p;

n5

7–10

/g

rou

p

Ora

l(d

iet)

,[d

ura

tio

no

ftr

eatm

ent

no

tcl

earl

yre

po

rted

]

25p

pm

(2m

g/

kg

bw

/d

ay)

r25

0[r

68

]c–

–H

old

eret

al.

(199

9)

250

pp

m(2

0m

g/

kg

bw

/d

ay)

1500

[40

5]

(mal

e)–

–20

00[5

40

](f

emal

e)12

50p

pm

(100

mg

/k

gb

w/

day

)60

00[1

62

0](m

ale)

––

9000

[24

30]

(fem

ale)

Rat

,S

pra

gu

e-D

awle

y11

Wee

ks,

fem

ale,

n5

2–8

Ora

l(d

iet)

for

3w

eek

s,b

egin

nin

gat

8w

eek

so

fag

e

049

[13

]aC

otr

on

eoet

al.

(200

1)25

0p

pm

(B16

mg

/k

gb

w/

day

)11

15[3

01

]13

8[3

7]a

12

1000

pp

m20

31[5

48

]44

6[1

20

]23

Rat

,S

pra

gu

e-D

awle

y11

Wee

ks,

fem

ale,

n5

4–5

SC

for

3w

eek

s,b

egin

nin

gat

8w

eek

so

fag

e,b

loo

dco

llec

ted

16–1

8h

raf

ter

last

inje

ctio

n

04

[1]a

––

Co

tro

neo

etal

.(2

001)

5m

g/

kg

bw

/d

ay45

0[1

22

]–

–16

6m

g/

kg

bw

/d

ay13

80[3

73

]66

2[1

79]a

4850

mg

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430 MCCARVER ET AL.

Birth Defects Research (Part B) 92:421–468, 2011

Page 11: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

feed by the dam (Brown and Setchell, 2001; Weber et al.,2001). In one study, gestation day (GD) 20.5 fetuses andPND 3.5 pups contained about half the total genisteinconcentration and about one-tenth the total equol concen-tration measured in dams; total daidzein concentrationswere about one-third lower in GD 20.5 fetuses and aboutthe same in PND 3.5 pups compared with dams (Weberet al. 2001). A second study reported that in pups born todams fed a soy-containing diet, total genistein levelsremained steady between birth and PND 12, while totaldaidzein levels were reduced by half during the same timeperiod (Brown and Setchell, 2001). On PND 16, the timewhen pups likely began eating food, there was a 5- to10-fold drop in total genistein and daidzein concentrationscompared with earlier time periods. In contrast, total equollevels in pups decreased steadily following birth.

Genistein glucuronide is the most abundant genisteinmetabolite in rat blood (Coldham and Sauer, 2000).Genistein is conjugated with glucuronide in the intestineand liver, and a study in rats demonstrated that themajority of glucuronidation most likely occurs in theintestine (Sfakianos et al., 1997). With the exception of4-hydroxyphenyl-2-propionic acid, all other urinarygenistein metabolites identified in rats were alsoreported for humans, suggesting pathways common tothe two species. Parent compound was the predominantform of genistein in the uterus, while in prostate the mostabundant form was the metabolite 4-hydroxyphenyl-2-propionic acid. One study reported no evidence thatgenistein aglycone or conjugate levels in blood weresaturated following exposure to dietary genistein at up to1250 ppm.

The Expert Panel noted that comparisons of serumaglycone levels in adult versus fetal or neonatal rodentsof the same study can be made from the rat datapresented in Table 5. A sc dosing study conducted in ratsdemonstrated similar percentages of serum aglycone(35–46%) at PND 21, 50, or 100. One study with gavageexposure demonstrated higher aglycone percentages infetuses (27–34%) than dams (5–18%) on GD 20 or 21(Doerge et al., 2001). A dietary study in which dams werefed 25 or 250 ppm genistein did not consistentlydemonstrate higher percentages of aglycone in dams(1.7–23%) compared with pups on PND 7 (14–19%) orPND 21 (6.6–33%) (Fritz et al., 1998). In an evaluationof all the data in Table 5, it was noted that percentagesof free genistein following oral exposure of adult ratswere usually below 10% but sometimes attained levelsof B20%; percentages of aglycone following direct and/or indirect oral exposure to genistein in rat pups r21days old were reported at 1 to 33%.

In a mass-balance study of rats orally treated bygavage with 4 mg/kg bw 14C-genistein, B65% of thedose was excreted in urine and 33% in feces at 166 hrfollowing dosing (Coldham and Sauer, 2000). Approxi-mately, 90% of the dose was recovered within the first48 hr following dosing. Total clearance was 1.18 mL/minin males and 2.0 mL/min in females. Genistein elimina-tion half-lives have been reported at 2 to 9 hr in rats and 5to 8 hr in mice (Coldham and Sauer, 2000). The ExpertPanel noted an apparent contradiction between the half-lives reported by Chang (2000) (B3–4 hr) and Coldhamand Sauer (2000) (B9–12 hr). The differences in half-livesmay have resulted from dosing regimen. Coldham andSauer used a single low dose of 4 mg/kg bw and ChangM

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431NTP-CERHR EXPERT PANEL REPORT

Birth Defects Research (Part B) 92:421–468, 2011

Page 12: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

et al. (2000) used a high daily dose rate of 50 mg/kg bw.The greatly decreased half-life at the higher dose mayhave resulted in part from saturation of glucuronidationand, hence, reduced enterohepatic circulation. Because itis expected that protein binding is saturated at highgenistein doses, a much smaller portion of the higherdose would be bound to plasma proteins, contributing tothe shorter half-life. In neonatal mice, elimination halflives were reported at 12 to 16 hr for genistein aglyconeand 16 to 19 hr for genistein conjugate.

SUMMARY OF DEVELOPMENTAL TOXICITYOF SOY INFANT FORMULA, INDIVIDUAL

ISOFLAVONES FOUND IN SOY INFANTFORMULA, OR OTHER SOY TREATMENTS

Human Data

No human data were identified on exposures to theindividual isoflavones found in soy formula.

Studies on outcomes after feeding soy formula ininfancy are summarized in Table 6. Most of the studieson growth have not detected differences in growth offull-term infants fed soy and cow-milk formula, but mostof the studies had small sample sizes (Jung and Carr,1977; Steichen and Tsang, 1987; Venkataraman et al.,1992; Mimouni et al., 1993; Lasekan et al., 1999). Agostoniet al. (2007) reported better short-term weight gain ininfants with immunoglobulin E-mediated cow’s milkallergy who were fed a rice or casein hydrolysate formulacompared with soy formula. Some studies reported thatinfants given soy formula had transiently lower bone-mineral content than infants fed cow-milk formula(Kohler et al., 1984) or human milk (Chan et al., 1987);however, other studies reported that serum concentra-tions of bone accretion-related hormones and minerals insoy formula-fed infants demonstrated the appropriatecompensatory response to the vitamin and mineralcontent of the food source (Hillman, 1988; Hillmanet al., 1988; Mimouni et al., 1993). Reports in very lowbirth-weight and preterm babies suggest that soyformula may not support adequate growth and bonedevelopment in these groups (Kulkarni et al., 1984). Soyinfant formula is not marketed for use in preterm infants,and the AAP recommends against its use in this group.

Studies comparing soy- and cow milk-formula feedingin infants with familial predispositions to allergic diseasedid not detect an advantage of one formula over another(Gruskay, 1982; Hillman et al., 1988; Klemola et al., 2002),but most of these studies have demonstrated that breastfeeding was superior to the use of either formula.A series of studies by Chandra (1989, x864; 1989, x765;1991, x865; 1997, x549; 1998, x550) related to allergicdisease were considered by the Expert Panel butclassified as no utility for the evaluation because thevalidity of the articles has been challenged and thescientific integrity cannot be confirmed.

Case reports suggest that hypothyroid infants on oralthyroxine therapy fed soy formula may exhibit lessefficient absorption of the thyroxine from the intestine.This effect has been attributed to fecal wastage withdecreased enterohepatic circulation (Shepard, 1960;Chorazy et al., 1995; Jabbar et al., 1997). Although theaddition of iodine and reduction in fiber content of soyformulas is a partial solution, one article noted that the

problem may occur if formula intolerance increases stoolfrequency (Chorazy et al., 1995). Conrad et al. (2004)reported that infants with CH-fed soy formula had aprolonged elevation of TSH levels compared with infantswith CH-fed nonsoy formula, suggesting that infantswith CH-fed soy formula may require higher levothyr-oxine doses to achieve normal thyroid function tests.

A case–control study of premature thelarche used 130subjects from 552 potentially eligible girls (Freni-Titulaeret al., 1986). Age-matched controls were recruited,consisting in some but not all instances of friends ofthe cases. Parents were interviewed with regard to familyhistory and possible exposures, including the use of soyformula. Multivariate analysis did not show a significantrelationship between premature thelarche and soy-formula feeding. When the analysis was restricted togirls with onset of premature thelarche before 2 years ofage, a significant association with soy-formula feedingwas identified (OR 2.7, 95% CI 1.1–6.8). Other significantfactors included maternal ovarian cysts and consumptionof chicken. Consumption of corn was protective.

Strom et al. (2001) identified 952 adults who hadparticipated as infants in a controlled, nonrandomizedformula trial. There were 248 adults who had been givensoy formula and 563 who had been given cow-milkformula. The subjects were asked about height, weight,sexual maturation, education level, and reproductiveoutcomes. No formula-related differences in height,weight, body-mass index, or sexual maturation wereidentified. Women who had been given soy formula hadlonger menstrual periods (mean 0.37 days longer, 95% CI0.06–0.68 days) and there was a soy formula-associatedincrease in the risk of experiencing severe menstrualdiscomfort (RR 1.7, 95% CI 1.04–3.00 compared with noor mild discomfort, unadjusted). After adjustment formultiple comparisons, these findings were no longerstatistically significant (more than 30 different endpointswere evaluated).

In a study comparing women with and without breastcancer by Boucher et al. (2008), the point estimates of theodds ratios were less than unity. However the variabilityof these estimates indicate that feeding soy formula wasnot statistically significantly associated with developingbreast cancer (soy formula only during first 4 months oflife: OR 5 0.42, 95% CI 5 0.13–1.40; soy formula onlyduring 5–12 months of age: OR 5 0.59, 95% CI 5 0.18–1.90).

Experimental Animal Studies on the IndividualIsoflavones Found in Soy Formula

Studies reporting the most sensitive and apparentlytreatment-related developmental effects are summarizedin Table 7 for oral and parenteral exposures in mice,Table 8 for oral and parenteral exposures in rats, andTable 9 for animal studies in other mammalian species. Inthese tables, dose levels have been converted to mg/kgbw. In general, the most complete information wasavailable from parenteral exposure studies in mice andoral exposure studies in rats. In cases where doses wereconverted to mg/kg bw/day values, ranges were oftenestimated over periods of gestation or lactation or indifferent stages of the offspring’s life.

Pre- and postnatal survival, growth, and gen-eral development endpoints. Oral exposure studiesconducted in rats suggested that genistein exposures can

432 MCCARVER ET AL.

Birth Defects Research (Part B) 92:421–468, 2011

Page 13: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

Table 6Studies of Human Infants Exposed to Soy Formula

Comparison groups Major findings Reference Utilitya

Growth and NutritionInfants with immunoglobulin E-mediated cow’s milk

allergy fed breastmilk (n 5 32) (reference) andinfants randomly assigned to one of three specialformulas during a feeding period of 6 to 12 monthsof age: soy formula (n 5 32), a casein hydrolysate(n 5 31), and a rice hydrolysate (n 5 30)

The 6- to 12-month change in weight-for-age z-scorefor the soy formula group was significantly lowercompared to the rice (0.18, p 5 0.019) and casein(0.16, p 5 0.029) groups. This indicates better short-term weight gain with hydrolyzed products whencompared with soy formula

Agostoni et al.(2007)

Limited

Infants randomized to one of two different soyformulas (n 5 10/group) and 10 breast-fedinfants (for comparisons to 4 months of age)

k bone mineral density and plasma zinc higher in soyformula-fed infants at 4 months of age; unable todetect difference between soy formula-fed infantsand historical controls in these parameters at 6 and12 months

Chan et al.(1987)

Limited

No effect: on measures of growth and serumchemistries

Infants fed soy infant formula (n 5 28) and infantsfed cow-milk formula (n 5 30) for 6 months. Thesoy formula was not methionine-supplementedas is modern soy formula

Soy-fed infants, especially girls, lagged in volumeconsumed and growth from 2 to 4 months of age;k weight gain per fluid ounce of formula;k vomiting; k number of infants hungry afterfeeding; m loose stools

Cherry et al.(1968)

Limited

No effect: on anemia or hematologic parametersInfants on soy formula (n 5 11), cow-milk formula

(n 5 11), or human milk (n 5 9), followed for 1year

Unable to detect a difference in bone width or bonemineral content; differences in serum and urineminerals and bone-related hormones wereconsistent with homeostatic adjustments todifferent mineral content in the food sources

Hillman et al.(1988, 1988)

Limited

Infants on soy formula (n 5 20) and infants on cow-milk formula (n 5 20) for 16 weeks

Unable to detect a difference between the 2 groups ingrowth parameters, hematology measures, or bloodchemistry

Jung and Carr(1977)

Limited

Infants on soy formula (n 5 13), infants on cow-milk formula (n 5 20), and breast-fed infants(n 5 26). Infants selected at 6 weeks of age andfollowed for 1 year

Weight at birth; unable to detect growth differencesbetween groups after 6 weeks of age; soy-fedinfants showed slower bone mineralization at 3months but not thereafter

Kohler et al.(1984)

Limited

Very low birth-weight infants given soy formula,cow-milk formula, or high-calorie cow-milkformula until 3–4 months of age

k serum phosphorus and serum alkaline phosphataseafter three weeks of age

Kulkarni et al.(1984)

Limited

Infants on soy formula with (n 5 73) or without(n 5 73) supplemental nucleotides, and infantsbreast-fed for 2 months and then given cow-milk formula (n 5 67); infants followed to 12months of age

Groups were not comparable in weight and lengthat birth. No group differences in growth weredetected after 6 months of age

Lasekan et al.(1999)

Limited

Infants given 1 of 2 different soy formulas (n 5 21/group), infants given cow-milk formula (n 5 20),and breast-fed infants (n 5 10), followed for 1year; solid food introduced at 3 months inbreast-fed and 4 months in formula-fed groups

m length gain; m serum 1,25-dihydroxyvitamin D in 1of the soy-formula groups at 8 weeks andthereafter; m serum phosphorus in combinedformula groups at 8 weeks. Unable to detect effectof feeding type on weight and head circumference;bone mineral content and bone width; bloodchemistry

Mimouni et al.(1993)

Limited

Infants being breastfed (n 5 401) and infantsassigned to either cow-milk (n 5 839) or soybased formula (n 5 239) based on family historyof allergy. Evaluated monthly until 6 months ofage and bi-monthly thereafter

No differences in length or weight were detectedbetween the 3 feeding groups.

Sellars et al.(1971)

Limited

Infants fed soy formula (n 5 18) or cow-milkformula (n 5 17) for 12 months

k bone mineral content; Unable to detect differencesin energy intake or growth

Steichen andTsang (1987)

Limited

Infants exclusively fed soy formula (n 5 20), cow-milk formula (n 5 19), or breast-fed (n 5 17) for 4months and followed until 6 months of age

m bone mineral content and bone width in soyformula-fed infants compared to breast-fed infants;Unable to detect group differences in growth andserum measurements related to bone accretion

Venkataramanet al. (1992)

Limited

Allergy, immunology, and gastrointestinal effectsInfants with a family history of major allergy

assigned to soy formula (n 5 79) or cow-milkformula (n 5 201), followed 17 years; 48 infantswith a family history of major allergy werebreast fed

Breast-fed children were significantly less likely todevelop allergy after 3 years than soy or cow-milkformula-fed children

Gruskay (1982) Limited

No significant difference in development of allergicdisease by formula type

433NTP-CERHR EXPERT PANEL REPORT

Birth Defects Research (Part B) 92:421–468, 2011

Page 14: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

Table 6Continued

Comparison groups Major findings Reference Utilitya

Infants with cow milk allergy diagnosed at age 2–11 months were randomly assigned toextensively hydrolyzed formula (n 5 90) or soyformula (n 5 80) and followed until 2 years ofage

Parents suspected adverse reaction in 28% of subjectson soy formula and 11% of subjects on extensivelyhydrolyzed formula. Among children younger than6 months, 40% were suspected by parents of havingadverse reaction to soy formula

Klemola et al.(2002)

Limited

Infants with milk allergy fed whey formula(n 5 76) or soy formula (n 5 72), examined atage 2, 3, and 4 years

Non-significant increase in soy IgE levels in soyformula-fed infants (OR 2.28, 95% CI 0.90–5.76;p 5 0.082)

Klemola et al.(2005)

Limited

No effect: prevalence of peanut IgE positivity (OR1.27, 95% CI 0.35–4.71; p 5 0.717)

Children with peanut allergy (n 5 49), childrenwith atopy (n 5 70), and non-allergic children(n 5 140) surveyed for infant feeding history

Soy consumption was a significant and independentrisk factor for peanut allergy (adjusted OR 2.61;95% CI 1.31–5.20)

Lack et al. (2003) Limited

Infants given 1 of 2 different soy formulas (n 5 92,94), one of which contained added nucleotides,and breast-fed children who were weaned tocow-milk formula at 2 months (n 5 81); 1-yearfollow-up

Unable to detect a difference by feeding group in antibodyresponse to immunizations (except Hemophilus influenzab), parent-reported diarrhea, or otitis media. Noconsistent differences were detected in immune status,maturation, or level of immunocompetence betweensoy and cow-milk formula-fed infants

Ostrom et al.(2002), Cordleet al. (2002)

Limited

Infants with cow’s milk allergy fed soy formula(n 5 84, mean starting age 5 7.8 mths) or aextensively hydrolyzed whey formula (HWF)(n 5 84, mean starting age 5 7.5 mths),examined until 48 mths of age

m percentage of energy; mintake of zinc and vitamin E;k riboflavin

Seppo et al.(2005)

Limited

No effect: percentages of abnormally low lab values;percentages of high alkaline phosphatase; growthmeasured between 1 to 4 years; nutritional status

Thyroid functionInfant with congenital hypothyroidism who was

fed soy formula (n 5 1)Oral thyroxine therapy did not decrease thyroid-

stimulating hormone until cow-milk formula wassubstituted for soy formula

Chorazy et al.(1995)

Limited

Infants fed soy formula (n 5 8) and infants fednonsoy formula (n 5 70)

Infants with congenital hypothyroidism fed soyformula had prolonged increase of TSH levelscompared to infants with congenitalhypothyroidism fed non-soy formula

Conrad et al.(2004)

Limited

No effect: on total T4 between groups; weight; height;weight for height

Infants with congenital hypothyroidism who werefed soy formula (n 5 3)

Switching from soy formula to cow-milk formularesulted in increased absorption of thyroidreplacement doses

Jabbar et al.(1997)

Limited

Children with goiter related to soy formula-feeding (n 5 3)

Improvement with discontinuation of soy formula(n 5 2) or addition of iodine (n 5 1)

Shepard (1960) Limited

Reproductive function or tissue effectsAdults with breast cancer (n 5 372) and without

breast cancer (n 5 356) who had been fed soyformula, cow-milk formula, or breastmilk

A reduced, but non-significant, association was foundbetween soy formula intake and breast cancer. Soyformula only during fist 4 months of life: OR 5 0.42,95% 5 0.13–1.40. Soy formula only during 5–12months of age: OR 5 0.59, 95% CI 5 0.18–1.90

Boucher et al.(2008)

Limited

Girls with premature thelarche (n 5 130) and age-matched control subjects, retrospectivequestioning of parents about infant feeding

Unable to detect a significant association overallbetween premature thelarche and soy infantformula intake; restriction of multivariate analysisto subjects with thelarche before age 2 yearsshowed significant association (OR 2.7; 95% CI 1.1–6.8, p 5 0.029)

Freni-Titulaeret al. (1986)

Limited

Adults who had been fed soy (n 5 248) or cow-milk formula (n 5 563) during infancy as part ofa controlled trial; interviewed at 20–34 years ofage

Unable to detect infant feeding-related differences inadult height, weight, body-mass index, or sexualmaturation history; duration of menstrual bleedingwas 0.37 days longer and severe menstrualdiscomfort was more common in women fed withsoy formula than with cow-milk formula

Strom et al.(2001)

Limited

Other endpointsInfants on soy formula (n 5 16, some with

cholesterol added), cow-milk formula (n 5 10),or breast-fed with supplemental cow-milkformula (n 5 12)

Breast-fed infants had the highest serum cholesterollevels and lowest fractional cholesterol synthesisrate. There was a significant inverse relationshipbetween cholesterol intake and fractionalcholesterol synthesis

Cruz et al. (1994) Limited

aThe term utility refers to the applicability to the purpose of drawing conclusions on whether or not a chemical adversely affects reproduction.

434 MCCARVER ET AL.

Birth Defects Research (Part B) 92:421–468, 2011

Page 15: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

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on

GD

12th

rou

gh

PN

D20

kfr

agm

ente

deg

gs

on

PN

D10

5–

0.1b

Fie

lden

etal

.(2

003)

Lim

ited

(ora

l)k

per

cen

to

fo

ne-

cell

fert

iliz

edeg

gs

on

PN

D31

50.

10.

5k

ano

gen

ital

dis

tan

cein

mal

eso

nP

ND

21;m

per

cen

to

fin

vit

rofe

rtil

izat

ion

by

sper

mo

nP

ND

105

and

315;

mfr

agm

ente

deg

gs

on

PN

D31

5

2.5

10

No

effe

cto

nn

um

ber

of

dam

sg

ivin

gb

irth

toli

ve

pu

ps,

pu

psu

rviv

alto

PN

D4

or

21,

litt

ersi

ze,

pu

po

rli

tter

wei

gh

t,an

dse

xra

tio

of

pu

ps,

sper

mco

un

to

rm

oti

lity

,se

min

alv

esic

le,

test

is,

adu

ltb

od

yw

eig

ht,

or

test

icu

lar

gen

eex

pre

ssio

no

fes

tro

gen

and

and

rog

enre

cep

tors

.

10(h

igh

do

se;n

oef

fect

)–

CD

-1m

ice;

0.17

mg

/k

gb

w/

day

gen

iste

inb

yo

ral

gav

age

GD

13th

rou

gh

GD

17m

freq

uen

cyo

fh

yp

osp

adia

sin

mal

es(2

5%)

–0.

17(s

ing

led

ose

stu

dy

)V

ilel

aet

al.

(200

7)L

imit

ed(o

ral)

CD

-1m

ice;

0,0.

5,5,

or

50m

g/

kg

bw

/d

ayg

enis

tein

by

scin

ject

ion

on

PN

D1–

5D

istr

ibu

tio

no

ffe

mal

esin

var

iou

sst

ages

of

estr

ou

scy

cle

at2

mo

nth

so

fag

e–

0.5

Jeff

erso

net

al.

(200

5)H

igh (par

ente

ral)

kn

um

ber

of

dam

sw

ith

litt

ers

at2

and

6m

on

ths

of

age

(au

tho

r’s

rep

ort

that

‘‘a

tren

dte

stsh

ow

eda

stat

isti

call

ysi

gn

ific

ant

dec

reas

ein

the

nu

mb

ero

fm

ice

wit

hli

tter

sat

2an

d6

mo

nth

so

fag

ew

ith

incr

easi

ng

do

seas

det

erm

ined

by

the

Co

chra

n-A

rmit

age

test

[po

0.05

].’’

)

–Z

0.5

(sig

nif

ican

tn

egat

ive

tren

d)

kn

um

ber

of

liv

ep

up

sb

orn

tod

ams

of

2,4

and

6m

on

ths

of

age

(wh

enal

lag

eslo

ok

edat

sim

ult

aneo

usl

y)

0.5

5

kco

rpo

ralu

tea

per

dam

at4

mo

nth

so

fag

e5

50n

oef

fect

on

nu

mb

ero

fp

lug

po

siti

ve

mic

e,n

um

ber

of

ov

ula

ted

oo

cyte

sfo

llo

win

gtr

eatm

ent

of

mic

ew

ith

hu

man

cho

rio

nic

go

nad

otr

op

inat

4m

on

ths

of

age,

ov

eral

ltr

eatm

ent

effe

cts

on

seru

mp

rog

este

ron

e,17b-

estr

adio

l,o

rte

sto

ster

on

ele

vel

s

50(h

igh

do

se;

no

effe

ct)

435NTP-CERHR EXPERT PANEL REPORT

Birth Defects Research (Part B) 92:421–468, 2011

Page 16: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

Tab

le7

Co

nti

nu

ed

An

imal

mo

del

and

stu

dy

des

ign

En

dp

oin

tsN

OE

LL

OE

LR

efer

ence

Uti

lity

a

CD

-1m

ice;

0o

r50

mg

/k

gb

w/

day

gen

iste

inb

ysc

inje

ctio

no

nP

ND

1to

5k

imp

lan

tati

on

site

s(b

oth

nu

mb

ero

fm

ice

and

nu

mb

ero

fsi

tes/

mo

use

);k

per

cen

tp

reg

nan

tm

ice;

kn

um

ber

of

corp

ora

lute

a

–50

(sin

gle

do

sest

ud

y)

Jeff

erso

net

al.

(200

5)L

imit

ed(p

aren

tera

l)

CD

-1m

ice;

0o

r50

mg

/k

gb

w/

day

gen

iste

inb

ysc

inje

ctio

no

nP

ND

1to

5k

nu

mb

ero

fem

bry

os

coll

ecte

dp

erm

ou

sefo

llo

win

gh

CG

adm

inis

trat

ion

;kn

um

ber

and

size

of

imp

lan

tati

on

site

sin

mic

ew

ho

wer

ere

cip

ien

tso

ftr

ansf

erre

db

last

ocy

sts

ob

tain

edfr

om

un

trea

ted

mic

e

–50

(sin

gle

do

sest

ud

y)

Jeff

erso

net

al.

(200

9b)

Lim

ited

(par

ente

ral)

No

effe

cto

nth

en

um

ber

of

ov

ula

ted

egg

s,ti

min

go

fd

evel

op

men

to

rp

erce

nta

ge

of

emb

ryo

sto

reac

hb

last

ocy

stag

e,th

en

um

ber

of

liv

ep

up

s,o

rli

tter

size

50(h

igh

do

se;n

oef

fect

)–

CD

-1;

0,12

.6,

20,

or

25m

g/

kg

bw

/d

ayg

enis

tein

scin

ject

ion

fro

mP

ND

1to

5m

ute

rin

ew

eig

ht

lim

ited

(par

ente

ral)

12.6

20Je

ffer

son

etal

.(2

009a

)sc

po

rtio

n

Lim

ited

(par

ente

ral)

CD

-1m

ice;

0o

r50

mg

/k

gb

w/

day

gen

iste

inb

ysc

inje

ctio

no

nP

ND

1to

5m

nu

mb

ero

fre

pro

du

ctiv

ele

sio

ns:

no

corp

ora

lute

a,ab

no

rmal

ov

idu

cth

isto

log

y,u

teri

ne

squ

amo

us

met

apla

sia,

cyst

icen

do

met

rial

hy

per

pla

sia

and

ute

rin

eca

rcin

om

a

–50

(sin

gle

do

sest

ud

y)

New

bo

ldet

al.

(200

1)L

imit

ed(p

aren

tera

l)

CD

-1m

ice;

0,0.

5,o

r10

mg

/k

gb

w/

day

gen

iste

inb

ysc

inje

ctio

no

nG

D15

to18

mb

od

yw

eig

ht

gai

n;

0.5–

1d

ayea

rlie

ro

nse

to

fv

agin

alo

pen

ing

;m

estr

ou

scy

cle

len

gth

,1.

2–2

day

s;m

len

gth

of

die

stru

s

–0.

5N

ikai

do

etal

.(2

004)

kn

um

ber

of

anim

als

wit

hco

rpo

ralu

tea

at4

wee

ks

of

age,

tran

sien

tef

fect

0.5

10

ICR

mic

e;0

or

1000

mg

/k

gb

w/

day

gen

iste

inb

yin

ject

ion

on

PN

D1

to5

kte

stic

ula

rm

RN

Aex

pre

ssio

no

fE

Ra,

ERb,

AR

and

lam

inin

-g2

–10

00(s

ing

led

ose

stu

dy

)A

dac

hi

etal

.(2

004)

Lim

ited

(par

ente

ral)

No

effe

cto

nb

od

yw

eig

ht,

abso

lute

or

rela

tiv

ete

stis

wei

gh

to

rh

isto

log

ical

chan

ges

inth

ete

stes

at12

wee

ks

of

age

1000

(hig

hd

ose

;n

oef

fect

)–

CD

-1p

reg

nan

tm

ice;

0,0.

2o

r2

mg

/k

gb

w/

day

of

gen

iste

inb

yip

inje

ctio

nfr

om

GD

1to

21N

oef

fect

on

gro

sso

rh

isto

log

ical

ano

mal

ies

of

the

ute

rus,

or

Hox

a10

mR

NA

exp

ress

ion

inth

eu

teru

s2

(hig

hd

ose

;n

oef

fect

)–

Ak

bas

etal

.(2

007)

Lim

ited

(par

ente

ral)

CD

-1p

reg

nan

tm

ice;

0o

r2

mg

/k

gb

w/

day

of

dai

dze

inb

yip

inje

ctio

nfr

om

GD

1to

21N

oef

fect

on

gro

sso

rh

isto

log

ical

ano

mal

ies

of

the

ute

rus,

or

Hox

a10

mR

NA

exp

ress

ion

inth

eu

teru

s2

(hig

hd

ose

;n

oef

fect

)–

CD

-1m

ice;

0,1,

10,

or

100mg

/d

ay(0

,0.

5,5,

or

50m

g/

kg

bw

/d

ay)

gen

iste

inb

ysc

inje

ctio

no

nP

ND

1to

5

mm

ult

i-o

ocy

tefo

llic

les

550

Jeff

erso

net

al.

(200

2)L

imit

ed(p

aren

tera

l)

C57

BL

/6,

ERa

and

ERb

mic

e;0,

1,10

,o

r10

0mg

/d

ay(0

,0.

5,5,

or

50m

g/

kg

bw

/d

ay)

gen

iste

inb

ysc

inje

ctio

no

nP

ND

1–5

mm

ult

i-o

ocy

tefo

llic

les

inE

Ra

and

no

effe

ctin

ERb

0.5

5

CD

-1m

ice;

50m

g/

kg

bw

/d

ayg

enis

tein

by

scin

ject

ion

fro

mP

ND

1to

5m

nu

mb

ero

fm

ult

i-o

ocy

tefo

llic

les;

few

ersi

ng

leo

ocy

tes

–50

(sin

gle

do

sest

ud

y)

Jeff

erso

net

al.

(200

6)L

imit

ed(p

aren

tera

l)C

D-1

mic

e;0

or

10m

g/

kg

bw

/d

ayg

enis

tein

by

scin

ject

ion

on

PN

D15

to18

acce

lera

tio

no

fv

agin

alo

pen

ing

–10

(sin

gle

do

sest

ud

y)

Nik

aid

oet

al.

([20

05)

Lim

ited

(par

ente

ral)

No

effe

ct:

on

bo

dy

wei

gh

t,es

tro

us

cycl

ing

,p

oly

ov

ula

ro

var

ian

foll

icle

s,m

orp

ho

log

ical

abn

orm

alit

ies

inv

agin

alo

ru

teri

ne

epit

hel

ium

,o

rm

amm

ary

gla

nd

dev

elo

pm

ent

10(h

igh

do

se;n

oef

fect

)–

ICR

mic

e;0,

7,71

,an

d71

4m

g/

kg

bw

/d

ayg

enis

tein

by

scin

ject

ion

on

PN

D1

to5

kA

Rm

RN

Aex

pre

ssio

nin

test

is7

71S

hib

ayam

aet

al.

(200

1)L

imit

ed(p

aren

tera

l)k

ERa

mR

NA

exp

ress

ion

inte

stis

7171

4 –

436 MCCARVER ET AL.

Birth Defects Research (Part B) 92:421–468, 2011

Page 17: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

No

effe

cto

nte

stis

wei

gh

t,sp

erm

cou

nt,

or

sper

mm

oti

lity

at12

wee

ks

of

age

714

(hig

hd

ose

;n

oef

fect

)M

ale

Han

-NM

RI

mic

e;0,

0.1

or

1m

g/

day

(50

or

500

mg

/k

gb

w/

day

)g

enis

tein

by

scin

ject

ion

on

PN

D1

to3

kv

entr

alp

rost

ate

wei

gh

tin

adu

lth

oo

d(h

isto

log

ical

chan

ges

ob

serv

ed)

–50

Str

auss

etal

.(1

998)

Lim

ited

(par

ente

ral)

kco

agu

lati

ng

gla

nd

wei

gh

t;m

his

tolo

gic

abn

orm

alit

ies

(hy

per

pla

sia

and

dis

org

aniz

atio

no

fth

eep

ith

eliu

mo

fth

ep

rost

atic

coll

ecti

ng

du

cts,

ven

tral

lob

es,

and

sem

inal

ves

icle

s);m

fib

rom

usc

ula

rst

rom

aan

din

flam

mat

ory

cell

sin

po

ster

ior

per

iure

thra

lre

gio

n

5050

0

No

effe

cto

nc-

fos

mR

NA

exp

ress

ion

inp

rost

atic

ure

thra

500

(hig

hd

ose

;n

oef

fect

)–

Mam

mar

ygl

and

deve

lopm

ent

and

carc

inog

enes

isC

D-1

mic

e;0

orB

0.7–

0.8

mg

/k

gb

w/

day

gen

iste

inb

yin

ject

ion

on

GD

15to

20m

mam

mar

yg

lan

dep

ith

elia

lar

eao

nP

ND

35(b

ut

no

to

nP

ND

25o

rP

ND

46);m

den

sity

of

TE

Bs

on

PN

D35

and

45;

mP

ND

25b

od

yw

eig

ht;

del

ayed

eye

op

enin

g;

acce

lera

ted

tim

ing

of

vag

inal

op

enin

g

–B

0.7–

0.8

(sin

gle

do

sele

vel

)H

ilak

ivi-

Cla

rke

etal

.(1

998)

Lim

ited

(par

ente

ral)

No

effe

cto

nn

um

ber

of

off

spri

ng

bo

rn,

PN

D1

bo

dy

wei

gh

t,d

iffe

ren

tiat

ion

of

bre

ast

tiss

ue

(ass

esse

du

sin

gd

ensi

tyo

fT

EB

san

dlo

bu

loal

veo

lar

un

its)

,se

rum

17b-

estr

adio

lo

res

tro

us

cycl

icit

y

B0.

7–0.

8(h

igh

do

se;

no

effe

ct)

CD

-1m

ice;

0,0.

5,5,

or

50m

g/

kg

bw

/d

ayg

enis

tein

by

scin

ject

ion

on

PN

D1

to5

Mam

mar

yg

lan

dh

orm

on

ere

cep

tor

lev

els:m

PR

pro

tein

exp

ress

ion

at5

wee

ks,

kE

Ra

mR

NA

at5

and

6w

eek

s(c

om

bin

ed)

–0.

5P

adil

la-B

ank

set

al.

(200

6)L

imit

ed(p

aren

tera

l)

md

uct

alel

on

gat

ion

at6

wee

ks;

mE

Rb

mR

NA

inm

amm

ary

gla

nd

at5

and

6w

eek

s(c

om

bin

ed)b

–0.

5b

kn

um

ber

of

TE

Bs

at6

wee

ks;k

nu

mb

ero

fb

ran

chp

oin

tsat

5w

eek

s(b

ut

no

tat

6w

eek

s);

mam

mar

yg

lan

dm

orp

ho

log

yat

9m

on

ths:

kal

veo

lar

dev

elo

pm

ent,

dil

ated

and

/o

rd

ilat

edb

ead

edd

uct

s

0.5

5

kn

um

ber

of

TE

Bs

at5

wee

ks;

km

amm

ary

gla

nd

du

ctal

gro

wth

at5

or

6w

eek

s;k

aver

age

area

of

mam

mar

yg

lan

dat

5o

r6

wee

ks;

alte

red

estr

ou

scy

clic

ity

550

kn

um

ber

of

pu

ps

per

litt

er,

litt

erw

eig

hts

,p

up

wei

gh

ts,

%p

up

ssu

rviv

ing

un

til

wea

nin

g5

50(n

oli

ve

pu

ps

del

iver

ed)

No

effe

cto

nci

rcu

lati

ng

lev

els

of

estr

adio

lo

rp

rog

este

ron

e,li

tter

size

,li

tter

wei

gh

ts,

calc

ula

ted

aver

age

pu

pw

eig

hts

,o

r%

of

pu

ps

surv

ivin

gu

nti

lw

ean

ing

50(h

igh

do

se;n

oef

fect

)–

Sp

rag

ue-

Daw

ley

;50

mg/

day

(au

tho

rses

tim

ated

that

the

do

ses

rece

ived

wer

e1.

25to

3.3

mg

/k

gb

wg

enis

tein

by

scin

ject

ion

on

PN

D8

to20

km

amm

ary

epit

hel

ial

den

sity

;kte

rmin

alen

db

ud

nu

mb

ers;

min

crea

sed

lob

ulo

alv

eola

rst

ruct

ure

s;at

8w

eek

so

fag

e;m

BR

CA

1ex

pre

ssio

n;m

ERa

exp

ress

ion

inlo

bu

les

at3

and

8w

eek

s

–50

(sin

gle

do

sest

ud

y)

Cab

anes

etal

.(2

004)

Lim

ited

(par

ente

ral)

Oth

er/m

echa

nis

tic

Av

ym

ice;

250

mg

/k

gg

enis

tein

ind

iet

bef

ore

mat

ing

thro

ug

hp

reg

nan

cyan

dla

ctat

ion

;as

sess

men

to

fh

eter

ozy

go

us

via

ble

yel

low

ago

uti

(Av

y/a

)o

ffsp

rin

g

Sh

ift

inco

atco

lor

ph

eno

typ

eto

war

ds

the

pse

ud

o-a

go

uti

ph

eno

typ

ean

dre

du

ced

bo

dy

wei

gh

tin

pse

ud

o-a

go

uti

ph

eno

typ

e;h

yp

erm

eth

yla

tio

n

–25

0(s

ing

led

ose

stu

dy

)D

oli

no

yet

al.

(200

6)L

imit

ed(o

ral)

No

effe

cto

nli

tter

size

,m

ean

pu

pw

eig

ht,

per

cen

tsu

rviv

alo

rse

xra

tio

250

(hig

hd

ose

;n

oef

fect

)–

437NTP-CERHR EXPERT PANEL REPORT

Birth Defects Research (Part B) 92:421–468, 2011

Page 18: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

Tab

le7

Co

nti

nu

ed

An

imal

mo

del

and

stu

dy

des

ign

En

dp

oin

tsN

OE

LL

OE

LR

efer

ence

Uti

lity

a

Av

yfe

mal

em

ice;

wer

eas

sig

ned

too

ne

of

fou

rm

od

ifie

dd

iets

for

two

wee

ks

pri

or

tom

atin

gw

ith

Av

y/a

mal

esan

dth

rou

gh

ou

tp

reg

nan

cyan

dla

ctat

ion

:(1

)m

od

ifie

dA

IN-9

3d

iet

(co

rno

ilsu

bst

itu

ted

for

soy

bea

no

il);

(2)

mo

dif

ied

AIN

-93

die

tsu

pp

lem

ente

dw

ith

50m

gB

PA

/k

gd

iet;

(3)

mo

dif

ied

AIN

-93

die

tsu

pp

lem

ente

dw

ith

50m

gB

PA

and

250

mg

gen

iste

in/

kg

die

t;an

d(4

)m

od

ifie

dA

IN-9

3d

iet

sup

ple

men

ted

wit

h50

mg

BP

A/

kg

die

tan

dm

eth

yl

do

no

rco

mp

ou

nd

s(4

.3m

gfo

lic

acid

,0.

53m

gv

itam

inB

12,

5g

bet

ain

e,an

d7.

97g

cho

lin

ech

lori

de/

kg

die

t)

Mat

ern

ald

ieta

ryB

PA

sig

nif

ican

tly

shif

ted

the

coat

colo

rd

istr

ibu

tio

no

fg

enet

ical

lyid

enti

cal

d22

Av

y/a

off

spri

ng

tow

ard

the

yel

low

coat

colo

rp

hen

oty

pe;

mat

ern

alsu

pp

lem

enta

tio

nw

ith

met

hy

ld

on

ors

or

gen

iste

inre

sto

red

the

coat

colo

rd

istr

ibu

tio

nin

the

BP

A-e

xp

ose

do

ffsp

rin

gto

that

ob

serv

edin

the

con

tro

ls

–25

0(s

ing

led

ose

stu

dy

)D

oli

no

yet

al.

(200

7)L

imit

ed(o

ral)

No

effe

cts:

litt

ersi

ze,

surv

ival

,w

ean

wei

gh

t,g

eno

typ

icra

tio

or

sex

rati

o25

0(h

igh

do

se;

no

effe

ct)

C57

Bl/

6m

ice;

0,25

,25

0,o

r12

50p

pm

gen

iste

inin

die

tfr

om

GD

14to

lact

atio

nv

iad

am(m

g/

kg

fee

d;

est

ima

ted

by

the

stu

dy

au

tho

rsto

pro

vid

eg

en

iste

in0

,2

,2

0,

or

10

0m

g/k

gb

w/

da

yto

a2

5-g

mm

ou

se)

Alt

ered

imm

un

ece

llen

dp

oin

ts,

e.g

.,v

ario

us

typ

eso

fth

ym

ocy

tes

and

sple

no

cyte

s(m

any

did

no

td

isp

lay

aco

nsi

sten

tp

atte

rno

fre

spo

nse

);m

mal

ep

up

bo

dy

wei

gh

ts;

msp

leen

wei

gh

tin

mal

es

–2b

Gu

oet

al.

(200

6)L

imit

ed(o

ral)

mm

ater

nal

bo

dy

wei

gh

t;m

mat

ern

alsp

leen

wei

gh

t2

250

ER

E-t

K-L

UC

tran

sgen

icm

ale

mic

e;0

or

50m

g/

kg

gen

iste

into

dam

sb

yo

ral

gav

age

on

PN

D4

mlu

cife

rase

acti

vit

yin

liv

er,

lun

g,

hea

rt,

thy

mu

s,te

stis

,an

db

rain

of

pu

ps

–50

(sin

gle

do

sest

ud

y)

Mo

nta

ni

etal

.(2

008)

Lim

ited

(ora

l)

ER

E-t

K-L

UC

mic

e;0,

0.5,

5,an

d50

mg

/k

gg

enis

tein

on

PN

D4

by

ora

lg

avag

eto

lact

atin

gd

am

mlu

cife

rase

acti

vit

yin

the

test

eso

fm

ale

pu

ps

550

Mo

nta

ni

etal

.(2

009)

Lim

ited

(ora

l)

CD

-1m

ice;

0o

r50

mg

/k

gb

w/

day

gen

iste

inb

ysc

inje

ctio

no

nP

ND

1to

5H

yp

erm

eth

yla

tio

nin

Nsb

p1p

rom

ote

rC

Gis

lan

d(C

G1)

inan

age

dep

end

ent

man

ner

–50

(sin

gle

do

sest

ud

y)

Tan

get

al.

(200

8)L

imit

ed(p

aren

tera

l)

m,k

5S

ign

ific

ant

incr

ease

,d

ecre

ase.

aT

he

term

uti

lity

refe

rsto

the

app

lica

bil

ity

toth

ep

urp

ose

of

dra

win

gco

ncl

usi

on

so

nw

het

her

or

no

ta

chem

ical

adv

erse

lyaf

fect

sre

pro

du

ctio

n.

bD

idn

ot

dis

pla

ya

do

se–r

esp

on

se.

438 MCCARVER ET AL.

Birth Defects Research (Part B) 92:421–468, 2011

Page 19: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

Tab

le8

Ex

per

imen

tal

Stu

die

sw

ith

Dev

elo

pm

enta

lT

ox

icit

yE

nd

po

ints

inR

ats

Ex

po

sed

toG

enis

tein

,D

aid

zein

,o

rE

qu

ol

An

imal

mo

del

and

stu

dy

des

ign

En

dp

oin

tsN

OE

LL

OE

LR

efer

ence

Uti

lity�

Gro

wth

,re

prod

uct

ive

syst

eman

den

docr

ine-

rela

ted

endp

oin

tsS

pra

gu

e-D

awle

yra

t;0,

5,10

0,o

r50

0p

pm

gen

iste

inin

die

td

uri

ng

pre

gn

ancy

and

lact

atio

n;

on

eh

alf

of

mal

eo

ffsp

rin

gco

nti

nu

edo

nth

eg

enis

tein

die

tsat

wea

nin

g(G

/G

);se

con

dh

alf

of

mal

eo

ffsp

rin

gw

ere

giv

enco

ntr

ol

die

tsat

wea

nin

g(G

/C

);m

ult

igen

erat

ion

des

ign

.(I

nta

ke

sa

ssu

me

dto

be

sim

ila

rto

tho

sein

NC

TR

(NC

TR

,2

00

5)o

fw

hic

hth

isst

ud

yw

as

ap

art

:m

ale

s:0

,0

.3,

7,

35

mg

/kg

bw

/da

y;

fem

ale

s:0

,0

.4,

9,

44

mg

/kg

bw

/day

;fe

mal

es

du

rin

gla

cta

tio

n:

0.7

,1

5,

an

d7

8m

g/k

gb

w/d

ay)

kE

Rb

pro

tein

ind

ors

ola

tera

lp

rost

ate

of

F1

mal

esat

PN

D14

0(G

Cg

rou

po

nly

)–

5p

pm

Dal

uet

al.

(200

2)L

imit

ed(o

ral)

mse

rum

DH

Tle

vel

sin

F1

mal

esat

PN

D14

0(b

oth

G/

Gan

dG

/C

gro

up

s)5

pp

m10

0p

pm

mse

rum

test

ost

ero

ne

lev

els

inF

1m

ales

atP

ND

140

(bo

thG

/G

and

G/

Cg

rou

ps)

100

pp

m50

0p

pm

Sp

rag

ue-

Daw

ley

rat;

0,5,

25,

100,

250,

625,

and

1250

pp

mg

enis

tein

thro

ug

hd

iet

du

rin

gp

reg

nan

cyan

dla

ctat

ion

and

un

til

PN

D50

ino

ffsp

rin

g.

(Me

an

do

ses:

0.3

1,1

.7,

5.7

,1

5,

34

,8

3m

g/k

gb

w/d

ay

inp

reg

na

nt

da

ms;

0.5

6,

2.8

,11

,3

0,

73

,1

38

inla

ctat

ing

da

ms;

B0

.6,

3.0

,1

2,

30

,7

2,

an

d1

80

mg

/kg

bw

/day

inp

up

sa

fte

rw

ea

nin

g.)

Acc

eler

ated

vag

inal

op

enin

g;m

rela

tiv

ev

agin

alw

eig

ht

–S

ign

ific

ant

lin

ear

tren

dD

elcl

os

etal

.(2

001)

Lim

ited

(ora

l)H

yp

ertr

op

hy

of

mam

mar

yal

veo

lian

dd

uct

sin

mal

esat

PN

D50

c;

abn

orm

alit

ies

of

sper

mat

og

enes

is5

pp

m25

pp

m

His

top

ath

olo

gy

inv

agin

aat

PN

D50

250

pp

m62

5p

pm

Alv

eola

rp

roli

fera

tio

nin

mam

mar

yo

ffe

mal

esat

PN

D50

;m

ren

altu

bu

lem

iner

aliz

atio

nin

mal

esan

dfe

mal

es10

0p

pm

250

pp

m

kd

ams

del

iver

ing

litt

ers

andk

litt

erb

od

yw

eig

hts

atb

irth

;kre

lati

ve

ven

tral

pro

stat

ew

eig

ht

atP

ND

50;

pro

stat

ein

flam

mat

ion

;h

isto

pat

ho

log

yin

ov

arie

sat

PN

D50

;k

po

stn

atal

bo

dy

wei

gh

tsin

mal

esan

dfe

mal

es

625

pp

m12

50p

pm

Del

ayed

eye

op

enin

gan

dea

ru

nfo

ldin

g62

5p

pm

1250

pp

m(s

ign

ific

ant

lin

ear

tren

d)

No

effe

cto

nm

ater

nal

bo

dy

wei

gh

td

uri

ng

the

lact

atio

np

erio

d,

ges

tati

on

len

gth

,li

tter

size

,p

rop

ort

ion

of

liv

ep

up

s,se

xra

tio

of

pu

ps,

ano

gen

ital

dis

tan

ceo

nP

ND

2,p

rep

uti

alse

par

atio

n;

or

test

icu

lar

sper

mh

ead

or

epid

idy

mal

sper

mco

un

ts

(hig

hd

ose

;n

oef

fect

)–

Sp

rag

ue-

Daw

ley

rat;

0,5,

100,

500

pp

mg

enis

tein

ind

iet;

mu

ltig

ener

atio

nal

des

ign

(mal

es:

0,0.

3,7,

35m

g/

kg

bw

/d

ay;

fem

ales

,av

erag

een

tire

feed

ing

per

iod

:0,

0.5,

10,

51m

g/

kg

bw

/d

ay;

fem

ales

,n

on

lact

atin

g:

0,0.

4,9,

44;

and

fem

ales

,la

ctat

ing

:0,

0.7,

15,

and

78m

g/

kg

bw

/d

ay)

kp

up

wei

gh

tat

bir

th(F

5)

(no

dir

ect

gen

iste

intr

eatm

ent)

–5

pp

mN

CT

R(2

008)

Lim

ited

(ora

l)M

amm

ary

gla

nd

hy

per

pla

sia

inm

ales

(F1,

F2,

F3);k

mal

ep

up

wei

gh

td

uri

ng

lact

atio

np

erio

d(F

3)

5p

pm

100

pp

m

kli

tter

size

(F2);

dis

rup

ted

estr

ou

scy

cles

,i.

e.,m

len

gth

or

nu

mb

ero

fab

no

rmal

cycl

es(F

1);

incr

ease

dcy

cle

len

gth

(F1,

F2);k

bo

dy

wei

gh

tat

vag

inal

op

enin

g(F

1,

F2,

F3)

and

acce

lera

ted

vag

inal

op

enin

g(F

1,

F2);

del

ayed

test

icu

lar

dec

ent

(F3

);k

ano

gen

ital

dis

tan

cein

fem

ales

(F1,

F2);k

ano

gen

ital

dis

tan

cem

ales

(F1);k

fem

ale

pu

pw

eig

ht

du

rin

gla

ctat

ion

per

iod

(F1,

F3,

F4);k

mal

ep

up

wei

gh

td

uri

ng

lact

atio

np

erio

d(F

2,

F4);k

infe

edco

nsu

mp

tio

nin

adu

ltfe

mal

es(F

0,

F1,

and

F4)

100

pp

m50

0p

pm

439NTP-CERHR EXPERT PANEL REPORT

Birth Defects Research (Part B) 92:421–468, 2011

Page 20: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

Tab

le8

Co

nti

nu

ed

An

imal

mo

del

and

stu

dy

des

ign

En

dp

oin

tsN

OE

LL

OE

LR

efer

ence

Uti

lity�

kli

tter

size

(F1,

F3)

–S

ign

ific

ant

neg

ativ

eli

nea

rtr

end

kan

og

enit

ald

ista

nce

infe

mal

es(F

3)

–10

0a

km

ale

pu

pw

eig

ht

du

rin

gla

ctat

ion

per

iod

(F1)

?5

pp

mN

oef

fect

:o

nm

atin

g,

fert

ilit

y,o

rp

reg

nan

cyin

dic

esin

any

gen

erat

ion

;o

nd

ura

tio

n;

on

of

ges

tati

on

;o

nre

sorp

tio

ns

site

sin

anim

als

that

did

no

tb

eco

me

pre

gn

ant;

on

ov

aria

nfo

llic

leco

un

to

rsp

erm

par

amet

ers

500

pp

m(h

igh

do

se;

no

effe

ct)

CD

sS

DIG

Sra

t;0,

20,2

00,o

r10

00p

pm

gen

iste

inin

die

t(m

ean

:1

.7,

18

,a

nd

90

mg

/kg

bw

/day

)fr

om

GD

15to

PN

D10

kb

od

yw

eig

ht

inm

ales

at11

wee

ks

of

age

–1.

7M

asu

tom

iet

al.

(200

3)

Lim

ited

(ora

l)m

rela

tiv

eb

rain

wei

gh

t;m

rela

tiv

ep

itu

itar

yw

eig

ht

–1.

7a

mre

lati

ve

adre

nal

wei

gh

t1.

718

kab

solu

tep

itu

itar

yw

eig

ht;k

bo

dy

wei

gh

tg

ain

inm

ales

on

PN

D21

–42

1890

Wis

tar

(RO

RO

)ra

ts;

0,20

,15

0,o

r10

00m

g/

kg

bw

/d

ayg

enis

tein

fro

mG

D6–

20b

yg

avag

em

pu

pm

ort

alit

y–

20a

McC

lain

etal

.(2

007)

Lim

ited

(ora

l)V

isce

ral

mal

form

atio

ns

(art

ery

ori

gin

var

ian

t)15

010

00(o

nli

tter

inci

den

ceb

asis

)N

oef

fect

on

nu

mb

ero

fd

eliv

ered

pu

ps,

imp

lan

tati

on

or

reso

rpti

on

site

s,o

rex

tern

alm

alfo

rmat

ion

1000

(hig

hd

ose

;n

oef

fect

)–

Wis

tar

(RO

RO

)ra

ts;

0,5,

50,

100,

500

mg

/k

gb

w/

day

gen

iste

infr

om

GD

5–21

inth

ed

iet

mp

ost

-im

pla

nta

tio

nlo

ss,k

nu

mb

ero

ffe

tuse

sp

erfe

mal

e,k

feta

lb

od

yw

eig

ht

(per

litt

erb

asis

),in

cid

ence

skel

etal

oss

ific

atio

n

100

500

Ald

erle

yP

ark

rat;

0,0.

2,o

r2

mg

/k

gb

w/

day

gen

iste

inb

ysc

inje

ctio

nd

uri

ng

PN

D1–

6an

d4

and

40m

g/

kg

bw

/d

ayb

yg

avag

eo

nP

ND

7–21

(sc

do

ses

wer

ed

eter

min

edto

be

equ

ival

ent

tog

avag

ed

ose

so

f4

and

20m

g/

kg

bw

/d

ay);

on

ep

art

of

the

stu

dy

exam

inin

gS

DN

-PO

Ad

ose

dan

imal

sd

uri

ng

the

sam

ep

erio

dw

ith

scan

do

ral

do

ses

equ

ival

ent

to4

and

40m

g/

kg

bw

/d

ayb

yo

ral

exp

osu

re

Ad

van

ced

vag

inal

op

enin

g,

per

sist

ent

vag

inal

corn

ific

atio

n,

ute

rotr

op

hic

resp

on

se,k

seru

mp

rog

este

ron

ein

fem

ales

,kb

od

yw

eig

ht

infe

mal

es

440

ora

lP

ND

7–21

;20

PN

D1–

6(e

qu

ival

ent

toan

scin

ject

ion

do

seo

f2

mg

/k

gb

w/

day

)

Lew

iset

al.

(200

3)

Nag

aoet

al.

(200

1)

Hig

h(o

ral)

Hig

h(o

ral)

mS

DN

PO

Av

olu

me

infe

mal

es4

40

Sp

rag

ue-

Daw

ley

rat;

0,12

.5,

25,

50,

or

100

mg

/k

gb

w/

day

gen

iste

inb

yg

avag

eo

nP

ND

1–5.

kfe

rtil

ity

ind

ex(g

enis

tein

-tre

ated

fem

ales

mat

edw

ith

un

trea

ted

mal

es);

po

lyo

vu

lar

foll

icle

sin

wea

nli

ng

fem

ales

;k

epid

idy

mal

wei

gh

t;k

bo

dy

wei

gh

tso

fm

ales

at18

wee

ks

of

age;

(kb

od

yw

eig

hts

of

fem

ales

at9

wee

ks

of

age)

–12

.5

kn

orm

ales

tro

us

cycl

e(n

ot

do

sed

epen

den

t)–

12.5

a

kn

um

ber

of

imp

lan

tsp

erli

tter

5010

0k

bo

dy

wei

gh

tso

fb

oth

sex

esat

1,2,

3,5,

7,9

and

18(m

ales

on

ly)

wee

ks

of

age

(kb

od

yw

eig

hts

of

bo

thse

xes

at50

mg

/k

gb

w/

day

fro

m5,

7,9,

and

18(m

ales

on

ly)

wee

ks

of

age)

–10

0a

440 MCCARVER ET AL.

Birth Defects Research (Part B) 92:421–468, 2011

Page 21: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

Hy

per

tro

ph

yo

fu

teri

ne

my

om

etri

um

–50

(rep

ort

edin

anim

als

atlo

wer

do

sele

vel

s,b

ut

no

tst

atis

tica

lly

anal

yze

d)

mat

reti

cfo

llic

les,k

corp

us

lute

um

18w

eek

s,h

yp

ertr

op

hy

of

lum

inal

and

gla

nd

ula

rep

ith

elia

lce

lls,

andk

inn

um

ber

of

ute

rin

eg

lan

ds

–10

0(r

epo

rted

inan

imal

sat

low

erd

ose

lev

els,

bu

tn

ot

stat

isti

call

yan

aly

zed

)N

oef

fect

:M

ales

-n

oef

fect

inti

me

top

rep

uti

alse

par

atio

n,

cop

ula

tio

n,

or

fert

ilit

y;

inn

um

ber

of

imp

lan

tso

rn

um

ber

of

reso

rpti

on

sin

sire

dp

reg

nan

cies

;se

rum

test

ost

ero

ne;

epid

idy

mal

sper

mco

nce

ntr

atio

n;

or

test

icu

lar

his

tolo

gic

chan

ges

Fem

ales

-n

oef

fect

inag

eat

vag

inal

op

enin

g

100

(hig

hd

ose

;n

oef

fect

)–

Sp

rag

ue-

Daw

ley

rat;

0o

rd

iet

con

tain

ing

0.5

g/

kg

gen

iste

in(5

00

mg

/kg

die

t;a

uth

ors

est

ima

ted

inta

kes

of

10

mg

/da

yd

uri

ng

pre

gn

ancy

an

d1

8.5

mg

/da

yd

uri

ng

lact

ati

on

;th

ise

qu

als

B2

6–

47

mg

/kg

bw

/da

yb

ase

do

nth

ere

po

rte

db

od

yw

eig

ht

ofB

38

0g

ind

am

s)

No

effe

ct:

on

pre

gn

ancy

ou

tco

me;

pu

pb

od

yw

eig

ht

du

rin

gp

reg

nan

cy,

lact

atio

n,

or

afte

rw

ean

ing

;o

rgan

wei

gh

tsin

off

spri

ng

(ute

rus,

ov

ary,

test

es,

epid

idy

mid

esat

PN

D15

,49

and

75)

B26

–47

(hig

hd

ose

;n

oef

fect

)

–T

ou

sen

etal

.(2

006)

Lim

ited

(ora

l)

Sp

rag

ue-

Daw

ley

dam

sw

ere

fed

die

tco

nta

inin

g0

or

5p

pm

gen

iste

infr

om

GD

17th

rou

gh

ou

tth

ela

ctat

ion

per

iod

up

toP

ND

70in

off

spri

ng

.(E

xp

osu

rein

off

spri

ng

est

imate

datB

0.6

8m

g/

kg

bw

/day

ov

er

the

life

tim

e.)

Ch

ang

esin

ov

aria

nh

isto

log

yat

PN

D21

and

70;k

bo

dy

wei

gh

tin

PN

D70

fem

ales

(co

nti

nu

ou

sex

po

sure

toP

ND

70);m

bo

dy

wei

gh

tin

PN

D70

fem

ales

(ex

po

sure

pri

or

toP

ND

21)

–B

0.68

b(s

ing

led

ose

)A

wo

niy

iet

al.

(199

8)

Lim

ited

(ora

l)

No

effe

ctin

fem

ales

on

PN

D70

on

seru

mL

H,

FS

H,

17b-

estr

adio

l,p

rog

este

ron

e,o

var

ian

or

ute

rin

ew

eig

ht

B0.

68b

(sin

gle

do

se;

no

effe

ct)

Pre

gn

ant

Sp

rag

ue-

Daw

ley

rats

wer

efe

dd

iets

con

tain

ing

0,20

,o

r10

0p

pm

gen

iste

in(0

,2

0,

or

87

mg

/kg

bw

/day

)fr

om

con

cep

tio

nth

rou

gh

po

stn

atal

life

(GD

1to

PN

D56

).

man

og

enit

ald

ista

nce

infe

mal

es;k

age

and

wei

gh

tat

vag

inal

op

enin

g;m

ute

rus

wei

gh

to

nP

ND

21;m

rela

tiv

ete

stis

wei

gh

to

nP

ND

21;m

rela

tiv

ete

stis

wei

gh

to

nP

ND

56;k

ven

tral

pro

stat

ew

eig

ht

2087

Cas

ano

va

etal

.(1

999)

Lim

ited

(ora

l)

No

effe

ct:

on

imp

lan

tati

on

site

sp

erd

am;x

of

liv

ep

up

sp

erli

tter

;o

rli

tter

wei

gh

tat

bir

th;

pro

po

rtio

no

fm

ales

wit

hre

tain

edn

ipp

les;

age

or

wei

gh

tat

pre

pu

tial

sep

arat

ion

;o

rw

eig

ht

(ab

solu

teo

rre

lati

ve)

of

the

test

is(P

ND

21o

r56

)o

rv

entr

alp

rost

ate

(PN

D56

)as

litt

erm

ean

s

87(h

igh

do

se;n

oef

fect

)–

Lo

ng

Ev

ans

rat;

0o

r15

mg

/k

gb

w/

day

gen

iste

inb

yg

avag

eo

nG

D14

toP

ND

21.

mu

teri

ne

pro

ges

tero

ne

rece

pto

rex

pre

ssio

nin

gla

nd

ula

rep

ith

elia

lce

lls

–15

(sin

gle

do

sest

ud

y)

Hu

gh

eset

al.

(200

4)L

imit

ed(o

ral)

No

effe

ct:

ute

rin

elu

min

alep

ith

elia

lce

llh

eig

ht,

ute

rin

ep

roli

fera

tio

n,

ERa

exp

ress

ion

inu

teri

ne

lum

inal

or

gla

nd

ula

rep

ith

elia

lce

lls,

or

pro

ges

tero

ne

rece

pto

rex

pre

ssio

nin

lum

inal

epit

hel

ial

cell

s

15(h

igh

do

se;n

oef

fect

)–

Sp

rag

ue-

Daw

ley

rat;

at0,

25,

250,

or

1250

pp

mg

enis

tein

inth

ed

iet

fro

mG

D7

tow

ean

ing

via

dam

and

dir

ectl

yto

off

spri

ng

afte

rw

ean

ing

thro

ug

hP

ND

50(B

2,

20

,2

00

mg

/kg

bw

/day

)

Hep

atic

CY

P3A

enzy

me

exp

ress

ion

inm

ales

;al

tere

dfo

rmat

ion

of

test

ost

ero

ne

met

abo

lite

sin

liv

erm

icro

som

es,

i.e.

,D

HT

/3-

dio

lan

d7a

-OH

B2

ZB

20a

Lau

ren

zan

aet

al.

(200

2)

Lim

ited

(ora

l)

441NTP-CERHR EXPERT PANEL REPORT

Birth Defects Research (Part B) 92:421–468, 2011

Page 22: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

Tab

le8

Co

nti

nu

ed

An

imal

mo

del

and

stu

dy

des

ign

En

dp

oin

tsN

OE

LL

OE

LR

efer

ence

Uti

lity�

Liv

ercy

toso

lic

ERa

exp

ress

ion

,m

infe

mal

esan

dk

inm

ales

;k

form

atio

no

fte

sto

ster

on

em

etab

oli

tes

inli

ver

mic

roso

mes

,i.

e.,

2a-O

Han

d16a-

OH

B20

B20

0

Wis

tar

rats

;p

hy

toes

tro

gen

-fre

e(S

snif

fS

MR

/M

-H)

and

gen

iste

inri

chd

iet

(700

mg/

gg

enis

tein

)d

uri

ng

ges

tati

on

and

lact

atio

n;

F1

fem

ale

off

spri

ng

wea

ned

tod

iet

of

the

dam

;F

1o

ffsp

rin

gas

sess

edas

inta

ctju

ven

iles

and

ov

arie

cto

miz

edad

ult

s(O

VX

)(T

he

au

tho

rse

stim

ate

ex

po

sure

sfo

rth

eg

en

iste

inri

chd

iet

we

re7

3m

g/k

gb

w/d

ay

for

juv

enil

ea

nd

ad

ult

rats

,re

spec

tiv

ely

.)

Juv

enil

e:m

ute

rin

ew

eig

ht;k

of

IGF

-1an

dIG

F-1

Rin

ute

rus

;k

Ra

mR

NA

exp

ress

ion

inu

teru

s;k

PR

mR

NA

exp

ress

ion

inu

teru

s;m

C3

exp

ress

ion

inu

teru

s

–73

Mo

ller

etal

.(2

009)

Lim

ited

(ora

l)

Ad

ult

(OV

X):k

C3

exp

ress

ion

inu

teru

s–

93

Sp

rag

ue-

Daw

ley

rat;

0o

r5

(n5

16)

pp

mg

enis

tein

infe

ed(0

.12

mg

/kg

bw

/day

)in

feed

fro

mG

D17

toP

ND

21.

At

wea

nin

g,

on

eh

alf

of

gen

iste

ino

ffsp

rin

gw

ere

con

tin

ued

on

gen

iste

ind

iet

and

rem

ain

der

wer

ep

rov

ided

con

tro

ld

iet

kse

rum

LH

and

test

ost

ero

ne

on

PN

D21

;k

pit

uit

ary

mR

NA

exp

ress

ion

of

LH

a-su

bu

nit

on

PN

D21

;k

epid

idy

mis

wei

gh

tan

dk

bo

dy

wei

gh

t,an

dk

seru

mL

Hat

PN

D13

0in

all

mal

esw

ith

pre

nat

al/

lact

atio

nal

exp

osu

re;k

test

isw

eig

ht

atP

ND

130

wit

hp

ren

atal

/la

ctat

ion

alex

po

sure

on

ly(n

ot

con

tin

uo

us

exp

osu

re)

–0.

12b

Ro

ber

tset

al.

(200

0)L

imit

ed(o

ral)

No

effe

ct:

seru

mte

sto

ster

on

ele

vel

so

rp

itu

itar

ym

RN

Aex

pre

ssio

no

fL

Hb-

sub

un

ito

nP

ND

130

inal

lm

ales

wit

hp

ren

atal

/la

ctat

ion

alex

po

sure

;te

stic

ula

rsp

erm

atid

cou

nt,

seru

mF

SH

or

pit

uit

ary

mR

NA

exp

ress

ion

of

FS

Hb-

sub

un

itat

any

age

CD

sS

DIG

Sra

t;0

or

1250

pp

mg

enis

tein

ind

iet

(me

an1

47

mg

/kg

bw

/day

)fr

om

GD

15to

PN

D11

.

kli

tter

size

,m

dis

rup

ted

estr

ou

scy

cles

,m

end

om

etri

al,

vag

inal

and

mam

mar

yh

yp

erp

lasi

a,an

dat

reti

co

var

ian

foll

icle

s

–14

7(s

ing

led

ose

lev

elst

ud

y)

Tak

agi

etal

.(2

004)

Lim

ited

(ora

l)

No

effe

ct:

on

dam

feed

con

sum

pti

on

or

bo

dy

wei

gh

t,p

up

bo

dy

wei

gh

to

nP

ND

3,p

up

bo

dy

wei

gh

tg

ain

du

rin

gla

ctat

ion

per

iod

,p

up

surv

ival

tow

ean

ing

,se

rum

test

ost

ero

ne

or

17b-

estr

adio

lo

nP

ND

3

147

(hig

hd

ose

;n

oef

fect

)–

Sp

rag

ue-

Daw

ley

rat;

0,0.

1,1,

or

10m

g/

kg

bw

/d

ayg

enis

tein

by

gav

age

fro

mG

D14

tob

irth

.m

Raf

1an

dE

rk2

mR

NA

exp

ress

ion

inP

ND

3te

stes

–0.

1aT

hu

illi

eret

al.,

(200

9)

Lim

ited

(ora

l)P

ND

3:N

oef

fect

on

Erk

1an

dM

ek1

mR

NA

exp

ress

ion

or

mo

rph

olo

gic

alch

ang

esin

test

es10

(hig

hd

ose

;no

effe

ct)

Ad

ult

:N

oef

fect

on

fert

ilit

yo

rle

vel

so

rlo

cati

on

of

the

ph

op

ho

-ER

Ksi

gn

als

inte

stes

or

circ

ula

tin

gte

sto

ster

on

ele

vel

sS

pra

gu

e-D

awle

yra

t;0,

or

10m

g/

kg

bw

/d

ayg

enis

tein

by

gav

age

fro

mG

D14

tob

irth

.k

go

no

cyte

pro

life

rati

on

inP

ND

3te

stes

;m

nu

mb

ers

of

sper

mat

og

on

iaan

dp

rele

pto

ten

e/le

pto

ten

esp

erm

ato

cyte

so

nP

ND

21(b

ut

no

tP

ND

60);m

Ley

dig

cell

nu

mb

ers

on

PN

D21

and

PN

D60

–10

(sin

gle

do

sele

vel

stu

dy

)T

hu

illi

eret

al.,

(200

9)

Lim

ited

(ora

l)

Sp

rag

ue-

Daw

ley

rat;

0,0.

1,10

,o

r10

0m

g/

kg

bw

/d

ayg

enis

tein

by

scin

ject

ion

on

GD

11–2

0A

lter

edex

pre

ssio

no

f23

gen

esb

ased

on

feta

lte

stis

or

epid

idy

mis

sam

ple

s(p

oo

led

)in

hig

hd

ose

gro

up

ina

do

se-r

elat

edm

ann

er

1010

0N

acif

fet

al.

(200

5)L

imit

ed(p

aren

tera

l)

442 MCCARVER ET AL.

Birth Defects Research (Part B) 92:421–468, 2011

Page 23: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

No

effe

ct:

mat

ern

alb

od

yw

eig

ht;

nu

mb

erli

ve

fetu

ses/

litt

er;

gro

ssh

isto

pat

ho

log

ical

effe

cts

on

feta

lte

stis

or

epid

idy

mis

100

(hig

hd

ose

;n

oef

fect

)

Lo

bu

nd

-Wis

tar

rat;

0o

r25

0m

gg

enis

tein

/k

gA

IN-

76d

iet.

Fo

ur

gro

up

so

fg

enis

tein

-ex

po

sed

mal

es:

con

tro

l(G

rou

pA

),b

irth

–P

ND

35(G

rou

pB

),P

ND

90—

11m

on

ths

(Gro

up

C);

bir

thth

rou

gh

ou

tli

fe(G

rou

pD

)

Res

po

nse

toN

MU

inch

emic

ally

-cas

trat

edra

tsim

pla

nte

dw

ith

asi

last

icca

psu

leco

nta

inin

gte

sto

ster

on

e:k

po

orl

yd

iffe

ren

tiat

edp

rost

atic

tum

ors

inG

rou

ps

C&

D(r

egu

lati

on

of

AR

/A

kt/

PT

EN

axis

sug

ges

ted

asm

ole

cula

rm

ech

anis

ms)

–25

0m

gg

enis

tein

/k

gA

IN-7

6d

iet

(sin

gle

do

sele

vel

)

Wan

get

al.

(200

9)L

imit

ed(o

ral)

N-m

eth

yln

itro

sou

rea

(NM

U)

use

dto

ind

uce

pro

stat

eca

nce

rat

PN

D70

Sp

rag

ue-

Daw

ley

rat;

0,30

0,o

r80

0p

pm

gen

iste

inin

die

td

uri

ng

pre

gn

ancy

and

lact

atio

nan

du

pto

PN

D90

ino

ffsp

rin

g;

(me

an

ex

po

sure

s:2

5a

nd

53

mg

/kg

bw

/day

ind

am

sa

nd

30

an

d8

4m

g/k

gb

w/d

ay

inp

up

s.)

kb

irth

wei

gh

to

ffe

mal

eo

ffsp

rin

g;

acce

lera

ted

vag

inal

op

enin

g–

25Y

ou

etal

.(2

002a

)L

imit

ed(o

ral)

kb

od

yw

eig

ht

atP

ND

21an

dP

ND

110

inm

ales

and

fem

ales

;m

pit

uit

ary

wei

gh

tin

mal

es;k

age

atp

rep

uti

alse

par

atio

nw

hen

usi

ng

bo

dy

wei

gh

tas

cov

aria

te;m

mam

mar

yg

lan

db

ran

chin

gan

dP

CN

Aim

mu

no

stai

nin

go

fm

amm

ary

epit

hel

ial

cell

sin

mal

es

3084

No

effe

ct:

liv

er,

bra

in,

ven

tral

pro

stat

e,te

stis

,o

ru

teri

ne

wei

gh

tsat

PN

D21

or

PN

D11

0;n

oh

isto

log

icef

fect

sin

mal

eo

rfe

mal

eti

ssu

es

84(h

igh

do

se;n

oef

fect

)–

Lo

ng

Ev

ans

rats

;0,

10m

g/

kg

bw

gen

iste

inb

ysc

inje

ctio

nP

ND

0–3

Ad

van

ced

vag

inal

op

enin

g;

alte

red

estr

ou

scy

clin

gb

y10

wee

ks;

kG

nR

Hac

tiv

atio

n;k

AV

PV

KIS

Sd

ensi

ty–

10(s

ing

led

ose

lev

el)

Bat

eman

and

Pat

isau

l(2

009)

Lim

ited

(par

ente

ral)

No

effe

ct:

on

AR

CK

ISS

fib

erd

ensi

ty10

(sin

gle

do

sele

vel

)–

Sp

rag

ue-

Daw

ley

rats

;0,

250mg

gen

iste

inb

ysc

inje

ctio

nev

ery

12h

rb

egin

nin

go

nP

ND

1fo

ra

tota

lo

f4

inje

ctio

ns

(ass

um

ing

aS

pra

gu

e-

Da

wle

yra

tp

up

we

igh

s7

.5g

,e

ach

do

sew

ou

ldb

e3

3.3

mg

/kg

bw

/day

.T

wo

inje

ctio

ns

pe

rd

ay

for

ato

tal

of

66

.7m

g/k

gb

w/d

ayg

en

iste

in)

No

effe

ct:

on

5-H

Tfi

ber

den

sity

;o

nco

lab

elin

go

fV

MN

v1

ERa

and

Hu

C/

D66

.7(s

ing

led

ose

lev

el)

–P

atis

aul

etal

.(2

008)

Lim

ited

(par

ente

ral)

Alp

k:

AP

fSD

rat:

0,0.

2,o

r2

mg

/k

gb

w/

day

gen

iste

inb

ysc

inje

ctio

nd

uri

ng

PN

D1–

6an

d4

and

40m

g/

kg

bw

/d

ayb

yg

avag

eo

nP

ND

7–21

(sc

do

ses

wer

ed

eter

min

edto

be

equ

ival

ent

tog

avag

ed

ose

so

f4

and

20m

g/

kg

bw

/d

ay);

on

ep

art

of

the

stu

dy

exam

inin

gS

DN

-PO

Ad

ose

dan

imal

sd

uri

ng

the

sam

ep

erio

dw

ith

scan

do

ral

do

ses

equ

ival

ent

to4

and

40m

g/

kg

bw

/d

ayb

yo

ral

exp

osu

re

Ad

van

ced

vag

inal

op

enin

g,k

bo

dy

wei

gh

tin

fem

ales

fro

mP

ND

57to

13w

eek

so

fag

e,p

ersi

sten

tv

agin

alco

rnif

icat

ion

,an

dk

seru

mp

rog

este

ron

e

440

Lew

iset

al.

(200

3)L

imit

ed(p

aren

tera

l)

mu

teri

ne

wei

gh

tat

PN

D22

(fo

llo

win

gsc

inje

ctio

no

nP

DN

1–6

on

ly)

0.2

2

mS

DN

PO

Av

olu

me

infe

mal

es,m

ute

rin

ew

eig

ht

atP

ND

224

40

Sp

rag

ue-

Daw

ley

rat;

0,0.

1,10

,o

r10

0m

g/

kg

bw

/d

ayg

enis

tein

by

scin

ject

ion

on

GD

11to

20A

lter

edex

pre

ssio

no

f22

7g

enes

bas

edin

po

ole

dfe

tal

ov

ary

and

ute

rin

esa

mp

les;

66g

enes

resp

on

ded

insi

mil

arp

atte

rnto

eth

iny

les

trad

iol

and

bis

ph

eno

lA

1010

0N

acif

fet

al.

(200

2)L

imit

ed(p

aren

tera

l)

443NTP-CERHR EXPERT PANEL REPORT

Birth Defects Research (Part B) 92:421–468, 2011

Page 24: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

Tab

le8

Co

nti

nu

ed

An

imal

mo

del

and

stu

dy

des

ign

En

dp

oin

tsN

OE

LL

OE

LR

efer

ence

Uti

lity�

No

effe

ct:

on

mat

ern

alb

od

yw

eig

ht,

nu

mb

ero

fli

ve

fetu

ses/

litt

er,

gro

sso

rh

isto

pat

ho

log

icef

fect

so

no

var

yo

ru

teru

s

100

(hig

hd

ose

;n

oef

fect

)–

Wis

tar

rat;

0o

r1

mg

/d

ay[B

19

mg

/kg

]g

enis

tein

by

scin

ject

ion

fro

mP

ND

1to

5E

arly

on

set

of

vag

inal

op

enin

g,

alte

red

estr

ou

scy

clin

g;k

bo

dy

wei

gh

tin

fem

ales

;k

ov

aria

nw

eig

ht;k

nu

mb

ero

fco

rpo

ralu

tea

–B

19(s

ing

led

ose

stu

dy

)K

ou

ki

etal

.(2

003)

Lim

ited

(par

ente

ral)

B19

(hig

hd

ose

;n

oef

fect

)–

Wis

tar

rat;

0o

r1

mg

/d

ay[B

19

mg

/kg

]d

aid

zein

by

scin

ject

ion

fro

mP

ND

1to

5E

arly

on

set

of

vag

inal

op

enin

g,

alte

red

estr

ou

scy

clin

g;k

bo

dy

wei

gh

tin

fem

ales

;k

ov

aria

nw

eig

ht;k

nu

mb

ero

fco

rpo

ralu

tea

–B

19(s

ing

led

ose

stu

dy

)K

ou

ki

etal

.(2

003)

Lim

ited

(par

ente

ral)

CR

CD

rat;

0,5,

or

25m

g/

anim

al/

day

gen

iste

inb

ysc

inje

ctio

nfr

om

GD

16to

20(1

5a

nd

75

mg

/kg

bw

/day

)

kb

irth

wei

gh

to

ffe

mal

es15

75L

evy

etal

.(1

995)

Lim

ited

(par

ente

ral)

kan

og

enit

ald

ista

nce

inm

ales

;d

elay

edv

agin

alo

pen

ing

15a

No

effe

ct:

vo

lum

eo

fS

DN

-PO

Ain

eith

erse

x75

(hig

hd

ose

;no

effe

ct)

0o

r50

0m

g/

kg

bw

gen

iste

inb

ysc

inje

ctio

no

nP

ND

16,

18,

and

20m

ute

rin

ew

eig

ht,m

seru

m17

b-es

trad

iol,

andk

seru

mp

rog

este

ron

eo

nP

ND

21;k

ERa

pro

tein

;k

and

rog

enre

cep

tor

pro

tein

;m

pro

ges

tero

ne

rece

pto

rp

rote

in(b

oth

iso

form

s)

–50

0(s

ing

led

ose

stu

dy

)C

otr

on

eoet

al.

(200

1)

Lim

ited

(par

ente

ral)

Bra

inan

dbe

havi

orC

Ds

(SD

)IG

Sra

t;0,

20,

200,

or

1000

pp

mg

enis

tein

ind

iet

fro

mG

D15

toP

ND

10(m

ean

est

ima

ted

inta

kes

of

1.3

–2

.1,

13

.7–

23

.0,

an

d6

6.6

–11

3.1

mg

/k

gb

w/d

ay)

No

effe

ct:

on

pro

po

rtio

no

fp

itu

itar

yce

lls

stai

nin

gfo

rL

H,

FS

H,

and

pro

lact

in66

.6–1

13.1

(hig

hd

ose

;n

oef

fect

)

–M

asu

tom

iet

al.

(200

4b)

Lim

ited

(ora

l)

Sp

rag

ue-

Daw

ley

rat;

0,5,

100,

and

500

pp

mg

enis

tein

ind

iet

thro

ug

hg

esta

tio

nan

dla

ctat

ion

and

ino

ffsp

rin

gu

nti

lP

ND

140

(0,

0.3

1,5

.7,

34

mg

/kg

bw

/da

y)

mca

lbin

din

-po

siti

ve

cell

sin

SD

N-P

OA

inm

ales

–0.

31S

call

etet

al.

(200

4)L

imit

ed(o

ral)

Sp

rag

ue-

Daw

ley

rat;

0o

r10

00p

pm

gen

iste

inin

die

tfr

om

GD

15to

PN

D11

(B6

6.6

–11

3.1

mg

/kg

bw

/day

)

No

effe

ct:

gen

eex

pre

ssio

no

fE

Ra,

ERb,

pro

ges

tero

ne

rece

pto

r,an

dst

ero

idre

cep

tor

coac

tiv

ato

rin

the

hy

po

thal

amic

pre

op

tic

area

B66

.6–1

13.1

(sin

gle

do

sest

ud

y;

no

effe

ct)

Tak

agi

etal

.(2

005)

Lim

ited

(ora

l)

CR

CD

rat;

0,10

0,o

r10

00mg

gen

iste

ino

nP

ND

1–10

0.1,

or

1,m

g/

day

by

scin

ject

ion

on

PN

D1–

10.

(Me

anE

12

an

d11

7m

g/k

gb

w/d

ay)

No

n-d

ose

-rel

ated

min

LH

secr

etio

n–

12a

Fab

eran

dH

ug

hes

(199

1)

Lim

ited

(par

ente

ral)

mS

DN

-PO

Av

olu

me

infe

mal

es12

117

CR

CD

rat;

0,0.

001,

0.01

,0.

1,0.

200,

0.4,

0.5,

or

1.0

mg

0,1,

10,

100,

200,

400,

500,

or

1000

mgg

enis

tein

by

scin

ject

ion

on

PN

D1–

10.

(Me

anE

0.1

2,

1.2

,1

2,

23

,4

7,

58

,a

nd

117

mg

/kg

bw

/d

ay.

)

mG

nR

H-i

nd

uce

dL

Hse

cret

ion

–0.

12F

aber

and

Hu

gh

es(1

991)

Lim

ited

(par

ente

ral)

mS

DN

-PO

Av

olu

me

4758

444 MCCARVER ET AL.

Birth Defects Research (Part B) 92:421–468, 2011

Page 25: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

Sp

rag

ue-

Daw

ley

rat;

0o

r25

0mg

/p

up

of

gen

iste

inb

ysc

inje

ctio

ntw

ice

ad

ayo

nP

ND

1an

d2

(B1

00

mg

/kg

bw

/day

)

min

nu

mb

ero

fA

VP

Vce

lls

po

siti

ve

for

tyro

sin

eh

yd

rox

yla

sein

mal

es;k

nu

mb

ero

fA

VP

Vce

lls

po

siti

ve

for

bo

thty

rosi

ne

hy

dro

xy

lase

and

ER

ain

fem

ales

;k

%o

fA

VP

Vce

lls

wit

hE

Ra

inb

oth

mal

esan

dfe

mal

es

–B

100

(sin

gle

do

sest

ud

y)

Pat

isau

let

al.

(200

6)L

imit

ed(p

aren

tera

l)

Sp

rag

ue-

Daw

ley

mal

era

t;0

or

250mg

/p

up

of

gen

iste

inb

ysc

inje

ctio

ntw

ice

ad

ayo

nP

ND

1an

d2

(B10

0m

g/

kg

bw

/d

ay)

mca

lbin

din

imm

un

ore

ativ

ece

lls

inC

AL

B-S

DN

inm

ales

;mA

VP

Vv

olu

me

inm

ales

–B

100

(sin

gle

do

sest

ud

y)

Pat

isau

let

al.

(200

7)L

imit

ed(p

aren

tera

l)N

oef

fect

:S

DN

or

CA

LB

-SD

Nv

olu

me;

nu

mb

ero

fG

nR

Hn

euro

ns,

Fo

sex

pre

ssio

nB

100

(hig

hd

ose

;n

oef

fect

)

Lo

ng

Ev

ans

mal

era

t;0

or

10m

g/

kg

of

gen

iste

inb

ysc

inje

ctio

nfr

om

bir

th(P

ND

0)to

PN

D3

No

effe

ct:

KIS

Sim

mu

no

reac

tiv

en

euro

ns

inth

eA

VP

Van

dA

RC

inm

ales

10(h

igh

do

se;n

oef

fect

)–

Pat

isau

let

al.

(200

9)L

imit

ed(p

aren

tera

l)L

on

gE

van

sm

ale

rat;

0o

r10

mg

/k

go

feq

uo

lb

ysc

inje

ctio

nfr

om

bir

th(P

ND

0)to

PN

D3

No

effe

ct:

KIS

Sim

mu

no

reac

tiv

en

euro

ns

inth

eA

VP

Van

dA

RC

inm

ales

10(h

igh

do

se;n

oef

fect

)–

Pat

isau

let

al.

(200

9)L

imit

ed(p

aren

tera

l)M

amm

ary

glan

dde

velo

pmen

tan

dca

rcin

ogen

esis

Sp

rag

ue-

Daw

ley

rat,

die

tco

nta

inin

gr

5p

pm

each

of

gen

iste

inan

dd

aid

zein

or

5,10

0,o

r50

0p

pm

gen

iste

in,

mu

ltig

ener

atio

nal

des

ign

(Th

eF

0g

ener

atio

nw

asex

po

sed

fro

msi

xw

eek

so

fag

eu

nti

lte

rmin

atio

n;

the

F1

and

F2

gen

erat

ion

sw

ere

exp

ose

dfr

om

con

cep

tio

nth

rou

gh

term

inat

ion

;th

eF

3g

ener

atio

nw

asex

po

sed

fro

mco

nce

pti

on

thro

ug

hw

ean

ing

on

PN

D21

and

then

pla

ced

on

the

con

tro

ld

iet

un

til

term

inat

ion

;th

eF

4g

ener

atio

nw

asn

ot

dir

ectl

yex

po

sed

toth

ep

rep

ared

die

ts).

Asu

bse

to

fm

ale

wea

nli

ng

F1

and

F3

anim

als

fro

mth

em

ult

igen

erat

ion

stu

die

sw

ere

assi

gn

edto

2-y

ear

stu

die

s,th

ree

exp

osu

red

ura

tio

ns

wer

est

ud

ied

:co

nti

nu

ou

sex

po

sure

fro

mco

nce

pti

on

thro

ug

h2

yea

rs(F

1C–

F1

gen

erat

ion

),ex

po

sure

fro

mco

nce

pti

on

thro

ug

hP

ND

140

foll

ow

edb

yco

ntr

ol

die

tu

nti

lte

rmin

atio

n(F

1T14

0—F

1g

ener

atio

n),

exp

osu

refr

om

con

cep

tio

nth

rou

gh

wea

nin

gat

PN

D21

foll

ow

edb

yco

ntr

ol

die

tu

nti

lte

rmin

atio

n(F

3T21

—F

3g

ener

atio

n).

All

surv

ivin

gan

imal

sw

ere

kil

led

afte

r2

yea

rsan

dco

mp

lete

nec

rop

sies

wer

ep

erfo

rmed

Mam

mar

yg

lan

dh

yp

erp

lasi

ain

mal

esin

stu

dy

term

inat

edo

nP

ND

140

(F1,

F2)

5p

pm

100

pp

mL

aten

dre

sse

etal

.(2

009)

Lim

ited

(ora

l)

Mam

mar

yg

lan

dh

yp

erp

lasi

ain

mal

esin

2-y

ear

stu

dy

(F1T

140)

100

pp

m50

0p

pm

No

effe

ct:

mam

mar

yg

lan

dfi

bro

ma,

fib

road

eno

ma,

neo

pla

sia,

or

pat

tern

of

fem

iniz

atio

nin

mal

era

ts;

du

ctal

hy

per

pla

sia

atan

yd

ose

500

pp

m(h

igh

do

se;

no

effe

ct)

Sp

rag

ue-

Daw

ley

rat;

0,30

0,o

r80

0p

pm

gen

iste

inin

die

td

uri

ng

ges

tati

on

and

lact

atio

nm

IGF

-1re

cep

tor

300

pp

m80

0p

pm

Yo

uet

al.

(200

2b)

Lim

ited

(ora

l)m

bra

nch

es,

term

inal

end

bu

ds,

and

late

ral

bu

ds

inm

ale

off

spri

ng

300

pp

m(p

50.

06)

800

pp

m

No

effe

ct:

seru

mp

rola

ctin

800

pp

m(h

igh

do

se;

no

effe

ct)

445NTP-CERHR EXPERT PANEL REPORT

Birth Defects Research (Part B) 92:421–468, 2011

Page 26: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

Tab

le8

Co

nti

nu

ed

An

imal

mo

del

and

stu

dy

des

ign

En

dp

oin

tsN

OE

LL

OE

LR

efer

ence

Uti

lity�

Sp

rag

ue-

Daw

ley

rat;

0,25

,o

r25

0p

pm

gen

iste

inin

die

t(B

0,

2.2

,a

nd

22

mg

/kg

bw

/day

)d

uri

ng

pre

gn

ancy

and

lact

atio

n.

At

PN

D50

,al

lfe

mal

esw

ere

adm

inis

tere

dd

imet

hy

lben

zan

thra

cen

e(D

MB

A)

toin

du

cem

amm

ary

gla

nd

tum

ors

kD

MB

A-i

nd

uce

dtu

mo

rs;k

typ

e1

lob

ule

s–

2.2

Fri

tzet

al.

(199

8)L

imit

ed(o

ral)

kte

rmin

alen

db

ud

s2.

222

No

adv

erse

effe

cts

on

rep

rod

uct

ive

dev

elo

pm

ent

inm

ales

or

fem

ales

;n

um

ber

of

typ

eII

lob

ule

s;D

NA

lab

elin

go

fm

amm

ary

end

bu

ds

or

term

inal

du

cts

22(h

igh

do

se;n

oef

fect

)

Sp

rag

ue-

Daw

ley

rat;

0,15

,15

0,o

r30

0m

g(a

gly

con

eeq

uiv

alen

t)/

kg

gen

iste

inin

die

td

uri

ng

pre

gn

ancy

and

lact

atio

nv

iaa

cro

ss-

fost

ered

dam

.(e

stim

ate

dm

ate

rna

lin

tak

ea

t1

–1

.5,

10

–1

5,

an

d2

0–

30m

g/k

gb

w/d

ay

).A

tP

ND

47,

ap

ort

ion

of

fem

ales

wer

ead

min

iste

red

dim

eth

ylb

enza

nth

race

ne

(DM

BA

)to

ind

uce

mam

mar

yg

lan

dtu

mo

rs

kp

rop

ort

ion

surv

ivin

gto

17w

eek

sin

F1

off

spri

ng

foll

ow

ing

DM

BA

trea

tmen

to

nP

ND

471–

1.5

10–1

5H

ilak

ivi-

Cla

rke

etal

.(2

002)

Lim

ited

(ora

l)

kse

rum

17b-

estr

adio

lat

8w

eek

s;k

nu

mb

ers

of

lob

ule

s;m

TE

Bs;

mm

amm

ary

tum

ors

inF

1o

ffsp

rin

gfo

llo

win

gD

MB

Atr

eatm

ent

on

PN

D47

10–1

520

–30

No

effe

ct:

litt

ersi

ze;

po

stn

atal

pu

pw

eig

ht

gai

n;

tum

or

late

ncy

or

mu

ltip

lici

tyin

F1

off

spri

ng

foll

ow

ing

DM

BA

trea

tmen

to

nP

ND

47

20–3

0(h

igh

do

se;

no

effe

ct)

Sp

rag

ue-

Daw

ley

rat;

0,30

0,80

0p

pm

gen

iste

inin

die

tfr

om

GD

0th

rou

gh

ges

tati

on

and

lact

atio

n,

off

spri

ng

on

sam

ed

iet

asd

ams

afte

rw

ean

ing

(PN

D22

)u

nti

lP

ND

90

Mo

der

ate

ing

lan

du

lar

size

and

tiss

ue

den

sity

of

mam

mar

yg

lan

ds

inm

ales

–30

0p

pm

Wan

get

al.

(200

6)L

imit

ed(o

ral)

kse

rum

IGF

-I(f

emal

e)30

0p

pm

800

pp

mN

oef

fect

:es

trad

iol,

test

ost

ero

ne,

GH

,F

SH

,L

H,

or

pro

lact

inin

fem

ales

800

pp

m(h

igh

do

se;

no

effe

ct)

Sp

rag

ue-

Daw

ley

rat;

0o

r10

mg

/k

gb

w/

day

gen

iste

inb

ysc

inje

ctio

no

nP

ND

2–8

Mam

mar

yg

lan

ds

sho

wed

evid

ence

of

lact

atio

nw

ith

cyst

icd

uct

ald

ilat

atio

n,

aty

pic

alep

ith

elia

lh

yp

erp

lasi

a,an

dm

icro

calc

ific

atio

ns;

insi

tud

uct

alca

rcin

om

aw

asid

enti

fied

in2/

5an

imal

sex

amin

ed

–10

(sin

gle

do

sest

ud

y)

Fo

ster

etal

.(2

004)

Lim

ited

(par

ente

ral)

Sp

rag

ue-

Daw

ley

rats

;0

orB

0.1

mg

/k

gb

w/

day

gen

iste

inb

yin

ject

ion

on

GD

15–2

0(‘

‘Ex

per

imen

t1’

’);

eval

uat

edfe

mal

eo

ffsp

rin

g

min

cid

ence

of

mam

mar

ytu

mo

rsin

F1

off

spri

ng

foll

ow

ing

DM

BA

trea

tmen

to

nP

ND

45;m

mam

mar

yE

Rp

rote

inco

nte

nt

on

PN

D35

;k

pro

tein

kin

ase

Cac

tiv

ity

on

PN

D45

(bu

tn

ot

PN

D21

)

–B

0.1

(sin

gle

do

sele

vel

)H

ilak

ivi-

Cla

rke

etal

.(1

999a

)

Lim

ited

(par

ente

ral)

On

PN

D45

,fe

mal

esw

ere

adm

inis

tere

dd

imet

hy

lben

zan

thra

cen

e(D

MB

A)

toin

du

cem

amm

ary

gla

nd

can

cer

No

effe

ct:

nu

mb

ero

fp

up

s/li

tter

;P

ND

2b

od

yw

eig

ht;

late

ncy

totu

mo

rd

evel

op

men

t,n

um

ber

of

tum

ors

per

anim

al,

or

nu

mb

ero

ftu

mo

rssh

ow

ing

reg

ula

rg

row

th

B0.

1(h

igh

do

se;

no

effe

ct)

Sp

rag

ue-

Daw

ley

rats

;0,B

0.5,

orB

1.5

mg

/k

gb

w/

day

gen

iste

inb

ysc

inje

ctio

no

nG

D15

–20

(‘‘E

xp

erim

ent

2’’)

;ev

alu

ated

fem

ale

off

spri

ng

kb

od

yw

eig

ht

atP

ND

35(b

ut

no

tea

rlie

ro

rla

ter

tim

ep

oin

ts)

–B

0.5

Hil

akiv

i-C

lark

eet

al.

(199

9a)

Lim

ited

(par

ente

ral)

On

PN

D50

,fe

mal

esw

ere

adm

inis

tere

dd

imet

hy

lben

zan

thra

cen

e(D

MB

A)

toin

du

cem

amm

ary

gla

nd

can

cer

min

cid

ence

of

mam

mar

ytu

mo

rsin

F1

off

spri

ng

foll

ow

ing

DM

BA

trea

tmen

to

nP

ND

50;m

mam

mar

yE

Rp

rote

inco

nte

nt

on

PN

D50

B0.

5B

1.5

446 MCCARVER ET AL.

Birth Defects Research (Part B) 92:421–468, 2011

Page 27: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

Lat

ency

totu

mo

rd

evel

op

men

t,n

um

ber

of

tum

ors

per

anim

al,

or

nu

mb

ero

ftu

mo

rssh

ow

ing

reg

ula

rg

row

thB

1.5

(hig

hd

ose

;n

oef

fect

)–

Sp

rag

ue-

Daw

ley

rats

;0

or

20mg

gen

iste

inb

ysc

inje

ctio

no

nP

ND

7,10

,14

,17

,20

(do

sele

vel

ran

ge

ofB

2m

g/

kg

bw

on

PN

D7

toB

0.7

mg

/k

gb

wo

nP

ND

7);

fem

ale

off

spri

ng

eval

uat

ed

ktu

mo

rm

ult

ipli

city

;k

per

cen

tag

eo

fp

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mo

rsin

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off

spri

ng

foll

ow

ing

DM

BA

trea

tmen

to

nP

ND

45;m

lob

ula

rd

iffe

ren

tiat

ion

,k

term

inal

end

du

ctd

ensi

ty,m

alv

eola

rb

ud

den

sity

–B

0.7–B

2(s

ing

led

ose

lev

el)

Hil

akiv

i-C

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al.

(199

9b)

Lim

ited

(par

ente

ral)

On

PN

D45

,fe

mal

esw

ere

adm

inis

tere

dd

imet

hy

lben

zan

thra

cen

e(D

MB

A)

toin

du

cem

amm

ary

gla

nd

can

cer

No

effe

ct:

bo

dy

wei

gh

tg

ain

;E

Rp

rote

inle

vel

sin

mam

mar

yg

lan

d;

inci

den

ceo

fm

amm

ary

tum

ors

,tu

mo

rla

ten

cyin

F1

off

spri

ng

foll

ow

ing

DM

BA

trea

tmen

to

nP

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45

B0.

7–B

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igh

do

se;

no

effe

ct)

Oth

er/m

echa

nis

tic

Sp

rag

ue-

Daw

ley

rat;

0,5,

100,

or

500mg

/g

gen

iste

inin

feed

du

rin

gg

esta

tio

nan

dla

ctat

ion

(B0

.75,

15

,a

nd

75

mg

/kg

bw

/da

yfo

rw

ea

nli

ng

sa

ndB

0.5

,1

0,

an

d5

0m

g/k

gb

w/d

ay

ina

du

ltfe

ma

les)

kth

yro

idp

ero

xid

ase

acti

vit

yin

bo

thse

xes

–B

0.5–

0.75

Ch

ang

and

Do

erg

e(2

000)

Lim

ited

(ora

l)N

oef

fect

:se

rum

lev

els

of

T3,

T4,

and

TS

HB

50–7

5(h

igh

do

se;

no

effe

ct)

Sp

rag

ue-

Daw

ley

rat;

0,5,

100,

or

500

pp

mg

enis

tein

ind

iet

(B0

.0,

0.4

,8

an

d4

0m

gg

en

iste

in/k

g/

da

y),

mu

ltig

ener

atio

nal

stu

dy

des

ign

(F0–

F4

wit

hF

4n

ever

exp

ose

d)

F1

and

F2:

kb

od

yw

eig

ht

of

bo

thse

xes

0.4

8F

erg

uso

net

al.

(200

9)

Lim

ited

(ora

l)A

lter

atio

ns

inse

xu

ald

imo

rph

ism

of

inta

ke

of

3%so

diu

mso

luti

on

40(h

igh

do

se;n

oef

fect

)–

Sp

rag

ue-

Daw

ley

rat;

0,25

,25

0,o

r12

50p

pm

gen

iste

in(0

,2,

20,

and

100

mg

/k

gb

w/

day

)in

die

tfr

om

GD

7,d

uri

ng

ges

tati

on

and

lact

atio

n,

un

til

PN

D77

ino

ffsp

rin

g

msa

lin

ein

ges

tio

nin

bo

thm

ales

and

fem

ales

2010

0F

lyn

net

al.

(200

0)L

imit

ed(o

ral)

kD

amb

od

yw

eig

ht;k

feed

inta

ke;

ko

ffsp

rin

gw

eig

ht

PN

D42

-PN

D77

250

1250

No

effe

ct:

on

ges

tati

on

ald

ura

tio

n,

tota

lp

up

s/li

tter

;li

ve

pu

ps/

litt

er;

or

sex

rati

o12

50(h

igh

do

se;

no

effe

ct)

Sp

rag

ue-

Daw

ley

rat;

0,30

0,o

r80

0p

pm

gen

iste

inin

die

t(B

26

an

dB

69

mg

/kg

bw

/day

)d

uri

ng

ges

tati

on

and

lact

atio

n.

Alt

ered

sple

enn

atu

ral

kil

ler

cell

acti

vit

yin

mal

ean

dfe

mal

eo

ffsp

rin

g;k

nu

mb

eran

dp

erce

nta

ge

of

CD

41C

D8

thy

mo

cyte

sin

mal

eo

ffsp

rin

g;k

per

cen

tag

eo

fC

D41

CD

8�

thy

mo

cyte

sin

fem

ale

off

spri

ng

a

–26

Gu

oet

al.

(200

2)L

imit

ed(o

ral)

kb

od

yw

eig

ht

inm

ale

and

fem

ale

off

spri

ng

;k

nu

mb

eran

dp

erce

nta

ge

of

CD

4�C

D8�

thy

mo

cyte

san

dp

erce

nta

ge

of

CD

41C

D81

thy

mo

cyte

sin

fem

ale

off

spri

ng

2669

No

effe

ct:

sple

eno

rth

ym

us

size

inm

ale

or

fem

ale

off

spri

ng

69(h

igh

do

se;n

oef

fect

)–

Sp

rag

ue-

Daw

ley

rat;

0,25

,25

0,o

r12

50p

pm

die

tary

gen

iste

in(B

2,

20

,a

nd

10

0m

g/k

gb

w/

da

y)

fro

mG

D7

thro

ug

hla

ctat

ion

kb

on

em

arro

wD

NA

syn

thes

is;m

colo

ny

form

ing

un

its

incu

bat

edw

ith

gra

nu

locy

tem

acro

ph

age

colo

ny

stim

ula

tin

gfa

cto

rin

bo

ne

mar

row

cell

sin

fem

ales

–2a

Gu

oet

al.

(200

5)L

imit

ed(o

ral)

kco

lon

yfo

rmin

gu

nit

sin

cub

ated

wit

hg

ran

ulo

cyte

mac

rop

hag

eco

lon

yst

imu

lati

ng

fact

or

inb

on

em

arro

wce

lls

inm

ales

220

kco

lon

yfo

rmin

gu

nit

sin

cub

ated

wit

hm

acro

ph

age

colo

ny

stim

ula

tin

gfa

cto

rin

bo

ne

mar

row

cell

sin

mal

es2

20a

kre

cov

ered

bo

ne

mar

row

cell

sin

fem

ales

2010

0N

oef

fect

:b

od

yw

eig

ht

of

mal

era

tes

100

(hig

hd

ose

;n

oef

fect

)–

Lo

ng

Ev

ans

mal

era

t;0,

5,o

r30

0m

gg

enis

tein

/k

gfe

ed(0

.42

an

d2

5m

g/k

gb

w/d

ay)

by

mat

ern

alex

po

sure

du

rin

gp

reg

nan

cyan

dla

ctat

ion

sple

enco

un

to

fto

tal

Tce

lls,k

thy

mu

sco

un

tso

fC

D4�

CD

8�

cell

s,m

thy

mu

sco

un

tso

fC

D41

CD

81ce

lls

–0.

42K

lein

etal

.(2

002)

Lim

ited

(ora

l)

kte

sto

ster

on

ele

vel

sa–

0.42

a

447NTP-CERHR EXPERT PANEL REPORT

Birth Defects Research (Part B) 92:421–468, 2011

Page 28: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

adversely affect prenatal endpoints such as growth andpossibly survival. The most consistent and sensitiveprenatal endpoint was lower pup birth weight, whichwas reported at Z300 ppm genistein (Z25 mg/kg bw/day in dams during pregnancy) administered in diet(You et al., 2002a); lower pup birth weight was seen inother studies at higher dose levels (Flynn et al., 2000,2008). A lower number of mated dams delivering litterswas reported in one study at 1250 ppm genistein in diet(83 mg/kg bw/day in dams during pregnancy; Delcloset al., 2001). Decreased live litter size was reported in twostudies at Z500 ppm in diet (44 mg/kg bw/day in damsduring pregnancy) (2008; Takagi et al., 2004). In ratsorally treated by gavage with genistein during theneonatal period, a lower pregnancy rate was observedat Z12.5 mg/kg bw/day and lower numbers of implantswere observed at 100 mg/kg bw/day (Nagao et al., 2001).None of the studies assessed structural malformations.

Oral exposure studies examining postnatal develop-ment in rats suggested that genistein exposures canresult in lower and delayed growth. In well-designedmultiple dose-level studies, lower pup weight or weightgain during the lactation period were observed withexposures in diet given to dams from early-to-midgestation through lactation (Delclos et al., 2001; Youet al., 2002a; Delclos et al., 2009). The lowest effect level inthese studies was Z100 ppm genistein (Z11 mg/kg bw/day in dams during lactation) in the NCTR multi-generation study (2008). Lower body weight was alsoshown with gavage dosing of pups with Z100 mg/kgbw/day during the lactation period (Nagao et al., 2001).One multiple-dose level study with gestational andlactation exposure reported trends for developmentaldelay and significant delays in eye and ear opening at1250 ppm genistein (Z138 mg/kg bw/day in damsduring lactation) (Delclos et al., 2001). None of thestudies reported adverse effects on postnatal survival.

Reproductive endpointsMouse: Female mice: There is some evidence that

genistein affects endocrine-mediated endpoints in femalemice. Disrupted estrous cycles were seen in miceexposed neonatally by oral (Jefferson et al., 2009a) or sc(Nikaido et al., 2004; Jefferson et al., 2005) dosing. Earlyvaginal opening was observed following fetal (Nikaidoet al., 2004) or PND15-19 (Nikaido et al., 2005) exposurevia sc injections to dams or pups, respectively. A lowernumber of live pups was observed in mice exposedneonatally by oral (Jefferson et al., 2009a) or sc dosing(Jefferson et al., 2005, 2009b). Following neonatal–prepubertal sc exposures, abnormal uterine and ovarianhistology was observed (Newbold et al., 2001; Nikaidoet al., 2005). Additionally, multiple oocyte ovarianfollicles were observed following neonatal sc exposure(Jefferson et al., 2002, 2006), although the relevance tohumans is unclear.

Male mice: A shorter anogenital distance, adjusted forbody weight, was observed in 21-day-old male offspringof dams exposed to 10 mg/kg bw/day genistein fromGD 12 to PND 20 by gavage (Fielden et al., 2003),suggesting an antiandrogenic effect of treatment. Sinceanogenital distance was not consistently evaluated in theavailable mouse studies, it is not clear whether this is areproducible effect of genistein in mice. Anogenitaldistance was not altered consistently in male ratsexposed to genistein during development (see below).

Tab

le8

Co

nti

nu

ed

An

imal

mo

del

and

stu

dy

des

ign

En

dp

oin

tsN

OE

LL

OE

LR

efer

ence

Uti

lity�

msp

leen

cou

nts

of

CD

81ce

lls

0.42

25N

oef

fect

:sp

leen

cou

nts

of

CD

41ce

lls,

thy

mu

sco

un

tso

fC

D41

CD

8�,C

D4�

CD

81ce

lls,

inte

rleu

kin

-4o

rin

terf

ero

n-g

by

cult

ure

dly

mp

ho

cyte

s

25(h

igh

do

se,n

oef

fect

)–

Sp

rag

ue-

Daw

ley

rat;

0,0.

1,1,

or

10m

g/

kg

bw

/d

ayg

enis

tein

by

gav

age

on

GD

14-

PN

D0

mex

pre

ssio

no

fP

DG

Fa-

and

PD

GFb-

rece

pto

rm

RN

Ain

test

eso

fP

ND

3–

0.1

Th

uil

lier

etal

.(2

003)

Lim

ited

(ora

l)

mex

pre

ssio

no

fP

DG

Fa-

rece

pto

rm

RN

Ain

ters

titi

um

and

PD

GFb-

rece

pto

rm

RN

Ain

inte

rsti

tiu

m,

cen

tral

and

per

iph

eral

sem

inif

ero

us

cord

s,an

dg

on

ocy

tes

atP

ND

3

110

m,k

5S

ign

ific

ant

incr

ease

,d

ecre

ase.

aD

idn

ot

dis

pla

ya

do

se-r

esp

on

se.

bT

he

Ex

per

tP

anel

has

lim

ited

con

fid

ence

inth

eac

cura

cyo

fth

ed

ose

det

erm

inat

ion

inth

isst

ud

y.� T

he

term

uti

lity

refe

rsto

the

app

lica

bil

ity

toth

ep

urp

ose

of

dra

win

gco

ncl

usi

on

so

nw

het

her

or

no

ta

chem

ical

adv

erse

lyaf

fect

sre

pro

du

ctio

n.

448 MCCARVER ET AL.

Birth Defects Research (Part B) 92:421–468, 2011

Page 29: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

A higher incidence of hypospadias in male fetuses wasobserved following oral exposure of dams to 0.17 mg/kgbw/day genistein between GD 13 and 17 (Vilela et al.,2007). No other studies in mice or rats in which maleoffspring were exposed to genistein during late gestationhave reported a higher incidence of hypospadias.Hyperplasia was reported in the prostate and seminalvesicles of adult mice that had been treated sc with500 mg/kg bw/day genistein on PND 1 to 3 (Strausset al., 1998). Conversely, the relative weights of prostatelobes were lower in adult mice from the same studyfollowing sc treatment with Z50 mg/kg bw/day genis-tein on PND 1 to 3 (Strauss et al., 1998). No effects onsperm count or motility were reported and in vitrofertilization was not lower following oral or sc exposuresof dams or developing offspring to genistein (Shibayamaet al., 2001). There were also no consistent effects on testisweights or testicular morphology following oral or scexposure of male mice (Shibayama et al., 2001; Adachiet al., 2004).

Rat: Female rat: Oral exposure studies suggest thatgenistein can affect endocrine-mediated reproductiveendpoints in female rats. Trends or significant effectson accelerated vaginal opening were observed in severalstudies by oral (Casanova et al., 1999; Delclos et al., 2001;Dalu et al., 2002; You et al., 2002a; Lewis et al., 2003,2008;) or sc injection (Kouki et al., 2003) exposure duringthe prenatal or neonatal period. The lowest genisteineffect level for alterations in vaginal opening wasZ300 ppm (Z30 mg/kg bw/day in pups) in the studyof You et al. (2002a). One study reported a higher numberof polyovular follicles in 21-day-old rats following directgavage dosing with Z12.5 mg/kg bw/day genisteinduring the neonatal period (Nagao et al., 2001). Abnor-mal estrous cycles were reported by oral (2008; Takagiet al., 2004) or sc (Kouki et al., 2003) exposure routes.Smaller litter sizes were seen with oral transplacentalexposure (2008; Takagi et al., 2004). Direct ovarian anduterine effects (including morphological changes) wereobserved in several studies with oral or sc exposureduring the prenatal or neonatal period (Awoniyi et al.,1998; Casanova et al., 1999; Cotroneo et al., 2001; Delcloset al., 2001; Nagao et al., 2001; Naciff et al., 2002; Kouki

et al., 2003; Lewis et al., 2003; Takagi et al., 2004; Molleret al., 2009). Effects of genistein on uterine weight arereported in ‘‘Summary of Pharmacokinetics and GeneralToxicology,’’ which describes in vitro and in vivo studiesof estrogenic activity. No other consistent effects onfemale reproductive organ weights were reported.

Male rat: The majority of effects of genistein reportedin the reproductive system of male rats were on theprostate and male mammary glands (see below for adiscussion of the mammary data). Chronic inflammationof the dorsolateral prostate on PND 50 was reportedfollowing mid-gestational, lactational, and postweaningexposure to dietary genistein at 180 mg/kg bw/day(dose in offspring) (Delclos et al., 2001). Lower ventralprostate weight was observed at PND 50 to 56 followingdietary exposure to Z87 mg/kg bw/day genistein (dosein offspring) (Casanova et al., 1999; Delclos et al., 2001).A limited number of studies examined effects of genisteinexposure during development on hormone levels, and theresults were variable in males and females.

There were no consistent effects on testicular andepididymal weights or testicular morphology in maleoffspring. Lower gonocyte proliferation at PND 3, highernumbers of spermatogonia and preleptotene/leptotenespermatocytes were observed at PND 21, and higherLeydig cell numbers at PND 21 and PND 60 were observedin male offspring of dams given 10 mg/kg bw/daygenistein from GD 14 to birth by gavage (Thuillier et al.,2009). With the exception of one study reporting greaterseverity of abnormal spermatogenesis on PND 50 in malerats given a dietary dose of 180 mg/kg bw/day genisteinfrom GD7–PND 50, which may have been related to theperipubertal status of the rats (Delclos et al., 2001), no otherstudies reported adverse effects on sperm count and/ormotility at genistein doses up to 35 mg/kg bw/daygenistein in diet with exposure during gestation, lactation,and postweaning (2008) or 100 mg/kg bw/day by gavageduring the neonatal period (Nagao et al., 2001). A multi-generation study that included exposures in males duringprenatal and postnatal development reported smaller littersizes at dietary doses of 51 mg/kg bw/day in dams, but noadverse effects on fertility in males at dietary doses up to35 mg/kg bw/day genistein (Delclos et al., 2009).

Table 9Experimental Studies with Developmental Toxicity Endpoints in Other Species Exposed to Genistein, Daidzein, or Equol

Animal model and study design Endpoints NOEL LOEL Reference Utility�

Piglets; 0, 1, or 14 mg/liter genistein informula for 10 days [B0, 0.1–0.4, and2–3 mg/kg bw/day]

k trefoil faction mRNA in stomach – B0.1–0.4 Chen et al.(2005)

Limited(oral)

k enterocyte proliferation and a trend for kenterocyte migration

B0.1–0.4 B2–3

No effect: body weight; intestinal size; jejunavillous morphometric parameters;electrophysiological/clinical measurements(ion, glucose, glutamine transport in jejunumor ileum); jejuna disaccharide, lactase, sucrose;apoptosis in intestinal villi; ERa or ERbexpression in jejunum or ileum; phospho-srcTyr 416 protein expression in jejunum; trefoilfaction mRNA in jejunum or ileum

B2–3 (highdose; noeffect)

m,k5 Significant increase, decrease.aBold values represent dose conversions calculated or estimated by CERHR.�The term utility refers to the applicability to the purpose of drawing conclusions on whether or not a chemical adversely affects reproduction.

449NTP-CERHR EXPERT PANEL REPORT

Birth Defects Research (Part B) 92:421–468, 2011

Page 30: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

Tab

le10

Stu

die

sin

Ex

per

imen

tal

An

imal

sE

xp

ose

dto

So

yF

orm

ula

,S

oy

Die

ts,

or

Oth

erS

oy

Ex

po

sure

sD

uri

ng

Dev

elo

pm

ent

An

imal

mo

del

and

stu

dy

des

ign

En

dp

oin

tsR

efer

ence

Uti

lity

Gro

wth

,re

prod

uct

ive

syst

eman

den

docr

ine-

rela

ted

endp

oin

ts(R

at)

Wis

tar

rat;

soy

pro

tein

-bas

edd

iet

or

sam

ed

iet

wit

his

ofl

avo

nes

rem

ov

edfr

om

pre

-mat

ing

thro

ug

hp

reg

nan

cyan

dla

ctat

ion

So

yp

rote

in-b

ased

die

t:m

acti

vit

yd

uri

ng

dar

kp

erio

dat

3m

on

ths,

bu

tn

ot

6m

on

ths;m

sen

siti

vit

yto

acet

ylc

ho

lin

eat

6m

on

ths

(no

effe

ctat

3m

on

ths)

;m

esen

teri

car

teri

esfr

om

fem

ales

sig

nif

ican

tly

mo

red

iste

nsi

ble

at6

mo

nth

s(u

naf

fect

edat

3m

on

ths)

Do

ug

las

etal

.(2

006)

Lim

ited

(ora

l)

No

effe

ct:

bo

dy

wei

gh

tin

off

spri

ng

;es

tro

us

cycl

ing

;to

tal

or

HD

Lch

ole

ster

ol

or

trig

lyce

rid

esin

3-o

r6-

mo

nth

old

off

spri

ng

;b

loo

dp

ress

ure

or

hea

rtra

te;

mes

ente

ric

arte

ryd

iam

eter

Sp

rag

ue-

Daw

ley

rat

fed

soy

and

alfa

lfa-

free

die

t;D

ams

trea

ted

dai

lyb

yg

avag

ew

ith

0,10

,50

,10

0,15

0,20

0m

g/

kg

bw

/d

ayso

yis

ofl

avo

nes

(80%

,g

enis

tin

:d

aid

zin

:g

lyci

tin

513

:5:2

)fr

om

PN

D5

to10

Die

tsco

nta

inin

gso

yis

ofl

avo

nes

:m

ute

rin

ew

eig

ht

(Z15

0m

g/

kg

bw

/d

ay);m

end

om

etri

alth

ick

nes

s(Z

150

mg

/k

gb

w/

day

);m

thic

kn

ess

of

ute

rin

elu

men

(Z10

0m

g/

kg

bw

/d

ay);m

ov

aria

nw

eig

ht

(Z10

0m

g/

kg

bw

/d

ay);m

seru

mes

trad

iol

(Z50

mg

/k

gb

w/

day

);k

seru

mp

rog

este

ron

e(1

00an

d20

0m

g/

kg

bw

/d

ay;m

inte

nsi

tyo

fP

CN

Ast

ain

ing

ino

var

yan

du

teru

s(Z

150

mg

/k

gb

w/

day

);k

PR

mR

NA

exp

ress

ion

ino

var

y(Z

150

mg

/k

gb

w/

day

);m

ER

mR

NA

exp

ress

ion

ino

var

y(Z

150

mg

/k

gb

w/

day

);k

ER

mR

NA

exp

ress

ion

inu

teru

s(Z

150

mg

/k

gb

w/

day

)

Liu

etal

.(2

008)

Hig

h(o

ral)

No

effe

ct:

pu

pw

eig

ht;

nu

mb

ero

fu

teri

ne

gla

nd

sW

ista

rra

tfe

dca

sein

-bas

edd

iet

or

sam

ed

iet

enri

ched

wit

h0.

87m

g/

gto

tal

iso

flav

on

es[i

sofl

av

on

ein

tak

eo

fB

40

mg

/bw

/day

]d

uri

ng

ges

tati

on

and

lact

atio

n.

At

wea

nin

g,

hal

fo

fth

eF

1p

up

sfr

om

each

mat

ern

ald

iet

gro

up

wer

eas

sig

ned

toei

ther

the

con

tro

ld

iet

or

iso

flav

on

een

rich

edd

iet

for

ato

tal

of

4tr

eatm

ent

gro

up

s(C

-C,

C-I

F,IF

-C,

IF-I

F)

F1

gen

erat

ion

:m

bo

dy

wei

gh

to

fal

lra

tsre

ceiv

ing

iso

flav

on

een

rich

edd

iet;m

ute

rin

ew

eig

ht

fro

m6

to18

mo

nth

s,b

ut

no

tat

24m

on

ths

(IF

-C,

IF-I

Fg

rou

ps)

;p

rolo

ng

edp

erio

do

fin

crea

sin

gb

on

em

iner

ald

ensi

tyo

rB

MD

(IF

-C,

IF-I

Fg

rou

ps)

;m

tota

lri

gh

tfe

mu

rB

MD

and

dis

tal

fem

ur

met

aph

yse

alzo

ne

BM

Dat

24m

on

ths

(IF

-C,

IF-I

Fg

rou

ps)

;m

bo

ne

stre

ng

thw

ith

age

(IF

-C,

IF-I

Fg

rou

ps)

Mar

do

net

al.

(200

8)L

imit

ed(o

ral)

No

effe

ct:

age

atw

hic

hp

eak

bo

ne

mas

sw

asac

hie

ved

;fe

mo

ral

size

;p

lasm

ao

steo

calc

in;

uri

ne

deo

xy

py

rid

ino

lin

e;d

ista

lfe

mu

rd

iap

hy

seal

zon

eB

MD

Lo

ng

Ev

ans

rat;

off

spri

ng

of

dam

sfe

da

die

to

f0,

5,50

,50

0,o

r10

00p

pm

iso

flav

on

esfr

om

GD

12u

nti

lw

ean

ing

atP

ND

21

F1

off

spri

ng

of

dam

sfe

dd

iets

con

tain

ing

iso

flav

on

es:m

PN

D5

bo

dy

wei

gh

to

fm

ale

pu

ps

(5an

d50

pp

m);m

PN

D21

bo

dy

wei

gh

to

fm

ales

(5,

50an

d10

00p

pm

);m

PN

D5

ano

gen

ital

dis

tan

ce(A

GD

)in

mal

ep

up

s(5

,50,

and

500

pp

m)

[AG

Dd

iffe

ren

ces

wer

en

ot

app

aren

tw

hen

no

rmal

ized

for

the

pu

pb

od

yw

eig

hts

];m

PN

D21

test

icu

lar

wei

gh

t,ab

solu

tep

aire

d(Z

5p

pm

);m

test

icu

lar

wei

gh

t,re

lati

ve

(Z50

pp

m)

PN

D21

;m

test

icu

lar

wei

gh

t,ab

solu

te(Z

50p

pm

)P

ND

90;m

seru

mte

sto

ster

on

e(

5p

pm

)at

PN

D21

;k

seru

mte

sto

ster

on

e(5

00an

d10

00p

pm

)at

PN

D21

;m

seru

mte

sto

ster

on

ele

vel

san

dsi

gn

ific

antl

yh

igh

erte

stic

ula

rte

sto

ster

on

ese

cret

ion

PN

D90

(100

0);k

test

ost

ero

ne

pro

du

ctio

np

erL

eyd

igce

llw

as(5

00an

d10

00)

PN

D90

;k

ERa

mR

NA

lev

els

of

the

ven

tral

pro

stat

eo

fP

ND

90

Ak

ing

bem

iet

al.

(200

7)L

imit

ed(o

ral)

No

effe

ct:

litt

ersi

ze;

pu

pw

eig

ht;

sex

rati

os;

PN

D90

bo

dy

wei

gh

t;w

eig

hts

of

the

epid

idy

mis

,d

ors

ola

tera

lan

dv

entr

alp

rost

ate,

bu

lbo

ure

thra

lg

lan

ds

and

sem

inal

ves

icle

PN

D90

Wis

tar

rat;

dam

sg

iven

15.5

%so

y-m

eal

die

to

rso

y-f

ree

die

tp

rio

rto

and

du

rin

gm

atin

g,

pre

gn

ancy

,an

dla

ctat

ion

(n5

7–29

,d

epen

din

go

nen

dp

oin

t)

F1

off

spri

ng

of

dam

sfe

dso

y-m

eal

die

t:m

Ser

toli

cell

nu

clea

rv

olu

me

on

PN

D18

;m

sper

mat

ocy

te/

Ser

toli

cell

nu

clea

rv

olu

me

on

PN

D18

and

PN

D25

;kb

od

yw

eig

ht

and

kte

stis

wei

gh

to

nP

ND

90–9

5;m

pla

sma

FS

Ho

nP

ND

90–9

5

Ata

nas

sov

aet

al.

(200

0)L

imit

ed(o

ral)

Wis

tar

rats

;m

ale

off

spri

ng

of

dam

sfe

da

soy

free

or

soy

mea

l-co

nta

inin

gd

iet

du

rin

gg

esta

tio

nan

dla

ctat

ion

(to

tal

iso

flav

on

eco

nte

nt

inb

reed

ing

and

mai

nte

nan

ced

iets

wer

e31

1an

d26

4mg

/g

die

t)

F1

off

spri

ng

of

dam

sfe

dso

y-m

eal

die

t:m

PN

D60

pla

sma

LH

and

pro

lact

in;

Go

rsk

iet

al.

(200

6)L

imit

ed(o

ral)

No

effe

ct:

rep

rod

uct

ive

org

anw

eig

hts

PN

D22

or

PN

D60

;

450 MCCARVER ET AL.

Birth Defects Research (Part B) 92:421–468, 2011

Page 31: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

Sp

rag

ue-

Daw

ley

rats

,tw

ow

eek

so

fag

e[f

ee

dn

ot

des

crib

ed];

sin

gle

dai

lyd

ose

of

gen

iste

in(4

0m

g/

kg

BW

)b

ysc

inje

ctio

nfo

r3

day

s

mex

pre

ssio

nle

vel

so

fg

enes

inim

mat

ure

rat

ute

rus

(m9.

97%

)H

on

get

al.

(200

6)L

imit

ed(p

aren

tera

l)

Lo

ng

Ev

ans

rat;

dam

s(n

55/

gro

up

)g

iven

ph

yto

estr

og

en-c

on

tain

ing

die

t(6

00mg

/g

die

t)o

rp

hy

toes

tro

gen

-fre

efi

shm

eal-

bas

edd

iet

thro

ug

ho

ut

pre

gn

ancy

and

lact

atio

n.

Off

spri

ng

wea

ned

tod

am’s

die

t,ex

cep

tat

PN

D80

wh

eno

ne-

hal

fo

fp

hy

toes

tro

gen

-co

nta

inin

gd

iet

fed

off

spri

ng

wer

esw

itch

edto

ph

yto

estr

og

en-f

ree

die

t

F1

off

spri

ng

of

dam

sfe

dp

hy

toes

tro

gen

-co

nta

inin

gd

iet:

del

ayed

vag

inal

op

enin

g;k

bo

dy

wei

gh

to

nP

ND

50an

d12

0in

mal

ean

dfe

mal

eo

ffsp

rin

g;m

inp

rost

ate

wei

gh

t(a

bso

lute

and

rela

tiv

e);m

SD

N-P

OA

inp

hy

toes

tro

gen

die

tm

ales

com

par

edto

con

tro

lm

ales

and

mal

essw

itch

edfr

om

ph

yto

estr

og

end

iet

top

hy

toes

tro

gen

-fre

ed

iet

atP

ND

80

Lu

nd

etal

.(2

001)

Lim

ited

(ora

l)

Sp

rag

ue-

Daw

ley

rat;

pre

gn

ant

rats

(n5

15/

gro

up

)g

iven

CR

F-1

,a

soy

-bas

edd

iet

(gen

isti

nat

10.2

mg

/10

0g

die

tan

dd

aid

zin

at8.

7m

g/

100

gd

iet)

,or

NIH

-07,

aso

y-f

ree

die

t

F1

off

spri

ng

inso

y-b

ased

die

t(C

RF

-1)

gro

up

:mP

ND

2m

ale

pu

pb

od

yw

eig

ht

on

PN

D2;

mP

ND

21fe

mal

ep

up

bo

dy

wei

gh

t;k

ano

gen

ital

dis

tan

cead

just

edfo

rb

od

yw

eig

ht

infe

mal

es

Mas

uto

mi

etal

.(2

004a

)L

imit

ed(o

ral)

Sp

rag

ue-

Daw

ley

rat;

mal

es(n

56–

12/

gro

up

)fr

om

mu

ltig

ener

atio

nst

ud

yth

atco

nti

nu

edm

ale

off

spri

ng

on

1o

f6

die

tsg

iven

toth

eir

par

ents

:A

IN-9

3G(s

oy

-fr

ee,

case

in-b

ased

die

t),

Co

ntr

ol

die

t1so

yp

rote

in(i

sofl

avo

nes

31.7

mg

/k

gfe

ed),

or

Co

ntr

ol

die

t1so

yp

rote

in1

soy

-iso

flav

on

eco

nce

ntr

ate

(No

vas

oys

)at

36.1

,74

.5,

235.

8,o

r10

46.6

mg

/k

gfe

ed

mT

esti

sw

eig

ht,

PN

D28

in3

hig

hes

tis

ofl

avo

ne

gro

up

s(t

ota

lis

ofl

avo

ne

inta

keZ

2m

g/

kg

bw

/d

ay)

McV

eyet

al.

(200

4a,b

)L

imit

ed(o

ral)

mS

eru

mte

sto

ster

on

ean

dd

ihy

dro

test

ost

ero

ne,

PN

D12

0in

2h

igh

est

iso

flav

on

eg

rou

ps

(to

tal

iso

flav

on

ein

tak

eZ

6.3

mg

/k

gb

w/

day

)m

Tes

ticu

lar

3b-h

yd

rox

yst

ero

idd

ehy

dro

gen

ase

acti

vit

y,P

ND

28,

in2

hig

hes

tis

ofl

avo

ne

gro

up

s[B

ased

on

PN

D28

test

isw

eig

ht:

NO

AE

L1.

2m

g/

kg

bw

/d

ayan

dL

OA

EL

2.0

mg

/k

gb

w/

day

]N

oef

fect

:m

ean

bo

dy

wei

gh

to

rfe

edco

nsu

mp

tio

nat

any

tim

ed

uri

ng

the

stu

dy

;W

ista

r-d

eriv

edra

t;d

ams

(n5

12/

gro

up

)g

iven

assi

gn

edd

iet

du

rin

gp

reg

nan

cyan

dla

ctat

ion

,an

do

ffsp

rin

gw

ean

edto

assi

gn

edd

iet

thro

ug

hP

ND

68.

Die

tas

sig

nm

ents

(dam

/o

ffsp

rin

g)

wer

e:

Eff

ects

com

pare

dto

RM

3/R

M1

Con

trol

diet

:O

du

met

al.

(200

1)L

imit

ed

RM

3/R

M1

(sta

nd

ard

soy

-bas

edd

iets

)A

IN-7

6/A

IN-7

6(s

oy

-an

dal

falf

a-fr

eed

iet)

AIN

-76A

/A

IN-7

6A(s

oy

free

die

td

uri

ng

pre

gn

ancy

and

lact

atio

n):m

age

atte

stis

des

cen

t;k

age

atp

rep

uti

alse

par

atio

n;k

age

ato

nse

to

fv

agin

alo

pen

ing

;P

ND

26fe

mal

es:m

bo

dy

wei

gh

t,u

teri

ne

wei

gh

tan

dv

agin

alw

eig

ht;

PN

D68

mal

es:m

bo

dy

wei

gh

t;m

liv

eran

dk

idn

eyw

eig

ht;k

test

isan

dep

idid

ym

alw

eig

ht;

PN

D12

8m

ales

:mb

od

yw

eig

ht;k

test

isw

eig

ht.

PN

D14

0–14

4fe

mal

es:m

bo

dy

wei

gh

t;m

kid

ney

wei

gh

t;k

ute

rin

ew

eig

ht

RM

3/A

IN-7

6A(s

oy

die

td

uri

ng

pre

gn

ancy

and

soy

free

die

td

uri

ng

lact

atio

n):k

age

atte

stis

RM

3/A

IN-7

6AN

oef

fect

:ey

eo

pen

ing

Glo

bal

2016

/G

lob

al20

16(s

oy

-an

dal

falf

a-fr

eed

iet)

Pu

rin

a50

01/

Pu

rin

a50

01(b

ased

on

soy

bea

ns

and

alfa

lfa)

Wis

tar

rat;

soy

-co

nta

inin

gd

iet,

soy

-fre

ed

iet,

and

soy

-fre

ed

iet

sup

ple

men

ted

wit

hm

eth

ion

ine

and

L-l

ysi

ne

km

atin

gef

fici

ency

for

F0

anim

als;k

mea

nli

ver

wei

gh

tat

60d

ays

inF

1fe

mal

es;m

LH

and

pro

lact

inat

60d

ays;

dif

fere

nce

inte

sto

ster

on

ele

vel

no

tco

nfi

rmed

stat

isti

call

yP

astu

szew

ska

etal

.(2

008)

Lim

ited

No

effe

ct:

feed

inta

ke

and

bo

dy

wei

gh

tfo

rF

0g

ener

atio

n;

acti

vit

yo

fh

epat

icen

zym

es;

tota

lch

ole

ster

ol

Gro

wth

,R

epro

duct

ive

Sys

tem

and

En

docr

ine-

Rel

ated

En

dpoi

nts

(Mou

se)

CD

-1m

ice;

F0

dam

sd

uri

ng

ges

tati

on

and

lact

atio

nan

do

ffsp

rin

gaf

ter

wea

nin

gw

ere

fed

aso

y-b

ased

die

t(P

MI

5008

or

PM

I50

01)

or

soy

-fre

ed

iet

(PM

I5K

96)

F1

off

spri

ng

of

dam

sfe

dso

y-b

ased

die

t(P

MI

5008

or

PM

I50

01)

com

par

edto

soy

-fre

ed

iet

(PM

I5K

96):k

seru

mes

trad

iol

lev

els

infe

tuse

s;m

bir

thw

eig

ht

of

pu

ps;k

PN

D26

and

PN

D90

bo

dy

wei

gh

t(b

ut

no

effe

ctat

PN

D20

);k

ute

rin

ew

eig

ht

and

epit

hel

ial

cell

hei

gh

tin

PN

D20

fem

ales

inre

spo

nse

toes

trad

iol

stim

ula

tio

n;k

ute

rin

ew

eig

ht

and

epit

hel

ial

cell

hei

gh

tin

PN

D26

fem

ales

;la

ter

on

set

of

fert

ilit

yin

fem

ales

(46.

5v

ersu

s44

.7d

ays)

;k

pro

stat

ew

eig

ht

inm

ales

;b

ette

rg

luco

secl

eara

nce

inad

ult

mal

es;

mte

stes

,ep

idid

ym

ides

,se

min

alv

esic

les,

liv

eran

dri

gh

tk

idn

eyw

eig

ht

inm

ales

;k

wei

gh

to

fg

on

adal

and

ren

alfa

tp

ads

inan

imal

s;k

seru

mle

pti

nin

PN

D26

fem

ales

and

PN

D90

inm

ales

and

fem

ales

Ru

hle

net

al.

(200

8)L

imit

ed(o

ral)

451NTP-CERHR EXPERT PANEL REPORT

Birth Defects Research (Part B) 92:421–468, 2011

Page 32: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

Tab

le10

Co

nti

nu

ed

An

imal

mo

del

and

stu

dy

des

ign

En

dp

oin

tsR

efer

ence

Uti

lity

No

effe

ct:

seru

mes

trad

iol

lev

els

pre

gn

ant

dam

s;P

ND

20se

rum

lep

tin

;b

asal

blo

od

glu

cose

lev

els

and

glu

cose

clea

ran

cein

adu

ltfe

mal

es;

mea

np

up

wei

gh

to

rth

en

um

ber

of

pu

ps

pro

du

ced

by

fem

ales

on

eith

erd

iet

C3H

mic

e:F

0g

ener

atio

nfe

da

stan

dar

dco

ntr

ol

die

t[a

ssu

me

dto

con

tain

som

eso

y]

or

aco

ntr

ol

die

t12%

(So

yL

ifes

)su

pp

lem

ent

(IS

Fd

iet)

du

rin

gp

reg

nan

cyan

dla

ctat

ion

;F

1fe

dth

esa

me

die

tsas

thei

rp

aren

tsp

ost

-wea

nin

g

F1

off

spri

ng

inIS

Fd

iet

gro

up

:ac

cele

rate

dv

agin

alo

pen

ing

;k

bo

dy

wei

gh

t,si

zean

dan

og

enit

ald

ista

nce

infe

mal

esat

the

day

of

vag

inal

op

enin

g;k

size

and

bo

dy

wei

gh

to

nP

ND

42;

loss

of

sex

ual

dim

orp

his

min

DN

Am

eth

yla

ton

inli

ver

Gu

erre

ro-

Bo

sag

na

etal

.(2

008)

Lim

ited

(ora

l)

No

effe

ct:p

up

sex

rati

oo

rli

tter

size

;an

og

enit

ald

ista

nce

inm

ales

or

fem

ales

on

PN

D42

;p

up

size

or

wei

gh

tat

PN

D7,

PN

D14

,o

rP

ND

21;

ER

ap

rom

ote

rin

liv

er;

gen

der

dif

fere

nce

so

rw

ith

inm

ales

or

fem

ales

inA

cta1

inp

ancr

eas;

lack

of

met

hy

lati

on

of

c-fo

sp

rom

oto

rH

an-N

MR

Im

ice;

Dam

sfe

dso

yd

iet

or

soy

-fre

ed

iet

du

rin

gp

reg

nan

cyan

dla

ctat

ion

;m

ales

inea

chli

tter

wer

eco

nti

nu

edo

nth

ed

am’s

die

to

rsw

itch

edto

the

op

po

site

die

t;co

llec

tio

nat

2an

d12

mo

nth

so

fag

e(m

ales

)

2m

on

th:

Mak

ela

etal

.(1

995)

Lim

ited

(ora

l)m

coag

ula

tin

gg

lan

dan

dco

mb

ined

pro

stat

elo

be

rela

tiv

ew

eig

hts

inm

ales

fed

aso

yd

iet

afte

rw

ean

ing

,fo

llo

win

ga

soy

-fre

ed

iet

giv

ento

the

dam

du

rin

gp

reg

nan

cyan

dla

ctat

ion

;m

rela

tiv

ew

eig

ht

of

the

pro

stat

elo

bes

wh

enco

mp

ared

tom

ales

pla

ced

on

aso

y-f

ree

die

taf

ter

wea

nin

g,

reg

ard

less

of

wh

ich

die

tth

eir

dam

sh

adb

een

fed

;S

oy

feed

ingm

rela

tiv

ew

eig

ht

of

coag

ula

tin

gg

lan

d(4

6%),

do

rsal

ater

alp

rost

ate

(81%

)12

mo

nth

:S

oy

feed

ingm

rela

tiv

ere

pro

du

ctiv

eo

rgan

wei

gh

ts-

ven

tral

pro

stat

e(4

0%),

coag

ula

tin

gg

lan

d(6

0%),

do

rsal

pro

stat

e(6

3%),

sem

inal

ves

icle

(35%

)an

dte

stes

(20%

);N

oef

fect

:o

nb

od

yw

eig

ht

Gro

wth

,re

prod

uct

ive

syst

eman

den

docr

ine-

rela

ted

endp

oin

ts(n

onhu

man

prim

ate)

Mar

mo

set

mo

nk

eys;

7se

tso

fco

-tw

ins

wh

ere

on

etw

inw

asfe

da

cow

-mil

kb

ased

form

ula

(SM

AG

oldt

)an

dth

eo

ther

was

fed

soy

infa

nt

form

ula

(Wy

soys

)fr

om

day

4o

r5

tod

ay35

to45

;fo

rmu

lau

sew

aso

nly

par

tial

asm

on

key

sal

son

urs

ed(e

stim

ated

tore

sult

inis

ofl

avo

ne

inta

ke

bet

wee

n40

and

87%

of

the

rep

ort

edin

tak

efo

ra

4-m

on

tho

ldh

um

anex

clu

siv

ely

fed

soy

form

ula

)

Eff

ects

inso

yin

fan

tfo

rmu

lag

rou

pu

pto

120

to13

8w

eek

so

fag

e:m

test

isw

eig

ht;m

Ser

toli

cell

and

Ley

dig

cell

nu

mb

ers/

test

isT

anet

al.

(200

6)L

imit

ed(o

ral)

No

effe

ct:

bo

dy

wei

gh

t;w

eig

hts

of

thy

mu

s,sp

leen

,p

rost

ate,

sem

inal

ves

icle

s,p

itu

itar

y;

pen

ile

len

gth

,ti

min

go

fo

nse

to

fp

ub

erty

;p

lasm

ate

sto

ster

on

e;fe

rtil

ity

Mar

mo

set

mal

em

on

key

s;co

-tw

ins

wh

ere

on

etw

inw

asfe

da

cow

-mil

kb

ased

form

ula

(SM

AG

oldt

)an

dth

eo

ther

was

fed

soy

infa

nt

form

ula

(Wy

soys

)fr

om

day

4–5

tod

ay35

–45

(n5

7–14

twin

pai

rs,

dep

end

ing

on

age

of

eval

uat

ion

);fo

rmu

lau

sew

aso

nly

par

tial

asm

on

key

sal

son

urs

ed(e

stim

ated

tore

sult

inis

ofl

avo

ne

inta

ke

ofB

1.6–

3.5

mg

/k

gb

w/

day

)

Eff

ects

inso

yin

fan

tfo

rmu

lag

rou

pu

pto

PN

D35

–45:

kp

lasm

ate

sto

ster

on

eat

PN

D35

–45

;m

Ley

dig

cell

s/te

stis

atP

ND

35–4

5S

har

pe

etal

.(2

002)

Lim

ited

(ora

l)

No

effe

ct:

bo

dy

wei

gh

t;fo

rmu

lain

tak

e;p

lasm

ate

sto

ster

on

eP

ND

18–2

0;te

stis

wei

gh

t,S

erto

lice

llan

dg

erm

cell

nu

mb

er/

test

isat

PN

D35

–45;

17a-

hy

dro

xy

lase

/C

17–20

lyas

est

ain

ing

inte

stis

and

imm

un

op

osi

tiv

ece

lls

forb-

sub

un

itL

Ho

rF

SH

inp

itu

itar

yse

ctio

ns

atP

ND

35–4

5

Mam

mar

ygl

and

deve

lopm

ent

and

carc

inog

enes

isS

pra

gu

e-D

awle

yra

tfe

dA

IN-9

3Gd

iet

inw

hic

hso

yb

ean

oil

was

rep

lace

db

yco

rno

ilan

dth

ep

rote

inso

urc

ew

asei

ther

case

in,

wh

ey,

or

soy

pro

tein

iso

late

con

tain

ing

iso

flav

on

es43

0m

g/

kg

die

t(g

enis

tein

276

mg

/k

gd

iet

and

dai

dze

in13

2m

g/

kg

die

t)[B

20

.4g

en

iste

inm

g/k

gb

w/d

ay].

At

wea

nin

g,

the

F1

and

F2

off

spri

ng

wer

efe

dth

esa

me

die

tsas

thei

rd

ams

and

con

tin

ued

tore

ceiv

e

F1

and

/o

rF

2fe

mal

esin

soy

-pro

tein

gro

up

:k

bo

dy

wei

gh

tg

ain

at8

wee

ks

(bo

thg

ener

atio

ns)

;ac

cele

rate

dv

agin

alo

pen

ing

(PN

D37

vs

PN

D38

);m

late

ncy

tod

evel

op

mam

mar

yg

lan

dtu

mo

rs,

inte

rms

of

the

nu

mb

ero

fp

ost

-tre

atm

ent

day

sfo

r50

%o

fra

tsto

dev

elo

pat

leas

t1

tum

or

(F1

and

F2,

com

par

edto

case

in);k

late

ncy

tod

evel

op

mam

mar

yg

lan

dtu

mo

rs,

inte

rms

of

the

nu

mb

ero

fp

ost

-tre

atm

ent

day

sfo

r50

%o

fra

tsto

dev

elo

pat

leas

t1

tum

or

(F2,

com

par

edto

wh

ey);k

per

cen

tag

eo

fra

tsw

ith

at

Hak

kak

etal

.(2

000)

Lim

ited

(ora

l)

452 MCCARVER ET AL.

Birth Defects Research (Part B) 92:421–468, 2011

Page 33: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

the

die

tsth

rou

gh

ou

tth

eir

life

tim

es.

At

PN

D50

,ra

tsg

avag

edw

ith

80m

g/

kg

DM

BA

and

the

dev

elo

pm

ent

of

pal

pab

lem

amm

ary

tum

ors

asse

ssed

leas

t1

mam

mar

ytu

mo

rat

the

end

of

the

stu

dy

(F2);m

tum

ors

/ra

tco

mp

ared

tow

hey

die

tg

rou

p(F

2)

No

effe

ct:

rela

tiv

eo

rgan

wei

gh

t;es

tro

us

cycl

e;su

cces

sfu

lb

reed

ing

;se

xra

tio

;li

tter

size

;ti

me

tofi

rst

tum

or;

%o

fra

tsw

ith

aden

oca

rcin

om

ao

rtu

mo

rw

ith

intr

adu

ctal

pro

life

rati

on

;m

edia

ntu

mo

rv

olu

me;

tum

ors

/ra

tco

mp

ared

toca

sein

die

tg

rou

pS

pra

gu

e-D

awle

yra

t;fe

mal

eF

1o

ffsp

rin

go

fF

0p

aren

tsfe

dA

IN-9

3Gd

iets

con

tain

ing

eith

erca

sein

or

soy

-pro

tein

iso

late

fro

mG

D4

tola

ctat

ion

,at

wea

nin

gfe

mal

esw

ere

wea

ned

toth

ed

iet

of

the

dam

.A

tP

ND

50,

rats

ivin

ject

edw

ith

50m

g/

kg

MN

Uan

dfo

llo

wed

un

til

115

day

sfo

llo

win

gM

NU

trea

tmen

t

Fem

ale

F1

off

spri

ng

of

F0

par

ents

fed

soy

-pro

tein

iso

late

:kin

cid

ence

of

rats

wit

hat

leas

t1

mam

mar

yg

lan

dtu

mo

ran

dm

tum

or

late

ncy

inra

tsfe

dth

eso

y-p

rote

ind

iet;k

inci

den

ceo

fd

uct

alca

rcin

om

ain

situ

bu

ta

hig

her

inci

den

ceo

fin

filt

rati

ng

du

ctal

carc

ino

ma;

mP

Ran

dH

ER

-2/n

eu(i

nv

olv

edin

cell

pro

life

rati

on

)g

ene

exp

ress

ion

:k

seru

mp

rog

este

ron

ele

vel

s;m

apo

pto

tic

cell

sin

anM

CF

-7cu

ltu

rein

cub

ated

wit

hse

ra

Sim

men

etal

.(2

005)

Lim

ited

(ora

l)

No

effe

ct:

cell

pro

life

rati

on

or

apo

pto

sis;

seru

mes

trad

iol

FV

Bm

ice

fed

(I)

con

tro

ld

iet

(F1

fem

ales

),(I

I)27

0m

gis

ofl

avo

ne/

kg

die

tth

rou

gh

ou

tla

ctat

ion

(PN

D0–

21),

(III

)27

0m

gis

ofl

avo

ne/

kg

die

tfr

om

wea

nin

gth

rou

gh

the

end

of

the

stu

dy,

and

(IV

)E

2d

uri

ng

the

lact

atio

np

erio

d

Eff

ects

inis

ofl

avo

ne-

trea

ted

gro

up

s(G

rou

ps

IIan

d/

or

III)

:m

bra

nch

ing

inm

amm

ary

tree

s(G

rou

ps

II/

III)

;m

ino

ver

all

bra

nch

ing

inju

ven

ile

mam

mar

yg

lan

d(P

ND

28;

Gro

up

sII

/II

I));m

TE

Baf

ter

po

stw

ean

ing

iso

flav

on

etr

eatm

ent

(Gro

up

III)

;k

TE

Bs

atP

ND

42–4

3af

ter

po

stw

ean

ing

(Gro

up

sII

I)

Th

om

sen

etal

.(2

006)

Lim

ited

(ora

l)

No

effe

ct:

PN

Ds

70–7

3;le

vel

so

fp

lasm

aes

trad

iol;

gen

eex

pre

ssio

np

rofi

les;

gen

eex

pre

ssio

nle

vel

wh

enco

mp

arin

gp

ost

wea

nin

gis

ofl

avo

ne

exp

osu

reto

E2

exp

osu

re

Bra

inan

dbe

havi

orL

on

gE

van

rat;

pre

gn

ant

dam

sfe

da

die

tco

nta

inin

gp

hy

toes

tro

gen

gly

cosi

des

600mg

/g

die

t(p

hy

to-6

00)

or

ap

hy

toes

tro

gen

-fre

ed

iet

thro

ug

ho

ut

the

ges

tati

on

and

lact

atio

np

erio

d.

Off

spri

ng

wer

ew

ean

edto

the

sam

ed

iet

asth

ed

am.

On

PN

D80

,h

alf

the

off

spri

ng

fed

ph

yto

-600

wer

esw

itch

edto

ap

hy

toes

tro

gen

-fre

ed

iet

for

40d

ays

pri

or

toco

llec

tio

nat

PN

D12

0

Eff

ects

inp

hy

to-6

00):k

bo

dy

wei

gh

t,ab

solu

tep

rost

ate

wei

gh

tan

dre

lati

ve

pro

stat

ew

eig

ht

PN

D75

;mA

VP

Vn

ucl

eus

vo

lum

ein

mal

essw

itch

edto

the

ph

yto

estr

og

en-f

ree

die

to

nP

ND

80

Lep

har

tet

al.

(200

1)L

imit

ed(o

ral)

No

effe

ct:

bra

inar

om

atas

eac

tiv

ity

inA

PV

Nan

dan

tero

ven

tral

per

iven

tric

ula

rn

ucl

eus

vo

lum

ein

fem

ales

un

affe

cted

by

chan

ge

ind

iet,

PN

D11

0;se

xu

ald

imo

rph

ism

inA

VP

Vv

olu

me;

Lo

ng

Ev

ans

rat;

Dam

sg

iven

ph

yto

estr

og

en-c

on

tain

ing

die

t(6

00mg

/g

die

t)o

rp

hy

toes

tro

gen

-fre

efi

shm

eal-

bas

edd

iet

thro

ug

ho

ut

pre

gn

ancy

and

lact

atio

n.

Off

spri

ng

wea

ned

tod

am’s

die

t

F1

off

spri

ng

of

dam

sfe

dp

hy

toes

tro

gen

-co

nta

inin

gd

iet:k

PN

D50

bo

dy

wei

gh

t;m

PN

D50

wat

erin

tak

e;m

tim

esp

end

ino

pen

arm

san

dn

um

ber

of

entr

ies

into

the

op

enar

ms

of

elev

ated

plu

s-m

aze

app

arat

us

Lu

nd

and

Lep

har

t(2

001)

Lim

ited

(ora

l)

Sp

rag

ue-

Daw

ley

rats

;D

ams

fed

ap

hy

toes

tro

gen

con

tain

ing

die

t(2

00mg

/g

die

t,g

enis

tein

95mg

/g

,g

lyci

tin

17mg

/g

,an

dd

aid

zein

82mg

/g

)o

rp

hy

toes

tro

gen

free

die

tfr

om

GD

0–20

Fet

use

so

fd

ams

fed

ph

yto

estr

og

enco

nta

inin

gd

iet:k

calb

ind

inp

rote

inex

pre

ssio

nin

the

med

ial

bas

alh

yp

oth

alam

us

and

pre

op

tic

area

infe

mal

es(a

nd

dis

pla

yed

mo

reo

fa

sex

ual

dim

orp

his

mco

mp

ared

toan

imal

sin

the

ph

yto

estr

og

en-f

ree

die

tg

rou

p);

Tay

lor

etal

.(1

999)

Lim

ited

(ora

l)

No

effe

ct:

litt

ersi

ze,

ano

gen

ital

dis

tan

ce,

feta

lb

od

yw

eig

ht;

calb

ind

inp

rote

inex

pre

ssio

nin

mal

es

Oth

er/M

echa

nis

tic

Fem

ale

New

Zea

lan

dra

bb

its

(8m

on

ths

old

)fe

d(G

rou

p1)

soy

and

alfa

lfa

free

die

t(G

rou

p2)

soy

and

alfa

lfa

free

die

tp

lus

5m

g/

kg

bw

/d

ayay

of

soy

iso

flav

on

es(I

SG

O5)

,(G

rou

p3)

aso

yan

dal

falf

afr

eed

iet,

and

(Gro

up

4)d

iet

con

tain

ing

18%

soy

mea

lp

lus

aco

rnst

arch

pla

ceb

o(S

1)

(B13

mg

/k

gb

w/

day

ayo

fis

ofl

avo

nes

).P

up

sw

ean

edat

5w

eek

so

ldan

dfe

dsa

me

die

tas

mo

ther

kw

eig

ht

inIS

F20

gro

up

at13

wee

ks

of

age;

kfo

od

con

sum

pti

on

inIS

F20

gro

up

at13

wee

ks

of

age

Car

do

soan

dB

ao(2

007)

Lim

ited

(ora

l)

No

effe

ct:

org

anw

eig

hts

;h

isto

pat

ho

log

ical

dif

fere

nce

sin

the

test

eso

rac

cess

ory

sex

gla

nd

s;ag

eth

atm

ales

exh

ibit

edth

em

ou

nti

ng

refl

exo

rin

the

tim

eo

fre

acti

on

;

Rab

bit

s;P

reg

nan

td

oes

fed

(1)

con

tro

ld

iet

(aso

yan

dal

falf

afr

eed

iet)

,(2

)co

ntr

ol

die

tsu

pp

lem

ente

dw

ith

10m

g/

kg

bw

/d

ayay

of

soy

iso

flav

on

es,(

3)co

ntr

ol

die

tsu

pp

lem

ente

dw

ith

20m

g/

kg

bw

/d

ayay

iso

flav

on

es,

or

(4)

ad

iet

con

tain

ing

18%

soy

mea

l

No

effe

ct:

on

dam

feed

inta

ke,

du

rati

on

of

ges

tati

on

,or

litt

ersi

ze;o

ffsp

rin

gb

od

yw

eig

ht,

his

top

ath

olo

gy

of

the

test

eso

rep

idid

ym

ides

;o

rgan

wei

gh

ts;

fem

iniz

atio

no

rd

emas

culi

niz

atio

n;

mal

ese

xu

alb

ehav

ior;

ejac

ula

tev

olu

me;

sper

mm

oti

lity

,v

igo

r,co

nce

ntr

atio

n

Car

do

soan

dB

ao(2

008)

Lim

ited

(ora

l)

453NTP-CERHR EXPERT PANEL REPORT

Birth Defects Research (Part B) 92:421–468, 2011

Page 34: NTP-CERHR expert panel report on the developmental toxicity of soy infant formula

Tab

le10

Co

nti

nu

ed

An

imal

mo

del

and

stu

dy

des

ign

En

dp

oin

tsR

efer

ence

Uti

lity

Ou

tbre

dC

D-1

mic

efe

dA

IN-9

3Gd

iets

dev

oid

of

estr

og

enic

com

po

un

ds;

F1

off

spri

ng

trea

ted

by

scin

ject

ion

wit

hco

rno

il,

dai

dze

in(2

mg

/k

gb

w/

day

ay),

gen

iste

in(5

mg

/k

gb

w/

day

ay),

dai

dze

inp

lus

gen

iste

in(2

mg

dai

dze

in1

5m

gg

enis

tein

/k

g/

day

),o

rd

ieth

yls

tilb

estr

ol

(2m

g/

kg

bw

/d

ayay

);ad

min

iste

red

each

mo

rnin

gfr

om

PN

D1

toP

ND

5(5

do

ses)

var

iety

of

effe

cts

on

bo

ne

mea

sure

s,i.

e.,

bo

ne

min

eral

con

ten

t,b

on

em

iner

ald

ensi

ty,

mic

roar

chit

ectu

reth

atw

ere

inte

rpre

ted

as‘‘

po

siti

ve’

’ef

fect

sal

tho

ug

hth

eco

mb

inat

ion

of

gen

iste

inan

dd

aid

zein

was

no

tco

nsi

der

edto

hav

ea

gre

ater

ben

efit

than

the

ind

ivid

ual

trea

tmen

ts

Kal

ud

jero

vic

etal

.(2

009)

Lim

ited

(par

ente

ral)

No

effe

ct:

bo

dy

wei

gh

t

Pig

lets

(n5

16fr

om

4li

tter

s)ra

nd

om

lyas

sig

ned

48%

soy

bea

nm

eal-

bas

edli

qu

idd

iet

or

cow

-mil

kb

ased

die

t;p

rote

inso

urc

eco

nti

nu

edaf

ter

wea

nin

gu

nti

l56

day

so

fag

e

kb

od

yw

eig

ht

gai

nat

28d

ays

of

age;

inte

stin

alv

illi

sho

rten

edat

28b

ut

no

t56

day

so

fag

e;m

IgG

tite

rsto

soy

inb

oth

age

gro

up

so

fp

igle

tsfe

dso

yb

ean

com

par

edto

mil

k-

pro

tein

die

ts

Li

etal

.(1

990)

Lim

ited

(ora

l)

No

effe

cts

of

die

to

nse

rum

con

cen

trat

ion

so

fzi

nc,

sele

niu

m,

iro

n,

and

cop

per

wer

ed

etec

ted

at28

and

56d

ays

of

age.

;N

osi

gn

ific

ant

dif

fere

nce

sin

skin

thic

kn

ess

foll

ow

ing

intr

ader

mal

inje

ctio

no

fso

yo

rm

ilk

pro

tein

sw

ere

ob

serv

edb

etw

een

the

soy

bea

n-

and

mil

k-d

iet

gro

up

sat

27an

d55

day

so

fag

e;o

nb

last

og

enic

resp

on

ses

of

per

iph

eral

or

inte

stin

ally

mp

ho

cyte

sco

llec

ted

atei

ther

age

and

cult

ure

dw

ith

pu

rifi

edso

yp

rote

ins,

ph

yto

hem

agg

luti

nin

,o

rp

ok

ewee

dS

pra

gu

e-D

awle

yra

ts;

Ex

per

imen

t1:

Pre

gn

ant

rats

fed

AIN

-93G

(CA

S)

die

t.O

nP

ND

15li

tter

sas

sig

ned

to:

con

tro

l(C

AS

)d

iet,

SP

I1d

iet

(286

mg

/k

gg

enis

tein

and

226

mg

/k

gd

aid

zein

,80

mg

tota

lis

ofl

avo

nes

/k

gB

W/

day

),S

PI-

die

t,C

1G

die

t(2

50m

g/

kg

gen

iste

in),

C1

Gd

iet

(250

mg

/k

gd

aid

zein

);p

up

sfe

dto

PN

D33

Eff

ects

inS

PI

die

tg

rou

pco

mp

ared

toca

sein

con

tro

l:m

Ser

um

gen

iste

inle

vel

so

fm

ale

rats

inth

eC

1G

die

tg

rou

p(2

700

nm

ol/

lite

r)th

anth

eS

PI1

die

tg

rou

p(8

08n

mo

l/li

ter)

atP

ND

50;k

bo

dy

wei

gh

tan

dse

rum

IGF

-1co

nce

ntr

atio

ns,

and

alte

red

gen

eex

pre

ssio

np

atte

rnw

ith

ano

ver

all

pat

tern

of

incr

ease

dex

pre

ssio

no

fh

epat

icg

enes

reg

ula

ted

by

PP

ARa,

PP

ARg,

and

LX

Ra

and

dec

reas

edex

pre

ssio

no

fg

enes

reg

ula

ted

by

SR

EB

P-1

c

Ro

nis

etal

.(2

009)

Lim

ited

(ora

l)

Ex

per

imen

t2:

Mal

era

tsre

ceiv

edA

IG-9

36(C

AS

die

t),

Wes

tern

case

ind

iet,

or

Wes

tern

SP

I1d

iet

fro

mP

ND

24to

64

mw

eig

ht

gai

n,

per

cen

tb

od

yfa

t,p

erce

nt

liv

erw

eig

ht;m

seru

min

suli

nco

nce

ntr

atio

n;m

insu

lin

sen

siti

vit

y;m

exp

ress

ion

of

hep

atic

gen

esre

gu

late

db

yP

PA

Ra,

PP

ARg,

and

LX

Ra;

kex

pre

ssio

no

fg

enes

reg

ula

ted

by

SR

EB

P-1

cA

du

ltfe

mal

ecy

no

mo

lgu

sm

on

key

s(n

519

)an

do

ffsp

rin

g(n

525

)fe

dty

pic

alA

mer

ican

die

t(T

AD

)d

iet

wit

hp

rote

ind

eriv

edfr

om

soy

or

TA

Dd

iet

wit

hth

ep

rote

ind

eriv

edfr

om

case

in-l

acta

lbu

min

.O

ffsp

rin

gco

nti

nu

edT

AD

die

tfe

dto

mo

ther

saf

ter

wea

nin

g.T

AD

soy

die

tp

rov

ided

iso

flav

on

eag

lyco

ne-

equ

ival

ent

do

seo

f18

0m

g/

mo

nk

ey/

day

(B40

–50%

gen

iste

in,

40%

dai

dze

in,

and

10–1

5%g

lyci

tein

)

mse

rum

iso

flav

on

eco

nce

ntr

atio

nin

TA

Dso

yd

iet

mo

nk

eys;

(Off

spri

ng

con

sum

ing

TA

Dca

sein

had

sim

ilar

iso

flav

on

eco

nce

ntr

atio

ns

toad

ult

sco

nsu

min

gT

AD

case

in,

bu

to

ffsp

rin

gco

nsu

min

gT

AD

soy

had

hig

her

con

cen

trat

ion

sth

anth

ead

ult

fem

ales

con

sum

ing

TA

Dso

y);k

fru

cto

sam

ine

con

cen

trat

ion

s;k

bo

dy

wei

gh

tat

1an

d2

yea

rso

fag

e(o

ffsp

rin

g);m

insu

lin

inm

ales

com

par

edw

ith

fem

ales

;m

HD

LC

infe

mal

esco

mp

ared

wit

hm

ales

;k

glu

cose

AU

Can

dfa

ster

dis

app

eara

nce

of

glu

cose

(off

spri

ng

);k

insu

lin

resp

on

ses

tog

luco

sech

alle

ng

e

Wag

ner

etal

.(2

009)

Lim

ited

(ora

l)

No

effe

ct:

bo

dy

wei

gh

t,T

C,

TG

,ap

oB

-C,

glu

cose

(ad

ult

s);

bo

dy

wei

gh

tat

bir

th(o

ffsp

rin

g);

HD

LC

con

cen

trat

ion

;fa

stin

gg

luco

sean

din

suli

nco

nce

ntr

atio

n

� Th

ete

rmu

tili

tyre

fers

toth

eap

pli

cab

ilit

yto

the

pu

rpo

seo

fd

raw

ing

con

clu

sio

ns

on

wh

eth

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The majority of oral exposure studies reported no effectson anogenital distance after adjustment for body weightin male and female rats following genistein doses up to180 mg/kg bw/day (doses in offspring) administeredduring gestation, lactation, and/or postweaning develop-ment (Delclos et al., 2001; You et al., 2002a; Masutomiet al., 2003; McClain et al., 2007). Furthermore, a shorteranogenital distance, adjusted for body weight, wasreported in F1 male and F1 and F2 female rats on PND2 in a multigeneration study that included exposuresduring prenatal and postnatal development at dietarydoses of 51 mg/kg bw/day (Delclos et al., 2009). Incontrast, longer anogenital distance at birth was reportedfor female rats exposed to a diet containing both genisteinand daidzein (16 mg genistein and 14 mg daidzein per100 g of feed) during gestation, lactation, and postweaningdevelopment (Casanova et al., 1999).

Most studies reported no effect on age at preputialseparation at dietary doses up to 180 mg/kg bw/daygenistein in offspring (Casanova et al., 1999; Delcloset al., 2001; Masutomi et al., 2003; Takagi et al., 2004)or 100 mg/kg bw/day by gavage (Nagao et al., 2001)following direct or indirect exposure during the gesta-tional, lactational, and/or postweaning periods. How-ever, a dietary dose of 84 mg/kg bw/day genistein(in offspring) enhanced the effect of methoxychlor indelaying preputial separation when administered GD1 -PND 21 (You et al., 2002a).

Effects of developmental exposure to genistein on pupweight were variable; however, few studies reported anassociation with lower fetal body weight (McClain et al.,2007), lower body weight of male and/or female pupsduring lactation (Dalu et al., 2002, 2008), and lowerpostweaning or adult body weight or weight gain inmales and/or females (Awoniyi et al., 1998; Delclos et al.,2001; Nagao et al., 2001; Masutomi et al., 2003; Nagaoet al., 2008) at oral doses of 35 to 180 mg/kg bw/daygenistein.

Mammary gland development and carcinogenesisMouse: No effects on mammary growth or differ-

entiation in adult mice were reported following gavageexposure of their dams with up to 10 mg/kg bw/dayduring mid gestation through lactation (Fielden et al.,2002). Two studies examined the effects of genisteininjection in CD-1 mice. In a single dose study, Hilakivi-Clarke (1998) administered 0.7 to 0.8 mg/kg bw/day onGD 15 to 20 to pregnant dams and measured morpho-logical changes in the mammary gland at variouspostnatal times in the female offspring. These investiga-tors found significantly higher mammary gland epithe-lial area on PND 35 (but not PND 25 or PND 46; and apersistently higher density of terminal end buds whenmeasured on PND 35 and 45. Padilla-Banks et al. (2006)administered 0, 0.5, 5, or 50 mg/kg bw/day on PND 1 to5 and reported higher mammary gland ductal elongationat 6 weeks. The physiological relevance of effects theyobserved at the highest exposures 50 mg/kg bw/day isuncertain. However, lower numbers of terminal endbuds (at 6 weeks) reduced alveolar development (LOEL5 mg/kg bw/day), and increased mammary gland PRand ERb and lower ERa expression levels also werereported (occurred at LOEL 0.5 mg/kg bw/day). Neitherof these studies included assessments of mammarycarcinogenesis but higher numbers of terminal end budsis generally associated with an increased susceptibility to

mammary neoplasia (Hilakivi-Clarke et al., 1999a). Thechanges reported in the normal mammary glands at thehigher doses and later exposures by Padilla-Banks et al.(2006) are generally associated with a reduced suscepti-bility to mammary carcinogenesis. The use of singledoses and the route of administration (injection) arelimiting factors for several of the studies noted above.

Rat: Hypertrophy/hyperplasia of mammary struc-tures was reported following dietary genistein exposureduring periods including mid-to-late gestation and/orthe neonatal stage, at doses Z100 ppm in males(Z5.7 mg/kg bw/day in dams and 7–12 mg/kg bw/day in offspring) (Delclos et al., 2001; Latendresse et al.,2008, 2009) and 1250 ppm in females (Z83 mg/kg bw/day in dams and 180 mg/kg bw/day in offspring;Delclos et al., 2001; Takagi et al., 2004). Higher ductalbranching of the mammary glands was also reported in22 day-old male rats that had been exposed to 84 mg/kgbw/day genistein (dose in offspring) from GD 1 to PND22 (You et al., 2002a).

Smaller numbers of terminal end buds/ducts andgreater numbers of lobules in mammary glands werereported in adult female rats that received genistein by scinjection during development (Lamartiniere et al.,1995a,b; Murrill et al., 1996). Inconsistent effects onmammary structures were observed in adult rats thatwere exposed to genistein through diet during thedevelopmental period, with one study reporting lowernumbers of terminal end buds and lobules (Fritz et al.,1998) and another study reporting no effects onmammary structures of females (You et al., 2002b).Numbers of chemically induced mammary tumors werelower in rats sc treated during postnatal developmentwith 500 mg/kg bw/day genistein (Lamartiniere et al.,1995a,b; Murrill et al., 1996). In the only oral dose studyexamining the effects of genistein exposure on chemi-cally induced mammary tumors, dietary exposure toZ25 ppm genistein (B2.2 mg/kg bw/day) during gesta-tion and lactation reduced dimethylbenzanthracene-induced tumorignicity in adult females (Fritz et al., 1998).

Males: A multigenerational, dose response study inmale rats reported mammary gland hyperplasias at thetermination of the study on PND 140 in both the F1 andF2 generations (LOEL 5 100 ppm; Latendresse et al.(2009). Up to the highest dose tested (500 ppm; all dosesadministered p.o.) no effects were reported with respectto mammary gland neoplasia or ductal hyperplasia. Youet al. (2002) reported greater branching and numbers ofterminal end buds and lateral buds in the mammaryglands of male offspring (dams exposed orally to 0, 25, or800 ppm during pregnancy and lactation) that were ofborderline significance (p 5 0.06) at 300 ppm and signi-ficant at 800 ppm exposure (You et al., 2002b). Dietaryexposure from GD0 through gestation and lactation(offspring on same diet after weaning) to 0, 300, or800 ppm genistein produced greater glandular size(LOEL 5 300 ppm) in male offspring (Wang et al., 2006).

Females–GD0 through lactation exposures: Fritz(1998) reported no effects on chemically induced mam-mary carcinogenesis in rats exposed to dietary genistein(0, 2.2, 22 mg/kg bw/day during pregnancy and lacta-tion). Exposure (parenteral) to 1.5 mg/kg bw/day on GD15 to 20 (but not 0.5 mg/kg bw/day) was associatedwith a higher incidence of mammary tumors (DMBA;B40 mg/kg bw; PND 50) and greater mammary gland of

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total ER binding (measured on PND 50) fHilakivi-Clarke, 1999 x173g. Hilakivi-Clarke f, 2002 x31g adminis-tered 1 to 1.5, 10 to 15, or 20 to 30 mg/kg bw/day duringpregnancy and lactation and reported lower numbers oflobules, higher numbers of terminal end buds, andhigher numbers of mammary tumors (DMBA; B50 mg/kg; PND 47) only with the highest dose. In a single doselevel study (0.1 mg/kg bw/day, sc, GD 15–20), Hilakivi-Clarke (1999b) reported a higher incidence of mammarytumors in F1 offspring (DMBA; B50 mg/kg; PND45)associated with a higher number of mammary ERbinding sites (measured on PND 35) and lower proteinkinase C activity (PND45 but not PND 21)–experiment 1;and a higher incidence of mammary tumors and shorterlatency–experiment 2.

Females–postnatal exposures: Subcutaneous admin-istration of 10 mg/kg bw/day genistein on PND 2 to 8showed evidence of lactation with cystic ductal dilation,atypical epithelial hyperplasia, microcalcifications, andin situ ductal carcinomas (two of five animals examined)in a study reported by Foster et al. (2004). Hilakivi-Clarkeet al. (1999b) reported lower tumor multiplicity (DMBA;B50 mg/kg; PND45), greater lobular development,lower TEB density, increased alveolar bud densityfollowing parenteral administration of genistein (LOEL0.7–2 mg/kg bw/day). The use of single dose levels, theroute of administration (parenteral), and the occasionaluse of small numbers of animals are limiting factors formany of the studies noted above.

Studies of genistein/soy exposure conducted inrodents were largely designed to test hypotheses relatedto how the physiology of the normal mammary glandmight be modified to affect susceptibility to mammarycarcinogenesis. Few were designed to test a standardtoxicological hypothesis and with the rigor requiredfor detailed toxicological analysis, e.g. dose responsefeatures are often not well represented among the studydesigns. The route of administration and dosing variessignificantly across studies, with some using exposuresor regimens that are not readily seen to be relevant tohuman exposures. Hence, many studies were eitherexcluded or judged to be of limited utility.

Despite the limitations, there are some potential trendsevident in the studies. The potential for an effect of thetiming of exposure on outcome is a relatively consistentobservation when viewed across all studies. Althoughthe precise role of each developmental time of exposureis unclear, there is evidence suggesting that in uteroexposure only may increase later susceptibility tomammary carcinogenesis, while later exposure (birth toonset of sexual maturity) may be protective. Exposureonly during normal adulthood (after sexual maturation)may have no major effect on susceptibility to carcinogen-esis in the mammary gland. The limited data on cross-generational effects are also interesting but insufficient toallow for any definitive conclusion.

It is difficult to derive any overall conclusion on a clearassociation of soy exposure with mammary carcinogenesis.When compared with the limited human data from themeta-analyses, the animal model data support the poten-tial for a modestly protective effect for some exposures,e.g. childhood/adolescent exposure might have a smallreduction in risk. A protective effect of exposure in pre-existing breast cancers is potentially more problematic. Thelimited but possibly more consistent data from in vitro and

in vivo studies using low (perhaps more physiologicallyrelevant) exposures in breast cancer models show thatgenistein can act as an estrogen. Consistent with thisactivity, a small number of studies suggest that genisteinmay reduce responsiveness to antiestrogens or aromataseinhibitors. These data likely explain the increasing practiceamong medical oncologists to advise against soy/isofla-vone consumption for breast cancer patients, as furtherreflected in the guidelines proposed by the AmericanCancer Society (see http://www.cancer.org/docroot/ETO/content/ETO_5_3x_Soybean.asp). For the moment,this would appear to be a reasonable precaution.

Brain and behaviorRat: Treatment with genistein has been reported to

increase the size of the sexually dimorphic nucleus(SDN) of the preoptic area, as quantified by Nisslstaining, in adult female rats. Lewis et al. (2003) observeda greater size of the SDN in adult females following scadministration of 2 mg genistein/kg bw during PND 1 to6 (day of birth was PND 1) followed by oral consumptionof 40 mg genistein/kg bw/day (LOEL and NOEL: 40 and4 mg/kg bw/day oral, respectively) from PND 7 to 21.The dose of genistein increased the SDN in femalesrelative to control; however, it was not as effective as ahigh dose of DES (10 mg/kg bw/day) which produced afemale SDN equal to the size of the control male (Lewiset al., 2003). Faber (1991, 1993) conducted two studies inwhich the SDN was examined (Faber and Hughes, 1991,1993). In the first study, pups were injected (sc) fromPND 1 to 10 with 0, 0.1, or 1 mg of genistein, includingpositive controls DES and Zearalenone. Both DES and1 mg genistein (LOEL 12 mg/kg bw/day oral) increasedthe size of the SDN in females to that of males (Faber andHughes, 1991). In the second study (Faber and Hughes,1993), a range of lower doses (0, 0.001, 0.01, 0.1, 0.2, 0.4,0.5, or 1 mg sc) were administered daily from PND 1 to10. In this study, only the two highest doses of genistein(0.5 and 1 mg; corresponding to dosages of 58 and117 mg/kg bw/day sc, respectively) increased the SDNin adult females. The only other study that simply usedNissl staining to examine the SDN did not find anyeffects of much higher doses of genistein In contrast, scinjections of genistein at 5 or 25 mg (corresponding to 15and 75 mg/kg bw/day) did not affect the size of theSDN; however, the sc injections were given to gestatingdams on GD 16 to 20 so the level of genistein the embryoswere exposed to is unclear (Levy et al., 1995).

Another way to visualize the SDN is by usingimmunocytochemistry to stain the region for Calbindind28k. Scallet et al. (2004) fed dams a casein-based dietsupplemented with 0, 5, 100, or 500 ppm genistein(corresponding to 0, 0.31, 5.7, and 34 mg/kg bw/day;LOEL40.31 mg/kg bw/day oral) from conceptionthrough lactation, and the F1 offspring were continuedon these diets until examination at PND140. Maleoffspring exposed to the genistein treatments had a largerSDN as compared with the control males, while there wasno effect of treatment in female offspring. Patisaul et al.(2007) injected pups on PND 1 to 4 with 0.25 mg ofgenistein (LOEL B100 mg/kg bw/day) and found higherCalbindin-SDN volumes in genistein-treated males inadulthood. In contrast, to the Calbindin result, there wasno effect of genistein on the Nissl-stained SDN in thefemale rats relative to controls. These two studies (Scalletet al., 2004; Patisaul et al., 2007) used Sprague-Dawley rats

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that were fed a base diet of soy-free diet. All the studies inthe previous paragraph involved rats fed standard diet(which contains phytoestrogens and soy), except onestudy (Lewis et al., 2003) that referenced diet R&M No 3(Special Diet Services, Stepfield Witham, Essex) containing100 to 110 ppm genistein. In addition, the other studiesused different rat model; CD (Faber and Hughes, 1991,1993; Levy et al., 1995) and Alderley Park rats (Lewis et al.,2003). Thus, strain/stock and diet might play major roleson the differentiation of the SDN and its sensitivity togenistein. In addition, the data suggest that the classical‘‘biomarker’’ of the SDN, calbindin d28k, is not alwaysinformative for the responses of all the neurons in theSDN. Finally, the finding that genistein exposure canincrease the SDN in males but not in females is not aspredicted if genistein was acting only as an estrogenagonist and speaks to a complexity in the actions ofgenistein.

Another SDN that has been examined is the ante-roventral periventricular nucleus of the hypothalamus(AVPV), which is typically larger in females than inmales. Patisaul et al. (2006) evaluated the AVPV bymeasuring tyrosine hydroxylase (TH) levels by immu-nocytochemistry. Pups received a total of four injectionssc of genistein (0.25 mg; LOEL B100 mg/kg bw/day sc)with one injection administered every 12 hr for the first 2days after birth. On PND 19, the brains were collectedand TH-positive cells were analyzed in the AVPV.Treatment lowered the number of TH cells co-expressingERa in the female brain closer to male cell numbervalues, while genistein increased the number of TH cellsin the AVPV of males closer to female values. These datasuggest that when endogenous estrogens are present (inthe PND 1–2 male) genistein has an anti-estrogenic effect.

Patisaul et al. (2009) reported there was no effect ofgenistein on the number of kisspeptin (KISS) immunor-eactive cells in the AVPV of adult males followinginjections of genistein (10 mg/kg) from PND 1 to 4.In another study (Bateman and Patisaul, 2009), femaleLong Evans rats were treated for the first 4 days afterbirth with estradiol, genistein (same dose as above),either an ERa- or ERb-specific agonist, or equol. Alltreatments were in oil given by sc injections. Inadulthood, females were ovariectomized and givensequential estradiol then progesterone to promote LHrelease. The numbers of co-labelled cfos/GnRH cells waslower in the early genistein-treated females than controls.In addition, kisspeptin immunoreactivity was lower inthe AVPV by the early genistein treatment. The ERbagonist had less of an effect on these measures than theERa agonist. This suggests that genistein can have itsactions via ERa.

Effects of genistein on other aspects of the hypotha-lamic–pituitary–gonad axis have been examined by fewstudies. Masutomi et al. (2004b) fed pregnant rats a dietcontaining genistein (0, 20, 200, and 1000 ppm; NOELrange of 66.6 to 113.1 mg/kg bw/day oral) from GD15until PND10. When pituitaries were analyzed forgonadotropin subtypes at 11 weeks of age, no effect ofgenistein was found. In another study, pregnant damswere fed a diet of 0 or 1000 ppm genistein (LOEL113.1 mg/kg/bw/day oral) from GD15 to PND10. OnPND10, the hypothalami (including the SDN) werecollected and RNA was used for real time RT-PCRdeterminations of PR, ERa, ERb, and SRC-1 (Takagi

et al., 2005). There were sex differences in ERa(females4males) and PR (males4females), but genisteinhad no effect on any of the measures.

Other endpoints and mechanistic studies. Onestudy reported lower thymocyte subsets and changes innatural killer cell activity in rats on PND 22 followingdietary exposure of dams during gestation and lactation(Guo et al., 2002). A second study found changes inthymocyte numbers suggesting augmented cell-mediated immunity in PND 70 rats the dams of whichhad been given dietary genistein during pregnancy andlactation (Klein et al., 2002). The inconsistency in the datadetracts from the utility of the developmental immuno-toxicology data set.

Most of the mechanistic studies used high sc doses.The most widely studied mechanistic effect was expres-sion of estrogen, progesterone, and androgen receptors inreproductive organs of rodents. In studies with gesta-tional and lactational exposure of dams, effects onoffspring were only observed with sc dosing. LowerERa and androgen receptor and increased progesteronereceptor expression were observed following sc injectionof rats with 500 mg/kg bw/dose on 3 days during thelate lactation period (Cotroneo et al., 2001). In mouseovary, increased ERa expression was noted at lowerdoses (r10mg/day) and lower expression was noted at ahigher dose (100mg/pup/day) following neonatal scexposure (Jefferson et al., 2002).

Two studies in which mice were sc injected withgenistein in the neonatal period reported reductions inexpression of testicular ERa (Z7 mg/kg bw) and andro-gen receptor (Z71 mg/kg bw/day) (Adachi et al., 2004),but no effect was reported following maternal dietarygenistein exposure during gestation and lactation at upto 10 mg/kg bw/day (Fielden et al., 2003). In a studyexamining ER expression in rats exposed through dietfrom gestation through weaning or adulthood, resultswere somewhat variable in different generations andoften not dose-related, but lower expressions were notedfor ERa (Z25 ppm) and ERb (Z100 ppm) (Dalu et al.,2002). A transgenic mouse model has been engineered toexpress luciferase activity as a reporter of ER transcrip-tional activity, and studies have shown that oral gavageof genistein to dams on PND4 results in lower luciferaseactivity in the male offspring confirming lactationalexposure to genistein is able to activate ER (Montaniet al., 2008, 2009).

Results of estrogen or progesterone receptor expres-sion in mammary gland following oral or sc exposure inrats were variable, with no obvious patterns related todose or period of exposure observed (Cotroneo et al.,2002; You et al., 2002b; Cabanes et al., 2004). One series ofstudies was interpreted by authors as suggesting thatacute sc exposure of immature animals to genistein500 mg/kg bw results in increased differentiation ofimmature terminal end buds, leading to a greaternumber of lobules, thought to be more resistant tocarcinogens, during adulthood (Lamartiniere, 2000). Itappeared that the effects were mediated through ERs,which regulate both progesterone receptor and EGFreceptor. Upregulation of EGF receptor (EGFR) inimmature rats does not occur through tyrosine phos-phorylation. EGFR is downregulated in adult rats, and ithas been hypothesized that a less active EGF-signalingpathway in adulthood suppresses mammary cancer

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development. A third study reported upregulatedexpression of BRCA1, a tumor suppressor gene involvedin DNA damage repair, following sc exposure of rats togenistein during the lactational period (Cabanes et al.,2004).

Experimental Animal Studies of Soy Formulaor other Soy Exposures During Development

Almost 30 experimental animal studies are summar-ized in Table 10, one study was judged to have highutility and the rest were found to be of limited utility forthe evaluation process.

Growth. The effect of exposure to dietary soy onpup body weight was inconsistent among studies. In astudy by Masutomi et al. (2004a) using Sprague-Dawleyrats, female offspring in the soy-diet group showed aincreased body weight on PND 21, greater body weightgain between PND 10 and 21, and shorter weight-adjusted anogenital distance compared with the controlgroup. Male offspring in the soy-diet group showed anincreased body weight on PND 2 and greater bodyweight gain between PND 10 and 21. In this study,exposure to dietary soy was likely limited to the damssince they were given a soy-based or a soy-free diet untilPND 10, before the time when pups will have eaten solidfood. Increased pup body weights before weaning werealso reported in male rats by Akingbemi et al. (2007), andin both female and male rats by Odum (2001). In thestudies by Akingbemi et al. (2007) and Odum et al.(2001), rats were exposed to soy during gestation andlactation. The body weight was greater in male offspringon PND 5 and PND 21 (Akingbemi et al., 2007), and inboth male and female offspring from birth to PND 13(Odum et al., 2001).

When body weight was measured after weaning, theopposite effect was observed with numerous studiesreporting a decreased adult body weight associated withdevelopmental exposures to soy-based diets (e.g. de-creased body weight in male and female rats at PND 50and PND 120 (Lund et al., 2001), decreased body weightin male rats at PND 75 (Lephart et al., 2001), decreasedbody weight in male rats at PND 90 (Atanassova et al.,2000), decreased body weight in male rats at PND 280(Gorski et al., 2006). Odum et al. (2001) observedincreased body weight in male and female rats frombirth to PND 13, no effect around weaning (i.e. PND13–21), and decreased body weight in males from PND26 to PND 128 and in females from PND 26 to PND 140when a standard soy-based diet was given to the damsduring gestation and lactation, and then to offspringpostnatally. Ruhlen et al. (2008) reported the samepattern in CD-1 mice, with increased birth weight, noeffect of body weight around weaning (PND 20 and 26),and decreased body weight with decreased renal andgonadal fat pad weights at PND 90 for F1 offspring ofCD-1 mice exposed to a soy-based diet when comparedwith a animal fed a soy-free diet.

There are also several studies that report no change inadult body weight following developmental exposure toa soy-based diet in rats (McVey et al., 2004b; Akingbemiet al., 2007; Pastuszewska et al., 2008). Mardon et al.(2008) reported body weight in rats given a soy-baseddiet with observations covering longer exposure periodsthan most studies, and including data on 2-year-old rats.

There was no effect of soy consumption on body weightin rats from birth to 18 months of age; however, there wasa increased body weight and body fat mass observed in24 month-old rats when a soy-based diet was given to thedam during gestation and lactation, and/or to the pupsfrom weaning to 24 months of age (Mardon et al., 2008).

There was no effect of soy intake on body weight atPND 35 to 45 in marmoset monkeys given soy-basedformula from days 4 or 5 until weaning at PND 35 to 45compared with controls fed a cow’s milk-based formula(Sharpe et al., 2002; Tan et al., 2006). There was also noeffect on body weight from birth to 6 months of age incynomolgus monkeys when a soy-based diet was givento pregnant monkeys and the offspring were fed thesame soy-based diet (Wagner et al., 2009). In contrast,body weight was decreased in older cynomolgusmonkeys (1 and 2 years of age) exposed to the soy-baseddiet developmentally and with continued maintenance(Wagner et al., 2009).

Female: In all experimental animal studies, exposureto soy proteins was via the oral route. However, findingswere inconsistent between the studies. In the mouse, onestudy reported an acceleration in the age at vaginalopening (Guerrero-Bosagna et al., 2008). In anotherstudy, Ruhlen et al. (2008) reported a delay in the ageat which the female mice produced their first litter. Bothstudies involved prenatal and postnatal exposure to soyproteins in the feed. Body weight was decreased in bothstudies, and there was less fetal circulating 17b-estradiol(Ruhlen et al., 2008). In addition, estradiol-stimulateduterine weight was decreased in PND20 females on thehigh-soy diet relative to those on the control diet.

In Wistar and Sprague-Dawley rats, exposure to soy inthe feed during the prenatal and postnatal periods waslinked to early vaginal opening, greater body weightsand uterine weights (Odum et al., 2001) relative to rats onsoy-free diets, with the exception of the females on theGlobal 2016 diet (soy-free) in which the age of vaginalopening onset was not different than in the soy-fedcontrols (Odum et al., 2001). Body weight was decreasedand vaginal opening onsets were delayed, relative tocontrols, in Long Evans rats exposed to isoflavones in thediet during the prenatal and postnatal period (Lundet al., 2001) and 264). Circulating 17b-estradiol serumlevels were increased in neonatal rats exposed via thedam on PND 5 to 10 (Liu et al., 2008).

The expert panel noted that due to inconsistentfindings it is difficult to draw conclusions about effectsof soy protein on female growth, reproductive system,and endocrine-related endpoints. However, a consistenteffect of genistein and soy protein in female mice andrats was an acceleration of the timing of vaginal opening.This finding may have clinical relevance for timing ofpuberty in girls.

Male: Several rodent studies compared reproductiveendpoints in male offspring of dams given soy-based andsoy-free diets during pregnancy and lactation with pupsweaned to their dam’s diet (Makela et al., 1995; Lundet al., 2001; Odum et al., 2001; McVey et al., 2004a,b). Theresults reported in these studies were inconsistent.Odum et al. (2001) reported advancement of pubertallandmarks in males (and females). Testis weight wasreported to be decreased at PND 90 to 95 by dietary soyin one study (Atanassova et al., 2000) and increased bydietary soy in rats at PND 28 (McVey et al., 2004b).

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Increased testicular weight was reported in 68- and128-day-old offspring of rats given a soy-based dietduring pre- and postnatally; epididymal weight was alsoincreased at PND 68 (Odum et al., 2001). Greater weightof the testes, epididymides, and seminal vesicles werealso reported in adult offspring (i.e., at PND 90) ofpregnant mice fed a soy-based diet during gestation,lactation, and given to offspring post-weaning (Ruhlenet al., 2008). Greater testicular and epididymal weightswere reported at PND 160 in male offspring of rats fed asoy meal-containing diet; however, testicular and epidi-dymal weights were not altered in older (i.e. PND 280) oryounger rats (PND 22 or 60) from the same study (Gorskiet al., 2006). Several studies have reported decreasedadult prostate weight in mice (Ruhlen et al., 2008) or rats(Lephart et al., 2001; Lund et al., 2001) exposed to soy- orphytoestrogen-based diets pre- and postnatally whencompared with animals raised on a soy-free diet. Otherstudies have reported no change in prostate weightfollowing exposure pre- and postnatally in rats (Gorskiet al., 2006; Akingbemi et al., 2007) or during lactation inmarmosets (Tan et al., 2006). These differences mayreflect different isoflavone contents of the diets used indifferent studies or other differences in the compositionof the feed. The studies of McVey et al. (2004a,b) permit adose–response evaluation of dietary isoflavone supple-mentation and developmental effects. These investiga-tors used a soy-free diet to which was added soy proteinand soy isoflavones at five exposure levels (plus thesoy-free diet control). The most sensitive endpoint wasincreased testis weight on PND 28 in rats that wereexposed during pregnancy, lactation, and weaning to adietary-isoflavone intake Z2 mg/kg bw/day; however, itis not known if this is related to changes in spermatogen-esis. The increased testis weight did not show a dose–response relationship.

The study of Sharpe et al. (2002), extended by Tan et al.(2006) involved the feeding of marmoset co-twins witheither a soy infant formula or a cow-milk formula. Theauthors expected the use of co-twins to permit pairedanalyses and to decrease variability between animalsassigned to different treatments. The study authorsreported decreased levels of plasma testosterone onPND 35 to 45, increased testis weight, and increasednumbers of Sertoli and Leydig cells at 120 to 138 weeks ofage. Interpretation of this study was complicated bydesign since the offspring were also nursed by theirmothers on a daily basis.

Mammary gland development and carcinogen-esis. Thomsen et al. (2006) fed FVB mice either controldiet, 270 mg isoflavone/kg diet throughout lactation(PND 0–21), or 270 mg isoflavone/kg diet from weaningthrough the end of the study. Effects in both isoflavone-treated groups included increased branching in mam-mary trees and branching in juvenile mammary glands.In the weaning through study termination group, thenumbers of terminal end buds during the early post-weaning phase were initially increased, but weresignificantly decreased by PND 42 to 43. An increase inthe number of terminal end buds would be expected toincrease susceptibility to carcinogenesis but the laterreduction would eliminate/reverse this effect. Thus,timing of carcinogen exposure would likely affect theapparent estimates of changes in the mammary gland’ssusceptibility to carcinogenesis.

Hakkak et al. (2000) fed Sprague-Dawley rats AIN-93Gdiets in which soybean oil was replaced by corn oil andthe protein source was either casein, whey, or soy-proteinisolate containing isoflavones 430 ppm diet (genistein276 ppm diet or B20.4 genistein mg/kg bw/day anddaidzein 132 ppm diet). At weaning, the F1 and F2offspring were fed the same diets as their dams andcontinued to receive the diets throughout their lifetimes.Accelerated vaginal opening was observed on days PND37 vs. PND 38. At PND 50, rats were orally treated bygavage with 80 mg/kg DMBA and the development ofpalpable mammary tumors assessed. The authors re-ported a shorter latency to develop mammary glandtumors (F1 and F2) and a greater number of tumors/ratcompared with the whey diet group (F2). Also inSprague–Dawley rats, Simmen et al. (2005) fed femaleF1 offspring of F0 parents fed AIN-93G diets containingeither casein or soy-protein isolate from GD 4 to lactation,at weaning females were weaned to the diet of the dam.At PND 50, rats iv injected with 50 mg/kg MNU andfollowed until 115 days following MNU treatment.The investigators reported a lower mammary tumorincidence (rats with at least one mammary gland tumor)and a longer tumor latency in rats fed the soy-proteindiet. Although the incidence of ductal carcinoma in situwas lower, a higher incidence of infiltrating ductalcarcinoma was observed.

Three primary tumorigenesis endpoints are usuallymeasured. Latency (time to appearance) and incidence(number of animals with one or more mammary tumors)are likely reasonable measures with respect to the humandisease. Multiplicity (number of tumors/animal) may beless widely applicable but is potentially relevant ascontralateral breast cancers arise in some women.Although the data from the rodent studies are mixed intheir general outcomes with respect to changes inmammary gland differentiation and cancer susceptibility,several of the exposures appear to induce changes thatincrease susceptibility to carcinogenesis. These may beestrogenic effects, as E2 can produce the same outcomesand other markers of estrogenicity are evident, e.g.accelerated vaginal opening and increased the terminalend buds. Although the weight of evidence suggestadverse effects from exposure, it is difficult to arrive at acompelling determination of the lifetime effects onmammary cancer risk. Some of the changes that couldaffect risk are time dependent and modifications thatcould either increase or decrease risks are reported.

Brain and behavior. In three studies, the mainmanipulation was phytoestrogens in the diet. The onlybehavioral study was conducted in Long Evans rats(Lund and Lephart, 2001) with life-long (starting beforeconception) exposure to phytoestrogen-free or phytoes-trogen-containing (600 mg/g) diet. As adults, males andfemales were tested in the elevated plus maze foranxiety-like behavior. Rats on the phytoestrogen-contain-ing diet were less anxious and more active in the mazethan the rats not exposed to phytoestrogens. Lephartet al. (2001) used the same stock and all rats wereingested with phytoestrogen-containing diet (600 mg/g).At PND 80, one half of the animals on the phytoestrogendiet were switched to phytoestrogen-free food on PN 80then all rats were killed on PN 120. The AVPV wasexamined by Nissl stain and the expected sex difference(female4male) was only noted in the animals that

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remained on phytoestrogen-containing diet. Notablymales moved to phytoestrogen-free diet had larger AVPVvolumes than the control males that remained onphytoestrogen-containing diet. This demonstrates thatthe neuronal changes can occur in the adult brain in theAVPV when phytoestrogens are eliminated from diet, butthis occurred only in males. Finally, another sexuallydimorphic region, the SDN, was examined in Sprague-Dawley rats by Taylor et al. (1999). Dams were placed onphytoestrogen-free or phytoestrogen-containing (200mg/g)diet when mated and fetuses were taken on GD 20.Western blots were used to quantify calbindin in themedial hypothalamus (most of the calbindin in this regionwould be in the SDN). The normal sex difference(male4female) was noted only in fetuses from thephytoestrogen-consuming dams. On the phytoestrogen-free diet, females had significantly more calbindin proteinthan the phytoestrogen-ingesting females. Neither of thesesex differences is related to the expression of anxiety.Interestingly, both of these classically described neuraldifferences require phytoestrogens in diet.

CONCLUSIONS

* Evidence is sufficient to conclude that genisteinproduces developmental toxicity in male and femalemice and rats. The panel considered oral or parenteralexposure between birth and weaning at dose levels(between 37.5 and 50 mg/kg bw/day in mice;between 25 and 100 ppm in rats) that produce bloodlevels similar to those reported in children. In femalemice dosed via the oral or parenteral routes, adverseeffects were manifested as histomorphologicalchanges of the reproductive tract and the mammarygland, a decrease in fertility, and/or a decrease innumbers of live pups per litter. In a multigenerationalstudy in rats with dietary exposure to genistein,changes were observed in mammary gland morphol-ogy in both sexes (25 ppm males and 100 ppmfemales). Although not a definitive marker of devel-opmental toxicity, consistent changes in the age ofvaginal opening were seen in mice and rats. Somebiological changes in a discrete brain region in femalerats have been documented at 40 mg/kg bw/day. Theexperimental animal data are considered relevant tothe assessment of human risk.

* Evidence for daidzein, equol, and glycitein is insuffi-cient due to a paucity of relevant studies. However,relative ER binding activity of equol and daidzein arebroadly similar to genistein.

* Evidence is insufficient to conclude that soy infantformula or other soy exposures, including soy-baseddiets, produces or does not produce developmentaltoxicity in experimental animals. Although a fewstudies have examined the developmental effects ofsoy infant formula or other soy exposures and somehave identified potential developmental effects, thesestudies have yet to be replicated. The experimentalanimal data are considered relevant to the assessmentof human risk.

* Evidence is insufficient to conclude that soy infantformula produces or does not produce toxicity withinfant exposure in girls or boys at recommended

intakes manifested by the following endpoints: bonemineral density, gastrointestinal effects, allergy/immunology, thyroid function, reproductive end-points, cholesterol, diabetes mellitus, and cognitivefunction.

* Evidence is sufficient to conclude that use of soyinfant formula in healthy full-term infants does notimpair growth during infancy. This conclusion isbased on a large number of studies of small samplesize that consistently show similar growth trajectoriesof anthropometric measurement.

OVERALL CONCLUSIONS ANDRESEARCH NEEDS

Human Exposure

Infant exposure to isoflavones occurs primarilythrough the consumption of soy formula. The isoflavonestypically found in soy formula are genistein (58–67%),daidzein (29–34%), and glycitein (5–8%) with themajority of isoflavones occurring as glycosides. Totalisoflavone levels found in soy formula worldwide was 10to 47 mg/liter formula (‘‘ready-to-feed’’ equivalent).These levels are two orders of magnitude higher thanthose observed in casein-based formula or breast milk.

The degree to which infants are exclusively fed soyformula versus a combination of soy and nonsoy formulaand/or breast milk is unclear. It is estimated thatupwards of 25% of newborns or infants in the UnitedStates are fed soy formula at some point. Exposure to soyformula also varies depending on developmental stage(e.g. weaning), and cultural variations in soy formulaand soy product usage are known to exist. Prenatalexposure to soy isoflavones via maternal soy intake isalso possible.

Recent sales of soy formula in the United Statesrepresent B12% of the total dollar sales for infantformula (personal communication with Robert Rankin,Manager of Regulatory and Technical Affairs at the IFC,October 13, 2009). U.S. sales data also suggest a 50%reduction in soy formula use over the last decade(public comment from the IFC, received December 3,

2009 and personal communication with Dr. Haley CurtisStevens, IFC). When sales are considered as a surrogatemeasure of actual reported usage, these data providea lower indication of usage compared with otherfrequently cited estimates. The usage and sales of soyformula also varies geographically ranging from 2 to 7%of infant formula sales in the United Kingdom, Italy,and France, to 13% in New Zealand (Agostoni et al., 2006;Turck, 2007),and to 31.5% in Israel (Berger-Achituv et al.,2005).

In the United States, total isoflavone intake by infantswas estimated at 2.3 to 9.3 mg/kg bw/day, depending onage of the infant. The estimated intake for genistein,expressed in aglycone equivalents, ranges from 1.3 to6.2 mg/kg bw/day. These intakes are several orders ofmagnitude greater than those infants who consumebreast milk or a cow’s milk-based formula. Soy for-mula-fed infants have higher daily intakes of genisteinand other isoflavones compared with other populations(excluding regular consumers of soy supplements)(Table 2).

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Guidelines regarding the use of soy formula have beenissued by both the AAP (Bhatia and Greer, 2008), theESPGHAN Committee on Nutrition (Agostoni et al.,2006), and reviewed in the literature (Scientific Commit-tee on Food, 2003; Turck, 2007; Thygarajan and Burks,2008). In general the exclusive use of soy formula overnonsoy and/or breast milk is not recommended. Theonly real indications for use are instances where thefamily prefers a vegetarian diet or for the management ofinfants with galactosemia or primary lactase deficiency(rare). Soy formula is not currently recommended forpreterm infants.

Mean blood-based levels of isoflavones in infants fedsoy formulas are considerably higher than other popula-tions, including vegans and Japanese adults (Table 3).For example, concentrations of total genistein in wholeblood samples from U.S. infants fed soy formula are1455 ng/ml at the 75th percentile, ranging from 13.5 to3562.9 ng/ml (Cao et al., 2009) (personal communicationwith Dr. Yang Cao, NIEHS). The geometric mean value oftotal genistein in the infants fed soy infant formula(757 ng/ml) was 53.3 and 70.1 times higher comparedwith levels measured in infants fed cow milk formula(14.2 ng/ml) or breastmilk (10.8 ng/ml), respectively.The maximum obtained value in the Cao et al. (2009)study is approximately 11 times higher than themaximum genistein concentration (325 ng/ml) detectedin plasma in a small study of Japanese men, n 5 6(Adlercreutz et al., 1994). Average blood levels of totalgenistein in the soy formula-fed infants (757 ng/ml) areB160 times higher than the mean levels of total genisteinin omnivorous adults in the United States (4.7 ng/ml)reported by Valentin-Blasini (Valentin-Blasini et al., 2003).

Pharmacokinetics

There are no pharmacokinetic data for individualisoflavones following administration of soy-based infantformula to infants or children. Thus, reliable estimates ofexposure, as defined by AUC, are not available andtherefore preclude meaningful comparisons of exposurebetween infants receiving recommended intakes onnormal feeding schedules and experimental animalmodels. There are currently no estimates of variabilityin exposure to individual isoflavones (genistein, daid-zein, equol, and glycitein), or pharmacokinetic para-meters describing the disposition of those isoflavones,following recommended intakes of soy-based infantformula. Given the heterogeneity of the human infantpopulation, population studies incorporating measuresof systemic exposure (i.e. accurately timed plasmasamples and quantitative urinary recoveries) are essen-tial to identify a potentially susceptible subgroup, if oneexists.

Nevertheless, human data demonstrate that hydrolysisof genistin, the glycoside conjugate of genistein that ispresent in soy formula, occurs in both adults and infantssuch that systemic exposure to genistein occurs (Setchellet al., 1997; Cassidy, 2006; Cao et al., 2009). Themechanism of deconjugation may involve bacterialhydrolysis in the gastrointestinal tract, although somedata suggest that the glycoside conjugate may beabsorbed. Irrespective of the mechanism, systemicexposure to genistein has been documented in soyformula-fed infants, with total genistein concentrations

(isoflavone and conjugates) ranging from 13.5 to3562.9 ng/ml (Cao et al., 2009) (personal communicationwith Dr. Yang Cao, NIEHS). Although it is generallyaccepted that the majority of isoflavone readily availablein accessible body fluids (e.g. blood and urine) is in aconjugated form, the relative proportion of measurableisoflavone that is available as aglycone, glucuronide, orsulfate has not been determined for infants or childrenfed soy-based formula. Thus, the age-related differencesin glucuronidation and sulfation of individual isofla-vones are unknown, and comparison of the relativeexposure to unconjugated forms of isoflavones betweeninfants and adults is not possible.

Equol exposure in human infants following daidzeinintake is relatively low compared with animals of acomparable developmental stage. This observation isrelevant for the risk assessment of daidzein, but not ofimportance to the risk assessment of soy formula due tothe detection of equol in infants independent of feedingtype.

Genistein, daidzein, and equol all have weak affinityfor ERs, when compared with an endogenous agonistsuch as estradiol, and the ability to activate ER-dependent transcription. There is also evidence suggest-ing that many of the developmental and reproductiveendpoints observed in experimental models could bemediated through ER-dependent mechanisms given thecentral role of ERs in modulating these systems andthe similarity of effects observed as compared with thosefound in response to estradiol. However, there arelimited studies to date that have definitively establishedthe essential role of ERs in relevant toxic endpoints(e.g. insufficient studies using null mice, siRNAs, etc.).One study has demonstrated that ERb is required forgenistein-induced multioocyte follicles in C57BL/6 mice,as this effect is not found in genistein-treated ERb-nullmice (Jefferson et al., 2002). However, this study alsodemonstrated that inhibition of tyrosine kinase activityby genistein could also contribute to the mechanisms ofother effects resulting from genistein exposure in thismodel. This finding is consistent with gene expressionprofiling studies showing that the signaling mechanismsinduced by selective ER agonists are substantivelydifferent than those resulting from treatment withisoflavones. This suggests that other receptor-dependentand/or receptor-independent (e.g. epigenetic) mechan-isms could contribute to the etiology of isoflavone-induced toxicities.

Developmental Hazards

Humans. With the exception of conclusions forgrowth (discussed below), the overall evidence wasconsidered insufficient to reach a conclusion on whetherthe use of soy infant formula produces or does notproduce developmental toxicity with infant exposure ingirls or boys at recommended intake levels. Commonlyencountered limitations included the nonrandom orunspecified method of assignment to feeding groups,the use of self-selected breast- and formula-feedingmothers, failure to control for the reasons for which soyformula was used, and the early and inconsistentintroduction of solid foods. Studies that comparedoutcomes in children randomized to soy or cow-milkformula were considered the most reliable, particularly

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when parents and outcome assessors were masked toformula assignment. The studies also were evaluatedbased upon adequate sample size by gender and feedinggroup, the presence or absence of longitudinal follow-up,validation of exposure to soy formula, and appropriateadjustment for potential confounding variables. Theevidence was considered sufficient to conclude that theuse of soy infant formula in healthy full-term infantsdoes not impair growth during infancy. This conclusionis based upon a large number of studies of small samplesize that consistently show similar growth trajectories ofanthropometric measurements.

The expert panel had several remarks related to thequality of the available information for specificendpoints:

* Full-term healthy infants fed soy formula havecomparable growth as compared with full-term,healthy infants fed breast-milk or cow-milk formula.Soy formula feeding may not support the growth ofpremature infants and causes an increased incidenceof rickets. Since the AAP does not recommend the useof soy formula for premature infants, current litera-ture on the subject is scant.

* Soy infant formula may or may not cause reproduc-tive toxicity in boys and girls based on currentevidence. Preliminary data addressed in the panel’sreport do not allow firm conclusions on this effect.Limited retrospective data suggest that soy formula-fed infants may demonstrate premature thelarche(the start of breast development at the beginning ofpuberty) (Freni-Titulaer et al., 1986). The only otherstudy considered to have limited utility that includedreproductive parameters did not have sufficientpower to rule out increased risks (Strom et al., 2001).

* Soy infant formula may or may not cause adverseeffects on thyroid function in male or female infantsand children. A special cohort of infants and childrenwith CH-fed soy infant formula demonstrated a delayof TSH levels to return to normal after adequatetreatment; these children may need increased doses oflevothyroxine and closer follow-up. However, thestudies that specifically targeted infants and childrenwith CH were case-studies, which results in limitedinferences.

* All studies of gastrointestinal effects reviewed for thisreport were classified as having no utility. However,extensive reviews by AAP and ESPGHAN havereported adverse effects in a subset of infants withdocumented cow milk protein allergy; infants withdocumented cow milk protein-induced enteropathyor enterocolitis frequently are as sensitive to soyprotein and should not be given soy protein formulas.

* Sensitivity to soy protein during human infancy andchildhood may occur, but it appears to affect a verysmall subset of the population. Villous atrophy wasreported with the use of soy formulas, but theseinferences were of no utility due to the study designsbeing case reports.

* One cholesterol study was reviewed for this report(Cruz et al., 1994) and it was classified as havinglimited utility. The fractional cholesterol synthesisrates were significantly greater in infants fed soyformula (12.02% per day) as compared with humanbreast milk fed infants (2.97% per day). This rate for

soy formula-fed infants was not statistically signi-ficantly different when compared with cow-milk fedinfants. These findings suggest that infants respond todifferent dietary cholesterol intakes through alteredcholesterol synthesis rates.

* One diabetes study was reviewed for this report (Fortet al., 1986). The design of the study was a retro-spective case–control, which examined feeding his-tories of diabetic children versus controls to study theeffect of breast feeding on the development ofdiabetes. Retrospective collection of infant feedinginformation on average of 14 years was used toclassify feeding groups. As a result of this type ofclassification, twice as many diabetic children hadbeen said to have been fed soy formulas comparedwith control. Poor recall is also associated with thelack of information regarding the duration andquantity of soy formula feeding. Furthermore, soyformula exposure was said to have been mixed withcow milk formula exposure. No association betweendiabetes and exposure to soy formula was found. As aresult of these deficiencies, the study was classified asno utility.

* Two cognitive function studies were reviewed for thisreport (Malloy and Berendes, 1998; Jing et al., 2008)and were considered of no utility. One studycompared cognitive performance in children whowere fed soy formula or human breast milk. Afteradjustment of confounding variables, no differenceswere found in the outcome measures. An additionalfactor which makes this study of no utility is thepossibility of recall bias (9–10 year span). The secondstudy compared soy formula-fed infants to cow milkformula-fed infants. Spectral EEG was used to assessbrain development. Duration of soy feeding was onemonth. None of the spectral variables differedbetween the exposure groups. The duration of feedingfor 1 month may not have been sufficient to discerndifferences in EEG patterns.

Experimental animals. Although experiments de-signed to provide information of potential health risks inhumans are ideally conducted in the same species, thereare numerous reasons why this is often not possible orpractical. The purist might then conclude that we cannotdo any relevant research. However, there are numerousexamples of both translational uses of animal studies todevelop targeted treatments and also of pure basicscience work to inform human studies. Animal modelsare considered to be useful in hazard identification sincethey allow investigators to control for potential con-founders and conditions of exposure that cannot beachieved in epidemiology or clinical studies and thuscausal associations and mechanistic pathways can beaddressed. ERs are expressed in key target tissues,regulate estrogen function in a similar manner in bothrodents and humans, and oral administration of phy-toestrogens results in similar circulating levels in bothrodents and humans.

Animal studies have been used for risk assessment andfor the development of new hypotheses about mechan-isms of action. Experiments in mice, rats, pigs, andnonhuman primates are routinely used to assess effectsof various compounds on endpoints including but notlimited to: reproduction, neural development, behavior,

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and toxicity. In the case of soy and isoflavone studies,routes of exposure have included oral and sc adminis-tration. The expert panel tried to preferentially evaluatestudies that used oral administration since it best mimicsthe human route of exposure. However, sc injectionstudies were considered when they used dose levelswhich produced blood levels representative of thosemeasured following human exposure were also consid-ered. Most weight in the assessment was given to thosestudies that exposed developing animals to soy, or inmost cases the specific isoflavone genistein, solely duringthe period from birth to weaning. During this window ofexposure, which approximates the timing of soy formulaingestion in infants, genistein can affect the following indeveloping animals: puberty onset, neural differentia-tion, reproductive tract morphology, and mammarygland organization.

Although the porcine model was seen to haveimportant advantages over rodents as a model of humanexposure because they do not produce equol fromdaidzein, the panel found that there was a paucity ofstudies using the porcine model. Furthermore, althoughhuman infants do not produce comparably highquantities of equol, they are exposed to daidzein whichhas a similar affinity for the ERs. Although it isrecognized that rodents do not produce SHBG, theyproduce other sex hormone binding proteins. Pharmaco-kinetic issues were considered by the panel, and keyoral and sc injection studies were shown to producesimilar blood concentrations and circulating patterns(Doerge et al., 2002; Jefferson et al., 2009a). Takentogether these results suggest that the sc route ofadministration can be used for hazard identificationstudies. The panel notes that all the animal modelsinclude exposure to genistein.

Level of Concern Conclusions

The Expert Panel has minimal concern for adversedevelopmental effects in infants fed soy infant formula.

This conclusion is based on:

* Lack of clarity on whether studies in experimentalanimals treated with genistein only can be extrapo-lated to infants fed soy infant formula, i.e. exposure toa single isoflavone versus soy infant formula

* Interpretation of findings from experimental animalsas demonstrating adverse effects, i.e. advancedvaginal opening, effects on the mammary gland inthe context of interspecies comparisons

* Although there are a large number of experimentalanimal studies published on genistein or soy, there areonly a limited number of studies where experimentalanimals were treated only during the relevant lifestage of birth to weaning. Multigenerational studiesdo not permit discerning effects attributed to gesta-tional or lactational exposure.

* However, few studies in experimental animals andone study in humans reported effects related to thereproductive system and this elevates the concernfrom ‘‘negligible’’ to ‘‘minimal.’’

* Studies of sufficient quality in humans have not beenconducted to address the concerns raised from theexperimental animal findings or to identify pre-viously unrecognized endpoints.

The panel was in favor of the conclusion by a tally of10 yes and 2 no votes (The expert panel had 14 membersbut the Chair, Dr. Gail McCarver, does not vote andDr. Michael Rybak was not present on the day of thevote.).

Dissenting opinions:One committee member, Dr. Jatinder Bhatia, expressed

negligible concern for adverse developmental effects ininfants fed soy infant formula based on a lack of findingin humans and lack of experimental data in animals fedsoy formula.

One committee member, Dr. Ruth Etzel, expressedsome concern for adverse developmental effects ininfants fed soy infant formula. Dr. Etzel supported herlevel of concern conclusion based on the following threepoints: (1) There are sufficient signals of adversereproductive and developmental effects in experimentalanimals to worry about long-term effects on develop-ment of infants; (2) Infants are exquisitely sensitive to theeffects of exogenous chemicals during early life, andnaturally occurring genistein in soy formula has a muchstronger estrogenic effect than non-natural estrogeniccompounds on the developing reproductive system; and(3) the absence of evidence of an effect in human studiesis not the same as evidence of absence of an effect,particularly given the paucity of human data to informthe conclusion.

Critical Data Gaps and Research Needs

Pharmacokinetics. Knowledge deficits and researchneeds can be summarized as follows:

1. Available pharmacokinetic data in human infantsessentially are equivalent to biomonitoring data, andpermit crude contextual assessment of the animaldata. Full pharmacokinetic data are needed in infantsfed soy formula to inform the questions of interest.

2. Although plasma/blood data approximating steadystate have been collected, the temporal relationshipwith feeding is unknown. In the absence of fullpharmacokinetic profiles, accurate timing of blood/plasma sampling relative to feeding would be animprovement over the available data.

3. From a purely scientific perspective, pharmacokineticdata for a range of doses with individual isoflavoneswould generate the most interpretable data withrespect to understanding the dose–response relation-ship between isoflavones and reproductive outcomes.However, this is unlikely to ever be practical orethically possible as isoflavones are administered tothe population of interest, infants, as a complexbiological mixture. Human ethics committees may bereluctant to approve investigations involving com-pounds of uncertain toxic potential, and parents areunlikely to consent to their infants participating insuch a study. Pharmacokinetic studies followingadministration of soy-based formulas may be moreacceptable to both human ethics committees andparents.

4. The adult data indicate that glucuronidation andsulfation are the two primary pathways for isoflavonebiotransformation. However, high-quality quantitativeassessment of their relative importance is not

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available, including the extent of variability ofglucuronidation and sulfation in relevant populations.

5. In vitro data on the enzymes most important forisoflavone disposition in humans are limited. Further-more, the tissue distribution of those isoforms(especially in liver and intestine) and the relativelevel of expression of individual isoforms in targettissues are unknown. This knowledge deficit pre-cludes further investigations of ontogeny as well aspharmacokinetic modeling studies.

6. Studies to firmly establish whether ERs are, or are not,required for isoflavone-dependent toxicity are needed.

7. Studies to determine the relative role of epigeneticmechanisms that may or may not be required forisoflavone-dependent toxicity are needed.

Human epidemiological.

1. Based upon the current state of the science, a basic(but difficult) question to address is, ‘‘If ingestion ofsoy formula results in altered onset of puberty, and/oralteration of reproductive organs, then what wouldthe cumulative exposure of soy formula have to be toobserve such effects?’’

2. Larger (in terms of sample size) and longer (timespan) longitudinal, prospective cohort studies areneeded, e.g. a longitudinal study that capturessoy exposure from birth through puberty. This islikely to be quite challenging due to current indica-tions for soy formula and declining prevalence of use.One opportunity would be to collect appropriatemeasures of soy protein exposure in the NationalChildren’s Study.

3. Human studies should include endpoints that havebeen used in previous studies (growth, bone mineraldensity, and cognitive performance), in addition toreproductive endpoints that reflect the greater timespan of the study, such as onset of puberty. The firstendpoints in the series collected should reflect a‘‘pure’’ exposure, i.e. minimal cross-feeding withbreastmilk or cows milk-based formula.

4. Case–control studies should include longer termendpoints such as breast cancer. Again, longer termendpoints could be quite challenging due to thedietary drift that occurs in the short term that willalmost certainly occur in the long-term.

5. Continued observational studies of thyroid function ininfants fed soy infant formulas are needed.

6. Studies that combine clinical outcomes with objectivemeasures of soy protein exposure are needed.

Experimental animal. Although animal studiesare essential to hazard identification and to addresspotential mechanisms of action, numerous data gapswere identified in this assessment.

1. There is a paucity of studies that examined the effectof soy formula as opposed to individual compounds.Use of full foods is thought to account for potentialinteractions among chemical constituents of theformula and thus is more representative of humanexposure than studies employing single soyphytoestrogens.

2. There are scant studies that examined the effects ofisoflavones other than genistein.

3. Although rodents are widely used in hazard identifi-cation there are important limitations to rats and miceas models for human exposure. Differences incomparative physiology can have important implica-tions to the model selection and the relevance of thedata generated. Of note, rodents unlike human infantsproduce significant amounts of equol from daidzein.The total estrogenicity of soy needs to be morecarefully considered in future studies.

4. The effects of soy need to be examined in the mostrelevant period of development.

5. Activities other than estrogenicity of soy productsneed to be evaluated at exposure concentrationsrepresentative of human exposure.

6. The impact of species differences in bioavailability ofsex steroid and isoflavones may influence the potencyof soy in rodent models and requires furtherinvestigation.

7. There is limited information concerning the effect ofearly life exposures to soy proteins and isoflavones onanimal susceptibility to subsequent chemical insults inlater life. This question addresses the concern thatearly life exposure to isoflavones or soy proteins mayhave a programming effect that alters risk forhormonally dependent diseases such as breast cancer.

8. More studies examining the effects of soy or iso-flavone exposure during infancy on developmentaleffects on puberty are needed. The relevance of somedevelopmental effects to human health, such asvaginal opening (time of puberty onset) in rodents,is uncertain. More studies, including additionalmeasures of puberty (e.g. ovulation, gonadotropinsecretion, and onset of estrus cyclicity) in rodents andhuman studies on timing of sexual maturation, areneeded.

9. The long-term effects of soy or isoflavones duringinfancy should be addressed in animal and humanstudies of fertility, reproductive senescence (meno-pause), and life span.

10. Animal and human studies that assess effects of soyor isoflavones from birth to weaning on nonrepro-ductive behaviors are needed.

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