{"id":5097,"date":"2026-01-06T15:48:01","date_gmt":"2026-01-06T15:48:01","guid":{"rendered":"https:\/\/www.stealthsyndromesstudy.com\/?p=5097"},"modified":"2026-02-26T23:02:33","modified_gmt":"2026-02-26T23:02:33","slug":"conflicts-of-interest-in-bpa-research","status":"publish","type":"post","link":"https:\/\/www.stealthsyndromesstudy.com\/?p=5097","title":{"rendered":"Conflict-of-Interest Signals in Key BPA Biomonitoring and Toxicokinetic Studies"},"content":{"rendered":"\n<p>Prose narrative derived directly from the COI audit table (V\u00f6lkel, Teeguarden, LaKind and related review\/panel literature), with superscripted numerical footnotes keyed to a citation table.<\/p>\n\n\n\n<hr class=\"wp-block-separator has-alpha-channel-opacity\"\/>\n\n\n\n<h1 class=\"wp-block-heading\">Overview<\/h1>\n\n\n\n<p>The audit table captures a recurring pattern in the BPA literature: a small number of high\u2011influence papers and reviews are repeatedly used to support broad conclusions about internal dose (\u201cfree BPA\u201d in serum), toxicokinetics (rapid first\u2011pass conjugation after oral intake), and population exposure (intake back\u2011calculated from urinary biomonitoring). Where these nodes shape public-facing reassurance or regulatory modeling, conflicts of interest matter\u2014not as proof of incorrect science, but as an interpretive context that can affect framing, choice of comparisons, sensitivity analyses, and how uncertainty is communicated. The narrative below follows the table\u2019s structure and preserves each entry\u2019s disclosed funding\/affiliations, its role in debate, and the recurring criticisms noted in COI discussions.<\/p>\n\n\n\n<p>Across the studies summarized here, the main scientific claims fall into three categories. First are arguments that reported serum \u201cfree BPA\u201d is frequently attributable to contamination rather than true circulating levels.<sup>1,6<\/sup> Second are controlled human toxicokinetic studies supporting extensive first\u2011pass metabolism after oral ingestion (with low systemic free BPA).<sup>3,5<\/sup> Third are biomonitoring-to-intake translations that conclude typical population intakes are low relative to prevailing guidance values.<sup>4,7<\/sup> The COI signals in the table cluster most clearly around industry trade-group sponsorship of key \u201clow exposure\/contamination\u201d narratives, particularly via the ACC Polycarbonate\/BPA Global Group (Global Alliance).<sup>12<\/sup><\/p>\n\n\n\n<h1 class=\"wp-block-heading\">A. Contamination control and the \u201cfree BPA in serum\u201d dispute<\/h1>\n\n\n\n<p>Dekant &amp; V\u00f6lkel\u2019s 2008 biomonitoring review is frequently cited to argue that many published reports of \u201cfree BPA\u201d in serum are implausible given known metabolism and are more consistent with contamination introduced during collection, processing, or analysis.<sup>1<\/sup> In policy debates, the review\u2019s influence is amplified because it provides a concise narrative: rapid conjugation should leave little unconjugated BPA in blood after oral exposure, so unexpectedly high serum values are treated as a red flag for artefact.<sup>1<\/sup> The COI relevance highlighted in the table is that the review disclosed partial support from the Polycarbonate\/BPA Global Group under the ACC\u2014an industry trade association representing manufacturers and stakeholders with a direct interest in BPA risk framing.<sup>12<\/sup> As a result, the paper is often treated as both a scientific position and an industry\u2011adjacent position within the broader controversy.<sup>9<\/sup><\/p>\n\n\n\n<p>Teeguarden et al. (2013) reinforces this contamination-centered skepticism from a different funding posture. In that Food and Chemical Toxicology review, the authors argue that many \u201ctypical\u201d serum BPA concentrations reported in the literature appear inconsistent with established toxicokinetics, and they emphasize contamination control as essential for credible serum measurements.<sup>6<\/sup> The audit table notes that this review reported U.S. EPA STAR grant support and stated no competing financial interests, making it a methodological ally of contamination skepticism without an industry sponsorship signal in the funding statement.<sup>6<\/sup><\/p>\n\n\n\n<p>Teeguarden et al. (2015) adds controlled human data in the same argumentative direction. In a soup\u2011ingestion design, the study reports extensive first\u2011pass metabolism over 24 hours and presents evidence against meaningful sublingual absorption under that scenario\u2014an important point because \u201csublingual bypass\u201d is sometimes invoked to reconcile high serum BPA reports with rapid hepatic conjugation.<sup>5<\/sup> The table flags COI concerns because the 2015 study acknowledges funding from the ACC Polycarbonate\/BPA Global Group (and describes FDA support for certain laboratory activities). Although the authors declared no competing interests, the trade-group grant source is regularly cited in COI discussions because the study\u2019s conclusions are strategically relevant to the serum\u2011BPA controversy.<sup>5,12<\/sup> In short, the contamination\/low\u2011free\u2011BPA thesis is supported by both industry\u2011funded and non\u2011industry\u2011funded sources in this set, but the table\u2019s purpose is to keep the sponsorship context visible when the thesis is used as a broad dismissal of contrary biomonitoring findings.<\/p>\n\n\n\n<h1 class=\"wp-block-heading\">B. Oral first-pass metabolism and \u201clow bioavailability\u201d as a regulatory backbone<\/h1>\n\n\n\n<p>V\u00f6lkel et al. (2002) is repeatedly treated as cornerstone human PK evidence for the \u201clow bioavailability\u201d model: after low oral doses, BPA is rapidly metabolized (primarily to conjugates) with low measurable free BPA in circulation.<sup>3<\/sup> The audit table lists the study\u2019s support as described in its disclosures (German Environment Agency support; with related institutional equipment support described in later disclosures). The COI signal here is not industry funding per se, but the study\u2019s downstream policy role: it is often used to justify modeling assumptions that treat oral BPA exposure as efficiently neutralized by first\u2011pass conjugation.<sup>3<\/sup> The table also notes limitations that recur in critiques\u2014small cohorts and the possibility that an oral\u2011dose paradigm may not capture all real\u2011world exposure routes or sources of variability in internal dose.<\/p>\n\n\n\n<p>V\u00f6lkel, Kiranoglu &amp; Fromme (2008) complements this framework with biomonitoring in urine. By measuring free and total BPA in human urine and using those data to assess daily uptake, the paper concludes that daily exposure is low and below guidance values.<sup>4<\/sup> In the audit table, this study is noted as having later declarations indicating no external funding and being conducted within a public health authority context (Bavarian Health and Food Safety Authority).<sup>4<\/sup> The key interpretive point is methodological: biomonitoring-to-intake back\u2011calculations depend strongly on PK assumptions (excretion fractions, timing, and steady\u2011state approximations). Thus, even absent a clear COI signal, the study\u2019s influence in risk characterization makes its assumptions and uncertainty framing part of the critical-reading burden.<\/p>\n\n\n\n<h1 class=\"wp-block-heading\">C. Urinary biomonitoring and intake estimation: where assumptions and COI intersect<\/h1>\n\n\n\n<p>LaKind &amp; Naiman (2011) is a central population-intake paper because it back\u2011calculates daily BPA intake from NHANES urinary biomonitoring (2005\u20132006) and reports low average intakes.<sup>7<\/sup> The audit table flags explicit COI relevance: the paper\u2019s disclosures include consulting relationships spanning government and industry contexts, and the work is described as supported by the Polycarbonate\/BPA Global Group.<sup>7,12<\/sup> Because this study is frequently cited to argue that exposures fall below regulatory thresholds, the funding and consulting disclosures are consequential: they sit at the interface between a technical modeling exercise (intake estimation from urine) and a public health narrative (population exposure is \u201clow\u201d).<sup>7<\/sup> The table\u2019s critique emphasis is that the numerical intake estimates are sensitive to assumptions about excretion fractions and the episodic, short\u2011lived nature of BPA exposure, meaning that \u201clow intake\u201d conclusions can be fragile to model structure and sampling design.<\/p>\n\n\n\n<p>LaKind et al. (2019) broadens the focus from a single-country intake estimate to how national biomonitoring data are interpreted across multiple countries, using BPA as a case study. The paper is often used in methodological debates about cross\u2011country comparisons and interpretation pitfalls for short\u2011lived chemical biomarkers.<sup>8<\/sup> The COI significance in the audit table is primarily contextual: the author affiliation includes LaKind Associates (private consulting), and readers are encouraged to consult the paper\u2019s own disclosure section and interpretive framing in light of the broader consulting role reflected across related BPA publications.<sup>8<\/sup><\/p>\n\n\n\n<h1 class=\"wp-block-heading\">D. Consensus reviews and declared interests: the Hengstler panel as an archetype<\/h1>\n\n\n\n<p>Hengstler et al. (2011), published in Critical Reviews in Toxicology, exemplifies how panel\u2011style reviews can consolidate contested evidence into a posture of reassurance. The panel argued (as assessed at that time) that BPA was unlikely to pose significant risk at prevailing exposures.<sup>2<\/sup> The audit table highlights explicit declared interests: the panel included an employee of Bayer; the declaration noted that V\u00f6lkel reported prior support from the BPA Global Group; and the declaration referenced industry sponsorship connected to a guest author\u2019s participation.<sup>2,12<\/sup> Because such reviews are repeatedly cited in regulatory and media contexts, the declared interests matter: they provide a concrete basis for readers to scrutinize how uncertainties are weighted and which studies are treated as authoritative when competing lines of evidence exist.<sup>9<\/sup><\/p>\n\n\n\n<p>The table also notes that later regulatory positions diverged, underscoring that apparent \u201cconsensus\u201d can shift. EFSA\u2019s April 2023 re\u2011evaluation adopted a much lower tolerable daily intake for BPA, while the U.S. FDA\u2019s public position around the same period maintained that BPA is safe for currently approved food\u2011contact uses at current exposure levels.<sup>10,11<\/sup> This divergence is not itself evidence of COI, but it is relevant to COI interpretation: it demonstrates that different institutions can legitimately reach different risk conclusions based on endpoint selection, evidentiary weighting, and evolving standards\u2014making it even more important to track how funding and declared interests intersect with the most policy\u2011leveraged claims in the literature.<\/p>\n\n\n\n<h1 class=\"wp-block-heading\">Interpretive synthesis: what the COI pattern does\u2014and does not\u2014prove<\/h1>\n\n\n\n<p>The COI signals captured in the audit table do not establish that any particular dataset is invalid. Instead, they identify where financially interested parties intersect with the most consequential narrative pivots in BPA disputes: whether serum \u201cfree BPA\u201d findings should be treated as artefact; whether oral exposure is effectively neutralized by first\u2011pass metabolism; and whether population intakes inferred from urine are reliably \u201clow.\u201d<sup>1,3,5,7,12<\/sup> When industry trade-group sponsorship aligns with conclusions that down\u2011weight internal exposure or risk, a prudent reader does not dismiss the science outright\u2014but does demand clearer documentation of methods, contamination controls, sensitivity analyses, and uncertainty framing, and gives added attention to independent replication and triangulation across study designs.<\/p>\n\n\n\n<h1 class=\"wp-block-heading\">Conflict-Of-Interest-Audit of BPA Studies by V\u00f6lkel, Teeguarden, and LaKind<\/h1>\n\n\n\n<p>This dossier summarizes key publications by three frequently cited BPA researchers (V\u00f6lkel, Teeguarden, LaKind), with attention to their study claims, funding sources, conflicts of interest (COI), regulatory uptake, and critiques. It is intended as an audit-ready reference for evaluating the weight regulators (FDA vs. EFSA) place on these studies.<\/p>\n\n\n\n<figure class=\"wp-block-table\"><table><tbody><tr><td>Paper<\/td><td>Claim<\/td><td>Funding \/ COI<\/td><td>Regulatory uptake<\/td><td>Critiques<\/td><\/tr><tr><td>Dekant &amp; V\u00f6lkel (2008) \u2014 biomonitoring review<sup>1<\/sup><\/td><td>Argues most reported \u201cfree BPA\u201d in serum is likely contamination; emphasizes rapid conjugation.<sup>1<\/sup><\/td><td>Review disclosed as supported in part by the Polycarbonate\/BPA Global Group (American Chemistry Council).<sup>2,12<\/sup><\/td><td>Widely cited in risk assessments and policy debates to support low internal exposure after oral intake.<sup>1<\/sup><\/td><td>Criticized as \u201cindustry-aligned\u201d in investigative and scientific critiques.<sup>9<\/sup><\/td><\/tr><tr><td>V\u00f6lkel et al. (2002) \u2014 human PK, low oral doses<sup>3<\/sup><\/td><td>Reports rapid first\u2011pass metabolism (primarily glucuronidation) after oral administration; low free BPA in circulation.<sup>3<\/sup><\/td><td>Funding described as German Environment Agency support; equipment support attributed to DFG and Bavaria in later disclosures.<sup>2<\/sup><\/td><td>Frequently used as cornerstone evidence for \u201clow bioavailability\u201d assumptions in regulatory modeling.<sup>3<\/sup><\/td><td>Limitations include small cohorts and dependence on oral\u2011dose paradigms that may not capture all exposure routes.<\/td><\/tr><tr><td>V\u00f6lkel, Kiranoglu &amp; Fromme (2008) \u2014 urine free vs total<sup>4<\/sup><\/td><td>Measures free and total BPA in urine; concludes daily uptake is low and below guidance values.<sup>4<\/sup><\/td><td>Later declarations report no external funding for this study (conducted at Bavarian Health and Food Safety Authority).<sup>2<\/sup><\/td><td>Cited to argue population exposure estimates remain well below tolerable intakes.<sup>4<\/sup><\/td><td>Critiques emphasize that biomonitoring\u2011to\u2011intake back\u2011calculations depend strongly on PK assumptions.<\/td><\/tr><tr><td>Teeguarden et al. (2015) \u2014 soup ingestion PK study<sup>5<\/sup><\/td><td>Finds extensive first\u2011pass metabolism after soup ingestion; argues against meaningful sublingual absorption.<sup>5<\/sup><\/td><td>Funding: American Chemistry Council Polycarbonate\/BPA Global Group (Grant 63289); NCTR lab activities supported by FDA. Authors declared no competing interests.<sup>5,10,12<\/sup><\/td><td>Often cited in disputes over whether reported serum \u201cfree BPA\u201d reflects true exposure vs. contamination.<sup>5<\/sup><\/td><td>Study sponsorship is repeatedly flagged in COI discussions of the BPA biomonitoring literature.<sup>9<\/sup><\/td><\/tr><tr><td>Teeguarden et al. (2013) \u2014 serum BPA measurability review<sup>6<\/sup><\/td><td>Concludes typical reported serum BPA levels are often inconsistent with known toxicokinetics; contamination is a key concern.<sup>6<\/sup><\/td><td>Funding: U.S. EPA STAR grant; authors reported no competing financial interests.<sup>6<\/sup><\/td><td>Used to support strict contamination\u2011control requirements and skepticism of high serum BPA reports.<sup>6<\/sup><\/td><td>Critiques focus on how contamination risk is weighted versus other lines of evidence.<\/td><\/tr><tr><td>LaKind &amp; Naiman (2011) \u2014 NHANES intake estimation (2005\u20132006)<sup>7<\/sup><\/td><td>Back\u2011calculates daily BPA intake from urinary biomonitoring; reports low population intakes.<sup>7<\/sup><\/td><td>Disclosures: author consults to government and industry; work supported by Polycarbonate\/BPA Global Group.<sup>7,12<\/sup><\/td><td>Frequently cited to argue population exposures are below regulatory thresholds.<sup>7<\/sup><\/td><td>Critiques note intake estimates hinge on excretion fraction assumptions and short\u2011lived exposure dynamics.<\/td><\/tr><tr><td>LaKind et al. (2019) \u2014 multi-country biomonitoring interpretation (BPA case study)<sup>8<\/sup><\/td><td>Compares national biomonitoring data across countries; discusses pitfalls in interpreting short\u2011lived chemical biomarkers.<sup>8<\/sup><\/td><td>Author affiliation includes LaKind Associates (private consulting). Consult the paper\u2019s own disclosure section for additional COI details.<sup>8<\/sup><\/td><td>Used in methodological debates about comparing biomonitoring datasets and deriving intake estimates.<sup>8<\/sup><\/td><td>Main relevance to COI auditing is the author\u2019s consulting disclosure history in related BPA work.<sup>7<\/sup><\/td><\/tr><tr><td>Hengstler et al. (2011) \u2014 Critical Reviews panel report<sup>2<\/sup><\/td><td>Panel argues BPA is unlikely to pose significant risk at prevailing exposures (as assessed at that time).<sup>2<\/sup><\/td><td>Declaration of interest includes: Bayer employee on panel; V\u00f6lkel reports prior support from BPA Global Group; panel notes industry sponsorship for a guest author\u2019s participation.<sup>2,9,12<\/sup><\/td><td>Cited in pre\u20112015 policy debates supporting \u201cBPA safe\u201d narratives.<sup>9<\/sup><\/td><td>Later regulatory positions diverge: EFSA (Apr 2023) sharply reduced the BPA TDI; FDA (Apr 2023) reaffirmed safety for approved food\u2011contact uses at current levels.<sup>10,11<\/sup><\/td><\/tr><\/tbody><\/table><\/figure>\n\n\n\n<h2 class=\"wp-block-heading\">References (verified; superscript numbers in text)<\/h2>\n\n\n\n<p>1. Dekant, W., &amp; V\u00f6lkel, W. (2008). Human exposure to bisphenol A by biomonitoring: methods, results and assessment of environmental exposures. Toxicology and Applied Pharmacology, 228(1), 114\u2013134. <a href=\"https:\/\/doi.org\/10.1016\/j.taap.2007.12.008\">doi:10.1016\/j.taap.2007.12.008<\/a> | <a href=\"https:\/\/pubmed.ncbi.nlm.nih.gov\/18207480\/\">PubMed<\/a> \u2014 Accessed January 4, 2026.<\/p>\n\n\n\n<p>2. Hengstler, J. G., et al. (2011). Critical evaluation of key evidence on the human health hazards of exposure to bisphenol A. Critical Reviews in Toxicology, 41(4), 263\u2013291. <a href=\"https:\/\/doi.org\/10.3109\/10408444.2011.558487\">doi:10.3109\/10408444.2011.558487<\/a> | <a href=\"https:\/\/pmc.ncbi.nlm.nih.gov\/articles\/PMC3135059\/\">PMC full text<\/a> \u2014 Accessed January 4, 2026.<\/p>\n\n\n\n<p>3. V\u00f6lkel, W., Colnot, T., Csanady, G. A., Filser, J. G., &amp; Dekant, W. (2002). Metabolism and kinetics of bisphenol A in humans at low doses following oral administration. Chemical Research in Toxicology, 15(10), 1281\u20131287. <a href=\"https:\/\/doi.org\/10.1021\/tx025548t\">doi:10.1021\/tx025548t<\/a> | <a href=\"https:\/\/pubmed.ncbi.nlm.nih.gov\/12387626\/\">PubMed<\/a> \u2014 Accessed January 4, 2026.<\/p>\n\n\n\n<p>4. V\u00f6lkel, W., Kiranoglu, M., &amp; Fromme, H. (2008). Determination of free and total bisphenol A in human urine to assess daily uptake as a basis for a valid risk assessment. Toxicology Letters, 179(3), 155\u2013162. <a href=\"https:\/\/doi.org\/10.1016\/j.toxlet.2008.05.002\">doi:10.1016\/j.toxlet.2008.05.002<\/a> | <a href=\"https:\/\/pubmed.ncbi.nlm.nih.gov\/18579321\/\">PubMed<\/a> \u2014 Accessed January 4, 2026.<\/p>\n\n\n\n<p>5. Teeguarden, J. G., Twaddle, N. C., Churchwell, M. I., Yang, X., Fisher, J. W., Seryak, L. M., &amp; Doerge, D. R. (2015). 24-hour human urine and serum profiles of bisphenol A: Evidence against sublingual absorption following ingestion in soup. Toxicology and Applied Pharmacology, 288(2), 131\u2013142. <a href=\"https:\/\/doi.org\/10.1016\/j.taap.2015.01.009\">doi:10.1016\/j.taap.2015.01.009<\/a> | <a href=\"https:\/\/pubmed.ncbi.nlm.nih.gov\/25620055\/\">PubMed<\/a> | <a href=\"https:\/\/stacks.cdc.gov\/view\/cdc\/202323\/cdc_202323_DS1.pdf\">CDC-hosted PDF<\/a> \u2014 Accessed January 4, 2026.<\/p>\n\n\n\n<p>6. Teeguarden, J. G., Hanson-Drury, S., Fisher, J. W., &amp; Doerge, D. R. (2013). Are typical human serum BPA concentrations measurable and sufficient to be estrogenic in the general population? Food and Chemical Toxicology, 62, 949\u2013963. <a href=\"https:\/\/doi.org\/10.1016\/j.fct.2013.08.001\">doi:10.1016\/j.fct.2013.08.001<\/a> \u2014 Accessed January 4, 2026.<\/p>\n\n\n\n<p>7. LaKind, J. S., &amp; Naiman, D. Q. (2011). Daily intake of bisphenol A and potential sources of exposure: 2005\u20132006 National Health and Nutrition Examination Survey. Journal of Exposure Science and Environmental Epidemiology, 21(3), 272\u2013279. <a href=\"https:\/\/doi.org\/10.1038\/jes.2010.9\">doi:10.1038\/jes.2010.9<\/a> | <a href=\"https:\/\/www.nature.com\/articles\/jes20109.pdf\">PDF<\/a> \u2014 Accessed January 4, 2026.<\/p>\n\n\n\n<p>8. LaKind, J. S., Pollock, T., Naiman, D. Q., Kim, S., Nagasawa, A., &amp; Clarke, J. (2019). Factors affecting interpretation of national biomonitoring data from multiple countries: Bisphenol A as a case study. Environmental Research, 173, 318\u2013329. <a href=\"https:\/\/doi.org\/10.1016\/j.envres.2019.03.047\">doi:10.1016\/j.envres.2019.03.047<\/a> | <a href=\"https:\/\/pubmed.ncbi.nlm.nih.gov\/30995718\/\">PubMed<\/a> \u2014 Accessed January 4, 2026.<\/p>\n\n\n\n<p>9. Rust, S. (2011, April 28). Industry linked to study supporting safety of plastics chemical BPA. Center for Public Integrity. <a href=\"https:\/\/publicintegrity.org\/environment\/industry-linked-to-study-supporting-safety-of-plastics-chemical-bpa\/\">Article<\/a> \u2014 Accessed January 4, 2026.<\/p>\n\n\n\n<p>10. U.S. Food and Drug Administration. (2023, April 20). Bisphenol A (BPA): Use in food contact application. <a href=\"https:\/\/www.fda.gov\/food\/food-packaging-other-substances-come-contact-food-information-consumers\/bisphenol-bpa-use-food-contact-application\">FDA page<\/a> \u2014 Accessed January 4, 2026.<\/p>\n\n\n\n<p>11. European Food Safety Authority. (n.d.). Bisphenol A (BPA) (topic page; notes April 2023 re-evaluation). <a href=\"https:\/\/www.efsa.europa.eu\/en\/topics\/topic\/bisphenol\">EFSA topic page<\/a> \u2014 Accessed January 4, 2026.<\/p>\n\n\n\n<p>12. American Chemistry Council. (n.d.). Polycarbonate\/Bisphenol A (BPA) Global Alliance. <a href=\"https:\/\/www.americanchemistry.com\/industry-groups\/polycarbonate-bisphenol-a-bpa-global-alliance\">ACC page<\/a> \u2014 Accessed January 4, 2026.<\/p>\n","protected":false},"excerpt":{"rendered":"<p>Prose narrative derived directly from the COI audit table (V\u00f6lkel, Teeguarden, LaKind and related review\/panel literature), with superscripted numerical footnotes keyed to a citation table. Overview The audit table captures a recurring pattern in the BPA literature: a small number of high\u2011influence papers and reviews are repeatedly used to support broad conclusions about internal dose [&hellip;]<\/p>\n","protected":false},"author":2,"featured_media":5075,"comment_status":"closed","ping_status":"closed","sticky":false,"template":"","format":"standard","meta":{"footnotes":""},"categories":[18,1],"tags":[],"_links":{"self":[{"href":"https:\/\/www.stealthsyndromesstudy.com\/index.php?rest_route=\/wp\/v2\/posts\/5097"}],"collection":[{"href":"https:\/\/www.stealthsyndromesstudy.com\/index.php?rest_route=\/wp\/v2\/posts"}],"about":[{"href":"https:\/\/www.stealthsyndromesstudy.com\/index.php?rest_route=\/wp\/v2\/types\/post"}],"author":[{"embeddable":true,"href":"https:\/\/www.stealthsyndromesstudy.com\/index.php?rest_route=\/wp\/v2\/users\/2"}],"replies":[{"embeddable":true,"href":"https:\/\/www.stealthsyndromesstudy.com\/index.php?rest_route=%2Fwp%2Fv2%2Fcomments&post=5097"}],"version-history":[{"count":3,"href":"https:\/\/www.stealthsyndromesstudy.com\/index.php?rest_route=\/wp\/v2\/posts\/5097\/revisions"}],"predecessor-version":[{"id":5117,"href":"https:\/\/www.stealthsyndromesstudy.com\/index.php?rest_route=\/wp\/v2\/posts\/5097\/revisions\/5117"}],"wp:featuredmedia":[{"embeddable":true,"href":"https:\/\/www.stealthsyndromesstudy.com\/index.php?rest_route=\/wp\/v2\/media\/5075"}],"wp:attachment":[{"href":"https:\/\/www.stealthsyndromesstudy.com\/index.php?rest_route=%2Fwp%2Fv2%2Fmedia&parent=5097"}],"wp:term":[{"taxonomy":"category","embeddable":true,"href":"https:\/\/www.stealthsyndromesstudy.com\/index.php?rest_route=%2Fwp%2Fv2%2Fcategories&post=5097"},{"taxonomy":"post_tag","embeddable":true,"href":"https:\/\/www.stealthsyndromesstudy.com\/index.php?rest_route=%2Fwp%2Fv2%2Ftags&post=5097"}],"curies":[{"name":"wp","href":"https:\/\/api.w.org\/{rel}","templated":true}]}}