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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Pharmacol.</journal-id>
<journal-title>Frontiers in Pharmacology</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Pharmacol.</abbrev-journal-title>
<issn pub-type="epub">1663-9812</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="publisher-id">692442</article-id>
<article-id pub-id-type="doi">10.3389/fphar.2021.692442</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Pharmacology</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Development, Testing, Parameterisation and Calibration of a Human PBPK Model for the Plasticiser, Di-(2-propylheptyl) Phthalate (DPHP) Using in Silico, <italic>in&#x20;vitro</italic> and Human Biomonitoring Data</article-title>
<alt-title alt-title-type="left-running-head">McNally et&#x20;al.</alt-title>
<alt-title alt-title-type="right-running-head">DPHP, PBPK, Human, biomonitoring</alt-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>McNally</surname>
<given-names>Kevin</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="corresp" rid="c001">&#x2a;</xref>
<uri xlink:href="https://loop.frontiersin.org/people/28819/overview"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Sams</surname>
<given-names>Craig</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Hogg</surname>
<given-names>Alex</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Lumen</surname>
<given-names>Annie</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/215428/overview"/>
</contrib>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Loizou</surname>
<given-names>George</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="corresp" rid="c001">&#x2a;</xref>
<uri xlink:href="https://loop.frontiersin.org/people/12578/overview"/>
</contrib>
</contrib-group>
<aff id="aff1">
<label>
<sup>1</sup>
</label>Health and Safety Executive, <addr-line>Buxton</addr-line>, <country>United&#x20;Kingdom</country>
</aff>
<aff id="aff2">
<label>
<sup>2</sup>
</label>National Center for Toxicological Research, US Food and Drug Administration, <addr-line>Jefferson</addr-line>, <addr-line>AR</addr-line>, <country>United&#x20;States</country>
</aff>
<author-notes>
<fn fn-type="edited-by">
<p>
<bold>Edited by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/75206/overview">Eleonore Fr&#xf6;hlich</ext-link>, Medical University of Graz, Austria</p>
</fn>
<fn fn-type="edited-by">
<p>
<bold>Reviewed by:</bold> <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/1132163/overview">Malarvannan Govindan</ext-link>, University of Antwerp, Belgium</p>
<p>
<ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/899079/overview">Raju Prasad Sharma</ext-link>, Leiden Academic Centre for Drug Research, Netherlands</p>
</fn>
<corresp id="c001">&#x2a;Correspondence: Kevin McNally, <email>kevin.mcnally@hse.gov.uk</email>; George Loizou, <email>George.Loizou@hse.gov.uk</email>
</corresp>
<fn fn-type="other">
<p>This article was submitted to Predictive Toxicology, a section of the journal Frontiers in Pharmacology</p>
</fn>
</author-notes>
<pub-date pub-type="epub">
<day>02</day>
<month>09</month>
<year>2021</year>
</pub-date>
<pub-date pub-type="collection">
<year>2021</year>
</pub-date>
<volume>12</volume>
<elocation-id>692442</elocation-id>
<history>
<date date-type="received">
<day>08</day>
<month>04</month>
<year>2021</year>
</date>
<date date-type="accepted">
<day>13</day>
<month>08</month>
<year>2021</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2021 McNally, Sams, Hogg, Lumen and Loizou.</copyright-statement>
<copyright-year>2021</copyright-year>
<copyright-holder>McNally, Sams, Hogg, Lumen and Loizou</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/">
<p>This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these&#x20;terms.</p>
</license>
</permissions>
<abstract>
<p>A physiologically based pharmacokinetic model for Di-(2-propylheptyl) phthalate (DPHP) was developed to interpret the biokinetics in humans after single oral doses. The model was parameterized with <italic>in&#x20;vitro</italic> and in&#x20;silico derived parameters and uncertainty and sensitivity analysis was used during the model development process to assess structure, biological plausibility and behaviour prior to simulation and analysis of human biological monitoring data. To provide possible explanations for some of the counter-intuitive behaviour of the biological monitoring data the model included a simple lymphatic uptake process for DPHP and enterohepatic recirculation (EHR) for DPHP and the mono ester metabolite mono-(2-propylheptyl) phthalate (MPHP). The model was used to simultaneously simulate the concentration-time profiles of blood DPHP, MPHP and the&#x20;urinary excretion of two metabolites, mono-(2-propyl-6-hydroxyheptyl) phthalate (OH-MPHP) and mono-(2-propyl-6-carboxyhexyl) phthalate (cx-MPHP). The availability of blood and urine measurements permitted a more robust qualitative and quantitative investigation of the importance of EHR and lymphatic uptake. Satisfactory prediction of blood DPHP and urinary metabolites was obtained whereas blood MPHP was less satisfactory. However, the delayed peak of DPHP concentration relative to MPHP in blood and second order metabolites in urine could be explained as a result of three processes: 1) DPHP entering the systemic circulation from the lymph, 2) rapid and very high protein binding and 3) the efficiency of the liver in removing DPHP absorbed via the hepatic route. The use of sensitivity analysis is considered important in the evaluation of uncertainty around <italic>in&#x20;vitro</italic> and in&#x20;silico derived parameters. By quantifying their impact on model output sufficient confidence in the use of a model should be afforded. This approach could expand the use of PBPK models since parameterization with in&#x20;silico techniques allows for rapid model development. This in turn could assist in reducing the use of animals in toxicological evaluations by enhancing the utility of &#x201c;read across&#x201d; techniques.</p>
</abstract>
<kwd-group>
<kwd>plasticiser</kwd>
<kwd>DPHP</kwd>
<kwd>PBPK</kwd>
<kwd>in silico</kwd>
<kwd>
<italic>in&#x20;vitro</italic>
</kwd>
<kwd>biomonitoring</kwd>
<kwd>bayesian</kwd>
<kwd>markov chain Monte Carlo</kwd>
</kwd-group>
<contract-sponsor id="cn001">European Chemical Industry Council<named-content content-type="fundref-id">10.13039/100009420</named-content>
</contract-sponsor>
</article-meta>
</front>
<body>
<sec id="s1">
<title>Introduction</title>
<p>Plastics have many useful applications due to their plasticity, which is the ability to be shaped and moulded. Plasticisers are different classes of chemicals used in the manufacture of plastics to create products of varying flexibilities and brittleness. Phthalates, which are some of the most commonly used plasticisers, are dialkyl- or alkylarylesters of 1, 2-benzenedicarboxylic acid. The length of the ester chain determines the industrial application, with alkyl chain lengths from three to 13 carbons widely used in polymers such as polyvinyl chloride (PVC).</p>
<p>Di-(2-propylheptyl) phthalate (DPHP), CAS No. 53306-54-0, marketed under the trade name Palatinol<sup>&#xae;</sup>10-P, is a high molecular weight branched phthalate ester which is used in the manufacture of polyvinyl chloride (PVC) products. DPHP can be found in cables, car interiors, carpet backing, pool liners, roofing membranes or tarpaulins, and consumer products such as shoes and artificial leather (<xref ref-type="bibr" rid="B28">Klein et&#x20;al., 2018</xref>). Typical contents of DPHP in end-use products vary between 30 and 60% (w/w), 10.1&#x2013;48.2% (w/w). While DPHP is a plasticizer predominantly recommended for technical applications, and has in the past been found in toys, food packaging and medicinal products (<xref ref-type="bibr" rid="B28">Klein et&#x20;al., 2018</xref>) the European Union has advised against its use as well as not providing clearance for use in food contact materials<xref ref-type="fn" rid="fn1">
<sup>1</sup>
</xref>. DPHP, in common with other plasticizers, is not chemically bound in PVC products so can be released into the environment. Several studies have demonstrated the presence of DPHP in the general population (<xref ref-type="bibr" rid="B60">Wittassek and Angerer, 2008</xref>; <xref ref-type="bibr" rid="B61">Wittassek et&#x20;al., 2011</xref>; <xref ref-type="bibr" rid="B54">Schutze et&#x20;al., 2015</xref>; <xref ref-type="bibr" rid="B55">Schwedler et&#x20;al., 2019</xref>; <xref ref-type="bibr" rid="B52">Schmidtkunz et&#x20;al., 2019</xref>). However, when compared to human biomonitoring (HBM) health-based guidance values, (<xref ref-type="bibr" rid="B55">Schwedler et&#x20;al, 2019</xref>), report no exceedance of the HBM-I<xref ref-type="fn" rid="fn2">
<sup>2</sup>
</xref> value of 1&#xa0;mg/L for DPHP (Sum of OH-MPHP &#x2b; oxo-MPHP) (<xref ref-type="bibr" rid="B3">Apel et&#x20;al., 2017</xref>).</p>
<p>Currently, there are no data on the toxicology of DPHP in humans and in contrast with other phthalates, studies in rats suggest that it is neither a reproductive toxicant nor an endocrine disruptor (<xref ref-type="bibr" rid="B8">BASF, 1995a</xref>; <xref ref-type="bibr" rid="B7">BASF, 2003</xref>; <xref ref-type="bibr" rid="B6">BASF, 2009</xref>; <xref ref-type="bibr" rid="B21">Furr et&#x20;al., 2014</xref>). In other studies, increased liver weights, thyroid, and pituitary effects were observed following oral administration (<xref ref-type="bibr" rid="B9">BASF, 1995b</xref>; <xref ref-type="bibr" rid="B57">Union Carbide, 1997</xref>; <xref ref-type="bibr" rid="B58">Union Carbide, 1998</xref>; <xref ref-type="bibr" rid="B6">BASF, 2009</xref>). An oral reference dose of 0.1&#xa0;mg/kg body weight per day in humans was derived from a benchmark dose of 10&#xa0;mg/kg body weight per day for thyroid hypertrophy/hyperplasia in adult male rats (<xref ref-type="bibr" rid="B10">Bhat et&#x20;al., 2014</xref>). The adverse&#x20;effects that were observed with other phthalates that were related to metabolism of the parent phthalate to the primary monoester (<xref ref-type="bibr" rid="B47">Oishi and Hiraga, 1980</xref>; <xref ref-type="bibr" rid="B20">Foster et&#x20;al., 1981</xref>; <xref ref-type="bibr" rid="B56">Sj&#xf6;berg et&#x20;al., 1986</xref>) are not reported to occur with DPHP. Large species-specific burdens of the primary monoester of di-(2-ethylhexyl) phthalate (DEHP) in venous blood were observed (<xref ref-type="bibr" rid="B51">Rhodes et&#x20;al., 1986</xref>; <xref ref-type="bibr" rid="B26">Kessler et&#x20;al., 2004</xref>; <xref ref-type="bibr" rid="B30">Kurata et&#x20;al., 2012</xref>). Therefore, species-specific burdens of primary monoesters of DPHP in rat and human were proposed as a basis for a risk estimation of DPHP&#x20;(<xref ref-type="bibr" rid="B29">Klein et&#x20;al., 2016</xref>). A study involving the biological monitoring (BM) of human volunteers following administration of a single oral dose of DPHP was conducted for this purpose (<xref ref-type="bibr" rid="B28">Klein et&#x20;al., 2018</xref>).</p>
<p>BM is the repeated controlled measurement of a chemical, its metabolites, or biochemical markers in accessible media such as urine, blood and saliva, exhaled air and hair (<xref ref-type="bibr" rid="B38">Manno et&#x20;al., 2010</xref>). As a method of exposure assessment BM is considered superior to personal air or dermal deposition measurements. This is because more accurate estimates of body burden can be made, since BM measurements are a composite measure of multiple routes of exposure (<xref ref-type="bibr" rid="B17">Cocker and Jones, 2017</xref>). Differences in individual behaviour such as, personal hygiene and work rate, in addition to inter-individual differences in physiology and metabolism can be captured in BM measurements (<xref ref-type="bibr" rid="B17">Cocker and Jones, 2017</xref>). Uncertainty in external exposure assessment due to inter- and intra-individual variability can also be reduced by using BM if the measured biomarker, either parent chemical or metabolite(s), is proportionately related to the ultimate toxic entity (<xref ref-type="bibr" rid="B12">Boogaard et&#x20;al., 2011</xref>). The ability to estimate organ and tissue dose or &#x201c;tissue dosimetry&#x201d; from body burdens calculated using BM should further improve the correlation of exposure to health effects.</p>
<p>Tissue dosimetry can be estimated with the application of physiologically based pharmacokinetic (PBPK) modelling. PBPK modelling is a powerful means of simulating the factors that determine tissue dose within any biological organism and consequently, it&#x2019;s correlation with health effects (<xref ref-type="bibr" rid="B2">Andersen, 1995</xref>; <xref ref-type="bibr" rid="B15">Clewell III and Andersen, 1996</xref>; <xref ref-type="bibr" rid="B1">Andersen, 2003</xref>; <xref ref-type="bibr" rid="B4">Barton et&#x20;al., 2007</xref>; <xref ref-type="bibr" rid="B16">Clewell et&#x20;al., 2008</xref>; <xref ref-type="bibr" rid="B34">Loizou and Hogg, 2011</xref>). The value of PBPK models is that they are tools for integrating <italic>in&#x20;vitro</italic>, in&#x20;silico and <italic>in vivo</italic> mechanistic, pharmacokinetic, and toxicological information. PBPK models encode an explicit mathematical description of important anatomical, physiological and biochemical determinants of chemical uptake, distribution, and elimination. Thus, PBPK modelling is increasingly being used in chemical risk assessment (RA) (<xref ref-type="bibr" rid="B14">Chiu et&#x20;al., 2007</xref>; <xref ref-type="bibr" rid="B35">Loizou et&#x20;al., 2008</xref>; <xref ref-type="bibr" rid="B59">WHO, 2010</xref>).</p>
<p>In this study we present a PBPK model developed to interpret the venous blood concentrations of DPHP and its primary monoester metabolite, mono-(2-propylheptyl) phthalate (MPHP), and the urinary excretion of the two direct metabolites of MPHP, mono-(2-propyl-6-hydroxyheptyl) phthalate (OH-MPHP) and mono-(2-propyl-6-carboxyhexyl) phthalate (cx-MPHP). We adapted the model structure for di-isononyl-cyclohexane-1, 2-dicarboxylate (Hexamoll<sup>&#xae;</sup> DINCH) described previously (<xref ref-type="bibr" rid="B42">McNally et&#x20;al., 2019</xref>) to include a simple lymphatic uptake process for DPHP andenterohepatic recirculation of DPHP and MPHP (<xref ref-type="bibr" rid="B63">Yang et&#x20;al., 2015</xref>). The model was parameterized using <italic>in&#x20;vitro</italic> and in&#x20;silico methods. These were measured intrinsic hepatic clearance scaled from <italic>in&#x20;vitro</italic> to <italic>in vivo</italic> and predicted octanol&#x2013;water partition coefficient (Log P<sub>ow</sub>) values which, in turn, were used to predict parameters such as plasma unbound fraction and tissue:blood partition coefficients (PCs). Also, the sufficiency and relevance of PBPK model structure and the sensitivity of model output to <italic>in&#x20;vitro</italic> and in&#x20;silico derived model parameters was investigated using an approach based on global sensitivity analysis (GSA). The latter is part of the ongoing development of a good PBPK modelling practice (<xref ref-type="bibr" rid="B4">Barton et&#x20;al., 2007</xref>; <xref ref-type="bibr" rid="B35">Loizou et&#x20;al., 2008</xref>; <xref ref-type="bibr" rid="B5">Barton et&#x20;al., 2009</xref>; <xref ref-type="bibr" rid="B59">WHO, 2010</xref>; <xref ref-type="bibr" rid="B48">Paini et&#x20;al., 2017</xref>; <xref ref-type="bibr" rid="B18">Ellison et&#x20;al., 2019</xref>; <xref ref-type="bibr" rid="B19">Fabian et&#x20;al., 2019</xref>).</p>
</sec>
<sec sec-type="materials|methods" id="s2">
<title>Materials and Methods</title>
<sec id="s2-1">
<title>Experimental</title>
<sec id="s2-1-1">
<title>Chemicals</title>
<p>Pooled human microsomes were purchased from Tebu-bio (Peterborough, United&#x20;Kingdom). The microsomes were prepared from a pool of 50 liver samples; mixed gender (20&#xa0;mg protein ml<sup>&#x2212;1</sup>). DPHP and MPHP were provided by BASF SE. All chemicals used were of analytical grade or higher.</p>
</sec>
<sec id="s2-1-2">
<title>Analysis</title>
<p>Samples were analysed by liquid chromatography (Shimadzu Prominence) with tandem mass spectrometry detection (AB Sciex API 3200) using electrospray ionisation. Ion optics, temperatures and gas flows were optimised on our individual system. All analyses used a Synergi Hydro-RP column (150 &#xd7; 2&#xa0;mm; 4&#xa0;&#xb5;; Phenomenex) in conjunction with a methanol: 20&#xa0;mM ammonium acetate (0.1% acetic acid) gradient. Sample injection volume was 2&#xa0;&#xb5;l.</p>
</sec>
<sec id="s2-1-3">
<title>
<italic>In vitro</italic> Incubations</title>
<p>The very high lipophilicity of DPHP resulted in the formation of an insoluble film on the surface of the reaction medium which precluded the measurement of <italic>in&#x20;vitro</italic> clearance. Therefore, the measurement <italic>in&#x20;vitro</italic> clearance of MPHP only was possible (<xref ref-type="fig" rid="F1">Figure&#x20;1</xref>).</p>
<fig id="F1" position="float">
<label>FIGURE 1</label>
<caption>
<p>Postulated metabolism of DPHP in humans showing only those metabolites measured in human biological monitoring and described in the PBPK&#x20;model.</p>
</caption>
<graphic xlink:href="fphar-12-692442-g001.tif"/>
</fig>
<p>The NADPH regenerating system consisted of the following final concentrations: 1.3&#xa0;mM NADP<sup>&#x2b;</sup>; 3.3&#xa0;mM glucose-6-phosphate; 5&#xa0;mM magnesium chloride; 0.4&#xa0;U/ml glucose-6-phosphate dehydrogenase; 50&#xa0;mM phosphate buffer (pH 7.4). Final microsomal protein concentration was 0.5&#xa0;mg/ml. Incubations were performed in polypropylene tubes and pre-warmed reaction mixtures were started by addition of substrate dissolved in acetonitrile. The final acetonitrile concentration was less than 1% and, typically, a substrate concentration of 10&#xa0;&#xb5;M was used (initial investigations were performed to check solubility in the reaction mixture). Incubations were conducted in a water bath at 37&#xb0;C. At the time points chosen for measurement, tubes were mixed by inversion and an aliquot removed and quenched by adding to an equal volume of ice-cold methanol followed by centrifugation to precipitate the protein as a pellet. The supernatant was removed for analysis. Three replicates were sampled at each time point. Control incubations consisted of a reaction mix excluding glucose-6-phosphate dehydrogenase (for evaluation of non-specific binding) and reaction mix excluding microsomes (for evaluation of substrate stability).</p>
<p>The method of (<xref ref-type="bibr" rid="B25">Jones and Houston, 2004</xref>) was used to determine the <italic>in&#x20;vitro</italic> half-life of substrate depletion. At least three independent incubations were performed and results were assessed visually for reproducibility. However, due to differences in sampling time points between experiments, results from individual incubations were not combined.</p>
</sec>
</sec>
<sec id="s2-2">
<title>Determination of <italic>in&#x20;vitro</italic> Intrinsic Clearance</title>
<p>As described in (<xref ref-type="bibr" rid="B42">McNally, et&#x20;al, 2019</xref>) <italic>in&#x20;vitro</italic> intrinsic clearance for MPHP, <italic>CL</italic>
<sub>
<italic>in&#x20;vitro</italic>
</sub> (ml min<sup>&#x2212;1</sup>&#xa0;mg<sup>&#x2212;1</sup> microsomal protein) in human hepatic microsomes was calculated using the half-life (<italic>T</italic>
<sub>
<italic>&#xbd;</italic>
</sub>) derived from the decay constant (<italic>k</italic>) using the following equations (<xref ref-type="bibr" rid="B44">Obach et&#x20;al., 1997</xref>):<disp-formula id="e1">
<mml:math id="m1">
<mml:mrow>
<mml:mi>i</mml:mi>
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<mml:msub>
<mml:mi>T</mml:mi>
<mml:mrow>
<mml:mn>1</mml:mn>
<mml:mo>/</mml:mo>
<mml:mn>2</mml:mn>
</mml:mrow>
</mml:msub>
<mml:mo>&#x3d;</mml:mo>
<mml:mfrac>
<mml:mrow>
<mml:mi>ln</mml:mi>
<mml:mrow>
<mml:mo>(</mml:mo>
<mml:mn>2</mml:mn>
<mml:mo>)</mml:mo>
</mml:mrow>
</mml:mrow>
<mml:mi>k</mml:mi>
</mml:mfrac>
</mml:mrow>
</mml:math>
<label>(1)</label>
</disp-formula>
<disp-formula id="e2">
<mml:math id="m2">
<mml:mrow>
<mml:mi>C</mml:mi>
<mml:msub>
<mml:mi>L</mml:mi>
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<mml:mn>2</mml:mn>
</mml:mrow>
</mml:msub>
</mml:mrow>
</mml:mfrac>
<mml:mo>&#xd7;</mml:mo>
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<mml:mi>g</mml:mi>
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</mml:math>
<label>(2)</label>
</disp-formula>Where, <italic>ml incubation</italic> is the volume (ml) of the incubation medium and <italic>mg microsomes</italic> is the mass (mg) of microsomes in the incubation medium.</p>
</sec>
<sec id="s2-3">
<title>Calculation of <italic>in vivo</italic> Clearance</title>
<p>The intrinsic hepatic clearance CL<sub>int_H</sub> (L h<sup>&#x2212;1</sup>) was calculated using the following formula adapted from (<xref ref-type="bibr" rid="B45">Obach, 1999</xref>):<disp-formula id="e3">
<mml:math id="m3">
<mml:mrow>
<mml:mi>C</mml:mi>
<mml:msub>
<mml:mi>L</mml:mi>
<mml:mrow>
<mml:mi>int</mml:mi>
<mml:mo>_</mml:mo>
<mml:mi>H</mml:mi>
</mml:mrow>
</mml:msub>
<mml:mo>&#x3d;</mml:mo>
<mml:mi>C</mml:mi>
<mml:msub>
<mml:mi>L</mml:mi>
<mml:mrow>
<mml:mi>i</mml:mi>
<mml:mi>n</mml:mi>
<mml:mi>v</mml:mi>
<mml:mi>i</mml:mi>
<mml:mi>t</mml:mi>
<mml:mi>r</mml:mi>
<mml:mi>o</mml:mi>
</mml:mrow>
</mml:msub>
<mml:mo>&#xd7;</mml:mo>
<mml:mi>M</mml:mi>
<mml:mi>P</mml:mi>
<mml:mi>Y</mml:mi>
<mml:mo>&#xd7;</mml:mo>
<mml:mi>V</mml:mi>
<mml:mi>l</mml:mi>
<mml:mi>i</mml:mi>
<mml:mo>&#xd7;</mml:mo>
<mml:mn>60</mml:mn>
</mml:mrow>
</mml:math>
<label>(3)</label>
</disp-formula>Where, <italic>MPY</italic> is the microsomal protein yield per g liver (mg g<sup>&#x2212;1</sup>), <italic>Vli</italic> is mass of the liver (g) and the 60 converts from minutes to&#x20;hours.</p>
<p>Whole liver plasma clearance <italic>CL</italic>
<sub>
<italic>H</italic>
</sub> (L h<sup>&#x2212;1</sup>) was calculated assuming the well-stirred model of hepatic clearance taking into account the unbound fraction in plasma, <italic>fu</italic> and the red blood cells to plasma ratio, C<sub>RBC</sub>/C<sub>P</sub>, using the following equation (<xref ref-type="bibr" rid="B62">Yang et&#x20;al., 2007</xref>):<disp-formula id="e4">
<mml:math id="m4">
<mml:mrow>
<mml:mi>C</mml:mi>
<mml:msub>
<mml:mi>L</mml:mi>
<mml:mi>H</mml:mi>
</mml:msub>
<mml:mo>&#x3d;</mml:mo>
<mml:msub>
<mml:mi>Q</mml:mi>
<mml:mi>H</mml:mi>
</mml:msub>
<mml:mo>&#x00B7;</mml:mo>
<mml:mi>f</mml:mi>
<mml:mi>u</mml:mi>
<mml:mo>&#x00B7;</mml:mo>
<mml:mfrac>
<mml:mrow>
<mml:mi>C</mml:mi>
<mml:msub>
<mml:mi>L</mml:mi>
<mml:mrow>
<mml:mi>int</mml:mi>
<mml:mo>_</mml:mo>
<mml:mi>H</mml:mi>
</mml:mrow>
</mml:msub>
</mml:mrow>
<mml:mrow>
<mml:msub>
<mml:mi>Q</mml:mi>
<mml:mi>H</mml:mi>
</mml:msub>
<mml:mo>&#x2b;</mml:mo>
<mml:mi>f</mml:mi>
<mml:mi>u</mml:mi>
<mml:mo>&#x00B7;</mml:mo>
<mml:mi>C</mml:mi>
<mml:msub>
<mml:mi>L</mml:mi>
<mml:mrow>
<mml:mi>int</mml:mi>
<mml:mo>_</mml:mo>
<mml:mi>H</mml:mi>
</mml:mrow>
</mml:msub>
<mml:mo>/</mml:mo>
<mml:mrow>
<mml:mo>(</mml:mo>
<mml:mrow>
<mml:msub>
<mml:mi>C</mml:mi>
<mml:mrow>
<mml:mi>R</mml:mi>
<mml:mi>B</mml:mi>
<mml:mi>C</mml:mi>
</mml:mrow>
</mml:msub>
<mml:mo>/</mml:mo>
<mml:msub>
<mml:mi>C</mml:mi>
<mml:mi>P</mml:mi>
</mml:msub>
</mml:mrow>
<mml:mo>)</mml:mo>
</mml:mrow>
</mml:mrow>
</mml:mfrac>
</mml:mrow>
</mml:math>
<label>(4)</label>
</disp-formula>Where, <italic>Q</italic>
<sub>
<italic>H</italic>
</sub> (L h<sup>&#x2212;1</sup>) is the blood flow to the liver as a proportion of cardiac output.</p>
<p>The intrinsic gut clearance CL<sub>int_gut</sub> was calculated similarly as described for hepatic clearance but substituting <italic>MPY</italic>
<sub>
<italic>gut</italic>
</sub> and <italic>Vgu</italic> for <italic>MPY</italic> and <italic>Vli</italic>, respectively, in <xref ref-type="disp-formula" rid="e4">Eq. 4</xref>. The resulting calculated CL<sub>int_gut</sub> was used in place of CL<sub>int_H</sub> for calculation of CL<sub>gut</sub>.</p>
</sec>
<sec id="s2-4">
<title>Prediction of Log P<sub>ow</sub> and Tissue:blood Partition Coefficients (PCs) and Plasma Fraction Unbound</title>
<p>The tissue:blood PCs and unbound fractions in plasma were calculated from the logarithm of the octanol&#x2013;water partition coefficient, Log P<sub>ow</sub> as described in McNally, et&#x20;al. (2019). Briefly, the Log P<sub>ow</sub> for DPHP and MPHP were calculated using the ACDLogP algorithm (<xref ref-type="bibr" rid="B37">Mannhold et&#x20;al., 2009</xref>) implemented in the ACD/ChemSketch 2014 software (<xref ref-type="table" rid="T1">Table&#x20;1</xref>). The Log P<sub>ow</sub>s were input into two tissue-composition-based algorithms for the calculation of tissue:blood PCs. The method of (<xref ref-type="bibr" rid="B50">Poulin and Haddad, 2012</xref>), which was developed for the prediction of the tissue distribution of highly lipophilic compounds, defined as chemicals with a Log P<sub>ow</sub> &#x3e; 5.8, was used for DPHP (<xref ref-type="table" rid="T1">Table&#x20;1</xref>). The method of (<xref ref-type="bibr" rid="B53">Schmitt, 2008</xref>) , which was developed to predict the tissue distribution of chemicals with Log P<sub>ow</sub> &#x3c; 5.17, was used to predict the PCs of the monoester, MPHP (<xref ref-type="table" rid="T1">Table&#x20;1</xref>). The algorithm of (<xref ref-type="bibr" rid="B50">Poulin and Haddad, 2012</xref>) was implemented as a Microsoft<sup>&#xae;</sup> Excel Add-in whereas a modified version of the algorithm of (<xref ref-type="bibr" rid="B53">Schmitt, 2008</xref>) was available within the httk: R Package for High-Throughput Toxicokinetics (<xref ref-type="bibr" rid="B49">Pearce et&#x20;al., 2017</xref>). Where the tissue-composition-based algorithms did not provide a tissue:blood partition coefficient for a particular compartment, the value from a surrogate organ or tissue was assumed. These are presented in italicised text with the surrogate organ or tissue in brackets <xref ref-type="table" rid="T1">Table&#x20;1</xref>.</p>
<table-wrap id="T1" position="float">
<label>TABLE 1</label>
<caption>
<p>Tissue:blood partition coefficients and plasma fraction unbound predicted using Log P<sub>ow</sub>.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left"/>
<th align="center">DPHP</th>
<th align="center">MPHP</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">
<bold>Log Po:w</bold>
</td>
<td align="char" char=".">10.83</td>
<td align="char" char=".">5.3</td>
</tr>
<tr>
<td align="left">
<bold>Tissue:blood partition coefficient</bold>
</td>
<td align="left"/>
<td align="left"/>
</tr>
<tr>
<td align="left">&#x2003;Adipose</td>
<td align="char" char=".">63.4</td>
<td align="char" char=".">29.10</td>
</tr>
<tr>
<td align="left">&#x2003;Liver</td>
<td align="char" char=".">5.89</td>
<td align="char" char=".">54.8</td>
</tr>
<tr>
<td align="left">&#x2003;Muscle</td>
<td align="char" char=".">3.29</td>
<td align="char" char=".">7.51</td>
</tr>
<tr>
<td align="left">&#x2003;Blood cells</td>
<td align="char" char=".">3.01</td>
<td align="char" char=".">6.67</td>
</tr>
<tr>
<td align="left">&#x2003;Gut</td>
<td align="char" char=".">7.4</td>
<td align="char" char=".">25.2</td>
</tr>
<tr>
<td align="left">&#x2003;Spleen</td>
<td align="char" char=".">3.7</td>
<td align="char" char=".">12.20</td>
</tr>
<tr>
<td align="left">&#x2003;Stomach<xref ref-type="table-fn" rid="Tfn1">
<sup>a</sup>
</xref> (gut)</td>
<td align="char" char=".">7.4</td>
<td align="char" char=".">25.2</td>
</tr>
<tr>
<td align="left">&#x2003;Rapidly Perfused (spleen)</td>
<td align="char" char=".">3.7</td>
<td align="char" char=".">12.20</td>
</tr>
<tr>
<td align="left">&#x2003;Slowly Perfused (muscle)</td>
<td align="char" char=".">3.29</td>
<td align="char" char=".">7.51</td>
</tr>
<tr>
<td align="left">
<bold>Plasma Fraction Unbound</bold>
</td>
<td align="char" char=".">0.0025</td>
<td align="char" char=".">0.0146</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="Tfn1">
<label>a</label>
<p>Compartments in italics have surrogate values from another organ compartment. The corresponding surrogate organ compartment is in parentheses.</p>
</fn>
</table-wrap-foot>
</table-wrap>
<p>The fraction unbound (<italic>fu</italic>) was calculated from <italic>log ((1-fu)/fu)</italic> with the following equation:<disp-formula id="e5">
<mml:math id="m5">
<mml:mrow>
<mml:mi>f</mml:mi>
<mml:mi>u</mml:mi>
<mml:mo>&#x3d;</mml:mo>
<mml:mfrac>
<mml:mn>1</mml:mn>
<mml:mrow>
<mml:msup>
<mml:mrow>
<mml:mn>10</mml:mn>
</mml:mrow>
<mml:mi>x</mml:mi>
</mml:msup>
<mml:mo>&#x2b;</mml:mo>
<mml:mn>1</mml:mn>
</mml:mrow>
</mml:mfrac>
</mml:mrow>
</mml:math>
<label>(5)</label>
</disp-formula>Where, <inline-formula id="inf1">
<mml:math id="m6">
<mml:mrow>
<mml:mtext>x</mml:mtext>
<mml:mo>&#x3d;</mml:mo>
<mml:mtext>0</mml:mtext>
<mml:mtext>.</mml:mtext>
<mml:mn>4485</mml:mn>
<mml:mtext>logP</mml:mtext>
<mml:mo>-</mml:mo>
<mml:mtext>0</mml:mtext>
<mml:mtext>.</mml:mtext>
<mml:mn>4782</mml:mn>
</mml:mrow>
</mml:math>
</inline-formula>
</p>
<p>When <italic>x</italic> is the equation for the prediction of <italic>fu</italic> for a chemical with a predominantly uncharged state at pH 7.4 (<xref ref-type="bibr" rid="B33">Lobell and Sivarajah, 2003</xref>) (<xref ref-type="table" rid="T1">Table&#x20;1</xref>).</p>
</sec>
<sec id="s2-5">
<title>Calculation of Fraction Metabolised</title>
<p>The proportion of MPHP metabolised to cx- and OH-MPHP, represented by FracMetab (FracMetabcx to cx- MPHP and FracMetabOH to OH-MPHP) (<xref ref-type="table" rid="T2">Table&#x20;2</xref>) for each volunteer was estimated by expressing all the biological monitoring (BM) data (MPHP, OH-MPHP, cx-MPHP, oxo-MPHP) in moles and dividing the amount of cx- and OH-MPHP each by the sum total of all metabolites (<xref ref-type="table" rid="T2">Table&#x20;2</xref>).</p>
<table-wrap id="T2" position="float">
<label>TABLE 2</label>
<caption>
<p>Volunteer specific parameters.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left"/>
<th colspan="6" align="center">Volunteers</th>
</tr>
<tr>
<th align="left"/>
<th align="center">A</th>
<th align="center">B</th>
<th align="center">C</th>
<th align="center">D</th>
<th align="center">E</th>
<th align="center">F</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">Body weight (kg)</td>
<td align="center">83</td>
<td align="center">75</td>
<td align="center">76</td>
<td align="center">74</td>
<td align="center">90</td>
<td align="center">108</td>
</tr>
<tr>
<td align="left">Dose (mg kg<sup>&#x2212;1</sup>)</td>
<td align="center">0.717</td>
<td align="center">0.639</td>
<td align="center">0.781</td>
<td align="center">0.783</td>
<td align="center">0.775</td>
<td align="center">0.733</td>
</tr>
<tr>
<td align="left">Fraction Metabolised</td>
<td align="left"/>
<td align="left"/>
<td align="left"/>
<td align="left"/>
<td align="left"/>
<td align="left"/>
</tr>
<tr>
<td align="left">&#x2003;FracMetab to cx_MPHP</td>
<td align="center">0.02</td>
<td align="center">0.017</td>
<td align="center">0.02</td>
<td align="center">0.023</td>
<td align="center">0.018</td>
<td align="center">0.018</td>
</tr>
<tr>
<td align="left">&#x2003;FracMetab to OH_MPHP</td>
<td align="center">0.396</td>
<td align="center">0.340</td>
<td align="center">0.374</td>
<td align="center">0.359</td>
<td align="center">0.334</td>
<td align="center">0.329</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s2-6">
<title>Biological Monitoring Data</title>
<p>The BM data described in (<xref ref-type="bibr" rid="B28">Klein et&#x20;al, 2018</xref>) were kindly provided by Dr. Rainer Otter of BASF, SE. Briefly, DPHP was administered orally to six healthy male volunteers, aged between 30 and 64&#xa0;years, weighing between 74 and 108&#xa0;kg. A single dose of 738&#x20;&#xb1; 56&#xa0;&#xb5;g/kg BW DPHP was administered as an emulsion of 7% (w/v) in an aqueous saccharose solution (70% w/v) between 45 and 140&#xa0;min after breakfast. The resulting respective doses for the six individuals were between 0.639 and 0.783&#xa0;mg kg<sup>&#x2212;1</sup> body weight (<xref ref-type="table" rid="T2">Table&#x20;2</xref>).</p>
</sec>
<sec id="s2-7">
<title>The PBPK Model</title>
<p>A human PBPK model was developed to study the fate of DPHP following single oral doses. The initial model structure was based upon the PBPK model for the plasticizer DINCH described in (<xref ref-type="bibr" rid="B42">McNally, et&#x20;al, 2019</xref>), with a minor modification to account for a large proportion of administered oral dose that is not absorbed, but eliminated by faecal excretion (<xref ref-type="bibr" rid="B28">Klein et&#x20;al., 2018</xref>). The simulation of urinary excretion of metabolites as amount per hour was preferred as they were less variable than when expressed against creatinine to adjust for urinary dilution (<xref ref-type="bibr" rid="B32">Lermen et&#x20;al., 2019</xref>). The model included a description of absorption from the stomach and gastro-intestinal (GI) tract and a simple model of the lymphatic system describing uptake of DPHP via the lacteals in the intestine and entering venous blood after bypassing the liver. Inclusion of a lymph compartment was based on the assumption that DPHP like di(2-ethylhexyl) phthalate (DEHP) binds like lipid to lipoproteins (<xref ref-type="bibr" rid="B23">Griffiths et&#x20;al., 1988</xref>) which are formed in enterocytes and transported in the lymph of the thoracic duct (<xref ref-type="bibr" rid="B27">Kessler et&#x20;al., 2012</xref>). The dose that entered the&#x20;lymphatic system via the GI tract was coded as a fraction of the administered dose, with the complementary proportion entering the liver via the portal vein. The model described the metabolism of DPHP to MPHP in both liver and gut; therefore, both DPHP and MPHP entered systemic circulation via uptake from the gut. Enterohepatic circulation was also described as a&#x20;possible explanation of the second small peak in urinary metabolite concentration observed in several datasets. A sub-model was added to describe the kinetics of MPHP, with the two models connected through the gut and liver compartments. The model for DPHP differed from the sub-model only with the presence of a lymphatic component and the MPHP sub-model describing urinary excretion of metabolites. Both models had a stomach and GI tract draining into the liver and systemically circulated to adipose, blood (plasma and red blood cell) and slowly and rapidly perfused compartments. First order elimination constants described the removal of second order metabolites OH-MPHP and cx-MPHP from blood into the urine. A representation of the model structure is given in <xref ref-type="fig" rid="F2">Figure&#x20;2</xref>. The model code is available in <xref ref-type="sec" rid="s11">Supplementary Materials</xref>.</p>
<fig id="F2" position="float">
<label>FIGURE 2</label>
<caption>
<p>A schematic of the model for DPHP and sub-model for MPHP. The main model contained a lymphatic compartment which received a portion of oral dose from the stomach and GI tract. Urinary excretion of metabolites was ascribed to the sub-model.</p>
</caption>
<graphic xlink:href="fphar-12-692442-g002.tif"/>
</fig>
<p>The baseline model was subsequently refined using an iterative model development process to better represent the trends in BM (blood and urine) data from the human volunteer study reported in (<xref ref-type="bibr" rid="B28">Klein et&#x20;al., 2018</xref>). Techniques for uncertainty and sensitivity analysis (described in the statistical analysis section) were deployed, at each iteration of model development, to establish the bounding behaviour of the model and the key uncertain parameters that the model outputs under study were sensitive to. The improvements and a brief justification are described in the points below:<list list-type="simple">
<list-item>
<p>1. The model was adapted to account for a majority fraction of DPHP passing through the GI tract without being absorbed, as suggested by BM data, ranging from 75% (<xref ref-type="bibr" rid="B60">Wittassek and Angerer 2008</xref>; <xref ref-type="bibr" rid="B31">Leng et&#x20;al., 2014</xref>) to 94% (<xref ref-type="bibr" rid="B28">Klein et&#x20;al., 2018</xref>). <italic>FracDOSEHep</italic> and <italic>FracDOSELymph</italic> modelled the fractions of the administered dose entering hepatic and lymphatic circulation respectively, with the complementary fraction (1&#x20;&#x2013; <italic>FracDOSEHep &#x2013; FracDOSELymph)</italic> passing directly in faeces.</p>
</list-item>
<list-item>
<p>2. The model for lymphatic circulation was modified. A delay term, <italic>Lymphlag</italic> was introduced to describe a delay between DPHP entering lymphatic circulation and the subsequent appearance in venous blood at the thoracic duct. Mixing into venous blood was modelled as a first order process (proportional to the mass in lymphatic circulation). This description of the lymph in the baseline model resulted in slow emptying from the lymph into venous blood. This modification to the model was necessary in order to approximate the almost complete elimination of DPHP from blood over a 48&#xa0;h period apparent in BM&#x20;data.</p>
</list-item>
<list-item>
<p>3. A delay term, <italic>Gutlag</italic> was introduced to allow a delay in the uptake of DPHP from the GI tract. A better representation of the absorption phase of BM data was achieved following this modification.</p>
</list-item>
<list-item>
<p>4. The model was adapted to simulate the transport process of enterohepatic recirculation. Uptake of both DPHP and MPHP from the liver into bile was modelled as a first order uptake process with a delay (to represent transport from liver to gut) before DPHP (and MPHP) appeared in the gut where DPHP and MPHP were available for reabsorption (<xref ref-type="fig" rid="F3">Figure&#x20;3</xref>). Data on the deposition rates of OH-MPHP and cx-MPHP in urine voids (mg/hour), calculated from the raw BM data, showed evidence of regularly spaced harmonics following the initial peak that were consistent with this process. As a consequence of this modification the PBPK model was solved as a system of delay differential equations (DDEs) rather than ordinary differential equations (ODEs).</p>
</list-item>
<list-item>
<p>5. First order elimination rates for DPHP and MPHP were included to account for fractions of recirculated DPHP and MPHP that were eliminated in faeces rather than reabsorbed from the GI&#x20;tract.</p>
</list-item>
</list>
</p>
<fig id="F3" position="float">
<label>FIGURE 3</label>
<caption>
<p>A schematic showing pre-systemic metabolism and enterohepatic recirculation, systemic and lymphatic uptake of DPHP and uptake of MPHP from gastrointestinal&#x20;tract.</p>
</caption>
<graphic xlink:href="fphar-12-692442-g003.tif"/>
</fig>
</sec>
<sec id="s2-8">
<title>Parameterisation</title>
<p>Baseline estimates of organ and tissue masses and regional blood flows were taken from <xref ref-type="bibr" rid="B13">Brown et&#x20;al. (1997)</xref> and <xref ref-type="bibr" rid="B24">ICRP (2002)</xref>. The mass of the lymphatic system was obtained from <xref ref-type="bibr" rid="B46">Offman et&#x20;al. (2016)</xref>.</p>
<p>Tissue: blood partition coefficients were estimated using algorithms as described previously.</p>
<p>The bio-transformation of DPHP to MPHP in the liver was described by an intrinsic clearance term determined <italic>in&#x20;vitro</italic> and scaled to <italic>in-vivo</italic>: the half-life of DPHP was estimated using the PBPK model. The <italic>in-vivo</italic> intrinsic clearance of DPHP in the gut was calculated using the <italic>in&#x20;vitro</italic> hepatic clearance scaled to <italic>in vivo</italic> using gut microsomal protein yield and gut volume. The bio-transformation of MPHP to second order metabolites (OH-MPHP and cx-MPHP) in the liver was of the same form as the expression for DPHP, however an estimate of the half-life for MPHP was determined experimentally (as described above). A single term for metabolism of MPHP was coded in the PBPK model with the rates of removal of two direct metabolites, (OH-MPHP and cx-MPHP), from plasma assumed to be proportional to the rate of metabolism of MPHP. A urinary elimination constant was estimated for OH-MPHP and cx-MPHP.</p>
<p>Baseline values for parameters for which there was no prior knowledge such as <italic>FracDOSEHep, FracDOSELymph</italic> and the various delay terms and uptake and elimination rates were determined during the model development and testing process to provide a reasonable (but not optimised) fit to BM&#x20;data.</p>
<p>Baseline (default) values are given in <xref ref-type="table" rid="T3">Table&#x20;3</xref>.</p>
<table-wrap id="T3" position="float">
<label>TABLE 3</label>
<caption>
<p>Physiological and kinetic default values used in PBPK model and probability distributions applied for uncertainty and sensitivity analyses.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left">Physiological Parameters</th>
<th align="center">Abbreviation</th>
<th align="center">Default Value</th>
<th align="center">Distribution</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">
<bold>Body weight (kg)</bold>
</td>
<td align="center">BW</td>
<td align="center">72.3</td>
<td align="center">N<xref ref-type="table-fn" rid="Tfn2">
<sup>a</sup>
</xref>(72.3, 9.05)</td>
</tr>
<tr>
<td align="left">
<bold>% BW</bold>
</td>
</tr>
<tr>
<td align="left">&#x2003;Total vascularised tissues</td>
<td align="center">VT</td>
<td align="center">0.95</td>
<td align="center">-</td>
</tr>
<tr>
<td align="left">&#x2003;Liver</td>
<td align="center">VLiC</td>
<td align="center">3.09</td>
<td align="center">N(3.09, 0.8)</td>
</tr>
<tr>
<td align="left">&#x2003;Fat</td>
<td align="center">VFaC</td>
<td align="center">19.5</td>
<td align="center">LN(3.42, 0.43)</td>
</tr>
<tr>
<td align="left">&#x2003;Gut</td>
<td align="center">VGuC</td>
<td align="center">1.50</td>
<td align="center">U(1.19, 1.84)</td>
</tr>
<tr>
<td align="left">&#x2003;Stomach</td>
<td align="center">VStC</td>
<td align="center">0.22</td>
<td align="center">N(0.22, 0.07)</td>
</tr>
<tr>
<td align="left">&#x2003;Slowly perfused tissue</td>
<td align="center">VSpdC</td>
<td align="center">60.7</td>
<td align="center">N(60.7, 9.4)</td>
</tr>
<tr>
<td align="left">&#x2003;Rapidly perfused tissue</td>
<td align="center">VRpdC</td>
<td align="center">3.71</td>
<td align="center">N(3.7, 0.26)</td>
</tr>
<tr>
<td align="left">&#x2003;Blood</td>
<td align="center">VBldC</td>
<td align="center">5.0</td>
<td align="center">U(2.5, 10)</td>
</tr>
<tr>
<td align="left">&#x2003;Lymph</td>
<td align="center">VLymphC</td>
<td align="center">0.36</td>
<td align="center">U(0.18, 0.72)</td>
</tr>
<tr>
<td align="left">
<bold>Cardiac output (L h<sup>&#x2212;1</sup> kg<sup>&#x2212;1</sup> BW)</bold>
</td>
<td align="center">QCC</td>
<td align="center">14</td>
<td align="center">N(13.8, 2.5)</td>
</tr>
<tr>
<td align="left">
<bold>% Cardiac output</bold>
</td>
</tr>
<tr>
<td align="left">&#x2003;Liver</td>
<td align="center">QHepartC</td>
<td align="center">6.0</td>
<td align="center">N(6.89, 0.52)</td>
</tr>
<tr>
<td align="left">&#x2003;Fat</td>
<td align="center">QFaC</td>
<td align="center">5.0</td>
<td align="center">N(5.3, 0.3)</td>
</tr>
<tr>
<td align="left">&#x2003;Gut</td>
<td align="center">QGuC</td>
<td align="center">14.9</td>
<td align="center">U(13.2, 16.6)</td>
</tr>
<tr>
<td align="left">&#x2003;Stomach</td>
<td align="center">QStC</td>
<td align="center">1.1</td>
<td align="center">N(1.1, 0.08)</td>
</tr>
<tr>
<td align="left">&#x2003;Slowly perfused tissue</td>
<td align="center">QSpdC</td>
<td align="center">27.0</td>
<td align="center">N(28.7, 1.91)</td>
</tr>
<tr>
<td align="left">&#x2003;Rapidly perfused tissue</td>
<td align="center">QRpdC</td>
<td align="center">42.0</td>
<td align="center">N(43.1, 2.78)</td>
</tr>
<tr>
<td align="left">&#x2003;Lymph</td>
<td align="center">QLymphC</td>
<td align="center">0.04</td>
<td align="center">U(0.02, 0.08)</td>
</tr>
<tr>
<td align="left">
<bold>Metabolic Clearance (minutes)</bold>
</td>
</tr>
<tr>
<td align="left">&#x2003;In vitro half-life DPHP</td>
<td align="center">T<sub>&#xbd;DPHP</sub>
</td>
<td align="center">3<xref ref-type="table-fn" rid="Tfn3">
<sup>b</sup>
</xref>
</td>
<td align="center">U(15, 60)</td>
</tr>
<tr>
<td align="left">&#x2003;In vitro half-life MPHP</td>
<td align="center">T<sub>&#xbd;MPHP</sub>
</td>
<td align="center">8.05</td>
<td align="center">N(30.54, 2.39)</td>
</tr>
<tr>
<td align="left">&#x2003;In vivo DPHP gut half-life</td>
<td align="center">T<sub>&#xbd;DPHP_gut</sub>
</td>
<td align="center">60<xref ref-type="table-fn" rid="Tfn4">
<sup>c</sup>
</xref>
</td>
<td align="center">U(15, 60)</td>
</tr>
<tr>
<td align="left">
<bold>Elimination (gut to bowel) (h<sup>&#x2212;1</sup>)</bold>
</td>
</tr>
<tr>
<td align="left">&#x2003;DPHP</td>
<td align="center">k1_DPHP_gut</td>
<td align="center">0.1</td>
<td align="center">U(0.05, 0.15)</td>
</tr>
<tr>
<td align="left">&#x2003;MPHP</td>
<td align="center">k1_MPHP_gut</td>
<td align="center">0.1</td>
<td align="center">U(0.05, 0.15)</td>
</tr>
<tr>
<td align="left">
<bold>Elimination (liver to bile) (h<sup>&#x2212;1</sup>)</bold>
</td>
</tr>
<tr>
<td align="left">&#x2003;DPHP</td>
<td align="center">k1_DPHP_liver</td>
<td align="center">10</td>
<td align="center">U(5, 15)</td>
</tr>
<tr>
<td align="left">&#x2003;MPHP</td>
<td align="center">k1_MPHP_liver</td>
<td align="center">1</td>
<td align="center">U(0.5, 1.5)</td>
</tr>
<tr>
<td align="left">
<bold>Microsomal protein yield (mg g<sup>&#x2212;1</sup>)</bold>
</td>
</tr>
<tr>
<td align="left">&#x2003;Hepatic</td>
<td align="center">MPY</td>
<td align="center">34<xref ref-type="table-fn" rid="Tfn5">
<sup>d</sup>
</xref>
</td>
<td align="center">See <xref ref-type="table" rid="T4">Table&#x20;4</xref>
</td>
</tr>
<tr>
<td align="left">&#x2003;Gut</td>
<td align="center">MPY<sub>gut</sub>
</td>
<td align="center">3.9<xref ref-type="table-fn" rid="Tfn6">
<sup>e</sup>
</xref>
</td>
<td align="center">U(1.95, 7.8)</td>
</tr>
<tr>
<td align="left">
<bold>Fraction Bound in plasma (proportion)</bold>
</td>
</tr>
<tr>
<td align="left">&#x2003;DPHP</td>
<td align="left">FBDPHP</td>
<td align="center">0.0025</td>
<td align="left">U(10<sup>-5</sup>, 0.01)</td>
</tr>
<tr>
<td align="left">&#x2003;MPHP</td>
<td align="left">FBMPHP</td>
<td align="center">0.0146</td>
<td align="left">U(0.001, 0.01)</td>
</tr>
<tr>
<td align="left">
<bold>Gastric emptying (h<sup>&#x2212;1</sup>)<xref ref-type="table-fn" rid="Tfn7">
<sup>f</sup>
</xref>
</bold>
</td>
</tr>
<tr>
<td align="left">&#x2003;Maximum</td>
<td align="left">k<sub>(max)</sub>
</td>
<td align="center">10.2</td>
<td align="left">U(5.1, 20.4)</td>
</tr>
<tr>
<td align="left">&#x2003;Minimum</td>
<td align="left">k<sub>(min)</sub>
</td>
<td align="center">0.005</td>
<td align="left">U(0.0025, 0.01)</td>
</tr>
<tr>
<td align="left">
<bold>Absorption (h<sup>&#x2212;1</sup>)</bold>
</td>
</tr>
<tr>
<td align="left">&#x2003;Gut</td>
<td align="left">k<sub>Ga</sub>
</td>
<td align="center">25.1</td>
<td align="left">U(12.55, 50.2)</td>
</tr>
<tr>
<td align="left">&#x2003;Time taken to consume dose (h)</td>
<td align="left">DRINKTIME</td>
<td align="center">0.25</td>
<td align="left">U(0.125, 0.5)</td>
</tr>
<tr>
<td align="left">&#x2003;Absorption in Stomach</td>
<td align="left">BELLYPERM</td>
<td align="center">0.685</td>
<td align="left">U(0.34, 0.99)</td>
</tr>
<tr>
<td align="left">&#x2003;Absorption in GI Tract</td>
<td align="left">GIPERM</td>
<td align="center">5.1</td>
<td align="left">U(0.1, 0.3)</td>
</tr>
<tr>
<td align="left">&#x2003;Absorption in Lymph via stomach</td>
<td align="left">BELLYPERMLymph</td>
<td align="center">0.685</td>
<td align="left">U(0.34, 0.99)</td>
</tr>
<tr>
<td align="left">&#x2003;Absorption in Lymph via GI Tract</td>
<td align="left">GIPERMLymph</td>
<td align="center">5.1</td>
<td align="left">U(2.6, 7.6)</td>
</tr>
<tr>
<td align="left">&#x2003;Absorption into blood from lymph</td>
<td align="left">K1Lymph</td>
<td align="center">0.2</td>
<td align="left">U(0.1, 0.3)</td>
</tr>
<tr>
<td align="left">&#x2003;Fraction of dose taken up into liver</td>
<td align="left">FRACDOSEHep</td>
<td align="center">0.1</td>
<td align="left">See <xref ref-type="table" rid="T4">Table&#x20;4</xref>
</td>
</tr>
<tr>
<td align="left">&#x2003;Fraction of dose taken up into lymphatic system</td>
<td align="left">FracDOSELymph</td>
<td align="center">0.05</td>
<td align="left"/>
</tr>
<tr>
<td align="left">&#x2003;Fraction of MPHP metabolised</td>
<td align="left">FracMetab (cx and OH)</td>
<td align="left"/>
<td align="left">See <xref ref-type="table" rid="T4">Table&#x20;4</xref>
</td>
</tr>
<tr>
<td align="left">
<bold>Urinary elimination rate (h<sup>&#x2212;1</sup>)</bold>
</td>
</tr>
<tr>
<td align="left">&#x2003;OH-MPHP</td>
<td align="left">K1_MOH</td>
<td align="center">0.1</td>
<td align="left">U(0.05, 0.15)</td>
</tr>
<tr>
<td align="left">&#x2003;cx-MPHP</td>
<td align="left">K1_cx</td>
<td align="center">0.1</td>
<td align="left">U(0.05, 0.15)</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="Tfn2">
<label>a</label>
<p>Distributions, N &#x3d; normal, LN &#x3d; Lognormal, U &#x3d; uniform</p>
</fn>
<fn id="Tfn3">
<label>b</label>
<p>Estimated</p>
</fn>
<fn id="Tfn4">
<label>c</label>
<p>Estimated</p>
</fn>
<fn id="Tfn5">
<label>d</label>
<p>(Bartar et&#x20;al., 2007; Howgate et&#x20;al., 2006)</p>
</fn>
<fn id="Tfn6">
<label>e</label>
<p>(Pacifici, et&#x20;al., 1988; Soars, et&#x20;al., 2002)</p>
</fn>
<fn id="Tfn7">
<label>f</label>
<p>(Loizou and Spendiff, 2004)</p>
</fn>
</table-wrap-foot>
</table-wrap>
</sec>
<sec id="s2-9">
<title>Statistical Analysis</title>
<sec id="s2-9-1">
<title>Parameter Distributions</title>
<p>Probability distributions for uncertainty and sensitivity analysis of the final PBPK model are listed in <xref ref-type="table" rid="T3">Table&#x20;3</xref>. Anatomical and physiological parameter distributions were obtained from the freely available web-based application PopGen (<xref ref-type="bibr" rid="B40">McNally et&#x20;al., 2014</xref>). A population of 10,000 individuals comprising of 100% Caucasian males was generated. The range of ages, heights and body weights supplied as input to PopGen were chosen to encompass the characteristics of the volunteers who participated in the human volunteer study (<xref ref-type="bibr" rid="B28">Klein et&#x20;al., 2018</xref>). Parameter ranges for organ masses and blood flows were modelled by normal or log-normal distributions as appropriate with parameters estimated from the sample and truncated at the 5th and 95th percentiles.</p>
<p>Uniform distributions were ascribed to the various delay terms and uptake and elimination rates. The upper and lower bounds in <xref ref-type="table" rid="T3">Table&#x20;3</xref> were refined during the model development process. The tabulated values are therefore based upon expert judgement and represent conservative yet credible bounding estimates.</p>
</sec>
</sec>
<sec id="s2-10">
<title>Uncertainty Analysis</title>
<p>As described above, uncertainty analysis was conducted throughout the model development process in order to efficiently establish the bounding behaviour of the model (i.e. the variations in model outputs under study that were consistent with the current version of the model, and parameter value uncertainty defined through probability distributions). A 200 point maxi-min Latin Hypercube Design (LHD) was created based upon the probability distributions ascribed to model parameters and the PBPK model was run for each of these design points; the behaviour of the final model was studied based upon the probability distributions given in <xref ref-type="table" rid="T3">Table&#x20;3</xref>.</p>
<p>The development process followed here was broadly similar to that of (<xref ref-type="bibr" rid="B42">McNally et&#x20;al., 2019</xref>). However whereas (<xref ref-type="bibr" rid="B42">McNally et&#x20;al, 2019</xref>) monitored only three outputs from their PBPK model for DINCH, eight outputs from the model for DPHP were monitored in order to study the absorption, uptake, metabolism and excretion of DPHP, these were: amount of DPHP (mg) in the bowel compartment (i.e. DPHP excreted in faeces), amount of DPHP (mg) in the lymph compartment, concentrations of DPHP and MPHP in venous blood, masses of DPHP and MPHP in the plasma compartment (i.e. bound to proteins within plasma and hence unavailable for metabolism), rates of deposition of OH-MPHP and cx-MPHP in urine (mg/hour). Furthermore mass balance of DPHP and MPHP were monitored to ensure that mass balance was retained for all the tested parameter variations. The differing units of the outputs under study reflect the different aspects of model outputs that the uncertainty analysis was designed to study. This phase of work is only briefly reported on in results.</p>
</sec>
<sec id="s2-11">
<title>Sensitivity Analysis</title>
<p>Sensitivity analysis was conducted throughout the model development process in order to study the key model output sensitivities for each version of the model under development. A two-phased GSA was implemented (<xref ref-type="bibr" rid="B41">McNally et&#x20;al., 2011</xref>; <xref ref-type="bibr" rid="B36">Loizou et&#x20;al., 2015</xref>) comprising of elementary effects screening (Morris Test) followed by a variance-based approach. Results from sensitivity analysis for the final model were obtained using the probability distributions given in <xref ref-type="table" rid="T3">Table&#x20;3</xref>.</p>
<p>A total of 59 parameters were varied in elementary effects screening, with five elementary effects per input computed, leading to a design of 300 runs of the PBPK model. The model outputs studied are described&#x20;below.</p>
<p>Concentrations of DPHP and MPHP in venous blood at 0.5, 3 and 12&#xa0;h and 1, 3 and 12&#xa0;h following ingestion, respectively were studied using elementary effects screening. The three output times studied were broadly of representative of the following periods in the concentration-time courses: prior to peak concentration (of DPHP and MPHP); post peak concentration; and returning to baseline (zero) concentrations. Rates of deposition of OH-MPHP and cx-MPHP in urine were studied at 3-, 12- and 20-h following ingestion for both model outputs with these times corresponding to the periods where peak concentration in urine was reached; when the first harmonic (due to `hepatic recirculation) was predicted (12&#xa0;h); and returning to baseline. Finally, the concentrations of DPHP and MPHP in plasma were studied. Rather than studying model output at specific time points, instead the peak concentrations of DPHP and MPHP in plasma; the times that corresponded to these peak concentrations; and the rate of change of DPHP and MPHP in plasma over the hour following the peak concentrations, were extracted from each of the 300 model runs. These measures were chosen since they proved to be more useful metrics for understanding the BM data of <xref ref-type="bibr" rid="B28">Klein et&#x20;al. (2018)</xref>, and in particular the more rapid clearance from plasma than would be expected given the predictions of logP (and from this an estimate of protein binding) (<xref ref-type="bibr" rid="B42">McNally et&#x20;al., 2019</xref>). This phase of sensitivity analysis is only briefly described in results.</p>
<p>All parameters that were within 0.2 of the maximum value of &#xb5;&#x2a; (one of the two measures computed in elementary effects screening) for any of the 18 metrics studied (three metrics for each of the six outputs described above) were retained and studied in the second phase of analysis using the variance-based analysis.</p>
<p>In the second phase of analysis 31 retained parameters were studied using the extended Fourier Amplitude Sensitivity Test (eFAST). In this analysis 1,000 runs per retained parameter were conducted, leading to 31,000 simulations of the PBPK model. In this more computationally expensive phase of sensitivity analysis, the rates of deposition of OH-MPHP and cx-MPHP in urine and concentrations of DPHP and MPHP in plasma were studied.</p>
</sec>
<sec id="s2-12">
<title>Calibration</title>
<p>Calibration of a subset of sensitive model parameters using the BM data of (<xref ref-type="bibr" rid="B28">Klein, et&#x20;al., 2018</xref>) was attempted. A Bayesian approach was followed (<xref ref-type="bibr" rid="B39">McNally et&#x20;al., 2012</xref>). This requires the specification of a joint prior distribution for the parameters under study, which is refined through a comparison of PBPK model predictions and measurements within a statistical model. The resulting (refined) parameter space that is consistent with the prior specification and measurements is the posterior distribution.</p>
<p>The final calibration model utilised data from five of the six individuals (data from individual E were unusual and thus excluded) from the BM study of (<xref ref-type="bibr" rid="B28">Klein et&#x20;al., 2018</xref>) with data on four specific outputs formally compared within the calibration model. Concentrations of DPHP and MPHP (<italic>CBlood DPHP</italic> and <italic>CBlood MPHP</italic>) and the rates of deposition of OH-MPHP and cx-MPHP (mg/hour) into the bladder (<italic>RUrine OH</italic> and <italic>RUrine</italic> cx) were computed from the raw data (<xref ref-type="bibr" rid="B28">Klein et&#x20;al., 2018</xref>). The latter measure i.e. the concentration (mg/L), the volume of the void (ml) and the times between voids (hours)) &#x2013; (see for example <xref ref-type="bibr" rid="B43">Nehring et&#x20;al. (2020)</xref> represents the underlying trends in concentration response data in a more precise manner than expressing the metabolite concentration relative to creatinine concentration. These measurements were compared to corresponding predictions from the PBPK model using the statistical models depicted in <xref ref-type="disp-formula" rid="e7">Eqs. 7</xref>&#x2013;<xref ref-type="disp-formula" rid="e10">10</xref>.</p>
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</inline-formula>, <inline-formula id="inf4">
<mml:math id="m9">
<mml:mrow>
<mml:msub>
<mml:mi>&#x3bc;</mml:mi>
<mml:mrow>
<mml:mi>D</mml:mi>
<mml:mi>P</mml:mi>
<mml:mi>H</mml:mi>
<mml:mi>P</mml:mi>
</mml:mrow>
</mml:msub>
<mml:msub>
<mml:mrow>
<mml:mrow>
<mml:mo>(</mml:mo>
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<mml:mi>&#x3b8;</mml:mi>
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<mml:mi>i</mml:mi>
<mml:mi>j</mml:mi>
</mml:mrow>
</mml:msub>
</mml:mrow>
</mml:math>
</inline-formula>and <inline-formula id="inf5">
<mml:math id="m10">
<mml:mrow>
<mml:msub>
<mml:mi>&#x3bc;</mml:mi>
<mml:mrow>
<mml:mi>M</mml:mi>
<mml:mi>P</mml:mi>
<mml:mi>H</mml:mi>
<mml:mi>P</mml:mi>
</mml:mrow>
</mml:msub>
<mml:msub>
<mml:mrow>
<mml:mrow>
<mml:mo>(</mml:mo>
<mml:mrow>
<mml:mi>&#x3b8;</mml:mi>
<mml:mo>,</mml:mo>
<mml:msub>
<mml:mi>&#x3c9;</mml:mi>
<mml:mi>j</mml:mi>
</mml:msub>
</mml:mrow>
<mml:mo>)</mml:mo>
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<mml:mi>j</mml:mi>
</mml:mrow>
</mml:msub>
</mml:mrow>
</mml:math>
</inline-formula>denote the predictions from the PBPK model corresponding to parameters <inline-formula id="inf6">
<mml:math id="m11">
<mml:mrow>
<mml:mrow>
<mml:mo>(</mml:mo>
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</inline-formula>. The vectors <inline-formula id="inf7">
<mml:math id="m12">
<mml:mi>&#x3b8;</mml:mi>
</mml:math>
</inline-formula> and <inline-formula id="inf8">
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</p>
<p>Prior distributions for global and local parameters in the PBPK model were taken from <xref ref-type="table" rid="T3">Table&#x20;3</xref> (for the sensitive parameters that were studied). Non-informative gamma (0.01, 0.01) prior distributions were assumed for the four standard deviation parameters.</p>
<p>Inference for the model parameters was made using Markov chain Monte Carlo (MCMC) implemented in MCSim (see Software). Inference for model parameters in the final calibration model was made using thermo-dynamic integration (TI) as described in <xref ref-type="bibr" rid="B11">Bois et&#x20;al. (2020)</xref>. A single chain of 1,000,000 iterations was run with every 10th retained.</p>
</sec>
<sec id="s2-13">
<title>Software</title>
<p>The PBPK model was written in the R language and run using the RStudio and RVis software applications during the development of the PBPK model. PBPK models were solved using the deSolve package of R. The DiceDesign package of R was used for generating Latin Hypercube designs. GSA of model outputs (through elementary effects screening and eFAST) were conducted using the Sensitivity package of R. The reshape2 package of R was used for reshaping of data for plotting and other processing of results.</p>
<p>The PBPK model was rewritten in the GNU MCSim language prior to calibration. MCMC was undertaken using the TI option within GNU MCSim</p>
<p>All plots were created using R and the gg2plot package.</p>
</sec>
</sec>
<sec sec-type="results" id="s3">
<title>Results</title>
<sec id="s3-1">
<title>Uncertainty and Sensitivity Analysis</title>
<p>In <xref ref-type="fig" rid="F4">Figure&#x20;4</xref> a small subset of results from uncertainty analysis of the final model are shown: each curve shows the predictions of a particular model output corresponding to a design point. These plots indicate that the model structure remains stable over a wide range parameter values. <xref ref-type="fig" rid="F4">Figures 4A&#x2013;C</xref> show the mass of DPHP within the plasma, lymph and bowel compartments and were used to study the range of behaviours of specific aspects of the model that could be achieved based upon the form of the PBPK model and through variations in the uncertain parameters. Through this uncertainty analysis of the mass of DPHP in plasma (<xref ref-type="fig" rid="F4">Figure&#x20;4A</xref>) the effect of protein binding on the mass retained and subsequent elimination from plasma could be studied. Specifically, in this exploratory phase of work we had a particular interest in attempting to replicate the unusual findings from (<xref ref-type="bibr" rid="B29">Klein et&#x20;al., 2016</xref>), who reported peak concentrations of DPHP in the blood of volunteers which occurred later than the corresponding peak of the metabolite MPHP in blood and also later than peak concentrations of second order metabolites in urine. Through uncertainty analysis of DPHP in the lymph, variability in the uptake, retention and elimination of DPHP in the lymph compartment could be studied. The uncertainty analysis of DPHP in the bowel allowed the study of variability in the fraction of DPHP that was initially unabsorbed and the further removal of DPHP following elimination in bile. <xref ref-type="fig" rid="F4">Figure&#x20;4D</xref> shows predictions of the rate of elimination of OH-MPHP in urine (mg/hr), one of the chosen metrics for calibration, and was studied to establish how well the unique trends in urine voids from the six volunteers could be captured by the final model. Other checks on a range of outputs or functions of model outputs (masses, rates and concentrations) were also undertaken in this phase of modelling to ensure behaviour of the model appeared reasonable over the range of parameter space specified through probability distributions.</p>
<fig id="F4" position="float">
<label>FIGURE 4</label>
<caption>
<p>Uncertainty analysis. Variability in the mass of DPHP in plasma (mg) <bold>(A)</bold>, bowel (mg) <bold>(B)</bold> and lymph (mg) <bold>(C)</bold> and variability in predicted rates of elimination of OH-MPHP in urine (mg/hr) <bold>(D)</bold>.</p>
</caption>
<graphic xlink:href="fphar-12-692442-g004.tif"/>
</fig>
<p>
<xref ref-type="fig" rid="F5">Figure&#x20;5</xref> shows the results from elementary effects screening (Morris Test) applied to the mass of DPHP in plasma. A high &#x3bc;&#x2a; indicates a factor with an important overall influence on model output; a high &#x3c3; indicates either a factor interacting with other factors or a factor whose effects are non-linear. The magnitude of &#x3bc;&#x2a; and &#x3c3; for each model parameter is relative, i.e.,&#x20;a parameter has a low &#x3bc;&#x2a; relative to the parameter with the highest &#x3bc;&#x2a;. Results from this technique are usually obtained at specific time points, i.e. sensitivity analysis of a given model output at say, 1&#xa0;h following dosing. However sensitivity analysis can be applied to any chosen model outputs calculated from each model run specified through the design. The results shown <xref ref-type="fig" rid="F5">Figure&#x20;5</xref> correspond to some unusual measures calculated from model output that were chosen to study particular aspects of model behaviour: sensitivity analysis of the peak mass of DPHP in plasma (mg) (A), the time when peak concentration was reached (hours after dosing) (B) and the rate of change of DPHP in plasma (mg/hour) in the hour following peak concentration (C). The parameters with lower overall importance are clustered toward zero of both axes. Unfortunately, we could not prevent the overlapping of some parameter labels in this region (<xref ref-type="fig" rid="F5">Figure&#x20;5</xref>).</p>
<fig id="F5" position="float">
<label>FIGURE 5</label>
<caption>
<p>Elementary effects screening (Morris Test) of the mass of DPHP in plasma. Sensitivity of the peak mass of DPHP in plasma (mg) <bold>(A)</bold>, the time when peak concentration was reached (hours after dosing) <bold>(B)</bold> and the rate of change of DPHP in plasma (mg/hour) in the hour following peak concentration <bold>(C)</bold>. Areas with overlapping parameter labels represent clusters of parameters with minimal sensitivity.</p>
</caption>
<graphic xlink:href="fphar-12-692442-g005.tif"/>
</fig>
<p>The parameters ranked as most important by the Morris test were analysed by eFAST. The period from the start of the simulation to 20&#xa0;h showed the most variance in blood concentrations of DPHP and MPHP. The most important parameters were reduced further in number and ranked as follows: FBMPHP, FBDPHP, FracDoseLymph, FracDoseHep, Lymphlag, PbaM, QCC, K1Lymph, VspdC, VliC, QguC, and VbldC. The fractions of MPHP and DPHP bound to plasma proteins were significantly more important than the other parameters over this period.</p>
<p>The period from the start of the simulation to 25&#xa0;h showed the most variance in urinary excretion of OH-MPHP and cx-MPHP. The most important parameters were ranked as follows: FracDoseHep, FracMetabMOH, FracMetabcx, BW, K1_MOH, K1_cx, QCC, GIPERM1, PguM, QguC, PliM, and PbaM. The first four parameters were significantly more important for variance in urinary excretion than the other parameters over this period.</p>
</sec>
<sec id="s3-2">
<title>Calibration</title>
<p>Summary statistics based upon the retained sample (posterior median and a 95% credible interval) for the global and local (volunteer specific) parameters are provided in <xref ref-type="table" rid="T3">Table&#x20;3</xref> and <xref ref-type="table" rid="T4">Table&#x20;4</xref> respectively. The fit of the calibrated model is shown in <xref ref-type="fig" rid="F6">Figures 6A&#x2013;D</xref>, <xref ref-type="fig" rid="F7">Figures 7A&#x2013;D</xref> and <xref ref-type="fig" rid="F8">Figures 8A&#x2013;D</xref> for three of the five participants. The trends for the individual shown in <xref ref-type="fig" rid="F8">Figure&#x20;8</xref> are broadly representative of the two individuals whose data are not shown. The central estimates indicated in plots correspond to the posterior mode whereas the shaded regions represent 95% intervals for the respective curves. This is a pointwise credible interval which was derived through running the PBPK model for each retained parameter set, ordering the predictions by magnitude at each time point and reading off the 2.5<sup>th</sup> and 97.5<sup>th</sup> percentiles.</p>
<table-wrap id="T4" position="float">
<label>TABLE 4</label>
<caption>
<p>Summary statistics from marginal posterior distributions for calibrated global parameters.</p>
</caption>
<table>
<thead valign="top">
<tr>
<th align="left">Parameter</th>
<th align="center">Posterior median (95%credible interval)</th>
</tr>
</thead>
<tbody valign="top">
<tr>
<td align="left">FB_DPHP</td>
<td align="center">0.991 (0.989, 0.995)</td>
</tr>
<tr>
<td align="left">FB_MPHP</td>
<td align="center">0.975 (0.956, 0.986)</td>
</tr>
<tr>
<td align="left">DPHP_Gut_half_life</td>
<td align="center">56.80 (46.96, 59.90)</td>
</tr>
<tr>
<td align="left">DPHP_half_life</td>
<td align="center">4.38 (3.05, 9.10)</td>
</tr>
<tr>
<td align="left">Pbab</td>
<td align="center">22.92 (9.10, 29.70)</td>
</tr>
<tr>
<td align="left">Pgub</td>
<td align="center">20 (14.20, 26.98)</td>
</tr>
<tr>
<td align="left">Plib</td>
<td align="center">4.22 (1.14, 23.14)</td>
</tr>
<tr>
<td align="left">PbaM</td>
<td align="center">31.84 (8.37, 49.17)</td>
</tr>
<tr>
<td align="left">PliM</td>
<td align="center">14.92 (1.15, 48.51)</td>
</tr>
<tr>
<td align="left">PguM</td>
<td align="center">38.57 (24.70, 49.33)</td>
</tr>
<tr>
<td align="left">K1_MOH</td>
<td align="center">0.973 (0.87, 0.99)</td>
</tr>
<tr>
<td align="left">K1_cx</td>
<td align="center">0.778 (0.67, 0.89)</td>
</tr>
<tr>
<td align="left">FracMetab_OH</td>
<td align="center">0.24 (0.21, 0.31)</td>
</tr>
<tr>
<td align="left">FracMetab_cx</td>
<td align="center">0.011 (0.01, 0.014)</td>
</tr>
<tr>
<td align="left">K1_DPHP_Liver</td>
<td align="center">3.09 (0.1, 16.9)</td>
</tr>
<tr>
<td align="left">K1_MPHP_Liver</td>
<td align="center">0.9 (0.02, 10.9)</td>
</tr>
<tr>
<td align="left">K1_DPHP_Gut</td>
<td align="center">0.3 (0.04, 0.5)</td>
</tr>
<tr>
<td align="left">K1_DPHP_Gut</td>
<td align="center">0.4 (0.07, 0.5)</td>
</tr>
<tr>
<td align="left">
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</inline-formula>
</td>
<td align="center">0.018 (0.04, 0.024)</td>
</tr>
<tr>
<td align="left">
<inline-formula id="inf14">
<mml:math id="m23">
<mml:mrow>
<mml:msub>
<mml:mi>&#x3c3;</mml:mi>
<mml:mrow>
<mml:mi>M</mml:mi>
<mml:mi>P</mml:mi>
<mml:mi>H</mml:mi>
<mml:mi>P</mml:mi>
</mml:mrow>
</mml:msub>
</mml:mrow>
</mml:math>
</inline-formula>
</td>
<td align="center">0.019 (0.016, 0.024)</td>
</tr>
</tbody>
</table>
</table-wrap>
<fig id="F6" position="float">
<label>FIGURE 6</label>
<caption>
<p>Fit of the calibrated model to data <bold>(A)</bold> blood DPHP, <bold>(B)</bold> blood MPHP and urinary excretion of <bold>(C)</bold> OH-MPHP and <bold>(D)</bold>_cx-MPHP for volunteer A using global (non-volunteer specific) and local (volunteer specific) parameters provided in <xref ref-type="table" rid="T2">Table&#x20;2</xref>, <xref ref-type="table" rid="T3">Table&#x20;3</xref>, and <xref ref-type="table" rid="T4">Table&#x20;4</xref>. The central estimates indicated in plots correspond to the posterior mode whereas the shaded regions represent 95% intervals for the respective curves.</p>
</caption>
<graphic xlink:href="fphar-12-692442-g006.tif"/>
</fig>
<fig id="F7" position="float">
<label>FIGURE 7</label>
<caption>
<p>Fit of the calibrated model to data <bold>(A)</bold> blood DPHP, <bold>(B)</bold> blood MPHP and urinary excretion of <bold>(C)</bold> OH-MPHP and <bold>(D)</bold> cx-MPHP for volunteer C using global (non-volunteer specific) and local (volunteer specific) parameters provided in <xref ref-type="table" rid="T3">Table&#x20;3</xref> and <xref ref-type="table" rid="T4">Table&#x20;4</xref>. The central estimates indicated in plots correspond to the posterior mode whereas the shaded regions represent 95% intervals for the respective curves.</p>
</caption>
<graphic xlink:href="fphar-12-692442-g007.tif"/>
</fig>
<fig id="F8" position="float">
<label>FIGURE 8</label>
<caption>
<p>Fit of the calibrated model data <bold>(A)</bold> blood DPHP, <bold>(B)</bold> blood MPHP and urinary excretion of <bold>(C)</bold> OH-MPHP and <bold>(D)</bold>_cx-MPHP for volunteer D using global (non-volunteer specific) and local (volunteer specific) parameters provided in <xref ref-type="table" rid="T3">Table&#x20;3</xref> and <xref ref-type="table" rid="T4">Table&#x20;4</xref>. The central estimates indicated in plots correspond to the posterior mode whereas the shaded regions represent 95% intervals for the respective curves. The trends for volunteer D were broadly representative of volunteers B and F whose data are not&#x20;shown.</p>
</caption>
<graphic xlink:href="fphar-12-692442-g008.tif"/>
</fig>
<p>The BM data from each of the study participants showed unique trends. The blood DPHP data indicated differences in lag prior to uptake, rates of uptake and fractions absorbed from the gut. In the blood data of some participants, the first order metabolite MPHP was measurable in blood prior to the appearance of parent chemical (<xref ref-type="fig" rid="F6">Figure&#x20;6A</xref> and <xref ref-type="fig" rid="F7">Figure&#x20;7A</xref>). Uptake of DPHP appeared to be multi-phased in some participants. The PBPK model contained nine parameters that were tuned to the BM data from each participant for fitting the hepatic uptake of DPHP and a further three parameters governing uptake into the lymphatic system and subsequent deposition into blood at the thoracic duct (<xref ref-type="table" rid="T3">Table&#x20;3</xref>). The results in <xref ref-type="fig" rid="F6">Figures 6</xref>&#x2013;<xref ref-type="fig" rid="F8">8</xref> demonstrate that the BM data on DPHP in blood were captured by the calibrated model. The differences in the calibrated individual specific parameters (<xref ref-type="table" rid="T3">Table&#x20;3</xref>) reflect the large differences in the trends of DPHP in blood for the study participants.</p>
<p>In contrast, the rate of deposition of second order metabolites in urine was mainly governed through global (non-volunteer specific) parameters (<xref ref-type="table" rid="T4">Table&#x20;4</xref>). Reasonable fits were obtained for the urinary excretion of OH-MPHP and cx-MPHP with the model successfully fitting earlier peaks in the urine compared to blood. Enterohepatic recirculation of DPHP was an important mechanism which is observed in the harmonics seen in the OH-MPHP and cx-MPHP time courses at intervals of approximately 8&#xa0;h post peak concentration (<xref ref-type="fig" rid="F6">Figures 6C,D</xref> and <xref ref-type="fig" rid="F8">Figures 8C,D</xref>). The fit to the data shown in <xref ref-type="fig" rid="F7">Figures 7C,D</xref> was poorer and appears to be consistent with a second absorption event (not explicitly captured in the model). Data from another volunteer, not used in final calibration, showed even stronger evidence of a second absorption event. As enterohepatic recirculation was modelled using global parameters, the differences seen in the simulations of urine data for these three participants appear to arise as a consequence of differences in uptake of&#x20;DPHP.</p>
<p>The fits to MPHP in blood were generally quite poor; particularly when MPHP spiked in blood specimens shortly after DPHP was consumed by study participants. This highlights a deficiency in the model, which does not impact upon the ability of the model to accurately predict deposition of second order metabolites in urine. We address this deficiency further in the discussion section.</p>
<p>The bound fractions of DPHP and MPHP were 0.991 (0.989, 0.995) and 0.975 (0.956, 0.986), which represent very high binding in blood, although somewhat smaller than the very high fractions predicted by algorithms. There are no known direct measurements of protein binding of DPHP or MPHP in blood although there are estimates of the &#x201c;free&#x201d; area-under-the curve (AUC) concentrations of MPHP as a proportion of total DPHP concentration which are approximately 66% (<xref ref-type="bibr" rid="B28">Klein et&#x20;al., 2018</xref>). The half -life of DPHP, which could not be estimated in&#x20;vitro incubations, was estimated in the model to be very short in the liver at 4.38&#xa0;min (3.05, 9.10), and approximately a factor of 10 greater than in the gut 56.80&#xa0;min (46.96, 59.90).</p>
<p>The vast majority of DPHP was unabsorbed from the gut. Total uptake ranged from 16.3% (13.1%, 19.3%) to 2% (1.5&#x2013;2.6%), dominated by hepatic uptake at around a factor of five greater than lymphatic uptake. The fractions of absorbed DPHP excreted as OH-MPHP and cx-MPHP were estimated as 0.24 (0.21, 0.31) and 0.011 (0.01, 0.014).</p>
<p>A comparison of simulations of entry of DPHP through the hepatic (black line) and lymphatic (blue line) routes is shown in <xref ref-type="fig" rid="F9">Figure&#x20;9</xref>. These simulations were based upon optimised parameters for individual A where with lymphatic fraction was set to zero (black lines) or the hepatic fraction set to zero (blue lines). Thus, the independent effects of absorption through the two routes at otherwise credible values for model parameters could be studied. The key biological difference between the two routes of entry is that DPHP absorbed through the hepatic route is subject to first pass metabolism, primarily in the liver, whereas the lymphatic fraction by-passes first pass metabolism. Despite the hepatic fraction being a factor of five greater, the peak plasma concentration from the two routes was similar (<xref ref-type="fig" rid="F9">Figure&#x20;9A</xref>), which indicates that a very large fraction of DPHP absorbed through the hepatic route is intercepted by the liver and never enters systemic circulation. Uptake of DPHP into the systemic circulation from either hepatic or lymphatic routes is almost completely bound to proteins in plasma and is thus neither available for distribution to organs and tissues nor for metabolism. Our simulations indicate that DPHP entering the systemic blood circulation via the lymphatic route is almost entirely held in plasma and is important for understanding trends in plasma. It does however represent a small mass of DPHP, which has a negligible impact on trends in MPHP in blood and second-order metabolites in urine. In particular, due to the high binding in plasma and the consequent reduced rate of metabolism only a shallow peak with a long tail can be seen in urinary metabolite simulations.</p>
<fig id="F9" position="float">
<label>FIGURE 9</label>
<caption>
<p>Comparison of DPHP hepatic and lymphatic routes of uptake. Simulations were based upon optimised parameters for individual A but where the lymphatic fraction (black lines) or the hepatic fraction (blue lines) was set to&#x20;zero.</p>
</caption>
<graphic xlink:href="fphar-12-692442-g009.tif"/>
</fig>
</sec>
</sec>
<sec sec-type="discussion" id="s4">
<title>Discussion</title>
<p>In this study we supplement the interpretation of the data of (<xref ref-type="bibr" rid="B28">Klein et&#x20;al., 2018</xref>) with additional insights using a PBPK model calibrated for DPHP kinetics.</p>
<p>Only a minority fraction of ingested DPHP was absorbed from&#x20;the gut. The model suggested the fraction of absorbed DPHP (quantified as the complement of the fractions entering lymphatic and hepatic circulation respectively) ranged from 2% (1.5%&#x2013;2.6) to 16.3% (13.1%, 19.3%) for the six study participants. In addition to a substantial variation in the fraction absorbed between participants, there was also a substantial variation between participants in the rate of absorption, quantified through the <italic>Gutlag</italic> and <italic>GIperm</italic> parameters. The PBPK model contains only a simple description of the gut, with modelling via a single compartment. More detailed models of the GI tract, such as the ACAT (<xref ref-type="bibr" rid="B22">Gobeau et&#x20;al., 2016</xref>) model, describe the gut as a series of linked compartments, each with their own permeability and pH. The <italic>Gutlag</italic> in our PBPK model can be interpreted as a delay until parent chemical reaches a section of the GI tract where absorption occurs. <xref ref-type="bibr" rid="B28">Klein et&#x20;al. (2018)</xref> provided detailed information on the food consumed by individual study participants and the time of consumption relative to the ingestion of DPHP. This relatively uncontrolled aspect of the human volunteer study appears to have contributed, in addition to the measured volunteer specific parameters (<xref ref-type="table" rid="T2">Table&#x20;2</xref>) to the large inter-individual variability in BM&#x20;data.</p>
<p>Some features of the BM data are difficult to interpret, such as the time to peak concentrations of second order metabolites in urine occurring prior to the time to peak of DPHP concentration in blood, which is counter-intuitive. However, deeper insights into the pharmacokinetics of DPHP in humans are possible through the development of a PBPK model. Our model suggested that the majority of the absorbed fraction of DPHP entered via the hepatic route. Metabolism of DPHP was primarily in the liver, and following eventual absorption this was rapid. A fraction of DPHP was transported from the liver tissue to the gut in bile. The rapid elimination of DPHP is explained by first pass metabolism and biliary excretion. Only traces of parent chemical and first order metabolite appeared to enter into the systemic circulation. A small fraction of DPHP (approximately 20% of that entering via the hepatic route) entered the systemic circulation via the lymphatic route. A detailed description of lymphatic flow was not described in the model: instead the simplified process of absorption into the lymph compartment and appearance in venous blood at a rate proportionate to the amount in the lymph, following a lag time in hours (<italic>Lymphlag</italic>), was described. DPHP entering via this route avoided first pass metabolism and thus entered the systemic circulation. Binding of DPHP (approx. 99%) was high although notably lower (a factor of 10) than the extreme value predicted by the predictive algorithms (<xref ref-type="table" rid="T1">Table&#x20;1</xref>). DPHP entering via the lymph was almost entirely held within the plasma compartment until stripped from proteins and metabolized and as a consequence this minor absorption route had a significant influence on DPHP in plasma. The delayed peak of DPHP concentration in venous blood (relative to MPHP in blood and second order metabolites in urine) can be explained as a result of three processes: 1) DPHP entering the systemic circulation from the lymph, 2) rapid and very high protein binding and 3) the efficiency of the liver in removing DPHP absorbed via the hepatic&#x20;route.</p>
<p>MPHP concentration peaked prior to DPHP concentration in blood specimens for five of the six volunteers. In some volunteers MPHP spiked rapidly and could be detected in blood prior to DPHP. Through the inclusion of a two compartment gut and a description of metabolism of DPHP in the gut we were able to jointly model DPHP and MPHP in blood, however it was not possible to fit MPHP in blood once data from urine specimens were also used in calibration; the very early peak of MPHP observed in blood did not result in early peaks of OH-MPHP and cx-MPHP in urine. This inconsistency would indicate a deficiency in our model. This could potentially be explained if MPHP absorbed through the gut was bound within plasma and thus unavailable for metabolism. In the PBPK model, binding in arterial blood was described however, MPHP absorbed in the gut was fully available for first pass metabolism prior to binding. A better fit to blood MPHP may potentially be achieved by describing very rapid plasma binding following absorption of MPHP in the gut. This possible change to metabolism of DPHP in the gut and the subsequent absorption of MPHP would not affect the fit to urinary metabolite data since the vast majority of metabolism of DPHP and MPHP occurs very rapidly in the liver. The biological plausibility of this mechanism would require investigation and its importance to the risk assessment of DPHP confirmed to justify subsequent modification of the&#x20;model.</p>
<p>We consider the measurements of OH-MPHP and cx-MPHP in urine to provide the most reliable guide of the fate of DPHP following ingestion. These data indicate that parent chemical was absorbed from the gut and rapidly metabolised, with metabolism almost entirely occurring within the liver, and with further rapid metabolism of MPHP in the liver. Only traces of DPHP and MPHP appear to have entered into the systemic circulation. Elimination of second order metabolites OH-MPHP and cx-MPHP from blood was rapid. The urine samples provided evidence of enterohepatic recirculation with up to three visible harmonics following peak exposure, at intervals of approximately 8&#xa0;hours; this is a new insight from our modelling that was not discussed by <xref ref-type="bibr" rid="B28">Klein et&#x20;al. (2018)</xref>. The evidence for the lymphatic route was weaker from urinary metabolite data, since binding of DPHP and MPHP results in a prolonged elimination process, and the fraction entering via the lymphatic route is modest compared to the hepatic route. Elimination of secondary metabolites of DPHP is increased over a 24-h period compared to a model that does not account for this route. (<xref ref-type="bibr" rid="B28">Klein et&#x20;al., 2018</xref>) interpreted the first harmonic of secondary metabolites in urine specimens as evidence of the lymphatic route, however our simulations indicate that a sharp peak could not be achieved from lymphatic uptake, in contrast, enterohepatic recirculation could account for such sharp peaks. We are unaware of previous work that has suggested strong evidence of enterohepatic recirculation from urinary metabolite measurements.</p>
<p>An important finding of this work is that the BM data from venous blood provide an incomplete picture of the kinetics of DPHP, and a model built and calibrated to these data alone would be a poor description of the biology &#x2013; such a model would be tuned to the minor absorption route. For extremely lipophilic substances like DPHP and other plasticizers (di-(isononyl)phthalate, cyclohexane-1,2-dicarboxylic acid, di(isononyl) ester etc.) the established paradigm of development and calibration of a PBPK model based upon animal (rat) data, and extrapolation to the human can be problematic &#x2013; the rat study of <xref ref-type="bibr" rid="B29">Klein et&#x20;al. (2016)</xref> only studied DPHP and its metabolites in blood and thus did not obtain the most useful data (from urine specimens) for understanding the biological mechanisms. Similarly, for this class of chemicals an incomplete picture may be obtained from an analysis of only urine specimens in the absence of&#x20;blood.</p>
<p>Results from uncertainty and sensitivity analyses of the final model for DPHP only were presented in this work. However, uncertainty analysis conducted using Latin Hypercube sampling and GSA (using elementary effects screening and eFAST) were utilized iteratively at various phases as the model for DPHP was being developed. Although these techniques cannot inform which biological processes may be missing from a model in development, they can quickly identify the bounding behaviour of the current version of the model and identify the key uncertain parameters that drive variability observed in dose-response in simulations. These techniques proved to be invaluable in developing, debugging and understanding a complex PBPK model. The overall framework of uncertainty and sensitivity analysis followed in this work replicates that of <xref ref-type="bibr" rid="B42">McNally et&#x20;al. (2019)</xref>, however some of the metrics studied using GSA (the timing of a peak concentration and the rate of change following the peak) are novel. This work highlights the flexibility of the GSA techniques and demonstrates that through correct application of high level analyses within a model development framework, an experienced modeller may make insights about the behaviour of the model and thus the underlying biology to narrow the research space and guide targeted future experimental evaluations.</p>
<p>Development of the model was initially in R syntax with a system of DDE&#x2019;s solved using the deSolve package. The R language offers a flexible framework for the specification of PBPK models and the deSolve package offers a wide range of solvers. Whilst this modelling environment proved to be suitable for development of the model and uncertainty and sensitivity analysis, initial attempts at calibration demonstrated that R was too slow for the calibration of DDE&#x2019;s. The PBPK model was therefore rewritten in GNU MCSim, a more suitable language for intensive computations. Calibration was conducted using the thermodynamic integration variant of MCMC (<xref ref-type="bibr" rid="B11">Bois et&#x20;al., 2020</xref>).</p>
</sec>
</body>
<back>
<sec id="s5">
<title>Data Availability Statement</title>
<p>The raw data supporting the conclusions of this article will be made available by the authors, without undue reservation.</p>
</sec>
<sec id="s6">
<title>Ethics Statement</title>
<p>The studies involving human participants were reviewed and approved by Ethics Commission of the Faculty of Medicine of the Technical University of Munich (project number 5913/13). The patients/participants provided their written informed consent to participate in this&#x20;study.</p>
</sec>
<sec id="s7">
<title>Author Contributions</title>
<p>GL, KM, AH and AL developed the PBPK model, analyzed and interpreted the data. CS measured <italic>in&#x20;vitro</italic> clearance in human microsomes and analyzed the data. All authors made significant contributions to the writing of the manuscript.</p>
</sec>
<sec id="s8">
<title>Funding</title>
<p>This work was supported by The Members of European Plasticisers (Grant No:T 50_UK HSL-02-471-0000-07-T50), a sector group of CEFIC, the European Chemical Industry Council and VinylPlus&#xae;, the voluntary sustainable development programme of the European PVC industry.</p>
</sec>
<sec sec-type="COI-statement" id="s9">
<title>Conflict of Interest</title>
<p>The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
<sec id="s10" sec-type="disclaimer">
<title>Publisher&#x2019;s Note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
</sec>
<ack>
<p>The authors thank Dr. Tim Yates for the calculation of <italic>in&#x20;vitro</italic> half-life values for MPHP and Dr. Adrian Kelsey for his contribution to the analysis of model structure. The contents of this paper, including any opinions and/or conclusions expressed, are those of the authors alone and do not necessarily reflect HSE or FDA policy.</p>
</ack>
<sec id="s11">
<title>Supplementary Material</title>
<p>The Supplementary Material for this article can be found online at: <ext-link ext-link-type="uri" xlink:href="https://www.frontiersin.org/articles/10.3389/fphar.2021.692442/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fphar.2021.692442/full&#x23;supplementary-material</ext-link>
</p>
<supplementary-material xlink:href="DataSheet1.docx" id="SM1" mimetype="application/docx" xmlns:xlink="http://www.w3.org/1999/xlink"/>
</sec>
<fn-group>
<fn id="fn1">
<label>1</label>
<p>
<ext-link ext-link-type="uri" xlink:href="https://eur-lex.europa.eu/legal-content/EN/TXT/HTML/?uri=OJ:L:2011:012:FULL&amp;from=FR">https://eur-lex.europa.eu/legal-content/EN/TXT/HTML/?uri&#x3d;OJ:L:2011:012:FULL&#x26;from&#x3d;FR</ext-link>
</p>
</fn>
<fn id="fn2">
<label>2</label>
<p>Concentration in human biological material at which, and below which, there is no risk of adverse health effects</p>
</fn>
</fn-group>
<ref-list>
<title>References</title>
<ref id="B1">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Andersen</surname>
<given-names>M. E.</given-names>
</name>
</person-group> (<year>2003</year>). <article-title>Toxicokinetic Modeling and its Applications in Chemical Risk Assessment</article-title>. <source>Toxicol. Lett.</source> <volume>138</volume> (<issue>1&#x2013;2</issue>), <fpage>9</fpage>&#x2013;<lpage>27</lpage>. <pub-id pub-id-type="doi">10.1016/s0378-4274(02)00375-2</pub-id> </citation>
</ref>
<ref id="B2">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Andersen</surname>
<given-names>M. E.</given-names>
</name>
</person-group> (<year>1995</year>). <article-title>What Do We Mean by Dosedose?</article-title> <source>Inhalation Toxicol.</source> <volume>7</volume>, <fpage>909</fpage>&#x2013;<lpage>915</lpage>. <pub-id pub-id-type="doi">10.3109/08958379509012799</pub-id> </citation>
</ref>
<ref id="B3">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Apel</surname>
<given-names>P.</given-names>
</name>
<name>
<surname>Angerer</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Wilhelm</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Kolossa-Gehring</surname>
<given-names>M.</given-names>
</name>
</person-group> (<year>2017</year>). <article-title>New Hbm Values for Emerging Substances, Inventory of Reference and Hbm Values in Force, and Working Principles of the German Human Biomonitoring Commission</article-title>. <source>Int. J.&#x20;Hyg. Environ. Health</source> <volume>220</volume> (<issue>2</issue>), <fpage>152</fpage>&#x2013;<lpage>166</lpage>. <pub-id pub-id-type="doi">10.1016/j.ijheh.2016.09.007</pub-id> </citation>
</ref>
<ref id="B4">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Barton</surname>
<given-names>H. A.</given-names>
</name>
<name>
<surname>Chiu</surname>
<given-names>W. A.</given-names>
</name>
<name>
<surname>Setzer</surname>
<given-names>R. W.</given-names>
</name>
<name>
<surname>Andersen</surname>
<given-names>M. E.</given-names>
</name>
<name>
<surname>Bailer</surname>
<given-names>A. J.</given-names>
</name>
<name>
<surname>Bois</surname>
<given-names>F. Y.</given-names>
</name>
<etal/>
</person-group> (<year>2007</year>). <article-title>Characterizing Uncertainty and Variability in Physiologically Based Pharmacokinetic Models: State of the Science and Needs for Research and Implementation</article-title>. <source>Toxicol. Sci.</source> <volume>99</volume>, <fpage>395</fpage>&#x2013;<lpage>402</lpage>. <pub-id pub-id-type="doi">10.1093/toxsci/kfm100</pub-id> </citation>
</ref>
<ref id="B5">
<citation citation-type="book">
<person-group person-group-type="author">
<name>
<surname>Barton</surname>
<given-names>H. A.</given-names>
</name>
<name>
<surname>Bessems</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Bouvier d&#x27;Yvoire</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Buist</surname>
<given-names>H.</given-names>
</name>
<name>
<surname>Clewell</surname>
<given-names>H.</given-names>
<suffix>III</suffix>
</name>
<name>
<surname>Gundert-Remy</surname>
<given-names>U.</given-names>
</name>
<etal/>
</person-group> (<year>2009</year>). <source>Principles of Characterizing and Applying Physiologically-Based Pharmacokinetic and Toxicokinetic Models in Risk Assessment. <italic>IPCS Project on the Harmonization Of Approaches To the Assessment Of Risk From Exposure To Chemicals</italic>
</source>
<italic>.</italic>
</citation>
</ref>
<ref id="B6">
<citation citation-type="book">
<collab>BASF</collab> (<year>2009</year>). <source>Palatinol110-P Two-Generation Reproduction Toxicity Study in Wistar Rats, Administration via the Diet</source>. <comment>Project No. 70R0183/02087</comment>.</citation>
</ref>
<ref id="B7">
<citation citation-type="book">
<collab>BASF</collab> (<year>2003</year>). <source>Report. Palatinol110-P&#x2014;Prenatal Development Toxicity Study in Wistar Rats. Oral Administration (Gavage)</source>. <comment>Project No. 30R0183/02046</comment>.</citation>
</ref>
<ref id="B8">
<citation citation-type="book">
<collab>BASF</collab> (<year>1995a</year>). <source>Study of the Prenatal Toxicity of Dipropylheptylphthalate in Wistar Rats after Oral Administration (Gavage)</source>. <publisher-name>Performed by BASF Aktiengesellschaft Department of Toxicology</publisher-name>. <comment>FRG. Project N10R0110/94013</comment>.</citation>
</ref>
<ref id="B9">
<citation citation-type="book">
<collab>BASF</collab> (<year>1995b</year>). <source>Subchronic Oral Toxicity Study with Dipropylheptylphthalate in Wistar Rats. Administration in the Diet for 3&#x20;Months</source>. <publisher-name>Performed by BASF Aktiengesellschaft Department of Toxicology</publisher-name>. <comment>FRG. Project No. 50C110/94025</comment>.</citation>
</ref>
<ref id="B10">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Bhat</surname>
<given-names>V. S.</given-names>
</name>
<name>
<surname>Durham</surname>
<given-names>J.&#x20;L.</given-names>
</name>
<name>
<surname>English</surname>
<given-names>J.&#x20;C.</given-names>
</name>
</person-group> (<year>2014</year>). <article-title>Derivation of an Oral Reference Dose (RfD) for the Plasticizer, Di-(2-propylheptyl)phthalate (Palatinol&#xae; 10-P)</article-title>. <source>Regul. Toxicol. Pharmacol.</source> <volume>70</volume> (<issue>1</issue>), <fpage>65</fpage>&#x2013;<lpage>74</lpage>. <pub-id pub-id-type="doi">10.1016/j.yrtph.2014.06.002</pub-id> </citation>
</ref>
<ref id="B11">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Bois</surname>
<given-names>F. Y.</given-names>
</name>
<name>
<surname>Hsieh</surname>
<given-names>N. H.</given-names>
</name>
<name>
<surname>Gao</surname>
<given-names>W.</given-names>
</name>
<name>
<surname>Chiu</surname>
<given-names>W. A.</given-names>
</name>
<name>
<surname>Reisfeld</surname>
<given-names>B.</given-names>
</name>
</person-group> (<year>2020</year>). <article-title>Well-tempered MCMC Simulations for Population Pharmacokinetic Models</article-title>. <source>J.&#x20;Pharmacokinet. Pharmacodyn.</source> <volume>47</volume> (<issue>6</issue>), <fpage>543</fpage>&#x2013;<lpage>559</lpage>. <pub-id pub-id-type="doi">10.1007/s10928-020-09705-0</pub-id> </citation>
</ref>
<ref id="B12">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Boogaard</surname>
<given-names>P. J.</given-names>
</name>
<name>
<surname>Hays</surname>
<given-names>S. M.</given-names>
</name>
<name>
<surname>Aylward</surname>
<given-names>L. L.</given-names>
</name>
</person-group> (<year>2011</year>). <article-title>Human Biomonitoring as a Pragmatic Tool to Support Health Risk Management of Chemicals-Eexamples under the EU REACH Programme</article-title>. <source>Regul. Toxicol. Pharmacol.</source> <volume>59</volume> (<issue>1</issue>), <fpage>125</fpage>&#x2013;<lpage>132</lpage>. <pub-id pub-id-type="doi">10.1016/j.yrtph.2010.09.015</pub-id> </citation>
</ref>
<ref id="B13">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Brown</surname>
<given-names>R. P.</given-names>
</name>
<name>
<surname>Delp</surname>
<given-names>M. D.</given-names>
</name>
<name>
<surname>Lindstedt</surname>
<given-names>S. L.</given-names>
</name>
<name>
<surname>Rhomberg</surname>
<given-names>L. R.</given-names>
</name>
<name>
<surname>Beliles</surname>
<given-names>R. P.</given-names>
</name>
</person-group> (<year>1997</year>). <article-title>Physiological Parameter Values for Physiologically Based Pharmacokinetic Models</article-title>. <source>Toxicol. Ind. Health</source> <volume>13</volume> (<issue>4</issue>), <fpage>407</fpage>&#x2013;<lpage>484</lpage>. <pub-id pub-id-type="doi">10.1177/074823379701300401</pub-id> </citation>
</ref>
<ref id="B14">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Chiu</surname>
<given-names>W. A.</given-names>
</name>
<name>
<surname>Barton</surname>
<given-names>H. A.</given-names>
</name>
<name>
<surname>Dewoskin</surname>
<given-names>R. S.</given-names>
</name>
<name>
<surname>Schlosser</surname>
<given-names>P.</given-names>
</name>
<name>
<surname>Thompson</surname>
<given-names>C. M.</given-names>
</name>
<name>
<surname>Sonawane</surname>
<given-names>B.</given-names>
</name>
<etal/>
</person-group> (<year>2007</year>). <article-title>Evaluation of Physiologically Based Pharmacokinetic Models for Use in Risk Assessment</article-title>. <source>J.&#x20;Appl. Toxicol.</source> <volume>27</volume>, <fpage>218</fpage>&#x2013;<lpage>237</lpage>. <pub-id pub-id-type="doi">10.1002/jat.1225</pub-id> </citation>
</ref>
<ref id="B15">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Clewell</surname>
<given-names>H. J.</given-names>
<suffix>III</suffix>
</name>
<name>
<surname>Andersen</surname>
<given-names>M. E.</given-names>
</name>
</person-group> (<year>1996</year>). <article-title>Use of Physiologically Based Pharmacokinetic Modeling to Investigate Individual versus Population Risk</article-title>. <source>Toxicology</source> <volume>111</volume>, <fpage>315</fpage>&#x2013;<lpage>329</lpage>. <pub-id pub-id-type="doi">10.1016/0300-483x(96)03385-9</pub-id> </citation>
</ref>
<ref id="B16">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Clewell</surname>
<given-names>H. J.</given-names>
</name>
<name>
<surname>Tan</surname>
<given-names>Y. M.</given-names>
</name>
<name>
<surname>Campbell</surname>
<given-names>J.&#x20;L.</given-names>
</name>
<name>
<surname>Andersen</surname>
<given-names>M. E.</given-names>
</name>
</person-group> (<year>2008</year>). <article-title>Quantitative Interpretation of Human Biomonitoring Data</article-title>. <source>Toxicol. Appl. Pharmacol.</source> <volume>231</volume> (<issue>1</issue>), <fpage>122</fpage>&#x2013;<lpage>133</lpage>. <pub-id pub-id-type="doi">10.1016/j.taap.2008.04.021</pub-id> </citation>
</ref>
<ref id="B17">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Cocker</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Jones</surname>
<given-names>K.</given-names>
</name>
</person-group> (<year>2017</year>). <article-title>Biological Monitoring without Limits</article-title>. <source>Ann. Work Expo. Health</source> <volume>61</volume> (<issue>4</issue>), <fpage>401</fpage>&#x2013;<lpage>405</lpage>. <pub-id pub-id-type="doi">10.1093/annweh/wxx011</pub-id> </citation>
</ref>
<ref id="B18">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Ellison</surname>
<given-names>C. A.</given-names>
</name>
<name>
<surname>Blackburn</surname>
<given-names>K. L.</given-names>
</name>
<name>
<surname>Carmichael</surname>
<given-names>P. L.</given-names>
</name>
<name>
<surname>Clewell</surname>
<given-names>H. J.</given-names>
<suffix>III</suffix>
</name>
<name>
<surname>Cronin</surname>
<given-names>M. T. D.</given-names>
</name>
<name>
<surname>Desprez</surname>
<given-names>B.</given-names>
</name>
<etal/>
</person-group> (<year>2019</year>). <article-title>Challenges in Working towards an Internal Threshold of Toxicological Concern (iTTC) for Use in the Safety Assessment of Cosmetics: Discussions from the Cosmetics Europe iTTC Working Group Workshop</article-title>. <source>Regul. Toxicol. Pharmacol.</source> <volume>103</volume>, <fpage>63</fpage>&#x2013;<lpage>72</lpage>. <pub-id pub-id-type="doi">10.1016/j.yrtph.2019.01.016</pub-id> </citation>
</ref>
<ref id="B19">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Fabian</surname>
<given-names>E.</given-names>
</name>
<name>
<surname>Gomes</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Birk</surname>
<given-names>B.</given-names>
</name>
<name>
<surname>Williford</surname>
<given-names>T.</given-names>
</name>
<name>
<surname>Hernandez</surname>
<given-names>T. R.</given-names>
</name>
<name>
<surname>Haase</surname>
<given-names>C.</given-names>
</name>
<etal/>
</person-group> (<year>2019</year>). <article-title>In Vitro-to-In Vivo Extrapolation (IVIVE) by PBTK Modeling for Animal-free Risk Assessment Approaches of Potential Endocrine-Disrupting Compounds</article-title>. <source>Arch. Toxicol.</source> <volume>93</volume> (<issue>2</issue>), <fpage>401</fpage>&#x2013;<lpage>416</lpage>. <pub-id pub-id-type="doi">10.1007/s00204-018-2372-z</pub-id> </citation>
</ref>
<ref id="B20">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Foster</surname>
<given-names>P. M.</given-names>
</name>
<name>
<surname>Lake</surname>
<given-names>B. G.</given-names>
</name>
<name>
<surname>Thomas</surname>
<given-names>L. V.</given-names>
</name>
<name>
<surname>Cook</surname>
<given-names>M. W.</given-names>
</name>
<name>
<surname>Gangolli</surname>
<given-names>S. D.</given-names>
</name>
</person-group> (<year>1981</year>). <article-title>Studies on the Testicular Effects and Zinc Excretion Produced by Various Isomers of Monobutyl-O-Phthalate in the Rat</article-title>. <source>Chem. Biol. Interact</source> <volume>34</volume> (<issue>2</issue>), <fpage>233</fpage>&#x2013;<lpage>238</lpage>. <pub-id pub-id-type="doi">10.1016/0009-2797(81)90134-4</pub-id> </citation>
</ref>
<ref id="B21">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Furr</surname>
<given-names>J.&#x20;R.</given-names>
</name>
<name>
<surname>Lambright</surname>
<given-names>C. S.</given-names>
</name>
<name>
<surname>Wilson</surname>
<given-names>V. S.</given-names>
</name>
<name>
<surname>Foster</surname>
<given-names>P. M.</given-names>
</name>
<name>
<surname>Gray</surname>
<given-names>L. E.</given-names>
<suffix>Jr.</suffix>
</name>
</person-group> (<year>2014</year>). <article-title>A Short-Term <italic>In Vivo</italic> Screen Using Fetal Testosterone Production, a Key Event in the Phthalate Adverse Outcome Pathway, to Predict Disruption of Sexual Differentiation</article-title>. <source>Toxicol. Sci.</source> <volume>140</volume> (<issue>2</issue>), <fpage>403</fpage>&#x2013;<lpage>424</lpage>. <pub-id pub-id-type="doi">10.1093/toxsci/kfu081</pub-id> </citation>
</ref>
<ref id="B22">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Gobeau</surname>
<given-names>N.</given-names>
</name>
<name>
<surname>Stringer</surname>
<given-names>R.</given-names>
</name>
<name>
<surname>De Buck</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Tuntland</surname>
<given-names>T.</given-names>
</name>
<name>
<surname>Faller</surname>
<given-names>B.</given-names>
</name>
</person-group> (<year>2016</year>). <article-title>Evaluation of the GastroPlus&#x2122; Advanced Compartmental and Transit (ACAT) Model in Early Discovery</article-title>. <source>Pharm. Res.</source> <volume>33</volume> (<issue>9</issue>), <fpage>2126</fpage>&#x2013;<lpage>2139</lpage>. <pub-id pub-id-type="doi">10.1007/s11095-016-1951-z</pub-id> </citation>
</ref>
<ref id="B23">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Griffiths</surname>
<given-names>W. C.</given-names>
</name>
<name>
<surname>Camara</surname>
<given-names>P. D.</given-names>
</name>
<name>
<surname>Saritelli</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Gentile</surname>
<given-names>J.</given-names>
</name>
</person-group> (<year>1988</year>). <article-title>The <italic>In Vitro</italic> Serum Protein-Binding Characteristics of Bis-(2-Ethylhexyl) Phthalate and its Principal Metabolite, Mono-(2-Ethylhexyl) Phthalate</article-title>. <source>Environ. Health Perspect.</source> <volume>77</volume>, <fpage>151</fpage>&#x2013;<lpage>156</lpage>. <pub-id pub-id-type="doi">10.1289/ehp.8877151</pub-id> </citation>
</ref>
<ref id="B24">
<citation citation-type="journal">
<collab>ICRP</collab> (<year>2002</year>). <article-title>Basic Anatomical and Physiological Data for Use in Radiological protection: Reference Values. A Report of Age- and Gender-Related Differences in the Anatomical and Physiological Characteristics of Reference Individuals. ICRP Publication 89</article-title>. <source>Ann. ICRP</source> <volume>32</volume> (<issue>3-4</issue>), <fpage>5</fpage>&#x2013;<lpage>265</lpage>. </citation>
</ref>
<ref id="B25">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Jones</surname>
<given-names>H. M.</given-names>
</name>
<name>
<surname>Houston</surname>
<given-names>J.&#x20;B.</given-names>
</name>
</person-group> (<year>2004</year>). <article-title>Substrate Depletion Approach for Determining <italic>In Vitro</italic> Metabolic Clearance: Time Dependencies in Hepatocyte and Microsomal Incubations</article-title>. <source>Drug Metab. Dispos.</source> <volume>32</volume> (<issue>9</issue>), <fpage>973</fpage>&#x2013;<lpage>982</lpage>. <pub-id pub-id-type="doi">10.1124/dmd.104.000125</pub-id> </citation>
</ref>
<ref id="B26">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Kessler</surname>
<given-names>W.</given-names>
</name>
<name>
<surname>Numtip</surname>
<given-names>W.</given-names>
</name>
<name>
<surname>Grote</surname>
<given-names>K.</given-names>
</name>
<name>
<surname>Csan&#xe1;dy</surname>
<given-names>G. A.</given-names>
</name>
<name>
<surname>Chahoud</surname>
<given-names>I.</given-names>
</name>
<name>
<surname>Filser</surname>
<given-names>J.&#x20;G.</given-names>
</name>
</person-group> (<year>2004</year>). <article-title>Blood burden of di(2-ethylhexyl) phthalate and its primary metabolite mono(2-ethylhexyl) phthalate in pregnant and nonpregnant rats and marmosets</article-title>. <source>Toxicol. Appl. Pharmacol.</source> <volume>195</volume> (<issue>2</issue>), <fpage>142</fpage>&#x2013;<lpage>153</lpage>. <pub-id pub-id-type="doi">10.1016/j.taap.2003.11.014</pub-id> </citation>
</ref>
<ref id="B27">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Kessler</surname>
<given-names>W.</given-names>
</name>
<name>
<surname>Numtip</surname>
<given-names>W.</given-names>
</name>
<name>
<surname>V&#xf6;lkel</surname>
<given-names>W.</given-names>
</name>
<name>
<surname>Seckin</surname>
<given-names>E.</given-names>
</name>
<name>
<surname>Csan&#xe1;dy</surname>
<given-names>G. A.</given-names>
</name>
<name>
<surname>P&#xfc;tz</surname>
<given-names>C.</given-names>
</name>
<etal/>
</person-group> (<year>2012</year>). <article-title>Kinetics of di(2-ethylhexyl) phthalate (dehp) and mono(2-ethylhexyl) phthalate in blood and of dehp metabolites in urine of male volunteers after single ingestion of ring-deuterated dehp</article-title>. <source>Toxicol. Appl. Pharmacol.</source> <volume>264</volume> (<issue>2</issue>), <fpage>284</fpage>&#x2013;<lpage>291</lpage>. <pub-id pub-id-type="doi">10.1016/j.taap.2012.08.009</pub-id> </citation>
</ref>
<ref id="B28">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Klein</surname>
<given-names>D.</given-names>
</name>
<name>
<surname>Kessler</surname>
<given-names>W.</given-names>
</name>
<name>
<surname>P&#xfc;tz</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Semder</surname>
<given-names>B.</given-names>
</name>
<name>
<surname>Kirchinger</surname>
<given-names>W.</given-names>
</name>
<name>
<surname>Langsch</surname>
<given-names>A.</given-names>
</name>
<etal/>
</person-group> (<year>2018</year>). <article-title>Single Ingestion of Di-(2-propylheptyl) Phthalate (DPHP) by Male Volunteers: DPHP in Blood and its Metabolites in Blood and Urine</article-title>. <source>Toxicol. Lett.</source> <volume>294</volume>, <fpage>105</fpage>&#x2013;<lpage>115</lpage>. <pub-id pub-id-type="doi">10.1016/j.toxlet.2018.05.010</pub-id> </citation>
</ref>
<ref id="B29">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Klein</surname>
<given-names>D.</given-names>
</name>
<name>
<surname>Kessler</surname>
<given-names>W.</given-names>
</name>
<name>
<surname>Semder</surname>
<given-names>B.</given-names>
</name>
<name>
<surname>P&#xfc;tz</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Lichtmannegger</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Otter</surname>
<given-names>R.</given-names>
</name>
<etal/>
</person-group> (<year>2016</year>). <article-title>Di-(2-propylheptyl) Phthalate (DPHP) and its Metabolites in Blood of Rats upon Single Oral Administration of DPHP</article-title>. <source>Toxicol. Lett.</source> <volume>259</volume>, <fpage>80</fpage>&#x2013;<lpage>86</lpage>. <pub-id pub-id-type="doi">10.1016/j.toxlet.2016.07.025</pub-id> </citation>
</ref>
<ref id="B30">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Kurata</surname>
<given-names>Y.</given-names>
</name>
<name>
<surname>Makinodan</surname>
<given-names>F.</given-names>
</name>
<name>
<surname>Shimamura</surname>
<given-names>N.</given-names>
</name>
<name>
<surname>Katoh</surname>
<given-names>M.</given-names>
</name>
</person-group> (<year>2012</year>). <article-title>Metabolism of di (2-ethylhexyl) phthalate (DEHP): comparative study in juvenile and fetal marmosets and rats</article-title>. <source>J.&#x20;Toxicol. Sci.</source> <volume>37</volume> (<issue>1</issue>), <fpage>33</fpage>&#x2013;<lpage>49</lpage>. <pub-id pub-id-type="doi">10.2131/jts.37.33</pub-id> </citation>
</ref>
<ref id="B31">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Leng</surname>
<given-names>G.</given-names>
</name>
<name>
<surname>Koch</surname>
<given-names>H. M.</given-names>
</name>
<name>
<surname>Gries</surname>
<given-names>W.</given-names>
</name>
<name>
<surname>Sch&#xfc;tze</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Langsch</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Br&#xfc;ning</surname>
<given-names>T.</given-names>
</name>
<etal/>
</person-group> (<year>2014</year>). <article-title>Urinary Metabolite Excretion after Oral Dosage of Bis(2-Propylheptyl) Phthalate (Dphp) to Five Male Volunteers-Ccharacterization of Suitable Biomarkers for Human Biomonitoring</article-title>. <source>Toxicol. Lett.</source> <volume>231</volume> (<issue>2</issue>), <fpage>282</fpage>&#x2013;<lpage>288</lpage>. <pub-id pub-id-type="doi">10.1016/j.toxlet.2014.06.035</pub-id> </citation>
</ref>
<ref id="B32">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Lermen</surname>
<given-names>D.</given-names>
</name>
<name>
<surname>Bartel-Steinbach</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Gwinner</surname>
<given-names>F.</given-names>
</name>
<name>
<surname>Conrad</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Weber</surname>
<given-names>T.</given-names>
</name>
<name>
<surname>von Briesen</surname>
<given-names>H.</given-names>
</name>
<etal/>
</person-group> (<year>2019</year>). <article-title>Trends in Characteristics of 24-h Urine Samples and Their Relevance for Human Biomonitoring Studies - 20&#x202f;years of Experience in the German Environmental Specimen Bank</article-title>. <source>Int. J.&#x20;Hyg. Environ. Health</source> <volume>222</volume> (<issue>5</issue>), <fpage>831</fpage>&#x2013;<lpage>839</lpage>. <pub-id pub-id-type="doi">10.1016/j.ijheh.2019.04.009</pub-id> </citation>
</ref>
<ref id="B33">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Lobell</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Sivarajah</surname>
<given-names>V.</given-names>
</name>
</person-group> (<year>2003</year>). <article-title>In Silico prediction of Aqueous Solubility, Human Plasma Protein Binding and Volume of Distribution of Compounds from Calculated pKa and AlogP98 Values</article-title>. <source>Mol. Divers.</source> <volume>7</volume> (<issue>1</issue>), <fpage>69</fpage>&#x2013;<lpage>87</lpage>. <pub-id pub-id-type="doi">10.1023/b:modi.0000006562.93049.36</pub-id> </citation>
</ref>
<ref id="B34">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Loizou</surname>
<given-names>G.</given-names>
</name>
<name>
<surname>Hogg</surname>
<given-names>A.</given-names>
</name>
</person-group> (<year>2011</year>). <article-title>MEGen: A Physiologically Based Pharmacokinetic Model Generator</article-title>. <source>Front. Pharmacol.</source> <volume>2</volume> (<issue>56</issue>), <fpage>56</fpage>&#x2013;<lpage>14</lpage>. <pub-id pub-id-type="doi">10.3389/fphar.2011.00056</pub-id> </citation>
</ref>
<ref id="B35">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Loizou</surname>
<given-names>G.</given-names>
</name>
<name>
<surname>Spendiff</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Barton</surname>
<given-names>H. A.</given-names>
</name>
<name>
<surname>Bessems</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Bois</surname>
<given-names>F. Y.</given-names>
</name>
<name>
<surname>d&#x27;Yvoire</surname>
<given-names>M. B.</given-names>
</name>
<etal/>
</person-group> (<year>2008</year>). <article-title>Development of Good Modelling Practice for Physiologically Based Pharmacokinetic Models for Use in Risk Assessment: The First Steps</article-title>. <source>Regul. Toxicol. Pharmacol.</source> <volume>50</volume>, <fpage>400</fpage>&#x2013;<lpage>411</lpage>. <pub-id pub-id-type="doi">10.1016/j.yrtph.2008.01.011</pub-id> </citation>
</ref>
<ref id="B36">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Loizou</surname>
<given-names>G. D.</given-names>
</name>
<name>
<surname>McNally</surname>
<given-names>K.</given-names>
</name>
<name>
<surname>Jones</surname>
<given-names>K.</given-names>
</name>
<name>
<surname>Cocker</surname>
<given-names>J.</given-names>
</name>
</person-group> (<year>2015</year>). <article-title>The Application of Global Sensitivity Analysis in the Development of a Physiologically Based Pharmacokinetic Model for M-Xylene and Ethanol Co-exposure in Humans</article-title>. <source>Front. Pharmacol.</source> <volume>6</volume>, <fpage>1</fpage>&#x2013;<lpage>19</lpage>. <pub-id pub-id-type="doi">10.3389/fphar.2015.00135</pub-id> </citation>
</ref>
<ref id="B37">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Mannhold</surname>
<given-names>R.</given-names>
</name>
<name>
<surname>Poda</surname>
<given-names>G. I.</given-names>
</name>
<name>
<surname>Ostermann</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Tetko</surname>
<given-names>I. V.</given-names>
</name>
</person-group> (<year>2009</year>). <article-title>Calculation of Molecular Lipophilicity: State-Of-The-Art and Comparison of Log P Methods on More Than 96,000 Compounds</article-title>. <source>J.&#x20;Pharm. Sci.</source> <volume>98</volume> (<issue>3</issue>), <fpage>861</fpage>&#x2013;<lpage>893</lpage>. <pub-id pub-id-type="doi">10.1002/jps.21494</pub-id> </citation>
</ref>
<ref id="B38">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Manno</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Viau</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Cocker</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Cocker</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Colosio</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Lowry</surname>
<given-names>L.</given-names>
</name>
<etal/>
</person-group> (<year>2010</year>). <article-title>Biomonitoring for Occupational Health Risk Assessment (BOHRA)</article-title>. <source>Toxicol. Lett.</source> <volume>192</volume> (<issue>1</issue>), <fpage>3</fpage>&#x2013;<lpage>16</lpage>. <pub-id pub-id-type="doi">10.1016/j.toxlet.2009.05.001</pub-id> </citation>
</ref>
<ref id="B39">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>McNally</surname>
<given-names>K.</given-names>
</name>
<name>
<surname>Cotton</surname>
<given-names>R.</given-names>
</name>
<name>
<surname>Cocker</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Jones</surname>
<given-names>K.</given-names>
</name>
<name>
<surname>Bartels</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Rick</surname>
<given-names>D.</given-names>
</name>
<etal/>
</person-group> (<year>2012</year>). <article-title>Reconstruction of Exposure to M-Xylene from Human Biomonitoring Data Using PBPK Modelling, Bayesian Inference, and Markov Chain Monte Carlo Simulation</article-title>. <source>J.&#x20;Toxicol.</source> <volume>2012</volume>, <fpage>760281</fpage>. <pub-id pub-id-type="doi">10.1155/2012/760281</pub-id> </citation>
</ref>
<ref id="B40">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>McNally</surname>
<given-names>K.</given-names>
</name>
<name>
<surname>Cotton</surname>
<given-names>R.</given-names>
</name>
<name>
<surname>Hogg</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Loizou</surname>
<given-names>G.</given-names>
</name>
</person-group> (<year>2014</year>). <article-title>PopGen: A Virtual Human Population Generator</article-title>. <source>Toxicology</source> <volume>315</volume> (<issue>0</issue>), <fpage>70</fpage>&#x2013;<lpage>85</lpage>. <pub-id pub-id-type="doi">10.1016/j.tox.2013.07.009</pub-id> </citation>
</ref>
<ref id="B41">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>McNally</surname>
<given-names>K.</given-names>
</name>
<name>
<surname>Cotton</surname>
<given-names>R.</given-names>
</name>
<name>
<surname>Loizou</surname>
<given-names>G. D.</given-names>
</name>
</person-group> (<year>2011</year>). <article-title>A Workflow for Global Sensitivity Analysis of PBPK Models</article-title>. <source>Front. Pharmacol.</source> <volume>2</volume> (<issue>31</issue>), <fpage>31</fpage>&#x2013;<lpage>21</lpage>. <pub-id pub-id-type="doi">10.3389/fphar.2011.00031</pub-id> </citation>
</ref>
<ref id="B42">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>McNally</surname>
<given-names>K.</given-names>
</name>
<name>
<surname>Sams</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Loizou</surname>
<given-names>G.</given-names>
</name>
</person-group> (<year>2019</year>). <article-title>Development, Testing, Parameterization, and Calibration of a Human Physiologically Based Pharmacokinetic Model for the Plasticizer, Hexamoll&#xae; Diisononyl-Cyclohexane-1, 2-Dicarboxylate Using In Silico, <italic>In Vitro</italic>, and Human Biomonitoring Data</article-title>. <source>Front. Pharmacol.</source> <volume>10</volume> (<issue>1394</issue>), <fpage>1394</fpage>. <pub-id pub-id-type="doi">10.3389/fphar.2019.01394</pub-id> </citation>
</ref>
<ref id="B43">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Nehring</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Bury</surname>
<given-names>D.</given-names>
</name>
<name>
<surname>Ringbeck</surname>
<given-names>B.</given-names>
</name>
<name>
<surname>Kling</surname>
<given-names>H. W.</given-names>
</name>
<name>
<surname>Otter</surname>
<given-names>R.</given-names>
</name>
<name>
<surname>Weiss</surname>
<given-names>T.</given-names>
</name>
<etal/>
</person-group> (<year>2020</year>). <article-title>Metabolism and urinary excretion kinetics of di(2-ethylhexyl) adipate (DEHA) in four human volunteers after a single oral dose</article-title>. <source>Toxicol. Lett.</source> <volume>321</volume>, <fpage>95</fpage>&#x2013;<lpage>102</lpage>. <pub-id pub-id-type="doi">10.1016/j.toxlet.2019.12.006</pub-id> </citation>
</ref>
<ref id="B44">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Obach</surname>
<given-names>R. S.</given-names>
</name>
<name>
<surname>Baxter</surname>
<given-names>J.&#x20;G.</given-names>
</name>
<name>
<surname>Liston</surname>
<given-names>T. E.</given-names>
</name>
<name>
<surname>Silber</surname>
<given-names>B. M.</given-names>
</name>
<name>
<surname>Jones</surname>
<given-names>B. C.</given-names>
</name>
<name>
<surname>MacIntyre</surname>
<given-names>F.</given-names>
</name>
<etal/>
</person-group> (<year>1997</year>). <article-title>The Prediction of Human Pharmacokinetic Parameters from Preclinical and <italic>In Vitro</italic> Metabolism Data</article-title>. <source>J.&#x20;Pharmacol. Exp. Ther.</source> <volume>283</volume> (<issue>1</issue>), <fpage>46</fpage>&#x2013;<lpage>58</lpage>. <pub-id pub-id-type="doi">10.1016/s0294-3506(97)87687-9</pub-id> </citation>
</ref>
<ref id="B45">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Obach</surname>
<given-names>R. S.</given-names>
</name>
</person-group> (<year>1999</year>). <article-title>Prediction of Human Clearance of Twenty-Nine Drugs from Hepatic Microsomal Intrinsic Clearance Data: an Examination of <italic>In Vitro</italic> Half-Life Approach and Nonspecific Binding to Microsomes</article-title>. <source>Drug Metab. Dispos.</source> <volume>27</volume> (<issue>11</issue>), <fpage>1350</fpage>&#x2013;<lpage>1359</lpage>. </citation>
</ref>
<ref id="B46">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Offman</surname>
<given-names>E.</given-names>
</name>
<name>
<surname>Phipps</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Edginton</surname>
<given-names>A. N.</given-names>
</name>
</person-group> (<year>2016</year>). <article-title>Population Physiologically-Based Pharmacokinetic Model Incorporating Lymphatic Uptake for a Subcutaneously Administered Pegylated Peptide</article-title>. <source>Silico Pharmacol.</source> <volume>4</volume> (<issue>3</issue>), <fpage>3</fpage>&#x2013;<lpage>14</lpage>. <pub-id pub-id-type="doi">10.1186/s40203-016-0018-5</pub-id> </citation>
</ref>
<ref id="B47">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Oishi</surname>
<given-names>S.</given-names>
</name>
<name>
<surname>Hiraga</surname>
<given-names>K.</given-names>
</name>
</person-group> (<year>1980</year>). <article-title>Testicular Atrophy Induced by Phthalic Acid Monoesters: Effects of Zinc and Testosterone Concentrations</article-title>. <source>Toxicology</source> <volume>15</volume> (<issue>3</issue>), <fpage>197</fpage>&#x2013;<lpage>202</lpage>. <pub-id pub-id-type="doi">10.1016/0300-483X(80)90053-0</pub-id> </citation>
</ref>
<ref id="B48">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Paini</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Leonard</surname>
<given-names>J.&#x20;A.</given-names>
</name>
<name>
<surname>Kliment</surname>
<given-names>T.</given-names>
</name>
<name>
<surname>Tan</surname>
<given-names>Y. M.</given-names>
</name>
<name>
<surname>Worth</surname>
<given-names>A.</given-names>
</name>
</person-group> (<year>2017</year>). <article-title>Investigating the State of Physiologically Based Kinetic Modelling Practices and Challenges Associated with Gaining Regulatory Acceptance of Model Applications</article-title>. <source>Regul. Toxicol. Pharmacol.</source> <volume>90</volume> (<issue>Suppl. C</issue>), <fpage>104</fpage>&#x2013;<lpage>115</lpage>. <pub-id pub-id-type="doi">10.1016/j.yrtph.2017.08.019</pub-id> </citation>
</ref>
<ref id="B49">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Pearce</surname>
<given-names>R. G.</given-names>
</name>
<name>
<surname>Setzer</surname>
<given-names>R. W.</given-names>
</name>
<name>
<surname>Strope</surname>
<given-names>C. L.</given-names>
</name>
<name>
<surname>Wambaugh</surname>
<given-names>J.&#x20;F.</given-names>
</name>
<name>
<surname>Sipes</surname>
<given-names>N. S.</given-names>
</name>
</person-group> (<year>2017</year>). <article-title>Httk: R Package for High-Throughput Toxicokinetics</article-title>. <source>J.&#x20;Stat. Softw.</source> <volume>79</volume> (<issue>1</issue>), <fpage>1</fpage>&#x2013;<lpage>26</lpage>. <pub-id pub-id-type="doi">10.18637/jss.v079.i04</pub-id> </citation>
</ref>
<ref id="B50">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Poulin</surname>
<given-names>P.</given-names>
</name>
<name>
<surname>Haddad</surname>
<given-names>S.</given-names>
</name>
</person-group> (<year>2012</year>). <article-title>Advancing Prediction of Tissue Distribution and Volume of Distribution of Highly Lipophilic Compounds from a Simplified Tissue-Composition-Based Model as a Mechanistic Animal Alternative Method</article-title>. <source>J.&#x20;Pharm. Sci.</source> <volume>101</volume> (<issue>6</issue>), <fpage>2250</fpage>&#x2013;<lpage>2261</lpage>. <pub-id pub-id-type="doi">10.1002/jps.23090</pub-id> </citation>
</ref>
<ref id="B51">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Rhodes</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Orton</surname>
<given-names>T. C.</given-names>
</name>
<name>
<surname>Pratt</surname>
<given-names>I. S.</given-names>
</name>
<name>
<surname>Batten</surname>
<given-names>P. L.</given-names>
</name>
<name>
<surname>Bratt</surname>
<given-names>H.</given-names>
</name>
<name>
<surname>Jackson</surname>
<given-names>S. J.</given-names>
</name>
<etal/>
</person-group> (<year>1986</year>). <article-title>Comparative pharmacokinetics and subacute toxicity of di(2-ethylhexyl) phthalate (DEHP) in rats and marmosets: extrapolation of effects in rodents to man</article-title>. <source>Environ. Health Perspect.</source> <volume>65</volume>, <fpage>299</fpage>&#x2013;<lpage>307</lpage>. <pub-id pub-id-type="doi">10.1289/ehp.8665299</pub-id> </citation>
</ref>
<ref id="B52">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Schmidtkunz</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Gries</surname>
<given-names>W.</given-names>
</name>
<name>
<surname>Weber</surname>
<given-names>T.</given-names>
</name>
<name>
<surname>Leng</surname>
<given-names>G.</given-names>
</name>
<name>
<surname>Kolossa-Gehring</surname>
<given-names>M.</given-names>
</name>
</person-group> (<year>2019</year>). <article-title>Internal exposure of young German adults to di(2-propylheptyl) phthalate (DPHP): Trends in 24-h urine samples from the German Environmental Specimen Bank 1999-2017</article-title>. <source>Int. J.&#x20;Hyg. Environ. Health</source> <volume>222</volume> (<issue>3</issue>), <fpage>419</fpage>&#x2013;<lpage>424</lpage>. <pub-id pub-id-type="doi">10.1016/j.ijheh.2018.12.008</pub-id> </citation>
</ref>
<ref id="B53">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Schmitt</surname>
<given-names>W.</given-names>
</name>
</person-group> (<year>2008</year>). <article-title>General Approach for the Calculation of Tissue to Plasma Partition Coefficients</article-title>. <source>Toxicol. Vitro</source> <volume>22</volume> (<issue>2</issue>), <fpage>457</fpage>&#x2013;<lpage>467</lpage>. <pub-id pub-id-type="doi">10.1016/j.tiv.2007.09.010</pub-id> </citation>
</ref>
<ref id="B54">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Sch&#xfc;tze</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Gries</surname>
<given-names>W.</given-names>
</name>
<name>
<surname>Kolossa-Gehring</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Apel</surname>
<given-names>P.</given-names>
</name>
<name>
<surname>Schr&#xf6;ter-Kermani</surname>
<given-names>C.</given-names>
</name>
<name>
<surname>Fiddicke</surname>
<given-names>U.</given-names>
</name>
<etal/>
</person-group> (<year>2015</year>). <article-title>Bis-(2-propylheptyl)phthalate (DPHP) Metabolites Emerging in 24h Urine Samples from the German Environmental Specimen Bank (1999-2012)</article-title>. <source>Int. J.&#x20;Hyg. Environ. Health</source> <volume>218</volume> (<issue>6</issue>), <fpage>559</fpage>&#x2013;<lpage>563</lpage>. <pub-id pub-id-type="doi">10.1016/j.ijheh.2015.05.007</pub-id> </citation>
</ref>
<ref id="B55">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Schwedler</surname>
<given-names>G.</given-names>
</name>
<name>
<surname>Conrad</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Rucic</surname>
<given-names>E.</given-names>
</name>
<name>
<surname>Koch</surname>
<given-names>H. M.</given-names>
</name>
<name>
<surname>Leng</surname>
<given-names>G.</given-names>
</name>
<name>
<surname>Schulz</surname>
<given-names>C.</given-names>
</name>
<etal/>
</person-group> (<year>2020</year>). <article-title>Hexamoll DINCH and DPHP Metabolites in Urine of Children and Adolescents in Germany. Human Biomonitoring Results of the German Environmental Survey GerES V, 2014-2017</article-title>. <source>Int. J.&#x20;Hyg. Environ. Health</source> <volume>229</volume>, <fpage>113397</fpage>. <pub-id pub-id-type="doi">10.1016/j.ijheh.2019.09.004</pub-id> </citation>
</ref>
<ref id="B56">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Sj&#xf6;berg</surname>
<given-names>P.</given-names>
</name>
<name>
<surname>Bondesson</surname>
<given-names>U.</given-names>
</name>
<name>
<surname>Gray</surname>
<given-names>T. J.</given-names>
</name>
<name>
<surname>Pl&#xf6;en</surname>
<given-names>L.</given-names>
</name>
</person-group> (<year>1986</year>). <article-title>Effects of Di-(2-ethylhexyl) Phthalate and Five of its Metabolites on Rat Testis <italic>In Vivo</italic> and in <italic>In Vitro</italic>
</article-title>. <source>Acta Pharmacol. Toxicol. (Copenh)</source> <volume>58</volume> (<issue>3</issue>), <fpage>225</fpage>&#x2013;<lpage>233</lpage>. <pub-id pub-id-type="doi">10.1111/j.1600-0773.1986.tb00098.x</pub-id> </citation>
</ref>
<ref id="B57">
<citation citation-type="book">
<collab>Union Carbide</collab> (<year>1997</year>). <source>Letter from Union Carbide Corp to USEPA Regarding: Bis-2-Propylheptyl Phthalate Subchronic Feeding Study in Rats, Dated 03/17/1997. Microfiche No. OTS0001292, New Doc ID FYI-OTS-0397-1292</source>.</citation>
</ref>
<ref id="B58">
<citation citation-type="book">
<collab>Union Carbide</collab> (<year>1998</year>). <source>Support: Letter from Union Carbide Corp to USEPA Regarding: 90-day Rat Feeding Study with Bis-2-Propylheptyl Phthalate, Dated 01/15/1998Microfiche No. OTS0001292, New Doc ID FYI-OTS-0198-1292</source>.</citation>
</ref>
<ref id="B59">
<citation citation-type="book">
<collab>WHO</collab> (<year>2010</year>). <source>Characterization and Application of Physiologically Based Pharmacokinetic Models in Risk Assessment</source>, <volume>9</volume>. <publisher-loc>Geneva</publisher-loc>: <publisher-name>Harmonization Project Document</publisher-name>.</citation>
</ref>
<ref id="B60">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Wittassek</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Angerer</surname>
<given-names>J.</given-names>
</name>
</person-group> (<year>2008</year>). <article-title>Phthalates: Metabolism and Exposure</article-title>. <source>Int. J.&#x20;Androl.</source> <volume>31</volume> (<issue>2</issue>), <fpage>131</fpage>&#x2013;<lpage>138</lpage>. <pub-id pub-id-type="doi">10.1111/j.1365-2605.2007.00837.x</pub-id> </citation>
</ref>
<ref id="B61">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Wittassek</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Koch</surname>
<given-names>H. M.</given-names>
</name>
<name>
<surname>Angerer</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Br&#xfc;ning</surname>
<given-names>T.</given-names>
</name>
</person-group> (<year>2011</year>). <article-title>Assessing Exposure to Phthalates - the Human Biomonitoring Approach</article-title>. <source>Mol. Nutr. Food Res.</source> <volume>55</volume> (<issue>1</issue>), <fpage>7</fpage>&#x2013;<lpage>31</lpage>. <pub-id pub-id-type="doi">10.1002/mnfr.201000121</pub-id> </citation>
</ref>
<ref id="B62">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Yang</surname>
<given-names>J.</given-names>
</name>
<name>
<surname>Jamei</surname>
<given-names>M.</given-names>
</name>
<name>
<surname>Yeo</surname>
<given-names>K. R.</given-names>
</name>
<name>
<surname>Rostami-Hodjegan</surname>
<given-names>A.</given-names>
</name>
<name>
<surname>Tucker</surname>
<given-names>G. T.</given-names>
</name>
</person-group> (<year>2007</year>). <article-title>Misuse of the Well-Stirred Model of Hepatic Drug Clearance</article-title>. <source>Drug Metab. Dispos.</source> <volume>35</volume> (<issue>3</issue>), <fpage>501</fpage>&#x2013;<lpage>502</lpage>. <pub-id pub-id-type="doi">10.1124/dmd.106.013359</pub-id> </citation>
</ref>
<ref id="B63">
<citation citation-type="journal">
<person-group person-group-type="author">
<name>
<surname>Yang</surname>
<given-names>X.</given-names>
</name>
<name>
<surname>Doerge</surname>
<given-names>D. R.</given-names>
</name>
<name>
<surname>Teeguarden</surname>
<given-names>J.&#x20;G.</given-names>
</name>
<name>
<surname>Fisher</surname>
<given-names>J.&#x20;W.</given-names>
</name>
</person-group> (<year>2015</year>). <article-title>Development of a Physiologically Based Pharmacokinetic Model for Assessment of Human Exposure to Bisphenol a</article-title>. <source>Toxicol. Appl. Pharmacol.</source> <volume>289</volume> (<issue>3</issue>), <fpage>442</fpage>&#x2013;<lpage>456</lpage>. <pub-id pub-id-type="doi">10.1016/j.taap.2015.10.016</pub-id> </citation>
</ref>
</ref-list>
</back>
</article>