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<article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="1.3" xml:lang="en" article-type="research-article"><?properties open_access?><?properties manuscript?><processing-meta base-tagset="archiving" mathml-version="3.0" table-model="xhtml" tagset-family="jats"><restricted-by>pmc</restricted-by></processing-meta><front><journal-meta><journal-id journal-id-type="nlm-journal-id">9918383886106676</journal-id><journal-id journal-id-type="pubmed-jr-id">51553</journal-id><journal-id journal-id-type="nlm-ta">Adv Redox Res</journal-id><journal-id journal-id-type="iso-abbrev">Adv Redox Res</journal-id><journal-title-group><journal-title>Advances in redox research</journal-title></journal-title-group><issn pub-type="epub">2667-1379</issn></journal-meta><article-meta><article-id pub-id-type="pmid">38562524</article-id><article-id pub-id-type="pmc">10979698</article-id><article-id pub-id-type="doi">10.1016/j.arres.2023.100090</article-id><article-id pub-id-type="manuscript">HHSPA1977854</article-id><article-categories><subj-group subj-group-type="heading"><subject>Article</subject></subj-group></article-categories><title-group><article-title>Maternal nano-titanium dioxide inhalation exposure alters placental cyclooxygenase and oxidant balance in a sexually dimorphic manner</article-title></title-group><contrib-group><contrib contrib-type="author"><name><surname>Griffith</surname><given-names>Julie A.</given-names></name><xref rid="A1" ref-type="aff">a</xref><xref rid="A2" ref-type="aff">b</xref></contrib><contrib contrib-type="author"><name><surname>King</surname><given-names>Rachel D.</given-names></name><xref rid="A3" ref-type="aff">c</xref></contrib><contrib contrib-type="author"><name><surname>Dunn</surname><given-names>Allison C.</given-names></name><xref rid="A1" ref-type="aff">a</xref><xref rid="A2" ref-type="aff">b</xref></contrib><contrib contrib-type="author"><name><surname>Lewis</surname><given-names>Sara E.</given-names></name><xref rid="A1" ref-type="aff">a</xref></contrib><contrib contrib-type="author"><name><surname>Maxwell</surname><given-names>Brooke A.</given-names></name><xref rid="A1" ref-type="aff">a</xref></contrib><contrib contrib-type="author"><name><surname>Nurkiewicz</surname><given-names>Timothy R.</given-names></name><xref rid="A1" ref-type="aff">a</xref><xref rid="A2" ref-type="aff">b</xref></contrib><contrib contrib-type="author"><name><surname>Goldsmith</surname><given-names>William T.</given-names></name><xref rid="A1" ref-type="aff">a</xref><xref rid="A2" ref-type="aff">b</xref></contrib><contrib contrib-type="author"><name><surname>Kelley</surname><given-names>Eric E.</given-names></name><xref rid="A1" ref-type="aff">a</xref><xref rid="A2" ref-type="aff">b</xref></contrib><contrib contrib-type="author"><name><surname>Bowdridge</surname><given-names>Elizabeth C.</given-names></name><xref rid="A1" ref-type="aff">a</xref><xref rid="A2" ref-type="aff">b</xref><xref rid="CR1" ref-type="corresp">*</xref></contrib></contrib-group><aff id="A1"><label>a</label>Department of Physiology, Pharmacology and Toxicology, West Virginia University School of Medicine, Morgantown, WV, USA</aff><aff id="A2"><label>b</label>Center for Inhalation Toxicology, West Virginia University School of Medicine, Morgantown, WV, USA</aff><aff id="A3"><label>c</label>Department of Biochemistry, West Virginia University School of Medicine, Morgantown, WV, USA</aff><author-notes><corresp id="CR1"><label>*</label>Corresponding author at: Department of Physiology, Pharmacology, and Toxicology, University of West Virginia, School of Medicine, 3076 Health Sciences Center North, PO Box 9229, Morgantown, WV 26506-9229, USA. <email>ebowdrid@hsc.wvu.edu</email> (E.C. Bowdridge).</corresp></author-notes><pub-date pub-type="nihms-submitted"><day>22</day><month>3</month><year>2024</year></pub-date><pub-date pub-type="ppub"><month>4</month><year>2024</year></pub-date><pub-date pub-type="pmc-release"><day>01</day><month>4</month><year>2024</year></pub-date><volume>10</volume><elocation-id>10.1016/j.arres.2023.100090</elocation-id><permissions><license><ali:license_ref xmlns:ali="http://www.niso.org/schemas/ali/1.0/" specific-use="textmining" content-type="ccbyncndlicense">https://creativecommons.org/licenses/by-nc-nd/4.0/</ali:license_ref><license-p>This is an open access article under the CC BY-NC-ND license (<ext-link ext-link-type="uri" xlink:href="https://creativecommons.org/licenses/by-nc-nd/4.0/">http://creativecommons.org/licenses/by-nc-nd/4.0/</ext-link>).</license-p></license></permissions><abstract id="ABS1"><p id="P1">The placenta plays a critical role in nutrient-waste exchange between the maternal and fetal circulation, and thus impacts fetal growth and development. We have previously shown that nano-titanium dioxide (nano-TiO<sub>2</sub>) inhalation exposure during gestation decreased fetal female pup and placenta mass [<xref rid="R1" ref-type="bibr">1</xref>], which persists in the following generation [<xref rid="R2" ref-type="bibr">2</xref>]. In utero exposed females, once mated, their offspring&#x02019;s placentas had increased capacity for H<sub>2</sub>O<sub>2</sub> production. Generation of oxidants such as hydrogen peroxide (H<sub>2</sub>O<sub>2</sub>), have been shown to impact cyclooxygenase activity, specifically metabolites such as prostacyclin (PGI<sub>2</sub>) or thromboxane (TXA<sub>2</sub>). Therefore, we hypothesized that maternal nano-TiO<sub>2</sub> inhalation exposure during gestation results in alterations in placental production of prostacyclin and thromboxane mediated by enhanced H<sub>2</sub>O<sub>2</sub> production in a sexually dimorphic manner. Pregnant Sprague-Dawley rats were exposed to nano-TiO<sub>2</sub> aerosols or filtered air (sham--control) from gestational day (GD) 10&#x02013;19. Dams were euthanized on GD 20, and fetal serum and placental tissue were collected based on fetal sex. Fetal placental zones (junctional zone (JZ) and labyrinth zone (LZ)) were assessed for xanthine oxidoreductase (XOR) activity, H<sub>2</sub>O<sub>2</sub>, and catalase activity, as well as 6-keto-PGF<sub>1</sub>&#x003b1; and TXB<sub>2</sub> levels. Nano-TiO<sub>2</sub> exposed fetal female LZ demonstrated significantly greater XOR activity compared to exposed males. Exposed fetal female LZ also demonstrated significantly diminished catalase activity compared to sham-control females. Exposed fetal female LZ had significantly increased abundance of 6-keto-PGF<sub>1</sub>&#x003b1; compared to sham-control females and increased TXB<sub>2</sub> compared to exposed males. In the aggregate these data indicate that maternal nano-TiO<sub>2</sub> inhalation exposure has a greater impact on redox homeostasis and PGI<sub>2</sub>/TXA<sub>2</sub> balance in the fetal female LZ. Future studies need to address if treatment with an XO inhibitor during gestation can prevent diminished fetal female growth during maternal nano-TiO<sub>2</sub> inhalation exposure.</p></abstract><kwd-group><kwd>Titanium dioxide</kwd><kwd>Thromboxane</kwd><kwd>Prostacyclin</kwd><kwd>Sexual dimorphism</kwd><kwd>Oxidants</kwd><kwd>Xanthine oxidoreductase</kwd></kwd-group></article-meta></front><body><sec id="S1"><title>Introduction</title><p id="P2">Historically, the placenta has been considered an asexual organ, however the fertilized egg gives rise to both fetus and placenta, thus the placenta and fetus are the same sex [<xref rid="R1" ref-type="bibr">1</xref>,<xref rid="R3" ref-type="bibr">3</xref>,<xref rid="R4" ref-type="bibr">4</xref>]. Sex differences in fetal development and growth have long been established, with males having accelerated growth rates relative to females, which can be observed as early as the blastocyst stage [<xref rid="R5" ref-type="bibr">5</xref>&#x02013;<xref rid="R7" ref-type="bibr">7</xref>]. Additionally, growth of the placental unit is also sex dependent. In humans, male placentas exhibit greater placental growth (mass) compared to females, which facilitates the increased growth demands of the male fetus [<xref rid="R8" ref-type="bibr">8</xref>]. Blood flow to the placenta also differs between sexes with male fetuses from normotensive pregnancies having increased blood flow over time compared to female fetuses [<xref rid="R9" ref-type="bibr">9</xref>]. Sex also impacts placental nutrient transfer. Female placentas exhibit increased fatty acid oxidation, purine degradation, and uric acid levels, indicating that females may be more susceptible to oxidative stress [<xref rid="R10" ref-type="bibr">10</xref>]. Additional disease states [<xref rid="R11" ref-type="bibr">11</xref>,<xref rid="R12" ref-type="bibr">12</xref>] or environmental insults [<xref rid="R13" ref-type="bibr">13</xref>,<xref rid="R14" ref-type="bibr">14</xref>] can further alter and exacerbate oxidative stress within the placenta.</p><p id="P3">Oxidants are produced through aerobic metabolism [<xref rid="R15" ref-type="bibr">15</xref>] and can impair cellular function through damage to proteins, lipids, and DNA [<xref rid="R16" ref-type="bibr">16</xref>]. To combat oxidants, the body produces antioxidants to maintain a homeostatic balance of these redox compounds [<xref rid="R15" ref-type="bibr">15</xref>]. This balance is especially important in early gestation as redox signaling is required for placentation [<xref rid="R15" ref-type="bibr">15</xref>]. A study of hexavalent chromium (a by-product of industrial processes involving stainless steel or metals containing chromium [<xref rid="R17" ref-type="bibr">17</xref>]) exposure during gestation in humans found that male placentas had increased oxidative stress markers compared to females and exhibited a greater reduction in antioxidant activity of the enzymes, catalase and superoxide dismutase (SOD) [<xref rid="R18" ref-type="bibr">18</xref>]. Hydroxyl radicals (HO<sup>&#x02022;</sup> and hydroperoxyl, HO<sub>2</sub><sup>&#x02022;</sup>) can result in lipid peroxidation and HO<sup>&#x02022;</sup> is thought to be formed <italic toggle="yes">via</italic> the interaction of H<sub>2</sub>O<sub>2</sub> and free iron (Fe<sup>2+</sup>) [<xref rid="R19" ref-type="bibr">19</xref>]. The hydroperoxyl radical, HO<sub>2</sub><sup>&#x02022;</sup>, can yield H<sub>2</sub>O<sub>2</sub> which can further react with metals, such as iron or copper, to further generate more HO<sup>&#x02022;</sup> [<xref rid="R19" ref-type="bibr">19</xref>]. To add to this complex system, COX, along with lipoxygenase, have been demonstrated to be minor endogenous sources of these oxidants [<xref rid="R20" ref-type="bibr">20</xref>&#x02013;<xref rid="R23" ref-type="bibr">23</xref>]. The rat and human placenta have been shown to express increasing cyclooxygenase (COX)-1 and COX-2, with COX-2 expression towards parturition [<xref rid="R24" ref-type="bibr">24</xref>]. In a mouse model, oxidative stress increased close to term and the authors proposed that this played a physiologic role by increasing prostaglandin synthesis, some of which helped to induce parturition [<xref rid="R25" ref-type="bibr">25</xref>]. Nano-TiO<sub>2</sub> (a white powder used for its optical properties in paint or photocatalyst [<xref rid="R26" ref-type="bibr">26</xref>]) inhalation exposure during gestation increased maternal liver oxidant load and placentas from nano-TiO<sub>2</sub> exposed dams had greater H<sub>2</sub>O<sub>2</sub> production capacity [<xref rid="R2" ref-type="bibr">2</xref>]. This indicates that nano-TiO<sub>2</sub> exposure during gestation may increase oxidant balance.</p><p id="P4">Maternal nano-TiO<sub>2</sub> inhalation exposure during gestation increased inflammatory signals from the maternal lung, such as interleukin (IL)-4, -5, and -13 [<xref rid="R27" ref-type="bibr">27</xref>]. We also previously demonstrated increased prostacyclin synthase and decreased prostacyclin receptor mRNA expression in the exposed dam lungs [<xref rid="R28" ref-type="bibr">28</xref>]. Pulmonary inflammatory signals may enter the circulation due to the interdependence of the pulmonary and cardiovascular systems and therefore act systemically throughout the body. Nano-TiO<sub>2</sub> inhalation exposure decreased endothelium-dependent relaxation in thoracic and femoral arteries [<xref rid="R26" ref-type="bibr">26</xref>], uterine radial arterioles [<xref rid="R29" ref-type="bibr">29</xref>], and increased uterine radial arteriole vasoconstriction in response to TXA<sub>2</sub> mimetic, U46619 [<xref rid="R28" ref-type="bibr">28</xref>]. Additionally, maternal nano-TiO<sub>2</sub> inhalation exposure during gestation increased maternal hepatic mass and H<sub>2</sub>O<sub>2</sub> production capacity [<xref rid="R2" ref-type="bibr">2</xref>], and decreased GSH: GSSH ratio. Fetal female placental outflow [<xref rid="R1" ref-type="bibr">1</xref>] was decreased in response to cyclooxygenase metabolites after maternal nano-TiO<sub>2</sub> inhalation exposure during gestation. Hepatic oxidant production is linked to vascular oxidant production and atherosclerosis [<xref rid="R30" ref-type="bibr">30</xref>]. Changes in redox balance during gestation may underlie the hindered fetal development and increased cyclooxygenase vasoreactivity. Whole, placental samples had increased mass [<xref rid="R31" ref-type="bibr">31</xref>] and H<sub>2</sub>O<sub>2</sub> production capacity [<xref rid="R2" ref-type="bibr">2</xref>] from nano-TiO<sub>2</sub> exposed dams (highlighted in <xref rid="F1" ref-type="fig">Fig. 1</xref>). Due to the inflammatory changes within the lungs, microcirculatory adaptations in COX metabolites, and liver oxidant signaling changes, we sought to investigate the changes that occurred within distinct placental zones and how fetal sex impacted these changes. This led to our hypothesis that maternal nano-TiO<sub>2</sub> inhalation during gestation increased placental production of PGI<sub>2</sub> and TXA<sub>2</sub> through H<sub>2</sub>O<sub>2</sub> in a sexually dimorphic manner.</p></sec><sec id="S2"><title>Materials and methods</title><sec id="S3"><title>Nanomaterial</title><p id="P5">Nano-TiO<sub>2</sub> powder was obtained from Evonik (P25 Aeroxide TiO<sub>2</sub>, Parsippany, NJ) and is composed of a mixture of anatase (80 %) and rutile (20 %) TiO<sub>2</sub>. Particle characteristics have previously been determined, including primary particle size (21 nm), specific surface area (48.08 m<sup>2</sup>/g), and Zeta potential (&#x02212;56.6 mV) [<xref rid="R32" ref-type="bibr">32</xref>].</p></sec><sec id="S4"><title>Inhalation exposure and aerosol characterization</title><p id="P6">A high-pressure acoustical generator (HPAG, IEStechno, Morgantown, WV) created nano-TiO<sub>2</sub> aerosols from bulk TiO<sub>2</sub> dust. These aerosols were fed into a Venturi pump (JS-60M, Vaccon, Medway, MA) to further de-agglomerate the particles. The aerosols were passed into a stainless-steel whole-body exposure chamber (Cube 150, IEStechno, Morgantown, WV) where concentration levels were monitored with a light scattering device (pDR-1500; Thermo Environmental Instruments Inc, Franklin, MA) and regulated with software driven feedback loops to maintain a stable mass aerosol concentration. Real-time aerosol size distributions were regulated in the exposure chamber at a target mass concentration of 12 mg/m<sup>3</sup> for 6 h each exposure day. Similar exposure chambers were utilized only for sham-control dams which were exposed to HEPA-filtered air only. In order to increase the likelihood of a viable pregnancy and pups to study, pregnant rats were exposed after implantation during mid to late gestation (gestational day [GD] 10&#x02013;19) for a total of 6 days. The last exposure occurs on GD 19, 24 h prior tissue collection. The exposure paradigm and aerosol characterization utilized in this study have been previously described [<xref rid="R1" ref-type="bibr">1</xref>].</p></sec></sec><sec id="S5"><title>Animal model</title><p id="P7">Female Sprague-Dawley (SD) rats were purchased from Hilltop Laboratories (Scottdale, PA) and single-housed in an American Association for Accreditation of Laboratory Animal Care (AAALAC) approved facility at West Virginia University (WVU). Temperature (20&#x02013;26 &#x000b0;C), relative humidity (30&#x02013;70 %), and light-dark cycle (12:12 h) was maintained for housed rats. After 48&#x02013;72 h for acclimation, rats were randomly assigned to either sham-control (<italic toggle="yes">N</italic> = 13) or nano-TiO<sub>2</sub> (<italic toggle="yes">N</italic> = 14) exposure groups. Rats had ad libitum access to standard chow (2918X; Envigo, Indianapolis, IN) and water throughout the acclimation and exposure periods. Rats were euthanized <italic toggle="yes">via</italic> thoracotomy and heart removal and then fetal distribution within the uterine horns and fetal sex were recorded. Fetal tissue was weighed and grouped according to fetal sex: placental junctional zone (endocrine production site), and placental labyrinth zone (nutrient-waste exchange), serum, liver, and lung were collected. Placental junctional zone (JZ) and labyrinth zone (LZ) were bluntly dissected [<xref rid="R33" ref-type="bibr">33</xref>], flash frozen in liquid nitrogen, and stored at &#x02212;80 &#x000b0;C until use. All procedures were approved by the WVU Institutional Animal Care and Use Committee.</p><p id="P8">Briefly, once dams were euthanized and pup count was recorded (previously published [<xref rid="R1" ref-type="bibr">1</xref>]), the uterus was surgically excised and placed into a dissection dish containing physiological salt solution (PSS, in mmol/L: 129.8 NaCl, 5.4 KCl, 0.5 NaH<sub>2</sub>PO<sub>4</sub>, 0.83 MgSO<sub>4</sub>, 19.0 NaHCO<sub>3</sub>, 1.8 CaCl<sub>2</sub>, 5.5 glucose). The uterus was incised longitudinally, and amnionic sacs were opened to allow for quick identification of fetal sex. Fetal sex and position within the horn was recorded, then the first male and female nearest the cervix were removed with the placenta still attached. This unit was utilized for placental hemodynamic assessment and has been previously published [<xref rid="R1" ref-type="bibr">1</xref>]. The next set of male and female units were collected for H&#x00026;E and IHC assessment and has been previously published [<xref rid="R1" ref-type="bibr">1</xref>]. The remaining males and females in the litter were utilized for serum and tissue collection for this study.</p><sec id="S6"><title>Serum collection and protein isolation</title><p id="P9">Fetal blood samples (500 &#x003bc;L) collected by cardiac puncture were collected and pooled based on sex for each litter (BD SST Microtainer Tubes; Becton, Dickinson and Co, Franklin Lakes, NJ). Samples were allowed to clot at 20 &#x000b0;C for 30 min and centrifuged at 10,000 &#x000d7; g for 90 s. Serum was collected and flash frozen until use. JZ and LZ were individually homogenized with a bead mill homogenizer (1.6 mm stainless steel beads; Next Advance, Troy, New York) in phosphate buffered saline (PBS; Fisher Scientific, Waltham, MA) containing a protease and phosphatase inhibitor cocktail (Thermo Fisher Scientific, Waltham, MA). Homogenates were centrifuged at 4 &#x000b0;C and 14,000 &#x000d7; g for 15 min using a tabletop centrifuge (Hettich Lab Instrument AB, Stockholm, Sweden). Supernatant was collected, kept on ice, and total protein concentrations assessed according to the Bradford Method [<xref rid="R34" ref-type="bibr">34</xref>]. Isolated protein samples were stored at &#x02212;80 &#x000b0;C until assayed.</p></sec><sec id="S7"><title>Xanthine oxidoreductase activity</title><p id="P10">JZ and LZ samples were homogenized in ice cold RIPA containing protease inhibitor cocktail (Sigma) and were briefly spun down. Tissue samples were processed with a sample volume of 10 &#x003bc;L. Potential urate oxidase (uricase) activity was inhibited by the addition of oxonic acid (100 &#x003bc;M) to ensure UA levels were not altered and thus enzyme activity was not underestimated. Total UA production in 60 min at 37 &#x000b0;C in the presence of xanthine (75 &#x003bc;M) served as the basis for quantification of total xanthine oxidoreductase (XOR) activity. To ensure XO dependence on urate formation as well as establish base-line UA levels, allopurinol (100 &#x003bc;M) was used in parallel samples to inhibit XOR. Following incubation for 60 min at 37 &#x000b0;C, protein was precipitated with ice cold acetonitrile. The samples were centrifuged for 12 min at 13,200 &#x000d7; g, at 4 &#x000b0;C. Following centrifugation, the supernatant was removed, placed in borosilicate glass tubes, dried (60 min), and resuspended in isocratic mobile phase (300 &#x003bc;L) and filtered through 0.20 &#x003bc;m nylon membrane filter unit into 11 mm plastic snap top auto-sample vials. The UA content was measured by electrochemical detection (Vanquish UltiMate 3000 ECD-3000RS) coupled to reverse-phase HPLC using a C18 column (150 &#x000d7; 4.6 mm, 3 &#x003bc;m particle size, Luna Phenomenex) and isocratic mobile phase (50 mM sodium dihydrogen phosphate, 4 mM dodecyl-trimethylammonium chloride, 2.5 % methanol, pH 7.0). One unit of activity (U) was defined as 1 &#x003bc;mole/min urate formed at 37 &#x000b0;C and pH 7.4. Results were expressed as a concentration relative to total sample protein content [<xref rid="R35" ref-type="bibr">35</xref>]. Inter- and intra-assay variability were less than 10 %.</p></sec><sec id="S8"><title>Hydrogen peroxide activity assay</title><p id="P11">Placental zone samples were assessed for hydrogen peroxide activity using the Amplex<sup>&#x02122;</sup> Red Hydrogen Peroxide/Peroxidase Assay Kit (A22188; Invitrogen, Waltham, MA) and performed according to manufacturer recommendations. Inter- and intra-assay variability were less than 10 %.</p></sec><sec id="S9"><title>Catalase activity assay</title><p id="P12">Placental zone tissue and serum samples were assayed for catalase activity using the Catalase Activity Assay Kit (ab83464; Abcam, Cambridge, U.K.) and performed according to manufacturer recommendations. Inter- and intra-assay variability were less than 10 %.</p></sec><sec id="S10"><title>Enzyme-linked immunosorbent assays (ELISA)</title><p id="P13">Fetal tissue extracts and serum were diluted with assay buffer and assays were performed to assess TXB<sub>2</sub> (501020; Thromboxane B2 Elisa Kit) and 6-keto-PGF<sub>1</sub>&#x003b1; (515211, 6-keto Prostaglandin F<sub>1</sub>&#x003b1; Elisa Kit) according to manufacturer recommendations (Cayman Chemical Company, Ann Arbor, MI). Inter- and intra-assay variability were less than 10 %.</p></sec><sec id="S11"><title>mRNA analysis by real-time PCR</title><p id="P14">Total RNA was extracted from placental zones, fetal lungs, and resorption sites <italic toggle="yes">via</italic> the RNeasy Kit based on manufacturers recommendations (74104; Qiagen, Hilden, Germany). Total RNA was then transcribed to cDNA <italic toggle="yes">via</italic> the High-Capacity RNA-to-cDNA kit (4387406; Thermo Fisher Scientific, Waltham, MA).</p><p id="P15">Using real-time PCR, prostacyclin synthase (<italic toggle="yes">Ptgis</italic>), prostacyclin receptor (<italic toggle="yes">Ptgir</italic>), thromboxane receptor (<italic toggle="yes">Tbxa2r</italic>), superoxide dismutase (<italic toggle="yes">Sod1</italic>), catalase (<italic toggle="yes">Cat</italic>), estrogen receptor alpha (<italic toggle="yes">Esr1</italic>), and estrogen receptor beta (<italic toggle="yes">Esr2</italic>) were assessed. Primers were purchased from Integrated DNA Technologies (Coralville, IA); GenBank accession numbers, primer sequences, and references are listed in <xref rid="T1" ref-type="table">Table 1</xref>. Samples were analyzed in triplicate using iTAQ Universal SYBR Green Supermix (Bio-Rad Laboratories, Hercules, CA). Relative fold changes in expression of candidate genes were obtained using the 2&#x02212;&#x00394;&#x00394;Ct method [<xref rid="R36" ref-type="bibr">36</xref>]. The Ct values were used to calculate &#x00394;Ct values for genes of interest [Ct(test) &#x02013; Ct(housekeeping)]. A housekeeping panel consisting of <italic toggle="yes">beta actin, ribosomal small subunit 18</italic>, and GAPDH was run on each tissue. Across tested tissue types, GAPDH was the most stable housekeeping gene and therefore tissues were normalized to GAPDH (<italic toggle="yes">gapdh</italic>). Statistical representation for each gene is based on fold change with respect to GAPDH.</p></sec><sec id="S12"><title>Statistics</title><p id="P16">Values for xanthine oxidase, catalase, hydrogen peroxide, results from tissue ELISA&#x02019;s, and mRNA analyses were assessed <italic toggle="yes">via</italic> a two-way mixed-effects ANOVA. The two-way mixed-effects ANOVA was utilized to compare exposures and fetal sex in a two-by-two comparison. Litter size was nested within the two-way ANOVA to account for differences in pup number between dams. Exposure effects, sex effects, and an interaction of exposure and sex were assessed. If exposure, sex, or an interaction occurred, then individual group differences could be assessed with post-hoc tests. If statistical significance was noted, then &#x00160;&#x000ed;d&#x000e1;k<sub>&#x02019;</sub>s post-hoc test was used. All statistical analysis were performed with Graph Pad Prism 9 (San Diego, CA). Significance was set at <italic toggle="yes">p</italic> &#x02264; 0.05, with N representing the number of litters per group. All data is reported as the mean &#x000b1; SEM, unless otherwise stated.</p></sec></sec><sec id="S13"><title>Results</title><sec id="S14"><title>Nano-TiO<sub>2</sub> exposed fetal females have increased heart mass and decreased liver mass compared to nano-TiO<sub>2</sub> exposed fetal males</title><p id="P17">An exposure effect was observed with fetal heart mass, with nano-TiO<sub>2</sub> exposed hearts being significantly heavier (<xref rid="F2" ref-type="fig">Fig. 2A</xref>). A sex effect was seen in heart mass, of which fetal females had significantly heavier hearts. Additionally, there was an interaction between exposure and sex, whereby nano-TiO<sub>2</sub> fetal females had significantly increased heart mass compared to nano-TiO<sub>2</sub> fetal males and sham-control fetal females (<xref rid="F2" ref-type="fig">Fig. 2A</xref>). This same pattern persists with normalized fetal heart mass normalized to total fetal mass. There was an exposure effect, sex effect, and an interaction of exposure and sex. Nano-TiO<sub>2</sub> fetal female normalized heart mass was significantly increased compared to nano-TiO<sub>2</sub> fetal males and sham-control fetal females (<xref rid="F2" ref-type="fig">Fig. 2B</xref>).</p><p id="P18">No exposure effect, sex effect, or an interaction of sex and exposure was seen with fetal lung tissue (<xref rid="F2" ref-type="fig">Fig. 2C</xref>). Normalized fetal lung mass to fetal mass had an exposure effect, which nano-TiO<sub>2</sub> had decreased normalized lung tissue compared to sham-control (<xref rid="F2" ref-type="fig">Fig. 2D</xref>). There was no effect of sex or an interaction of exposure and sex.</p><p id="P19">Fetal liver mass did not have an exposure effect or sex effect but did have a trend (<italic toggle="yes">p</italic> = 0.054) towards an interaction of exposure and sex. Nano-TiO<sub>2</sub> fetal female livers trended (<italic toggle="yes">p</italic> = 0.051) towards significantly decreased in mass compared to nano-TiO<sub>2</sub> exposed fetal male liver mass (<xref rid="F2" ref-type="fig">Fig. 2E</xref>). Normalized fetal liver mass to total fetal mass did not have an exposure effect or sex effect but trended (<italic toggle="yes">p</italic> = 0.054) towards an interaction of exposure and sex (<xref rid="F2" ref-type="fig">Fig. 2F</xref>). Nano-TiO<sub>2</sub> fetal female normalized liver mass was significantly decreased compared to sham-control fetal female and nano-TiO<sub>2</sub> fetal male normalized liver masses.</p></sec><sec id="S15"><title>XOR activity is decreased in nano-TiO<sub>2</sub> fetal female JZ versus sham-control female JZ</title><p id="P20">In the JZ, there was a significant effect of exposure on XOR activity, with decreased XOR activity in nano-TiO<sub>2</sub> JZ compared to sham-control JZ (<xref rid="F3" ref-type="fig">Fig. 3A</xref>). There was not an effect of fetal sex, nor an interaction of exposure and fetal sex. In the LZ, there was not an effect of exposure on XOR activity, but there was a significant effect of fetal sex on XOR activity. Female LZ XOR activity was significantly increased compared to males. LZ XOR activity was increased in sham-control females compared to sham-control males and in exposed fetal females compared to exposed fetal males (<xref rid="F3" ref-type="fig">Fig. 3B</xref>). There was no interaction of exposure and fetal sex.</p></sec><sec id="S16"><title>Hydrogen peroxide levels are decreased in nano-TiO<sub>2</sub> fetal male JZ</title><p id="P21">In the JZ, there was a trend (<italic toggle="yes">p</italic> = 0.06) for an exposure effect, where nano-TiO<sub>2</sub> JZ&#x02019;s exhibited decreased H<sub>2</sub>O<sub>2</sub> concentration compared to sham-control JZ&#x02019;s (<xref rid="F3" ref-type="fig">Fig. 3C</xref>). There was no difference for sex effect or an interaction of exposure and sex. In the LZ, there were no differences among exposure, sex, or an interaction between groups for H<sub>2</sub>O<sub>2</sub> concentration, <xref rid="F3" ref-type="fig">Fig. 3D</xref>.</p></sec><sec id="S17"><title>Catalase activity was decreased in nano-TiO<sub>2</sub> fetal female LZ versus sham-control fetal female</title><p id="P22">An exposure effect was not seen in fetal serum catalase activity. Catalase activity in fetal serum differed in a sex-dependent manner, which levels were greater in males than females. There was no interaction between exposure or sex. Fetal serum catalase activity was significantly less in sham-control females compared to sham-control males (<xref rid="F4" ref-type="fig">Fig. 4A</xref>) and in nano-TiO<sub>2</sub> exposed pups.</p><p id="P23">In the JZ, exposed groups demonstrated significantly decreased levels of catalase activity than nonexposed groups (<xref rid="F4" ref-type="fig">Fig. 4B</xref>), but there was no effect of sex or an interaction of sex and exposure. Catalase activity within the LZ was impacted by exposure as catalase activity was significantly diminished in exposed than sham-control groups. There was also a trend (<italic toggle="yes">p</italic> = 0.08) toward an effect of sex. Females had increased catalase activity compared to males. LZ catalase activity was decreased in nano-TiO<sub>2</sub> exposed fetal females compared to sham-control fetal females (<xref rid="F4" ref-type="fig">Fig. 4C</xref>). Nano-TiO<sub>2</sub> exposed fetal males catalase activity was not different compared to sham-control males.</p></sec><sec id="S18"><title>Fetal female LZ TXB<sub>2</sub> levels were increased compared to sham-control females</title><p id="P24">There were significant effects of exposure, sex, and an exposure by sex interaction for circulating levels of fetal 6-keto-PGF<sub>1</sub>&#x003b1;. Nano-TiO<sub>2</sub> fetal serum had increased 6-keto-PGF<sub>1</sub>&#x003b1; compared to sham-control fetal serum. Fetal females had increased 6-keto-PGF<sub>1</sub>&#x003b1; compared to males. Due to an exposure by sex interaction, there was significantly increased levels of 6-keto-PGF<sub>1</sub>&#x003b1; in exposed fetal females compared to exposed males and sham-control females (<xref rid="F5" ref-type="fig">Fig. 5A</xref>). In contrast, no effect of exposure was observed in circulating levels of fetal TXB<sub>2</sub>. However, TXB<sub>2</sub> demonstrated an effect of sex as levels were increased in fetal females compared to males. TXB<sub>2</sub> was increased for sham-control females compared to sham-control males (<xref rid="F5" ref-type="fig">Fig. 5B</xref>). There was no interaction between exposure and sex.</p><p id="P25">Levels of 6-keto-PGF<sub>1</sub>&#x003b1; in the JZ did not show an effect of exposure, sex, or interaction (<xref rid="F5" ref-type="fig">Fig. 5C</xref>). However, concentrations of TXB<sub>2</sub> in JZ were not impacted by exposure but were significantly impacted by sex. TXB<sub>2</sub> JZ concentration was increased in females compared to males. JZ TXB<sub>2</sub> concentrations had a significant interaction of exposure and sex. JZ TXB<sub>2</sub> levels were significantly increased in exposed fetal females compared to exposed fetal males (<xref rid="F5" ref-type="fig">Fig. 5D</xref>) and sham-control fetal females. There was not a difference between sham-control females and males.</p><p id="P26">There was a significant effect of exposure on levels of 6-keto-PGF<sub>1</sub>&#x003b1; in LZs as values were increased in exposed groups. There was no effect of sex or an interaction of exposure by sex. LZ 6-keto-PGF<sub>1</sub>&#x003b1; was increased in exposed fetal females compared to sham-control fetal females (<xref rid="F5" ref-type="fig">Fig. 5E</xref>), the same pattern exists for fetal males. Conversely, LZ TXB<sub>2</sub> levels were significantly affected by exposure, sex, and their interaction. TXB<sub>2</sub> concentrations within the LZ were significantly increased in exposed LZs compared to sham-control. Fetal female LZ TXB<sub>2</sub> levels were increased compared to fetal male LZ&#x02019;s. TXB<sub>2</sub> concentrations was significantly increased in the exposed fetal female LZ compared to exposed males and sham-control female LZ&#x02019;s (<xref rid="F5" ref-type="fig">Fig. 5F</xref>).</p></sec><sec id="S19"><title>Exposed fetal female JZ had decreased catalase mRNA expression</title><p id="P27">JZ prostacyclin receptor gene expression was not impacted by exposure but was significantly affected by sex and the interaction of sex and exposure. Nano-TiO<sub>2</sub> exposed fetal JZ had significantly increased prostacyclin receptor mRNA expression compared to exposed fetal male JZs (<xref rid="T2" ref-type="table">Table 2</xref>) and sham-control females. JZ catalase expression was not different for exposure, but was significantly impacted by sex and the interaction of sex and exposure. Wherein catalase expression in exposed females was decreased compared to exposed males (<xref rid="T2" ref-type="table">Table 2</xref>). JZ mRNA expression was not different for thromboxane receptor, prostacyclin synthase, superoxide dismutase, ER&#x003b1;, or ER&#x003b2; (<xref rid="T2" ref-type="table">Table 2</xref>). Statistical differences were not detected in LZ mRNA expression for any of the evaluated targets across groups.</p><p id="P28">Fetal lung and implantation sites, where the embryo embeds into the uterus and is the last maternal interface that attaches to the placenta, were assessed for cyclooxygenase metabolites, prostacyclin synthase, prostacyclin receptor, and thromboxane receptor. Fetal lung thromboxane receptor mRNA expression expressed a trend for an effect of exposure (<italic toggle="yes">p</italic> = 0.06). Expression of thromboxane receptor mRNA was decreased in exposed fetal lung compared to sham-control, especially in male nano-TiO2 fetal lung (<xref rid="T3" ref-type="table">Table 3</xref>). There were no differences in fetal lung mRNA expression of prostacyclin receptor or prostacyclin synthase. Implantation site expression of prostacyclin synthase was not different for exposure but was impacted by sex and the interaction of sex and exposure. Nano-TiO2 exposed fetal female implantation sites had significantly increased prostacyclin synthase mRNA expression compared to exposed male counterparts (<xref rid="T3" ref-type="table">Table 3</xref>) and sham-control females. There were no significant effects of exposure or sex for implantation sites in mRNA expression of thromboxane receptor or prostacyclin receptor.</p></sec></sec><sec id="S20"><title>Discussion</title><p id="P29">This study aimed to identify the relationship between H<sub>2</sub>O<sub>2</sub> and the cyclooxygenase metabolites, PGI2 and TXA2, in male and female feto-placental units after maternal nano-TiO<sub>2</sub> inhalation exposure during gestation. We have previously demonstrated that maternal nano-TiO<sub>2</sub> inhalation exposure during gestation reduces fetal female mass, female placenta mass and area, as well as placenta immune cell invasion [<xref rid="R1" ref-type="bibr">1</xref>]. Liver and placental tissues from dams directly exposed to nano-TiO<sub>2</sub> exhibit increased indices of oxidant stress and an increased H<sub>2</sub>O<sub>2</sub> abundance, indicating that these tissues have increased oxidant load [<xref rid="R2" ref-type="bibr">2</xref>]. As adults, females exposed to nano-TiO<sub>2</sub>
<italic toggle="yes">in utero</italic> exhibited decreased circulating estrogen levels during gestation, decreased litter size, and decreased pup mass [<xref rid="R2" ref-type="bibr">2</xref>]. This suggests that maternal nano-TiO<sub>2</sub> inhalation exposure during gestation not only impacts redox balance in the dam but also impacts female feto-placental growth and development during gestation and later in life. Modifications in redox balance could potentially contribute to the reduced cyclooxygenase metabolite vasoreactivity in dam uterine radial arterioles [<xref rid="R28" ref-type="bibr">28</xref>] and/or decreased placental outflow in the presence of U46619, the stable TXA<sub>2</sub> mimetic, in exposed fetal females [<xref rid="R1" ref-type="bibr">1</xref>] previously shown. In this study, placentas from female pups whose mothers were exposed to nano-TiO<sub>2</sub> during gestation had increased XOR activity and decreased catalase activity, which indicates an oxidative stress/antioxidant imbalance. Taken together, placentas from female pups exposed <italic toggle="yes">in utero</italic> demonstrate redox and cyclooxygenase imbalance, impacts placental nutrient-waste exchange, and ultimately fetal growth and development.</p><p id="P30">It is important to note that toxicant exposure consistently increases oxidant production [<xref rid="R37" ref-type="bibr">37</xref>], decreases catalase activity [<xref rid="R38" ref-type="bibr">38</xref>], and increases prostacyclin metabolite production [<xref rid="R39" ref-type="bibr">39</xref>], in HUVECs or guinea pig alveolar cells. This implies that toxicants, such as nano-TiO<sub>2</sub>, can modify the balance between oxidants and antioxidants, thus disrupting downstream signaling by molecules such as prostacyclin or thromboxane. Additionally, placental growth occurs in a hypoxic environment, with oxygen tension residing at 2&#x02013;3 % (25&#x02013;38 &#x003bc;M dissolved O<sub>2</sub>) in the first trimester and beginning of the second [<xref rid="R40" ref-type="bibr">40</xref>]. This becomes important when considering that the low O<sub>2</sub> tension diminishes superoxide generation by xanthine oxidase (XO), thus elevates H<sub>2</sub>O<sub>2</sub> production to nearly 90 % [<xref rid="R41" ref-type="bibr">41</xref>]. Our current study found that nano-TiO<sub>2</sub> exposed females had increased XDH activity. This will lead to increased oxidants and uric acid production, which may increase placental inflammation and insufficiency, both of which we have previously demonstrated in exposed fetal females [<xref rid="R1" ref-type="bibr">1</xref>]. This implies that increased XOR in these exposed fetal females could contribute to their increased placental resistance and modified placental structure, thus impacting fetal female growth and development.</p><p id="P31">XOR can generate superoxide, H<sub>2</sub>O<sub>2</sub>, and NADH when transferring electrons from xanthine to oxygen and NAD<sup>+</sup> [<xref rid="R42" ref-type="bibr">42</xref>]. Due to the increased XOR activity found in exposed fetal female placentas, we examined H<sub>2</sub>O<sub>2</sub> levels. No differences were observed in H<sub>2</sub>O<sub>2</sub> levels across fetal sex or placental zones. This differs with previous results from our laboratory, which demonstrated increased placental capacity to produce H<sub>2</sub>O<sub>2</sub> in collected tissue from nano-TiO<sub>2</sub> exposed dams [<xref rid="R2" ref-type="bibr">2</xref>]. In a mouse model of gestational exposure to hypoxia, placentas from hypoxic male fetuses were heavier than the hypoxia exposed fetal female placentas [<xref rid="R43" ref-type="bibr">43</xref>], and the hypoxic fetal female placentas demonstrated increased oxidative stress markers. This study highlights that oxidative stress is impacted by fetal sex. In homeostasis, redox balance is maintained <italic toggle="yes">via</italic> the action of small molecule antioxidants and enzymes such as catalase. Herein, we demonstrated that catalase activity in nano-TiO<sub>2</sub> females was significantly decreased within the LZ. Therefore, the decreased growth in female fetuses previously shown to occur due to maternal nano-TiO<sub>2</sub> inhalation exposure [<xref rid="R1" ref-type="bibr">1</xref>] may be explained, at least in part, by oxidative imbalance within the LZ, where nutrient-waste exchange occurs.</p><p id="P32">Previous results from our laboratory demonstrated significantly decreased circulating TXB<sub>2</sub> levels in nano-TiO<sub>2</sub> exposed dams [<xref rid="R28" ref-type="bibr">28</xref>]. Based on these results, both 6-keto-PGF<sub>1</sub>&#x003b1; and TXB<sub>2</sub> are important vasoactive compounds, thus it was necessary to measure placental zone and fetal serum levels of 6-keto-PGF<sub>1</sub>&#x003b1; and TXB<sub>2</sub>. Increased circulating levels of 6-keto-PGF<sub>1</sub>&#x003b1; were found in the fetal females from nano-TiO<sub>2</sub> exposed dams, which could be indicative of an elevated immune response. Complications during gestation, such as asthma and gestational diabetes, have been associated with increased placental expression of inflammatory immune markers such as, TNF-&#x003b1;, IL-1&#x003b2;, IL-6, and IL-8 [<xref rid="R44" ref-type="bibr">44</xref>,<xref rid="R45" ref-type="bibr">45</xref>]. Further, Hofbauer cells, which are fetal derived macrophages, have increased production of pro-inflammatory cytokines in gestational diabetes [<xref rid="R45" ref-type="bibr">45</xref>]. Maternal nano-TiO<sub>2</sub> exposure significantly increased female placenta Hofbauer cell invasion [<xref rid="R1" ref-type="bibr">1</xref>] and maternal circulating IL-1&#x003b2; and TNF&#x003b1; [<xref rid="R27" ref-type="bibr">27</xref>]. IL-1&#x003b2; is reported to induce COX-2 expression [<xref rid="R46" ref-type="bibr">46</xref>&#x02013;<xref rid="R48" ref-type="bibr">48</xref>], which is the enzyme that catalyzes the production of PGI<sub>2</sub> [<xref rid="R48" ref-type="bibr">48</xref>], and could promote this increased 6-keto-PGF<sub>1</sub>&#x003b1; levels in fetal females from nano-TiO<sub>2</sub> exposed dams. Placental tissue, specifically the LZ, exhibited significantly increased 6-keto-PGF<sub>1</sub>&#x003b1; and TXB<sub>2</sub> levels from fetal females that were exposed <italic toggle="yes">in utero</italic>. Human pregnancies with intervillous blood flow below the normal mean (less than 130 mL/min) exhibit increased placental TXA<sub>2</sub> production [<xref rid="R49" ref-type="bibr">49</xref>]. In a preeclampsia mouse model that simulated modified blood flow to the fetoplacental unit, preeclampsia mice placentas had elevated TXA<sub>2</sub> synthase and plasma TXA<sub>2</sub>, but not prostacyclin levels [<xref rid="R50" ref-type="bibr">50</xref>]. This indicates that the balance of TXA<sub>2</sub> and PGI<sub>2</sub> levels is critical in regulating blood flow to the feto-placental unit. A rat intrauterine growth restriction (IUGR) study found that IUGR male umbilical arteries had decreased maximal contraction in response to U46619, the TXA<sub>2</sub> mimetic, compared to IUGR females [<xref rid="R51" ref-type="bibr">51</xref>]. This highlights that changes in placental production of TXA<sub>2</sub>, and PGI<sub>2</sub> to a lesser extent, impact blood flow and further impact fetal growth and development in a sex-based manner. It is possible that the redox imbalance, specifically the increased XOR-catalyzed peroxide production and decreased catalase activity within the LZ, leads to the overall increase in PGI<sub>2</sub> and TXA<sub>2</sub> levels seen in the LZ of exposed fetal females. This would ultimately result in modified uteroplacental blood flow [<xref rid="R1" ref-type="bibr">1</xref>], as we have observed previously, and impair fetal growth and development due to modified redox homeostasis.</p><p id="P33">However, with all this information, there are a few study limitations that need to be addressed. The first limitation is that we do not know where the XO is coming from. A way to address this concern would be the incorporation of an XO-tissue specific knock-out mouse model. We would need to run a few small studies on wild-type mice first, to verify that the pregnant mice would respond to nano-TiO<sub>2</sub> inhalation exposure during gestation similarly to our current rat model. Further, we do not have any febuxostat data in this study, to verify that XO could be driving these changes seen in H<sub>2</sub>O<sub>2</sub> and catalase activity after maternal nano-TiO<sub>2</sub> inhalation exposure during gestation. This is already an on-going study in our laboratory. Another limitation that should be addressed is the difference of H<sub>2</sub>O<sub>2</sub> levels seen in this study and a previous one from our laboratory [<xref rid="R2" ref-type="bibr">2</xref>]. The differences are most likely caused by a few things. First, herein, the placentas were split into the two main zones, JZ (the endocrine production site) and the LZ (nutrient-waste exchange site), previously the whole placenta was assessed. Second, this study assessed the impacts of fetal sex on placental tissue, which fetal sex does matter in relation to placental and fetal tissue assessment. The sex of the fetus was not accounted for in the previous study. Lastly, herein, we utilized an entirely different assay, and measurement for H<sub>2</sub>O<sub>2</sub>. In this study, we utilized an Amplex Red H<sub>2</sub>O<sub>2</sub> kit, which measured the amount of H<sub>2</sub>O<sub>2</sub>. Whereas the previous study used a Coumarin boronic acid (CBA) assay, which measures the production rate of H<sub>2</sub>O<sub>2</sub>. These limitations are important to note and are points that are planned to be addressed in future experiments in our laboratory.</p><p id="P34">In conclusion, this study sought to determine if maternal nano-TiO<sub>2</sub> inhalation exposure resulted in modified redox homeostasis that altered production of PGI<sub>2</sub>/TXA<sub>2</sub> within the placental zones in a sexually dimorphic manner. Our exposure paradigm has provided evidence that maternal nano-TiO<sub>2</sub> inhalation exposure modified redox homeostasis within placental zones and impacted fetal female growth and mass, placental development, and hemodynamics [<xref rid="R1" ref-type="bibr">1</xref>]. These modifications likely impact COX metabolite production, ultimately modifying fetal growth in a sexually dimorphic manner, with the greatest growth impacts on exposed females (<xref rid="F6" ref-type="fig">Fig. 6</xref>). These adaptations in the exposed fetal female likely ensures survival throughout gestation but could have lasting negative health impacts on females later in life. Future studies should focus on if treatment with an XO inhibitor, such as febuxostat, during gestation can prevent diminished fetal female growth and development during maternal nano-TiO<sub>2</sub> inhalation exposure. This will help elucidate if dysregulated redox homeostasis underlies the fetal and placental deficits observed after exposure and provide a possible treatment option to women who have imbalanced redox and COX metabolites.</p></sec></body><back><ack id="S21"><title>Acknowledgments</title><p id="P35">The authors are grateful to Dr. Stan Hileman for his review comments on the manuscript.</p><sec id="S22"><title>Funding</title><p id="P36">This work was supported by the following sources: National Institutes of Health K01 10029010 (ECB), WV-CTSI U54 GM104942-05 (ECB), R01 ES015022 (TRN), T32 AG 52375 (JAG), T32 ES032920 (JAG), WV-INBRE P20 GM103434.</p></sec></ack><fn-group><fn fn-type="COI-statement" id="FN1"><p id="P38">Declaration of Competing Interest</p><p id="P39">The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.</p></fn><fn id="FN3"><p id="P40">CRediT authorship contribution statement</p><p id="P41"><bold>Julie A. Griffith:</bold> Conceptualization, Data curation, Formal analysis, Investigation, Methodology, Writing &#x02013; original draft, Writing &#x02013; review &#x00026; editing. <bold>Rachel D. King:</bold> Data curation, Investigation, Writing &#x02013; review &#x00026; editing. <bold>Allison C. Dunn:</bold> Data curation, Investigation, Writing &#x02013; review &#x00026; editing. <bold>Sara E. Lewis:</bold> Data curation, Investigation, Writing &#x02013; review &#x00026; editing. <bold>Brooke A. Maxwell:</bold> Data curation, Investigation, Writing &#x02013; review &#x00026; editing. <bold>Timothy R. Nurkiewicz:</bold> Formal analysis, Funding acquisition, Writing &#x02013; review &#x00026; editing. <bold>William T. Goldsmith:</bold> Methodology, Writing &#x02013; review &#x00026; editing. <bold>Eric E. Kelley:</bold> Resources, Supervision, Writing &#x02013; review &#x00026; editing. <bold>Elizabeth C. Bowdridge:</bold> Conceptualization, Data curation, Formal analysis, Funding acquisition, Investigation, Methodology, Resources, Visualization, Writing &#x02013; original draft, Writing &#x02013; review &#x00026; editing.</p></fn></fn-group><sec sec-type="data-availability" id="S23"><title>Data availability</title><p id="P37">Data will be made available on request.</p></sec><glossary><title>Abbreviations:</title><def-list><def-item><term>COX</term><def><p id="P42">cyclooxygenase</p></def></def-item><def-item><term>GD</term><def><p id="P43">gestational day</p></def></def-item><def-item><term>H<sub>2</sub>O<sub>2</sub></term><def><p id="P44">hydrogen peroxide</p></def></def-item><def-item><term>JZ</term><def><p id="P45">junctional zone</p></def></def-item><def-item><term>LZ</term><def><p id="P46">labyrinth zone</p></def></def-item><def-item><term>PGI<sub>2</sub></term><def><p id="P47">prostacyclin</p></def></def-item><def-item><term>SOD</term><def><p id="P48">superoxide dismutase</p></def></def-item><def-item><term>TXA<sub>2</sub></term><def><p id="P49">thromboxane</p></def></def-item><def-item><term>XDH</term><def><p id="P50">xanthine dehydrogenase</p></def></def-item><def-item><term>XO</term><def><p id="P51">xanthine oxidase</p></def></def-item><def-item><term>XOR</term><def><p id="P52">xanthine oxidoreductase</p></def></def-item></def-list></glossary><ref-list><title>References</title><ref id="R1"><label>[1]</label><mixed-citation publication-type="journal"><name><surname>Griffith</surname><given-names>JA</given-names></name>, <name><surname>Dunn</surname><given-names>A</given-names></name>, <name><surname>DeVallance</surname><given-names>E</given-names></name>, <name><surname>Schafner</surname><given-names>KJ</given-names></name>, <name><surname>Engles</surname><given-names>KJ</given-names></name>, <name><surname>Batchelor</surname><given-names>TP</given-names></name>, <name><surname>Goldsmith</surname><given-names>WT</given-names></name>, <name><surname>Wix</surname><given-names>K</given-names></name>, <name><surname>Hussain</surname><given-names>S</given-names></name>, <name><surname>Bowdridge</surname><given-names>EC</given-names></name>, <name><surname>Nurkiewicz</surname><given-names>TR</given-names></name>, <article-title>Maternal nano-titanium dioxide inhalation alters fetoplacental outcomes in a sexually dimorphic manner</article-title>, <source>Front. 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</mixed-citation></ref></ref-list></back><floats-group><fig position="float" id="F1"><label>Fig. 1.</label><caption><title>Graphical representation of lung-liver-placenta axis interaction.</title><p id="P53">Maternal nano-TiO<sub>2</sub> inhalation exposure increases inflammatory signals within the maternal lung, which may spill over into the circulation. Maternal nano-TiO<sub>2</sub> inhalation exposure has been shown to decrease endothelium-dependent relaxation in many vascular beds. Further, maternal hepatic mass and H<sub>2</sub>O<sub>2</sub> production capacity is increased in nano-TiO<sub>2</sub> exposed dams. Changes in redox balance during gestation may underlie hindered fetal female development and increased cyclooxygenase vasoreactivity in fetal female placental outflow.</p></caption><graphic xlink:href="nihms-1977854-f0001" position="float"/></fig><fig position="float" id="F2"><label>Fig. 2.</label><caption><title>Fetal tissue mass and normalized fetal tissue mass.</title><p id="P54">Fetal wet tissue mass was weighed and then normalized to fetal weight mass. (A) Fetal heart mass. (B) Normalized fetal heart to fetal mass. (C) Fetal lung mass. (D) Normalized fetal lung to fetal mass. (E) Fetal liver mass. (F) Normalized fetal liver. Sham-control male (<italic toggle="yes">N</italic> = 10), sham-control female (<italic toggle="yes">N</italic> = 10), nano-TiO<sub>2</sub> male (<italic toggle="yes">N</italic> = 10), and nano-TiO<sub>2</sub> female (<italic toggle="yes">N</italic> = 10). *, <italic toggle="yes">p</italic> &#x02264; 0.05 exposure effect. #, <italic toggle="yes">p</italic> &#x02264; 0.05 for sex effect.</p></caption><graphic xlink:href="nihms-1977854-f0002" position="float"/></fig><fig position="float" id="F3"><label>Fig. 3.</label><caption><title>Placental xanthine oxidoreductase activity and hydrogen peroxide concentration.</title><p id="P55">Placental activity of xanthine oxidoreductase (XOR) and hydrogen peroxide (H<sub>2</sub>O<sub>2</sub>) concentration were assessed in each placenta zone. (A) Junctional zone (JZ) XOR activity. (B) Labyrinth zone (LZ) XOR activity. (C) JZ H<sub>2</sub>O<sub>2</sub> levels. (D) LZ H<sub>2</sub>O<sub>2</sub> concentration. Sham-control male (<italic toggle="yes">N</italic> = 8), sham-control female (<italic toggle="yes">N</italic> = 6&#x02013;8), nano-TiO<sub>2</sub> male (<italic toggle="yes">N</italic> = 8), and nano-TiO<sub>2</sub> female (<italic toggle="yes">N</italic> = 8). *, <italic toggle="yes">p</italic> &#x02264; 0.05 exposure effect. #, <italic toggle="yes">p</italic> &#x02264; 0.05 for sex effect.</p></caption><graphic xlink:href="nihms-1977854-f0003" position="float"/></fig><fig position="float" id="F4"><label>Fig. 4.</label><caption><title>Placental and fetal serum catalase activity.</title><p id="P56">Catalase activity was assessed in fetal serum and in each placenta zone. (A). Fetal serum catalase activity. (B) JZ catalase activity. (C) LZ catalase activity. Sham-control male (<italic toggle="yes">N</italic> = 3&#x02013;4), sham-control female (<italic toggle="yes">N</italic> = 3&#x02013;4), nano-TiO<sub>2</sub> male (<italic toggle="yes">N</italic> = 3&#x02013;4), and nano-TiO<sub>2</sub> female (<italic toggle="yes">N</italic> = 3&#x02013;4). *, <italic toggle="yes">p</italic> &#x02264; 0.05 exposure effect. #, <italic toggle="yes">p</italic> &#x02264; 0.05 for sex effect.</p></caption><graphic xlink:href="nihms-1977854-f0004" position="float"/></fig><fig position="float" id="F5"><label>Fig. 5.</label><caption><title>Placental and fetal serum 6-keto-PGF<sub>1&#x003b1;</sub> and TXB<sub>2</sub> production.</title><p id="P57">Cyclooxygenase metabolites (6-keto-PGF<sub>1&#x003b1;</sub> and TXB<sub>2</sub>) were assessed in fetal serum and each placenta zone. (A) Fetal serum levels of 6-keto-PGF<sub>1&#x003b1;</sub>. (B) Fetal serum TXB<sub>2</sub> levels. (C) JZ 6-keto-PGF<sub>1&#x003b1;</sub> levels. (D) JZ production of TXB<sub>2</sub>. (E) LZ levels of 6-keto-PGF<sub>1&#x003b1;</sub>. (F) LZ TXB<sub>2</sub> levels. Sham-control males (<italic toggle="yes">N</italic> = 5), sham-control females (<italic toggle="yes">N</italic> = 5), nano-TiO<sub>2</sub> males (<italic toggle="yes">N</italic> = 4&#x02013;5), and nano-TiO<sub>2</sub> female (<italic toggle="yes">N</italic> = 3&#x02013;5). *, <italic toggle="yes">p</italic> &#x02264; 0.05 exposure effect. #, <italic toggle="yes">p</italic> &#x02264; 0.05 for sex effect.</p></caption><graphic xlink:href="nihms-1977854-f0005" position="float"/></fig><fig position="float" id="F6"><label>Fig. 6.</label><caption><title>Summary of the impacts of maternal nano-TiO<sub>2</sub> inhalation exposure during gestation on placental oxidant balance in a sex dependent manner.</title><p id="P58">Maternal nano-TiO<sub>2</sub> inhalation exposure during gestation results in sexually dimorphic modifications to redox balance and thus impacts cyclooxygenase metabolites in the labyrinth zone at GD 20. Females have demonstrated greater impact in their mass (JZ and LZ), area (JZ) compared to exposed males [<xref rid="R1" ref-type="bibr">1</xref>]. Females also have increased XDH activity (LZ), decreased catalase activity (LZ), and increased production of both, 6-keto-PGF<sub>1&#x003b1;</sub> and TXB<sub>2</sub> (LZ). These resulting changes are likely responsible for the decreased fetal female weight at GD 20, of which progresses to female deficits into adulthood [<xref rid="R2" ref-type="bibr">2</xref>].</p></caption><graphic xlink:href="nihms-1977854-f0006" position="float"/></fig><table-wrap position="float" id="T1" orientation="landscape"><label>Table 1</label><caption><p id="P59">Real-time PCR primers, their sequence, length, and references.</p></caption><table frame="hsides" rules="none"><colgroup span="1"><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/></colgroup><thead><tr><th align="left" valign="top" rowspan="1" colspan="1"/><th align="left" valign="top" rowspan="1" colspan="1">Forward primer (5&#x02019;&#x02013;3&#x02019;)</th><th align="left" valign="top" rowspan="1" colspan="1">Reverse primer (5&#x02019;&#x02013;3&#x02019;)</th><th align="left" valign="top" rowspan="1" colspan="1">Length (bp)</th><th align="left" valign="top" rowspan="1" colspan="1">Ref.</th></tr><tr><th align="left" valign="top" colspan="5" rowspan="1">
<hr/>
</th></tr></thead><tbody><tr><td align="left" valign="top" rowspan="1" colspan="1">Gapdh NM_017008</td><td align="left" valign="top" rowspan="1" colspan="1">AGGGCTGCCTTCTCTTGTGAC</td><td align="left" valign="top" rowspan="1" colspan="1">TGGGTAGAATCATACTGGAACATGTAG</td><td align="left" valign="top" rowspan="1" colspan="1">101</td><td align="left" valign="top" rowspan="1" colspan="1">[<xref rid="R52" ref-type="bibr">52</xref>]</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">Esr1 NM_012689</td><td align="left" valign="top" rowspan="1" colspan="1">GCACATTCCTTCCTTCCGTC</td><td align="left" valign="top" rowspan="1" colspan="1">CTCGTTCCCTTGGATCTGGT</td><td align="left" valign="top" rowspan="1" colspan="1">216</td><td align="left" valign="top" rowspan="1" colspan="1">[<xref rid="R53" ref-type="bibr">53</xref>]</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">Esr2 NM_012754</td><td align="left" valign="top" rowspan="1" colspan="1">TTCCCGGCAGCACCAGTAACC</td><td align="left" valign="top" rowspan="1" colspan="1">TCCCTCTTTGCGTTTGGACTA</td><td align="left" valign="top" rowspan="1" colspan="1">262</td><td align="left" valign="top" rowspan="1" colspan="1">[<xref rid="R54" ref-type="bibr">54</xref>]</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">Cat NM_012520</td><td align="left" valign="top" rowspan="1" colspan="1">ACAACTCCCAGAAGCCTAAGAATG</td><td align="left" valign="top" rowspan="1" colspan="1">GCTTTTCCCTTGGCAGCTATG</td><td align="left" valign="top" rowspan="1" colspan="1">76</td><td align="left" valign="top" rowspan="1" colspan="1">[<xref rid="R52" ref-type="bibr">52</xref>]</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">Sod2 NM_017051</td><td align="left" valign="top" rowspan="1" colspan="1">CGAGCATGGGTTCCATGTC</td><td align="left" valign="top" rowspan="1" colspan="1">CTGGACCGCCATGTTTCTTAG</td><td align="left" valign="top" rowspan="1" colspan="1">100</td><td align="left" valign="top" rowspan="1" colspan="1">[<xref rid="R52" ref-type="bibr">52</xref>]</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">Tbxa2r NM_017054.1</td><td align="left" valign="top" rowspan="1" colspan="1">ATCTCCCATCTTGCCATAGTCC</td><td align="left" valign="top" rowspan="1" colspan="1">CCGATGATCCTTGAGCCTAAAG</td><td align="left" valign="top" rowspan="1" colspan="1">1880</td><td align="left" valign="top" rowspan="1" colspan="1">[<xref rid="R55" ref-type="bibr">55</xref>]</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">Ptgis NM_031557</td><td align="left" valign="top" rowspan="1" colspan="1">TGGTGTGGGATCTGCGTACA</td><td align="left" valign="top" rowspan="1" colspan="1">CCTCCACTCCATACAGGGTCA</td><td align="left" valign="top" rowspan="1" colspan="1">567</td><td align="left" valign="top" rowspan="1" colspan="1">[<xref rid="R56" ref-type="bibr">56</xref>]</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">Ptgir NM_001077644</td><td align="left" valign="top" rowspan="1" colspan="1">TGCTGGAACATCACCTACGT</td><td align="left" valign="top" rowspan="1" colspan="1">GTTTCGAGCATAGGCCACAA</td><td align="left" valign="top" rowspan="1" colspan="1">422</td><td align="left" valign="top" rowspan="1" colspan="1">[<xref rid="R56" ref-type="bibr">56</xref>]</td></tr></tbody></table><table-wrap-foot><fn id="TFN1"><p id="P60">Primers were used in placental junctional zone, labyrinth zone, fetal liver, fetal lung, implantation site, and resorption site tissue.</p></fn></table-wrap-foot></table-wrap><table-wrap position="float" id="T2" orientation="landscape"><label>Table 2</label><caption><p id="P61">mRNA Expression profiles for prostacyclin synthase (PGIS) and receptor (PGIR), thromboxane receptor (TXR), superoxide dismutase (SOD), catalase (CAT), and estrogen receptors (ER&#x003b1; or ER&#x003b2;) or in placental tissue, JZ and LZ.</p></caption><table frame="hsides" rules="none"><colgroup span="1"><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/></colgroup><thead><tr><th align="left" valign="top" rowspan="1" colspan="1">Tissue</th><th align="left" valign="top" rowspan="1" colspan="1">Group</th><th align="left" valign="top" rowspan="1" colspan="1">N</th><th align="left" valign="top" rowspan="1" colspan="1">Prostacyclin Synthase</th><th align="left" valign="top" rowspan="1" colspan="1">Prostacyclin Receptor</th><th align="left" valign="top" rowspan="1" colspan="1">Thromboxane Receptor</th><th align="left" valign="top" rowspan="1" colspan="1">Superoxide Dismutase</th><th align="left" valign="top" rowspan="1" colspan="1">Catalase</th><th align="left" valign="top" rowspan="1" colspan="1">ER&#x003b1;</th><th align="left" valign="top" rowspan="1" colspan="1">ER&#x003b2;</th></tr><tr><th align="left" valign="top" colspan="10" rowspan="1">
<hr/>
</th></tr></thead><tbody><tr><td align="left" valign="top" rowspan="1" colspan="1">Junctional zone</td><td align="left" valign="top" rowspan="1" colspan="1">Sham-control Male</td><td align="left" valign="top" rowspan="1" colspan="1">3&#x02013;5</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.19</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.32</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.21</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.17</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.18</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.73</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.96</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1"/><td align="left" valign="top" rowspan="1" colspan="1">Nano-TiO<sub>2</sub> Male</td><td align="left" valign="top" rowspan="1" colspan="1">3&#x02013;5</td><td align="left" valign="top" rowspan="1" colspan="1">0.68 &#x000b1; 0.22</td><td align="left" valign="top" rowspan="1" colspan="1">0.80 &#x000b1; 0.18</td><td align="left" valign="top" rowspan="1" colspan="1">1.13 &#x000b1; 0.31</td><td align="left" valign="top" rowspan="1" colspan="1">0.89 &#x000b1; 0.09</td><td align="left" valign="top" rowspan="1" colspan="1">1.46 &#x000b1; 0.12</td><td align="left" valign="top" rowspan="1" colspan="1">0.59 &#x000b1; 0.20</td><td align="left" valign="top" rowspan="1" colspan="1">1.36 &#x000b1; 1.10</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1"/><td align="left" valign="top" rowspan="1" colspan="1">Sham-control Female</td><td align="left" valign="top" rowspan="1" colspan="1">3&#x02013;5</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.33</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.26</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.29</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.09</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.21</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.54</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.15</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1"/><td align="left" valign="top" rowspan="1" colspan="1">Nano-TiO<sub>2</sub> Female</td><td align="left" valign="top" rowspan="1" colspan="1">3&#x02013;5</td><td align="left" valign="top" rowspan="1" colspan="1">0.58 &#x000b1; 0.12</td><td align="left" valign="top" rowspan="1" colspan="1"><bold>2.32 &#x000b1; 0.37</bold>
<xref rid="TFN3" ref-type="table-fn">a</xref><xref rid="TFN4" ref-type="table-fn">b</xref></td><td align="left" valign="top" rowspan="1" colspan="1">1.54 &#x000b1; 0.23</td><td align="left" valign="top" rowspan="1" colspan="1">0.85 &#x000b1; 0.03</td><td align="left" valign="top" rowspan="1" colspan="1"><bold>0.79 &#x000b1; 0.09</bold>
<xref rid="TFN4" ref-type="table-fn">b</xref></td><td align="left" valign="top" rowspan="1" colspan="1">1.21 &#x000b1; 0.42</td><td align="left" valign="top" rowspan="1" colspan="1">3.07 &#x000b1; 0.08</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">Labyrinth zone</td><td align="left" valign="top" rowspan="1" colspan="1">Sham-control Male</td><td align="left" valign="top" rowspan="1" colspan="1">3</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 1.40</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.42</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.83</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.27</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.21</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.62</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 8.56</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1"/><td align="left" valign="top" rowspan="1" colspan="1">Nano-TiO<sub>2</sub> Male</td><td align="left" valign="top" rowspan="1" colspan="1">3</td><td align="left" valign="top" rowspan="1" colspan="1">0.64 &#x000b1; 0.72</td><td align="left" valign="top" rowspan="1" colspan="1">0.76 &#x000b1; 0.18</td><td align="left" valign="top" rowspan="1" colspan="1">1.46 &#x000b1; 0.31</td><td align="left" valign="top" rowspan="1" colspan="1">1.03 &#x000b1; 0.27</td><td align="left" valign="top" rowspan="1" colspan="1">1.16 &#x000b1; 0.30</td><td align="left" valign="top" rowspan="1" colspan="1">1.55 &#x000b1; 1.02</td><td align="left" valign="top" rowspan="1" colspan="1">0.22 &#x000b1; 1.34</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1"/><td align="left" valign="top" rowspan="1" colspan="1">Sham-control Female</td><td align="left" valign="top" rowspan="1" colspan="1">3</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.28</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.08</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.18</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.13</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.17</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.29</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.18</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1"/><td align="left" valign="top" rowspan="1" colspan="1">Nano-TiO<sub>2</sub> Female</td><td align="left" valign="top" rowspan="1" colspan="1">3</td><td align="left" valign="top" rowspan="1" colspan="1">2.92 &#x000b1; 1.74</td><td align="left" valign="top" rowspan="1" colspan="1">1.27 &#x000b1; 0.22</td><td align="left" valign="top" rowspan="1" colspan="1">0.89 &#x000b1; 0.04</td><td align="left" valign="top" rowspan="1" colspan="1">1.55 &#x000b1; 0.05</td><td align="left" valign="top" rowspan="1" colspan="1">1.52 &#x000b1; 0.19</td><td align="left" valign="top" rowspan="1" colspan="1">1.55 &#x000b1; 0.88</td><td align="left" valign="top" rowspan="1" colspan="1">2.38 &#x000b1; 1.34</td></tr></tbody></table><table-wrap-foot><fn id="TFN2"><p id="P62"><italic toggle="yes">N</italic> represents the number of litters per group. Data are fold-change and represent mean &#x000b1; SEM. JZ TXR, PGIS, SOD, ER&#x003b1;, and ER&#x003b2; do not have significance for exposure, sex, or an interaction effect (<italic toggle="yes">p</italic> &#x0003e; 0.05). JZ PGIR has a trend to an exposure effect (<italic toggle="yes">p</italic> = 0.074), a sex effect (<italic toggle="yes">p</italic> = 0.019), and an interaction (<italic toggle="yes">p</italic> = 0.019). JZ CAT does not have an exposure effect (<italic toggle="yes">p</italic> &#x0003e; 0.05), a trend for a sex effect (<italic toggle="yes">p</italic> = 0.053), and an interaction (<italic toggle="yes">p</italic> = 0.053). LZ SOD, TXR, PGIS, PGIR, CAT, ER&#x003b1;, or ER&#x003b2; did not have an exposure, sex, or interaction effect (<italic toggle="yes">p</italic> &#x0003e; 0.05).</p></fn><fn id="TFN3"><label>a</label><p id="P63"><italic toggle="yes">p</italic> &#x02264; 0.05 vs sham-control female.</p></fn><fn id="TFN4"><label>b</label><p id="P64"><italic toggle="yes">p</italic> &#x02264; 0.05 vs nano-TiO<sub>2</sub> male.</p></fn></table-wrap-foot></table-wrap><table-wrap position="float" id="T3" orientation="landscape"><label>Table 3</label><caption><p id="P65">mRNA Expression for prostacyclin synthase (PGIS) and receptor (PGIR) and thromboxane receptor (TXR).</p></caption><table frame="hsides" rules="none"><colgroup span="1"><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/></colgroup><thead><tr><th align="left" valign="top" rowspan="1" colspan="1">Tissue</th><th align="left" valign="top" rowspan="1" colspan="1">Exposure/Group</th><th align="left" valign="top" rowspan="1" colspan="1">N</th><th align="left" valign="top" rowspan="1" colspan="1">Prostacyclin Synthase</th><th align="left" valign="top" rowspan="1" colspan="1">Prostacyclin Receptor</th><th align="left" valign="top" rowspan="1" colspan="1">Thromboxane Receptor</th></tr><tr><th align="left" valign="top" colspan="6" rowspan="1">
<hr/>
</th></tr></thead><tbody><tr><td align="left" valign="top" rowspan="1" colspan="1">Lung</td><td align="left" valign="top" rowspan="1" colspan="1">Sham-control Male</td><td align="left" valign="top" rowspan="1" colspan="1">5</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.08</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.23</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.11</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1"/><td align="left" valign="top" rowspan="1" colspan="1">Nano-TiO<sub>2</sub> Male</td><td align="left" valign="top" rowspan="1" colspan="1">5</td><td align="left" valign="top" rowspan="1" colspan="1">0.94 &#x000b1; 0.33</td><td align="left" valign="top" rowspan="1" colspan="1">0.73 &#x000b1; 0.21</td><td align="left" valign="top" rowspan="1" colspan="1">0.42 &#x000b1; 0.09</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1"/><td align="left" valign="top" rowspan="1" colspan="1">Sham-control Female</td><td align="left" valign="top" rowspan="1" colspan="1">5</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.26</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.22</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.29</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1"/><td align="left" valign="top" rowspan="1" colspan="1">Nano-TiO<sub>2</sub> Female</td><td align="left" valign="top" rowspan="1" colspan="1">5</td><td align="left" valign="top" rowspan="1" colspan="1">0.99 &#x000b1; 0.07</td><td align="left" valign="top" rowspan="1" colspan="1">1.16 &#x000b1; 0.26</td><td align="left" valign="top" rowspan="1" colspan="1">0.87 &#x000b1; 0.15</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1">Implantation site</td><td align="left" valign="top" rowspan="1" colspan="1">Sham-control Male</td><td align="left" valign="top" rowspan="1" colspan="1">3</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.15</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.18</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.17</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1"/><td align="left" valign="top" rowspan="1" colspan="1">Nano-TiO<sub>2</sub> Male</td><td align="left" valign="top" rowspan="1" colspan="1">3</td><td align="left" valign="top" rowspan="1" colspan="1">1.85 &#x000b1; 0.44</td><td align="left" valign="top" rowspan="1" colspan="1">1.05 &#x000b1; 0.35</td><td align="left" valign="top" rowspan="1" colspan="1">1.25 &#x000b1; 0.31</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1"/><td align="left" valign="top" rowspan="1" colspan="1">Sham-control Female</td><td align="left" valign="top" rowspan="1" colspan="1">3</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.92</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.05</td><td align="left" valign="top" rowspan="1" colspan="1">1.00 &#x000b1; 0.16</td></tr><tr><td align="left" valign="top" rowspan="1" colspan="1"/><td align="left" valign="top" rowspan="1" colspan="1">Nano-TiO<sub>2</sub> Female</td><td align="left" valign="top" rowspan="1" colspan="1">3</td><td align="left" valign="top" rowspan="1" colspan="1"><bold>5.78 &#x000b1; 1.27</bold>
<xref rid="TFN6" ref-type="table-fn">a</xref><xref rid="TFN7" ref-type="table-fn">b</xref></td><td align="left" valign="top" rowspan="1" colspan="1">1.23 &#x000b1; 0.40</td><td align="left" valign="top" rowspan="1" colspan="1">1.48 &#x000b1; 1.06</td></tr></tbody></table><table-wrap-foot><fn id="TFN5"><p id="P66"><italic toggle="yes">N</italic> represents the number of litters per group. Data are fold-change and represent mean &#x000b1; SEM. Fetal lung PGIR and PGIS did not have significance for exposure, sex, or an interaction effect (<italic toggle="yes">p</italic> &#x0003e; 0.05). Fetal lung TXR had a trend toward significance (<italic toggle="yes">p</italic> = 0.060) for exposure effect but did not have significance for sex or an interaction effect (<italic toggle="yes">p</italic> &#x0003e; 0.05). Implantation sites TXR or PGIR did not have an exposure, sex, or interaction effects (<italic toggle="yes">p</italic> &#x0003e; 0.05). Implantation site PGIS had an exposure effect (<italic toggle="yes">p</italic> = 0.009), a sex effect (<italic toggle="yes">p</italic> = 0.043), and an interaction (<italic toggle="yes">p</italic> = 0.043) effect.</p></fn><fn id="TFN6"><label>a</label><p id="P67"><italic toggle="yes">p</italic> &#x02264; 0.05 vs sham-control female.</p></fn><fn id="TFN7"><label>b</label><p id="P68"><italic toggle="yes">p</italic> &#x02264; 0.05 vs nano-TiO<sub>2</sub> male.</p></fn><fn id="TFN8"><label>c</label><p id="P69"><italic toggle="yes">p</italic> &#x02264; 0.05 vs sham-control male.</p></fn></table-wrap-foot></table-wrap></floats-group></article>