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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Vet. Sci.</journal-id>
<journal-title-group>
<journal-title>Frontiers in Veterinary Science</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Vet. Sci.</abbrev-journal-title>
</journal-title-group>
<issn pub-type="epub">2297-1769</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fvets.2026.1771581</article-id>
<article-version article-version-type="Version of Record" vocab="NISO-RP-8-2008"/>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Original Research</subject>
</subj-group>
</article-categories>
<title-group>
<article-title><italic>In vitro</italic> exposure to polystyrene microplastics exerts oocyte toxicity through cumulus cells damage in the sheep model</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Temerario</surname>
<given-names>Letizia</given-names>
</name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="corresp" rid="c001"><sup>&#x002A;</sup></xref>
<uri xlink:href="https://loop.frontiersin.org/people/3320122"/>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Podda</surname>
<given-names>Andrea</given-names>
</name>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Bogliolo</surname>
<given-names>Luisa</given-names>
</name>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Mastrorocco</surname>
<given-names>Antonella</given-names>
</name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref rid="fn00010" ref-type="author-notes"><sup>&#x2020;</sup></xref>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Ferrante</surname>
<given-names>Maria Carmela</given-names>
</name>
<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Pinto</surname>
<given-names>Pierfrancesco</given-names>
</name>
<xref ref-type="aff" rid="aff4"><sup>4</sup></xref>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Dell&#x2019;Aquila</surname>
<given-names>Maria Elena</given-names>
</name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Martino</surname>
<given-names>Nicola Antonio</given-names>
</name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
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</contrib-group>
<aff id="aff1"><label>1</label><institution>Department of Biosciences, Biotechnology and Environment, University of Bari Aldo Moro</institution>, <city>Bari</city>, <country country="it">Italy</country></aff>
<aff id="aff2"><label>2</label><institution>Department of Veterinary Medicine, University of Sassari</institution>, <city>Sassari</city>, <country country="it">Italy</country></aff>
<aff id="aff3"><label>3</label><institution>Department of Veterinary Medicine and Animal Productions, University of Naples Federico II</institution>, <city>Naples</city>, <country country="it">Italy</country></aff>
<aff id="aff4"><label>4</label><institution>Prevention Department of ASL BA, Animal Origin Food Hygiene Service</institution>, <city>Bari</city>, <country country="it">Italy</country></aff>
<author-notes>
<corresp id="c001"><label>&#x002A;</label>Correspondence: Letizia Temerario, <email xlink:href="mailto:letizia.temerario@uniba.it">letizia.temerario@uniba.it</email></corresp>
<fn id="fn00010" fn-type="present-address"><p><sup>&#x2020;</sup>Present address: Antonella Mastrorocco,Bambino Ges&#x00F9; Children&#x2019;s Hospital, IRCCS, Rome, Italy</p></fn>
</author-notes>
<pub-date publication-format="electronic" date-type="pub" iso-8601-date="2026-03-02">
<day>02</day>
<month>03</month>
<year>2026</year>
</pub-date>
<pub-date publication-format="electronic" date-type="collection">
<year>2026</year>
</pub-date>
<volume>13</volume>
<elocation-id>1771581</elocation-id>
<history>
<date date-type="received">
<day>19</day>
<month>12</month>
<year>2025</year>
</date>
<date date-type="rev-recd">
<day>29</day>
<month>01</month>
<year>2026</year>
</date>
<date date-type="accepted">
<day>12</day>
<month>02</month>
<year>2026</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x00A9; 2026 Temerario, Podda, Bogliolo, Mastrorocco, Ferrante, Pinto, Dell&#x2019;Aquila and Martino.</copyright-statement>
<copyright-year>2026</copyright-year>
<copyright-holder>Temerario, Podda, Bogliolo, Mastrorocco, Ferrante, Pinto, Dell&#x2019;Aquila and Martino</copyright-holder>
<license>
<ali:license_ref start_date="2026-03-02">https://creativecommons.org/licenses/by/4.0/</ali:license_ref>
<license-p>This is an open-access article distributed under the terms of the <ext-link ext-link-type="uri" xlink:href="https://creativecommons.org/licenses/by/4.0/">Creative Commons Attribution License (CC BY)</ext-link>. 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 terms.</license-p>
</license>
</permissions>
<abstract>
<sec>
<title>Introduction</title>
<p>In recent years, the widespread environmental presence of microplastics (MPs) has raised major concerns regarding animal and human health, including potential risks to reproductive function and offspring.</p>
</sec>
<sec>
<title>Methods</title>
<p>This study aimed to evaluate the effects of increasing concentrations of polystyrene MPs (PS-MPs; 0, 5, 50, or 100&#x202F;&#x03BC;g/mL) on ovine cumulus&#x2013;oocyte complexes (COCs) during <italic>in vitro</italic> maturation (IVM). Fluorescent microspheres were used for uptake assessment into COCs and cumulus cells (CCs) monolayers, whereas non-fluorescent PS-MPs were employed to evaluate potential toxic effects induced on CCs and oocytes.</p>
</sec>
<sec>
<title>Results</title>
<p>As regards CCs, increased PS-MPs uptake was highlighted at the highest exposure concentration (100&#x202F;&#x03BC;g/mL), whereas no significant differences were observed in oocyte intracellular fluorescence intensity, compared to the control. The bioaccumulation increment in CCs monolayers was already visible after 6&#x202F;h, both at 5 and 100&#x202F;&#x03BC;g/mL, and confirmed at 24&#x202F;h. The real-time PCR analysis in CCs revealed significant reductions in the expression levels of genes involved in antioxidant defense and alterations in those implicated in apoptosis. Finally, the TUNEL assay revealed a dose-dependent increase in CCs apoptotic index. Consequently, PS-MPs exposure impaired oocyte meiosis resumption by significantly reducing the maturation rates, particularly at 50 and 100&#x202F;&#x03BC;g/mL, whereas no effects were observed at 5&#x202F;&#x03BC;g/mL. Oocyte intracellular reactive oxygen species levels were significantly increased at all concentrations, whereas no differences in mitochondrial membrane potential were detected. The percentages of oocytes with abnormal configurations of meiotic spindle and cortical F-actin were found to be significantly increased, regardless of concentration. Finally, the cleavage rate was significantly reduced in oocytes exposed to 50&#x202F;&#x03BC;g/mL, whereas no differences were found in the blastocyst rate at both 50 and 5&#x202F;&#x03BC;g/mL.</p>
</sec>
<sec>
<title>Discussion</title>
<p>In conclusion, <italic>in vitro</italic> exposure of sheep COCs to PS-MPs during IVM reduced oocyte quality and developmental potential through alterations induced in the CCs, which turned out to be the main target of these environmental contaminants.</p>
</sec>
</abstract>
<kwd-group>
<kwd>microplastics</kwd>
<kwd>oocyte</kwd>
<kwd><italic>in vitro</italic> maturation</kwd>
<kwd>embryo</kwd>
<kwd>gene expression</kwd>
<kwd>apoptosis</kwd>
<kwd>oxidative stress</kwd>
<kwd>cytoskeleton</kwd>
</kwd-group>
<funding-group>
<funding-statement>The author(s) declared that financial support was received for this work and/or its publication. This research was funded by the Italian Ministry of University and Research, research program: Inv. M4. C2.1.1 PNRR (grant number: 2022WEPMKX), &#x201C;Effects of combined exposure to nano/microplastics and plastic additives on mammalian female fertility.&#x201D;</funding-statement>
</funding-group>
<counts>
<fig-count count="6"/>
<table-count count="3"/>
<equation-count count="0"/>
<ref-count count="50"/>
<page-count count="12"/>
<word-count count="9332"/>
</counts>
<custom-meta-group>
<custom-meta>
<meta-name>section-at-acceptance</meta-name>
<meta-value>Animal Reproduction - Theriogenology</meta-value>
</custom-meta>
</custom-meta-group>
</article-meta>
</front>
<body>
<sec sec-type="intro" id="sec1">
<label>1</label>
<title>Introduction</title>
<p>Currently, there is growing recognition of the role that environmental pollutants exert in declining human and animal fertility (<xref ref-type="bibr" rid="ref1 ref2 ref3 ref4 ref5 ref6 ref7 ref8">1&#x2013;8</xref>). Among them, plastic waste represents an escalating global health issue due to the increasing accumulation of small plastic particles, known as micro- and nano-plastics (MPs and NPs), in all environmental compartments, including water, soil, atmosphere, and food chains (<xref ref-type="bibr" rid="ref1">1</xref>, <xref ref-type="bibr" rid="ref9 ref10 ref11 ref12 ref13 ref14">9&#x2013;14</xref>). Plastic pollution primarily originates from industrial and agricultural anthropic activities, inadequate waste management, environmental calamities, and finally the common use of littering of single-use plastics, packaging, and food waste (<xref ref-type="bibr" rid="ref1">1</xref>, <xref ref-type="bibr" rid="ref9 ref10 ref11 ref12 ref13 ref14">9&#x2013;14</xref>). Once released into the environment, plastic undergoes degradation through physical, chemical, and biological processes (<xref ref-type="bibr" rid="ref15">15</xref>), thus leading to the breakdown of larger plastic debris into MPs, ranging from 100&#x202F;nm to 5&#x202F;mm in diameter, and NPs between 1 and 100&#x202F;nm (<xref ref-type="bibr" rid="ref1">1</xref>, <xref ref-type="bibr" rid="ref10 ref11 ref12 ref13 ref14">10&#x2013;14</xref>, <xref ref-type="bibr" rid="ref16">16</xref>, <xref ref-type="bibr" rid="ref17">17</xref>). Physically, these particles vary in size, color, and shape, ranging from fragments, foams, and beads to fibers, films, and flakes (<xref ref-type="bibr" rid="ref1">1</xref>, <xref ref-type="bibr" rid="ref10 ref11 ref12 ref13 ref14">10&#x2013;14</xref>). Chemically, their composition is variable and can include materials such as polystyrene (PS), polyethylene (PE), polypropylene (PP), polyvinyl chloride (PVC), and polyethylene terephthalate (PET) (<xref ref-type="bibr" rid="ref1">1</xref>, <xref ref-type="bibr" rid="ref10 ref11 ref12 ref13 ref14">10&#x2013;14</xref>). Moreover, the presence of toxic metals or plastic additives, adhering to their surfaces, can additionally influence the properties and effects of these particles (<xref ref-type="bibr" rid="ref1">1</xref>, <xref ref-type="bibr" rid="ref11">11</xref>).</p>
<p>Animals and humans can be exposed to MPs and NPs through multiple pathways, including ingestion, inhalation, and dermal contact (<xref ref-type="bibr" rid="ref1">1</xref>, <xref ref-type="bibr" rid="ref10 ref11 ref12 ref13 ref14">10&#x2013;14</xref>). Exposure to these particles poses several potential health risks, including those on reproductive function and offspring, exerted through multiple mechanisms, such as oxidative stress, inflammation, and apoptosis (<xref ref-type="bibr" rid="ref18">18</xref>). MPs and NPs are able to pass through the blood&#x2013;follicle barrier and to potentially penetrate the oocyte through gap junctions or cross the zona pellucida, resulting in impairment of oocyte maturation, fertilization, and embryo development (<xref ref-type="bibr" rid="ref1">1</xref>, <xref ref-type="bibr" rid="ref10">10</xref>, <xref ref-type="bibr" rid="ref13">13</xref>, <xref ref-type="bibr" rid="ref14">14</xref>, <xref ref-type="bibr" rid="ref18">18</xref>). Moreover, these particles are known to induce apoptosis of granulosa cells, reduce ovarian follicle reserve, and accumulate in the ovary and uterus with subsequent fibrosis (<xref ref-type="bibr" rid="ref1">1</xref>, <xref ref-type="bibr" rid="ref10">10</xref>, <xref ref-type="bibr" rid="ref13">13</xref>, <xref ref-type="bibr" rid="ref14">14</xref>). It has also been reported that MPs can intensify the toxic effect of environmental pollutants or endocrine disruptors on reproduction (<xref ref-type="bibr" rid="ref19">19</xref>). In addition, potential carry-over effects on the next generation are reported due to the ability of MPs and NPs to pass through the blood&#x2013;placenta barrier (<xref ref-type="bibr" rid="ref1">1</xref>, <xref ref-type="bibr" rid="ref12 ref13 ref14">12&#x2013;14</xref>).</p>
<p>Current knowledge on the potential effects of MPs and NPs mainly derives from studies on aquatic and terrestrial species of vertebrates and invertebrates (<xref ref-type="bibr" rid="ref1">1</xref>, <xref ref-type="bibr" rid="ref20 ref21 ref22">20&#x2013;22</xref>) and, more recently, from rodents (<xref ref-type="bibr" rid="ref1">1</xref>). On the contrary, research in farm animals is limited up to now, although their exposure is documented and they represent interesting translational models for human reproduction (<xref ref-type="bibr" rid="ref1">1</xref>, <xref ref-type="bibr" rid="ref13">13</xref>, <xref ref-type="bibr" rid="ref14">14</xref>). In particular, among them, the sheep has become a valuable experimental model due to the similarities with human ovarian structure, oocyte size, and follicle development dynamics. Specifically, oocytes retrieved from juvenile animals, representing a widely available source of biological material due to lamb meat consumption, are interesting for research in the pediatric age (<xref ref-type="bibr" rid="ref23">23</xref>).</p>
<p>This study aimed to evaluate the effects of PS-MPs on ovine cumulus&#x2013;oocyte complexes (COCs), exposed during <italic>in vitro</italic> maturation (IVM), by assessing uptake into COC and cumulus cell (CC) monolayers, CC&#x2019;s quantitative gene expression and apoptotic index, and oocyte maturation and developmental competence.</p>
</sec>
<sec sec-type="materials|methods" id="sec2">
<label>2</label>
<title>Materials and methods</title>
<p>The experimental design flowchart is presented in <xref ref-type="fig" rid="fig1">Figure 1</xref>.</p>
<fig position="float" id="fig1">
<label>Figure 1</label>
<caption>
<p>Experimental design flowchart. In the present study, the effects of exposure to polystyrene microplastics (PS-MPs) during <italic>in vitro</italic> maturation (IVM) on sheep cumulus&#x2013;oocyte complexes (COCs) were evaluated through uptake assessment into COCs and cumulus cells (CCs) monolayers <bold>(A)</bold>, CCs quantitative gene expression and apoptotic index <bold>(B)</bold>, and oocyte maturation and developmental competence <bold>(C)</bold>.</p>
</caption>
<graphic xlink:href="fvets-13-1771581-g001.tif" mimetype="image" mime-subtype="tiff">
<alt-text content-type="machine-generated">Diagram outlining experimental design for studying microplastic (MP) uptake and toxicity in sheep cumulus-oocyte complexes and cells, detailing concentrations, incubation periods, toxicological endpoints, and cellular or developmental outcomes for both cumulus cells and oocytes.</alt-text>
</graphic>
</fig>
<sec id="sec3">
<label>2.1</label>
<title>Chemicals</title>
<p>All chemicals were purchased from Sigma-Aldrich (Milan, Italy), unless otherwise indicated.</p>
</sec>
<sec id="sec4">
<label>2.2</label>
<title>Collection of ovaries and retrieval of cumulus&#x2013;oocyte complexes (COCs)</title>
<p>Ovaries were collected at a local slaughterhouse (Surace Carne s.r.l., Noci, Bari) from prepubertal lambs (&#x003C;3&#x202F;months of age) subjected to routine veterinary inspection and transported to the laboratory at room temperature within 2&#x2013;4&#x202F;h from slaughter. The lamb&#x2019;s prepubertal status was later confirmed at the ovarian level, in the laboratory, by evaluating the absence of growing follicles and corpora lutea. For the retrieval of COCs, the slicing technique was employed. The follicular contents were released into 60-mm sterile Petri dishes containing phosphate-buffered saline (PBS). COCs were selected using a Nikon SMZ 1500 optical stereomicroscope (Nikon Instruments, Firenze, Italy). Only those exhibiting at least three intact layers of CCs and homogeneous cytoplasm were selected for <italic>in vitro</italic> culture (<xref ref-type="bibr" rid="ref24">24</xref>).</p>
</sec>
<sec id="sec5">
<label>2.3</label>
<title>COC exposure to polystyrene microplastics (PS-MPs) and <italic>in vitro</italic> maturation (IVM)</title>
<p>To evaluate the effects of PS-MPs on COC uptake and oocyte IVM, specific culture medium solutions were prepared by incorporating commercially available PS beads (Bangs Laboratories Inc., Fishers, IN, USA) at several concentrations. Fluorescent microspheres conjugated with Flash Red (200&#x202F;nm diameter) were used for uptake assessment, while those not conjugated to the fluorophore (100&#x202F;nm diameter) were employed to assess oocyte and CCs toxicity. IVM medium was prepared, as previously described (<xref ref-type="bibr" rid="ref24">24</xref>), based on TCM-199 medium with Earle&#x2019;s salts, buffered with 5.87&#x202F;mmol/L HEPES and 33.09&#x202F;mmol/L sodium bicarbonate and supplemented with 0.1&#x202F;g/L&#x202F;L-glutamine, 2.27&#x202F;mmol/L sodium pyruvate, calcium lactate pentahydrate (1.62&#x202F;mmol/L Ca<sup>2+</sup>, 3.9&#x202F;mmol/L lactate), 50&#x202F;&#x03BC;g/mL gentamicin, 20% (v/v) fetal calf serum (FCS), 10&#x202F;&#x03BC;g/mL of porcine follicle-stimulating hormone and luteinizing hormone (FSH/LH; Pluset<sup>&#x00AE;</sup>, Calier, Barcelona, Spain) and 1&#x202F;&#x03BC;g/mL 17-<italic>&#x03B2;</italic>-estradiol. On the day of experiments, PS-MPs stock solutions were diluted with IVM medium to cover a concentration range from 5 to 100&#x202F;&#x03BC;g/mL, according to the experimental design. IVM medium without PS-MPs was used as a control. For each set of experiments, groups of 20&#x2013;25 selected COCs were placed in four-well dishes (Nunc Intermed, Roskilde, Denmark) containing 400&#x202F;&#x03BC;L of IVM, supplemented or not with PS-MPs, covered with an equal volume of pre-equilibrated lightweight mineral oil per well. IVM culture was performed for 22&#x2013;24&#x202F;h at 38.5&#x202F;&#x00B0;C with 5% CO<sub>2</sub> in a humidified incubator (<xref ref-type="bibr" rid="ref24">24</xref>).</p>
</sec>
<sec id="sec6">
<label>2.4</label>
<title>Exposure of CCs cultured in a single layer to PS-MPs</title>
<p>Considering the functions of CCs in COCs, the effects of exposure to PS-MPs were verified over time. Specifically, the bioaccumulation of fluorescent PS-MPs in the CCs after 6 and 24&#x202F;h of incubation was evaluated in the same experimental conditions previously described for COCs. Recovered CCs were centrifuged at 300&#x202F;<italic>g</italic> for 5&#x202F;min, the supernatant was aspirated, and the pellet was resuspended in 100&#x202F;&#x03BC;L of PBS. Meanwhile, 10 slides were prepared, coverslipped inside 2 plates with 35-mm diameter wells. Subsequently, CCs were adhered onto the slides, and Dulbecco&#x2019;s Modified Eagle Medium (DMEM) culture medium, implemented with 20% (v/v) FCS, with or without PS-MPs, was added.</p>
</sec>
<sec id="sec7">
<label>2.5</label>
<title>Assessment of fluorescent PS-MPs uptake</title>
<p>After IVM, COCs were washed in PBS and fixed in 4% paraformaldehyde (PFA) solution in PBS. Subsequently, COCs were washed a second time in PBS, mounted on slides in a drop of glycerol&#x2013;PBS solution with a ratio of 3:1 (v/v), covered with cover slips, and sealed with nail polish. Finally, the slides were stored at 4&#x202F;&#x00B0;C in the dark. To evaluate the uptake of fluorescent PS-MPs, COCs and CCs monolayers were observed under a Nikon C1/TE2000-U confocal laser scanning microscope (Nikon Instruments, Firenze, Italy) at 600x magnification under oil immersion. To detect Flash Red fluorescence, a 633-nm helium/neon laser beam and an LP-650 filter were used. The fluorescence intensities were measured on the equatorial plane, with the aid of the EZ-CI GoldVersion 3.70 image analysis software platform for the Nikon CI confocal microscope (Nikon Instruments, Firenze, Italy). A circular area was traced to delineate the cytoplasmic area of the oocytes, whereas a polygonal area was traced by dividing CCs into sectors. Instead, for the fluorescence intensity of the CCs plated in a monolayer, a polygonal area was traced for each CC of the group present in the framed field. The fluorescence intensity within the programmed scanning area (512 &#x00D7; 512 pixels) was recorded and expressed as arbitrary densitometric units (ADU). The evaluations of all samples were carried out under fixed scanning conditions with regard to laser energy, signal detection (gain), and pinhole size.</p>
</sec>
<sec id="sec8">
<label>2.6</label>
<title>RNA extraction from CCs and quantitative real-time PCR</title>
<p>After IVM, COCs underwent a denuding procedure through the enzymatic action of hyaluronidase and mechanical pipetting of a Gilson pipette. Collected CCs were centrifuged at 400&#x202F;<italic>g</italic> for 5&#x202F;min at room temperature, and the resulting pellet was immediately stored at &#x2212;80&#x202F;&#x00B0;C. Total RNA extraction was performed using the Rneasy<sup>&#x00AE;</sup> Plus Micro Kit (Qiagen, Hilden, Germany), following the manufacturer&#x2019;s instructions (<xref ref-type="bibr" rid="ref25">25</xref>). Single-stranded complementary DNA (cDNA) was synthesized by using the High-Capacity cDNA Reverse Transcription Kit (Applied Biosystems, Foster City, CA, USA) in a thermal cycler (Eppendorf, Hamburg, Germany) according to the following thermal program: (1) primers annealing at 25&#x202F;&#x00B0;C for 10&#x202F;min, (2) DNA polymerization at 37&#x202F;&#x00B0;C for 120&#x202F;min, and (3) enzyme deactivation at 85&#x202F;&#x00B0;C for 5&#x202F;min. Real-time PCR was used to perform gene expression analysis. For each sample, the reaction mix (20&#x202F;&#x03BC;L) contained: 11&#x202F;&#x03BC;L SYBR Green PCR Master Mix powerup (Applied Biosystems, 2x), 1&#x202F;&#x03BC;L forward primer (<xref ref-type="table" rid="tab1">Table 1</xref>), 1&#x202F;&#x03BC;L reverse primer (<xref ref-type="table" rid="tab1">Table 1</xref>), 1&#x202F;&#x03BC;L cDNA, and RNase-free water up to the final volume. Each reaction was performed using a StepOne thermal cycler (Applied Biosystems, Foster City, CA, USA) with the following thermal cycling parameters: (1) 40&#x202F;cycles of denaturation at 95&#x202F;&#x00B0;C for 15&#x202F;s each, (2) annealing at 60&#x202F;&#x00B0;C for 1&#x202F;min, (3) extension at 60&#x202F;&#x00B0;C for 1&#x202F;min. The specificity of each primer was confirmed through melting curve analysis. Each amplification was performed in duplicate, and the relative quantification of gene expression was conducted using the 2<sup>-&#x0394;&#x0394;Ct</sup> method (Livak method) using <italic>&#x03B2;</italic>-actin as the housekeeping gene.</p>
<table-wrap position="float" id="tab1">
<label>Table 1</label>
<caption>
<p>Primer sequences validated by real-time PCR.</p>
</caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th align="left" valign="top">Symbol</th>
<th align="left" valign="top">Gene name</th>
<th align="left" valign="top">Identification number</th>
<th align="left" valign="top">Primer sequence (5&#x2032;&#x202F;&#x2192;&#x202F;3&#x2032;)</th>
<th align="center" valign="top">Annealing temperature (&#x00B0;C)</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="middle">ACTB</td>
<td align="left" valign="middle">Actin Beta</td>
<td align="left" valign="middle">NM_001009784</td>
<td align="left" valign="middle">CCCTGGAGAAGAGCTACGAG TAGTTTCGTGAATGCCGCAG</td>
<td align="center" valign="middle">59</td>
</tr>
<tr>
<td align="left" valign="middle">SOD1</td>
<td align="left" valign="middle">Superoxide dismutase 1</td>
<td align="left" valign="middle">NM_001145185</td>
<td align="left" valign="middle">GGCAATGTGAAGGCTGACAA TGCCCAAGTCATCTGGTCTT</td>
<td align="center" valign="middle">59</td>
</tr>
<tr>
<td align="left" valign="middle">CAT</td>
<td align="left" valign="middle">Catalase</td>
<td align="left" valign="middle">GQ421282</td>
<td align="left" valign="middle">ACGCCTGTGTGAGAACATTG AGCCATACTCAGGATGGACA</td>
<td align="center" valign="middle">59</td>
</tr>
<tr>
<td align="left" valign="middle">GPX</td>
<td align="left" valign="middle">Glutathione peroxidase</td>
<td align="left" valign="middle">GAAI01007125</td>
<td align="left" valign="middle">ACCCAGATGAATGACCTGCA TCGGACGTACTTCAGGCAAT</td>
<td align="center" valign="middle">59</td>
</tr>
<tr>
<td align="left" valign="middle">BCL2</td>
<td align="left" valign="middle">B cell lymphoma 2</td>
<td align="left" valign="middle">DQ15929</td>
<td align="left" valign="middle">ATGACCGAGTACCTGAACCG GGAGAAATCAAACAGGGGCC</td>
<td align="center" valign="middle">59</td>
</tr>
<tr>
<td align="left" valign="middle">BAX</td>
<td align="left" valign="middle">BCL2-associated X protein</td>
<td align="left" valign="middle">XM_004015363</td>
<td align="left" valign="middle">AAGAAGCTGAGCGAGTGTCT AAAACATTTCAGCCGCCACT</td>
<td align="center" valign="middle">59</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="sec9">
<label>2.7</label>
<title>Terminal deoxynucleotidyl transferase-mediated dUTP Nick-end labeling (TUNEL)</title>
<p>For the TUNEL assay, CCs were centrifuged at 300&#x202F;<italic>g</italic> for 5&#x202F;min, and the resulting pellet was used to assess DNA fragmentation (<xref ref-type="bibr" rid="ref26">26</xref>) using the Click-iT<sup>&#x00AE;</sup> Plus TUNEL Assay (Invitrogen, Carlsbad, CA, USA) following the manufacturer&#x2019;s instructions. Briefly, CCs were fixed in 4% PFA for 15&#x202F;min at room temperature and then permeabilized with 0.5% Triton X-100 for 20&#x202F;min. After washing with deionized water, CCs were incubated in 50&#x202F;&#x03BC;L drops of the TUNEL reagent in the dark for 1&#x202F;h at 37&#x202F;&#x00B0;C in a humidified atmosphere. The total nuclei were stained with 2.5&#x202F;&#x03BC;g/mL Hoechst 33258 in a 3:1 (v/v) glycerol/PBS solution, mounted onto microscope slides, covered with a coverslip, sealed with nail polish, and stored at 4&#x202F;&#x00B0;C in the dark. CCs were observed under a Nikon E-600 fluorescence microscope equipped with excitation filters of 365&#x202F;nm for Hoechst 33258 and 495&#x202F;nm for TUNEL staining. For each condition, approximately 15 different fields were examined to evaluate at least 100 cells in total. The apoptotic index was determined as the percentage of TUNEL-positive cells relative to the total number of cells stained with Hoechst 33258. Fluorescence quantification was performed by manually selecting the area of each TUNEL-positive cell (<xref ref-type="bibr" rid="ref27">27</xref>).</p>
</sec>
<sec id="sec10">
<label>2.8</label>
<title>Oocyte mitochondria and reactive oxygen species (ROS) staining after IVM</title>
<p>After IVM culture and COC denuding, oocytes were washed in PBS with 3% BSA and incubated for 30&#x202F;min in the same medium containing 280&#x202F;nmoL/L of MitoTracker Orange CMTM Ros (Thermo Fisher Scientific, Waltham, MA, USA) at 38.5&#x202F;&#x00B0;C under 5% CO<sub>2</sub> in air (<xref ref-type="bibr" rid="ref28">28</xref>). Then, the cells were washed in PBS with 0.3% BSA and incubated in the same medium with 10&#x202F;&#x03BC;M 2&#x2032;,7&#x2032;-dichlorodihydrofluorescein diacetate (H<sub>2</sub>DCF-DA) for 15&#x202F;min at 38.5&#x202F;&#x00B0;C under 5% CO<sub>2</sub> in air for intracellular reactive oxygen species (ROS) detection (<xref ref-type="bibr" rid="ref28">28</xref>, <xref ref-type="bibr" rid="ref29">29</xref>). After incubation, oocytes were washed in pre-warmed PBS without BSA and fixed overnight in 4% PFA at 4&#x202F;&#x00B0;C.</p>
</sec>
<sec id="sec11">
<label>2.9</label>
<title>Oocyte nuclear chromatin evaluation after IVM</title>
<p>To evaluate nuclear chromatin status, fixed oocytes in PFA were stained with 2.5&#x202F;&#x03BC;g/mL Hoechst 33258 in a 3:1 (v/v) glycerol/PBS mixture, mounted on microscope slides, and stored at 4&#x202F;&#x00B0;C in the dark. Slides were analyzed using an epifluorescence microscope (Nikon Eclipse 600; &#x00D7;400 magnification) equipped with a B-2A filter (excitation 346&#x202F;nm/emission 460&#x202F;nm). Oocytes were classified according to their meiotic stage as germinal vesicles (GV), metaphase to telophase I (MI to TI), or metaphase II (MII) with the first polar body (PB) extruded. Oocytes displaying one pronucleus with extruded PB, irregular chromatin clumps, absence of chromatin, or a multipolar meiotic spindle were categorized as abnormal (<xref ref-type="bibr" rid="ref28">28</xref>).</p>
</sec>
<sec id="sec12">
<label>2.10</label>
<title>Mitochondrial distribution pattern and intracellular ROS localization assessment</title>
<p>To detect and localize mitochondria and ROS, mature oocytes were observed using a Nikon C1/TE2000-U laser scanning confocal microscope (Nikon Instruments, Firenze, Italy) equipped with the Apo 60&#x00D7;/NA 1.40 Nikon Plan objective in oil immersion. A 543&#x202F;nm helium/neon laser and a G-2A filter were used to detect the MitoTracker Orange CMTM Ros (551&#x202F;nm excitation and 576&#x202F;nm emission). A 488-nm argon ion laser and a B-2A filter were used to detect dichlorofluorescein (DCF) (495&#x202F;nm excitation and 519&#x202F;nm emission). Oocytes were observed in 25 optical sections with a step size of 0.45&#x202F;&#x03BC;m, thus allowing 3D distribution analysis. The mitochondrial distribution pattern was evaluated as &#x201C;perinuclear and subcortical (P/S)&#x201D;, index of cytoplasmic maturity, &#x201C;finely granular&#x201D;, typical of immature oocytes and &#x201C;abnormal&#x201D;, with irregular mitochondria distribution (<xref ref-type="bibr" rid="ref24">24</xref>). Concerning intracellular ROS localization, oocytes with intracellular ROS diffused throughout the cytoplasm, together with areas/sites of mitochondria/ROS overlapping, were considered viable.</p>
</sec>
<sec id="sec13">
<label>2.11</label>
<title>Quantification of bioenergetic/oxidative parameters</title>
<p>In each individual oocyte, MitoTracker and DCF fluorescence intensities and the Manders&#x2019; overlap coefficient (<xref ref-type="bibr" rid="ref30">30</xref>), indicating the extent of mitochondria/ROS colocalization, were measured at the equatorial plane using the EZ-C1 Gold Version 3.70 image analysis software platform for a Nikon C1 confocal microscope. A circular area was drawn around the ooplasm for the quantification analysis. The fluorescence intensity within the scanned area was recorded, and 16-bit images were obtained. Mitochondrial membrane potential and intracellular ROS concentrations were recorded as the fluorescence intensity emitted by each probe and expressed as arbitrary densitometric units (ADUs). Variables related to fluorescence intensity, such as laser energy, signal detection (gain), and pinhole size, were maintained at constant values for all measurements. In the mitochondria/ROS colocalization analysis, threshold levels were kept constant at 10% of the maximum pixel intensity for all measurements.</p>
</sec>
<sec id="sec14">
<label>2.12</label>
<title>Immunofluorescence detection of cytoskeletal</title>
<p>Metaphase II (MII) oocytes were fixed for 1&#x202F;h at 37&#x202F;&#x00B0;C in a microtubule-stabilizing buffer and subsequently stored at 4&#x202F;&#x00B0;C in blocking solution (<xref ref-type="bibr" rid="ref31">31</xref>). Samples were incubated overnight at 4&#x202F;&#x00B0;C with a mixture of mouse monoclonal antibodies directed against <italic>&#x03B1;</italic>-tubulin (1:1000 dilution) and <italic>&#x03B2;</italic>-tubulin (1:100 dilution). Immunolabeling was then performed using donkey anti-mouse secondary antibodies conjugated with fluorescein isothiocyanate (FITC-Alexa Fluor 488; 1:100 dilution; Life Technologies, Invitrogen, Carlsbad, CA, USA), in combination with rhodamine&#x2013;phalloidin (1:150 dilution; Invitrogen, Carlsbad, CA, USA), for 1&#x202F;h at room temperature. Nuclear chromatin was counterstained with Hoechst 33258 (10&#x202F;&#x03BC;g/mL). Confocal imaging of meiotic spindle microtubules, chromatin organization, and cortical F-actin architecture was carried out using a laser scanning confocal microscope (Leica TCS SP5, Leica, Wetzlar, Germany) equipped with Ar/He/Ne lasers and a 40&#x202F;&#x00D7;&#x202F;oil-immersion objective. Hoechst 33258, FITC, and rhodamine&#x2013;phalloidin were excited at 358&#x202F;nm, 488&#x202F;nm, and 551&#x202F;nm, respectively, with fluorescence emission signals collected at 461&#x202F;nm, 550&#x202F;nm, and 595&#x202F;nm. Oocytes were optically sectioned along the Z-axis, and cortical F-actin images were acquired at the equatorial plane. Oocytes were classified based on meiotic spindle morphology (normal symmetrical barrel-shaped spindles versus abnormal disorganized, clumped, or dispersed structures), chromosomal alignment (proper alignment versus misalignment or dispersion at the metaphase plate), and cortical F-actin distribution (continuous, uniformly distributed subplasmalemmal F-actin layer versus irregular or discontinuous organization) (<xref ref-type="bibr" rid="ref31">31</xref>). The proportion of oocytes displaying normal or aberrant spindle, chromatin, and cortical F-actin configurations was quantified for each experimental group.</p>
</sec>
<sec id="sec15">
<label>2.13</label>
<title>Oocyte parthenogenetic activation (PA) and <italic>in vitro</italic> embryo culture (IVEC)</title>
<p>To evaluate the effects of PS-MPs exposure on developmental competence, oocytes were parthenogenetically activated (PA) after IVM with 5&#x202F;&#x03BC;M ionomycin in TCM-199 for 5&#x202F;min, followed by 4&#x202F;h of culture in TCM-199 with 2&#x202F;mM 6-dimethylaminopurine (6-DMAP) in a humidified atmosphere with 5% CO<sub>2</sub> at 38.5&#x202F;&#x00B0;C (<xref ref-type="bibr" rid="ref32">32</xref>). PA oocytes underwent <italic>in vitro</italic> embryo culture (IVEC) for 7&#x202F;days in four-well dishes containing 500&#x202F;&#x03BC;L/well of synthetic oviductal fluid medium (SOFM) with essential and non-essential amino acids at oviductal concentrations and 0.4% bovine serum albumin (BSA) under mineral oil in humidified atmosphere with 5% CO<sub>2</sub>, 5% O<sub>2</sub>, and 90% N<sub>2</sub> at 38.5&#x202F;&#x00B0;C (<xref ref-type="bibr" rid="ref3">3</xref>). Embryo development was followed by conventional morphology assessment under phase contrast microscopy. The cleavage was evaluated morphologically after 24 and 48&#x202F;h of culture, while development to the blastocyst stage was assessed on day 7 (<xref ref-type="bibr" rid="ref32">32</xref>). Blastocysts were classified according to the expansion and hatching status as early (initiating blastocoelic cavity formation), cavitated (full blastocoelic cavity formation), expanded (increased size with blastocelic cavity greater than half of the embryo volume and thinner zona pellucida), hatching (beginning of the exit from the zona pellucida), or hatched (full exit from the zona pellucida). Moreover, blastocyst diameter was evaluated by Oosight&#x2122; Research Instruments as the distance between the outside borders of the trophectoderm. Finally, blastocyst formation was confirmed on the last day of the culture by observing blastomere nuclear chromatin under epifluorescence microscopy after staining with Hoechst 33258, as indicated before.</p>
</sec>
<sec id="sec16">
<label>2.14</label>
<title>Statistical analysis</title>
<p>Oocyte chromatin configurations, mitochondria distribution patterns, cytoskeletal configurations, cleavage rates, blastocyst rates, and apoptotic index were compared between conditions using the Chi-square test. PS-MPs uptake, bioenergetic oxidative status parameters, and gene expression were compared using one-way analysis of variance (ANOVA) followed by Tukey&#x2019;s multiple comparison test. Data were analyzed with GraphPad Prism (Software version 8.0.2, San Diego, CA, USA). Differences with <italic>p&#x202F;&#x003C;</italic>&#x202F;0.05 were considered statistically significant.</p>
</sec>
</sec>
<sec sec-type="results" id="sec17">
<label>3</label>
<title>Results</title>
<sec id="sec18">
<label>3.1</label>
<title>Assessment of fluorescent PS-MPs uptake into sheep COCs and CCs monolayers</title>
<p>The uptake of fluorescent 200&#x202F;nm PS-MPs was assessed on a total of 30 ovine COCs at the end of IVM culture. Only the lowest and highest PS-MPs concentrations were used for this test (5&#x202F;&#x03BC;g/mL and 100&#x202F;&#x03BC;g/mL, respectively). For oocytes, no significant differences in intracellular fluorescence intensity were observed in comparison to the control condition, regardless of PS-MPs concentration. In contrast, for CCs, increased PS-MPs uptake was observed after exposure to the highest tested concentration (<italic>p&#x202F;&#x003C;</italic>&#x202F;0.05; <xref ref-type="fig" rid="fig2">Figure 2A</xref>). Bioaccumulation of fluorescent PS-MPs over time in CCs was analyzed in monolayer-cultured CCs. Increased PS-MPs bioaccumulation was observed already after 6&#x202F;h of <italic>in vitro</italic> exposure, both at 5&#x202F;&#x03BC;g/mL (<italic>p&#x202F;&#x003C;</italic>&#x202F;0.05) and 100&#x202F;&#x03BC;g/mL (<italic>p&#x202F;&#x003C;</italic>&#x202F;0.0001) concentrations compared to the control condition. After 24&#x202F;h of exposure, the intracellular uptake of PS-MP was confirmed at the highest concentration (<italic>p&#x202F;&#x003C;</italic>&#x202F;0.0001; <xref ref-type="fig" rid="fig2">Figure 2B</xref>).</p>
<fig position="float" id="fig2">
<label>Figure 2</label>
<caption>
<p>Assessment of PS-MPs uptake into oocytes (OOs) and cumulus cells (CCs) of sheep COCs after 24&#x202F;h IVM <bold>(A)</bold> and CCs grown in monolayers after 6 and 24&#x202F;h <bold>(B)</bold> of exposure to fluorescent 200&#x202F;nm microparticles concentrated 0&#x202F;&#x03BC;g/mL <bold>(A1,B1)</bold>, 5&#x202F;&#x03BC;g/mL <bold>(A2,B2)</bold>, and 100&#x202F;&#x03BC;g/mL <bold>(A3,B3)</bold>. One-way analysis of variance (ANOVA) followed by Tukey&#x2019;s multiple comparison test: &#x002A;<italic>p&#x202F;&#x003C;</italic>&#x202F;0.05; &#x002A;&#x002A;&#x002A;&#x002A;<italic>p&#x202F;&#x003C;</italic>&#x202F;0.0001. Scale bar&#x202F;=&#x202F;10&#x202F;&#x03BC;m.</p>
</caption>
<graphic xlink:href="fvets-13-1771581-g002.tif" mimetype="image" mime-subtype="tiff">
<alt-text content-type="machine-generated">Composite figure containing two data bar graphs with error bars and statistical significance markers, alongside six labeled microscopy images showing magenta fluorescence. Graphs compare normalized ADU or ADU values for control and two experimental groups (5 micrograms per milliliter and 100 micrograms per milliliter) in cumulus-oocyte complexes (COCs) and cumulus cells (CCs) at different time points, highlighting increased uptake at higher concentrations or durations. Microscopy images (A1-A3 and B1-B3) display cellular fluorescence intensities under each condition, with scale bars indicating size reference.</alt-text>
</graphic>
</fig>
</sec>
<sec id="sec19">
<label>3.2</label>
<title>Effects of PS-MPs exposure on cumulus cell gene expression</title>
<p>The real-time PCR analysis of CCs isolated from 356 COCs exposed to PS-MPs during IVM revealed significant alterations in the expression of genes related to oxidative stress and apoptosis across the different treatment groups (<xref ref-type="fig" rid="fig3">Figure 3</xref>). The expression levels of GPX and SOD, key enzymes involved in antioxidant defense, were reduced at the concentration of 100&#x202F;&#x03BC;g/mL (<italic>p&#x202F;&#x003C;</italic>&#x202F;0.05). CAT expression did not vary at any tested concentration. Regarding apoptosis-related gene expression, BAX, a proapoptotic gene, was significantly upregulated only at 5&#x202F;&#x03BC;g/mL (<italic>p&#x202F;&#x003C;</italic>&#x202F;0.05), whereas BCL2 expression did not reach statistical significance.</p>
<fig position="float" id="fig3">
<label>Figure 3</label>
<caption>
<p>Effects of PS-MPs on oxidative stress and apoptosis in CCs. Relative expression of GPX <bold>(A)</bold>, SOD <bold>(B)</bold>, CAT <bold>(C)</bold>, BAX <bold>(D)</bold>, and BCL2 <bold>(E)</bold> genes, validated using real-time PCR, in CCs isolated from COCs exposed during IVM. One-way analysis of variance (ANOVA) followed by Tukey&#x2019;s multiple comparison test: &#x002A;<italic>p&#x202F;&#x003C;</italic>&#x202F;0.05.</p>
</caption>
<graphic xlink:href="fvets-13-1771581-g003.tif" mimetype="image" mime-subtype="tiff">
<alt-text content-type="machine-generated">Five grouped bar graphs display the relative expression of GPX, SOD, CAT, BAX, and BCL2 across control and three treatment concentrations. Significant differences are marked with asterisks for GPX, SOD, and BAX. Error bars indicate standard deviation.</alt-text>
</graphic>
</fig>
</sec>
<sec id="sec20">
<label>3.3</label>
<title>Effects of PS-MPs exposure on cumulus cell apoptotic index</title>
<p>The TUNEL assay revealed a dose-dependent increase in positive CCs (green-stained cells with fragmented DNA) isolated from a total of 68 COCs exposed to PS-MPs during IVM (46.6% at 5&#x202F;&#x03BC;g/mL, <italic>p&#x202F;&#x003C;</italic>&#x202F;0.05; 64% at 50&#x202F;&#x03BC;g/mL, <italic>p&#x202F;&#x003C;</italic>&#x202F;0.0001; and 81% at 100&#x202F;&#x03BC;g/mL, <italic>p&#x202F;&#x003C;</italic>&#x202F;0.0001) compared to the control condition, which showed only 34% of TUNEL-positive cells (<xref ref-type="fig" rid="fig4">Figure 4</xref>).</p>
<fig position="float" id="fig4">
<label>Figure 4</label>
<caption>
<p>Effects of PS-MPs on CCs apoptosis by terminal deoxynucleotidyltransferase-mediated dUTP nick-end labeling (TUNEL) assay. Bar graphs showing the percentages of TUNEL-positive (with fragmented DNA) CCs after COC exposure to different PS-MPs concentrations <bold>(A)</bold>. The number of analyzed CCs per experimental condition is indicated at the bottom of each graph. Chi-squared test: within each column, different superscripts indicate statistically significant differences: &#x002A;<italic>p&#x202F;&#x003C;</italic>&#x202F;0.05; &#x002A;&#x002A;&#x002A;&#x002A;<italic>p&#x202F;&#x003C;</italic>&#x202F;0.0001. Representative images of CCs observed after IVM in the presence of PS-MPs <bold>(B)</bold> at 0&#x202F;g/mL <bold>(a,a&#x2019;)</bold>, 5&#x202F;g/mL <bold>(b,b&#x2019;)</bold>, 50&#x202F;g/mL <bold>(c,c&#x2019;)</bold>, and 100&#x202F;g/mL <bold>(d,d&#x2019;)</bold>. Scale bar indicates 10&#x202F;m.</p>
</caption>
<graphic xlink:href="fvets-13-1771581-g004.tif" mimetype="image" mime-subtype="tiff">
<alt-text content-type="machine-generated">Panel A presents a bar graph showing increasing apoptotic index values with escalating treatment concentrations, with statistical significance indicated. Panel B contains Hoechst and TUNEL fluorescent microscopy images for control and treatment groups, where green TUNEL-positive cells increase with treatment dose, as indicated by arrows.</alt-text>
</graphic>
</fig>
</sec>
<sec id="sec21">
<label>3.4</label>
<title>Effects of PS-MPs exposure on oocyte nuclear maturation</title>
<p>The evaluation of the effects of non-functionalized 100&#x202F;nm PS-MPs was performed on a total of 426 cultured COCs after IVM (5 replicates). As shown in <xref ref-type="table" rid="tab2">Table 2</xref>, exposure to PS-MPs impaired meiosis resumption, particularly at higher tested concentrations. The percentage of oocytes reaching the MII&#x202F;+&#x202F;PB stage was significantly lower at 50 and 100&#x202F;&#x03BC;g/mL PS-MPs (<italic>p&#x202F;&#x003C;</italic>&#x202F;0.01), whereas exposure to 5&#x202F;&#x03BC;g/mL did not affect the maturation rate compared to untreated oocytes. These data were associated with a significant increase in the GV rates, particularly at 50&#x202F;&#x03BC;g/mL and 100&#x202F;&#x03BC;g/mL (<italic>p&#x202F;&#x003C;</italic>&#x202F;0.05). Notably, no significant differences were observed in the rates of abnormal chromatin configurations at all tested exposure concentrations.</p>
<table-wrap position="float" id="tab2">
<label>Table 2</label>
<caption>
<p>Effects of PS-MPs exposure during IVM on oocyte nuclear maturation.</p>
</caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th align="left" valign="top" rowspan="2">PS-MP concentration (&#x03BC;g/mL)</th>
<th align="center" valign="top" rowspan="2">Cultured COCs<break/>N.</th>
<th align="center" valign="top" rowspan="2">Evaluated oocytes<break/>N.</th>
<th align="center" valign="top" colspan="4">Nuclear chromatin configurations<break/>N. (%)</th>
</tr>
<tr>
<th align="center" valign="top">GV</th>
<th align="center" valign="top">MI to TI</th>
<th align="center" valign="top">MII&#x202F;+&#x202F;PB</th>
<th align="center" valign="top">Abnormal</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="middle">0 (Control)</td>
<td align="center" valign="middle">100</td>
<td align="center" valign="middle">88</td>
<td align="char" valign="middle" char="(">12 (13.6)<sup>&#x1D44E;</sup></td>
<td align="char" valign="middle" char="(">8 (9.1)<sup>&#x1D44E;</sup></td>
<td align="char" valign="middle" char="(">56 (63.6)<sup>a</sup></td>
<td align="char" valign="middle" char="(">8 (9.1)</td>
</tr>
<tr>
<td align="left" valign="middle">5</td>
<td align="center" valign="middle">94</td>
<td align="center" valign="middle">78</td>
<td align="char" valign="middle" char="(">15 (19.2)</td>
<td align="char" valign="middle" char="(">5 (6.4)</td>
<td align="char" valign="middle" char="(">46 (59)</td>
<td align="char" valign="middle" char="(">5 (6.4)</td>
</tr>
<tr>
<td align="left" valign="middle">50</td>
<td align="center" valign="middle">111</td>
<td align="center" valign="middle">99</td>
<td align="char" valign="middle" char="(">28 (28.3)<sup>&#x1D44F;</sup></td>
<td align="char" valign="middle" char="(">14 (14.1)</td>
<td align="char" valign="middle" char="(">44 (44.4)<sup>c</sup></td>
<td align="char" valign="middle" char="(">8 (8.1)</td>
</tr>
<tr>
<td align="left" valign="middle">100</td>
<td align="center" valign="middle">121</td>
<td align="center" valign="middle">110</td>
<td align="char" valign="middle" char="(">29 (26.4)<sup>&#x1D44F;</sup></td>
<td align="char" valign="middle" char="(">21 (19.1)<sup>&#x1D44F;</sup></td>
<td align="char" valign="middle" char="(">45 (41)<sup>c</sup></td>
<td align="char" valign="middle" char="(">12 (10.9)</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<p>PS-MPs, Polystyrene Microplastics; IVM, <italic>In Vitro</italic> Maturation; COC, Cumulus-Oocyte Complex; GV, Germinal Vesicle; MI, Metaphase I; TI, Telophase I; MII, Metaphase II; PB, Polar Body. Comparisons for meiotic stages, between each tested condition versus control: Chi-squared test: within each column, different superscripts indicate statistically significant differences: <sup>a,b</sup><italic>p&#x202F;&#x003C;</italic>&#x202F;0.05; <sup>a,c</sup><italic>p&#x202F;&#x003C;</italic>&#x202F;0.01.</p>
</table-wrap-foot>
</table-wrap>
</sec>
<sec id="sec22">
<label>3.5</label>
<title>Effects of PS-MPs exposure on oocyte cytoplasmic quality</title>
<p>Qualitative and quantitative parameters of bioenergetic/oxidative status were assessed in oocytes reaching nuclear maturation after IVM as a measure of cytoplasmic quality and developmental competence. Regarding the qualitative parameter, the rates of MII&#x202F;+&#x202F;PB oocytes displaying heterogeneous P/S distribution patterns (43% for control [9/21], 43% for 5&#x202F;&#x03BC;g/mL [10/23], 24% for 50&#x202F;&#x03BC;g/mL [4/17], and 31% for 100&#x202F;&#x03BC;g/mL [5/16]) were not significantly affected by PS-MPs exposure.</p>
<p>The quantification of bioenergetic/oxidative status parameters revealed increased intracellular ROS levels at all PS-MPs exposure concentration compared to the control group (<italic>p&#x202F;&#x003C;</italic>&#x202F;0.05 for 5&#x202F;&#x03BC;g/mL, <italic>p&#x202F;&#x003C;</italic>&#x202F;0.0001 for 50&#x202F;&#x03BC;g/mL and 100&#x202F;&#x03BC;g/mL; <xref ref-type="fig" rid="fig5">Figure 5A</xref>) whereas no differences were observed for mitochondrial membrane potential (<xref ref-type="fig" rid="fig5">Figure 5B</xref>). Finally, mitochondria/ROS colocalization showed a significant increase in oocytes exposed to 5&#x202F;&#x03BC;g/mL (<italic>p&#x202F;&#x003C;</italic>&#x202F;0.05) and 50&#x202F;&#x03BC;g/mL (<italic>p&#x202F;&#x003C;</italic>&#x202F;0.0001) (<xref ref-type="fig" rid="fig5">Figure 5C</xref>).</p>
<fig position="float" id="fig5">
<label>Figure 5</label>
<caption>
<p>Effects of PS-MPs exposure during IVM on mitochondrial activity, intracellular ROS levels, and mitochondria/ROS colocalization in sheep mature oocytes. MitoTracker Orange CM&#x2122; Ros fluorescence intensity levels <bold>(A)</bold>, dichlorofluorescein (DCF) <bold>(B)</bold>, and mitochondria/ROS overlap coefficients <bold>(C)</bold> are expressed in arbitrary densitometric units (ADU). The number of oocytes analyzed by LSCM per experimental condition is indicated at the bottom of each histogram. One-way analysis of variance (ANOVA) followed by Tukey&#x2019;s multiple comparison test: &#x002A;<italic>p&#x202F;&#x003C;</italic>&#x202F;0.05; &#x002A;&#x002A;&#x002A;&#x002A;<italic>p&#x202F;&#x003C;</italic>&#x202F;0.0001.</p>
</caption>
<graphic xlink:href="fvets-13-1771581-g005.tif" mimetype="image" mime-subtype="tiff">
<alt-text content-type="machine-generated">Three grouped bar graphs labeled A, B, and C compare four conditions: Control, 5 micrograms per milliliter, 50 micrograms per milliliter, and 100 micrograms per milliliter. Graph A shows reactive oxygen species (ROS) levels with significant increases at higher concentrations, indicated by asterisks. Graph B displays mitochondria activity with no significant differences between groups. Graph C shows mitochondria and ROS colocalization with significant increases at 50 micrograms per milliliter compared to control and 5 micrograms per milliliter, marked by asterisks. Error bars represent standard deviation.</alt-text>
</graphic>
</fig>
</sec>
<sec id="sec23">
<label>3.6</label>
<title>Effects of PS-MPs exposure on oocyte cytoskeletal organization</title>
<p>Oocyte exposure to PS-MPs resulted in perturbations in meiotic spindle assembly, chromosome alignment, and actin filament distribution. Indeed, the rate of oocytes exhibiting a classical barrel-shaped meiotic spindle structure was lower compared to untreated oocytes, regardless of PS-MPs concentration (<italic>p&#x202F;&#x003C;</italic>&#x202F;0.0001 for 5&#x202F;&#x03BC;g/mL, <italic>p&#x202F;&#x003C;</italic>&#x202F;0.05 for 50&#x202F;&#x03BC;g/mL, and <italic>p&#x202F;&#x003C;</italic>&#x202F;0.05 for 100&#x202F;&#x03BC;g/mL) (<xref ref-type="fig" rid="fig6">Figure 6A</xref>). The rate of oocytes with correctly aligned chromosomes was also found to be reduced, particularly after exposure to 5 and 50&#x202F;&#x03BC;g/mL (<italic>p&#x202F;&#x003C;</italic>&#x202F;0.0001 and <italic>p&#x202F;&#x003C;</italic>&#x202F;0.05, respectively) (<xref ref-type="fig" rid="fig6">Figure 6B</xref>). Finally, the percentage of oocytes with normally distributed actin filaments was reduced at all PS-MPs concentrations (<italic>p&#x202F;&#x003C;</italic>&#x202F;0.05 for 5&#x202F;&#x03BC;g/mL, <italic>p&#x202F;&#x003C;</italic>&#x202F;0.001 for 50&#x202F;&#x03BC;g/mL and <italic>p&#x202F;&#x003C;</italic>&#x202F;0.05 for 100&#x202F;&#x03BC;g/mL), with oocytes displaying irregular staining in the area beneath the oolemma or spots staining within the ooplasm (<xref ref-type="fig" rid="fig6">Figure 6C</xref>).</p>
<fig position="float" id="fig6">
<label>Figure 6</label>
<caption>
<p>Effects of PS-MPs exposure on oocyte chromatin and cytoskeleton morphology. Graphs showing the percentage of oocytes with normal chromatin <bold>(A)</bold>, meiotic spindle <bold>(B)</bold>, and F-actin configuration <bold>(C)</bold>. Chi-squared test: &#x002A;<italic>p&#x202F;&#x003C;</italic>&#x202F;0.05; &#x002A;&#x002A;&#x002A;<italic>p&#x202F;&#x003C;</italic>&#x202F;0.0001; &#x002A;&#x002A;&#x002A;&#x002A;<italic>p&#x202F;&#x003C;</italic>&#x202F;0.00001. Representative LSCM images representing normal chromatin (blue) and spindle (green) configuration <bold>(D1)</bold>, abnormal chromatin and spindle configuration <bold>(D2,D3)</bold>, normal cortical -actin (red) <bold>(D4)</bold>, and abnormal cortical -actin <bold>(D5,D6)</bold>. Scale bar&#x202F;=&#x202F;25&#x202F;m.</p>
</caption>
<graphic xlink:href="fvets-13-1771581-g006.tif" mimetype="image" mime-subtype="tiff">
<alt-text content-type="machine-generated">Three bar graphs labeled A, B, and C compare the percentage of normal spindle, chromatin, and cortical F-actin morphology among control and three treatment groups (5, 50, and 100 micrograms per milliliter), showing significant decreases in all treatments. Panel D displays six fluorescence micrographs of cells, D1-D3 showing merged channels with actin (red), tubulin (green), chromatin (blue), and magnified insets; D4-D6 show only actin (red) for each condition, highlighting structural changes across treatments. A scale bar of 25 micrometers is present.</alt-text>
</graphic>
</fig>
</sec>
<sec id="sec24">
<label>3.7</label>
<title>Effects of PS-MPs exposure on oocyte developmental competence</title>
<p>The evaluation of the effects of PS-MPs exposure on developmental competence was performed on a total of 151 oocytes (three replicates). Only the lowest and intermediate PS-MPs concentrations were used for this test (5&#x202F;&#x03BC;g/mL and 50&#x202F;&#x03BC;g/mL, respectively). After 24&#x202F;h of PA, the total cleavage rate was significantly reduced in oocytes exposed to 50&#x202F;&#x03BC;g/mL (<italic>p&#x202F;&#x003C;</italic>&#x202F;0.01; <xref ref-type="table" rid="tab3">Table 3</xref>), whereas no differences were found at 5&#x202F;&#x03BC;g/mL compared to the control. After 48&#x202F;h, no differences were observed in the cleavage rate, regardless of PS-MPs concentration (<xref ref-type="table" rid="tab3">Table 3</xref>). After 7&#x202F;days of IVEC, the blastocyst formation rate was not statistically different among conditions (<xref ref-type="table" rid="tab3">Table 3</xref>). Regarding blastocyst quality, no differences were observed in either the mean diameter or the total number of nuclei, among experimental groups (<xref ref-type="table" rid="tab3">Table 3</xref>). Nevertheless, hatched blastocysts were only obtained in the control group.</p>
<table-wrap position="float" id="tab3">
<label>Table 3</label>
<caption>
<p>Effects of PS-MPs exposure during IVM on oocyte developmental competence.</p>
</caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th align="left" valign="top">PS-MPs<break/>concentration<break/>(&#x03BC;g/mL)</th>
<th align="center" valign="top">PA oocytes<break/>N.</th>
<th align="center" valign="top">Cleavage rate at 24&#x202F;h<break/>N. (%)</th>
<th align="center" valign="top">Cleavage rate at 48&#x202F;h<break/>N. (%)</th>
<th align="center" valign="top">Blastocyst rate<break/>N. (%)</th>
<th align="center" valign="top">Blastocyst diameter<break/>Mean (&#x03BC;m)&#x202F;&#x00B1;&#x202F;s.d.</th>
<th align="center" valign="top">Blastocyst nuclei<break/>Mean &#x00B1; s.d.</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="middle">0 (Control)</td>
<td align="center" valign="middle">52</td>
<td align="char" valign="middle" char="(">26 (50)<sup>a</sup></td>
<td align="char" valign="middle" char="(">30 (58)</td>
<td align="char" valign="middle" char="(">7 (23)</td>
<td align="char" valign="middle" char="&#x00B1;">193.3 &#x00B1; 67.8</td>
<td align="char" valign="middle" char="&#x00B1;">79 &#x00B1; 29</td>
</tr>
<tr>
<td align="left" valign="middle">5</td>
<td align="center" valign="middle">49</td>
<td align="char" valign="middle" char="(">22 (45)</td>
<td align="char" valign="middle" char="(">31 (63)</td>
<td align="char" valign="middle" char="(">3 (10)</td>
<td align="char" valign="middle" char="&#x00B1;">176.4 &#x00B1; 40.6</td>
<td align="char" valign="middle" char="&#x00B1;">83 &#x00B1; 31</td>
</tr>
<tr>
<td align="left" valign="middle">50</td>
<td align="center" valign="middle">50</td>
<td align="char" valign="middle" char="(">11 (22)<sup>c</sup></td>
<td align="char" valign="middle" char="(">25 (50)</td>
<td align="char" valign="middle" char="(">3 (12)</td>
<td align="char" valign="middle" char="&#x00B1;">179.8 &#x00B1; 34.7</td>
<td align="char" valign="middle" char="&#x00B1;">102 &#x00B1; 34</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<p>PS-MPs, Polystyrene Microplastics; IVM, In Vitro Maturation; PA, Parthenogenetically Activated. Comparisons for cleavage and blastocyst rates, between each tested condition versus control: Chi-squared test: within each column, different superscripts indicate statistically significant differences: <sup>a,c</sup><italic>p&#x202F;&#x003C;</italic>&#x202F;0.01. Comparisons for blastocyst diameter and nuclei, between each tested condition versus control: One-way analysis of variance ANOVA followed by Tukey&#x2019;s multiple comparison test: not significant.</p>
</table-wrap-foot>
</table-wrap>
</sec>
</sec>
<sec sec-type="discussion" id="sec25">
<label>4</label>
<title>Discussion</title>
<p>In the present study, the effects of different concentrations of PS-MPs were evaluated on the cumulus&#x2013;oocyte complex in the ovine model. PS-MPs were chosen based on their global prevalence (<xref ref-type="bibr" rid="ref9">9</xref>, <xref ref-type="bibr" rid="ref18">18</xref>, <xref ref-type="bibr" rid="ref19">19</xref>, <xref ref-type="bibr" rid="ref33">33</xref>) and environmental persistence, which results from their slow degradation (<xref ref-type="bibr" rid="ref9">9</xref>). Furthermore, this polymer has been reported as the second most prevalent type detected in human blood samples, further supporting this choice (<xref ref-type="bibr" rid="ref34">34</xref>).</p>
<p>The first step was to evaluate PS-MPs uptake into COCs and CC monolayers. Previous studies have highlighted the ability of MPs to enter cells and accumulate in animal tissues, depending on particle size, concentration, and exposure time (<xref ref-type="bibr" rid="ref9">9</xref>, <xref ref-type="bibr" rid="ref10">10</xref>, <xref ref-type="bibr" rid="ref13">13</xref>, <xref ref-type="bibr" rid="ref14">14</xref>). Regarding the female reproductive system, PS-MPs presence is well-documented in the ovary (<xref ref-type="bibr" rid="ref9">9</xref>, <xref ref-type="bibr" rid="ref10">10</xref>, <xref ref-type="bibr" rid="ref13">13</xref>, <xref ref-type="bibr" rid="ref14">14</xref>, <xref ref-type="bibr" rid="ref35">35</xref>), whereas little is known regarding their ability to penetrate the COC. In the present study, the use of fluorescent particles allowed the detection of the presence of PS-MPs inside the ovine COC, specifically in CCs, where a significant increase in uptake was observed at the highest concentration. This result highlights that larger (microplastic) size particles are also able to penetrate the COC and not just PS-NPs, as already demonstrated in a previous study in the murine (<xref ref-type="bibr" rid="ref36">36</xref>) and bovine (30&#x202F;nm) (<xref ref-type="bibr" rid="ref37">37</xref>) models. In agreement with our study, in the murine model, PS-NPs internalization did not extend beyond the CCs (<xref ref-type="bibr" rid="ref36">36</xref>). Instead, in the bovine model, internalization occurred both in CCs and in the ooplasm, possibly via transcellular (CCs and transzonal projections) and paracellular (zona pellucida) routes (<xref ref-type="bibr" rid="ref37">37</xref>). This could be due to a smaller particle size than those used in our study (30&#x202F;nm rather than 200&#x202F;nm) or to differences in zona pellucida composition/structure between ovine and bovine COCs. Furthermore, the evaluation of CCs grown in monolayers confirmed that PS-MPs bioaccumulation is time-dependent, starting after 6&#x202F;h of culture and increasing after 24&#x202F;h.</p>
<p>Given the accumulation of PS-MPs in CCs, further experiments were conducted to evaluate the impact on CC functionality. Previous <italic>in vivo</italic> studies reported increased expression of pro-apoptotic genes and decreased expression of those protecting from oxidative stress, thus resulting in apoptosis of granulosa cells, isolated from rats to which 500&#x202F;nm PS-MPs were orally administered (<xref ref-type="bibr" rid="ref38">38</xref>, <xref ref-type="bibr" rid="ref39">39</xref>). Our findings confirmed alterations in the expression of genes, related to oxidative stress and apoptosis, in CCs recovered from COCs exposed to PS-MPs during IVM. In detail, GPX, a gene essential in neutralizing peroxides and mitigating oxidative damage, and SOD, an enzyme converting superoxide radicals into hydrogen peroxide, showed downregulation at 100&#x202F;&#x03BC;g/mL, thus indicating compromised antioxidant enzymatic response. The expression of CAT, an antioxidant gene responsible for converting hydrogen peroxide into water and oxygen, was not altered. Regarding the expression of genes involved in apoptosis, BAX, a pro-apoptotic gene, was upregulated at the lowest PS-MPs concentration, indicating an increased activation of apoptotic pathways. Conversely, the expression levels of BCL2, an anti-apoptotic gene, did not change across all treated groups.</p>
<p>In order to assess whether PS-MPs could affect CC viability, the TUNEL assay was used. This method is commonly employed to detect DNA fragmentation as one of the most specific markers in apoptosis, although also possibly linked to necrosis caused by toxic compounds or other insults (<xref ref-type="bibr" rid="ref26">26</xref>). In our study, we highlighted significant increases in the rates of positive CCs at any tested concentration. Most of the studies conducted so far on the effects of MPs on germline cells report induction of the apoptosis process triggered by ROS overproduction (<xref ref-type="bibr" rid="ref19">19</xref>). Thus, we hypothesized that the obtained results could be signs of an increase in the apoptotic index rather than necrosis. This observation aligns with a previous study in which increased apoptosis of granulosa cells was observed in rats treated with 500&#x202F;nm PS-MPs compared to untreated animals (<xref ref-type="bibr" rid="ref39">39</xref>). Overall, the combined results from real-time PCR for SOD, GPX, and BAX, and the TUNEL assay suggest that PS-MPs adversely impact CCs&#x2019; viability and functionality by inducing oxidative stress and apoptosis, in line with previous studies (<xref ref-type="bibr" rid="ref19">19</xref>, <xref ref-type="bibr" rid="ref38">38</xref>).</p>
<p>Considering the intense bi-directional communication established between CCs and oocytes, within the COC structure, culminating in the acquisition of maturation and embryo developmental competence (<xref ref-type="bibr" rid="ref40">40</xref>), this specific accumulation site could potentially lead to indirect oocyte damage resulting from CCs dysfunction and transzonal projections reduction, as already demonstrated (<xref ref-type="bibr" rid="ref36">36</xref>, <xref ref-type="bibr" rid="ref41">41</xref>). In our experimental conditions, exposure to 50 and 100&#x202F;&#x03BC;g/mL PS-MPs concentrations reduced the rate of mature oocytes. Concerning the higher tested concentration (100&#x202F;&#x03BC;g/mL), our data are in agreement with those of previous <italic>in vitro</italic> studies in which reduced maturation rates were observed after exposure to 300&#x202F;&#x03BC;g/mL of PS-MPs in porcine (<xref ref-type="bibr" rid="ref42">42</xref>) as well as to 100 and 200&#x202F;&#x03BC;g/mL of 100&#x202F;nm PS-MPs in the bovine species (<xref ref-type="bibr" rid="ref37">37</xref>). Conversely, another study in porcine oocytes showed a lack of toxicity after using 100&#x202F;nm PS-MPs at 100 and 200&#x202F;&#x03BC;g/mL (<xref ref-type="bibr" rid="ref43">43</xref>). Regarding the intermediate concentration (50&#x202F;&#x03BC;g/mL), the negative effect observed in our study is in line with data obtained in porcine oocytes exposed to 100&#x202F;nm PS-MPs at a concentration of 30 and 50&#x202F;&#x03BC;g/mL (<xref ref-type="bibr" rid="ref42">42</xref>, <xref ref-type="bibr" rid="ref44">44</xref>). Instead, the exposure to our same particle concentration (50&#x202F;&#x03BC;g/mL) and size did not exert any effect on bovine oocyte maturation (<xref ref-type="bibr" rid="ref37">37</xref>). Finally, in our study, the lowest tested concentration (5&#x202F;&#x03BC;g/mL) did not exert negative effects on oocyte maturation. In agreement with our data, no toxic effects were observed after exposure of porcine (<xref ref-type="bibr" rid="ref42">42</xref>) and bovine (<xref ref-type="bibr" rid="ref37">37</xref>) oocytes with 100&#x202F;nm PS-MPs concentrated at 3&#x202F;&#x03BC;g/mL and 5&#x202F;&#x03BC;g/mL, respectively, in the two studies. Conversely, another study in the pig, also using 100&#x202F;nm PS-MPs, highlighted a marked cytotoxic effect even at very low concentrations (1 and 10&#x202F;&#x03BC;g/mL) (<xref ref-type="bibr" rid="ref44">44</xref>). In addition, the negative impact observed after IVM is supported by an <italic>in vivo</italic> study, in which female mice treated with daily oral doses of 800&#x202F;nm PS-MPs (30&#x202F;mg/kg body weight for 35&#x202F;days) (<xref ref-type="bibr" rid="ref45">45</xref>) showed a significant decrease in the first PB extrusion rates compared to untreated animals, thus providing complementary evidence on the toxicological impact exerted by PS-MPs to <italic>in vitro</italic> studies.</p>
<p>In order to acquire embryo developmental competence, oocytes should reach not only nuclear but also cytoplasmic maturation, consisting of a remarkable reorganization of the ooplasm with important changes in structure, function, and/or distribution of all major organelles (<xref ref-type="bibr" rid="ref46">46</xref>). Among them, mitochondria are the main site of ATP production, necessary for spindle assembly and chromosome segregation (<xref ref-type="bibr" rid="ref47">47</xref>), and consequently of ROS, generated as by-products of oxidative phosphorylation mediated by the electron transport chain. When produced at low physiological levels, these molecules are important to trigger meiosis resumption and induce oocyte maturation (<xref ref-type="bibr" rid="ref47">47</xref>, <xref ref-type="bibr" rid="ref48">48</xref>), but when they exceed oocyte antioxidant capacity, this could result in oxidative stress, potentially leading to macromolecular damage and impairment in oocyte function and viability. Therefore, mitochondrial quality determines the quality of the oocyte and the future embryo since they are exclusively maternally inherited (<xref ref-type="bibr" rid="ref49">49</xref>). In our study, the rate of oocytes with perinuclear/subcortical mitochondrial distribution pattern, index of cytoplasmic maturation (<xref ref-type="bibr" rid="ref24">24</xref>), did not vary at all PS-MP tested concentrations. This finding is not in agreement with a study in the porcine model (<xref ref-type="bibr" rid="ref44">44</xref>) in which oocytes exposed to 100&#x202F;nm PS-MPs displayed mitochondria dispersed throughout the cytoplasm, generally considered as indicative of cytoplasmic immaturity (<xref ref-type="bibr" rid="ref46">46</xref>). These differences could be due to differences in methods used for mitochondria distribution staining and analysis. Instead, significantly increased ROS levels were observed in oocytes exposed to PS-MPs, in agreement with studies that tested PS-MPs ranging from 100 to 500&#x202F;nm in bovine (<xref ref-type="bibr" rid="ref37">37</xref>) and porcine (<xref ref-type="bibr" rid="ref42 ref43 ref44">42&#x2013;44</xref>) models, thus indicating the promotion of an oxidative stress condition.</p>
<p>Among cellular components that can be damaged by oxidative stress, the cytoskeleton appears to be particularly sensitive (<xref ref-type="bibr" rid="ref31">31</xref>). The organization and dynamics of spindle microtubules and actin filaments are necessary for meiosis progression, polar body extrusion, and the distribution of some organelles, such as mitochondria (<xref ref-type="bibr" rid="ref31">31</xref>). Our results revealed that PS-MP exposure disrupted chromosome alignment, meiotic spindle assembly, and cortical actin configuration, regardless of concentration, in agreement with a previous study in porcine oocytes (100&#x202F;nm) (<xref ref-type="bibr" rid="ref44">44</xref>). Instead, most of the control oocytes had chromosomes aligned on the meiotic spindle with a classical barrel-shape structure, with uniform intensity signals of actin filaments beneath the oolemma. Overall, our findings reveal that, regardless of PS-MP concentrations, those oocytes able to resume meiosis and reach the metaphase II stage are characterized by low quality due to oxidative stress and cytoskeletal disorganization, alterations that may impair their subsequent developmental competence.</p>
<p>Finally, to evaluate possible toxic carry-over effects on developmental competence derived from exposure to PS-MPs during IVM, oocytes were parthenogenetically activated, thus avoiding possible interfering sperm-related effects. At the concentration of 50&#x202F;&#x03BC;g/mL, our findings confirmed the negative effects, already observed in relation to oocyte nuclear and cytoplasmic maturation, on embryo developmental competence, as embryo cleavage was slowed. Instead, at the lowest tested concentration (5&#x202F;&#x03BC;g/mL), no toxic effects were evidenced on embryo cleavage as well as on blastocyst formation rate. To date, few controversial data have been published on the effects of MPs on embryo development. In the porcine model, a reduction in the blastocyst formation rate after exposure to 30&#x202F;&#x03BC;g/mL PS-MPs during IVM and PA was observed (<xref ref-type="bibr" rid="ref42">42</xref>). In another study in the same species, using 100&#x202F;nm PS-MPs particles (<xref ref-type="bibr" rid="ref43">43</xref>), no differences were evidenced in the blastocyst rates, not only at concentrations tested in the present study (5 and 50&#x202F;&#x03BC;g/mL) but also at higher ones (100 and 200&#x202F;&#x03BC;g/mL). In terms of blastocyst quality, the present study did not highlight any difference between treated and control groups, whereas in previous studies in the porcine species (<xref ref-type="bibr" rid="ref42">42</xref>, <xref ref-type="bibr" rid="ref43">43</xref>), the blastocysts obtained displayed a reduced number of nuclei. Therefore, possible differences in the implantation rate would be interesting to investigate in the future in the ovine species. Moreover, with regard to <italic>in vivo</italic> studies, our data are in agreement with those of some authors reporting a lack of difference in the cleavage and blastocyst rate of PA oocytes among treated and untreated mice with 800&#x202F;nm PS-MPs (<xref ref-type="bibr" rid="ref45">45</xref>).</p>
<p>Overall, our results contribute to expanding our knowledge of the direct effects of PS-MPs on COC in a livestock animal model and confirm previous studies regarding their mechanisms of action based on the induction of oxidative stress and apoptosis. It is interesting to note that data on the effects of PS-MPs exposure during culture are controversial among different studies. This could be due to oocyte morpho-functional species-specific differences, as well as to the used culture conditions and methods. In some cases, differing results have been reported within the same species using identical PS-MP sizes and concentrations. Even in a controlled <italic>in vitro</italic> system, these effects may be partially attributable to endocrine-disrupting mechanisms, as PS-MPs have the potential to mimic natural hormones, antagonize their action, alter their metabolism, or modify the expression of specific receptors (<xref ref-type="bibr" rid="ref50">50</xref>). Further studies are necessary to explore this hypothesis.</p>
</sec>
<sec sec-type="conclusions" id="sec26">
<label>5</label>
<title>Conclusion</title>
<p>In conclusion, the present study provides new insights into the toxicity of PS-MPs on female reproduction, highlighting their negative effects on ovine COCs during IVM and providing insights into their action mechanisms. Our findings indicate that PS-MPs can penetrate and accumulate primarily in CCs, leading to their dysfunction, as evidenced by altered expression of genes related to oxidative stress and an increased rate of apoptosis. This, in turn, indirectly damages oocytes by reducing their quality and interfering with oocyte maturation and embryo development. Future research should focus on elucidating additional molecular pathways through which PS-MPs exert their toxic effects on fertility and reproduction and explore possible strategies to counteract them.</p>
</sec>
</body>
<back>
<sec sec-type="data-availability" id="sec27">
<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 sec-type="ethics-statement" id="sec28">
<title>Ethics statement</title>
<p>Ethical approval was not required for the study involving animals in accordance with the local legislation and institutional requirements because ethical review and approval were waived for this study due to the lack of animal testing on live or sacrificed animals for scientific purposes as the biological samples were obtained as slaughter waste for food purposes.</p>
</sec>
<sec sec-type="author-contributions" id="sec29">
<title>Author contributions</title>
<p>LT: Conceptualization, Formal analysis, Investigation, Writing &#x2013; original draft, Writing &#x2013; review &#x0026; editing. AP: Formal analysis, Investigation, Writing &#x2013; review &#x0026; editing. LB: Conceptualization, Investigation, Supervision, Writing &#x2013; review &#x0026; editing. AM: Investigation, Writing &#x2013; review &#x0026; editing. MCF: Writing &#x2013; review &#x0026; editing. PP: Investigation, Writing &#x2013; review &#x0026; editing. MEDA: Conceptualization, Supervision, Writing &#x2013; original draft, Writing &#x2013; review &#x0026; editing. NAM: Conceptualization, Formal analysis, Investigation, Supervision, Writing &#x2013; original draft, Writing &#x2013; review &#x0026; editing.</p>
</sec>
<ack>
<title>Acknowledgments</title>
<p>The authors gratefully acknowledge all personnel at Surace Carne s.r.l. Noci (Bari) for their collaboration in collecting the biological samples.</p>
</ack>
<sec sec-type="COI-statement" id="sec30">
<title>Conflict of interest</title>
<p>The author(s) declared that this work was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
<p>The reviewer RP declared a past co-authorship with the author AP to the handling editor.</p>
</sec>
<sec sec-type="ai-statement" id="sec31">
<title>Generative AI statement</title>
<p>The author(s) declared that Generative AI was not used in the creation of this manuscript.</p>
<p>Any alternative text (alt text) provided alongside figures in this article has been generated by Frontiers with the support of artificial intelligence and reasonable efforts have been made to ensure accuracy, including review by the authors wherever possible. If you identify any issues, please contact us.</p>
</sec>
<sec sec-type="disclaimer" id="sec32">
<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>
<ref-list>
<title>References</title>
<ref id="ref1"><label>1.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Aardema</surname><given-names>H</given-names></name> <name><surname>Dick Vethaak</surname><given-names>A</given-names></name> <name><surname>Kamstra</surname><given-names>JH</given-names></name> <name><surname>Legler</surname><given-names>J</given-names></name></person-group>. <article-title>Farm animals as a critical link between environmental and human health impacts of micro-and nanoplastics. Aardema et al.</article-title> <source>Microplastics Nanoplastics</source>. (<year>202</year>) <volume>4</volume>:<fpage>5</fpage>. doi: <pub-id pub-id-type="doi">10.1186/s43591-024-00082-w</pub-id></mixed-citation></ref>
<ref id="ref2"><label>2.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Mastrorocco</surname><given-names>A</given-names></name> <name><surname>Temerario</surname><given-names>L</given-names></name> <name><surname>Vurchio</surname><given-names>V</given-names></name> <name><surname>Cotecchia</surname><given-names>S</given-names></name> <name><surname>Martino</surname><given-names>NA</given-names></name> <name><surname>Dell'Aquila</surname><given-names>ME</given-names></name></person-group>. <article-title>In vitro toxicity of a DEHP and cadmium mixture on sheep cumulus-oocyte complexes</article-title>. <source>Int J Mol Sci</source>. (<year>2024</year>) <volume>26</volume>:<fpage>5</fpage>. doi: <pub-id pub-id-type="doi">10.3390/ijms26010005</pub-id>, <pub-id pub-id-type="pmid">39795862</pub-id></mixed-citation></ref>
<ref id="ref3"><label>3.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Dell'Aquila</surname><given-names>ME</given-names></name> <name><surname>Asif</surname><given-names>S</given-names></name> <name><surname>Temerario</surname><given-names>L</given-names></name> <name><surname>Mastrorocco</surname><given-names>A</given-names></name> <name><surname>Marzano</surname><given-names>G</given-names></name> <name><surname>Martino</surname><given-names>NA</given-names></name> <etal/></person-group>. <article-title>Ochratoxin a affects oocyte maturation and subsequent embryo developmental dynamics in the juvenile sheep model</article-title>. <source>Mycotoxin Res</source>. (<year>2021</year>) <volume>37</volume>:<fpage>23</fpage>&#x2013;<lpage>37</lpage>. doi: <pub-id pub-id-type="doi">10.1007/s12550-020-00410-y</pub-id>, <pub-id pub-id-type="pmid">32996062</pub-id></mixed-citation></ref>
<ref id="ref4"><label>4.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Wrzeci&#x0144;ska</surname><given-names>M</given-names></name> <name><surname>Kowalczyk</surname><given-names>A</given-names></name> <name><surname>Cwynar</surname><given-names>P</given-names></name> <name><surname>Czerniawska-Pi&#x0105;tkowska</surname><given-names>E</given-names></name></person-group>. <article-title>Disorders of the reproductive health of cattle as a response to exposure to toxic metals</article-title>. <source>Biology</source>. (<year>2021</year>) <volume>10</volume>:<fpage>882</fpage>. doi: <pub-id pub-id-type="doi">10.3390/biology10090882</pub-id>, <pub-id pub-id-type="pmid">34571759</pub-id></mixed-citation></ref>
<ref id="ref5"><label>5.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Canipari</surname><given-names>R</given-names></name> <name><surname>De Santis</surname><given-names>L</given-names></name> <name><surname>Cecconi</surname><given-names>S</given-names></name></person-group>. <article-title>Female fertility and environmental pollution</article-title>. <source>Int J Environ Res Public Health</source>. (<year>2020</year>) <volume>17</volume>:<fpage>8802</fpage>. doi: <pub-id pub-id-type="doi">10.3390/ijerph17238802</pub-id>, <pub-id pub-id-type="pmid">33256215</pub-id></mixed-citation></ref>
<ref id="ref6"><label>6.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Guvvala</surname><given-names>PR</given-names></name> <name><surname>Ravindra</surname><given-names>JP</given-names></name> <name><surname>Selvaraju</surname><given-names>S</given-names></name></person-group>. <article-title>Impact of environmental contaminants on reproductive health of male domestic ruminants: a review</article-title>. <source>Environ Sci Pollut Res Int</source>. (<year>2020</year>) <volume>27</volume>:<fpage>3819</fpage>&#x2013;<lpage>36</lpage>. doi: <pub-id pub-id-type="doi">10.1007/s11356-019-06980-4</pub-id>, <pub-id pub-id-type="pmid">31845245</pub-id></mixed-citation></ref>
<ref id="ref7"><label>7.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Chiang</surname><given-names>C</given-names></name> <name><surname>Mahalingam</surname><given-names>S</given-names></name> <name><surname>Flaws</surname><given-names>JA</given-names></name></person-group>. <article-title>Environmental contaminants affecting fertility and somatic health</article-title>. <source>Semin Reprod Med</source>. (<year>2017</year>) <volume>35</volume>:<fpage>241</fpage>&#x2013;<lpage>9</lpage>. doi: <pub-id pub-id-type="doi">10.1055/s-0037-1603569</pub-id>, <pub-id pub-id-type="pmid">28658707</pub-id></mixed-citation></ref>
<ref id="ref8"><label>8.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Martino</surname><given-names>NA</given-names></name> <name><surname>Marzano</surname><given-names>G</given-names></name> <name><surname>Mangiacotti</surname><given-names>M</given-names></name> <name><surname>Miedico</surname><given-names>O</given-names></name> <name><surname>Sardanelli</surname><given-names>AM</given-names></name> <name><surname>Gnoni</surname><given-names>A</given-names></name> <etal/></person-group>. <article-title>Exposure to cadmium during in vitro maturation at environmental nanomolar levels impairs oocyte fertilization through oxidative damage: a large animal model study</article-title>. <source>Reprod Toxicol</source>. (<year>2017</year>) <volume>69</volume>:<fpage>132</fpage>&#x2013;<lpage>45</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.reprotox.2017.02.005</pub-id>, <pub-id pub-id-type="pmid">28188904</pub-id></mixed-citation></ref>
<ref id="ref9"><label>9.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Pause</surname><given-names>FC</given-names></name> <name><surname>Baufeld</surname><given-names>A</given-names></name> <name><surname>Urli</surname><given-names>S</given-names></name> <name><surname>Crociati</surname><given-names>M</given-names></name> <name><surname>Stradaioli</surname><given-names>G</given-names></name> <name><surname>Vanselow</surname><given-names>J</given-names></name> <etal/></person-group>. <article-title>Exploring the influence of polystyrene-nanoplastics on two distinct in vitro systems in farm animals: a pilot study</article-title>. <source>Sci Total Environ</source>. (<year>2025</year>) <volume>976</volume>:<fpage>179378</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.scitotenv.2025.179378</pub-id>, <pub-id pub-id-type="pmid">40209587</pub-id></mixed-citation></ref>
<ref id="ref10"><label>10.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Peng</surname><given-names>Y</given-names></name> <name><surname>He</surname><given-names>Q</given-names></name></person-group>. <article-title>Reproductive toxicity and related mechanisms of micro(nano)plastics in terrestrial mammals: review of current evidence</article-title>. <source>Ecotoxicol Environ Saf</source>. (<year>2024</year>) <volume>279</volume>:<fpage>116505</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.ecoenv.2024.116505</pub-id>, <pub-id pub-id-type="pmid">38810287</pub-id></mixed-citation></ref>
<ref id="ref11"><label>11.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Geng</surname><given-names>Y</given-names></name> <name><surname>Liu</surname><given-names>Z</given-names></name> <name><surname>Hu</surname><given-names>R</given-names></name> <name><surname>Huang</surname><given-names>Y</given-names></name> <name><surname>Li</surname><given-names>F</given-names></name> <name><surname>Ma</surname><given-names>W</given-names></name> <etal/></person-group>. <article-title>Toxicity of microplastics and nanoplastics: invisible killers of female fertility and offspring health</article-title>. <source>Front Physiol</source>. (<year>2023</year>) <volume>14</volume>:<fpage>1254886</fpage>. doi: <pub-id pub-id-type="doi">10.3389/fphys.2023.1254886</pub-id>, <pub-id pub-id-type="pmid">37700763</pub-id></mixed-citation></ref>
<ref id="ref12"><label>12.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Song</surname><given-names>X</given-names></name> <name><surname>Du</surname><given-names>L</given-names></name> <name><surname>Sima</surname><given-names>L</given-names></name> <name><surname>Zou</surname><given-names>D</given-names></name> <name><surname>Qiu</surname><given-names>X</given-names></name></person-group>. <article-title>Effects of micro(nano)plastics on the reproductive system: a review</article-title>. <source>Chemosphere</source>. (<year>2023</year>) <volume>336</volume>:<fpage>139138</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.chemosphere.2023.139138</pub-id>, <pub-id pub-id-type="pmid">37285987</pub-id></mixed-citation></ref>
<ref id="ref13"><label>13.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Yang</surname><given-names>S</given-names></name> <name><surname>Li</surname><given-names>M</given-names></name> <name><surname>Kong</surname><given-names>RYC</given-names></name> <name><surname>Li</surname><given-names>L</given-names></name> <name><surname>Li</surname><given-names>R</given-names></name> <name><surname>Chen</surname><given-names>J</given-names></name> <etal/></person-group>. <article-title>Reproductive toxicity of micro- and nanoplastics</article-title>. <source>Environ Int</source>. (<year>2023</year>) <volume>177</volume>:<fpage>108002</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.envint.2023.108002</pub-id>, <pub-id pub-id-type="pmid">37276763</pub-id></mixed-citation></ref>
<ref id="ref14"><label>14.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Yang</surname><given-names>J</given-names></name> <name><surname>Kamstra</surname><given-names>J</given-names></name> <name><surname>Legler</surname><given-names>J</given-names></name> <name><surname>Aardema</surname><given-names>H</given-names></name></person-group>. <article-title>The impact of microplastics on female reproduction and early life</article-title>. <source>Anim Reprod</source>. (<year>2023</year>) <volume>20</volume>:<fpage>e20230037</fpage>. doi: <pub-id pub-id-type="doi">10.1590/1984-3143-AR2023-0037</pub-id>, <pub-id pub-id-type="pmid">37547566</pub-id></mixed-citation></ref>
<ref id="ref15"><label>15.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Chamas</surname><given-names>A</given-names></name> <name><surname>Moon</surname><given-names>H</given-names></name> <name><surname>Zheng</surname><given-names>J</given-names></name> <name><surname>Qiu</surname><given-names>Y</given-names></name> <name><surname>Tabassum</surname><given-names>T</given-names></name> <name><surname>Jang</surname><given-names>JH</given-names></name> <etal/></person-group>. <article-title>Degradation rates of plastics in the environment</article-title>. <source>ACS Sustain Chem Eng</source>. (<year>2020</year>) <volume>8</volume>:<fpage>3494</fpage>&#x2013;<lpage>511</lpage>. doi: <pub-id pub-id-type="doi">10.1021/acssuschemeng.9b06635</pub-id></mixed-citation></ref>
<ref id="ref16"><label>16.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Hartmann</surname><given-names>NB</given-names></name> <name><surname>H&#x00FC;ffer</surname><given-names>T</given-names></name> <name><surname>Thompson</surname><given-names>RC</given-names></name> <name><surname>Hassell&#x00F6;v</surname><given-names>M</given-names></name> <name><surname>Verschoor</surname><given-names>A</given-names></name> <name><surname>Daugaard</surname><given-names>AE</given-names></name> <etal/></person-group>. <article-title>Are we speaking the same language? Recommendations for a definition and categorization framework for plastic debris</article-title>. <source>Environ Sci Technol</source>. (<year>2019</year>) <volume>53</volume>:<fpage>1039</fpage>&#x2013;<lpage>47</lpage>. doi: <pub-id pub-id-type="doi">10.1021/acs.est.8b05297</pub-id>, <pub-id pub-id-type="pmid">30608663</pub-id></mixed-citation></ref>
<ref id="ref17"><label>17.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Gigault</surname><given-names>J</given-names></name> <name><surname>Halle</surname><given-names>AT</given-names></name> <name><surname>Baudrimont</surname><given-names>M</given-names></name> <name><surname>Pascal</surname><given-names>PY</given-names></name> <name><surname>Gauffre</surname><given-names>F</given-names></name> <name><surname>Phi</surname><given-names>TL</given-names></name> <etal/></person-group>. <article-title>Current opinion: what is a nanoplastic?</article-title> <source>Environ Pollut</source>. (<year>2018</year>) <volume>235</volume>:<fpage>1030</fpage>&#x2013;<lpage>4</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.envpol.2018.01.024</pub-id>, <pub-id pub-id-type="pmid">29370948</pub-id></mixed-citation></ref>
<ref id="ref18"><label>18.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Afreen</surname><given-names>V</given-names></name> <name><surname>Hashmi</surname><given-names>K</given-names></name> <name><surname>Nasir</surname><given-names>R</given-names></name> <name><surname>Saleem</surname><given-names>A</given-names></name> <name><surname>Khan</surname><given-names>MI</given-names></name> <name><surname>Akhtar</surname><given-names>MF</given-names></name></person-group>. <article-title>Adverse health effects and mechanisms of microplastics on female reproductive system: a descriptive review</article-title>. <source>Environ Sci Pollut Res Int</source>. (<year>2023</year>) <volume>30</volume>:<fpage>76283</fpage>&#x2013;<lpage>96</lpage>. doi: <pub-id pub-id-type="doi">10.1007/s11356-023-27930-1</pub-id>, <pub-id pub-id-type="pmid">37247153</pub-id></mixed-citation></ref>
<ref id="ref19"><label>19.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Ferrante</surname><given-names>MC</given-names></name> <name><surname>Monnolo</surname><given-names>A</given-names></name> <name><surname>Del Piano</surname><given-names>F</given-names></name> <name><surname>Mattace Raso</surname><given-names>G</given-names></name> <name><surname>Meli</surname><given-names>R</given-names></name></person-group>. <article-title>The pressing issue of Micro- and Nanoplastic contamination: profiling the reproductive alterations mediated by oxidative stress</article-title>. <source>Antioxidants</source>. (<year>2022</year>) <volume>11</volume>:<fpage>193</fpage>. doi: <pub-id pub-id-type="doi">10.3390/antiox11020193</pub-id>, <pub-id pub-id-type="pmid">35204076</pub-id></mixed-citation></ref>
<ref id="ref20"><label>20.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Adhikari</surname><given-names>M</given-names></name> <name><surname>Biswas</surname><given-names>C</given-names></name> <name><surname>Mazumdar</surname><given-names>P</given-names></name> <name><surname>Sarkar</surname><given-names>S</given-names></name> <name><surname>Pramanick</surname><given-names>K</given-names></name></person-group>. <article-title>Evaluating the potential of daily intake of polystyrene microplastics via drinking water in inducing PCOS and its ovarian fibrosis progression using female zebrafish</article-title>. <source>NanoImpact</source>. (<year>2024</year>) <volume>34</volume>:<fpage>100507</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.impact.2024.100507</pub-id>, <pub-id pub-id-type="pmid">38663500</pub-id></mixed-citation></ref>
<ref id="ref21"><label>21.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Liu</surname><given-names>H</given-names></name> <name><surname>Li</surname><given-names>H</given-names></name> <name><surname>Liu</surname><given-names>Y</given-names></name> <name><surname>Zhao</surname><given-names>H</given-names></name> <name><surname>Peng</surname><given-names>R</given-names></name></person-group>. <article-title>Toxic effects of microplastic and nanoplastic on the reproduction of teleost fish in aquatic environments</article-title>. <source>Environ Sci Pollut Res Int</source>. (<year>2024</year>) <volume>31</volume>:<fpage>62530</fpage>&#x2013;<lpage>48</lpage>. doi: <pub-id pub-id-type="doi">10.1007/s11356-024-35434-9</pub-id>, <pub-id pub-id-type="pmid">39467868</pub-id></mixed-citation></ref>
<ref id="ref22"><label>22.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Sussarellu</surname><given-names>R</given-names></name> <name><surname>Suquet</surname><given-names>M</given-names></name> <name><surname>Thomas</surname><given-names>Y</given-names></name> <name><surname>Lambert</surname><given-names>C</given-names></name> <name><surname>Fabioux</surname><given-names>C</given-names></name> <name><surname>Pernet</surname><given-names>ME</given-names></name> <etal/></person-group>. <article-title>Oyster reproduction is affected by exposure to polystyrene microplastics</article-title>. <source>Proc Natl Acad Sci USA</source>. (<year>2016</year>) <volume>113</volume>:<fpage>2430</fpage>&#x2013;<lpage>5</lpage>. doi: <pub-id pub-id-type="doi">10.1073/pnas.1519019113</pub-id>, <pub-id pub-id-type="pmid">26831072</pub-id></mixed-citation></ref>
<ref id="ref23"><label>23.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Temerario</surname><given-names>L</given-names></name> <name><surname>Martino</surname><given-names>NA</given-names></name> <name><surname>Bennink</surname><given-names>M</given-names></name> <name><surname>de Wit</surname><given-names>A</given-names></name> <name><surname>Hiemstra</surname><given-names>SJ</given-names></name> <name><surname>Dell'Aquila</surname><given-names>ME</given-names></name> <etal/></person-group>. <article-title>Effects of Cryoprotectant concentration and exposure time during Vitrification of immature pre-pubertal lamb cumulus-oocyte complexes on nuclear and cytoplasmic maturation</article-title>. <source>Animals</source>. (<year>2024</year>) <volume>14</volume>:<fpage>2351</fpage>. doi: <pub-id pub-id-type="doi">10.3390/ani14162351</pub-id>, <pub-id pub-id-type="pmid">39199884</pub-id></mixed-citation></ref>
<ref id="ref24"><label>24.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Temerario</surname><given-names>L</given-names></name> <name><surname>Monaco</surname><given-names>D</given-names></name> <name><surname>Mastrorocco</surname><given-names>A</given-names></name> <name><surname>Martino</surname><given-names>NA</given-names></name> <name><surname>Cseh</surname><given-names>S</given-names></name> <name><surname>Lacalandra</surname><given-names>GM</given-names></name> <etal/></person-group>. <article-title>New strategies for conservation of gentile di Puglia sheep breed, an autochthonous capital of millennial tradition in southern Italy</article-title>. <source>Animals</source>. (<year>2023</year>) <volume>13</volume>:<fpage>2371</fpage>. doi: <pub-id pub-id-type="doi">10.3390/ani13142371</pub-id>, <pub-id pub-id-type="pmid">37508148</pub-id></mixed-citation></ref>
<ref id="ref25"><label>25.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Martino</surname><given-names>NA</given-names></name> <name><surname>Picardi</surname><given-names>E</given-names></name> <name><surname>Ciani</surname><given-names>E</given-names></name> <name><surname>D'Erchia</surname><given-names>AM</given-names></name> <name><surname>Bogliolo</surname><given-names>L</given-names></name> <name><surname>Ariu</surname><given-names>F</given-names></name> <etal/></person-group>. <article-title>Cumulus cell transcriptome after cumulus-oocyte complex exposure to nanomolar cadmium in an in vitro animal model of prepubertal and adult age</article-title>. <source>Biology</source>. (<year>2023</year>) <volume>12</volume>:<fpage>249</fpage>. doi: <pub-id pub-id-type="doi">10.3390/biology12020249</pub-id>, <pub-id pub-id-type="pmid">36829526</pub-id></mixed-citation></ref>
<ref id="ref26"><label>26.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Majtnerov&#x00E1;</surname><given-names>P</given-names></name> <name><surname>Rou&#x0161;ar</surname><given-names>T</given-names></name></person-group>. <article-title>An overview of apoptosis assays detecting DNA fragmentation</article-title>. <source>Mol Biol Rep</source>. (<year>2018</year>) <volume>45</volume>:<fpage>1469</fpage>&#x2013;<lpage>78</lpage>. doi: <pub-id pub-id-type="doi">10.1007/s11033-018-4258-9</pub-id>, <pub-id pub-id-type="pmid">30022463</pub-id></mixed-citation></ref>
<ref id="ref27"><label>27.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Mastrorocco</surname><given-names>A</given-names></name> <name><surname>Martino</surname><given-names>NA</given-names></name> <name><surname>Marzano</surname><given-names>G</given-names></name> <name><surname>Lacalandra</surname><given-names>GM</given-names></name> <name><surname>Ciani</surname><given-names>E</given-names></name> <name><surname>Roelen</surname><given-names>BAJ</given-names></name> <etal/></person-group>. <article-title>The mycotoxin beauvericin induces oocyte mitochondrial dysfunction and affects embryo development in the juvenile sheep</article-title>. <source>Mol Reprod Dev</source>. (<year>2019</year>) <volume>86</volume>:<fpage>1430</fpage>&#x2013;<lpage>43</lpage>. doi: <pub-id pub-id-type="doi">10.1002/mrd.23256</pub-id>, <pub-id pub-id-type="pmid">31410935</pub-id></mixed-citation></ref>
<ref id="ref28"><label>28.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Martino</surname><given-names>NA</given-names></name> <name><surname>Lacalandra</surname><given-names>GM</given-names></name> <name><surname>Filioli Uranio</surname><given-names>M</given-names></name> <name><surname>Ambruosi</surname><given-names>B</given-names></name> <name><surname>Caira</surname><given-names>M</given-names></name> <name><surname>Silvestre</surname><given-names>F</given-names></name> <etal/></person-group>. <article-title>Oocyte mitochondrial bioenergy potential and oxidative stress: within&#x2212;/between-subject, in vivo versus in vitro maturation, and age-related variations in a sheep model</article-title>. <source>Fertil Steril</source>. (<year>2012</year>) <volume>97</volume>:<fpage>720</fpage>&#x2013;<lpage>8.e1</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.fertnstert.2011.12.014</pub-id></mixed-citation></ref>
<ref id="ref29"><label>29.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Yang</surname><given-names>HW</given-names></name> <name><surname>Hwang</surname><given-names>KJ</given-names></name> <name><surname>Kwon</surname><given-names>HC</given-names></name> <name><surname>Kim</surname><given-names>HS</given-names></name> <name><surname>Choi</surname><given-names>KW</given-names></name> <name><surname>Oh</surname><given-names>KS</given-names></name></person-group>. <article-title>Detection of reactive oxygen species (ROS) and apoptosis in human fragmented embryos</article-title>. <source>Hum Reprod</source>. (<year>1998</year>) <volume>13</volume>:<fpage>998</fpage>&#x2013;<lpage>1002</lpage>. doi: <pub-id pub-id-type="doi">10.1093/humrep/13.4.998</pub-id>, <pub-id pub-id-type="pmid">9619561</pub-id></mixed-citation></ref>
<ref id="ref30"><label>30.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Manders</surname><given-names>EMM</given-names></name> <name><surname>Verbeek</surname><given-names>FJ</given-names></name> <name><surname>Aten</surname><given-names>JA</given-names></name></person-group>. <article-title>Measurement of co-localization of objects in dual-colour confocal images</article-title>. <source>J Microsc</source>. (<year>1993</year>) <volume>169</volume>:<fpage>375</fpage>&#x2013;<lpage>82</lpage>. doi: <pub-id pub-id-type="doi">10.1111/j.1365-2818.1993.tb03313.x</pub-id>, <pub-id pub-id-type="pmid">33930978</pub-id></mixed-citation></ref>
<ref id="ref31"><label>31.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Piras</surname><given-names>AR</given-names></name> <name><surname>Ariu</surname><given-names>F</given-names></name> <name><surname>Maltana</surname><given-names>A</given-names></name> <name><surname>Leoni</surname><given-names>GG</given-names></name> <name><surname>Martino</surname><given-names>NA</given-names></name> <name><surname>Mastrorocco</surname><given-names>A</given-names></name> <etal/></person-group>. <article-title>Protective effect of resveratrol against cadmium-induced toxicity on ovine oocyte in vitro maturation and fertilization</article-title>. <source>J Anim Sci Biotechnol</source>. (<year>2022</year>) <volume>13</volume>:<fpage>83</fpage>. doi: <pub-id pub-id-type="doi">10.1186/s40104-022-00731-1</pub-id>, <pub-id pub-id-type="pmid">35864507</pub-id></mixed-citation></ref>
<ref id="ref32"><label>32.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Podda</surname><given-names>A</given-names></name> <name><surname>Duj&#x00ED;&#x010D;kov&#x00E1;</surname><given-names>L</given-names></name> <name><surname>Ariu</surname><given-names>F</given-names></name> <name><surname>Leoni</surname><given-names>GG</given-names></name> <name><surname>Izquierdo</surname><given-names>D</given-names></name> <name><surname>Paramio</surname><given-names>MT</given-names></name> <etal/></person-group>. <article-title>Effect of liquid marble 3D culture system on in vitro maturation and embryo development of prepubertal goat oocytes</article-title>. <source>Animals</source>. (<year>2025</year>) <volume>15</volume>:<fpage>188</fpage>. doi: <pub-id pub-id-type="doi">10.3390/ani15020188</pub-id>, <pub-id pub-id-type="pmid">39858188</pub-id></mixed-citation></ref>
<ref id="ref33"><label>33.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Zhang</surname><given-names>R</given-names></name> <name><surname>Wang</surname><given-names>M</given-names></name> <name><surname>Chen</surname><given-names>X</given-names></name> <name><surname>Yang</surname><given-names>C</given-names></name> <name><surname>Wu</surname><given-names>L</given-names></name></person-group>. <article-title>Combined toxicity of microplastics and cadmium on the zebrafish embryos (<italic>Danio rerio</italic>)</article-title>. <source>Sci Total Environ</source>. (<year>2020</year>) <volume>743</volume>:<fpage>140638</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.scitotenv.2020.140638</pub-id>, <pub-id pub-id-type="pmid">32679492</pub-id></mixed-citation></ref>
<ref id="ref34"><label>34.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Leslie</surname><given-names>HA</given-names></name> <name><surname>van Velzen</surname><given-names>MJM</given-names></name> <name><surname>Brandsma</surname><given-names>SH</given-names></name> <name><surname>Vethaak</surname><given-names>AD</given-names></name> <name><surname>Garcia-Vallejo</surname><given-names>JJ</given-names></name> <name><surname>Lamoree</surname><given-names>MH</given-names></name></person-group>. <article-title>Discovery and quantification of plastic particle pollution in human blood</article-title>. <source>Environ Int</source>. (<year>2022</year>) <volume>163</volume>:<fpage>107199</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.envint.2022.107199</pub-id></mixed-citation></ref>
<ref id="ref35"><label>35.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Zurub</surname><given-names>RE</given-names></name> <name><surname>Cariaco</surname><given-names>Y</given-names></name> <name><surname>Wade</surname><given-names>MG</given-names></name> <name><surname>Bainbridge</surname><given-names>SA</given-names></name></person-group>. <article-title>Microplastics exposure: implications for human fertility, pregnancy and child health</article-title>. <source>Front Endocrinol</source>. (<year>2024</year>) <volume>14</volume>:<fpage>1330396</fpage>. doi: <pub-id pub-id-type="doi">10.3389/fendo.2023.1330396</pub-id>, <pub-id pub-id-type="pmid">38239985</pub-id></mixed-citation></ref>
<ref id="ref36"><label>36.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Xue</surname><given-names>Y</given-names></name> <name><surname>Cheng</surname><given-names>X</given-names></name> <name><surname>Ma</surname><given-names>ZQ</given-names></name> <name><surname>Wang</surname><given-names>HP</given-names></name> <name><surname>Zhou</surname><given-names>C</given-names></name> <name><surname>Li</surname><given-names>J</given-names></name> <etal/></person-group>. <article-title>Polystyrene nanoplastics induce apoptosis, autophagy, and steroidogenesis disruption in granulosa cells to reduce oocyte quality and fertility by inhibiting the PI3K/AKT pathway in female mice</article-title>. <source>J Nanobiotechnology</source>. (<year>2024</year>) <volume>22</volume>:<fpage>460</fpage>. doi: <pub-id pub-id-type="doi">10.1186/s12951-024-02735-7</pub-id>, <pub-id pub-id-type="pmid">39090717</pub-id></mixed-citation></ref>
<ref id="ref37"><label>37.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Merlo</surname><given-names>B</given-names></name> <name><surname>Volsa</surname><given-names>AM</given-names></name> <name><surname>Tovar</surname><given-names>L</given-names></name> <name><surname>Gaiani</surname><given-names>M</given-names></name> <name><surname>Gugole</surname><given-names>PM</given-names></name> <name><surname>Attolini</surname><given-names>E</given-names></name> <etal/></person-group>. <article-title>Effects of polystyrene nanoparticles on bovine oocyte in vitro maturation</article-title>. <source>Theriogenology</source>. (<year>2025</year>) <volume>244</volume>:<fpage>117482</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.theriogenology.2025.117482</pub-id>, <pub-id pub-id-type="pmid">40381591</pub-id></mixed-citation></ref>
<ref id="ref38"><label>38.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>An</surname><given-names>R</given-names></name> <name><surname>Wang</surname><given-names>X</given-names></name> <name><surname>Yang</surname><given-names>L</given-names></name> <name><surname>Zhang</surname><given-names>J</given-names></name> <name><surname>Wang</surname><given-names>N</given-names></name> <name><surname>Xu</surname><given-names>F</given-names></name> <etal/></person-group>. <article-title>Polystyrene microplastics cause granulosa cells apoptosis and fibrosis in ovary through oxidative stress in rats</article-title>. <source>Toxicology</source>. (<year>2021</year>) <volume>449</volume>:<fpage>152665</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.tox.2020.152665</pub-id>, <pub-id pub-id-type="pmid">33359712</pub-id></mixed-citation></ref>
<ref id="ref39"><label>39.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Hou</surname><given-names>J</given-names></name> <name><surname>Lei</surname><given-names>Z</given-names></name> <name><surname>Cui</surname><given-names>L</given-names></name> <name><surname>Hou</surname><given-names>Y</given-names></name> <name><surname>Yang</surname><given-names>L</given-names></name> <name><surname>An</surname><given-names>R</given-names></name> <etal/></person-group>. <article-title>Polystyrene microplastics lead to pyroptosis and apoptosis of ovarian granulosa cells via NLRP3/Caspase-1 signaling pathway in rats</article-title>. <source>Ecotoxicol Environ Saf</source>. (<year>2021</year>) <volume>212</volume>:<fpage>112012</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.ecoenv.2021.112012</pub-id>, <pub-id pub-id-type="pmid">33550074</pub-id></mixed-citation></ref>
<ref id="ref40"><label>40.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Turathum</surname><given-names>B</given-names></name> <name><surname>Gao</surname><given-names>EM</given-names></name> <name><surname>Chian</surname><given-names>RC</given-names></name></person-group>. <article-title>The function of cumulus cells in oocyte growth and maturation and in subsequent ovulation and fertilization</article-title>. <source>Cells</source>. (<year>2021</year>) <volume>10</volume>:<fpage>2292</fpage>. doi: <pub-id pub-id-type="doi">10.3390/cells10092292</pub-id>, <pub-id pub-id-type="pmid">34571941</pub-id></mixed-citation></ref>
<ref id="ref41"><label>41.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Zhang</surname><given-names>J</given-names></name> <name><surname>Hu</surname><given-names>H</given-names></name> <name><surname>Zhu</surname><given-names>Y</given-names></name> <name><surname>Xin</surname><given-names>X</given-names></name> <name><surname>Jin</surname><given-names>Y</given-names></name> <name><surname>Zhao</surname><given-names>Q</given-names></name> <etal/></person-group>. <article-title>Polystyrene/polylactic acid microplastics impair transzonal projections and oocyte maturation via gut microbiota-mediated lipoprotein lipase inhibition</article-title>. <source>J Hazard Mater</source>. (<year>2025</year>) <volume>496</volume>:<fpage>139475</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.jhazmat.2025.139475</pub-id>, <pub-id pub-id-type="pmid">40784117</pub-id></mixed-citation></ref>
<ref id="ref42"><label>42.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Huang</surname><given-names>HM</given-names></name> <name><surname>Peng</surname><given-names>HL</given-names></name> <name><surname>Huang</surname><given-names>CM</given-names></name> <name><surname>Zhang</surname><given-names>JT</given-names></name> <name><surname>Li</surname><given-names>YH</given-names></name> <name><surname>Lin</surname><given-names>ZL</given-names></name> <etal/></person-group>. <article-title>Melatonin alleviates the damage of polystyrene microplastics to porcine oocytes by reducing oxidative stress and mitochondrial damage, and regulating autophagy and apoptosis levels</article-title>. <source>Animals</source>. (<year>2025</year>) <volume>15</volume>:<fpage>3163</fpage>. doi: <pub-id pub-id-type="doi">10.3390/ani15213163</pub-id>, <pub-id pub-id-type="pmid">41227494</pub-id></mixed-citation></ref>
<ref id="ref43"><label>43.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Spinaci</surname><given-names>M</given-names></name> <name><surname>Dindo</surname><given-names>S</given-names></name> <name><surname>Govoni</surname><given-names>N</given-names></name> <name><surname>Tovar</surname><given-names>L</given-names></name> <name><surname>Volsa</surname><given-names>AM</given-names></name> <name><surname>Cappannari</surname><given-names>C</given-names></name> <etal/></person-group>. <article-title>Effect of polystyrene nanoplastics on in vitro maturation of pig cumulus-encosed oocytes</article-title>. <source>Res Vet Sci</source>. (<year>2025</year>) <volume>197</volume>:<fpage>105949</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.rvsc.2025.105949</pub-id>, <pub-id pub-id-type="pmid">41223719</pub-id></mixed-citation></ref>
<ref id="ref44"><label>44.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Cui</surname><given-names>Z</given-names></name> <name><surname>Zhang</surname><given-names>J</given-names></name> <name><surname>Zhang</surname><given-names>J</given-names></name> <name><surname>Zhong</surname><given-names>J</given-names></name> <name><surname>Wu</surname><given-names>J</given-names></name> <name><surname>Miao</surname><given-names>Y</given-names></name> <etal/></person-group>. <article-title>Microplastics (MPs) exposure impairs porcine oocyte quality by triggering oxidative stress-directed DNA damage and apoptosis with metabolomic alterations</article-title>. <source>Ecotoxicol Environ Saf</source>. (<year>2025</year>) <volume>300</volume>:<fpage>118461</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.ecoenv.2025.118461</pub-id>, <pub-id pub-id-type="pmid">40472692</pub-id></mixed-citation></ref>
<ref id="ref45"><label>45.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Liu</surname><given-names>Z</given-names></name> <name><surname>Zhuan</surname><given-names>Q</given-names></name> <name><surname>Zhang</surname><given-names>L</given-names></name> <name><surname>Meng</surname><given-names>L</given-names></name> <name><surname>Fu</surname><given-names>X</given-names></name> <name><surname>Hou</surname><given-names>Y</given-names></name></person-group>. <article-title>Polystyrene microplastics induced female reproductive toxicity in mice</article-title>. <source>J Hazard Mater</source>. (<year>2022</year>) <volume>424</volume>:<fpage>127629</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.jhazmat.2021.127629</pub-id>, <pub-id pub-id-type="pmid">34740508</pub-id></mixed-citation></ref>
<ref id="ref46"><label>46.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Coticchio</surname><given-names>G</given-names></name> <name><surname>Dal Canto</surname><given-names>M</given-names></name> <name><surname>Mignini Renzini</surname><given-names>M</given-names></name> <name><surname>Guglielmo</surname><given-names>MC</given-names></name> <name><surname>Brambillasca</surname><given-names>F</given-names></name> <name><surname>Turchi</surname><given-names>D</given-names></name> <etal/></person-group>. <article-title>Oocyte maturation: gamete-somatic cells interactions, meiotic resumption, cytoskeletal dynamics and cytoplasmic reorganization</article-title>. <source>Hum Reprod Update</source>. (<year>2015</year>) <volume>21</volume>:<fpage>427</fpage>&#x2013;<lpage>54</lpage>. doi: <pub-id pub-id-type="doi">10.1093/humupd/dmv011</pub-id>, <pub-id pub-id-type="pmid">25744083</pub-id></mixed-citation></ref>
<ref id="ref47"><label>47.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Gualtieri</surname><given-names>R</given-names></name> <name><surname>Kalthur</surname><given-names>G</given-names></name> <name><surname>Barbato</surname><given-names>V</given-names></name> <name><surname>Di Nardo</surname><given-names>M</given-names></name> <name><surname>Adiga</surname><given-names>SK</given-names></name> <name><surname>Talevi</surname><given-names>R</given-names></name></person-group>. <article-title>Mitochondrial dysfunction and oxidative stress caused by cryopreservation in reproductive cells</article-title>. <source>Antioxidants</source>. (<year>2021</year>) <volume>10</volume>:<fpage>337</fpage>. doi: <pub-id pub-id-type="doi">10.3390/antiox10030337</pub-id>, <pub-id pub-id-type="pmid">33668300</pub-id></mixed-citation></ref>
<ref id="ref48"><label>48.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Mateo-Otero</surname><given-names>Y</given-names></name> <name><surname>Yeste</surname><given-names>M</given-names></name> <name><surname>Damato</surname><given-names>A</given-names></name> <name><surname>Giaretta</surname><given-names>E</given-names></name></person-group>. <article-title>Cryopreservation and oxidative stress in porcine oocytes</article-title>. <source>Res Vet Sci</source>. (<year>2021</year>) <volume>135</volume>:<fpage>20</fpage>&#x2013;<lpage>6</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.rvsc.2020.12.024</pub-id>, <pub-id pub-id-type="pmid">33418187</pub-id></mixed-citation></ref>
<ref id="ref49"><label>49.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>van der Reest</surname><given-names>J</given-names></name> <name><surname>Nardini Cecchino</surname><given-names>G</given-names></name> <name><surname>Haigis</surname><given-names>MC</given-names></name> <name><surname>Kordowitzki</surname><given-names>P</given-names></name></person-group>. <article-title>Mitochondria: their relevance during oocyte ageing</article-title>. <source>Ageing Res Rev</source>. (<year>2021</year>) <volume>70</volume>:<fpage>101378</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.arr.2021.101378</pub-id>, <pub-id pub-id-type="pmid">34091076</pub-id></mixed-citation></ref>
<ref id="ref50"><label>50.</label><mixed-citation publication-type="journal"><person-group person-group-type="author"><name><surname>Campanale</surname><given-names>C</given-names></name> <name><surname>Massarelli</surname><given-names>C</given-names></name> <name><surname>Savino</surname><given-names>I</given-names></name> <name><surname>Locaputo</surname><given-names>V</given-names></name> <name><surname>Uricchio</surname><given-names>VF</given-names></name></person-group>. <article-title>A detailed review study on potential effects of microplastics and additives of concern on human health</article-title>. <source>Int J Environ Res Public Health</source>. (<year>2020</year>) <volume>17</volume>:<fpage>1212</fpage>. doi: <pub-id pub-id-type="doi">10.3390/ijerph17041212</pub-id>, <pub-id pub-id-type="pmid">32069998</pub-id></mixed-citation></ref>
</ref-list>
<fn-group>
<fn fn-type="custom" custom-type="edited-by" id="fn0001">
<p>Edited by: <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/1461883/overview">Paola Toschi</ext-link>, University of Turin, Italy</p>
</fn>
<fn fn-type="custom" custom-type="reviewed-by" id="fn0002">
<p>Reviewed by: <ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/1143816/overview">Rolando Pasquariello</ext-link>, University of Milan, Italy</p>
<p><ext-link ext-link-type="uri" xlink:href="https://loop.frontiersin.org/people/3224302/overview">Regina Lucia Dos Santos Silva</ext-link>, Federal University of Piau&#x00ED;, Brazil</p>
</fn>
</fn-group>
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