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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Ecol. Evol.</journal-id>
<journal-title>Frontiers in Ecology and Evolution</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Ecol. Evol.</abbrev-journal-title>
<issn pub-type="epub">2296-701X</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fevo.2022.850612</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Ecology and Evolution</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Negative Effects on Neurogenesis, Ovariogenesis, and Fitness in Sea Turtle Hatchlings Associated to <italic>ex situ</italic> Incubation Management</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name><surname>Unda-D&#x00ED;az</surname> <given-names>Nancy M.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>Phillips-Farf&#x00E1;n</surname> <given-names>Bryan V.</given-names></name>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/181317/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Nava</surname> <given-names>Hector</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
</contrib>
<contrib contrib-type="author">
<name><surname>Lopez-Toledo</surname> <given-names>Leonel</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/765491/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Murata</surname> <given-names>Chiharu</given-names></name>
<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/877026/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Lajud</surname> <given-names>Naima</given-names></name>
<xref ref-type="aff" rid="aff4"><sup>4</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/191688/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Herrera-Vargas</surname> <given-names>Ma. Antonia</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/455431/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Arreola Camacho</surname> <given-names>Claudia A.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/1630915/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Torner</surname> <given-names>Luz</given-names></name>
<xref ref-type="aff" rid="aff4"><sup>4</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/168430/overview"/>
</contrib>
<contrib contrib-type="author" corresp="yes">
<name><surname>Fuentes-Far&#x00ED;as</surname> <given-names>Alma L.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="corresp" rid="c002"><sup>&#x002A;</sup></xref>
</contrib>
<contrib contrib-type="author" corresp="yes">
<name><surname>Mel&#x00E9;ndez-Herrera</surname> <given-names>Esperanza</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="http://loop.frontiersin.org/people/1321554/overview"/>
</contrib>
</contrib-group>
<aff id="aff1"><sup>1</sup><institution>Departamento de Zoolog&#x00ED;a, Instituto de Investigaciones sobre los Recursos Naturales, Universidad Michoacana de San Nicol&#x00E1;s de Hidalgo</institution>, <addr-line>Morelia</addr-line>, <country>Mexico</country></aff>
<aff id="aff2"><sup>2</sup><institution>Laboratorio de Nutrici&#x00F3;n Experimental, Instituto Nacional de Pediatr&#x00ED;a</institution>, <addr-line>Mexico City</addr-line>, <country>Mexico</country></aff>
<aff id="aff3"><sup>3</sup><institution>Departamento de Metodolog&#x00ED;a de la Investigaci&#x00F3;n, Instituto Nacional de Pediatr&#x00ED;a</institution>, <addr-line>Mexico City</addr-line>, <country>Mexico</country></aff>
<aff id="aff4"><sup>4</sup><institution>Divisi&#x00F3;n de Neurociencias, Centro de Investigaci&#x00F3;n Biom&#x00E9;dica de Michoac&#x00E1;n, Instituto Mexicano del Seguro Social</institution>, <addr-line>Morelia</addr-line>, <country>Mexico</country></aff>
<author-notes>
<fn fn-type="edited-by"><p>Edited by: Jeanine M. Refsnider, University of Toledo, United States</p></fn>
<fn fn-type="edited-by"><p>Reviewed by: Nathan Freeman Putman, LGL, United States; Jeanette Wyneken, Florida Atlantic University, United States</p></fn>
<corresp id="c001">&#x002A;Correspondence: Esperanza Mel&#x00E9;ndez-Herrera, <email>emelendez@umich.mx</email></corresp>
<corresp id="c002">Alma L. Fuentes-Far&#x00ED;as, <email>alma.fuentes@umich.mx</email></corresp>
<fn fn-type="other" id="fn004"><p>This article was submitted to Behavioral and Evolutionary Ecology, a section of the journal Frontiers in Ecology and Evolution</p></fn>
</author-notes>
<pub-date pub-type="epub">
<day>13</day>
<month>06</month>
<year>2022</year>
</pub-date>
<pub-date pub-type="collection">
<year>2022</year>
</pub-date>
<volume>10</volume>
<elocation-id>850612</elocation-id>
<history>
<date date-type="received">
<day>07</day>
<month>01</month>
<year>2022</year>
</date>
<date date-type="accepted">
<day>12</day>
<month>05</month>
<year>2022</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x00A9; 2022 Unda-D&#x00ED;az, Phillips-Farf&#x00E1;n, Nava, Lopez-Toledo, Murata, Lajud, Herrera-Vargas, Arreola Camacho, Torner, Fuentes-Far&#x00ED;as and Mel&#x00E9;ndez-Herrera.</copyright-statement>
<copyright-year>2022</copyright-year>
<copyright-holder>Unda-D&#x00ED;az, Phillips-Farf&#x00E1;n, Nava, Lopez-Toledo, Murata, Lajud, Herrera-Vargas, Arreola Camacho, Torner, Fuentes-Far&#x00ED;as and Mel&#x00E9;ndez-Herrera</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/"><p>This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</p></license>
</permissions>
<abstract>
<p>Sea turtle egg relocation and hatchery incubation (hereafter termed <italic>ex situ</italic> incubation) is an effective strategy to protect clutches when <italic>in situ</italic> egg incubation is not viable. Nevertheless, it negatively affects the ontogenesis of male gonads and brain areas homologous to the mammalian hippocampus, as well as body size and fitness. Thus, it is imperative to analyze the effects of <italic>ex situ</italic> incubation on other developmental aspects and extend these observations to females. This work evaluated the effect of <italic>ex situ</italic> management on neurogenesis (cell proliferation in the dorsal and medial ventricular zones, neuronal integration in the dorsomedial and medial cortices), ovary cell proliferation, body size (mass and length) and self-righting ability. Additionally, this study examined if the incubation microenvironment is different between <italic>in situ</italic> and <italic>ex situ</italic> nests and whether it could contribute to explain the biological traits. An analysis of principal components showed differences in biological variables of hatchlings between <italic>in situ</italic> and <italic>ex situ</italic> clutches, driven by contrasting temperatures and silt composition. Each biological variable was also analyzed with linear mixed models using <italic>in situ</italic> vs. <italic>ex situ</italic> clutches, abiotic variables and their interaction. Turtles from <italic>ex situ</italic> clutches showed: (1) fewer proliferating cells in the dorsal and medial ventricular zones; (2) less mature neurons in the dorsomedial and medial cortices; (3) ovaries with a lesser number of proliferating cells; (4) lower body mass and length at emergence; and (5) slower self-righting time. Together, the results suggest that <italic>ex situ</italic> incubation in hatcheries is related to a slowing down of neurogenesis, ovariogenesis, body size and self-righting ability in hatchlings. Future studies should evaluate the effect of <italic>ex situ</italic> incubation on cognitive and reproductive performance to understand the long-term consequences of altered organogenesis. These studies should also disentangle the differential contribution of egg movement, reburial, nesting environment and parental origin to development. This information would likely result in better conservation strategies for sea turtles.</p>
</abstract>
<kwd-group>
<kwd><italic>Lepidochelys olivacea</italic></kwd>
<kwd>brain development</kwd>
<kwd>ovarian development</kwd>
<kwd>neuronal integration</kwd>
<kwd>temperature</kwd>
<kwd>substrate composition</kwd>
<kwd>moisture</kwd>
</kwd-group>
<counts>
<fig-count count="6"/>
<table-count count="2"/>
<equation-count count="0"/>
<ref-count count="113"/>
<page-count count="17"/>
<word-count count="11739"/>
</counts>
</article-meta>
</front>
<body>
<sec sec-type="intro" id="S1">
<title>Introduction</title>
<p>Natural sea turtle populations are threatened globally (<xref ref-type="bibr" rid="B49">IUCN, 2020</xref>). Conservation efforts implemented in the last decades have gradually managed to mitigate the loss of some populations with scarce effect on others (<xref ref-type="bibr" rid="B62">Mazaris et al., 2017</xref>). One of the most broadly employed strategies is the relocation of endangered eggs to protected hatcheries. Eggs continue their development in <italic>ex situ</italic> nests constructed near the original site selected by the mother. This strategy has shown considerable success and may be the only chance for survival in some species of major concern (<xref ref-type="bibr" rid="B13">Blanck and Sawyer, 1981</xref>; <xref ref-type="bibr" rid="B46">Heppell et al., 2005</xref>, <xref ref-type="bibr" rid="B45">2007</xref>; <xref ref-type="bibr" rid="B62">Mazaris et al., 2017</xref>).</p>
<p>However, several studies have reported negative effects associated to <italic>ex situ</italic> protection such as diminished hatching success, incomplete yolk resorption, sexual ratio bias, low body mass or length and reduced locomotor performance at emergence (<xref ref-type="bibr" rid="B55">Limpus et al., 1979</xref>; <xref ref-type="bibr" rid="B30">Eckert and Eckert, 1990</xref>; <xref ref-type="bibr" rid="B76">Pintus et al., 2009</xref>; <xref ref-type="bibr" rid="B61">Maulany et al., 2012</xref>; <xref ref-type="bibr" rid="B64">McElroy et al., 2015</xref>; <xref ref-type="bibr" rid="B3">Ahles and Milton, 2016</xref>; <xref ref-type="bibr" rid="B98">Tanabe et al., 2020</xref>). Recent studies evaluated the impact of the <italic>ex situ</italic> incubation strategy on organogenesis and proposed potential mechanisms of action for its negative effects (<xref ref-type="bibr" rid="B93">S&#x00F6;nmez et al., 2011</xref>; <xref ref-type="bibr" rid="B47">Herrera-Vargas et al., 2017</xref>).</p>
<p>Some studies explored the causal effect of abiotic variables on developmental traits (<xref ref-type="bibr" rid="B90">Sieg et al., 2011</xref>). A chief variable is nest temperature (<xref ref-type="bibr" rid="B100">Telemeco et al., 2013</xref>), which modifies incubation duration (<xref ref-type="bibr" rid="B68">Merchant-Larios et al., 1997</xref>; <xref ref-type="bibr" rid="B14">Booth and Astill, 2001a</xref>,<xref ref-type="bibr" rid="B15">b</xref>), sex determination (<xref ref-type="bibr" rid="B80">Reece et al., 2002</xref>), immune competence (<xref ref-type="bibr" rid="B33">Freedberg et al., 2008</xref>; <xref ref-type="bibr" rid="B23">Dang et al., 2015</xref>; <xref ref-type="bibr" rid="B81">Robledo-Avila et al., 2022</xref>) and brain development in reptiles (<xref ref-type="bibr" rid="B7">Amiel and Shine, 2012</xref>; <xref ref-type="bibr" rid="B74">Paredes et al., 2016</xref>; <xref ref-type="bibr" rid="B6">Amiel et al., 2017</xref>; <xref ref-type="bibr" rid="B86">Sanger et al., 2018</xref>). Another important factor is nest moisture, which alters sex ratio, incubation duration and embryo growth (<xref ref-type="bibr" rid="B107">Wallace et al., 2004</xref>; <xref ref-type="bibr" rid="B75">Patino-Mart&#x00ED;nez et al., 2012</xref>; <xref ref-type="bibr" rid="B56">Lolavar and Wyneken, 2020</xref>; <xref ref-type="bibr" rid="B101">Tezak et al., 2020</xref>). Successful sea turtle embryo development also depends on substrate composition, which could affect gas exchange and water retention, as well as the incubation period and sex-ratio (<xref ref-type="bibr" rid="B2">Ackerman, 1977</xref>; <xref ref-type="bibr" rid="B58">Lutcavage et al., 1997</xref>; <xref ref-type="bibr" rid="B71">Mitchell and Janzen, 2019</xref>).</p>
<p>The brain is a plastic organ; its early development is affected by external factors, such as temperature and moisture in ectotherms (<xref ref-type="bibr" rid="B21">Coomber et al., 1997</xref>; <xref ref-type="bibr" rid="B11">Beltr&#x00E1;n et al., 2021</xref>; <xref ref-type="bibr" rid="B85">Sanger et al., 2021</xref>). This is especially true for the hippocampus, a structure that participates in cognitive tasks such as spatial learning and memory (<xref ref-type="bibr" rid="B96">Suh et al., 2011</xref>; <xref ref-type="bibr" rid="B8">Bannerman et al., 2014</xref>), as well as in the regulation of the hypothalamic-pituitary-adrenal axis (<xref ref-type="bibr" rid="B88">Sapolsky et al., 1983</xref>, <xref ref-type="bibr" rid="B87">1984</xref>). Anatomical and genetic results suggest that the reptilian dorsomedial cortex is homologous to the mammalian CA1/CA3 hippocampal regions; whereas the medial cortex corresponds to the dentate gyrus (<xref ref-type="bibr" rid="B67">Medina et al., 2017</xref>; <xref ref-type="bibr" rid="B102">Tosches et al., 2018</xref>). Development of these cortices results from proliferation of neural precursors in the dorsal and medial walls of the lateral ventricles (<xref ref-type="bibr" rid="B18">Butler and Hodos, 2005</xref>; <xref ref-type="bibr" rid="B67">Medina et al., 2017</xref>; <xref ref-type="bibr" rid="B63">McDonald and Vickaryous, 2018</xref>; <xref ref-type="bibr" rid="B102">Tosches et al., 2018</xref>).</p>
<p>Proliferation is the earliest step in neurogenesis, which is followed by migration, differentiation, and integration of these new cells into the neural tissue (<xref ref-type="bibr" rid="B5">Altman and Das, 1965</xref>; <xref ref-type="bibr" rid="B35">Gage, 2002</xref>; <xref ref-type="bibr" rid="B10">Bayer and Altman, 2004</xref>; <xref ref-type="bibr" rid="B51">Kuhn et al., 2016</xref>). In mammals, early adverse environmental conditions can induce long-lasting brain alterations, including reduced hippocampal neurogenesis (<xref ref-type="bibr" rid="B54">Lajud and Torner, 2015</xref>; <xref ref-type="bibr" rid="B104">Vaiserman and Koliada, 2017</xref>). These alterations could result in lifelong cognitive and affective deficits, such as learning and memory disabilities, as well as anxiety-like or depressive-like behaviors (<xref ref-type="bibr" rid="B44">Heim and Nemeroff, 2002</xref>; <xref ref-type="bibr" rid="B65">McEwen, 2012</xref>; <xref ref-type="bibr" rid="B54">Lajud and Torner, 2015</xref>; <xref ref-type="bibr" rid="B104">Vaiserman and Koliada, 2017</xref>). Interestingly, species-specific non-optimal incubation temperatures decrease hippocampal neurogenesis in lizards, producing spatial learning disabilities (<xref ref-type="bibr" rid="B7">Amiel and Shine, 2012</xref>; <xref ref-type="bibr" rid="B6">Amiel et al., 2017</xref>; <xref ref-type="bibr" rid="B24">Dayananda and Webb, 2017</xref>). Likewise, early non-optimal conditions produce anxiety-like behaviors in lizards (<xref ref-type="bibr" rid="B103">Trnik et al., 2011</xref>), suggesting that reduced hippocampal neurogenesis during critical time windows may alter cognitive and behavioral traits in both mammals and reptiles.</p>
<p>Similarly, early environmental conditions also influence the development of the gonad. Its differentiation in reptiles displays the same progression as in other vertebrates and is highly sensitive to environmental variables such as temperature (<xref ref-type="bibr" rid="B113">Yntema and Mrosovsky, 1981</xref>; <xref ref-type="bibr" rid="B38">Ge et al., 2018</xref>; <xref ref-type="bibr" rid="B109">Weber et al., 2020</xref>). In humans and mice, altered seminiferous cord formation is associated with infertility, dysgenesis, and sexual development disorders (<xref ref-type="bibr" rid="B20">Chen and Liu, 2016</xref>). Likewise, disturbed oogenesis and folliculogenesis is related to reduced follicle reserves and infertility (<xref ref-type="bibr" rid="B48">Holm et al., 2016</xref>).</p>
<p>Motor abilities such as self-righting, crawling, and swimming speed constitute developmental traits associated with microenvironmental incubatory conditions like temperature and grain size. Better performance has been associated with cooler incubation temperatures and medium grain sand (<xref ref-type="bibr" rid="B95">Stewart et al., 2019</xref>; <xref ref-type="bibr" rid="B79">Reboul et al., 2021</xref>). Since reduced motor skills increase predation risk for newly emerged hatchlings during their displacement on land and sea, these traits constitute a good indicator of physical fitness and survival during this period. Indeed, these abilities may be good indicators of non-optimal incubation conditions in sea turtles (<xref ref-type="bibr" rid="B32">Fleming et al., 2020</xref>; <xref ref-type="bibr" rid="B60">Martins et al., 2020</xref>).</p>
<p><italic>Ex situ</italic> incubation may alter neural and gonadal development in male <italic>Lepidochelys olivacea</italic> hatchlings by reducing the cell size and dendritic arborization of dorsomedial cortical neurons, as well as the number of epithelial cells per seminiferous cord (<xref ref-type="bibr" rid="B47">Herrera-Vargas et al., 2017</xref>). The functional relevance of these alterations is unknown, but results in mammals and lizards suggests that defective differentiation of hippocampal neurons and the seminiferous cord causes cognitive and reproductive problems (see above). Studies in rodents suggest that males are more vulnerable to developmental disruption (<xref ref-type="bibr" rid="B29">Dimatelis et al., 2015</xref>; <xref ref-type="bibr" rid="B22">Cowan and Richardson, 2018</xref>; <xref ref-type="bibr" rid="B25">de Melo et al., 2018</xref>), but in ectotherms some studies associate better phenotypes with male-producing environmental conditions (<xref ref-type="bibr" rid="B33">Freedberg et al., 2008</xref>).</p>
<p>Neurogenesis, ovariogenesis and motor performance are vital for the survival of sea turtle populations. These processes are highly sensitive to early adverse environmental stimuli. <italic>Ex situ</italic> incubation in hatcheries involves the early handling of eggs, as well their relocation to hatcheries. Moreover, nesting beaches include microenvironments that vary in moisture (depending on distance to the shoreline or vegetation), substrate composition, microbial load, and temperature (<xref ref-type="bibr" rid="B95">Stewart et al., 2019</xref>). All these variables could contribute to create non-optimal conditions for suitable development of turtle hatchlings. Thus, it is necessary to evaluate the effects of <italic>ex situ</italic> incubation in female turtles to determine if early adverse conditions have sex-specific effects on developmental traits. Moreover, it is imperative to identify the environmental variables likely modifying these developing traits in sea turtles. To test these hypotheses, this study evaluated the effects of <italic>ex situ</italic> incubation on hippocampal neurogenesis (cell proliferation in the dorsal and medial ventricular zones, as well as integration of newborn neurons into the dorsomedial and medial cortices), ovariogenesis (cell proliferation), body size (mass and length), and self-righting ability in <italic>L. olivacea</italic> females at emergence. Furthermore, this work analyzed the contribution of several nest-related abiotic variables (sand temperature, moisture, and grain size) to identify the most relevant variables for hatchling development. The results will contribute to determine the impact of <italic>ex situ</italic> incubation in hatcheries on female organogenesis and to identify some of the variables determining the altered phenotype observed in turtles incubated in hatcheries.</p>
</sec>
<sec id="S2" sec-type="materials|methods">
<title>Materials and Methods</title>
<sec id="S2.SS1">
<title>Study Site and Nesting Conditions</title>
<p>This study was conducted at the <italic>Centro de Protecci&#x00F3;n de la Tortuga Marina</italic> in Boca Seca beach, located in L&#x00E1;zaro C&#x00E1;rdenas, Michoac&#x00E1;n, M&#x00E9;xico (18&#x00B0; 04&#x2032; N, 102&#x00B0; 58&#x2032; W; <xref ref-type="fig" rid="F1">Figure 1</xref>). Egg manipulation was kept to the bare minimum and done by the hatchery staff according to protocols stated in Mexican regulation (<xref ref-type="bibr" rid="B114">NOM-162-SEMARNAT, 2014</xref>) and a previous report (<xref ref-type="bibr" rid="B47">Herrera-Vargas et al., 2017</xref>). Briefly, beach patrolling during three consecutive nights (September 13&#x2013;15, 2017) allowed identification of nesting females. Ten nests located approximately in the same beach zone (30&#x2013;60 m away from the shoreline) were chosen and sheltered immediately after the female turtle covered the eggs and left the site. Five randomly selected natural nests remained undisturbed <italic>in situ</italic>, only fenced with cyclone mesh until hatchling emergence. The complete clutch of the other five nests was carefully collected as soon as the female left the nest, placed in individual plastic bags and transported to the hatchery. There, the eggs were immediately buried in previously built nests and remained undisturbed until emergence. This ensured that conditions related to clutch size (e.g., oxygen availability, temperature, metabolic heat, etc.) remained unaltered. The total time between laying and re-burial lasted less than 2 h. Efforts were made to avoid egg rotation and excessive handling, as well as to emulate natural nest architecture in hatcheries. <italic>Ex situ</italic> nests were constructed by the hatchery staff according to international norms for <italic>L. olivacea</italic>, with a narrow neck (20&#x2013;25 cm) and a wider flask-shaped bottom, at a depth of 40&#x2013;50 cm and 1 m separation between them (<xref ref-type="bibr" rid="B52">Kutzari, 2006</xref>). Nests from both conditions were not shaded or watered. Forty days after incubation started, the hatchery clutches were fenced with cyclone mesh until turtle emergence. This experimental design ensured that <italic>in situ</italic> nests were not disturbed and that clutches relocated to hatcheries only went through the routine procedures done by the hatchery staff. Egg handling was performed before organogenesis started (<xref ref-type="bibr" rid="B70">Miller, 1985</xref>).</p>
<fig id="F1" position="float">
<label>FIGURE 1</label>
<caption><p>Location of the study site and nesting conditions. <bold>(A)</bold> Map showing L&#x00E1;zaro C&#x00E1;rdenas nesting beaches in Michoac&#x00E1;n, M&#x00E9;xico. <bold>(B)</bold> Aerial photograph of <italic>ex situ</italic> (dotted line) and <italic>in situ</italic> nests (continuous line). <bold>(C,D)</bold> <italic>Lepidochelys olivacea</italic> hatchlings crawling to sea and emerging from nest, respectively.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-10-850612-g001.tif"/>
</fig>
</sec>
<sec id="S2.SS2">
<title>Hatchling Collection</title>
<p>Animal sampling, handling and sacrifice protocols were approved by an Animal Rights Committee, under License Number SEMARNAT: SGPA/DGVS/10395/17; in accordance with Mexican regulation (<xref ref-type="bibr" rid="B73">NOM-033-SAG/ZOO, 2014</xref>). One hundred and fifty turtles were collected from five <italic>in situ</italic> and five <italic>ex situ</italic> nests (15 hatchlings/nest). Fifty hatchlings were used for histological and morphometric observations: for neurogenesis studies, 24 brains per nest type were evaluated, since one brain for each condition was damaged during dissection (48 brains in total); for ovarian cell proliferation quantification, at least two ovaries per nest were used (27 ovaries in total), while all fifty individuals were sexed. The other one hundred hatchlings were used to evaluate motor performance.</p>
<p>Hatchling collection was described by <xref ref-type="bibr" rid="B47">Herrera-Vargas et al. (2017)</xref> and <xref ref-type="bibr" rid="B81">Robledo-Avila et al. (2022)</xref>. Briefly, fifteen emerging turtles from each nest were collected at 5-min intervals, as soon as they surfaced from each nest. Five randomly selected hatchlings per nest were weighted with a digital precision balance (OHAUS&#x2122; Scout Pro Sp 602, Max 600 g, <italic>d</italic> = 0.01 g). Their straight carapace length was measured using a digital Vernier caliper (Mitutoyo&#x2122;). These same five turtles per nest were used to investigate neurogenesis and gonadal cell proliferation.</p>
</sec>
<sec id="S2.SS3">
<title>Cell Proliferation and Neuronal Integration Studies</title>
<p>To evaluate the effect of <italic>ex situ</italic> incubation on brain and ovary cell proliferation, hatchlings received an intraperitoneal injection of the cell birth marker 5&#x2032;-bromo-2&#x2032;-deoxyuridine (BrdU, a thymidine analog incorporated in the S phase of the cell cycle. Sigma-Aldrich, 100 mg/Kg in 0.9% NaCl) immediately after morphometric data recording and a second injection 2 h after. Turtles were then placed in sand tubs and sacrificed 4 h after the last injection. This procedure (i.e., the timings) minimized the effect of factors other than the incubation condition on cell proliferation. The brain and gonad-mesonephros complex were dissected <italic>in situ</italic>, incubated in Bouin&#x2019;s solution (Sigma-Aldrich, Saint Louis, MO, United States) for 24 h and incubated in buffered paraformaldehyde (Sigma-Aldrich, Saint Louis, MO, United States, 4% in 0.1 M phosphate buffer) for 3 days at room temperature.</p>
<p>In the laboratory, brains were rinsed with 70% ethanol and transferred to buffered sucrose (Sigma-Aldrich, Saint Louis, MO, United States, 30% in 0.1 M phosphate buffer) at 4&#x00B0;C until they sank. Then they were frozen in the Peltier module of a cryostat (Microm) and sectioned coronally at 30 &#x03BC;m. Free-floating sections were collected in Tris-buffered saline (Sigma-Aldrich, Saint Louis, MO, United States, 50 mM Tris&#x2013;HCl, 150 mM NaCl, pH 7.6) and processed for immunohistochemistry. Cell proliferation in neurogenic niches was evaluated by immunoreactivity for BrdU and neuronal integration was evaluated by immunoreactivity for the anti-neuronal nuclear protein (NeuN) in separate brain sections. Briefly, the tissue was incubated in ImmunoDNA retriever 20&#x00D7; with citrate (Bio SB), then in 2 N HCl for 30 min at 65&#x00B0;C and finally in 0.1 M sodium borate buffer at room temperature. Blocking of non-specific binding was done by incubating the sections in 0.1% bovine serum albumin (Sigma-Aldrich, Saint Louis, MO, United States) for 30 min. Sections including the dorsal and medial ventricular zones were incubated with mouse anti-BrdU monoclonal antibody (1: 500, Roche) and independent cortical sections were incubated with mouse anti-NeuN monoclonal antibody (1: 1000, Millipore) for 16 h at 4&#x00B0;C. Then they were incubated with a donkey anti-mouse biotin-conjugated secondary antibody (1:500, Vector Laboratories) for 2 h. Sections were incubated in avidin/biotin horseradish peroxidase (Vectastain Elite, PK-6100) for 2 h at room temperature and then incubated in diaminobenzidine as a chromogen, with peroxide and buffer for 10 min (Vector Staining Kit, SK-4100). Finally, the tissue was mounted onto gelatinized slides, dehydrated and cover-slipped using Cytoseal 60 (Richard Alan Scientific).</p>
<p>To evaluate cell proliferation in neurogenic niches, three equivalent non-adjacent brain sections containing the dorsal and medial ventricular zones were selected per turtle according morphological criteria (appearance of lateral ventricles) along the antero-posterior axis. BrdU + immunoreactive cells were quantified in two microphotographs per section per neurogenic zone at 1000&#x00D7; magnification. To evaluate neuronal integration, three equivalent non-adjacent brain sections including the dorsomedial and medial cortices were selected per turtle according morphological criteria (opening of the lateral ventricles). NeuN + immunoreactive cells in the cellular layer were quantified in three microphotographs per section per cortex at 1000&#x00D7; magnification. Microphotographs were captured with a Zeiss microscope using the Axio Vision 4.6 software and analyzed using NIH ImageJ software.</p>
<p>For gonadal sex determination, one gonad-mesonephros complex was dehydrated using increasing ethanol concentrations, embedded in paraffin, sliced transversally (7 &#x03BC;m) in a microtome (Leica) and stained with hematoxylin-eosin (Merck), as previously described (<xref ref-type="bibr" rid="B47">Herrera-Vargas et al., 2017</xref>). Gonadal histology showed that all fifty specimens were females, thus all gonadal analysis were performed in ovaries. To evaluate ovarian cell proliferation, at least two gonad-mesonephros complexes per nest were frozen, cryosectioned at 30 &#x03BC;m and immuno-stained for BrdU as described for the brain (the other gonad-mesonephros complexes were frozen for RNA quantification). Five adjacent gonadal sections per hatchling were selected from the central ovary. BrdU + immunoreactive germ cells were quantified in the cortex of ovaries throughout the whole section at 400 x magnification, as described for brain sections. After quantification, selected ovarian sections were stained with hematoxylin-eosin to observe cell density and cytoarchitecture.</p>
</sec>
<sec id="S2.SS4">
<title>Self-Righting</title>
<p>To evaluate the effect of <italic>ex situ</italic> incubation on motor skills, ten hatchlings per nest were randomly selected and separated in tubs with sand for 15 min, to prevent lethargy from interfering with performance (<xref ref-type="bibr" rid="B16">Booth et al., 2013</xref>). Turtles were placed upside-down on a tray full of dry sand and the time they took to self-right was recorded with a chronometer (Sper scientific 810015 5 channel timer). Hatchlings that exceeded 10 min to self-right were discarded from the analysis. Thus, 48 turtles from <italic>in situ</italic> nests and 31 <italic>ex situ</italic> hatchlings were analyzed.</p>
</sec>
<sec id="S2.SS5">
<title>Measurement of Abiotic Variables</title>
<p>To evaluate the contribution of abiotic variables to the developmental traits, nest temperature, moisture and sand grain size were determined. Nest temperature was recorded from developmental day 11 until emergence, since this period includes the bulk of hippocampal neurogenesis previously described for <italic>Emys orbicularis</italic> (<xref ref-type="bibr" rid="B40">Goffinet et al., 1986</xref>) and the critical time for gonadal development in <italic>L. olivacea</italic> (<xref ref-type="bibr" rid="B68">Merchant-Larios et al., 1997</xref>). Temperature was registered by data loggers (Onset HOBO<sup>&#x00AE;</sup> Bluetooth Pendant MX2202 series; accuracy &#x00B1; 0.2&#x00B0;C) carefully located outside the nest to avoid disturbing the clutch. They were placed in sand 30 cm from the center of the nest and 50 cm deep, 11 days after the incubation period began. They were programmed to record the temperature every hour; results were averaged by nest.</p>
<p>Moisture and grain size were determined from 100 g of sand, sampled 10 cm deep inside the nests, immediately after hatchling emergence. The sand was placed in a sealed plastic bag, weighed, dried at 105&#x2013;110&#x00B0;C in a standard oven and weighed again. Moisture content was calculated as the ratio of wet to dry sand mass (<xref ref-type="bibr" rid="B43">Head, 1992</xref>). Grain size analysis was performed by particle sieving, using international parameters (gravel: &#x003E;2.0; coarse sand: 2.0 &#x00B1; 0.2; fine sand: 0.2 &#x00B1; 0.02; silt: 0.02&#x2013;0.002 mm; <xref ref-type="bibr" rid="B17">Brady and Weil, 2008</xref>), and subsequent weighting with an analytical balance. Gravel, coarse- and fine-sand, as well as silt proportions were calculated dividing by the total dry mass (<xref ref-type="bibr" rid="B39">Gee and Or, 2002</xref>).</p>
</sec>
<sec id="S2.SS6">
<title>Statistical Analyses</title>
<p>Preliminary analysis showed that only one nest had a different gravel composition from the rest, thus gravel was discarded from further examination. Similarly, fine sand was collinear with coarse sand, hence only the latter was used. This was done because multivariate analyses are sensitive to collinearity between variables, which causes interpretation problems (<xref ref-type="bibr" rid="B42">Harrison et al., 2018</xref>). Accordingly, the selected parameters for analysis were abiotic variables within nests (temperature and moisture, coarse sand and silt), as well as turtle biological variables (cell proliferation in the dorsal and medial ventricular zones, as well as the ovary; neuronal integration in the cellular layer of the dorsomedial and medial cortices; body mass and length, as well as self-righting time).</p>
<p>Multivariate principal components analysis (PCA) was performed to reduce data dimensionality and investigate the distribution of samples in two-dimensions. This allowed the assessment of possible differences between conditions, based on the abiotic variables within nests and turtle biological data.</p>
<p>The outcomes of <italic>in situ</italic> (<italic>n</italic> = 5) vs. <italic>ex situ</italic> clutches (<italic>n</italic> = 5), abiotic variables and their interaction (<italic>in situ</italic> vs. <italic>ex situ</italic> condition interacting with each abiotic variable) were studied with linear mixed models to avoid violation of independence assumptions (turtles within clutches). Biological results were used as the response variables in these models; which included the following effects: <italic>in situ</italic> vs. <italic>ex situ</italic> clutches (main); abiotic variables and their interaction (fixed) plus turtles within clutches (random). All abiotic variables (temperature, moisture, coarse sand and silt) were standardized by subtracting the mean from every value and dividing by the standard deviation (<xref ref-type="bibr" rid="B42">Harrison et al., 2018</xref>), due to wide differences in their ranges. Outliers were removed from most turtle biological data (all except body mass and length). Ovarian cell proliferation and self-righting were also transformed to meet normality and homocedasticity assumptions; with square-root and natural logarithm, respectively.</p>
<p>Stepwise backward elimination followed by selection with the conditional Akaike information criterion (cAIC) were performed to obtain the best linear mixed model (<xref ref-type="supplementary-material" rid="DS1">Supplementary Data 1</xref>). The marginal <italic>R</italic><sup>2</sup> for each model was determined as a measure of the proportion of the variance explained by the model. The effect size for <italic>in situ</italic> vs. <italic>ex situ</italic> clutches was evaluated by Glass&#x2019;s &#x0394; (<xref ref-type="bibr" rid="B92">Sink and Mvududu, 2010</xref>; <xref ref-type="bibr" rid="B97">Sullivan and Feinn, 2012</xref>). Graphs presented in the results for each of the eight biological variables were obtained back-transforming the predictions of the final models. Residuals for each model were plotted to assess the distribution of the model fit (<xref ref-type="supplementary-material" rid="DS1">Supplementary Data 1</xref>).</p>
<p>Data analyses were done using R (<xref ref-type="bibr" rid="B77">R Core Team, 2020</xref>; version 4.1.1) and RStudio (<xref ref-type="bibr" rid="B83">RStudio Team, 2020</xref>; version 1.3.1073). Linear mixed models were performed using: readxl (<xref ref-type="bibr" rid="B112">Wickham and Bryan, 2019</xref>), lme4 (<xref ref-type="bibr" rid="B9">Bates et al., 2015</xref>), lmerTest (<xref ref-type="bibr" rid="B53">Kuznetsova et al., 2017</xref>), and cAIC (<xref ref-type="bibr" rid="B84">S&#x00E4;efken et al., 2018</xref>). Model parameters, including residuals, were evaluated with the performance package (<xref ref-type="bibr" rid="B57">L&#x00FC;decke et al., 2021</xref>). Principal component analysis results were graphed with ggbiplot (<xref ref-type="bibr" rid="B106">Vu, 2011</xref>).</p>
</sec>
</sec>
<sec sec-type="results" id="S3">
<title>Results</title>
<p>Data provided by the national meteorological service during the entire incubation period (September 13&#x2013;October 31, 2017) showed an average environmental temperature of 26.41&#x00B0;C &#x00B1; 0.98 SD (mean minimum temperature = 20.53&#x00B0;C and mean maximum temperature = 32.27&#x00B0;C; <xref ref-type="supplementary-material" rid="DS1">Supplementary Table 1</xref>). Data loggers in sand near the nests recorded average maximum temperatures of 35.68&#x00B0;C &#x00B1; 0.83 SD for <italic>in situ</italic> nests and 37.03&#x00B0;C &#x00B1; 1.29 SD for <italic>ex situ</italic> nests, as well mean minimum temperatures of 26.28 &#x00B1; 2.91 SD for <italic>in situ</italic> nests and 25.01 &#x00B1; 0.14 SD for <italic>ex situ</italic> nests (<xref ref-type="table" rid="T1">Table 1</xref>). The average incubation period &#x00B1; SD for hatchlings from <italic>in situ</italic> clutches was 46.40 &#x00B1; 0.55 and 45.60 &#x00B1; 1.82 days for hatchlings from <italic>ex situ</italic> clutches (<xref ref-type="table" rid="T1">Table 1</xref>). The mean moisture, coarse and fine sand, as well as silt proportions were: <italic>in situ</italic> (0.1180 &#x00B1; 0.0936 SD; 0.9238 &#x00B1; 0.0363 SD; 0.0643 &#x00B1; 0.0384 SD; and 0.0005 &#x00B1; 0.0008 SD, respectively) and <italic>ex situ</italic> clutches (0.0980 &#x00B1; 0.0487 SD; 0.9011 &#x00B1; 0.0176 SD; 0.0880 &#x00B1; 0.0156 SD; and 0.0062 &#x00B1; 0.0041 SD, respectively; <xref ref-type="supplementary-material" rid="DS1">Supplementary Table 2</xref>).</p>
<table-wrap position="float" id="T1">
<label>TABLE 1</label>
<caption><p>Sand temperatures (&#x00B0;C) monitored by data loggers located 30 cm from the center of the clutch and 50 cm deep, as well as incubation periods registered for <italic>L. olivacea</italic> hatchlings at Boca Seca beach, L&#x00E1;zaro C&#x00E1;rdenas, Michoac&#x00E1;n, M&#x00E9;xico.</p></caption>
<table cellspacing="5" cellpadding="5" frame="hsides" rules="groups">
<thead>
<tr>
<td valign="top" align="left"></td>
<td valign="top" align="left"/>
<td valign="top" align="center" colspan="3">Incubation period<hr/></td>
<td valign="top" align="left"/>
<td valign="top" align="left"/></tr>
<tr>
<td valign="top" align="left">Nest no.</td>
<td valign="top" align="left">Incubation condition</td>
<td valign="top" align="left">Mean temperature &#x00B1; SEM</td>
<td valign="top" align="left">Maximum temperature</td>
<td valign="top" align="left">Minimum temperature</td>
<td valign="top" align="left">Incubation dates</td>
<td valign="top" align="left">Incubation days</td>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">1</td>
<td valign="top" align="left"><italic>in situ</italic></td>
<td valign="top" align="left">34.17 &#x00B1; 0.75</td>
<td valign="top" align="left">35.44</td>
<td valign="top" align="left">31.47</td>
<td valign="top" align="left">15/09&#x2013;30/10</td>
<td valign="top" align="left">46</td>
</tr>
<tr>
<td valign="top" align="left">2</td>
<td valign="top" align="left"><italic>in situ</italic></td>
<td valign="top" align="left">33.19 &#x00B1; 1.26</td>
<td valign="top" align="left">34.90</td>
<td valign="top" align="left">24.93</td>
<td valign="top" align="left">15/09&#x2013;30/10</td>
<td valign="top" align="left">46</td>
</tr>
<tr>
<td valign="top" align="left">3</td>
<td valign="top" align="left"><italic>in situ</italic></td>
<td valign="top" align="left">34.15 &#x00B1; 1.50</td>
<td valign="top" align="left">36.51</td>
<td valign="top" align="left">25.22</td>
<td valign="top" align="left">15/09&#x2013;30/10</td>
<td valign="top" align="left">46</td>
</tr>
<tr>
<td valign="top" align="left">4</td>
<td valign="top" align="left"><italic>in situ</italic></td>
<td valign="top" align="left">34.24 &#x00B1; 1.66</td>
<td valign="top" align="left">36.40</td>
<td valign="top" align="left">25.03</td>
<td valign="top" align="left">15/09&#x2013;31/10</td>
<td valign="top" align="left">47</td>
</tr>
<tr>
<td valign="top" align="left">5</td>
<td valign="top" align="left"><italic>in situ</italic></td>
<td valign="top" align="left">32.64 &#x00B1; 1.21</td>
<td valign="top" align="left">34.69</td>
<td valign="top" align="left">24.74</td>
<td valign="top" align="left">15/09&#x2013;31/10</td>
<td valign="top" align="left">47</td>
</tr>
<tr>
<td valign="top" align="left">6</td>
<td valign="top" align="left"><italic>ex situ</italic></td>
<td valign="top" align="left">34.36 &#x00B1; 1.49</td>
<td valign="top" align="left">36.30</td>
<td valign="top" align="left">24.93</td>
<td valign="top" align="left">13/09&#x2013;30/10</td>
<td valign="top" align="left">48</td>
</tr>
<tr>
<td valign="top" align="left">7</td>
<td valign="top" align="left"><italic>ex situ</italic></td>
<td valign="top" align="left">34.50 &#x00B1; 1.68</td>
<td valign="top" align="left">36.95</td>
<td valign="top" align="left">25.22</td>
<td valign="top" align="left">14/09&#x2013;31/10</td>
<td valign="top" align="left">47</td>
</tr>
<tr>
<td valign="top" align="left">8</td>
<td valign="top" align="left"><italic>ex situ</italic></td>
<td valign="top" align="left">34.38 &#x00B1; 1.47</td>
<td valign="top" align="left">36.30</td>
<td valign="top" align="left">25.03</td>
<td valign="top" align="left">15/09&#x2013;29/10</td>
<td valign="top" align="left">44</td>
</tr>
<tr>
<td valign="top" align="left">9</td>
<td valign="top" align="left"><italic>ex situ</italic></td>
<td valign="top" align="left">35.12 &#x00B1; 2.18</td>
<td valign="top" align="left">39.28</td>
<td valign="top" align="left">24.84</td>
<td valign="top" align="left">15/09&#x2013;29/10</td>
<td valign="top" align="left">44</td>
</tr>
<tr>
<td valign="top" align="left">10</td>
<td valign="top" align="left"><italic>ex situ</italic></td>
<td valign="top" align="left">34.42 &#x00B1; 1.49</td>
<td valign="top" align="left">36.30</td>
<td valign="top" align="left">25.03</td>
<td valign="top" align="left">15/09&#x2013;30/10</td>
<td valign="top" align="left">45</td>
</tr>
<tr>
<td valign="top" align="center" colspan="7"><hr/></td>
</tr>
<tr>
<td valign="top" align="left"></td>
<td valign="top" align="left"/>
<td valign="top" align="left"/>
<td valign="top" align="center" colspan="5"><bold>Thermosensitive period</bold></td>
</tr>
<tr>
<td valign="top" align="left"></td>
<td valign="top" align="left"/>
<td valign="top" align="left"/>
<td valign="top" align="center" colspan="4"><hr/></td>
</tr>
<tr>
<td valign="top" align="left"><bold>Nest no.</bold></td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left"><bold>Incubation condition</bold></td>
<td valign="top" align="left"><bold>Mean temperature &#x00B1; SEM</bold></td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left"><bold>Maximum temperature</bold></td>
<td valign="top" align="left"><bold>Minimum temperature</bold></td>
</tr>
<tr>
<td valign="top" align="center" colspan="7"><hr/></td>
</tr>
<tr>
<td valign="top" align="left">1</td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left"><italic>in situ</italic></td>
<td valign="top" align="left">32.98 &#x00B1; 0.68</td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left">34.06</td>
<td valign="top" align="left">31.98</td>
</tr>
<tr>
<td valign="top" align="left">2</td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left"><italic>in situ</italic></td>
<td valign="top" align="left">32.14 &#x00B1; 1.22</td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left">33.95</td>
<td valign="top" align="left">24.93</td>
</tr>
<tr>
<td valign="top" align="left">3</td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left"><italic>in situ</italic></td>
<td valign="top" align="left">32.96 &#x00B1; 1.53</td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left">35.22</td>
<td valign="top" align="left">25.22</td>
</tr>
<tr>
<td valign="top" align="left">4</td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left"><italic>in situ</italic></td>
<td valign="top" align="left">32.61 &#x00B1; 1.34</td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left">34.59</td>
<td valign="top" align="left">25.03</td>
</tr>
<tr>
<td valign="top" align="left">5</td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left"><italic>in situ</italic></td>
<td valign="top" align="left">31.69 &#x00B1; 1.17</td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left">33.43</td>
<td valign="top" align="left">24.74</td>
</tr>
<tr>
<td valign="top" align="left">6</td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left"><italic>ex situ</italic></td>
<td valign="top" align="left">33.49 &#x00B1; 1.71</td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left">35.65</td>
<td valign="top" align="left">24.93</td>
</tr>
<tr>
<td valign="top" align="left">7</td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left"><italic>ex situ</italic></td>
<td valign="top" align="left">33.41 &#x00B1; 1.84</td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left">35.97</td>
<td valign="top" align="left">25.22</td>
</tr>
<tr>
<td valign="top" align="left">8</td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left"><italic>ex situ</italic></td>
<td valign="top" align="left">33.20 &#x00B1; 1.68</td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left">35.33</td>
<td valign="top" align="left">25.03</td>
</tr>
<tr>
<td valign="top" align="left">9</td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left"><italic>ex situ</italic></td>
<td valign="top" align="left">33.04 &#x00B1; 1.53</td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left">34.69</td>
<td valign="top" align="left">24.84</td>
</tr>
<tr>
<td valign="top" align="left">10</td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left"><italic>ex situ</italic></td>
<td valign="top" align="left">33.38 &#x00B1; 1.62</td>
<td valign="top" align="center" colspan="1"></td>
<td valign="top" align="left">35.33</td>
<td valign="top" align="left">25.03</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="tfn1"><p><italic>The table shows temperatures registered from incubation day 11 until emergence (incubation period) and during the thermosensitive period per clutch (in situ, n = 5; ex situ, n = 5).</italic></p></fn>
</table-wrap-foot>
</table-wrap>
<p>The PCA suggested that the synergic effect of some or all abiotic variables may be important to determine turtle phenotypes (see below). The first two principal components of the PCA, based on the biological and abiotic variables, explained 71.7% of the total data variance (<xref ref-type="fig" rid="F2">Figure 2</xref> and <xref ref-type="supplementary-material" rid="DS1">Supplementary Table 3</xref>). Principal component 1 (52%) showed that coarse sand (<italic>r</italic> = -0.202) and moisture (<italic>r</italic> = -0.122) were higher for <italic>in situ</italic> nests, while temperature (<italic>r</italic> = 0.304) and silt (<italic>r</italic> = 0.295) were lower. In addition, all biological variables from hatchlings (except self-righting) were higher for <italic>in situ</italic> conditions (<xref ref-type="fig" rid="F2">Figure 2</xref> and <xref ref-type="supplementary-material" rid="DS1">Supplementary Table 3</xref>). Principal component 2 (20%) showed that moisture (<italic>r</italic> = -0.543) and coarse sand proportions (<italic>r</italic> = -0.300) most influenced environmental variation for <italic>in situ</italic> nests (<xref ref-type="fig" rid="F2">Figure 2</xref> and <xref ref-type="supplementary-material" rid="DS1">Supplementary Table 3</xref>).</p>
<fig id="F2" position="float">
<label>FIGURE 2</label>
<caption><p>Multivariate principal components analysis of developmental and abiotic variables from <italic>in situ</italic> (<italic>n</italic> = 5, dark gray, left) vs. <italic>ex situ</italic> clutches (<italic>n</italic> = 5, light gray, right). W, body weight/mass (gr); L, body length (mm); M, neuronal integration in the cellular layer of the medial cortex (number of NeuN + cells/mm); D, neuronal integration in the cellular layer of the dorsomedial cortex (number of NeuN + cells/mm); O, cell proliferation in the ovary (number of BrdU + cells/mm); Dv, cell proliferation in the dorsal ventricular zone (number of BrdU + cells/mm); Mv, cell proliferation in the medial ventricular zone (number of BrdU + cells/mm); Cs, coarse sand (proportion); H, humidty (proportion); T, temperature (&#x00B0;C); SR, self-righting time (s); S, silt (proportion); PC1, principal component 1 of PCA; PC2, principal component 2 of PCA.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-10-850612-g002.tif"/>
</fig>
<p>Principal components analysis results showed a clear difference between nest conditions. Thus, linear mixed models were performed to confirm these differences and explore their relationship to abiotic variables. Linear mixed models showed that <italic>ex situ</italic> nests were negatively related to <italic>L. olivacea</italic> development at nest emergence with moderate (Glass&#x2019;s &#x0394; &#x003C; 1) to very large effect sizes (Glass&#x2019;s &#x0394; &#x003E; 1.3; <xref ref-type="bibr" rid="B97">Sullivan and Feinn, 2012</xref>; <xref ref-type="table" rid="T2">Table 2</xref>). The simplest linear mixed models (<italic>in situ</italic> vs. <italic>ex situ</italic> nests and intercept) were the best fit for all biological variables (<xref ref-type="table" rid="T2">Table 2</xref>). Additionally, models with each abiotic variable alone (i.e., without <italic>in situ-ex situ</italic> factor) were performed for each biological variable. In all cases, the cAIC was better with the <italic>in situ-ex situ</italic> factor than with only one abiotic variable (<xref ref-type="supplementary-material" rid="DS1">Supplementary Data 1</xref>). Altogether, linear mixed models indicated that abiotic variables (temperature, moisture, and the proportion of different sediment sizes) did not individually affect any response variables, at least when using backward elimination and the lowest conditional AIC to select the best model.</p>
<table-wrap position="float" id="T2">
<label>TABLE 2</label>
<caption><p>Summary of the best linear mixed effect models for each variable, selected by cAIC, explaining biological variables of <italic>Lepidochelys olivacea in situ</italic> vs. <italic>ex situ</italic> hatchlings.</p></caption>
<table cellspacing="5" cellpadding="5" frame="hsides" rules="groups">
<thead>
<tr>
<td valign="top" align="left">Best model</td>
<td valign="top" align="center">&#x03B2; &#x00B1; SE</td>
<td valign="top" align="center">d.f.</td>
<td valign="top" align="center"><italic>F</italic></td>
<td valign="top" align="center"><italic>p</italic></td>
<td valign="top" align="center">ES</td>
<td valign="top" align="center"><italic>R</italic><sup>2</sup></td>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left" colspan="6">Dorsal ventricular zone-cell proliferation (# BrdU + cells/area)</td>
<td valign="top" align="center">0.33</td>
</tr>
<tr>
<td valign="top" align="left">Intercept</td>
<td valign="top" align="center">483.05 &#x00B1; 56.13</td>
<td/>
<td/>
<td valign="top" align="center">&#x003C;0.001</td>
<td/>
<td/>
</tr>
<tr>
<td valign="top" align="left"><italic>in situ</italic> vs. <italic>ex situ</italic></td>
<td valign="top" align="center">&#x2013;244.92 &#x00B1; 78.21</td>
<td valign="top" align="center">8.15</td>
<td valign="top" align="center">9.81</td>
<td valign="top" align="center">0.014</td>
<td valign="top" align="center">2.63</td>
<td/>
</tr>
<tr>
<td valign="top" align="left" colspan="6">&#x002A;Medial ventricular zone-cell proliferation (# BrdU + cells/area)</td>
<td valign="top" align="center">0.28</td>
</tr>
<tr>
<td valign="top" align="left">Intercept</td>
<td valign="top" align="center">991.31 &#x00B1; 144.94</td>
<td/>
<td/>
<td valign="top" align="center">&#x003C;0.001</td>
<td/>
<td/>
</tr>
<tr>
<td valign="top" align="left"><italic>in situ</italic> vs. <italic>ex situ</italic></td>
<td valign="top" align="center">&#x2013;534.39 &#x00B1; 204.97</td>
<td valign="top" align="center">7.96</td>
<td valign="top" align="center">6.80</td>
<td valign="top" align="center">0.031</td>
<td valign="top" align="center">1.72</td>
<td/>
</tr>
<tr>
<td valign="top" align="left" colspan="6">Dorsomedial cortex-neuronal integration (# NeuN + cells/area)</td>
<td valign="top" align="center">0.18</td>
</tr>
<tr>
<td valign="top" align="left">Intercept</td>
<td valign="top" align="center">2031.77 &#x00B1; 43.73</td>
<td/>
<td/>
<td valign="top" align="center">&#x003C;0.001</td>
<td/>
<td/>
</tr>
<tr>
<td valign="top" align="left"><italic>in situ</italic> vs. <italic>ex situ</italic></td>
<td valign="top" align="center">&#x2013;145.82 &#x00B1; 60.89</td>
<td valign="top" align="center">8.78</td>
<td valign="top" align="center">5.73</td>
<td valign="top" align="center">0.041</td>
<td valign="top" align="center">3.25</td>
<td/>
</tr>
<tr>
<td valign="top" align="left" colspan="6">Medial cortex-neuronal integration (# NeuN + cells/area)</td>
<td valign="top" align="center">0.37</td>
</tr>
<tr>
<td valign="top" align="left">Intercept</td>
<td valign="top" align="center">2062.49 &#x00B1; 97.28</td>
<td/>
<td/>
<td valign="top" align="center">&#x003C;0.001</td>
<td/>
<td/>
</tr>
<tr>
<td valign="top" align="left"><italic>in situ</italic> vs. <italic>ex situ</italic></td>
<td valign="top" align="center">&#x2013;665.58 &#x00B1; 136.35</td>
<td valign="top" align="center">8.57</td>
<td valign="top" align="center">23.83</td>
<td valign="top" align="center">0.001</td>
<td valign="top" align="center">52.46</td>
<td/>
</tr>
<tr>
<td valign="top" align="left" colspan="6">Ovary-cell proliferation (# BrdU + cells/area)</td>
<td valign="top" align="center">0.89</td>
</tr>
<tr>
<td valign="top" align="left">Intercept</td>
<td valign="top" align="center">3.64 &#x00B1; 0.18</td>
<td/>
<td/>
<td valign="top" align="center">&#x003C;0.001</td>
<td/>
<td/>
</tr>
<tr>
<td valign="top" align="left"><italic>in situ</italic> vs. <italic>ex situ</italic></td>
<td valign="top" align="center">&#x2013;2.56 &#x00B1; 0.26</td>
<td valign="top" align="center">7.61</td>
<td valign="top" align="center">99.31</td>
<td valign="top" align="center">&#x003C;0.001</td>
<td valign="top" align="center">24.71</td>
<td/>
</tr>
<tr>
<td valign="top" align="left" colspan="6">Body mass (g)</td>
<td valign="top" align="center">0.31</td>
</tr>
<tr>
<td valign="top" align="left">Intercept</td>
<td valign="top" align="center">17.72 &#x00B1; 0.50</td>
<td/>
<td/>
<td valign="top" align="center">&#x003C;0.001</td>
<td/>
<td/>
</tr>
<tr>
<td valign="top" align="left"><italic>in situ</italic> vs. <italic>ex situ</italic></td>
<td valign="top" align="center">&#x2013;1.73 &#x00B1; 0.71</td>
<td valign="top" align="center">7.96</td>
<td valign="top" align="center">5.97</td>
<td valign="top" align="center">0.041</td>
<td valign="top" align="center">1.48</td>
<td/>
</tr>
<tr>
<td valign="top" align="left" colspan="6">Body length (mm)</td>
<td valign="top" align="center">0.32</td>
</tr>
<tr>
<td valign="top" align="left">Intercept</td>
<td valign="top" align="center">67.27 &#x00B1; 0.73</td>
<td/>
<td/>
<td valign="top" align="center">&#x003C;0.001</td>
<td/>
<td/>
</tr>
<tr>
<td valign="top" align="left"><italic>in situ</italic> vs. <italic>ex situ</italic></td>
<td valign="top" align="center">&#x2013;3.35 &#x00B1; 1.04</td>
<td valign="top" align="center">7.90</td>
<td valign="top" align="center">10.39</td>
<td valign="top" align="center">0.012</td>
<td valign="top" align="center">3.09</td>
<td/>
</tr>
<tr>
<td valign="top" align="left" colspan="6">Self-righting (sec)</td>
<td valign="top" align="center">0.26</td>
</tr>
<tr>
<td valign="top" align="left">Intercept</td>
<td valign="top" align="center">0.94 &#x00B1; 0.20</td>
<td/>
<td/>
<td valign="top" align="center">0.003</td>
<td/>
<td/>
</tr>
<tr>
<td valign="top" align="left"><italic>in situ</italic> vs. <italic>ex situ</italic></td>
<td valign="top" align="center">1.14 &#x00B1; 0.31</td>
<td valign="top" align="center">7.42</td>
<td valign="top" align="center">13.99</td>
<td valign="top" align="center">0.007</td>
<td valign="top" align="center">&#x2013;6.16</td>
<td/>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="tfn2"><p><italic>cAIC, conditional Akaike information criteria; &#x03B2; &#x00B1; SE, regression coefficient &#x00B1; standard error; d.f., degrees of freedom calculated by Welch&#x2013;Satterthwaite equation; F, Fratio; p, p-value; ES, effect size calculated by Glass&#x2019;s &#x0394;; R<sup>2</sup>, marginal coefficient of determination.</italic></p></fn>
</table-wrap-foot>
</table-wrap>
<p><italic>In situ</italic> hatchlings showed on average 253.72 and 502.09 more proliferating cells in the dorsal (<italic>in situ</italic>: 491.04 &#x00B1; 186.63 vs. <italic>ex situ</italic>: 237.32 &#x00B1; 158.5 BrdU + cells/mm<sup>2</sup> mean &#x00B1; SD; <italic>p</italic> = 0.014) and medial ventricular zones (<italic>in situ</italic>: 1005.45 &#x00B1; 468.77 vs. <italic>ex situ</italic>: 503.36 &#x00B1; 333.62 BrdU + cells/mm<sup>2</sup> mean &#x00B1; SD; <italic>p</italic> = 0.031), respectively (<xref ref-type="fig" rid="F3">Figure 3</xref> and <xref ref-type="table" rid="T2">Table 2</xref>) than <italic>ex situ</italic> incubated offspring. They also showed on average 148.26 and 664.82 more mature neurons in the dorsomedial (<italic>in situ</italic>: 2033.85 &#x00B1; 151.42 vs. <italic>ex situ</italic>: 1885.59 &#x00B1; 157.67 NeuN + cells/mm<sup>2</sup> mean &#x00B1; SD; <italic>p</italic> = 0.041) and medial cortices (<italic>in situ</italic>: 2061.57 &#x00B1; 283.11 vs. <italic>ex situ</italic>: 1396.75 &#x00B1; 541.07 NeuN + cells/mm<sup>2</sup> mean &#x00B1; SD; <italic>p</italic> = 0.001), respectively (<xref ref-type="fig" rid="F4">Figure 4</xref> and <xref ref-type="table" rid="T2">Table 2</xref>) than <italic>ex situ</italic> hatchlings. The best models for dorsal and medial ventricular zone cell proliferation explained 33 and 28% of the data variation, while those for the dorsomedial and medial cortices explained 18 and 37% of the data variation (<xref ref-type="table" rid="T2">Table 2</xref>).</p>
<fig id="F3" position="float">
<label>FIGURE 3</label>
<caption><p>Cell proliferation in neurogenic niches of <italic>L. olivacea</italic> hatchlings. <bold>(A)</bold> Schematic drawing of turtle brain hemi-section showing the dorsal (Dvz, dotted line) and medial ventricular zone (Mvz, continuous dark line), lining the lateral ventricle. <bold>(B)</bold> Timeline for 5&#x2032;-bromo-2&#x2032;-deoxyuridine (BrdU) pulse-chase protocol for cell proliferation analysis. <bold>(C,D)</bold> Representative brain sections showing BrdU + nuclei in the Dvz (open arrow) and Mvz (filled arrow) of one turtle from each condition (<italic>in situ</italic> and <italic>ex situ</italic>, respectively). <bold>(E,F)</bold> Representative high magnification photographs showing BrdU + nuclei in the Dvz of one turtle from each condition (<italic>in situ</italic> and <italic>ex situ</italic>, respectively). <bold>(G,H)</bold> Representative high magnification photographs showing BrdU + nuclei in the Mvz of one turtle from each condition (<italic>in situ</italic> and <italic>ex situ</italic>, respectively). <bold>(I,J)</bold> Graphs showing the density of BrdU + nuclei. <italic>In situ</italic> (<italic>n</italic> = 5), <italic>ex situ</italic> (<italic>n</italic> = 5). Mean &#x00B1; SD, Type III Analysis of Variance &#x002A;<italic>p</italic> &#x2264; 0.05, scale bar = 200 &#x03BC;m for panels <bold>(C,D)</bold> and 50 &#x03BC;m for panels <bold>(E&#x2013;H)</bold>.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-10-850612-g003.tif"/>
</fig>
<fig id="F4" position="float">
<label>FIGURE 4</label>
<caption><p>Neuronal integration in brain areas homologous to the mammalian hippocampus in <italic>L. olivacea</italic> hatchlings. <bold>(A)</bold> Schematic drawing of turtle brain hemi-section showing the dorsomedial (Dmc, stripes) and medial (Mc, stippled) cortices. <bold>(B)</bold> Timeline for neuronal integration analysis. <bold>(C,D)</bold> Representative brain sections showing neuronal nuclear protein (NeuN) in the Dmc and Mc of one turtle from each condition (<italic>in situ</italic> and <italic>ex situ</italic>, respectively). <bold>(E,F)</bold> Representative high magnification photographs showing NeuN + nuclei in the Dmc of one turtle from each condition (<italic>in situ</italic> and <italic>ex situ</italic>, respectively). <bold>(G,H)</bold> Representative high magnification photographs showing NeuN + nuclei in the Mc of one turtle from each condition (<italic>in situ</italic> or <italic>ex situ</italic>, respectively). <bold>(I,J)</bold> Graphs showing the density of NeuN + nuclei. <italic>In situ</italic> (<italic>n</italic> = 5), <italic>ex situ</italic> (<italic>n</italic> = 5). Mean &#x00B1; SD, Type III Analysis of Variance &#x002A;<italic>p</italic> &#x2264; 0.05, &#x002A;&#x002A;&#x002A;<italic>p</italic> &#x2264; 0.001, scale bar = 200 &#x03BC;m for panels <bold>(C,D)</bold> and 50 &#x03BC;m for panels <bold>(E&#x2013;H)</bold>.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-10-850612-g004.tif"/>
</fig>
<p>The ovaries from <italic>in situ</italic> incubated hatchlings showed on average 11.99 more proliferating cells (<italic>in situ</italic>: 13.28 &#x00B1; 2.21 vs. <italic>ex situ</italic>: 1.29 &#x00B1; 1.38 BrdU + cells/mm<sup>2</sup> mean &#x00B1; SD; <italic>p</italic> &#x003C; 0.001; <xref ref-type="fig" rid="F5">Figure 5</xref> and <xref ref-type="table" rid="T2">Table 2</xref>) in comparison with ovaries from <italic>ex situ</italic> offspring. The best model for ovarian cell proliferation explained 89% of the data variation (<xref ref-type="table" rid="T2">Table 2</xref>). Cell density and architecture were evaluated in sections with hematoxylin/eosin staining after BrdU quantification, but it was not possible to quantify the number of ovarian cells due to section thickness (<xref ref-type="supplementary-material" rid="DS1">Supplementary Figure 1</xref>).</p>
<fig id="F5" position="float">
<label>FIGURE 5</label>
<caption><p>Ovarian cell proliferation in <italic>L. olivacea</italic> females. <bold>(A)</bold> Schematic drawing of the turtle gonad-mesonephros complex. <bold>(B)</bold> Timeline for ovarian cell proliferation analysis. <bold>(C,D)</bold> Representative ovarian sections showing 5&#x2032;-bromo-2&#x2032;-deoxyuridine (BrdU) + nuclei in one turtle from each condition (<italic>in situ</italic> and <italic>ex situ</italic>, respectively). <bold>(E,F)</bold> Representative high magnification photographs showing BrdU + nuclei in the ovarian cortex of one turtle from each condition (<italic>in situ</italic> and <italic>ex situ</italic>, respectively). <bold>(G)</bold> Graph showing the density of ovarian BrdU + nuclei. <italic>In situ</italic> (<italic>n</italic> = 5), <italic>ex situ</italic> (<italic>n</italic> = 5). Mean &#x00B1; SD, Type III Analysis of Variance &#x002A;&#x002A;&#x002A;<italic>p</italic> &#x2264; 0.001, scale bar = 200 &#x03BC;m for panels <bold>(C,D)</bold> and 50 &#x03BC;m for panels <bold>(E,F)</bold>.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-10-850612-g005.tif"/>
</fig>
<p>Turtles from <italic>in situ</italic> clutches were on average 1.66 g heavier (<italic>in situ</italic>: 17.65 &#x00B1; 1.35 g vs. <italic>ex situ</italic>: 15.99 &#x00B1; 1.1 g mean &#x00B1; SD; <italic>p</italic> = 0.041; <xref ref-type="fig" rid="F6">Figure 6A</xref> and <xref ref-type="table" rid="T2">Table 2</xref>), and 3.34 mm larger than <italic>ex situ</italic> offspring (<italic>in situ</italic>: 67.22 &#x00B1; 2.50 mm vs. <italic>ex situ</italic>: 63.88 &#x00B1; 2.33 mm mean &#x00B1; SD; <italic>p</italic> = 0.012; <xref ref-type="fig" rid="F6">Figure 6B</xref> and <xref ref-type="table" rid="T2">Table 2</xref>). Additionally, <italic>in situ</italic> incubated hatchlings were on average 5.49 s faster for self-righting (<italic>in situ</italic>: 2.56 &#x00B1; 8.45 s vs. <italic>ex situ</italic>: 8.05 &#x00B1; 6.90 s mean &#x00B1; SD; <italic>p</italic> = 0.007; <xref ref-type="fig" rid="F6">Figure 6C</xref> and <xref ref-type="table" rid="T2">Table 2</xref>) than <italic>ex situ</italic> hatchlings. The best model for body mass explained 31% of the data variation, while the model for body length explained 32% of the data variation and that for self-righting explained 26% of data variation (<xref ref-type="table" rid="T2">Table 2</xref>).</p>
<fig id="F6" position="float">
<label>FIGURE 6</label>
<caption><p>Body size and self-righting time of <italic>L. olivacea</italic> hatchlings. <bold>(A)</bold> Graph showing body mass. <bold>(B)</bold> Graph of body length. <bold>(C)</bold> Graph of self-righting time. <italic>In situ</italic> (<italic>n</italic> = 5), <italic>ex situ</italic> (<italic>n</italic> = 5). Mean &#x00B1; SD, Type III Analysis of Variance &#x002A;<italic>p</italic> &#x2264; 0.05, &#x002A;&#x002A;<italic>p</italic> &#x2264; 0.01.</p></caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-10-850612-g006.tif"/>
</fig>
</sec>
<sec sec-type="discussion" id="S4">
<title>Discussion</title>
<p>This work shows that <italic>ex situ</italic> protection of eggs in hatcheries can result in developmental deficits (compared to <italic>in situ</italic> nests) in female hatchlings, expanding our prior report in males (<xref ref-type="bibr" rid="B47">Herrera-Vargas et al., 2017</xref>). Herein, the <italic>ex situ</italic> incubation strategy was related to negative effects on neurogenesis, ovariogenesis, body size, and motor performance. Turtles from <italic>ex situ</italic> clutches showed lower cell proliferation in the ovary and neurogenic niches, as well as fewer differentiated neurons in brain areas homologous to the mammalian CA1/CA3 hippocampal regions and dentate gyrus. Additionally, newly hatched turtles from <italic>ex situ</italic> clutches showed lower body size and lesser motor abilities. Many factors could potentially account for the negative effects of <italic>ex situ</italic> incubation on offspring development. This study focused on the nest microenvironment (sand temperature, moisture, and sediment particle size). The PCA showed that this microenvironment was related to turtle phenotypes. However, the isolated contribution of the different abiotic variables to development could not be disentangled. A main limitation of this study was an impossibility to differentiate the effects of hatchery incubation from the effects of egg movement and reburial as well as genetic factors (i.e., parental origin). Of note, this study used a relatively small number of nests over a relatively narrow, but important, temperature range.</p>
<sec id="S4.SS1">
<title><italic>Ex situ</italic> Protection in Hatcheries Is Associated With a Lower Rate of Neurogenesis in Turtle Hatchlings</title>
<p>To evaluate the effect of <italic>ex situ</italic> incubation while minimizing the effect of turtle retention, two important events for early neurogenesis were evaluated 6 h after nest emergence: cell proliferation in neurogenic niches and neuron integration in cortices homologous to the mammalian hippocampus. The results showed that the <italic>ex situ</italic> incubation strategy is associated with a lower number of proliferating cells and differentiated neurons in turtle hatchlings. In vertebrates, hippocampal neurogenesis is a highly regulated process that includes cell proliferation, migration, differentiation and integration (<xref ref-type="bibr" rid="B5">Altman and Das, 1965</xref>; <xref ref-type="bibr" rid="B35">Gage, 2002</xref>; <xref ref-type="bibr" rid="B10">Bayer and Altman, 2004</xref>; <xref ref-type="bibr" rid="B51">Kuhn et al., 2016</xref>; <xref ref-type="bibr" rid="B63">McDonald and Vickaryous, 2018</xref>). Proper development of the mammalian hippocampus is required to achieve ecologically relevant cognitive tasks such as spatial learning and memory, as well as to regulate emotional responses (<xref ref-type="bibr" rid="B41">Gould et al., 1999</xref>; <xref ref-type="bibr" rid="B26">Deng et al., 2010</xref>).</p>
<p>In reptiles, newly born cells from the dorsal and lateral ventricular zones migrate radially for several days and mature as neurons as they approach the cortices. Neurogenic niches in the postnatal gecko brain produce neurons exclusively (<xref ref-type="bibr" rid="B63">McDonald and Vickaryous, 2018</xref>). Thus, it is highly likely that the BrdU + cells we observed herein were neuronal progenitors. Nonetheless, future cell-fate mapping studies should confirm the lineage of BrdU + cells produced in newly emerged sea turtles. In this study, BrdU + cells were only present lining the ventricular walls in both conditions, confirming the idea that proliferating neurons migrate several days after birth.</p>
<p>Offspring from <italic>ex situ</italic> clutches showed fewer BrdU + proliferating cells early after nest emergence, suggesting that a lower number of neural precursors will migrate to hippocampal cortices postnatally. Thus, less neurons (or glial cells) differentiate and integrate into functional circuits. Similarly, the lower density of NeuN + cells observed in the medial and dorsomedial cortices of hatchlings from <italic>ex situ</italic> clutches could reflect deficient prenatal cell proliferation or precursor migration. The difference between <italic>in situ</italic> and <italic>ex situ</italic> conditions for NeuN + cells was higher in the medial cortex, suggesting differential cortical sensitivity to early non-optimal conditions, as observed in mammals (<xref ref-type="bibr" rid="B4">Alkadhi, 2019</xref>). These findings, together with our prior work in male hatchlings (<xref ref-type="bibr" rid="B47">Herrera-Vargas et al., 2017</xref>), suggest that <italic>ex situ</italic> incubation alters neurogenic events during critical prenatal and early postnatal windows. The functional relevance of our findings for sea turtle cognitive and behavioral performance in the short and long-term are still unknown. However, recent evidence in lizards supports prior studies in mammals and birds, showing that a disturbance in neurogenesis during development could impair spatial memory and migration either during early life or adulthood (<xref ref-type="bibr" rid="B6">Amiel et al., 2017</xref>; <xref ref-type="bibr" rid="B24">Dayananda and Webb, 2017</xref>). Interestingly, these studies have related non-optimal incubation temperatures with decreased hippocampal neurogenesis in lizards (<xref ref-type="bibr" rid="B6">Amiel et al., 2017</xref>; <xref ref-type="bibr" rid="B24">Dayananda and Webb, 2017</xref>). Herein, nest temperature, moisture, and substrate composition differentiate <italic>in situ</italic> vs. <italic>ex situ nests</italic>; however, neither isolated abiotic variable was directly associated to altered neurogenesis in hatchling turtles. Follow-up studies should experimentally assess the effect of either variable separately or as a whole on hippocampal cell proliferation and neuronal integration early during ontogenesis in sea turtles.</p>
<p>Brain development begins at stage III (incubation day 4) in <italic>Caretta caretta</italic> turtles (<xref ref-type="bibr" rid="B37">Garc&#x00ED;a-Cerd&#x00E1; and L&#x00F3;pez-Jurado, 2009</xref>). Thus, early relocation to hatcheries is not likely to account for the observed developmental alterations. However, future studies should be done to rule-out this possibility.</p>
</sec>
<sec id="S4.SS2">
<title><italic>Ex situ</italic> Incubation Is Associated With a Lower Ovarian Cell Proliferation in <italic>Lepidochelys olivacea</italic> Hatchlings</title>
<p>The <italic>ex situ</italic> incubation strategy was associated with a dramatic reduction of ovarian cell proliferation in turtle hatchlings at nest emergence, evidenced by few BrdU + cells. In <italic>L. olivacea</italic>, gonadal development starts in the middle third of incubation (day 16 of development), when primordial germ cells accumulate at the base of gonadal ridge (<xref ref-type="bibr" rid="B68">Merchant-Larios et al., 1997</xref>). In this species, warm temperatures (32&#x2013;33&#x00B0;C) promote ovary formation by stimulating the production of estradiol and aromatase from the undifferentiated gonad and adjacent tissues: the mesonephros and inter-renal glands (<xref ref-type="bibr" rid="B110">Wibbels et al., 1991</xref>, <xref ref-type="bibr" rid="B111">1993</xref>; <xref ref-type="bibr" rid="B31">Ewert et al., 2004</xref>; <xref ref-type="bibr" rid="B34">Freedberg et al., 2006</xref>; <xref ref-type="bibr" rid="B27">D&#x00ED;az-Hern&#x00E1;ndez et al., 2015</xref>, <xref ref-type="bibr" rid="B28">2017</xref>). The highest peak of ovarian cell proliferation is not known for <italic>L. olivacea</italic> hatchlings. However, folliculogenesis and oocyte entry into meiosis occur in the 3rd&#x2013;5th post-hatching months (<xref ref-type="bibr" rid="B69">Merchant-Larios et al., 1989</xref>), suggesting that this peak occurs perinatally. The consequences of reduced germ cell proliferation in female juvenile or adult turtles have not been evaluated. In rodents, germ cell absence does not allow ovarian follicle development (<xref ref-type="bibr" rid="B66">McLaren et al., 1984</xref>) or results in follicle degeneration (<xref ref-type="bibr" rid="B78">Ray and Potu, 2010</xref>; <xref ref-type="bibr" rid="B12">Bishop et al., 2019</xref>). In mammals, reduced cell proliferation may result in delayed ovarian formation or even complete infertility (<xref ref-type="bibr" rid="B72">Monniaux, 2018</xref>).</p>
<p>In this study, ovarian weight was not formally evaluated, since each was dissected together with the mesonephros. Interestingly, qualitative histological observations of ovarian sections did not obviously evidence a reduction in cell density. Herein, the main variable explaining the diminished ovarian cell proliferation was the <italic>ex situ</italic> condition, which probably included the effect of incubation temperature plus moisture and substrate composition. Future studies are needed to identify the effects of <italic>ex situ</italic> incubation on ovarian cell density, evaluate the contribution of each abiotic variable on the ovarian phenotype and elucidate the long-term effects of poorly developed ovaries.</p>
</sec>
<sec id="S4.SS3">
<title><italic>Ex situ</italic> Incubation Is Related to a Lower Body Size and Motor Performance at Nest Emergence</title>
<p>Hatchlings from <italic>ex situ</italic> clutches showed a lower body mass and straight carapace length than those from <italic>in situ</italic> nests. Linear mixed models for body mass and length suggested that the nest condition (<italic>in situ</italic> vs. <italic>ex situ</italic>) was an important factor influencing them. A direct contribution of isolated abiotic variables could not be identified. However, it is known that temperature plays a chief role determining reptile body size (<xref ref-type="bibr" rid="B95">Stewart et al., 2019</xref>). Although sand temperatures were above the threshold to promote female differentiation in both conditions, they likely differentially affected hatchling body size, as previously suggested (<xref ref-type="bibr" rid="B81">Robledo-Avila et al., 2022</xref>). Mean sand temperatures registered for <italic>in situ</italic> clutches were approximately 1&#x00B0;C below those in <italic>ex situ</italic> clutches, whereas mean maximum temperatures registered for both conditions showed broader ranges (35.68&#x00B0;C &#x00B1; 0.83 SD for <italic>in situ</italic> nests and 37.03&#x00B0;C &#x00B1; 1.29 SD for <italic>ex situ</italic> nests). Accordingly, the incubation duration was shorter by one day for <italic>ex situ</italic> clutches.</p>
<p>The mechanisms that may account for a differential temperature effect on the growth rate include a direct action on cell, tissue, or organ differentiation, as well as long-term neuroendocrine changes possibly <italic>via</italic> epigenetic alterations (<xref ref-type="bibr" rid="B91">Singh et al., 2020</xref>). Additionally, it is recognized that moisture also plays a role on body size, although the mechanisms are less well known. Modifications to gas exchange could explain the effects of moisture on development (<xref ref-type="bibr" rid="B107">Wallace et al., 2004</xref>). Other variables, such as nesting female size (<xref ref-type="bibr" rid="B19">Chatting et al., 2018</xref>), egg mass (<xref ref-type="bibr" rid="B108">Wallace et al., 2006</xref>), metabolic expenditure (<xref ref-type="bibr" rid="B82">Rusli et al., 2016</xref>; <xref ref-type="bibr" rid="B36">Gammon et al., 2020</xref>), or yolk absorption (<xref ref-type="bibr" rid="B94">Stand, 2002</xref>) also may contribute to determining body size in reptiles. A study showed an interaction between the maternal component, sand temperature, moisture, and body length in the loggerhead sea turtles. Moreover, it described differential effects of moisture on body length throughout development (i.e., a more prominent role of nest moisture on body mass during the last third of development; <xref ref-type="bibr" rid="B101">Tezak et al., 2020</xref>). Thus, the combined contribution of several abiotic and biotic variables could explain our results, as discussed below.</p>
<p>A larger body size has been consistently related with better motor performance and thus with better survival chances (<xref ref-type="bibr" rid="B32">Fleming et al., 2020</xref>; <xref ref-type="bibr" rid="B60">Martins et al., 2020</xref>). In this study, principal component 1 showed a negative relationship between body mass and length with self-righting ability, supporting prior observations. Moreover, self-righting has been associated with incubatory conditions like temperature and substrate composition, therefore constituting a good indicator of microenvironmental conditions (<xref ref-type="bibr" rid="B95">Stewart et al., 2019</xref>; <xref ref-type="bibr" rid="B79">Reboul et al., 2021</xref>). Herein, nest silt and temperature were related to increased turning time of hatchlings, in accordance with prior studies (<xref ref-type="bibr" rid="B95">Stewart et al., 2019</xref>; <xref ref-type="bibr" rid="B79">Reboul et al., 2021</xref>).</p>
</sec>
<sec id="S4.SS4">
<title>Impact of Abiotic Variables on Developmental Responses</title>
<p>Several nest-related abiotic variables were measured to determine their potential contribution to the observed developmental effects in <italic>L. olivacea</italic> hatchlings. The results showed that <italic>in situ</italic> clutch conditions were related to a better turtle phenotype (i.e., greater body size, higher neurogenesis, increased ovariogenesis, and lesser time to self-righting). <italic>In situ</italic> nests showed lower temperatures, were located higher on the beach and in coarse sand with lower silt levels, while <italic>ex situ</italic> clutches showed the opposite. Accordingly, sand composition, temperature, and moisture were important for differences between <italic>in situ</italic> and <italic>ex situ</italic> clutches. However, a differential contribution of each abiotic variable, in isolation, to the developmental traits could not be identified. One possible explanation is that emergent properties of microenvironment-associated abiotic variables affect the turtle hatchling development. Recent reports support this idea (<xref ref-type="bibr" rid="B101">Tezak et al., 2020</xref>; <xref ref-type="bibr" rid="B99">Tanabe et al., 2021</xref>).</p>
<p>Interestingly, although <italic>in situ</italic> nests showed lower temperatures than <italic>ex situ</italic> nests, the average temperatures for the incubation period, as well the mean maximum temperatures for both conditions were above the thermal tolerance reported for <italic>L. olivacea</italic> embryos (<xref ref-type="bibr" rid="B105">Valverde et al., 2010</xref>; <xref ref-type="bibr" rid="B61">Maulany et al., 2012</xref>). Temperature is a chief parameter that determines brain, gonadal and motor system development (<xref ref-type="bibr" rid="B80">Reece et al., 2002</xref>; <xref ref-type="bibr" rid="B7">Amiel and Shine, 2012</xref>; <xref ref-type="bibr" rid="B74">Paredes et al., 2016</xref>; <xref ref-type="bibr" rid="B6">Amiel et al., 2017</xref>; <xref ref-type="bibr" rid="B32">Fleming et al., 2020</xref>), as well embryo survival inside the nest (<xref ref-type="bibr" rid="B81">Robledo-Avila et al., 2022</xref>). Thus, it likely also plays a major role in explaining the observed phenotypes. However, its direct contribution could not be determined.</p>
<p><italic>Ex situ</italic> clutches showed a higher silt proportion, which was negatively associated with hatchling development. Previous studies have shown that successful embryo development occurs in sandy substrates (grain diameter: 0.063&#x2013;2 mm), whereas substrates with a high silt content (grain size &#x003C; 0.063) cause mortality and diminished egg weight, reduced hatchling mass and size, as well as lower fitness (<xref ref-type="bibr" rid="B89">Sarmiento-Ram&#x00ED;rez et al., 2014</xref>; <xref ref-type="bibr" rid="B59">Marco et al., 2017</xref>). The proportion of silt observed in both incubation conditions was below the value described as detrimental for embryo development (0.02; <xref ref-type="bibr" rid="B1">Abella-P&#x00E9;rez, 2011</xref>). Thus, although its effects on neurogenesis, ovariogenesis, body size, and motor abilities should not be ruled out, silt is unlikely to completely explain the observed phenotypes. The proportion of silt may affect moisture, gas exchange and/or microbial load (<xref ref-type="bibr" rid="B59">Marco et al., 2017</xref>).</p>
<p>Alternatively, the scarce contribution of sediment size, temperature, and moisture to completely explain the observed phenotypes could result from procedural details. Sand temperature was recorded before the thermosensitive period began (developmental day 11), until turtle emergence to avoid disturbing egg development. This interval includes the peak of hippocampal neurogenesis and the critical window for sex determination. Surface sand (10 cm deep) was sampled for moisture and particle size measurements right after turtles emerged. Future studies should record the temperature inside the nest during the entire incubation period and collect sand surrounding the eggs. This should verify the microenvironmental contribution to the effects of clutch relocation on development of sea turtle hatchlings. Moreover, future experiments should measure temperature inside the nest to consider the effect of metabolic heating on the observed phenotypes.</p>
<p>It must be noted that the <italic>ex situ</italic> incubation strategy, <italic>per se</italic> likely did not directly affect hatchling development. However, the combined effect of the incubation microenvironment was probably directly to blame for the phenotypic effects. This idea is supported by our prior study on the action of <italic>ex situ</italic> nests on the configuration of the immune system (<xref ref-type="bibr" rid="B81">Robledo-Avila et al., 2022</xref>).</p>
<p>Besides the measured abiotic factors, other variables such as micro-biological parameters (<xref ref-type="bibr" rid="B75">Patino-Mart&#x00ED;nez et al., 2012</xref>) may explain the developmental changes. Recent split-clutch designs have highlighted the maternal contribution to hatchling body size and self-righting response (<xref ref-type="bibr" rid="B50">Kobayashi et al., 2020</xref>; <xref ref-type="bibr" rid="B101">Tezak et al., 2020</xref>). This study did not consider the maternal component to privilege normal conditions (i.e., leaving natural nests undisturbed). However, parental origin, egg movement, and reburial should be studied to identify the factors that determine the altered phenotypes. These studies will result in recommendations for hatchery management to maximize the developmental potential of sea turtles.</p>
</sec>
</sec>
<sec sec-type="conclusion" id="S5">
<title>Conclusion</title>
<p><italic>Ex situ</italic> protection in hatcheries is undoubtedly the only choice if <italic>in situ</italic> incubation is not viable. However, our results suggest that this strategy can be associated with negative effects on sea turtle phenotypes. This include reduced neurogenesis, ovariogenesis, and motor performance during critical windows of development. Our results suggest a synergic effect of environmental variables on the observed phenotypes, but it was not possible to identify a differential contribution of each factor alone. More research should be done on the impact of <italic>ex situ</italic> incubation on cognitive, behavioral, and reproductive performance of juvenile or adult sea turtles experimentally manipulating abiotic variables.</p>
</sec>
<sec sec-type="data-availability" id="S6">
<title>Data Availability Statement</title>
<p>The original contributions presented in the study are included in the article/<xref ref-type="supplementary-material" rid="DS1">Supplementary Material</xref>, further inquiries can be directed to the corresponding authors.</p>
</sec>
<sec id="S7">
<title>Ethics Statement</title>
<p>The animal study was reviewed and approved by Secretar&#x00ED;a de Medio Ambiente y Recursos Naturales SGPA/DGVS/10395/17.</p>
</sec>
<sec id="S8">
<title>Author Contributions</title>
<p>NU-D and CA: methodology and investigation. BP-F: formal analysis, writing &#x2013; original draft, review, and editing. HN: formal analysis and writing &#x2013; review and editing. LL-T and CM: methodology and formal analysis. NL and LT: visualization and supervision. MH-V: methodology. AF-F: conceptualization and funding acquisition. EM-H: conceptualization, data curation, writing &#x2013; original draft, review, and editing. All authors contributed to the article and approved the submitted version.</p>
</sec>
<sec id="conf1" sec-type="COI-statement">
<title>Conflict of Interest</title>
<p>The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.</p>
</sec>
<sec id="pudiscl1" sec-type="disclaimer">
<title>Publisher&#x2019;s Note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
</sec>
</body>
<back>
<sec sec-type="funding-information" id="S9">
<title>Funding</title>
<p>This work was supported by the Consejo Nacional de Ciencia y Tecnolog&#x00ED;a (CONACyT no. 258747 to AF-F) and the Coordinaci&#x00F3;n de la Investigaci&#x00F3;n Cient&#x00ED;fica-UMSNH to EM-H and AF-F. NU-D was Ph.D. fellow from CONACYT (grant number 256790).</p>
</sec>
<ack>
<p>We thank M. C. Jos&#x00E9; Alejandro Marmolejo Valencia, Biol. Edel Pineda L&#x00F3;pez, and Biol. Fidel Anguiano Rodr&#x00ED;guez for their valuable technical assistance.</p>
</ack>
<sec id="S11" sec-type="supplementary-material">
<title>Supplementary Material</title>
<p>The Supplementary Material for this article can be found online at: <ext-link ext-link-type="uri" xlink:href="https://www.frontiersin.org/articles/10.3389/fevo.2022.850612/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fevo.2022.850612/full#supplementary-material</ext-link></p>
<supplementary-material xlink:href="Data_Sheet_1.zip" id="DS1" mimetype="application/zip" xmlns:xlink="http://www.w3.org/1999/xlink"/>
</sec>
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