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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.2023.1234562</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>Indirect effects of urbanization: consequences of increased aggression in an urban male songbird for mates and offspring</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Lane</surname>
<given-names>Samuel J.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="author-notes" rid="fn001">
<sup>*</sup>
</xref>
<xref ref-type="author-notes" rid="fn003">
<sup>&#x2020;</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/1660998"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>VanDiest</surname>
<given-names>Isaac J.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/1659749"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Brewer</surname>
<given-names>Valerie N.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="author-notes" rid="fn003">
<sup>&#x2020;</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Linkous</surname>
<given-names>Courtney R.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Fossett</surname>
<given-names>Taylor E.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Goodchild</surname>
<given-names>Christopher G.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="author-notes" rid="fn003">
<sup>&#x2020;</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/1559217"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Sewall</surname>
<given-names>Kendra B.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/377919"/>
</contrib>
</contrib-group>
<aff id="aff1">
<sup>1</sup>
<institution>Department of Biological Sciences, Virginia Tech</institution>, <addr-line>Blacksburg, VA</addr-line>, <country>United States</country>
</aff>
<aff id="aff2">
<sup>2</sup>
<institution>Department of Biological Sciences and School of Neuroscience, Virginia Tech</institution>, <addr-line>Blacksburg, VA</addr-line>, <country>United States</country>
</aff>
<author-notes>
<fn fn-type="edited-by">
<p>Edited by: Zoltan Elek, University of Szeged, Hungary</p>
</fn>
<fn fn-type="edited-by">
<p>Reviewed by: Attila Marton, Babe&#x219;-Bolyai University, Romania; Zolt&#xe1;n N&#xe9;meth, University of Debrecen, Hungary</p>
</fn>
<fn fn-type="corresp" id="fn001">
<p>*Correspondence: Samuel J. Lane, <email xlink:href="mailto:samuellane496@gmail.com">samuellane496@gmail.com</email>
</p>
</fn>
<fn fn-type="present-address" id="fn003">
<p>&#x2020;Present address: Samuel J. Lane, Department of Biological Sciences, North Dakota State University, Fargo, ND, United States; Valerie N. Brewer, Department of Integrative Biology, Oregon State University, Corvallis, OR, United States; Christopher G. Goodchild, Department of Biology, University of Central Oklahoma, Edmond, OK, United States</p>
</fn>
</author-notes>
<pub-date pub-type="epub">
<day>22</day>
<month>08</month>
<year>2023</year>
</pub-date>
<pub-date pub-type="collection">
<year>2023</year>
</pub-date>
<volume>11</volume>
<elocation-id>1234562</elocation-id>
<history>
<date date-type="received">
<day>04</day>
<month>06</month>
<year>2023</year>
</date>
<date date-type="accepted">
<day>18</day>
<month>07</month>
<year>2023</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2023 Lane, VanDiest, Brewer, Linkous, Fossett, Goodchild and Sewall</copyright-statement>
<copyright-year>2023</copyright-year>
<copyright-holder>Lane, VanDiest, Brewer, Linkous, Fossett, Goodchild and Sewall</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>Behavioral traits are often the first response to changing environmental conditions, including human induced rapid environmental change. For example, animals living in urban areas are often more aggressive than rural animals. This is especially evident in songbirds; males of several species display elevated aggression in urban habitats. Increased male aggression has been associated with reduced parental care, but the consequences of this trade-off for males, social partners, and offspring in the context of urbanization remains unclear. We explored the effects of increased urban male aggression on the life history traits, parental care, and offspring outcomes of song sparrows (<italic>Melospiza melodia</italic>). We predicted that urban males would reduce paternal investment and result in urban females providing greater nestling care or reduced fledging success in urban habitats compared to rural. Contrary to our prediction, aggressive urban males did not decrease care but visited the nest more often compared to rural males. Additionally, urban birds had higher nest and fledging success compared to rural, though this was largely due to higher nest predation in rural habitats. Our study is among the first to evaluate trade-offs associated with elevated aggression expressed by urban animals and adds to a growing body of evidence that urban habitats provide benefits to some species.</p>
</abstract>
<kwd-group>
<kwd>fitness</kwd>
<kwd>parental care</kwd>
<kwd>territorial aggression</kwd>
<kwd>trade-offs</kwd>
<kwd>urbanization</kwd>
</kwd-group>
<counts>
<fig-count count="6"/>
<table-count count="1"/>
<equation-count count="0"/>
<ref-count count="110"/>
<page-count count="13"/>
<word-count count="7253"/>
</counts>
<custom-meta-wrap>
<custom-meta>
<meta-name>section-in-acceptance</meta-name>
<meta-value>Urban Ecology</meta-value>
</custom-meta>
</custom-meta-wrap>
</article-meta>
</front>
<body>
<sec id="s1" sec-type="intro">
<label>1</label>
<title>Introduction</title>
<p>Life-history theory is structured around the idea that the evolution of suites of traits meant to maximize an individual&#x2019;s fitness constrain each other and consequently generate trade-offs (<xref ref-type="bibr" rid="B102">Stearns, 1992</xref>; <xref ref-type="bibr" rid="B82">Reznick et&#xa0;al., 2000</xref>; <xref ref-type="bibr" rid="B85">Roff and Fairbairn, 2007</xref>). With time and energy being limited, behavioral trade-offs occur when animals must strike a balance among behaviors that are energetically costly or require substantial time. The habitat in which an individual lives has been shown to modulate trade-offs between behaviors, because the environmental context determines an animal&#x2019;s time and energy budget, and the extent to which behaviors constrain each other (<xref ref-type="bibr" rid="B39">Gunnarsson et&#xa0;al., 2005</xref>; <xref ref-type="bibr" rid="B42">Holtmann et&#xa0;al., 2017</xref>). Resource availability, conspecific density, predator presence, and heterospecific interactions are among the contextual factors that determine an individual&#x2019;s capacity to maximize fitness linked traits (<xref ref-type="bibr" rid="B53">Linden and M&#xf8;ller, 1989</xref>; <xref ref-type="bibr" rid="B58">Martin, 1995</xref>), all of which are being altered by global anthropogenic change (<xref ref-type="bibr" rid="B67">McKinney, 2008</xref>; <xref ref-type="bibr" rid="B38">Grimm et&#xa0;al., 2008b</xref>). Supporting the expansion of species to urban habitats can maintain urban biodiversity as human expansion continues (<xref ref-type="bibr" rid="B65">McKinney, 2002</xref>; <xref ref-type="bibr" rid="B38">Grimm et&#xa0;al., 2008b</xref>). However, urban habitats present wildlife with an altered abiotic and biotic landscape in which to live and reproduce (<xref ref-type="bibr" rid="B15">Chace and Walsh, 2006</xref>; <xref ref-type="bibr" rid="B37">Grimm et&#xa0;al., 2008a</xref>) that may modify the trade-offs among life-history traits.</p>
<p>Many species of songbirds have readily adjusted to cities, but breeding adults likely face new or exaggerated challenges not present in their native habitats. One way that animals can adjust to novel conditions is by shifting how they resolve life-history trade-offs. Urban habitats contain anthropogenic predators (e.g., domestic cats) (<xref ref-type="bibr" rid="B54">Loss et&#xa0;al., 2013</xref>; <xref ref-type="bibr" rid="B87">Rosenberg et&#xa0;al., 2019</xref>) that influence survival rates of both offspring and adults (<xref ref-type="bibr" rid="B7">Baker et&#xa0;al., 2008</xref>; <xref ref-type="bibr" rid="B104">van Heezik et&#xa0;al., 2010</xref>). These habitats are more fragmented than native habitats with different resource distribution and availability (<xref ref-type="bibr" rid="B89">Saunders et&#xa0;al., 1991</xref>; <xref ref-type="bibr" rid="B15">Chace and Walsh, 2006</xref>; <xref ref-type="bibr" rid="B66">McKinney, 2006</xref>). Finally, obligate brood parasites tend to follow fragmentation and human disturbance (<xref ref-type="bibr" rid="B14">Brittingham and Temple, 1983</xref>; <xref ref-type="bibr" rid="B83">Robinson et&#xa0;al., 1995</xref>; <xref ref-type="bibr" rid="B16">Chace et&#xa0;al., 2003</xref>; <xref ref-type="bibr" rid="B84">Rodewald, 2009</xref>; <xref ref-type="bibr" rid="B26">Faaborg et&#xa0;al., 2010</xref>) and may be more prevalent in urban communities. Comparing the behaviors of species in which individuals maintain breeding territories in both urban and rural habitats (termed &#x2018;urban adapters&#x2019;; <xref ref-type="bibr" rid="B10">Blair, 1996</xref>; <xref ref-type="bibr" rid="B65">McKinney, 2002</xref>; <xref ref-type="bibr" rid="B96">Shochat et&#xa0;al., 2006</xref>; <xref ref-type="bibr" rid="B11">Bonier, 2012</xref>), can reveal how individuals re-allocate effort into different life-history behaviors in response to novel urban habitats (<xref ref-type="bibr" rid="B10">Blair, 1996</xref>; <xref ref-type="bibr" rid="B65">McKinney, 2002</xref>; <xref ref-type="bibr" rid="B96">Shochat et&#xa0;al., 2006</xref>; <xref ref-type="bibr" rid="B11">Bonier, 2012</xref>).</p>
<p>One trade-off that could be shifted in urban habitats is the balance between territoriality and paternal care in male songbirds. During the breeding season, male songbirds choose and defend territories with quality nesting substrates and resources needed to survive and rear young (<xref ref-type="bibr" rid="B101">Stamps and Krishnan, 1997</xref>; <xref ref-type="bibr" rid="B31">Garcia and Arroyo, 2002</xref>). In theory, the highest quality males should be the most aggressive and best able to defend the highest quality breeding territories (<xref ref-type="bibr" rid="B72">Otter and Ratcliffe, 1996</xref>; <xref ref-type="bibr" rid="B31">Garcia and Arroyo, 2002</xref>; <xref ref-type="bibr" rid="B91">Scales et&#xa0;al., 2013</xref>) leading to increased fitness (<xref ref-type="bibr" rid="B72">Otter and Ratcliffe, 1996</xref>). Urban habitats often have fewer available breeding territories and resources compared to rural habitats (<xref ref-type="bibr" rid="B47">Ju&#xe1;rez et&#xa0;al., 2020</xref>), and urban habitats likely favor a more aggressive phenotype (<xref ref-type="bibr" rid="B22">Duckworth, 2008</xref>; <xref ref-type="bibr" rid="B30">Foltz et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B47">Ju&#xe1;rez et&#xa0;al., 2020</xref>). Indeed, one behavioral pattern found in many urban populations (<xref ref-type="bibr" rid="B55">Lowry et&#xa0;al., 2013</xref>; <xref ref-type="bibr" rid="B80">Renthlei et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B18">Dammhahn et&#xa0;al., 2020</xref>) but especially in songbirds, is increased male conspecific aggression (<xref ref-type="bibr" rid="B25">Evans et&#xa0;al., 2010</xref>; <xref ref-type="bibr" rid="B29">Fokidis et&#xa0;al., 2011</xref>; <xref ref-type="bibr" rid="B90">Scales et&#xa0;al., 2011</xref>; <xref ref-type="bibr" rid="B5">Atwell et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B20">Davies and Sewall, 2016</xref>). While an exaggerated aggressive phenotype may facilitate territory acquisition in urban habitats, investment in aggressive behavior could result in a trade-off with other energetically costly behaviors, such as parental care (<xref ref-type="bibr" rid="B48">Ketterson and Nolan, 1994</xref>; <xref ref-type="bibr" rid="B49">Ketterson and Nolan, 1999</xref>; <xref ref-type="bibr" rid="B21">Duckworth, 2006</xref>; <xref ref-type="bibr" rid="B64">McGlothlin et&#xa0;al., 2007</xref>). For socially monogamous urban songbirds, any trade-offs in breeding behaviors (i.e., territoriality and parental care) can have consequences for social partners because mates cooperate in rearing young (<xref ref-type="bibr" rid="B39">Gunnarsson et&#xa0;al., 2005</xref>; <xref ref-type="bibr" rid="B42">Holtmann et&#xa0;al., 2017</xref>). Thus, if urban habitats drive shifts in how male songbirds resolve life-history trade-offs, there may also be consequences for their female partners and the condition and survival of their offspring (<xref ref-type="bibr" rid="B62">Marzluff, 2001</xref>; <xref ref-type="bibr" rid="B21">Duckworth, 2006</xref>; <xref ref-type="bibr" rid="B37">Grimm et&#xa0;al., 2008a</xref>; <xref ref-type="bibr" rid="B92">Scolozzi and Geneletti, 2012</xref>).</p>
<p>Many territorial songbird species establish social partnerships during the breeding season to provide biparental care to their offspring (<xref ref-type="bibr" rid="B106">Westneat, 1987</xref>; <xref ref-type="bibr" rid="B4">Arcese, 1989</xref>; <xref ref-type="bibr" rid="B36">Griffith et&#xa0;al., 2002</xref>). This social monogamy allows partners to split the energetic demands of reproduction, so the burden of care does not fall on one individual (<xref ref-type="bibr" rid="B68">M&#xf8;ller and Birkhead, 1993</xref>; <xref ref-type="bibr" rid="B36">Griffith et&#xa0;al., 2002</xref>). However, female&#x2019;s higher energetic investment, and guaranteed genetic relatedness to offspring, means they often show increased reproductive investment compared to males (<xref ref-type="bibr" rid="B106">Westneat, 1987</xref>; <xref ref-type="bibr" rid="B4">Arcese, 1989</xref>; <xref ref-type="bibr" rid="B36">Griffith et&#xa0;al., 2002</xref>). Indeed, prior studies of the consequences of male aggression have highlighted impacts on mates and offspring, including compensatory behaviors and reduced fledging success (<xref ref-type="bibr" rid="B108">Whittingham et&#xa0;al., 1994</xref>; <xref ref-type="bibr" rid="B88">Saino and M&#xf8;ller, 1995</xref>; <xref ref-type="bibr" rid="B73">Paredes et&#xa0;al., 2005</xref>). More aggressive male house finches, for instance, provide less paternal care and females compensate by providing more care (<xref ref-type="bibr" rid="B6">Badyaev and Hill, 2002</xref>). While females can often compensate for reduced care by their male partners, harsh environmental conditions that make compensation impossible can result in smaller offspring or reduced fledging success. If increased aggression in urban males constrains their ability to provide paternal care, this could increase the demands on their social partner to provide greater maternal care.</p>
<p>Here, we investigated the effects of urbanization and the associated increase in male aggression on the parental care provided by males, the care provided by their mates, and the condition and fledging success of their offspring by comparing adult behavior and nestling outcomes among wild song sparrows (<italic>Melospiza melodia</italic>) in urban and rural habitats. Song sparrows are a commonly studied urban adapter that, like many songbird species, are open cup nesters with altricial young, for which biparental parental care is especially vital (<xref ref-type="bibr" rid="B70">Nice, 1943</xref>; <xref ref-type="bibr" rid="B98">Smith and Roff, 1980</xref>; <xref ref-type="bibr" rid="B86">Roff et&#xa0;al., 2005</xref>; <xref ref-type="bibr" rid="B59">Martin and Briskie, 2009</xref>). We hypothesized that urban males, which are reliably more aggressive toward conspecifics, may resolve trade-offs between territoriality and paternal care differently than their rural counterparts and provide less care to offspring. We expected that their social partners would compensate to maintain offspring fitness or, if they could not, nestling growth and survival would be reduced. Specifically, we predicted that urban males would provide less care compared to rural males. We also predicted that maternal care would be positively correlated with social partner aggression, and negatively correlated with paternal care. Finally, we predicted urban nesting success would be lower, and urban offspring would be underdeveloped near fledging compared to rural birds.</p>
</sec>
<sec id="s2">
<label>2</label>
<title>Methods</title>
<sec id="s2_1">
<label>2.1</label>
<title>Parental behavior</title>
<sec id="s2_1_1">
<label>2.1.1</label>
<title>Subjects</title>
<p>To examine the relationship between male aggression, parental visitation, and its effects on social partners, in the breeding seasons of 2018 &#x2013; 2021 we measured parental care at nests located within 6 previously established sites in Southwestern Virginia, USA that vary along an urban-rural gradient (<xref ref-type="bibr" rid="B20">Davies and Sewall, 2016</xref>; <xref ref-type="bibr" rid="B19">Davies et&#xa0;al., 2018</xref>). We only monitored nest outcomes and nestling growth in 2017, all additional parental measures began in 2018. To evaluate the levels of urbanization, <xref ref-type="bibr" rid="B19">Davies et&#xa0;al. (2018)</xref> used an automated system to assign an urbanization score to each site using the protocols described in <xref ref-type="bibr" rid="B94">Seress et&#xa0;al. (2014)</xref> (For detailed descriptions and photos of field sites and for full analysis details see <xref ref-type="bibr" rid="B19">Davies et&#xa0;al., 2018</xref>). After we located a nest and established the breeding stage, we measured male territorial aggression in response to a simulated territorial intrusion following <xref ref-type="bibr" rid="B44">Hyman et&#xa0;al. (2004)</xref> (see below). We performed behavioral trials between April and July of each breeding season (see <xref ref-type="supplementary-material" rid="SM1">
<bold>supplemental materials</bold>
</xref> for a detailed figure outlining our methods timeline).</p>
<p>To monitor parental visitation by focal males and their social partners, we captured adult birds with mist nets between 0500- and 1115-hours from March through July of each year. Of the 288 song sparrow nests monitored during this project (166 urban and 119 rural), we were able to monitor paternal care at 86 nests (67 urban and 19 rural), and maternal care at 54 nests (38 urban and 16 rural). At 43 nests, both the male and female were captured and only these nests were included in the social partner behavior analysis. At all other nests, we were only able to capture either the male or female. We captured males by targeting them immediately after simulated territorial intrusions, while we captured females when they were leaving or returning to the nest. To avoid nest abandonment, we allowed all active nests to reach at least mid- to late-incubation before capture, did not attempt to catch a social pair (a) for more than 120 min/day, (b) during inclement weather, or (c) on sequential days. We took morphological measurements from the adults and banded them with a unique color band. Before releasing each bird, we fitted a passive integrated transponder (PIT) tag (2.12x10mm; CYNTAG, Inc; Item#: 601205-2248) to the tarsometatarsus of each adult following the methods established in <xref ref-type="bibr" rid="B12">Bridge and Bonter (2011)</xref> to monitor parental visitation. The PIT tags are small coils of magnetic wire programed with a unique 10-digit code that can be read by any radio frequency identification (RFID) system (<xref ref-type="bibr" rid="B12">Bridge and Bonter, 2011</xref>; <xref ref-type="bibr" rid="B13">Bridge et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B27">Farr et&#xa0;al., 2021</xref>). We gave every bird a unique combination of color bands and multicolored heat shrink tubing incasing the PIT tags (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1A</bold>
</xref>) to allow us to visually identify individuals using binoculars.</p>
<fig id="f1" position="float">
<label>Figure&#xa0;1</label>
<caption>
<p>A PIT tag attached to the tarsometatarsus of a song sparrow <bold>(A)</bold> and an antenna fitted around a song sparrow nest <bold>(B)</bold> during the 2018 field season. When the magnetic coil built into the PIT tag disrupts the magnetic field created by the antenna the duration of the visit is recorded, time stamped and stored by the microprocessor hidden nearby in a waterproof container.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-11-1234562-g001.tif"/>
</fig>
</sec>
<sec id="s2_1_2">
<label>2.1.2</label>
<title>Male aggression</title>
<p>To examine the tradeoff between male aggression and parental care, we quantified male aggression in 140 males between 2018 and 2021. Of these males, we were also able to monitor parental behavior in 61 (46 urban and 15 rural males). During aggression trials we located focal males based on location of spontaneous singing relative to the active nest and/or in response to brief (&lt; 1&#xa0;min) playback. Once located, we exposed a male to 6&#xa0;min of playback with one of 6 3D printed song sparrow mounts placed at the approximate center of the territory (For details on the design and construction of the 3D printed models please see <xref ref-type="bibr" rid="B9">Beck et&#xa0;al., 2019</xref>). Each playback consisted of 2 song types recorded from the same male designed to approximate a male&#x2019;s natural song (<xref ref-type="bibr" rid="B44">Hyman et&#xa0;al., 2004</xref>; <xref ref-type="bibr" rid="B20">Davies and Sewall, 2016</xref>). To assess male territorial aggression during each playback, we recorded distance to speaker/mount, number of low amplitude songs (soft songs), and number of wing waves each minute (<xref ref-type="bibr" rid="B44">Hyman et&#xa0;al., 2004</xref>; <xref ref-type="bibr" rid="B3">Ak&#xe7;ay et&#xa0;al., 2011</xref>; <xref ref-type="bibr" rid="B20">Davies and Sewall, 2016</xref>; <xref ref-type="bibr" rid="B19">Davies et&#xa0;al., 2018</xref>). To measure the average distance to the speaker during the trials, we recorded the bin distance from the speaker (0-2, 2-4, 4-8,8-16, and &gt;24m) every 5 seconds for the entire 6&#xa0;min behavioral trail. During data extraction average distance was calculated following methods in <xref ref-type="bibr" rid="B75">Peters et&#xa0;al. (1980)</xref> (<xref ref-type="bibr" rid="B44">Hyman et&#xa0;al., 2004</xref>; <xref ref-type="bibr" rid="B19">Davies et&#xa0;al., 2018</xref>). We combined all the territorial response data into a single &#x2018;territorial aggression score&#x2019; using Principal Component Analysis (PCA; See <xref ref-type="supplementary-material" rid="SM1">
<bold>supplementary materials</bold>
</xref> for table of loadings). Male aggression is repeatable within individuals during a breeding season (<xref ref-type="bibr" rid="B20">Davies and Sewall, 2016</xref>), even though territorial aggression declines over the season. Therefore, we used a single trial to quantify aggression but include day of year in all analysis.</p>
</sec>
<sec id="s2_1_3">
<label>2.1.3</label>
<title>RFID and parental visitation</title>
<p>To monitor parental nest visitation rates in 2018 &#x2013; 2021, we placed a RFID system at the nest (for details on function, form, and construction of RFID systems for monitoring wild bird populations see <xref ref-type="bibr" rid="B2">Adelman et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B13">Bridge et&#xa0;al., 2019</xref>) on the days leading up to nestling hatch. The system consisted of an antenna wrapped in camouflage electrical tape (for waterproofing) that was carefully placed around the external diameter of the nest (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1B</bold>
</xref>). The antenna was attached to a battery-powered microprocessor (E. Bridge; GEN 2 RFID Reader and Data Logger, 2012; <xref ref-type="bibr" rid="B12">Bridge and Bonter, 2011</xref>) with a 2 GB card (hereafter referred to as the &#x201c;board&#x201d;). The board and battery were housed in a waterproof container that was hidden near the nest. When the PIT tag disrupts the magnetic field created by the antenna, it is powered on and transmits a unique identification number which is recorded by the board as long as the PIT tag is within its range (here the range is the internal area of the nest cup plus a few centimeters above, and below the bottom of the nest cup). Batteries for the RFID system were changed every 2 &#x2013; 3 days, and parental visitation was monitored for 24 hours a day throughout the breeding attempt.</p>
<p>This RFID system was set with a read interval of 6 seconds and allows for continuous fine-scale monitoring of parental visitation during the entire nestling period. All RFID data were inspected visually for quality and accuracy. We used videos to spot-check RFID data by visually recording behavior and matching it to data recorded by the boards. We considered a lag time of &gt;1&#xa0;min between reads of a PIT tag number as a male leaving the nest. This was marked as an &#x2018;OFF&#x2019; time in the data. To calculate the number of nest visits made by an individual, we summed the number of OFF visits recorded in a day. Females move frequently when on the nest during the early nestling stage, so we increased the OFF time to &gt;2&#xa0;min to be more conservative in analyzing female visitations. To calculate &#x201c;total time&#x201d; an individual provided care for a given day, we subtracted the first and last read for that individual for the day. We used the number of visits and the &#x201c;total time&#x201d; for each day to calculate visitation rate (visits/(time of final visits in the day &#x2013; time of first visit of the day)) for each parent each day of the nestling period. Additionally, we calculated the average duration of each nest visit (total time on the nest/visits) per day. In total, we measure parental visitation in 76 males (57 urban and 19 rural) and 54 females (38 urban and 16 rural). Of these adults were able to capture both social partners at 43 nests (32 urban and 11 rural). Not all nests survived the breeding attempts, and some nests were located, or parents were captured after hatch. To account for variation in monitoring duration, nestling age, and day of year were included as fixed-effects covariates in all analysis.</p>
</sec>
</sec>
<sec id="s2_2">
<label>2.2</label>
<title>Monitoring nesting success and offspring development</title>
<sec id="s2_2_1">
<label>2.2.1</label>
<title>Nest searching and monitoring</title>
<p>To examine the effects of urbanization on the fitness of wild song sparrows, we located and monitored nests in urban and rural habitats throughout 5 breeding seasons. In the spring and summers of 2017 to 2021 we searched for and monitored song sparrow nests at the previously mentioned field sites. We searched habitat types evenly (2 days searching urban, 2 days searching rural repeated across the field season) to control for nest searching effort. Nest searching was conducted primarily in the early morning (0500 to 1100) during peak parental behavior, from early May until late July in 2017, and from early March to late July in 2018- 2021. For analysis we only included one nest from each pair that was closest to the mean lay date for the year. In total, we found and monitored 166 nests in urban habitats and 119 nests in rural habitats.</p>
<p>We located nests primarily through behavioral observations of adults and systematic searching of known territories and nesting substrates (<xref ref-type="bibr" rid="B60">Martin and Geupel, 1993</xref>). When we located nests during incubation, a minimum of two eggs were candled to establish incubation stage and target hatching date. After we located a nest, we limited the amount of time spent at the nests and number of visits to the nests to reduce nest abandonment. We only visited nests to establish vital developmental stages (lay date, onset of incubation, and hatch date), monitor offspring development, and conduct adult behavior assays and capture. We used previously published life-history data for this species to estimate dates for events (i.e., nest building, lay and incubation duration) that occurred before a nest was found (<xref ref-type="bibr" rid="B98">Smith and Roff, 1980</xref>; <xref ref-type="bibr" rid="B99">Sogge and Van Riper, 1988</xref>).</p>
<p>We defined nest success as at least one song sparrow nestling fledging from the nest and nest failure as complete nest predation (all eggs gone from the nest, all nestlings gone while still altricial), parental abandonment, or an anthropogenic form of nest destruction. Fledging success was the number of nestlings that fledged from the nest. If we did not record nest success or failure on the RFID system, we estimated the date of nest completion as the midpoint between the last two nest visits (<xref ref-type="bibr" rid="B63">Mayfield, 1961</xref>). We controlled for stage location bias (nests found in late stages overestimate nesting success), by calculating daily nest survival rates and nest survival rates for each habitat using Mayfield estimations (<xref ref-type="bibr" rid="B63">Mayfield, 1961</xref>; <xref ref-type="bibr" rid="B45">Jehle et&#xa0;al., 2004</xref>). We visually inspected all final clutches for brood parasitism by brown-headed cowbirds (<italic>Molothrus ater</italic>), using previously established methods to distinguish host eggs from brown-headed cowbirds (<xref ref-type="bibr" rid="B97">Smith and Arcese, 1994</xref>). If a nest was found after hatch, we used visual identification and morphometrics to identify brood parasitism (<xref ref-type="bibr" rid="B77">Pyle, 1997</xref>).</p>
</sec>
<sec id="s2_2_2">
<label>2.2.2</label>
<title>Offspring condition</title>
<p>To examine the effect of urbanization, and possible indirect effects it has on parental nest visitation, and on offspring condition we compared nestling body condition just prior to fledging (Day 9 and 10) between habitat types. Across all years we measured 155 urban nestlings and 36 rural nestlings from 61 urban nests and 14 rural nests. We measured nestling song sparrow mass, and tarsus just before fledging (Day 9; <xref ref-type="bibr" rid="B77">Pyle, 1997</xref>). To ensure accuracy, each measurement was taken 5 times, the highest and lowest measurement were dropped, and an average was taken from the remaining 3. If we located a nest after the clutch had hatched, measurements were taken on the day it was found and nestling age was estimated from morphometric variables (<xref ref-type="bibr" rid="B77">Pyle, 1997</xref>; <xref ref-type="bibr" rid="B46">Jonsomjit et&#xa0;al., 2007</xref>).</p>
</sec>
</sec>
<sec id="s2_3">
<label>2.3</label>
<title>Statistical analysis</title>
<sec id="s2_3_1">
<label>2.3.1</label>
<title>Behavior</title>
<p>We conducted statistical analyses using R (<xref ref-type="bibr" rid="B78">R Core Team, 2021</xref>, v. 4.0.4). We analyzed all parental visitation and male aggression data using linear mixed effects models (LMM). We fitted all LMM&#x2019;s and generalized linear mixed effects models (GLMM) using the package &#x201c;lme4&#x201d; (<xref ref-type="bibr" rid="B1">Bates et&#xa0;al., 2015</xref>) and we checked the model assumptions using the &#x201c;performance&#x201d; package (<xref ref-type="bibr" rid="B56">L&#xfc;decke et&#xa0;al., 2021</xref>). We tested the significance of fixed effects from the LMMs using the lmerTest (<xref ref-type="bibr" rid="B51">Kuznetsova et&#xa0;al., 2017</xref>) package, which estimates degrees of freedom (<italic>df</italic>) with the Satterthwaite approximation. A full summary of results from all models presented in this paper are included in the <xref ref-type="supplementary-material" rid="SM1">
<bold>supplemental materials</bold>
</xref>. We analyzed the effect of habitat on paternal visitation, maternal visitation, and the correlation between paternal visitation and aggression in separate LMMs using a data set that included all adults monitored during this project. In each model, visits/hour (by either the male or female depending on the model) was used as the response variable. For the two models examining paternal and maternal visitation, habitat type was a categorical fixed-effect. To examine the relationship between paternal visitation and aggression we included male aggression score (PC1, which explained 53.19% of the variation in behavior, see <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S1</bold>
</xref>, model results) and habitat type as the predictor variables. To examine the relationship between maternal visitation and male aggression we included maternal visits/hour calculated for each day as the response variable with social partner&#x2019;s aggression score and habitat type as the predictor variable with an interaction indicated. We created a final LMM to examine the relationship between social partner parental visitation that only included the nests from which we had parental visitation from both social partners (41 pairs). For this model, we averaged male and female social partners visitation rates for each day, then included female visitation as the predictor variable, with male visitation and habitat type as fixed-effects. For all behavioral analysis we included age of the nestlings (day 1 &#x2013; 10), total number of nestlings in the nest (including brood parasites), Julian day, and year sampled as fixed-effect covariates. Parental visitation did not vary with the presence of a brood parasite in the nest, and the covariate was dropped from all parental visitation models, but brood parasite nestlings were included in all brood sizes. We included the unique nest ID as the random effect in each model to control for autocorrelation within the nest and for repeated measure of continuous recording of parental visitation.</p>
</sec>
<sec id="s2_3_2">
<label>2.3.2</label>
<title>Nest outcomes and nestling condition</title>
<p>To analyze patterns of nest success, nest predation, and brood parasitism by brown-headed cowbirds between urban and rural habits we used separate linear models (LMs) fitted to a binomial distribution. For each model we included nest success or failure, presence or absence of nest predation, and presence or absence of brood parasitism as binomial response variables. We used habitat type, and year as fixed-effect covariates in the models. For the nest success and nest predation models, we also included the presence or absence of brood parasitism as fixed-effect covariates. We further analyzed fitness measures of fledging success and hatching success between urban and rural habitat using generalized linear models (GLMs) fitted to a negative binomial distribution using the Mass (<xref ref-type="bibr" rid="B105">Venables and Ripley, 2002</xref>) package. In each model, fledging success or hatching success was the response variable, with habitat type, the presences of brood parasitism, lay initiation date and year included as fixed-effect covariates. We did the same analysis on the subset of nests that were successful, except the data was fitted to a normal distribution. Finally, we examined a commonly used fitness metric, lay date, between habitat types using a LM (<xref ref-type="bibr" rid="B109">Winkler et&#xa0;al., 2020</xref>). We included Julian lay date as the response variable and habitat type, brood parasitism, and year as fixed-effect covariates in the model. For this model, we used a data set that included the first breeding attempt for each pair, rather than the closest breeding attempt to the mean lay date.</p>
<p>To determine if there were any differences in nestling condition near fledging between habitat types, we used two separate LMMs with morphological measures (either nestling tarsus length or mass) as the response variable in each model. We included habitat type and nestling age as fixed-effects. Julian date, number of nestlings in the nest, brood parasitism, and year were also included as fixed-effect covariates. To control for autocorrelation between nestlings in the same nest, we included the unique nest ID as the random effect.</p>
</sec>
</sec>
</sec>
<sec id="s3" sec-type="results">
<label>3</label>
<title>Results</title>
<sec id="s3_1">
<label>3.1</label>
<title>Male aggression and parental visitation between urban and rural habitats</title>
<p>Male nest visitation rates significantly increased with the total number of nestlings present in the nest (&#x3b2; = 0.43 &#xb1; 0.11, <italic>t</italic>
<sub>490.09&#xa0;=&#xa0;</sub>3.78, p = 0.0002) and nestling age (&#x3b2; = 0.16 &#xb1; 0.03, <italic>t<sub>552.09&#xa0;=&#xa0;</sub>
</italic>5.59, p = &lt;0.0001) across habitat types. However, independent of brood size and nestling age, urban males visited the nest significantly more often compared to rural males (&#x3b2; = 0.96 &#xb1; 0.46, <italic>t</italic>
<sub>79.09&#xa0;=&#xa0;</sub>2.07, p = 0.04; <xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2</bold>
</xref>; Random effects: among-nest variance = 2.30, residuals variance = 2.60). Contrary to our predictions, we found no relationship between male aggression and nest visitation rates through the brooding period (&#x3b2; = 0.09 &#xb1; .62, <italic>t</italic>
<sub>54.35&#xa0;=&#xa0;</sub>0.15, p = 0.89; <xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3</bold>
</xref>) nor did we find a relationship between male aggression and maternal visitation rates (&#x3b2; = -0.81 &#xb1; 0.67, <italic>t</italic>
<sub>29.12</sub> = -1.20, p = 0.24; Random effects: among-nest variance = 0.70, residuals variance = 2.04). While urban males visited the nest more frequently than rural males, urban females did not. There was a trend for increased maternal visitation in urban habitats (&#x3b2; = 0.66 &#xb1; 0.33, <italic>t</italic>
<sub>48.39&#xa0;=&#xa0;</sub>1.99, p = 0.05; <xref ref-type="fig" rid="f4">
<bold>Figure&#xa0;4</bold>
</xref>; Random effects: among-nest variance = 0.64, residuals variance = 1.94) and a significant negative relationship between female visitation rates and nestling age (&#x3b2; = -0.08 &#xb1; 0.03, <italic>t</italic>
<sub>315.98</sub> = -2.60, p = 0.01), but female visitation rates did not vary with the number of nestlings present in the nest (&#x3b2; = 0.08 &#xb1; 0.12, <italic>t</italic>
<sub>223.87&#xa0;=&#xa0;</sub>0.62, p = 0.53). Finally, there was a significant positive relationship between daily social partner nest visitation rates across habitat types (&#x3b2; = 0.33 &#xb1; 0.05, <italic>t<sub>231.20&#xa0;=&#xa0;</sub>
</italic>7.17, p = &lt;0.0001; Random effects: among-nest variance = 0.56, residuals variance = 1.53; <xref ref-type="fig" rid="f5">
<bold>Figure&#xa0;5</bold>
</xref>) and there was no difference in this relationship between habitats.</p>
<fig id="f2" position="float">
<label>Figure&#xa0;2</label>
<caption>
<p>Paternal visitation between urban (gray) and rural (black) habitats during the nestling period (day 0 &#x2013; 10). Urban males (67) visited the nest significantly more often (5.66 &#xb1; 0.11 times/hour) during nestling provisioning compared to rural males (19) that visited the nest on average 4.70 &#xb1; 0.18 times/hour. During these visits, urban males spent on average 7.60 &#xb1; 0.31 minutes per visits compared to rural, who spent on average 7.72 &#xb1; 1.04 minutes per visit. Each time point is averaged from 388 urban observation (days) and 92 rural observations (days).</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-11-1234562-g002.tif"/>
</fig>
<fig id="f3" position="float">
<label>Figure&#xa0;3</label>
<caption>
<p>Male aggression in urban (triangles) and rural (circles) song sparrows was not correlated with paternal care. Urban males (46) had an average aggression score of 0.49 &#xb1; 0.08 compared to rural (15) that had an average aggression score of -0.40 &#xb1; 0.09.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-11-1234562-g003.tif"/>
</fig>
<fig id="f4" position="float">
<label>Figure&#xa0;4</label>
<caption>
<p>Maternal visitations varied between urban (gray) and rural (black) habitats during the nestling period (day 0 &#x2013; 10) depending on time of day. Urban females appear to increase nest activity compared to rural during the day, and the opposite occurs at night. Urban females (38) visited the nest on average 5.84 &#xb1; 0.10 times/hour during nestling provisioning compared to rural females (16) that visited the nest on average 5.24 &#xb1; 0.16 times/hour. During these visits, urban females spent on average 41.94 &#xb1; 2.89 minutes per visits compared to rural, who spent on average 55.99 &#xb1; 4.76 minutes per visit. Each time point is averaged from 216 urban observation (days) and 67 rural observations (days).</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-11-1234562-g004.tif"/>
</fig>
<fig id="f5" position="float">
<label>Figure&#xa0;5</label>
<caption>
<p>Social partner care was positively corelated during offspring provisioning in both urban (triangles) and rural (circles) habitats. Females (32 urban 11 rural) that visited the nest on average 5.72 &#xb1; 0.10 times/hour had social partners (32 urban 11 rural) that visited on nest on average 5.80 &#xb1; 0.14 times/hour. Each data point represents the average care provided in a day by the female and her social partner for a total of 274 days of combined parental care data.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-11-1234562-g005.tif"/>
</fig>
</sec>
<sec id="s3_2">
<label>3.2</label>
<title>Offspring condition and nest outcomes between urban and rural habitats</title>
<p>There was no effect of habitat type on nestling body mass (&#x3b2; = -0.13 &#xb1; 9.65, <italic>t</italic> <sub>64.99</sub> = -0.01, p = 0.99; <xref ref-type="fig" rid="f6">
<bold>Figure&#xa0;6A</bold>
</xref>) or tarsus length (&#x3b2; = 1.03 &#xb1; 6.29, <italic>t</italic> <sub>63.89&#xa0;=&#xa0;</sub>0.16, p = 0.87) just before fledge (day 9 and 10). However, nestling mass (&#x3b2; = -1.61 &#xb1; 0.52, <italic>t</italic> <sub>80.28</sub> = -3.13, p = 0.002; Random effects: among-nest variance = 1.59, residuals variance = 2.58; <xref ref-type="fig" rid="f6">
<bold>Figure&#xa0;6B</bold>
</xref>) and tarsus length (&#x3b2; = 0.93 &#xb1; 0.33, <italic>t</italic> <sub>73.27</sub> = -2.81, p = 0.006; Random effects: among-nest variance = 0.82, residuals variance = 0.76) were significantly lower before fledge in nests containing brown headed cowbirds compared to unparasitized nests. Additionally, of nests that survived to fledge and were not predated, nests that were parasitized by brown-headed cowbirds hatched (&#x3b2; = -1.26 &#xb1; 0.188, <italic>t</italic> <sub>85</sub> = -6.69, p = &lt;0.0001) and fledged (&#x3b2; = -1.29 &#xb1; 0.23, <italic>t</italic> <sub>97</sub> = -5.66, p = &lt;0.0001) significantly less song sparrow offspring compared to unparasitized nests.</p>
</sec>
<sec id="s3_3">
<label>3.3</label>
<title>The fitness effects of breeding habitat type</title>
<p>Nest success rates were significantly higher in urban habitats compared to rural (&#x3b2; = 1.80 &#xb1; 0.32, <italic>z<sub>279&#xa0;=&#xa0;</sub>
</italic>3.15, p = &lt;0.0001) but success rates varied across years (&#x3b2; = -0.34 &#xb1; 0.11, <italic>z<sub>279</sub>
</italic> = -3.15, p = 0.002). Similarly, hatching success (&#x3b2; = 0.063 &#xb1; 0.16, z<sub>236&#xa0;=&#xa0;</sub>3.82, p = 0.0001) and fledging success (&#x3b2; = 1.09 &#xb1; 0.21, <italic>z<sub>203&#xa0;=&#xa0;</sub>
</italic>5.22, p = &lt;0.0001) were significantly higher in urban habitats compared to rural. Nest predation rates were significantly higher in rural habitats compared to urban (&#x3b2; = -1.84 &#xb1; 0.29, <italic>z</italic> <sub>284</sub>= -6.37, p = &lt;0.0001) and nest predation rates also expressed inter-year variation (&#x3b2; = 0.24 &#xb1; 0.33, <italic>z<sub>284&#xa0;=&#xa0;</sub>
</italic>0.79, p = 0.02). Brood parasitism by brown headed cowbirds was significantly higher in urban habitats compared to rural (&#x3b2; = 2.29 &#xb1; 0.40, <italic>z</italic>
<sub>287&#xa0;=&#xa0;</sub>5.74, p = &lt;0.0001). We found that lay date was significantly earlier in urban habitats compared to rural (&#x3b2; = -18.69 &#xb1; 3.47, <italic>t</italic>
<sub>144</sub> = -5.39, p = &lt;0.0001), with rural birds starting to lay on May 27<sup>th</sup> &#xb1; 2.35 days (64 nests with confirmed building or lay dates across 5 years) and urban around May 8th<sup>th</sup> &#xb1; 1.96 days (110 nests with confirmed building or lay dates across 5 years).</p>
</sec>
</sec>
<sec id="s4" sec-type="discussion">
<label>4</label>
<title>Discussion</title>
<p>Time and energy are limiting resources for seasonal breeding species that have a narrow window to mate and raise their offspring, and decisions on how individuals allocate these resources can be influenced by the environment. For example, greater male aggression may shift an existing trade-off between paternal care and territorial defense, such that more aggressive males provide less paternal care (<xref ref-type="bibr" rid="B88">Saino and M&#xf8;ller, 1995</xref>; <xref ref-type="bibr" rid="B6">Badyaev and Hill, 2002</xref>; <xref ref-type="bibr" rid="B76">Pryke and Griffith, 2009</xref>). We hypothesized that this trade-off could result in urban male song sparrows, which are reliably more aggressive, providing less paternal care. Decreased male care could, in turn, force females to increase maternal investment. However, if females are unable to compensate for reduced paternal care, offspring condition and survival could decrease. Contrary to the described theoretical framework, we found no evidence that urban male song sparrows sacrificed parental visitation for territorial aggression. Urban males did not have lower visitation rates than rural males at any nestling age or time of day (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2</bold>
</xref>). In fact, we found that the more aggressive urban males visited the nest more often than their rural counterparts and began feeding earlier in the day (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2</bold>
</xref>). Additionally, there was no correlation between male aggression and parental visitation rates for males or females within or across habitats (<xref ref-type="fig" rid="f6">
<bold>Figure&#xa0;6</bold>
</xref>; <xref ref-type="bibr" rid="B52">Lane and Sewall, 2022</xref>). This refutes both the idea that urban males are facing a trade-off between territorial defense and parental care, and that urban habitats compromise male parental care. Previously, researchers found that urban male songbirds in this population had better body condition and access to greater fat reserves compared to rural (<xref ref-type="bibr" rid="B34">Goodchild et&#xa0;al., 2022</xref>), suggesting that birds in urban habitats are of higher quality than their rural counterparts and are therefore released from constraints experienced by other birds (<xref ref-type="bibr" rid="B82">Reznick et&#xa0;al., 2000</xref>). Additionally, urban males likely have different time and energy budgets compared to rural. Our previous research has shown that urban song sparrows have decreased conspecific density and increased territory size compared to rural ones (<xref ref-type="bibr" rid="B66">McKinney, 2006</xref>; <xref ref-type="bibr" rid="B20">Davies and Sewall, 2016</xref>; <xref ref-type="bibr" rid="B47">Ju&#xe1;rez et&#xa0;al., 2020</xref>). With larger territories to defend, but decreased conspecific density, urban male song sparrows may be more aggressive yet have fewer territorial encounters with neighbors each day. Though future studies of time budgets for urban and rural birds would be required to evaluate this possibility, we can conclude that neither rural nor urban song sparrows seem to be under sufficient constraint to force a behavioral trade-off between our measures of aggression and paternal care. However, it is important to point out that some of the most aggressive males in the population provided the least amount of care (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1</bold>
</xref>). It may be possible that with an even larger sample size the extremes in behavior would be detected and a trade-off between male aggression and parental care could be established.</p>
<fig id="f6" position="float">
<label>Figure&#xa0;6</label>
<caption>
<p>Nestling mass near fledging (Day 9 and 10) between habitat types <bold>(A)</bold> and in the presence of brood parasitism <bold>(B)</bold>. Song sparrow nestling mass were similar in urban (a, gray) and rural (a, black) nests. However, song sparrow nestling mass is significantly lower in nests containing brown-headed cowbirds compared to those without. Rural (b, closed black) nestlings (15.51 &#xb1; 0.34) and urban (b, open black) nestlings (14.83 &#xb1; 0.17) were larger on average without brown-headed cowbird nestlings, compared to urban (b, closed grey) nestlings (13.31 &#xb1; 0.52) competing with brood parasite nestlings. Only 1 rural nest was documented with cowbird nestlings and was removed from the data for this comparison. The asterisks indicates a significance affect of brood parasitism on nestling growth. Parasitized nestling were significantly smaller compared to nestlings from non parasatized nests.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fevo-11-1234562-g006.tif"/>
</fig>
<p>Female visitation rates were not significantly different across habitats, but there was a nonsignificant trend for urban females to visit the nest at a higher frequency (<xref ref-type="fig" rid="f4">
<bold>Figure&#xa0;4</bold>
</xref>). Specifically, urban females increased visitation rates during the day compared to rural, while rural females are more active at night compared to urban females (<xref ref-type="fig" rid="f4">
<bold>Figure&#xa0;4</bold>
</xref>). We were unable to confirm this night behavior was not an artifact of the RFID systems through video recordings because we did not have access to night vision equipment. However, we would expect to see similar patterns of behavior at night in both habitat types if the RFID systems were causing an artifact. Understanding nocturnal time budgets around species with different life-history strategies, such as cavity or open-cup nesting species, is a current gap in our understanding of animal behavior (<xref ref-type="bibr" rid="B35">Graham et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B40">Hau et&#xa0;al., 2017</xref>). Future studies examining daily patterns of behavior across urban and rural habitats in species with different life-history traits could determine which behaviors are adaptive under different environmental conditions and confirm or refute our surprising observation of nocturnal activity in rural song sparrows.</p>
<p>Since urban male song sparrows provide as much, if not more, paternal care as their rural counterparts we found no evidence that females were compensating for their mates. In fact, we found a strong positive relationship between parental care provided by social partners (<xref ref-type="fig" rid="f5">
<bold>Figure&#xa0;5</bold>
</xref>). Females that visited the nest more often each day were paired with males that did the same. Collectively, these parental care findings also refute the hypothesis that urban females are compensating for their social partners; rather, song sparrows seem to match their reproductive effort with that of their partner. This behavioral matching raises the hypothesis that song sparrow social pairs express assortative mating and/or matching of parental behaviors within the brooding periods (<xref ref-type="bibr" rid="B110">Wolfenbarger, 1999</xref>; <xref ref-type="bibr" rid="B107">Westneat et&#xa0;al., 2011</xref>). Our finding contrasts with a previous study in a cavity nesting species that found that urban birds showed decreased coordination in provisioning behavior compared to rural (<xref ref-type="bibr" rid="B8">Baldan and Ouyang, 2020</xref>). Rather, male song sparrows at our urban study sites maintain higher territorial aggression and high parental visitation, presumably because time and energy resources allow them to do so.</p>
<p>Song sparrow nestlings in urban and rural habitats had similar body size (tarsus and mass; <xref ref-type="fig" rid="f6">
<bold>Figure&#xa0;6A</bold>
</xref>) before fledging, suggesting that urban habitats are not negatively affecting offspring condition before fledging. However, offspring body mass (<xref ref-type="fig" rid="f6">
<bold>Figure&#xa0;6B</bold>
</xref>) and tarsus length near fledge were significantly smaller in parasitized nests compared to unparasitized nests. Additionally, in the subset of nests that avoided predation, hatching and fledging success of song sparrow nestlings was significantly reduced in parasitized nests compared to unparasitized nests. Obligate brood parasites, such as brown-headed cowbirds, lay their eggs in the nest of a host species, forcing the host to raise the nestling, often to the detriment of the parent and their offspring (<xref ref-type="bibr" rid="B71">Ortega et&#xa0;al., 2005</xref>; <xref ref-type="bibr" rid="B26">Faaborg et&#xa0;al., 2010</xref>). Nestlings that hatch later often die of malnutrition in nests with brood parasites, and only the largest, most robust host nestlings survive to fledge (<xref ref-type="bibr" rid="B74">Payne, 1977</xref>; <xref ref-type="bibr" rid="B79">Reme&#x15d;, 2006</xref>). This may explain why nestling body size and mass at fledge was reduced, and why the number of host offspring that were able to hatch and fledge from the nest were significantly lower in nests with brown-headed cowbirds. Collectively, this suggests that urban parental care is adequate, if not elevated, compared to that of rural, but the elevated rates of brood parasitism in urban habitats still compromise their ability to fledge a full clutch of offspring, and reduce nestling body mass and size at fledge.</p>
<p>We found that urban nests had higher daily and annual survival rates across all five years of our study compared to rural (<xref ref-type="table" rid="T1">
<bold>Table&#xa0;1</bold>
</xref>). Additionally, we found that urban song sparrows had greater nesting, hatching, and fledging success, and began nesting significantly earlier (16 days &#xb1; 2.27 days) compared to rural. This higher nestling survival was driven by significantly lower nest predation rates compared to rural. Our findings add to a growing body of evidence that, despite many studies demonstrating increased predator presence in urban habitats, nest predation rates decrease in urban settings compared to rural habitats (<xref ref-type="bibr" rid="B24">E&#xf6;tv&#xf6;s et&#xa0;al., 2018</xref>; <xref ref-type="bibr" rid="B28">Fischer et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B32">Gering and Blair, 1999</xref>; <xref ref-type="bibr" rid="B96">Shochat et&#xa0;al., 2006</xref>). Nest predation may be lower in urban environments because predators can exploit anthropogenic food sources such as trash cans and human food supplementation (i.e., the Predator Paradox hypothesis; Fischer et&#xa0;al., 2020; <xref ref-type="bibr" rid="B93">Seress and Liker, 2015</xref>). Alternatively, or additionally, snakes are often important nest predators, and their conspecific density decreases in urban habitats (<xref ref-type="bibr" rid="B50">Klug and Jackrel, 2010</xref>). The difference we found in nest predation rates between habitat types could also influence the differences in urban parental visitation rates (<xref ref-type="bibr" rid="B57">Lyon and Montgomerie, 1987</xref>; <xref ref-type="bibr" rid="B61">Martin and Ghalambor, 1999</xref>; <xref ref-type="bibr" rid="B23">Eggers et&#xa0;al., 2006</xref>). Previous research has experimentally shown that increased nest predation pressure decreased nest visitation rates (<xref ref-type="bibr" rid="B33">Ghalambor and Martin, 2002</xref>; <xref ref-type="bibr" rid="B69">Mouton et&#xa0;al., 2020</xref>). Therefore, it is possible that rural birds limit their visitation rates to their nests to reduce the risk of attracting nest predators. Collectively, these results suggest that some urban generalist species, such as song sparrows, can have greater nesting success in urban habitats compared to rural ones. Resolving the impacts of abiotic aspects of urbanization, nest predation, and nest parasitism risk on parental behavior in songbirds would require future studies that experimentally manipulate these variables using brood size manipulations or manipulations of parental effort.</p>
<table-wrap id="T1" position="float">
<label>Table&#xa0;1</label>
<caption>
<p>Daily, apparent, and Mayfield estimations (<xref ref-type="bibr" rid="B63">Mayfield, 1961</xref>) of nest survival rates between urban and rural song sparrows from 2017 &#x2013; 2021.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="bottom" align="left"/>
<th valign="bottom" colspan="3" align="center">Rural (%)</th>
<th valign="bottom" colspan="3" align="center">Urban (%)</th>
</tr>
<tr>
<th valign="middle" align="center">Year</th>
<th valign="middle" align="center">Daily Survival</th>
<th valign="middle" align="center">Apparent Survival</th>
<th valign="middle" align="center">Mayfield Estimate</th>
<th valign="middle" align="center">Daily Survival</th>
<th valign="middle" align="center">Apparent Survival</th>
<th valign="middle" align="center">Mayfield Estimate</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="bottom" align="center">2017</td>
<td valign="bottom" align="center">92.75</td>
<td valign="bottom" align="center">33.33</td>
<td valign="bottom" align="center">17.73</td>
<td valign="bottom" align="center">96.55</td>
<td valign="bottom" align="center">63.16</td>
<td valign="bottom" align="center">44.61</td>
</tr>
<tr>
<td valign="bottom" align="center">2018</td>
<td valign="bottom" align="center">91.11</td>
<td valign="bottom" align="center">20</td>
<td valign="bottom" align="center">17.73</td>
<td valign="bottom" align="center">98.26</td>
<td valign="bottom" align="center">79.17</td>
<td valign="bottom" align="center">66.75</td>
</tr>
<tr>
<td valign="bottom" align="center">2019</td>
<td valign="bottom" align="center">90.91</td>
<td valign="bottom" align="center">13.95</td>
<td valign="bottom" align="center">11.17</td>
<td valign="bottom" align="center">97</td>
<td valign="bottom" align="center">58</td>
<td valign="bottom" align="center">49.63</td>
</tr>
<tr>
<td valign="bottom" align="center">2020</td>
<td valign="bottom" align="center">89.08</td>
<td valign="bottom" align="center">7.14</td>
<td valign="bottom" align="center">6.99</td>
<td valign="bottom" align="center">95.22</td>
<td valign="bottom" align="center">35.14</td>
<td valign="bottom" align="center">32.41</td>
</tr>
<tr>
<td valign="bottom" align="center">2021</td>
<td valign="bottom" align="center">81.29</td>
<td valign="bottom" align="center">13.51</td>
<td valign="bottom" align="center">0.85</td>
<td valign="bottom" align="center">96.67</td>
<td valign="bottom" align="center">41.03</td>
<td valign="bottom" align="center">45.85</td>
</tr>
<tr>
<td valign="bottom" align="center">Cumulative</td>
<td valign="bottom" align="center">89.03</td>
<td valign="bottom" align="center">17.59</td>
<td valign="bottom" align="center">10.89</td>
<td valign="bottom" align="center">96.74</td>
<td valign="bottom" align="center">55.3</td>
<td valign="bottom" align="center">47.85</td>
</tr>
</tbody>
</table>
</table-wrap>
</sec>
<sec id="s5" sec-type="conclusions">
<label>5</label>
<title>Conclusions</title>
<p>There is an underlying assumption in many urban ecology studies that urban habitats are detrimental to animal fitness compared to the rural, less disturbed environments. Our data join an increasing number of studies showing this is not the case for all species, and that urban habitats provide benefits to species that are able to invade these novel environments (<xref ref-type="bibr" rid="B65">McKinney, 2002</xref>; <xref ref-type="bibr" rid="B67">McKinney, 2008</xref>; <xref ref-type="bibr" rid="B17">Chamberlain et&#xa0;al., 2009</xref>). We found that more aggressive urban male song sparrows did not sacrifice parental care for territorial aggression. Consequently, their social partners are not suffering increased energetic demands to care for young. This indicates that either song sparrows do not face such a trade-off, or they are released from it in urban habitats. In fact, urban males visited the nest more often than their rural counterparts, a pattern also observed in females though the relationship was not significant. These behavioral differences could be the result of decreased nest predation pressure in urban habitats. Few studies have examined the effects of urbanization on parental care, and these studies have focused on incubation behavior in cavity nesting species (<xref ref-type="bibr" rid="B8">Baldan and Ouyang, 2020</xref>; <xref ref-type="bibr" rid="B41">Heppner and Ouyang, 2021</xref>; <xref ref-type="bibr" rid="B43">Hope et&#xa0;al., 2022</xref>). <xref ref-type="bibr" rid="B43">Hope et&#xa0;al., 2022</xref> found that urban great tits (<italic>Parus major</italic>) increased overall incubation, yet decreased incubation bout rates compared to rural. <xref ref-type="bibr" rid="B41">Heppner and Ouyang (2021)</xref> found the opposite, with urban house wrens (<italic>Troglodytes aedon</italic>) decreasing incubation time and increasing bout rate. The limited number of studies in this area and their disparate results further illustrates the need for research on the effects of urbanization on parental care, and the importance of including species with diverse life history traits.</p>
<p>We observed a negative effect of brood parasitism on the hatching and fledging success of parasitized nests compared to unparasitized. However, this impact is minimal relative to the much higher nest success in urban habitats and the high nest predation in rural habitats. Understanding the effects of urbanization requires understanding community dynamics, including the interactions between brood parasites, predators, and their hosts. Previous studies found that urban adapters, such as the songbirds in this study, receive benefits such as increased food, water, maintained breeding substrates, and respite from predators (<xref ref-type="bibr" rid="B65">McKinney, 2002</xref>; <xref ref-type="bibr" rid="B17">Chamberlain et&#xa0;al., 2009</xref>; <xref ref-type="bibr" rid="B95">Shochat et&#xa0;al., 2010</xref>; <xref ref-type="bibr" rid="B103">Stracey and Robinson, 2012</xref>; <xref ref-type="bibr" rid="B100">Soulsbury and White, 2016</xref>; <xref ref-type="bibr" rid="B81">Reynolds et&#xa0;al., 2019</xref>). Collectively, our findings align with these studies, and suggest that, if given the space and opportunity to breed and reproduce, some generalist urban adapters and the species that rely on them can flourish in urban environments.</p>
</sec>
<sec id="s6" sec-type="data-availability">
<title>Data availability statement</title>
<p>The raw data supporting the conclusions of this article will be made available by the authors, without undue reservation.</p>
</sec>
<sec id="s7" sec-type="ethics-statement">
<title>Ethics statement</title>
<p>The animal study was reviewed and approved by Institutional Animal Care and Use Committee of Virginia Tech.</p>
</sec>
<sec id="s8" sec-type="author-contributions">
<title>Author contributions</title>
<p>SL and KS conceived the ideas and designed methodology. SL, IV, VB, CL, and TF collected the data. SL and CG analyzed the data. SL, CG, and KS led the writing of the manuscript. All authors contributed critically to the drafts and gave final approval for publication.</p>
</sec>
</body>
<back>
<sec id="s9" sec-type="funding-information">
<title>Funding</title>
<p>SL received funding from the Virginia Tech Ralph E. Carlson Memorial Scholarship in Ornithology, the Global Change Center at Virginia Tech, the Graduate Student Assembly at Virginia Tech, the Virginia Society for Ornithology, the American Ornithological Society, and the Society for Integrative and Comparative Biology. VB and CL received independent funding from the Multicultural Academic Opportunities Program, the Global Change Center at Virginia Tech and from the Howard Hughes Medical Institute&#x2019;s 2014 Science Education grant 52008103 to New Mexico State University. This research was further supported by funding from National Science Foundation grant IOS 1652496 and 2114288</p>
</sec>
<ack>
<title>Acknowledgments</title>
<p>We thank Radford University, Virginia Tech&#x2019;s Kentland Farms, and StREAM lab at Virginia Tech for allowing us to perform field research on their premises. We thank WA. Hopkins, J. McGlothlin, and IT. Moore for assistance on project development and comments on manuscript drafts and A. Gamero, and CE. Moore, for assistance in the field.</p>
</ack>
<sec id="s10" 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="s11" 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>
<sec id="s12" 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.2023.1234562/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fevo.2023.1234562/full#supplementary-material</ext-link>
</p>
<supplementary-material xlink:href="DataSheet_1.pdf" id="SM1" mimetype="application/pdf"/>
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