<?xml version="1.0" encoding="utf-8"?>
<!DOCTYPE article PUBLIC "-//NLM//DTD Journal Publishing DTD v2.3 20070202//EN" "journalpublishing.dtd">
<article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" article-type="research-article" dtd-version="2.3" xml:lang="EN">
<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Psychol.</journal-id>
<journal-title>Frontiers in Psychology</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Psychol.</abbrev-journal-title>
<issn pub-type="epub">1664-1078</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fpsyg.2023.1080149</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Psychology</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>On the relationships between auditory and visual factors in a residential environment context: A SEM approach</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Garz&#x00F3;n</surname>
<given-names>Luis</given-names>
</name>
<xref rid="aff1" ref-type="aff"><sup>1</sup></xref>
<xref rid="aff2" ref-type="aff"><sup>2</sup></xref>
<xref rid="c001" ref-type="corresp"><sup>&#x002A;</sup></xref>
<uri xlink:href="https://loop.frontiersin.org/people/2000908/overview"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Bravo-Moncayo</surname>
<given-names>Luis</given-names>
</name>
<xref rid="aff3" ref-type="aff"><sup>3</sup></xref>
<uri xlink:href="https://loop.frontiersin.org/people/182425/overview"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Arellana</surname>
<given-names>Juli&#x00E1;n</given-names>
</name>
<xref rid="aff2" ref-type="aff"><sup>2</sup></xref>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Ort&#x00FA;zar</surname>
<given-names>Juan de Dios</given-names>
</name>
<xref rid="aff4" ref-type="aff"><sup>4</sup></xref>
</contrib>
</contrib-group>
<aff id="aff1"><sup>1</sup><institution>Facultad de Ingenier&#x00ED;a y Ciencias Aplicadas, Universidad T&#x00E9;cnica del Norte</institution>, <addr-line>Ibarra</addr-line>, <country>Ecuador</country></aff>
<aff id="aff2"><sup>2</sup><institution>Departamento de Ingenier&#x00ED;a Civil y Ambiental, Universidad del Norte</institution>, <addr-line>Barranquilla</addr-line>, <country>Colombia</country></aff>
<aff id="aff3"><sup>3</sup><institution>Grupo de Investigaci&#x00F3;n de Entornos Ac&#x00FA;sticos, Universidad de las Am&#x00E9;ricas</institution>, <addr-line>Quito</addr-line>, <country>Ecuador</country></aff>
<aff id="aff4"><sup>4</sup><institution>Departamento de Ingenier&#x00ED;a de Transporte y Log&#x00ED;stica, Instituto Sistemas Complejos de Ingenier&#x00ED;a (ISCI), BRT+ Centre of Excellence, Pontificia Universidad Cat&#x00F3;lica de Chile</institution>, <addr-line>Santiago</addr-line>, <country>Chile</country></aff>
<author-notes>
<fn id="fn0001" fn-type="edited-by"><p>Edited by: Seungkwang Shon, Dongshin University, Republic of Korea</p></fn>
<fn id="fn0002" fn-type="edited-by"><p>Reviewed by: Nahyang Byun, Chungbuk National University, Republic of Korea; Chan Kook, Dongshin University, Republic of Korea</p></fn>
<corresp id="c001">&#x002A;Correspondence: Luis Garzon, <email>lagarzon@utn.edu.ec</email></corresp>
<fn id="fn0003" fn-type="other"><p>This article was submitted to Environmental Psychology, a section of the journal Frontiers in Psychology</p></fn>
</author-notes>
<pub-date pub-type="epub">
<day>01</day>
<month>03</month>
<year>2023</year>
</pub-date>
<pub-date pub-type="collection">
<year>2023</year>
</pub-date>
<volume>14</volume>
<elocation-id>1080149</elocation-id>
<history>
<date date-type="received">
<day>27</day>
<month>10</month>
<year>2022</year>
</date>
<date date-type="accepted">
<day>08</day>
<month>02</month>
<year>2023</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x00A9; 2023 Garz&#x00F3;n, Bravo-Moncayo, Arellana and Ort&#x00FA;zar.</copyright-statement>
<copyright-year>2023</copyright-year>
<copyright-holder>Garz&#x00F3;n, Bravo-Moncayo, Arellana and Ort&#x00FA;zar</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>To understand the effects of specific elements that may enhance or detract residents&#x2019; well-being, it is important to explore the relationships between auditory and visual factors, based on people&#x2019;s sensory experiences. Although residential environments provide natural experimental conditions to observe these relationships, the complexity of measuring sensory perceptions and their subsequent interpretation constitutes a challenge. This study aims to identify the influence of socio-demographics and residential location characteristics on three latent variables: noise-<italic>Sensitivity</italic>, sound-<italic>Pleasantness</italic>, and visual-<italic>Liveability</italic> in a Latin American city. The methodology is replicable and relies on a digital survey that displays environments in 360-format video and uses sound immersion techniques; it was applied to a sample of household heads in Quito, Ecuador. Based on an efficient experimental design, we selected different residential environments according to acoustic-visual attributes and the proximity to residential, commercial, and recreational land uses. Structural Equation Models (SEM) were estimated using mediating variables. Our results reveal the influence of noise-<italic>Sensitivity</italic> on sound-<italic>Pleasantness</italic> and, indirectly, on visual-<italic>Liveability</italic>. Further analysis shows that the impact of sound and visual perception changes with different socio-demographics and residential location characteristics.</p>
</abstract>
<kwd-group>
<kwd>noise-sensitivity</kwd>
<kwd>pleasantness</kwd>
<kwd>liveability</kwd>
<kwd>SEM</kwd>
<kwd>residential environment</kwd>
<kwd>immersive environments</kwd>
</kwd-group>
<contract-num rid="cn1">5000011771</contract-num>
<contract-num rid="cn2">AFB180003</contract-num>
<contract-sponsor id="cn1">Universidad de las Am&#x00E9;ricas</contract-sponsor>
<contract-sponsor id="cn2">Instituto Sistemas Complejos de Ingenier&#x00ED;a (ISCI)</contract-sponsor>
<counts>
<fig-count count="5"/>
<table-count count="8"/>
<equation-count count="0"/>
<ref-count count="65"/>
<page-count count="16"/>
<word-count count="10712"/>
</counts>
</article-meta>
</front>
<body>
<sec id="sec1" sec-type="intro">
<label>1.</label>
<title>Introduction</title>
<p>Sounds and visual elements are interdependent in urban environments. In particular, individual perceptions about them tend to vary with socio-demographics and housing location characteristics concerning the neighbourhood and urban services (<xref ref-type="bibr" rid="ref51">Sun et al., 2018a</xref>). However, most applied research on this subject has gravitated towards the idea of controlling noise annoyance by reducing sound pressure levels to enhance well-being (<xref ref-type="bibr" rid="ref14">EEA, 2020</xref>). Beyond the noise abatement approach, it has been highlighted that audio-visual elements may be subjectively measured to identify improvements in urban settings (<xref ref-type="bibr" rid="ref17">Hasegawa and Lau, 2022</xref>). This requires the collection of individual perceptions on site, but implementing a methodology to control the stimuli, and collect information from multiple locations at a time, represents an experimental challenge (<xref ref-type="bibr" rid="ref52">Tarlao et al., 2021</xref>). Moreover, integrating complex path models for exploring the influence of objective attributes amongst subjective factors also requires sophisticated analytical modelling tools (<xref ref-type="bibr" rid="ref31">Lionello et al., 2020</xref>).</p>
<p>Regarding the study of sounds in the urban environment, the soundscape series of <xref ref-type="bibr" rid="ref24">ISO (2014)</xref> provides a conceptual framework for acoustic and sound-related research. A growing number of auditory factors are revealed in the literature (i.e., noise annoyance, pleasantness and eventfulness) and used to evaluate the conditions of the acoustic environment (<xref ref-type="bibr" rid="ref2">Aletta et al., 2016</xref>). Traditionally, experiments designed to analyse residential selection have aimed to discover the influences between noise-sensitivity and noise-annoyance, using socio-demographic characteristics as mediation factors (<xref ref-type="bibr" rid="ref35">Miedema and Vos, 2003</xref>; <xref ref-type="bibr" rid="ref57">Van Kamp et al., 2004</xref>; <xref ref-type="bibr" rid="ref38">Nijland et al., 2007</xref>). However, there has been recent interest in the analysis of auditory factors (e.g., pleasantness and eventfulness) and person-related attributes (noise annoyance) in a residential context, as well as using mediating pathways concerning socio-demographic characteristics (<xref ref-type="bibr" rid="ref52">Tarlao et al., 2021</xref>).</p>
<p>The evidence reviewed about the perception of visual factors studies have demonstrated its association with numerous concepts such as liveability, satisfaction, and happiness (<xref ref-type="bibr" rid="ref1">Ahmed and El-Halafawy, 2019</xref>). These concepts play a crucial role when studying the enhancement of the residential environment (<xref ref-type="bibr" rid="ref29">Kovacs-Gy&#x00F6;ri et al., 2019</xref>). <xref ref-type="bibr" rid="ref37">Mouratidis and Yiannakou (2022)</xref> recently asked what makes cities liveable and explored how objective and subjective measures may be used to assess the liveability conditions of a place. These measures tend to differ according to the world&#x2019;s regions because citizens and societies have different wealth and degrees of accessibility to public services (<xref ref-type="bibr" rid="ref56">UN, 2022</xref>). Thus, urban liveability conditions have become an important topic to be subjectively investigated as a qualifying factor, as well as to be objectively measured. However, in the Latin American region, only a few studies have attempted to capture measures of subjective indicators such as liveability (i.e., by responding to survey questions where audio-visual stimuli are reproduced on the senses of participants), for subsequent interpretation using other perceptual factors (<xref ref-type="bibr" rid="ref28">Kogan et al., 2017</xref>; <xref ref-type="bibr" rid="ref45">Rey-Gozalo et al., 2018</xref>).</p>
<p>A systematic process to interpret the relationships amongst the perceptual factors and their corresponding indicators has required the application of sophisticated analytical tools, including advanced machine learning techniques, but the focus has been on the use of multivariate techniques such as the Structural Equation Models (SEM) approach. Applied complex models using SEM have involved perceptual factors of interest (i.e., auditory and visual factors), and include mediating effects through the specification of quantitative attributes (<xref ref-type="bibr" rid="ref20">Hong and Jeon, 2015</xref>; <xref ref-type="bibr" rid="ref32">Liu et al., 2019</xref>; <xref ref-type="bibr" rid="ref64">Zhao et al., 2021</xref>). However, we are not aware of prior statistical estimations using a combined specification between <italic>Pleasantness</italic> and <italic>Liveability</italic> in a residential environment, when exploring direct and indirect effects amongst objective attributes.</p>
<p>This study explores the relationships between three latent variables (i.e., noise-<italic>Sensitivity</italic>, sound-<italic>Pleasantness</italic> and visual-<italic>Liveability</italic>) based on experimental conditions in a selection of residential environments. For this, audio-visual stimuli were recorded in widely dispersed residential locations selected to match different configurations of attributes defined under an efficient experimental design. Audio-visual stimuli were reproduced using immersive devices (360&#x00B0;-format video and immersive sound) and applied to a sample of household heads, collecting perceptual indicators about their residential locations using a digitally assisted survey format. Finally, SEM was estimated to understand the behaviour of the latent variables when modifying quantitative measures of visual and acoustic attributes, socio-demographics and housing location characteristics.</p>
<p>The rest of the paper is organised as follows. The second section briefly reviews our theoretical auditory and visual factor evaluation framework. The third section describes the hypothesis statements and the survey design process methodology. The fourth section contains modelling results for an Exploratory Factor Analysis (EFA), Confirmatory Factor Analysis (CFA), SEM structure and subsequent mediation analysis. The fifth section presents a discussion, and the sixth summarises our main conclusions.</p>
</sec>
<sec id="sec2">
<label>2.</label>
<title>Theoretical framework</title>
<p>In terms of evaluating the acoustic environment, urban studies have traditionally been concerned with assessing perceptions such as noise-annoyance (<xref ref-type="bibr" rid="ref53">Tillema et al., 2012</xref>). However, several auditory indicators have emerged as a part of the soundscape concept, providing a broader understanding of improvements in acoustic environments in residential settings (<xref ref-type="bibr" rid="ref2">Aletta et al., 2016</xref>). There is a growing body of literature using this framework to investigate how contextual indicators (person-related characteristics and non-auditory contextual indicators) influence both auditory indicators (i.e., perceived sources and sound indicators) and soundscape factors (<xref ref-type="bibr" rid="ref20">Hong and Jeon, 2015</xref>; <xref ref-type="bibr" rid="ref32">Liu et al., 2019</xref>; <xref ref-type="bibr" rid="ref64">Zhao et al., 2021</xref>; <xref ref-type="bibr" rid="ref17">Hasegawa and Lau, 2022</xref>). The notion of auditory factors, especially pleasantness, has &#x201C;proved particularly relevant to assess the quality of the sound environment&#x201D; (<xref ref-type="bibr" rid="ref600">Aumond et al., 2017</xref>, pp. 431). The literature highlights the study of pleasantness based on the selection of a number of auditory indices defined in the Circumplex Model of soundscape perception (<xref ref-type="bibr" rid="ref7">Axelsson et al., 2010</xref>). The model uses four bipolar factors that can be synthesised by specifying two latent constructs, <italic>Pleasantness</italic> and <italic>Eventfulness</italic> (two main orthogonal factors). <xref ref-type="bibr" rid="ref2">Aletta et al. (2016)</xref> suggest that the former is the main factor analysed in soundscape studies, and several indicators focused attention on its identification, such as <italic>agitating-calm</italic>, <italic>interesting</italic>, <italic>pleasant&#x2013;unpleasant</italic>, <italic>appropriateness</italic>, <italic>harmonious</italic> and <italic>comfortable&#x2013;uncomfortable</italic>.</p>
<p>In addition, a growing literature has looked at liveability (<xref ref-type="bibr" rid="ref10">Campbell et al., 1976</xref>; <xref ref-type="bibr" rid="ref58">Van Kamp et al., 2003</xref>), although we are not aware of previous modelling approaches selecting subjective indices to analyse it. In European cities, liveability has been associated with indices measuring the quality of life (<xref ref-type="bibr" rid="ref34">Marans, 2012</xref>; <xref ref-type="bibr" rid="ref40">Okulicz-Kozaryn and Valente, 2019</xref>). However, <xref ref-type="bibr" rid="ref37">Mouratidis and Yiannakou (2022)</xref> argue that &#x201C;liveability can be assessed in a subjective way,&#x201D; if the term is understood and measured as visual perception (<xref ref-type="bibr" rid="ref59">Veenhoven, 2000</xref>; <xref ref-type="bibr" rid="ref48">Rossetti et al., 2019</xref>; <xref ref-type="bibr" rid="ref55">T&#x00FC;rko&#x011F;lu et al., 2019</xref>; <xref ref-type="bibr" rid="ref43">Ram&#x00ED;rez et al., 2021</xref>). On the other hand, <xref ref-type="bibr" rid="ref1">Ahmed and El-Halafawy (2019)</xref> suggested that the perception of visual factors may be associated with concepts such as liveability, satisfaction and well-being. So, these concepts may play a crucial role when studying enhancements to the residential environment (<xref ref-type="bibr" rid="ref29">Kovacs-Gy&#x00F6;ri et al., 2019</xref>).</p>
<p>Several approaches have used SEM to discover relationships between pleasantness and eventfulness but also specify visual constructs such as satisfaction and visual quality (<xref ref-type="bibr" rid="ref36">Mouratidis, 2020</xref>; <xref ref-type="bibr" rid="ref37">Mouratidis and Yiannakou, 2022</xref>). However, to the best of our knowledge, none has examined and quantified the relationship between <italic>Pleasantness</italic> and <italic>Liveability</italic>, and only a theoretical framework has been developed (<xref ref-type="bibr" rid="ref6">Aulia, 2016</xref>; <xref ref-type="bibr" rid="ref3">Amir et al., 2021</xref>). This lack of knowledge is even more notorious in the Latin American context, as only a few studies have attempted to conceptualise multidimensional sensory indicators when exploring residential environments (<xref ref-type="bibr" rid="ref28">Kogan et al., 2017</xref>, <xref ref-type="bibr" rid="ref27">2018</xref>; <xref ref-type="bibr" rid="ref44">Rey-Gozalo and Barrig&#x00F3;n-Morillas, 2017</xref>; <xref ref-type="bibr" rid="ref45">Rey-Gozalo et al., 2018</xref>).</p>
<p>From a methodological perspective, experiments conducted to evaluate the conditions of the urban environment highlight the importance of determining the roles of audio-visual attributes and their effects on individual perceptions (<xref ref-type="bibr" rid="ref22">Hong et al., 2020</xref>; <xref ref-type="bibr" rid="ref63">Yong et al., 2021</xref>). The variation of sound and visual&#x2013;spatial metrics stimulates different feelings in people, and their relationship may enhance well-being in residential environments (<xref ref-type="bibr" rid="ref17">Hasegawa and Lau, 2022</xref>). However, it is complex to recreate different urban configurations to evaluate audio-visual conditions in an experimental setting with appropriate trade-off levels (<xref ref-type="bibr" rid="ref41">Ortega et al., 2020</xref>; <xref ref-type="bibr" rid="ref43">Ram&#x00ED;rez et al., 2021</xref>). Recently, access to new technological tools has facilitated the recording and reproduction of visual features (i.e., people and vehicles, green spaces and the built environment) in terms of dynamics, position in space, dimensions and even colours (<xref ref-type="bibr" rid="ref42">Puyana-Romero et al., 2016</xref>; <xref ref-type="bibr" rid="ref5">Arellana et al., 2020</xref>). In particular, the use of immersive environments and digital format questionnaires has allowed a more significant number of scenarios to be assessed, allowing for a larger number of data points to be collected simultaneously. However, beyond the overall flexibility provided by these technological tools for survey implementation, some other issues need to be addressed, such as the reproduction length of the experiment, when audio-visual stimuli are projected on the senses of participants and the way to capture the responses. An inadequate method for experimental reproduction can lead to boredom, fatigue, and a high cognitive load on respondents (<xref ref-type="bibr" rid="ref18">Heggie et al., 2019</xref>).</p>
</sec>
<sec id="sec3" sec-type="materials|methods">
<label>3.</label>
<title>Materials and methods</title>
<p>This section describes the characteristics of the participants in the study, the survey design and the statistical tools used to analyse the data.</p>
<sec id="sec4">
<label>3.1.</label>
<title>Participants</title>
<p>Five hundred and forty-three household heads participated in this study. The participants were selected according to the socio-demographic characteristics of the population by groups of sex and age (trends from the latest 2010 national census). The information was collected from November 2020 to June 2021 in 31 urban districts distributed in three main areas of the Metropolitan Area of Quito (i.e., North, Centre and South). <xref rid="tab1" ref-type="table">Table 1</xref> summarises the main information collected from participants.</p>
<table-wrap position="float" id="tab1">
<label>Table 1</label>
<caption>
<p>Socio-demographic information (<italic>N</italic>&#x2009;=&#x2009;543).</p>
</caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th align="left" valign="top">Age</th>
<th align="center" valign="top">Total (%)</th>
<th align="left" valign="top">Level of education</th>
<th align="center" valign="top">Total (%)</th>
<th align="left" valign="top">Impairment problems</th>
<th align="center" valign="top">Hearing (%)</th>
<th align="center" valign="top">Visual (%)</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="top">26&#x2013;35</td>
<td align="center" valign="top">225 (41%)</td>
<td align="left" valign="top">Not specified</td>
<td align="center" valign="top">3 (0.6%)</td>
<td align="left" valign="top">Eyeglasses</td>
<td align="center" valign="top">-</td>
<td align="center" valign="top">195 (36%)</td>
</tr>
<tr>
<td align="left" valign="top">36&#x2013;45</td>
<td align="center" valign="top">132 (24%)</td>
<td align="left" valign="top">Undergraduate</td>
<td align="center" valign="top">116 (21.4%)</td>
<td align="left" valign="top">Unknown<xref rid="tfn1" ref-type="table-fn"><sup>&#x002A;</sup></xref></td>
<td align="center" valign="top">11 (2%)</td>
<td align="center" valign="top">22 (4%)</td>
</tr>
<tr>
<td align="left" valign="top">46&#x2013;55</td>
<td align="center" valign="top">108 (20%)</td>
<td align="left" valign="top">Bachelor</td>
<td align="center" valign="top">67 (12.3%)</td>
<td align="left" valign="top">None</td>
<td align="center" valign="top">532 (98%)</td>
<td align="center" valign="top">326 (60%)</td>
</tr>
<tr>
<td align="left" valign="top">56&#x2013;65</td>
<td align="center" valign="top">61 (12%)</td>
<td align="left" valign="top">University</td>
<td align="center" valign="top">276 (50.8%)</td>
<td/>
<td/>
<td/>
</tr>
<tr>
<td align="left" valign="top">65&#x2013;70</td>
<td align="center" valign="top">17 (3%)</td>
<td align="left" valign="top">Master</td>
<td align="center" valign="top">59 (10.9%)</td>
<td/>
<td/>
<td/>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="tfn1">
<label>&#x002A;</label>
<p>Unknown refers to participants who stated that they were unaware of any problem impairment.</p>
</fn>
</table-wrap-foot>
</table-wrap>
</sec>
<sec id="sec5">
<label>3.2.</label>
<title>Factor and attribute selection</title>
<p>Our aim was to measure multisensorial factors regarding different residential environment locations. Specifically, the following factors were assessed: (i) noise-<italic>Sensitivity</italic> described as <italic>&#x03B7;<sub>1</sub></italic>, (ii) sound-<italic>Pleasantness,</italic> labelled as <italic>&#x03B7;<sub>2</sub></italic>, and (iii) <italic>Liveability</italic>, listed as <italic>&#x03B7;</italic><sub><italic>3</italic>,</sub> to explore visual characteristics in the surroundings of a residence. The factor selection process and corresponding indicators are described in the following sub-section. The statements associated with each perceptual indicator resulted from an extensive literature review and subsequent pilot surveys applied to evaluate their appropriateness according to the experimental context, as shown in <xref rid="tab2" ref-type="table">Table 2</xref>. To measure the indicators, we used a five-point Likert scale (1&#x2009;=&#x2009;strongly disagree to 5&#x2009;=&#x2009;strongly agree). The applied survey also included a questionnaire to collect data on sound-visual measures, socio-demographics and dwelling location characteristics, as these attributes could be correlated with the multisensorial factors.</p>
<table-wrap position="float" id="tab2">
<label>Table 2</label>
<caption>
<p>Factors, indicators, and variables.</p>
</caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th align="left" valign="top">Variable/factor</th>
<th align="left" valign="top">Question/indicator</th>
<th align="left" valign="top">Scale</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="top" colspan="2">Socio-demographics (household head)</td>
<td/>
</tr>
<tr>
<td/>
<td align="left" valign="top">Gender</td>
<td align="left" valign="top">Binary</td>
</tr>
<tr>
<td/>
<td align="left" valign="top">Age</td>
<td align="left" valign="top">Categorical</td>
</tr>
<tr>
<td/>
<td align="left" valign="top">Occupation</td>
<td align="left" valign="top">Categorical</td>
</tr>
<tr>
<td/>
<td align="left" valign="top">Health insurance</td>
<td align="left" valign="top">Categorical</td>
</tr>
<tr>
<td/>
<td align="left" valign="top">Level of education</td>
<td align="left" valign="top">Categorical</td>
</tr>
<tr>
<td/>
<td align="left" valign="top">Family income</td>
<td align="left" valign="top">Categorical</td>
</tr>
<tr>
<td/>
<td align="left" valign="top">Health impairment declaration</td>
<td align="left" valign="top">Categorical</td>
</tr>
<tr>
<td align="left" valign="top" colspan="2">Residential location characteristics</td>
<td/>
</tr>
<tr>
<td/>
<td align="left" valign="top">District of residence</td>
<td align="left" valign="top">Categorical</td>
</tr>
<tr>
<td/>
<td align="left" valign="top">Dwelling type and type of ownership</td>
<td align="left" valign="top">Categorical</td>
</tr>
<tr>
<td align="left" valign="top" colspan="2">Noise-Sensitivity <inline-formula>
<mml:math id="M1">
<mml:mrow>
<mml:mrow>
<mml:mo>(</mml:mo>
<mml:mrow>
<mml:msub>
<mml:mi>&#x03B7;</mml:mi>
<mml:mn>1</mml:mn>
</mml:msub>
</mml:mrow>
<mml:mo>)</mml:mo>
</mml:mrow>
</mml:mrow>
</mml:math>
</inline-formula></td>
<td/>
</tr>
<tr>
<td/>
<td align="left" valign="top">I1. I am easily awakened by noise (<italic>easily awakened</italic>)</td>
<td align="left" valign="top">Five-point Likert</td>
</tr>
<tr>
<td/>
<td align="left" valign="top">I2. I find it difficult to relax in a noisy place (<italic>relaxation</italic>)</td>
<td align="left" valign="top">Five-point Likert</td>
</tr>
<tr>
<td/>
<td align="left" valign="top">I3. I complain to people who make intense sounds that keep me from falling asleep (<italic>complain</italic>)</td>
<td align="left" valign="top">Five-point Likert</td>
</tr>
<tr>
<td/>
<td align="left" valign="top">I4. I am sensitive to noise (<italic>sensitivity</italic>)</td>
<td align="left" valign="top">Five-point Likert</td>
</tr>
<tr>
<td align="left" valign="top" colspan="2">Sound-Pleasantness <inline-formula>
<mml:math id="M2">
<mml:mrow>
<mml:mrow>
<mml:mo>(</mml:mo>
<mml:mrow>
<mml:msub>
<mml:mi>&#x03B7;</mml:mi>
<mml:mn>2</mml:mn>
</mml:msub>
</mml:mrow>
<mml:mo>)</mml:mo>
</mml:mrow>
</mml:mrow>
</mml:math>
</inline-formula></td>
<td/>
</tr>
<tr>
<td/>
<td align="left" valign="top">I5. Sounds in this area are pleasant to hear in the surrounding of a dwelling (<italic>pleasant</italic>)</td>
<td align="left" valign="top">Five-point Likert</td>
</tr>
<tr>
<td/>
<td align="left" valign="top">I6. Sounds in this area transmit calm to the surrounding houses (<italic>calm</italic>)</td>
<td align="left" valign="top">Five-point Likert</td>
</tr>
<tr>
<td/>
<td align="left" valign="top">I7. Sounds of this place transmit harmony to inhabitants (<italic>harmonious</italic>)</td>
<td align="left" valign="top">Five-point Likert</td>
</tr>
<tr>
<td align="left" valign="top" colspan="2">Visual-Liveability <inline-formula>
<mml:math id="M3">
<mml:mrow>
<mml:mrow>
<mml:mo>(</mml:mo>
<mml:mrow>
<mml:msub>
<mml:mi>&#x03B7;</mml:mi>
<mml:mn>3</mml:mn>
</mml:msub>
</mml:mrow>
<mml:mo>)</mml:mo>
</mml:mrow>
</mml:mrow>
</mml:math>
</inline-formula></td>
<td/>
</tr>
<tr>
<td/>
<td align="left" valign="top">I8. This residential neighbourhood is attractive to live in (<italic>attractive</italic>)</td>
<td align="left" valign="top">Five-point Likert</td>
</tr>
<tr>
<td/>
<td align="left" valign="top">I9. I could live in a dwelling located in the surroundings of this place (<italic>liveable</italic>)</td>
<td align="left" valign="top">Five-point Likert</td>
</tr>
<tr>
<td/>
<td align="left" valign="top">I10. In this place, I feel safe from crime (<italic>safe</italic>)</td>
<td align="left" valign="top">Five-point Likert</td>
</tr>
</tbody>
</table>
</table-wrap>
<sec id="sec6">
<label>3.2.1.</label>
<title>Noise-sensitivity perception</title>
<p>Insights into the effects of noise-sensitivity and noise-annoyance have been traditionally explored in urban environments (<xref ref-type="bibr" rid="ref38">Nijland et al., 2007</xref>). We extend this line of research by investigating how noise-sensitivity impacts auditory factors, by measuring individual perceptions and how they change according to person-related characteristics (<xref ref-type="bibr" rid="ref52">Tarlao et al., 2021</xref>). Noise-<italic>Sensitivity</italic> can be measured using different questionnaires, including six items (<xref ref-type="bibr" rid="ref26">Kishikawa et al., 2006</xref>), 10 items (<xref ref-type="bibr" rid="ref65">Zimmer and Ellermeier, 1999</xref>) or 21 items (<xref ref-type="bibr" rid="ref61">Weinstein, 1978</xref>). Following <xref ref-type="bibr" rid="ref26">Kishikawa et al. (2006)</xref>, we selected four items from their six-item questionnaire to measure noise-<italic>Sensitivity</italic> in residential environments.</p>
</sec>
<sec id="sec7">
<label>3.2.2.</label>
<title>Sound perception</title>
<p>According to the Circumplex Model of <xref ref-type="bibr" rid="ref7">Axelsson et al. (2010)</xref>, at least two orthogonal descriptors are required to achieve a comprehensive understanding of the acoustic environment. However, we specified sound-<italic>Pleasantness</italic> (<italic>&#x03B7;<sub>2</sub></italic>) as a single latent variable, representing only a part of the aspects investigated for the soundscape. We attempted to build a model keeping a parsimonious structure by using only one factor. Note that <italic>Pleasantness</italic> in outdoor conditions already explains 50% of the variance of the urban soundscape (<xref ref-type="bibr" rid="ref7">Axelsson et al., 2010</xref>). Hence, we sought to discover the causal relationships between <italic>Pleasantness</italic>, socio-demographic characteristics, and the residential location of the participants. The selection of the indicators <italic>pleasant</italic> (I5), <italic>calm</italic> (I6), and <italic>harmonious</italic> (I7), was guided by the estimation of the highest factor loading amongst those reported by <xref ref-type="bibr" rid="ref52">Tarlao et al. (2021)</xref>, <xref ref-type="bibr" rid="ref32">Liu et al. (2019)</xref>, and <xref ref-type="bibr" rid="ref20">Hong and Jeon (2015)</xref>. Further analysis showed that these three adjectives were highly correlated with <italic>Pleasantness</italic> and jointly described the positive characteristics of sounds.</p>
</sec>
<sec id="sec8">
<label>3.2.3.</label>
<title>Visual perception</title>
<p>Visual<italic>-Liveability</italic> (<italic>&#x03B7;<sub>3</sub></italic>) was selected as the latent construct to evaluate visual conditions. Several perceptual indicators can measure this factor, such as <italic>aesthetics</italic> (<xref ref-type="bibr" rid="ref8">Bonaiuto et al., 1999</xref>), <italic>habitable</italic> (<xref ref-type="bibr" rid="ref59">Veenhoven 2000</xref>), <italic>attractive</italic> (<xref ref-type="bibr" rid="ref55">T&#x00FC;rko&#x011F;lu et al., 2019</xref>), and <italic>satisfaction</italic> (<xref ref-type="bibr" rid="ref37">Mouratidis and Yiannakou, 2022</xref>). In this study, the selected indicators refer to issues previously evaluated in Latin American cities, such as <italic>attractive</italic> (I8), <italic>liveable</italic> (I9), and <italic>safe</italic> (I10). The first two are associated with the positive physical neighbourhoods&#x2019; qualitative attributes, which vary according to physical and natural components (<xref ref-type="bibr" rid="ref48">Rossetti et al., 2019</xref>; <xref ref-type="bibr" rid="ref43">Ram&#x00ED;rez et al., 2021</xref>). <italic>Safe</italic>, on the other hand, can affect people&#x2019;s overall liveability perception and is closely related to the presence of people and vehicles in the city (<xref ref-type="bibr" rid="ref23">Iglesias et al., 2013</xref>).</p>
</sec>
<sec id="sec9">
<label>3.2.4.</label>
<title>Socio-demographic and residential location characteristics</title>
<p>The socio-demographic information was consistent with the variables included in Ecuador&#x2019;s population censuses and complemented using household information such as the residential location.</p>
</sec>
<sec id="sec10">
<label>3.2.5.</label>
<title>Survey experimental design</title>
<p>Instead of recreating sound-visual stimuli artificially, we recorded several real-life scenarios to represent different levels of sound-visual attributes. Five sound-visual attributes associated with residential environments were selected (see <xref rid="tab3" ref-type="table">Table 3</xref>) following the results of previous studies (<xref ref-type="bibr" rid="ref25">Jo and Jeon, 2020</xref>; <xref ref-type="bibr" rid="ref63">Yong et al., 2021</xref>). In particular, the <italic>Sound Pressure Level</italic> (SPL) was used and classified as lower and higher than 70&#x2009;dbA (<xref ref-type="bibr" rid="ref62">Yang and Kang, 2005</xref>). The <italic>green space</italic> attribute was measured and classified into lower and higher than 0.25&#x2009;ha using the imagery available on Google Maps. The variables <italic>pedestrian-flow</italic> and <italic>vehicular-flow</italic> were measured on-site and put into two categories: pedestrian-flow lower and higher than 50 (ped/min/m), and vehicle-flow lower and higher than 18<xref rid="fn0004" ref-type="fn"><sup>1</sup></xref> (veh/min/lane; <xref ref-type="bibr" rid="ref54">Transportation Research Board, 2010</xref>). Finally, land uses were categorised to discover the influences in the residential location of proximity to residential, commercial, and recreational environments.</p>
<table-wrap position="float" id="tab3">
<label>Table 3</label>
<caption>
<p>Attributes considered in the experiment.</p>
</caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th align="left" valign="top">Attribute</th>
<th align="left" valign="top">Description</th>
<th align="left" valign="top">Levels</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="top">Equivalent SPL(L<sub>Aeq</sub>)</td>
<td align="left" valign="top">dBA</td>
<td align="left" valign="top">[less than 70] Moderate and High [more than 70]</td>
</tr>
<tr>
<td align="left" valign="top">Green space (<italic>GS</italic>)</td>
<td align="left" valign="top">Hectares</td>
<td align="left" valign="top">[less than 0.25] Low and High [more than 0.25]</td>
</tr>
<tr>
<td align="left" valign="top">Pedestrian flow (<italic>PF</italic>)</td>
<td align="left" valign="top">ped/min/m</td>
<td align="left" valign="top">[less than 50] Low and High [more than 50]</td>
</tr>
<tr>
<td align="left" valign="top">Vehicle flow (<italic>VF</italic>)</td>
<td align="left" valign="top">veh/min/lane</td>
<td align="left" valign="top">[less than 18] Low and High [more than 18]</td>
</tr>
<tr>
<td align="left" valign="top">Land uses (<italic>LU</italic>)</td>
<td/>
<td align="left" valign="top">Residential, commercial, and recreational</td>
</tr>
</tbody>
</table>
</table-wrap>
<p>Using the above attributes, a D-efficient experimental design (<xref ref-type="bibr" rid="ref46">Rose et al., 2008</xref>) using the NGENE software allowed us to configure 36 residential scenarios. As shown in <xref rid="fig1" ref-type="fig">Figure 1</xref>, the residential surroundings locations were selected according to the experimental design and the noise map of Quito (<xref ref-type="bibr" rid="ref9">Bravo-Moncayo et al., 2019</xref>), which is categorised according to SPL.</p>
<fig position="float" id="fig1">
<label>Figure 1</label>
<caption>
<p>Residential environment scenarios.</p>
</caption>
<graphic xlink:href="fpsyg-14-1080149-g001.tif"/>
</fig>
</sec>
<sec id="sec11">
<label>3.2.6.</label>
<title>Sound and visual stimuli</title>
<p>After identifying the residential environment of the different Quito districts, we measured and collected audio-visual extracts <italic>in situ</italic>. Then, two research group members observed the 36 recordings separately to ensure consistency and correspondence to the category specified on each attribute, as described in <xref rid="tab3" ref-type="table">Table 3</xref>.</p>
<p>Once the location was identified, 1-min auditory samples were recorded <italic>in situ</italic> using a portable four-channel cardioid Ambisonic 3D TA-1 microphone, which captured the natural directionality of the spatial audio. Afterwards, these stimuli were used in a playback setup. A second microphone was connected simultaneously with a portable sound level metre (NTI-Audio Model-XL2) for acoustic measurement, as described in <xref rid="tab4" ref-type="table">Table 4</xref>. Both microphones were installed at 1.6&#x2009;m from the ground to approximate the height of a person&#x2019;s ears when standing.</p>
<table-wrap position="float" id="tab4">
<label>Table 4</label>
<caption>
<p>Sound-visual value measurements.</p>
</caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th align="left" valign="top">Scenario</th>
<th align="center" valign="top">L<sub>Ceq,60s</sub> dB</th>
<th align="center" valign="top">TSLV dB</th>
<th align="center" valign="top">L<sub>10</sub> dB</th>
<th align="center" valign="top">L<sub>90</sub> dB</th>
<th align="center" valign="top">L<sub>10&#x2212;</sub>L<sub>90</sub> dB</th>
<th align="center" valign="top">L<sub>Aeq,60s</sub> dB</th>
<th align="center" valign="top">Pedestrian ped/min/m</th>
<th align="center" valign="top">Vehicles veh/min/lane</th>
<th align="center" valign="top">Green spaces hectares</th>
<th align="left" valign="top">Link (YouTube) <ext-link xlink:href="https://youtu.be/" ext-link-type="uri">https://youtu.be/</ext-link></th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="top">1</td>
<td align="center" valign="top">67</td>
<td align="center" valign="top">1.47</td>
<td align="center" valign="top">52.5</td>
<td align="center" valign="top">46.7</td>
<td align="center" valign="top">5.8</td>
<td align="center" valign="top">50.3</td>
<td align="center" valign="top">8</td>
<td align="center" valign="top">7</td>
<td align="center" valign="top">0.30</td>
<td align="left" valign="top">cmExi8ApWD4</td>
</tr>
<tr>
<td align="left" valign="top">2</td>
<td align="center" valign="top">70.6</td>
<td align="center" valign="top">4.83</td>
<td align="center" valign="top">60.5</td>
<td align="center" valign="top">44.1</td>
<td align="center" valign="top">16.4</td>
<td align="center" valign="top">58.7</td>
<td align="center" valign="top">3</td>
<td align="center" valign="top">5</td>
<td align="center" valign="top">0.01</td>
<td align="left" valign="top">Ncuqh7GbVhw</td>
</tr>
<tr>
<td align="left" valign="top">3</td>
<td align="center" valign="top">69.6</td>
<td align="center" valign="top">0.99</td>
<td align="center" valign="top">63.3</td>
<td align="center" valign="top">58.0</td>
<td align="center" valign="top">5.3</td>
<td align="center" valign="top">61.2</td>
<td align="center" valign="top">&#x003E;99</td>
<td align="center" valign="top">1</td>
<td align="center" valign="top">0.30</td>
<td align="left" valign="top">_SzT2on7SHY</td>
</tr>
<tr>
<td align="left" valign="top">4</td>
<td align="center" valign="top">68.6</td>
<td align="center" valign="top">10.61</td>
<td align="center" valign="top">63.3</td>
<td align="center" valign="top">50.5</td>
<td align="center" valign="top">12.8</td>
<td align="center" valign="top">58.8</td>
<td align="center" valign="top">4</td>
<td align="center" valign="top">9</td>
<td align="center" valign="top">0.01</td>
<td align="left" valign="top">0nA9a2We36M</td>
</tr>
<tr>
<td align="left" valign="top">5</td>
<td align="center" valign="top">84.8</td>
<td align="center" valign="top">5.56</td>
<td align="center" valign="top">74.2</td>
<td align="center" valign="top">66.9</td>
<td align="center" valign="top">7.3</td>
<td align="center" valign="top">73.1</td>
<td align="center" valign="top">53</td>
<td align="center" valign="top">41</td>
<td align="center" valign="top">0.06</td>
<td align="left" valign="top">Vv1ifivpKbY</td>
</tr>
<tr>
<td align="left" valign="top">6</td>
<td align="center" valign="top">72.2</td>
<td align="center" valign="top">0.4</td>
<td align="center" valign="top">60.8</td>
<td align="center" valign="top">57.8</td>
<td align="center" valign="top">3.0</td>
<td align="center" valign="top">59.5</td>
<td align="center" valign="top">14</td>
<td align="center" valign="top">4</td>
<td align="center" valign="top">0.40</td>
<td align="left" valign="top">L7J6SkIOlhY</td>
</tr>
<tr>
<td align="left" valign="top">7</td>
<td align="center" valign="top">84.6</td>
<td align="center" valign="top">16.11</td>
<td align="center" valign="top">79</td>
<td align="center" valign="top">65</td>
<td align="center" valign="top">14.0</td>
<td align="center" valign="top">74.5</td>
<td align="center" valign="top">91</td>
<td align="center" valign="top">42</td>
<td align="center" valign="top">0.17</td>
<td align="left" valign="top">eLcCJ1GCN_c</td>
</tr>
<tr>
<td align="left" valign="top">8</td>
<td align="center" valign="top">76.8</td>
<td align="center" valign="top">15.96</td>
<td align="center" valign="top">67.8</td>
<td align="center" valign="top">54.4</td>
<td align="center" valign="top">13.4</td>
<td align="center" valign="top">63.8</td>
<td align="center" valign="top">9</td>
<td align="center" valign="top">77</td>
<td align="center" valign="top">&#x003E;0.99</td>
<td align="left" valign="top">uSKB1JT0CKk</td>
</tr>
<tr>
<td align="left" valign="top">9</td>
<td align="center" valign="top">97.1</td>
<td align="center" valign="top">3.5</td>
<td align="center" valign="top">76.2</td>
<td align="center" valign="top">66.2</td>
<td align="center" valign="top">10.0</td>
<td align="center" valign="top">72.7</td>
<td align="center" valign="top">9</td>
<td align="center" valign="top">&#x003E;99</td>
<td align="center" valign="top">0.02</td>
<td align="left" valign="top">3zJTAPv_6yM</td>
</tr>
<tr>
<td align="left" valign="top">10</td>
<td align="center" valign="top">78.1</td>
<td align="center" valign="top">6.22</td>
<td align="center" valign="top">67.1</td>
<td align="center" valign="top">61.7</td>
<td align="center" valign="top">5.4</td>
<td align="center" valign="top">64.6</td>
<td align="center" valign="top">1</td>
<td align="center" valign="top">1</td>
<td align="center" valign="top">0.01</td>
<td align="left" valign="top">Y6Q18O-7zVs</td>
</tr>
<tr>
<td align="left" valign="top">11</td>
<td align="center" valign="top">83.9</td>
<td align="center" valign="top">5.57</td>
<td align="center" valign="top">68.9</td>
<td align="center" valign="top">60.2</td>
<td align="center" valign="top">8.7</td>
<td align="center" valign="top">55.4</td>
<td align="center" valign="top">1</td>
<td align="center" valign="top">&#x003E;99</td>
<td align="center" valign="top">0.53</td>
<td align="left" valign="top">4&#x2009;g-flhXB_S8</td>
</tr>
<tr>
<td align="left" valign="top">12</td>
<td align="center" valign="top">83</td>
<td align="center" valign="top">1.48</td>
<td align="center" valign="top">80.8</td>
<td align="center" valign="top">73.7</td>
<td align="center" valign="top">7.1</td>
<td align="center" valign="top">77.9</td>
<td align="center" valign="top">&#x003E;99</td>
<td align="center" valign="top">3</td>
<td align="center" valign="top">0.01</td>
<td align="left" valign="top">Xi6Rf2vCbF0</td>
</tr>
<tr>
<td align="left" valign="top">13</td>
<td align="center" valign="top">76.5</td>
<td align="center" valign="top">0.81</td>
<td align="center" valign="top">70.7</td>
<td align="center" valign="top">63.5</td>
<td align="center" valign="top">7.2</td>
<td align="center" valign="top">68.6</td>
<td align="center" valign="top">70</td>
<td align="center" valign="top">58</td>
<td align="center" valign="top">0.35</td>
<td align="left" valign="top">K-Ual5evQi0</td>
</tr>
<tr>
<td align="left" valign="top">14</td>
<td align="center" valign="top">79.2</td>
<td align="center" valign="top">3.74</td>
<td align="center" valign="top">76</td>
<td align="center" valign="top">68.8</td>
<td align="center" valign="top">7.2</td>
<td align="center" valign="top">73.6</td>
<td align="center" valign="top">&#x003E;99</td>
<td align="center" valign="top">8</td>
<td align="center" valign="top">0.01</td>
<td align="left" valign="top">teTZ6hRLrdc</td>
</tr>
<tr>
<td align="left" valign="top">15</td>
<td align="center" valign="top">87.7</td>
<td align="center" valign="top">4.39</td>
<td align="center" valign="top">81.3</td>
<td align="center" valign="top">74.9</td>
<td align="center" valign="top">6.4</td>
<td align="center" valign="top">78.5</td>
<td align="center" valign="top">8</td>
<td align="center" valign="top">&#x003E;99</td>
<td align="center" valign="top">0.01</td>
<td align="left" valign="top">r1UZnNOaq98</td>
</tr>
<tr>
<td align="left" valign="top">16</td>
<td align="center" valign="top">84.4</td>
<td align="center" valign="top">8.73</td>
<td align="center" valign="top">78.9</td>
<td align="center" valign="top">72.3</td>
<td align="center" valign="top">6.6</td>
<td align="center" valign="top">78.9</td>
<td align="center" valign="top">6</td>
<td align="center" valign="top">&#x003E;99</td>
<td align="center" valign="top">0.20</td>
<td align="left" valign="top">eTckO6zJHOA</td>
</tr>
<tr>
<td align="left" valign="top">17</td>
<td align="center" valign="top">86.9</td>
<td align="center" valign="top">4.79</td>
<td align="center" valign="top">74.8</td>
<td align="center" valign="top">65.9</td>
<td align="center" valign="top">8.9</td>
<td align="center" valign="top">73.1</td>
<td align="center" valign="top">8</td>
<td align="center" valign="top">21</td>
<td align="center" valign="top">0.01</td>
<td align="left" valign="top">rrPub_afPhk</td>
</tr>
<tr>
<td align="left" valign="top">18</td>
<td align="center" valign="top">83.6</td>
<td align="center" valign="top">10.62</td>
<td align="center" valign="top">71.7</td>
<td align="center" valign="top">63.3</td>
<td align="center" valign="top">8.4</td>
<td align="center" valign="top">68.4</td>
<td align="center" valign="top">29</td>
<td align="center" valign="top">72</td>
<td align="center" valign="top">0.10</td>
<td align="left" valign="top">krew6cil3FM</td>
</tr>
<tr>
<td align="left" valign="top">19</td>
<td align="center" valign="top">72.9</td>
<td align="center" valign="top">0.31</td>
<td align="center" valign="top">68.9</td>
<td align="center" valign="top">64.7</td>
<td align="center" valign="top">4.2</td>
<td align="center" valign="top">67.1</td>
<td align="center" valign="top">52</td>
<td align="center" valign="top">4</td>
<td align="center" valign="top">0.01</td>
<td align="left" valign="top">-Kjyh55qsFA</td>
</tr>
<tr>
<td align="left" valign="top">20</td>
<td align="center" valign="top">86</td>
<td align="center" valign="top">4.64</td>
<td align="center" valign="top">79.3</td>
<td align="center" valign="top">68.9</td>
<td align="center" valign="top">10.4</td>
<td align="center" valign="top">76.5</td>
<td align="center" valign="top">91</td>
<td align="center" valign="top">42</td>
<td align="center" valign="top">0.17</td>
<td align="left" valign="top">eLcCJ1GCN_c</td>
</tr>
<tr>
<td align="left" valign="top">21</td>
<td align="center" valign="top">81.5</td>
<td align="center" valign="top">2.09</td>
<td align="center" valign="top">67.1</td>
<td align="center" valign="top">61.5</td>
<td align="center" valign="top">5.6</td>
<td align="center" valign="top">64.5</td>
<td align="center" valign="top">5</td>
<td align="center" valign="top">18</td>
<td align="center" valign="top">0.99</td>
<td align="left" valign="top">HNzlrihiV-o</td>
</tr>
<tr>
<td align="left" valign="top">22</td>
<td align="center" valign="top">67.1</td>
<td align="center" valign="top">1.47</td>
<td align="center" valign="top">57.5</td>
<td align="center" valign="top">51.2</td>
<td align="center" valign="top">6.3</td>
<td align="center" valign="top">54.2</td>
<td align="center" valign="top">5</td>
<td align="center" valign="top">1</td>
<td align="center" valign="top">&#x003E;0.99</td>
<td align="left" valign="top">GCSYAeuJXwM</td>
</tr>
<tr>
<td align="left" valign="top">23</td>
<td align="center" valign="top">79.4</td>
<td align="center" valign="top">3.77</td>
<td align="center" valign="top">70</td>
<td align="center" valign="top">63.4</td>
<td align="center" valign="top">6.6</td>
<td align="center" valign="top">67.5</td>
<td align="center" valign="top">52</td>
<td align="center" valign="top">7</td>
<td align="center" valign="top">0.01</td>
<td align="left" valign="top">Qxx9m0FLFfE</td>
</tr>
<tr>
<td align="left" valign="top">24</td>
<td align="center" valign="top">76.5</td>
<td align="center" valign="top">0.81</td>
<td align="center" valign="top">70.7</td>
<td align="center" valign="top">63.5</td>
<td align="center" valign="top">7.2</td>
<td align="center" valign="top">68.6</td>
<td align="center" valign="top">51</td>
<td align="center" valign="top">58</td>
<td align="center" valign="top">0.40</td>
<td align="left" valign="top">DjChFYcVet0</td>
</tr>
<tr>
<td align="left" valign="top">25</td>
<td align="center" valign="top">84.8</td>
<td align="center" valign="top">5.56</td>
<td align="center" valign="top">74.2</td>
<td align="center" valign="top">66.9</td>
<td align="center" valign="top">7.3</td>
<td align="center" valign="top">73.1</td>
<td align="center" valign="top">89</td>
<td align="center" valign="top">51</td>
<td align="center" valign="top">0.01</td>
<td align="left" valign="top">Vv1ifivpKbY</td>
</tr>
<tr>
<td align="left" valign="top">26</td>
<td align="center" valign="top">65.3</td>
<td align="center" valign="top">3.36</td>
<td align="center" valign="top">57</td>
<td align="center" valign="top">47.1</td>
<td align="center" valign="top">9.9</td>
<td align="center" valign="top">53.2</td>
<td align="center" valign="top">4</td>
<td align="center" valign="top">6</td>
<td align="center" valign="top">0.99</td>
<td align="left" valign="top">MNwvuKQVrSM</td>
</tr>
<tr>
<td align="left" valign="top">27</td>
<td align="center" valign="top">81.8</td>
<td align="center" valign="top">1.06</td>
<td align="center" valign="top">70</td>
<td align="center" valign="top">66.4</td>
<td align="center" valign="top">3.6</td>
<td align="center" valign="top">68.6</td>
<td align="center" valign="top">17</td>
<td align="center" valign="top">98</td>
<td align="center" valign="top">0.39</td>
<td align="left" valign="top">Raet_pTkY1E</td>
</tr>
<tr>
<td align="left" valign="top">28</td>
<td align="center" valign="top">83</td>
<td align="center" valign="top">1.48</td>
<td align="center" valign="top">80.8</td>
<td align="center" valign="top">73.7</td>
<td align="center" valign="top">7.1</td>
<td align="center" valign="top">77.9</td>
<td align="center" valign="top">84</td>
<td align="center" valign="top">11</td>
<td align="center" valign="top">0.01</td>
<td align="left" valign="top">Xi6Rf2vCbF0</td>
</tr>
<tr>
<td align="left" valign="top">29</td>
<td align="center" valign="top">80.4</td>
<td align="center" valign="top">3.51</td>
<td align="center" valign="top">69.9</td>
<td align="center" valign="top">59.3</td>
<td align="center" valign="top">10.6</td>
<td align="center" valign="top">66.4</td>
<td align="center" valign="top">39</td>
<td align="center" valign="top">63</td>
<td align="center" valign="top">0.01</td>
<td align="left" valign="top">llzO18JpsgU</td>
</tr>
<tr>
<td align="left" valign="top">30</td>
<td align="center" valign="top">88.1</td>
<td align="center" valign="top">10.57</td>
<td align="center" valign="top">79.2</td>
<td align="center" valign="top">69.5</td>
<td align="center" valign="top">9.7</td>
<td align="center" valign="top">76.4</td>
<td align="center" valign="top">7</td>
<td align="center" valign="top">&#x003E;99</td>
<td align="center" valign="top">0.01</td>
<td align="left" valign="top">6W134ASMQwo</td>
</tr>
<tr>
<td align="left" valign="top">31</td>
<td align="center" valign="top">83.6</td>
<td align="center" valign="top">10.62</td>
<td align="center" valign="top">71.7</td>
<td align="center" valign="top">63.3</td>
<td align="center" valign="top">8.4</td>
<td align="center" valign="top">68.4</td>
<td align="center" valign="top">29</td>
<td align="center" valign="top">72</td>
<td align="center" valign="top">0.10</td>
<td align="left" valign="top">krew6cil3FM</td>
</tr>
<tr>
<td align="left" valign="top">32</td>
<td align="center" valign="top">86.9</td>
<td align="center" valign="top">4.79</td>
<td align="center" valign="top">74.8</td>
<td align="center" valign="top">65.9</td>
<td align="center" valign="top">8.9</td>
<td align="center" valign="top">73.1</td>
<td align="center" valign="top">8</td>
<td align="center" valign="top">21</td>
<td align="center" valign="top">0.01</td>
<td align="left" valign="top">rrPub_afPhk</td>
</tr>
<tr>
<td align="left" valign="top">33</td>
<td align="center" valign="top">67.5</td>
<td align="center" valign="top">0.18</td>
<td align="center" valign="top">61.2</td>
<td align="center" valign="top">58.8</td>
<td align="center" valign="top">2.4</td>
<td align="center" valign="top">60.2</td>
<td align="center" valign="top">38</td>
<td align="center" valign="top">1</td>
<td align="center" valign="top">&#x003E;0.99</td>
<td align="left" valign="top">-G0RVZKco-I</td>
</tr>
<tr>
<td align="left" valign="top">34</td>
<td align="center" valign="top">78.8</td>
<td align="center" valign="top">2.58</td>
<td align="center" valign="top">70.7</td>
<td align="center" valign="top">63.5</td>
<td align="center" valign="top">7.2</td>
<td align="center" valign="top">68.9</td>
<td align="center" valign="top">6</td>
<td align="center" valign="top">79</td>
<td align="center" valign="top">&#x003E;0.99</td>
<td align="left" valign="top">cZ0R4Z2Ja_E</td>
</tr>
<tr>
<td align="left" valign="top">35</td>
<td align="center" valign="top">70.4</td>
<td align="center" valign="top">3.18</td>
<td align="center" valign="top">64.3</td>
<td align="center" valign="top">54.8</td>
<td align="center" valign="top">9.5</td>
<td align="center" valign="top">69.6</td>
<td align="center" valign="top">76</td>
<td align="center" valign="top">1</td>
<td align="center" valign="top">&#x003E;0.99</td>
<td align="left" valign="top">KEQ7uNgW3K0</td>
</tr>
<tr>
<td align="left" valign="top">36</td>
<td align="center" valign="top">68.6</td>
<td align="center" valign="top">10.61</td>
<td align="center" valign="top">63.3</td>
<td align="center" valign="top">50.5</td>
<td align="center" valign="top">12.8</td>
<td align="center" valign="top">58.8</td>
<td align="center" valign="top">1</td>
<td align="center" valign="top">5</td>
<td align="center" valign="top">0.01</td>
<td align="left" valign="top">cnTxJfG1BUQ</td>
</tr>
</tbody>
</table>
</table-wrap>
<p>The equivalent A-weighted (L<sub>Aeq,60s</sub>) and C-weighted (L<sub>Ceq,60s</sub>) continuous sound pressure levels were measured. Then, its difference was calculated in dB (L<sub>Ceq,60s</sub>-L<sub>Aeq,60s</sub>) to indicate the relative proportion of low-frequency sounds. Acoustic measurements of the SPL of the 10th percentile were also obtained (L<sub>10</sub>), representing the most energetic noise sources exceeding 10% of measurement time. In addition, the Temporal Variance of the Sound Pressure Level (TSLV), indicating the variability of the SPL over time during the measurement, was also estimated. The range L<sub>A10</sub>&#x2013;L<sub>A90</sub> was also used as an index of sound environment variability, and it denotes the difference between percentile levels exceeding 10 and 90% of the time.</p>
<p>Complementing the sound recordings, visual stimuli were also obtained using a spherical panoramic camera with 4&#x2009;k ultra-high definition (RICOH THETA V) mounted at 1.6&#x2009;m from the ground to capture omnidirectional video at each location. All videos were recorded for 60&#x2009;s. Each excerpt was processed as a 360-format video in combination with the spatial audio format. This method was described by <xref ref-type="bibr" rid="ref19">Hong et al. (2017)</xref> and recently applied to recreate artificially audio-visual stimuli conditions (<xref ref-type="bibr" rid="ref22">Hong et al., 2020</xref>; <xref ref-type="bibr" rid="ref63">Yong et al., 2021</xref>). However, in this research, all scenarios were recorded to capture the real conditions in different residential surroundings and then reproduced for experimental purposes. All scenarios were captured regarding daytime and avoiding rainy conditions (from 09:00&#x2009;a.m. to 5:00&#x2009;p.m.). The immersive audio-visual excerpts were uploaded to the YouTube platform to be displayed on any device that supports 360 format videos; the links are presented in <xref rid="tab4" ref-type="table">Table 4</xref>, together with the values of the acoustic measurements.</p>
</sec>
</sec>
<sec id="sec12">
<label>3.3.</label>
<title>Experimental setup and exposure conditions</title>
<p>The survey was issued in a digital format and comprised three sections:</p>
<list list-type="order">
<list-item>
<p>Socio-demographic and location information (see <xref rid="tab2" ref-type="table">Table 2</xref>).</p>
</list-item>
<list-item>
<p>Perceptual indicator measurements (see <xref rid="tab2" ref-type="table">Table 2</xref>). In this section, the 36 scenarios were grouped into four blocks of nine scenarios. Then, each participant observed the reproduction of nine scenarios according to the experimental design (see <xref rid="fig1" ref-type="fig">Figure 1</xref>). Note that data gathered from each participant correspond to the level of agreement with all indicators measuring noise-<italic>Sensitivity</italic>, sound-<italic>Pleasantness</italic>, and visual-<italic>Liveability</italic> for every situation within one block.</p>
</list-item>
<list-item>
<p>A stated preference experiment containing three choice situations to assess location preferences. This last section is not used in this paper.</p>
</list-item>
</list>
<p>The experiment was conducted under isolated conditions using a portable round cabin (see <xref rid="fig2" ref-type="fig">Figure 2</xref>). Three columns of the cabin were used to support a curtain attached to a rail. This configuration was intended to isolate respondents from external distractions during the experiment administration. Before entering the cabin, each participant was instructed to use a 13-in digital tablet screen and noise-cancelling headphones, as shown in <xref rid="fig2" ref-type="fig">Figure 2</xref>. The SPL was also measured as a part of the experiment setup applications. On average, it took between 25 and 30&#x2009;min to complete each survey, including viewing time.</p>
<fig position="float" id="fig2">
<label>Figure 2</label>
<caption>
<p>Top view <bold>(A)</bold>, front view <bold>(B)</bold>, and photo <bold>(C)</bold> of the experimental setup <bold>(C)</bold>. Details of equipment and portable structure (1) headphones, (2) tablet, (3) columns, (4) curtain rails, (5) curtain, (6) sonometer, (7) dummy head, and (8) swivel chair.</p>
</caption>
<graphic xlink:href="fpsyg-14-1080149-g002.tif"/>
</fig>
<p>Our approach offers the advantage of portability for conducting the survey. In addition, its cost is lower than the investment needed to use a laboratory, according to the respondents&#x2019; schedules. We had also planned to use a head-mounted virtual reality device (VR-HMD). However, its implementation was complex, and the internet connection required for its operation was not always available on-site. Therefore, a tablet with mobile data and internet support was chosen to administer the survey. The ecological validity of visual devices has been evaluated previously (<xref ref-type="bibr" rid="ref50">Sun et al., 2018b</xref>; <xref ref-type="bibr" rid="ref22">Hong et al., 2020</xref>), as well as applying digital surveys formats in different fields of knowledge (<xref ref-type="bibr" rid="ref30">Liebe et al., 2015</xref>; <xref ref-type="bibr" rid="ref5">Arellana et al., 2020</xref>; <xref ref-type="bibr" rid="ref60">Weber et al., 2022</xref>).</p>
</sec>
<sec id="sec13">
<label>3.4.</label>
<title>Data analysis</title>
<p>First, we performed an exploratory factor analysis (EFA) to extract the main latent constructs from a set of measured indicators without a preconceived structure. Once the structure between indicators and latent variables was identified, a second step based on CFA was applied. The CFA tests the reliability and validity of measurement scales for observed and latent variables. Next, an advanced SEM model was formulated to validate the hypothesis path by estimating the regressor coefficient loadings on the structural model. SEM models were processed and analysed using the Lavaan library (<xref ref-type="bibr" rid="ref47">Rosseel, 2012</xref>) in R-Studio (<xref ref-type="bibr" rid="ref12">CoreTeam, 2018</xref>). Finally, SEM allows the use of mediation analysis and then estimates the loadings of the total effects involving both latent and explanatory variables.</p>
</sec>
</sec>
<sec id="sec14" sec-type="results">
<label>4.</label>
<title>Results</title>
<p>The results are presented in five sections: (1) a descriptive statistical analysis of collected indicators; (2) the EFA to extract principal factors; (3) the CFA to examine the reliability and validity of latent variables; (4) the SEM to describe the relationships amongst the latent constructs; (5) and the mediation analysis to estimate the influence of observable variables on the latent constructs.</p>
<sec id="sec15">
<label>4.1.</label>
<title>Descriptive analysis of indicators</title>
<p><xref rid="fig3" ref-type="fig">Figure 3</xref> summarises the responses to the perceptual indicators described in <xref rid="tab2" ref-type="table">Table 2</xref>. The averages for <italic>relaxation</italic> (I2), <italic>easily awakened</italic> (I1), <italic>complaint</italic> (I3) and <italic>sensitivity</italic> (I4), related to noise-<italic>Sensitivity</italic>, show high perceived values (3.55, 3.33, 3.34 and 3.18, respectively). The mean values for sound-<italic>Pleasantness</italic> indicators, such as <italic>calm</italic> (I6), <italic>harmonious</italic> (I7) and <italic>pleasant</italic> (I5), are relatively neutral (2.57, 2.48 and 2.52, respectively), and the same happens with the visual-<italic>Liveability</italic> indicators, that is, <italic>liveable</italic> (I9), <italic>safe</italic> (I10) and <italic>attractive</italic> (I8), with values of 2.83, 2.77 and 2.69, respectively.</p>
<fig position="float" id="fig3">
<label>Figure 3</label>
<caption>
<p>Rates of perceived indicators of noise-sensitivity <bold>(A)</bold>, sound-pleasantness <bold>(B)</bold>, and visual-liveability <bold>(C)</bold>.</p>
</caption>
<graphic xlink:href="fpsyg-14-1080149-g003.tif"/>
</fig>
</sec>
<sec id="sec16">
<label>4.2.</label>
<title>Exploratory factor analysis</title>
<p>A varimax-rotated principal component analysis was employed to define orthogonal factors and extract their main indicators. We used the Kaiser&#x2013;Meyer&#x2013;Olkin Index (KMO&#x2009;=&#x2009;0.87) and the Measure of Sampling Adequacy (MSA) for each indicator (<xref ref-type="bibr" rid="ref11">Cerny and Kaiser, 1977</xref>) as sample adequacy criteria. In particular, based on the MSA measures, all indicators were above the 0.7 threshold index and were considered acceptable.</p>
<p><xref rid="tab5" ref-type="table">Table 5</xref> shows that three factors with the criterion of an eigenvalue more significant than one were extracted. These represented 59.8% of the total variance, with loadings ranging from 0.45 to 0.86. Factor 1 represented the noise-<italic>Sensitivity</italic> of householders and explained 14.1% of the variances. Factor 2 showed high factors loading, principally for <italic>pleasant</italic> and then <italic>calm</italic> and <italic>harmonious</italic>. Factor 3 was measured by indicators including <italic>attractive, liveable</italic> and <italic>safe</italic>. Factors 2 and 3 explained 27.2 and 18.5% of the variance. The principal factors extracted from the EFA align with previous studies (<xref ref-type="bibr" rid="ref20">Hong and Jeon, 2015</xref>). The corresponding structure was used in the CFA.</p>
<table-wrap position="float" id="tab5">
<label>Table 5</label>
<caption>
<p>Factor loadings for the analysis EFA model.</p>
</caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th align="left" valign="top">Indicators</th>
<th align="center" valign="top">MSA</th>
<th align="center" valign="top">Factor loading</th>
<th align="center" valign="top">Variance explained (%)</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="top">Factor 1: Noise-sensitivity</td>
<td/>
<td/>
<td align="center" valign="top"><bold>14.1</bold></td>
</tr>
<tr>
<td align="left" valign="top"><italic>I1. Easily awakened</italic></td>
<td align="center" valign="top">0.75</td>
<td align="center" valign="top">0.57</td>
<td/>
</tr>
<tr>
<td align="left" valign="top"><italic>I2. Relaxation</italic></td>
<td align="center" valign="top">0.78</td>
<td align="center" valign="top">0.45</td>
<td/>
</tr>
<tr>
<td align="left" valign="top"><italic>I3. Complain</italic></td>
<td align="center" valign="top">0.70</td>
<td align="center" valign="top">0.67</td>
<td/>
</tr>
<tr>
<td align="left" valign="top"><italic>I4. Sensitivity</italic></td>
<td align="center" valign="top">0.71</td>
<td align="center" valign="top">0.65</td>
<td/>
</tr>
<tr>
<td align="left" valign="top">Factor 2: Sound-pleasantness</td>
<td/>
<td/>
<td align="center" valign="top"><bold>27.2</bold></td>
</tr>
<tr>
<td align="left" valign="top"><italic>I5. Pleasant</italic></td>
<td align="center" valign="top">0.87</td>
<td align="center" valign="top">0.86</td>
<td/>
</tr>
<tr>
<td align="left" valign="top"><italic>I6. Calm</italic></td>
<td align="center" valign="top">0.91</td>
<td align="center" valign="top">0.78</td>
<td/>
</tr>
<tr>
<td align="left" valign="top"><italic>I7. Harmonious</italic></td>
<td align="center" valign="top">0.87</td>
<td align="center" valign="top">0.86</td>
<td/>
</tr>
<tr>
<td align="left" valign="top">Factor 3: Visual-liveability</td>
<td/>
<td/>
<td align="center" valign="top"><bold>18.5</bold></td>
</tr>
<tr>
<td align="left" valign="top"><italic>I8. Attractive</italic></td>
<td align="center" valign="top">0.87</td>
<td align="center" valign="top">0.73</td>
<td/>
</tr>
<tr>
<td align="left" valign="top"><italic>I9. Liveable</italic></td>
<td align="center" valign="top">0.86</td>
<td align="center" valign="top">0.79</td>
<td/>
</tr>
<tr>
<td align="left" valign="top"><italic>I10. Safe</italic></td>
<td align="center" valign="top">0.94</td>
<td align="center" valign="top">0.57</td>
<td/>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="tfn8">
<p>The bold values represent the total variance estimated for each factor.</p>
</fn>
</table-wrap-foot>
</table-wrap>
</sec>
<sec id="sec17">
<label>4.3.</label>
<title>Confirmatory factor analysis</title>
<p>A CFA (<xref ref-type="bibr" rid="ref33">Long, 1983</xref>) was performed to examine the reliability and validity of the latent variables (see <xref rid="tab6" ref-type="table">Table 6</xref>). A Cronbach-alpha coefficient with a minimum value of 0.7 is usually considered to determine good reliability (<xref ref-type="bibr" rid="ref39">Nunnally and Bernstein, 1968</xref>). However, <xref ref-type="bibr" rid="ref16">Hair et al. (2018)</xref> suggested examining convergent validity according to three reliability criteria values: construct reliability (CR), average variance extracted (AVE), and standardised factor loadings. The observed variables showed reasonably good convergent validity with values higher than 0.5 and confirmed satisfactory convergent validity (Std.factor.loading &#x2265;0.5, AVE&#x2009;&#x2265;&#x2009;0.6, CR&#x2009;&#x2265;&#x2009;0.6). The constructs show good validity and adequate values of reliability, in line with recommended values in the literature (MSV&#x2009;&#x003C;&#x2009;AVE, ASV&#x2009;&#x003C;&#x2009;AVE; <xref ref-type="bibr" rid="ref64">Zhao et al., 2021</xref>). Therefore, the goodness-of-fit estimates in the CFA model were barely accepted for the indicators associated with noise-<italic>Sensitivity</italic>, in contrast to the other factors of sound-<italic>Pleasantness</italic> and visual-<italic>Liveability</italic>, which were superior.</p>
<table-wrap position="float" id="tab6">
<label>Table 6</label>
<caption>
<p>CFA Results.</p>
</caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th align="left" valign="top">Latent variable</th>
<th align="center" valign="top">Cronbach&#x2019;s alpha</th>
<th align="center" valign="top">Std. factor loading</th>
<th align="center" valign="top">CR</th>
<th align="center" valign="top">AVE</th>
<th align="center" valign="top">MSV</th>
<th align="center" valign="top">ASV</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="top">Noise-sensitivity <inline-formula>
<mml:math id="M4">
<mml:mrow>
<mml:msub>
<mml:mi>&#x03B7;</mml:mi>
<mml:mn>1</mml:mn>
</mml:msub>
</mml:mrow>
</mml:math>
</inline-formula></td>
<td align="center" valign="top"><bold>0.67</bold></td>
<td/>
<td align="center" valign="top"><bold>0.68</bold></td>
<td align="center" valign="top"><bold>0.65</bold></td>
<td align="center" valign="top"><bold>0.63</bold></td>
<td align="center" valign="top"><bold>0.43</bold></td>
</tr>
<tr>
<td align="left" valign="top"><italic>I1. Easily awakened</italic></td>
<td/>
<td align="center" valign="top">0.56</td>
<td/>
<td/>
<td/>
<td/>
</tr>
<tr>
<td align="left" valign="top"><italic>I2. Relaxation</italic></td>
<td/>
<td align="center" valign="top">0.50</td>
<td/>
<td/>
<td/>
<td/>
</tr>
<tr>
<td align="left" valign="top"><italic>I3. Complain</italic></td>
<td/>
<td align="center" valign="top">0.64</td>
<td/>
<td/>
<td/>
<td/>
</tr>
<tr>
<td align="left" valign="top"><italic>I4. Sensitivity</italic></td>
<td/>
<td align="center" valign="top">0.67</td>
<td/>
<td/>
<td/>
<td/>
</tr>
<tr>
<td align="left" valign="top">Sound-pleasantness <inline-formula>
<mml:math id="M5">
<mml:mrow>
<mml:msub>
<mml:mi>&#x03B7;</mml:mi>
<mml:mn>2</mml:mn>
</mml:msub>
</mml:mrow>
</mml:math>
</inline-formula></td>
<td align="center" valign="top"><bold>0.94</bold></td>
<td/>
<td align="center" valign="top"><bold>0.94</bold></td>
<td align="center" valign="top"><bold>0.84</bold></td>
<td align="center" valign="top"><bold>0.30</bold></td>
<td align="center" valign="top"><bold>0.18</bold></td>
</tr>
<tr>
<td align="left" valign="top"><italic>I5. Pleasant</italic></td>
<td/>
<td align="center" valign="top">0.94</td>
<td/>
<td/>
<td/>
<td/>
</tr>
<tr>
<td align="left" valign="top"><italic>I6. Calm</italic></td>
<td/>
<td align="center" valign="top">0.89</td>
<td/>
<td/>
<td/>
<td/>
</tr>
<tr>
<td align="left" valign="top"><italic>I7. Harmonious</italic></td>
<td/>
<td align="center" valign="top">0.91</td>
<td/>
<td/>
<td/>
<td/>
</tr>
<tr>
<td align="left" valign="top">Visual-liveability <inline-formula>
<mml:math id="M6">
<mml:mrow>
<mml:msub>
<mml:mi>&#x03B7;</mml:mi>
<mml:mn>3</mml:mn>
</mml:msub>
</mml:mrow>
</mml:math>
</inline-formula></td>
<td align="center" valign="top"><bold>0.85</bold></td>
<td/>
<td align="center" valign="top"><bold>0.85</bold></td>
<td align="center" valign="top"><bold>0.67</bold></td>
<td align="center" valign="top"><bold>0.18</bold></td>
<td align="center" valign="top"><bold>0.12</bold></td>
</tr>
<tr>
<td align="left" valign="top"><italic>I8. Attractive</italic></td>
<td/>
<td align="center" valign="top">0.81</td>
<td/>
<td/>
<td/>
<td/>
</tr>
<tr>
<td align="left" valign="top"><italic>I9. Liveable</italic></td>
<td/>
<td align="center" valign="top">0.88</td>
<td/>
<td/>
<td/>
<td/>
</tr>
<tr>
<td align="left" valign="top"><italic>I10. Safe</italic></td>
<td/>
<td align="center" valign="top">0.76</td>
<td/>
<td/>
<td/>
<td/>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="tfn5">
<p>The bold values represent the total variance estimated for each factor.</p>
</fn>
</table-wrap-foot>
</table-wrap>
</sec>
<sec id="sec18">
<label>4.4.</label>
<title>Concept of a structural equation model</title>
<p>Although there are studies examining associations between auditory and visual latent variables, we have not found prior theory-driven considerations to jointly explore the relationships between noise-<italic>Sensitivity</italic>, sound-<italic>Pleasantness</italic> and visual-<italic>Liveability</italic> (<xref ref-type="bibr" rid="ref6">Aulia, 2016</xref>; <xref ref-type="bibr" rid="ref3">Amir et al., 2021</xref>). Latent constructs, such as noise-<italic>Sensitivity</italic>, have been traditionally analysed jointly with person-related attributes (i.e., socio-demographic information) and noise-annoyance (<xref ref-type="bibr" rid="ref57">Van Kamp et al., 2004</xref>).</p>
<p>Moreover, there is evidence in the literature to suggest that the socio-demographic variables influence both noise-<italic>Sensitivity</italic> and auditory factors and that these influences may change with location and activity (<xref ref-type="bibr" rid="ref22">Hong et al., 2020</xref>; <xref ref-type="bibr" rid="ref52">Tarlao et al., 2021</xref>). The effects of auditory and visual factors in different urban contexts have also been demonstrated. However, only a limited discussion is available concerning the influence of <italic>Pleasantness</italic> as an auditory factor and latent visual constructs such as <italic>Liveability</italic> (<xref ref-type="bibr" rid="ref58">Van Kamp et al., 2003</xref>; <xref ref-type="bibr" rid="ref3">Amir et al., 2021</xref>; <xref ref-type="bibr" rid="ref37">Mouratidis and Yiannakou, 2022</xref>), especially in a Latin American context. Conversely, <xref ref-type="bibr" rid="ref63">Yong et al. (2021)</xref> highlight that objective sound-visual components correlate with urban auditory factors. Within the framework of this paper, following relationships found in previous studies and former results, a conceptual SEM was tested concerning the four hypotheses depicted in <xref rid="fig4" ref-type="fig">Figure 4</xref> for a residential environment context:</p>
<fig position="float" id="fig4">
<label>Figure 4</label>
<caption>
<p>Conceptual SEM model.</p>
</caption>
<graphic xlink:href="fpsyg-14-1080149-g004.tif"/>
</fig>
<disp-quote>
<p><bold><italic>H</italic></bold><sub><bold><italic>A</italic></bold>
</sub>: The noise-Sensitivity of individuals negatively influences the Pleasantness of the sounds.</p>
</disp-quote>
<disp-quote>
<p><bold><italic>H</italic></bold><sub><bold><italic>B</italic></bold>
</sub>: The visual-Liveability conditions are positively correlated to sound-Pleasantness.</p>
</disp-quote>
<disp-quote>
<p><bold><italic>H</italic></bold><sub><bold><italic>C1</italic>:</bold>
</sub> The socio-demographic characteristics of citizens influence noise-Sensitivity, sound-Pleasantness, and visual-Liveability.</p>
</disp-quote>
<disp-quote>
<p><bold><italic>H</italic></bold><sub><bold><italic>C2</italic>:</bold>
</sub> The location of the dwelling influences noise-Sensitivity, sound-Pleasantness, and visual-Liveability.</p>
</disp-quote>
<p>The conceptual model in <xref rid="fig4" ref-type="fig">Figure 4</xref> considers the socio-demographic and location variables as regressors and includes the latent variables. The values of the goodness-of-fit indices<xref rid="fn0005" ref-type="fn"><sup>2</sup></xref> for the conceptual model are presented in <xref rid="tab7" ref-type="table">Table 7</xref>. The socio-demographic variables were categorised as follows: <italic>gender</italic> (&#x201C;female,&#x201D; male), <italic>age</italic> (&#x201C;young,&#x201D; adult and elderly), <italic>income level</italic> (&#x201C;low-income,&#x201D; middle-income and upper-income), <italic>education degree</italic> (&#x201C;elementary,&#x201D; high-school and university), <italic>employment status</italic> (&#x201C;unskilled,&#x201D; qualified and specialised). The location variables were defined as <italic>residential location</italic> (&#x201C;south-Quito,&#x201D; north-Quito, and centre-Quito) and <italic>land use</italic> (&#x201C;residential,&#x201D; recreational, and commercial). All these variables have a reference category put in quotation marks (e.g., &#x201C;south-Quito&#x201D; is the reference category for residential locations in the city) to capture the heterogeneity across householders&#x2019; perceptions.</p>
<table-wrap position="float" id="tab7">
<label>Table 7</label>
<caption>
<p>Goodness-of-fit indices of the tested models and recommended values (<italic>N</italic>&#x2009;=&#x2009;543).</p>
</caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th align="left" valign="top">Model fit index</th>
<th align="center" valign="top"><inline-formula>
<mml:math id="M7">
<mml:mrow>
<mml:msubsup>
<mml:mi>&#x03C7;</mml:mi>
<mml:mrow>
<mml:mi>S</mml:mi>
<mml:mi>B</mml:mi>
</mml:mrow>
<mml:mn>2</mml:mn>
</mml:msubsup>
</mml:mrow>
</mml:math>
</inline-formula>/df</th>
<th align="center" valign="top">CFI</th>
<th align="center" valign="top">TLI</th>
<th align="center" valign="top">RMSEA</th>
<th align="center" valign="top">SRMR</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="top">Conceptual model values</td>
<td align="center" valign="top">4.40</td>
<td align="center" valign="top">0.997</td>
<td align="center" valign="top">0.999</td>
<td align="center" valign="top">0.025</td>
<td align="center" valign="top">0.018</td>
</tr>
<tr>
<td align="left" valign="top">Modified model values</td>
<td align="center" valign="top">4.20</td>
<td align="center" valign="top">0.997</td>
<td align="center" valign="top">0.999</td>
<td align="center" valign="top">0.027</td>
<td align="center" valign="top">0.018</td>
</tr>
<tr>
<td align="left" valign="top">Recommended values</td>
<td align="center" valign="top">&#x003C; 5.0</td>
<td align="center" valign="top">&#x003E;0.90</td>
<td align="center" valign="top">&#x003E;0.90</td>
<td align="center" valign="top">&#x003C; 0.08</td>
<td align="center" valign="top">&#x003C; 0.05</td>
</tr>
</tbody>
</table>
</table-wrap>
<p>In particular, the respondent&#x2019;s socio-demographics and residential location characteristics were associated with all latent constructs as explanatory variables. Besides, on the specification of <italic>sound-Pleasantness</italic> <inline-formula>
<mml:math id="M8">
<mml:mrow>
<mml:mrow>
<mml:mo>(</mml:mo>
<mml:mrow>
<mml:msub>
<mml:mi>&#x03B7;</mml:mi>
<mml:mn>2</mml:mn>
</mml:msub>
</mml:mrow>
<mml:mo>)</mml:mo>
</mml:mrow>
</mml:mrow>
</mml:math>
</inline-formula> all acoustic components were also included (i.e., <italic>L<sub>Aeq,60s</sub></italic>, <italic>L<sub>Ceq,60s</sub>, L<sub>10</sub></italic>, <italic>L<sub>90</sub></italic>, <italic>L<sub>10</sub></italic>-<italic>L<sub>90,</sub> TSLV</italic>). On the other hand, the understanding of <italic>visual-Liveability</italic> <inline-formula>
<mml:math id="M9">
<mml:mrow>
<mml:mrow>
<mml:mo>(</mml:mo>
<mml:mrow>
<mml:msub>
<mml:mi>&#x03B7;</mml:mi>
<mml:mn>3</mml:mn>
</mml:msub>
</mml:mrow>
<mml:mo>)</mml:mo>
</mml:mrow>
</mml:mrow>
</mml:math>
</inline-formula> was complemented by the specification of the visual measures used in the configuration of the experimental design (see <xref rid="tab4" ref-type="table">Table 4</xref>).</p>
</sec>
<sec id="sec19">
<label>4.5.</label>
<title>Modified structural equation model</title>
<p>The approach to identifying the best path model was as follows. First, we checked if the regressors had the correct sign. Then, to define the paths, we specified those categories that were statistically significant. Finally, the modification process stopped when the goodness-of-fit indices surpassed the recommended values from the precedent model, as shown in <xref rid="tab7" ref-type="table">Table 7</xref>. The modified model has 78 parameters, as shown in <xref rid="fig5" ref-type="fig">Figure 5</xref>, and the estimation results are given in <xref rid="tab8" ref-type="table">Table 8</xref>. These results indicate a good-level-of-fit for assessing the structural model validity, according to the recommended criteria described in the literature (<xref ref-type="bibr" rid="ref16">Hair et al., 2018</xref>). The regression path loadings of the models were estimated using the Diagonally Weighted Least Squares (DWLS) method, where the explanatory variables were specified as ordinal in the latent construct (<xref ref-type="bibr" rid="ref13">Distefano and Morgan, 2014</xref>).</p>
<fig position="float" id="fig5">
<label>Figure 5</label>
<caption>
<p>Results of the modified SEM model.</p>
</caption>
<graphic xlink:href="fpsyg-14-1080149-g005.tif"/>
</fig>
<table-wrap position="float" id="tab8">
<label>Table 8</label>
<caption>
<p>Full structural equation model, measurement, and regressions.</p>
</caption>
<table frame="hsides" rules="groups">
<thead>
<tr>
<th align="left" valign="top">Measurement</th>
<th align="center" valign="top">Estimate</th>
<th align="center" valign="top">S.E.</th>
<th align="center" valign="top">Value of <italic>p</italic></th>
<th align="center" valign="top">Standardised estimate</th>
</tr>
</thead>
<tbody>
<tr>
<td align="left" valign="top">Noise-sensitivity</td>
<td/>
<td/>
<td/>
<td/>
</tr>
<tr>
<td align="left" valign="top"><italic>I1. Easily awakened</italic></td>
<td align="center" valign="top">0.619</td>
<td align="center" valign="top">0.011</td>
<td align="center" valign="top">&#x003C; 0.001</td>
<td align="center" valign="top">0.628</td>
</tr>
<tr>
<td align="left" valign="top"><italic>I2. Relaxation</italic></td>
<td align="center" valign="top">0.523</td>
<td align="center" valign="top">0.012</td>
<td align="center" valign="top">&#x003C; 0.001</td>
<td align="center" valign="top">0.533</td>
</tr>
<tr>
<td align="left" valign="top"><italic>I3. Complaint</italic></td>
<td align="center" valign="top">0.701</td>
<td align="center" valign="top">0.011</td>
<td align="center" valign="top">&#x003C; 0.001</td>
<td align="center" valign="top">0.709</td>
</tr>
<tr>
<td align="left" valign="top"><italic>I4. Sensitivity</italic></td>
<td align="center" valign="top">0.704</td>
<td align="center" valign="top">0.011</td>
<td align="center" valign="top">&#x003C; 0.001</td>
<td align="center" valign="top">0.713</td>
</tr>
<tr>
<td align="left" valign="top">Sound-pleasantness</td>
<td/>
<td/>
<td/>
<td/>
</tr>
<tr>
<td align="left" valign="top"><italic>I5. Pleasant</italic></td>
<td align="center" valign="top">0.907</td>
<td align="center" valign="top">0.003</td>
<td align="center" valign="top">&#x003C; 0.001</td>
<td align="center" valign="top">0.924</td>
</tr>
<tr>
<td align="left" valign="top"><italic>I6. Calm</italic></td>
<td align="center" valign="top">0.888</td>
<td align="center" valign="top">0.004</td>
<td align="center" valign="top">&#x003C; 0.001</td>
<td align="center" valign="top">0.908</td>
</tr>
<tr>
<td align="left" valign="top"><italic>I7. Harmonious</italic></td>
<td align="center" valign="top">0.902</td>
<td align="center" valign="top">0.003</td>
<td align="center" valign="top">&#x003C; 0.001</td>
<td align="center" valign="top">0.920</td>
</tr>
<tr>
<td align="left" valign="top">Visual-liveability</td>
<td/>
<td/>
<td/>
<td/>
</tr>
<tr>
<td align="left" valign="top"><italic>I8. Attractive</italic></td>
<td align="center" valign="top">0.527</td>
<td align="center" valign="top">0.007</td>
<td align="center" valign="top">&#x003C; 0.001</td>
<td align="center" valign="top">0.907</td>
</tr>
<tr>
<td align="left" valign="top"><italic>I9. Liveable</italic></td>
<td align="center" valign="top">0.530</td>
<td align="center" valign="top">0.007</td>
<td align="center" valign="top">&#x003C; 0.001</td>
<td align="center" valign="top">0.910</td>
</tr>
<tr>
<td align="left" valign="top"><italic>I10. Safe</italic></td>
<td align="center" valign="top">0.464</td>
<td align="center" valign="top">0.006</td>
<td align="center" valign="top">&#x003C; 0.001</td>
<td align="center" valign="top">0.817</td>
</tr>
<tr>
<td align="left" valign="top">Regressions</td>
<td align="center" valign="top">Noise-sensitivity</td>
<td align="center" valign="top">Sound-pleasantness</td>
<td align="center" valign="top" colspan="2">Visual-liveability</td>
</tr>
<tr>
<td align="left" valign="top">Direct effect</td>
<td align="center" valign="top">(<italic>y</italic><sub>0</sub>) &#x2212;0.094<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top">(<italic>z</italic><sub>0</sub>) 0.762<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td colspan="2"/>
</tr>
<tr>
<td align="left" valign="top">Gender</td>
<td align="center" valign="top">(<italic>x</italic><sub>1</sub>) 0.074<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top">(<italic>y<sub>1</sub></italic>) &#x2212;0.064<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>1</sub>) &#x2212;0.021<sup>&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">Adult</td>
<td/>
<td align="center" valign="top">(<italic>y</italic><sub>2</sub>) &#x2212;0.063<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>2</sub>) &#x2212;0.022<sup>&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">Elderly</td>
<td align="center" valign="top">(<italic>x</italic><sub>3</sub>) 0.073<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td/>
<td colspan="2"/>
</tr>
<tr>
<td align="left" valign="top">High-school-degree</td>
<td align="center" valign="top">(<italic>x</italic><sub>4</sub>) 0.303<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td/>
<td colspan="2"/>
</tr>
<tr>
<td align="left" valign="top">University-degree</td>
<td align="center" valign="top">(<italic>x</italic><sub>5</sub>)0.368<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top">(<italic>y</italic><sub>5</sub>) &#x2212;0.115<sup>&#x002A;&#x002A;</sup></td>
<td colspan="2"/>
</tr>
<tr>
<td align="left" valign="top">Qualified-work</td>
<td align="center" valign="top">(<italic>x</italic><sub>6</sub>) 0.207<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top">(<italic>y</italic><sub>6</sub>) &#x2212;0.077<sup>&#x002A;&#x002A;</sup></td>
<td colspan="2"/>
</tr>
<tr>
<td align="left" valign="top">Specialised-work</td>
<td align="center" valign="top">(<italic>x</italic><sub>7</sub>) 0.240<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td/>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>7</sub>) &#x2212;0.070<sup>&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">Middle-income</td>
<td align="center" valign="top">(<italic>x</italic><sub>8</sub>) 0.080<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td/>
<td colspan="2"/>
</tr>
<tr>
<td align="left" valign="top">Upper-income</td>
<td align="center" valign="top">(<italic>x</italic><sub>9</sub>) 0.110<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td/>
<td colspan="2"/>
</tr>
<tr>
<td align="left" valign="top">Pedestrian flow</td>
<td/>
<td/>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>8</sub>) &#x2212;0.086<sup>&#x002A;&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">Vehicles flow</td>
<td/>
<td/>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>9</sub>) 0.043<sup>&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">Green-spaces</td>
<td/>
<td/>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>15</sub>) 0.031</td>
</tr>
<tr>
<td align="left" valign="top">Commercial land_use</td>
<td/>
<td/>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>11</sub>) &#x2212;0.177<sup>&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">L<sub>Aeq,60s</sub></td>
<td/>
<td align="center" valign="top">(<italic>y</italic><sub>10</sub>) &#x2212;0.250<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td colspan="2"/>
</tr>
<tr>
<td align="left" valign="top">L<sub>Ceq,60s</sub></td>
<td/>
<td align="center" valign="top">(<italic>y</italic><sub>11</sub>) &#x2212;0.121<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td colspan="2"/>
</tr>
<tr>
<td align="left" valign="top">L<sub>10</sub>-L<sub>90</sub></td>
<td/>
<td align="center" valign="top">(<italic>y</italic><sub>12</sub>) &#x2212;0.072<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td colspan="2"/>
</tr>
<tr>
<td align="left" valign="top">North-Quito</td>
<td/>
<td align="center" valign="top">(<italic>y</italic><sub>13</sub>) &#x2212;0.037<sup>&#x002A;</sup></td>
<td colspan="2"/>
</tr>
<tr>
<td align="left" valign="top">Centre-Quito</td>
<td align="center" valign="top">(<italic>x</italic><sub>14</sub>) 0.048<sup>&#x002A;&#x002A;</sup></td>
<td/>
<td colspan="2"/>
</tr>
<tr>
<td align="left" valign="top">Total effect</td>
<td/>
<td/>
<td colspan="2"/>
</tr>
<tr>
<td align="left" valign="top">Gender</td>
<td align="center" valign="top">(<italic>x</italic><sub>1</sub>) 0.074<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top">(<italic>y</italic><sub>1</sub> + <italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>1</sub>) &#x2212;0.071<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>1</sub> + <italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>1</sub> + <italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>1</sub>) &#x2212;0.075<sup>&#x002A;&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">Adult</td>
<td/>
<td align="center" valign="top">(<italic>y</italic><sub>2</sub>) &#x2212;0.063<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>2</sub> + <italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>2</sub> + <italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>2</sub>) &#x2212;0.07<sup>&#x002A;&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">Elderly</td>
<td align="center" valign="top">(<italic>x</italic><sub>3</sub>) 0.073<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top">(<italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>3</sub>) &#x2212;0.007<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>3</sub>) &#x2212;0.005<sup>&#x002A;&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">High-school-degree</td>
<td align="center" valign="top">(<italic>x</italic><sub>4</sub>) 0.303<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top">(<italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>4</sub>) &#x2212;0.029<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>4</sub>) &#x2212;0.022<sup>&#x002A;&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">University-degree</td>
<td align="center" valign="top">(<italic>x</italic><sub>5</sub>) 0.368<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top">(<italic>y</italic><sub>5</sub> + <italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>5</sub>) &#x2212;0.150<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>5</sub> + <italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>5</sub>) &#x2212;0.114<sup>&#x002A;&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">Qualified-work</td>
<td align="center" valign="top">(<italic>x</italic><sub>6</sub>) 0.207<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top">(<italic>y</italic><sub>6</sub> + <italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>6</sub>) &#x2212;0.097<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>6</sub> + <italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>6</sub>)&#x2212;0.074<sup>&#x002A;&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">Specialised-work</td>
<td align="center" valign="top">(<italic>x</italic><sub>7</sub>) 0.240<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top">(<italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>7</sub>) &#x2212;0.023<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>7</sub> + <italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>7</sub>) &#x2212;0.087<sup>&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">Middle-income</td>
<td align="center" valign="top">(<italic>x</italic><sub>8</sub>) 0.080<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top">(<italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>8</sub>) &#x2212;0.008<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>8</sub>) &#x2212;0.006<sup>&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">Upper-income</td>
<td align="center" valign="top">(<italic>x</italic><sub>9</sub>) 0.110<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top">(<italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>9</sub>) &#x2212;0.010<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>9</sub>) &#x2212;0.008<sup>&#x002A;&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">Pedestrian flow</td>
<td/>
<td/>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>8</sub>) &#x2212;0.086<sup>&#x002A;&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">Vehicle flow</td>
<td/>
<td/>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>9</sub>) 0.043<sup>&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">Green-spaces</td>
<td/>
<td/>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>15</sub>) 0.031</td>
</tr>
<tr>
<td align="left" valign="top">Commercial land_use</td>
<td/>
<td/>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>11</sub>) &#x2212;0.177<sup>&#x002A;&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">L<sub>Aeq,60s</sub></td>
<td/>
<td align="center" valign="top">(<italic>y</italic><sub>10</sub>) &#x2212;0.250<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>10</sub>) &#x2212;0.019<sup>&#x002A;&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">L<sub>Ceq,60s</sub></td>
<td/>
<td align="center" valign="top">(<italic>y</italic><sub>11</sub>) &#x2212;0.121<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>11</sub>) &#x2212;0.092<sup>&#x002A;&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">L<sub>10</sub>-L<sub>90</sub></td>
<td/>
<td align="center" valign="top">(<italic>y</italic><sub>12</sub>) &#x2212;0.072<sup>&#x002A;&#x002A;&#x002A;</sup></td>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>12</sub>) &#x2212;0.055<sup>&#x002A;&#x002A;&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">North-Quito</td>
<td/>
<td align="center" valign="top">(<italic>y</italic><sub>13</sub>) &#x2212;0.037<sup>&#x002A;</sup></td>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>13</sub>) &#x2212;0.028<sup>&#x002A;</sup></td>
</tr>
<tr>
<td align="left" valign="top">Centre-Quito</td>
<td align="center" valign="top">(<italic>x</italic><sub>14</sub>) 0.048<sup>&#x002A;&#x002A;</sup></td>
<td align="center" valign="top">(<italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>14</sub>) &#x2212;0.005<sup>&#x002A;</sup></td>
<td align="center" valign="top" colspan="2">(<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>14</sub>) &#x2212;0.003<sup>&#x002A;</sup></td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<p><italic>p</italic>&#x2009;&#x003C;&#x2009;0.10, <sup>&#x002A;</sup><italic>p</italic>&#x2009;&#x003C;&#x2009;0.05, <sup>&#x002A;&#x002A;</sup><italic>p</italic>&#x2009;&#x003C;&#x2009;0.01, <sup>&#x002A;&#x002A;&#x002A;</sup><italic>p</italic>&#x2009;&#x003C;&#x2009;0.001. All effects are standardised. Significance levels are calculated with DWLS method.</p>
</table-wrap-foot>
</table-wrap>
</sec>
<sec id="sec20">
<label>4.6.</label>
<title>Testing hypotheses H<sub>A</sub> and H<sub>B</sub></title>
<p><xref rid="tab8" ref-type="table">Table 8</xref> shows the estimated parameters of the modified SEM model, such as standard error (S.E.), value of <italic>p</italic>, and standardised estimates. Regarding hypothesis H<sub>A</sub>, the standardised path loadings (<italic>y</italic><sub>0</sub> =&#x2009;&#x2212;0.094) suggest that noise-<italic>Sensitivity</italic> negatively influences on sound-<italic>Pleasantness</italic> at the 95% confidence level. This result is consistent with those described by <xref ref-type="bibr" rid="ref52">Tarlao et al. (2021)</xref>. However, in this study, four indicators were used to measure noise-<italic>Sensitivity</italic>. The path underlying hypothesis H<sub>B</sub> is accepted at the 95% confidence level, that is, there is a positive influence of sound-<italic>Pleasantness</italic> on visual-<italic>Liveability</italic> conditions (<italic>z</italic><sub>0</sub> =&#x2009;0.762). To estimate the statistical effects of the structural equation model, we used reliable significance levels for the statistical effects, as shown below in <xref rid="tab8" ref-type="table">Table 8</xref>.</p>
<p>Sound-<italic>Pleasantness</italic> (<italic>&#x03B7;<sub>2</sub></italic>) was negatively correlated with the acoustic measurements of the A-weighted SPL (<italic>y</italic><sub>10</sub>&#x2009;=&#x2009;&#x2212;0.25, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001), the equivalent C-weighted SPL (<italic>y</italic><sub>11</sub>&#x2009;=&#x2009;&#x2212;0.121, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001) and the differences between percentiles L<sub>10</sub>&#x2013;L<sub>90</sub> (<italic>y</italic><sub>12</sub>&#x2009;=&#x2009;&#x2212;0.072, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001). On the other hand, visual-<italic>Liveability</italic> (<italic>&#x03B7;<sub>3</sub></italic>) was associated with decreased pedestrian flow (<italic>z</italic><sub>8</sub>&#x2009;=&#x2009;&#x2212;0.086, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001). The visual components, such as vehicle flow (<italic>z</italic><sub>9</sub>&#x2009;=&#x2009;0.043, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.05) and green spaces (<italic>z</italic><sub>15</sub>&#x2009;=&#x2009;0.031, <italic>p</italic>&#x2009;=&#x2009;0.067), influenced positively visual-<italic>Liveability</italic> conditions. In contrast, the model revealed that being close to commercial zones (<italic>z</italic><sub>11</sub>&#x2009;=&#x2009;&#x2212;0.177, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001) negatively affects people&#x2019;s visual-<italic>Liveability</italic>.</p>
</sec>
<sec id="sec21">
<label>4.7.</label>
<title>Testing hypotheses H<sub>C1</sub> and H<sub>C2</sub> using a mediation analysis</title>
<p>Hypothesis H<sub>C1</sub> was analysed considering the estimates of the total effect of the socio-economic variables on all perceptions <italic>n<sub>1</sub></italic>, <italic>n<sub>2</sub></italic> and <italic>n<sub>3</sub></italic>. Hypothesis H<sub>C2</sub> was tested regarding the total effect of the residential location on all factors <italic>n</italic><sub><italic>1</italic>,</sub> <italic>n</italic><sub><italic>2</italic>,</sub> and <italic>n</italic><sub><italic>3</italic>.</sub></p>
<p>Based on the stated hypotheses, we performed a mediation analysis by estimating the total effect between observed variables and the interrelated latent constructs. The total impact of each variable was computed by adding their direct and indirect effects (<italic>z</italic><sub>n</sub>&#x2009;+&#x2009;<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>n</sub>&#x2009;+&#x2009;<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>n</sub>). The indirect effect was obtained by multiplying the estimates of noise-<italic>Sensitivity</italic> (<italic>y</italic><sub>0</sub>) or sound-<italic>Pleasantness</italic> (<italic>z</italic><sub>0</sub>) and the reported direct effect of each categorised variable (<italic>x</italic><sub>n</sub>, <italic>y</italic><sub>n</sub> and <italic>z</italic><sub>n</sub>). <xref rid="tab8" ref-type="table">Table 8</xref> presents the total effects in an aggregated form, given the different directions of significant direct and indirect effects.</p>
<p>The mediation analysis reports a positive and significant correlation and total effect between <italic>socio-economics</italic> and noise-<italic>Sensitivity</italic>. Women tend to be more sensitive to noise than men (<italic>x</italic><sub>1</sub>&#x2009;=&#x2009;0.074, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001). The increase in noise-<italic>Sensitivity</italic> in aged people is represented by the <italic>elderly</italic> variable (<italic>x</italic><sub>3</sub>&#x2009;=&#x2009;0.073, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001). Noise-<italic>Sensitivity</italic> is also proportional to education level. The higher the education level, the higher the noise-<italic>Sensitivity</italic>. Heads of households with a level of education degree categorised as <italic>high-school</italic> (<italic>x</italic><sub>4</sub>&#x2009;=&#x2009;0.303, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001) and <italic>university-degree</italic> (<italic>x</italic><sub>5</sub>&#x2009;=&#x2009;0.368, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001) are more noise-sensitive than low educated participants. Following the same logic, noise-<italic>Sensitivity</italic> increases for those individuals with high-skilled jobs. Particularly, those participants performing <italic>qualified-work</italic> (<italic>x</italic><sub>6</sub>&#x2009;=&#x2009;0.207, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001) and <italic>specialised-work</italic> (<italic>x</italic><sub>7</sub>&#x2009;=&#x2009;0.240, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001) are more noise-sensitive than those in unskilled labours. Additionally, noise-<italic>Sensitivity</italic> increases for households reporting <italic>middle-income</italic> (<italic>x</italic><sub>8</sub>&#x2009;=&#x2009;0.080, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001) and <italic>upper-income</italic> (<italic>x</italic><sub>9</sub>&#x2009;=&#x2009;0.110, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001).</p>
<p>The mediation analysis also reports relationships between <italic>socio-economics</italic> and the sound-<italic>Pleasantness</italic> construct. The total effect was estimated by summing up the direct effect from socio-demographics interacting directly with the construct, and the indirect effect, which was determined by multiplying the (<italic>y</italic><sub>0</sub>) value estimated for noise-<italic>Sensitivity</italic>. The analysis indicates a negative and significant correlation and total effect of <italic>gender</italic> (<italic>y</italic><sub>1</sub>&#x2009;+&#x2009;<italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>1</sub>&#x2009;=&#x2009;&#x2212;0.071, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001), <italic>adult</italic> (<italic>y</italic><sub>2</sub> <italic>=</italic>&#x2009;&#x2212;0.063, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001), <italic>elderly</italic> (<italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>3</sub>&#x2009;=&#x2009;&#x2212;0.007, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001), <italic>high-school-degree</italic> (<italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>4</sub>&#x2009;=&#x2009;&#x2212;0.029, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001), <italic>university-degree</italic> (<italic>y</italic><sub>5</sub>&#x2009;+&#x2009;<italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>5</sub>&#x2009;=&#x2009;&#x2212;0.150, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.01), <italic>qualified-work</italic> (<italic>y</italic><sub>6</sub>&#x2009;+&#x2009;<italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>6</sub>&#x2009;=&#x2009;&#x2212;0.097, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001), <italic>specialised-work</italic> (<italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>7</sub>&#x2009;=&#x2009;&#x2212;0.023, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001), <italic>middle-income</italic> (<italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>8</sub> <italic>=</italic>&#x2009;&#x2212;0.008, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001) and <italic>upper-income</italic> (<italic>y</italic><sub>0</sub><sup>&#x002A;</sup>x<sub>9</sub> <italic>=</italic>&#x2009;&#x2212;0.010, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001). In other words, although women are more noise-sensitive, men find the sounds in residential environments less pleasant. Moreover, sound-<italic>Pleasantness</italic> in residential environments has an inverse relationship with <italic>age</italic>, <italic>education level</italic>, <italic>employment</italic> and <italic>income</italic> (i.e., sound-<italic>Pleasantness</italic> decreases when age increases).</p>
<p>The perception of the visual construct <italic>Liveability</italic> also varies across the population, according to several socio-demographic attributes. The indirect effect (<italic>z</italic><sub>n</sub>&#x2009;+&#x2009;<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>n</sub>&#x2009;+&#x2009;<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>n</sub>) was calculated by multiplying the estimates for the socio-demographics (<italic>x</italic><sub>n</sub>, <italic>y</italic><sub>n</sub>, <italic>z</italic><sub>n</sub>) and the values (<italic>z</italic><sub>0</sub>) and (<italic>y</italic><sub>0</sub>) estimated for sound-<italic>Pleasantness</italic> and noise-<italic>Sensitivity</italic>, respectively. Men rated lower the construct of <italic>Liveability</italic> for the observed surroundings residential scenarios than women (<italic>z<sub>1</sub> +&#x2009;z<sub>0</sub><sup>&#x002A;</sup>y<sub>1</sub> +&#x2009;z<sub>0</sub><sup>&#x002A;</sup>y<sub>0</sub><sup>&#x002A;</sup>x<sub>1</sub> =</italic>&#x2009;&#x2212;0.075, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001). The results indicate that aged participants categorised such as <italic>adult</italic> (<italic>z</italic><sub>2</sub>&#x2009;+&#x2009;<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>2</sub>&#x2009;+&#x2009;<italic>z<sub>0</sub></italic><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>2</sub>&#x2009;=&#x2009;&#x2212;0.07, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001) and <italic>elderly</italic> (<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>3</sub>&#x2009;=&#x2009;&#x2212;0.005, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001) rated visual-<italic>Liveability</italic> conditions of the residential environment lower than younger residents. Additionally, visual-<italic>Liveability</italic> decreases in household heads with a higher educational degree. Particularly, those holding <italic>high-school</italic> (<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>4</sub>&#x2009;=&#x2009;&#x2212;0.022, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001) and <italic>university</italic> (<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>5</sub>&#x2009;+&#x2009;<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>5</sub>&#x2009;=&#x2009;&#x2212;0.114, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001) degrees reported lower <italic>liveable</italic> conditions than less educated participants. Visual-<italic>Liveability</italic> was also lower for those household heads performing <italic>qualified</italic> (<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>6</sub>&#x2009;+&#x2009;<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>6</sub>&#x2009;=&#x2009;&#x2212;0.074, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001) and <italic>specialised</italic> (<italic>z</italic><sub>7</sub>+ <italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>7</sub>&#x2009;=&#x2009;&#x2212;0.087, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.01) work when compared with individuals performing unskilled activities. Finally, visual-<italic>Liveability</italic> perception decreases when income status increases. Specifically, <italic>middle-income</italic> (<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>8</sub>&#x2009;=&#x2009;&#x2212;0.006, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.01) and <italic>upper-income</italic> (<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>9</sub>&#x2009;=&#x2009;&#x2212;0.008, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.001) individuals reported lower <italic>Liveability</italic> conditions than low-income participants.</p>
<p>Therefore, considering the non-zero estimates of the total effects of <italic>socio-economics</italic> on the noise-<italic>Sensitivity</italic>, sound-<italic>Pleasantness</italic> and visual-<italic>Liveability</italic> constructs, we cannot reject the H<sub>C1</sub> hypothesis at the 95% confidence level.</p>
<p>Furthermore, based on the mediation analysis and the relationships between the dwelling location of participants and the three latent constructs, the model suggests a significant heterogeneity effect amongst households placed in Quito&#x2019;s main districts (North, Centre and South). Note that household heads living in <italic>centre-Quito</italic> (<italic>x</italic><sub>14</sub>&#x2009;=&#x2009;0.048, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.01) declared to be more sensitive to noise than those living in the city&#x2019;s south. In addition, participants with a dwelling in <italic>north-Quito</italic> (<italic>y</italic><sub>13</sub>&#x2009;=&#x2009;&#x2212;0.037, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.05) and <italic>centre-Quito</italic> (<italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>14</sub>&#x2009;=&#x2009;&#x2212;0.005, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.05) rated sound-<italic>Pleasantness</italic> lower than those located in <italic>south-Quito</italic>. Consequently, households living in <italic>north-Quito</italic> (<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>13</sub>&#x2009;=&#x2009;&#x2212;0.028, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.05) and <italic>centre-Quito</italic> (<italic>z</italic><sub>0</sub><sup>&#x002A;</sup><italic>y</italic><sub>0</sub><sup>&#x002A;</sup><italic>x</italic><sub>14</sub>&#x2009;=&#x2009;&#x2212;0.003, <italic>p</italic>&#x2009;&#x003C;&#x2009;0.05) also rated lower visual<italic><bold>-</bold>Liveability</italic> than participants in <italic>south-Quito</italic>. This is probably because the city-centre and north areas of Quito have higher noise exposure than the southern part, due to increased commercial activities in those areas. The estimations of the total effects calculated above suggest that the perceptual dimensions vary according to the place of residence of the household heads, which allows accepting hypothesis H<sub>C2</sub> at the 95% confidence level.</p>
</sec>
</sec>
<sec id="sec22" sec-type="discussions">
<label>5.</label>
<title>Discussion</title>
<p>This study provides new insights to identify the influence of household heads&#x2019; socio-demographic and housing location characteristics on their auditory and visual perceptions when selecting a residential environment. Previous knowledge especially that developed in the Latin American region, has provided limited evidence about the relationships between person-related attributes (i.e., noise annoyance), auditory and indirect visual factors in the residential context (<xref ref-type="bibr" rid="ref28">Kogan et al., 2017</xref>; <xref ref-type="bibr" rid="ref45">Rey-Gozalo et al., 2018</xref>). Our study also considers four relationships between auditory and visual perceptions in a residential setting. This is done by looking at the direct and indirect effects between objective attributes and the participants&#x2019; own personal traits.</p>
<p>The results of the SEM model show first, a significant negative relationship between noise sensitivity and sound pleasantness, and, indirectly, with visual liveability. This means that household heads who reported higher noise-<italic>Sensitivity</italic> also rated the sounds reproduced in the selected residential locations as less pleasant, in line with the result described by <xref ref-type="bibr" rid="ref52">Tarlao et al. (2021)</xref>. Also, participants are susceptible to a broader range of positive latent constructs and are not only associated with noise-annoyance as was found in previous studies (<xref ref-type="bibr" rid="ref15">Fyhri and Kl&#x00E6;boe, 2009</xref>; <xref ref-type="bibr" rid="ref49">Ryu and Jeon, 2011</xref>). The examination of the direct influence of the objective sonic measures on sound-<italic>Pleasantness</italic> revealed a significant negative relationship with the values of the acoustic parameters L<sub>Aeq,60s</sub>, L<sub>Ceq,60s</sub>, and the percentile difference between L<sub>A10</sub> and L<sub>A90</sub>. These influences could be compared with those recently described by <xref ref-type="bibr" rid="ref63">Yong et al. (2021)</xref>, except for the A-weighted SPL, and highlight the adequate association of sonic parameters on psychoacoustics descriptors as carriers of information when studying the enhancement of urban places.</p>
<p>Our study also demonstrates a second positive significant relationship between sound-<italic>Pleasantness</italic> and visual-<italic>Liveability</italic> in a Latin American context. Interestingly, in residential conditions, the direct effect of <italic>Pedestrian flow</italic> on visual-<italic>Liveability</italic> revealed a negative influence of this observable variable on the construct, differing from other studies where the presence of people in public spaces had been reported as a positive characteristic (<xref ref-type="bibr" rid="ref23">Iglesias et al., 2013</xref>; <xref ref-type="bibr" rid="ref42">Puyana-Romero et al., 2016</xref>), albeit from a safety point of view in the first case. It is possible that the negative sign was motivated by the restrictions on mobility during the COVID-19 pandemic, as people were warned to avoid crowds. Considering other visual components, we observed a positive relationship between <italic>Vehicle-flow</italic>, <italic>Green spaces</italic> and visual-<italic>Liveability</italic> in the residential context, and these results are in line with those described by <xref ref-type="bibr" rid="ref63">Yong et al. (2021)</xref>. In contrast, note that being close to <italic>commercial</italic> land use negatively influences visual-<italic>Liveability</italic>. In other words, the perception of <italic>Liveability</italic> differs amongst family heads because they are heterogeneous in terms of their socio-demographic and location attributes.</p>
<p>Based on the parameters estimated by the SEM model, which include a mediation analysis to assess direct effects and total effects loadings, our results reveal the relationships between socio-demographic characteristics of households heads and their perceptions of noise-<italic>Sensitivity</italic>, sound-<italic>Pleasantness</italic> and visual-<italic>Livability</italic>. The direct effect showed a negative influence between <italic>socio-demographics</italic> and noise-<italic>Sensitivity</italic>. Consistent with <xref ref-type="bibr" rid="ref57">van Kamp et al. (2004)</xref>, we found that the influence of socio-demographic characteristics on noise-<italic>Sensitivity</italic> varies significantly in the population under study. Family heads reported greater sensitivity if their education, employment and income status were higher. Thus, this study extends several patterns for noise-<italic>Sensitivity</italic> and auditory factors in a Latin American country. The direct effect estimates are influenced by age and gender. For example, respondents over 65 declared high sensitivity and perceived sounds as less pleasant than adults or young individuals. The model also suggests that older people rated sound-<italic>Pleasantness</italic> and visual-<italic>Liveability</italic> lower than younger people due to their noise-<italic>Sensitivity</italic>. Additionally, regarding <italic>gender</italic>, on average men in Quito perceive the residential environment as less pleasant and less liveable than women.</p>
<p>The last relationships concern the analysis of direct and total effects using the mediation analysis. Our results indicate that the household dwelling location and proximity to land uses and activities influence the latent constructs. This finding suggests a significant heterogeneity amongst households located in Quito&#x2019;s main districts. For example, households located in the <italic>centre</italic> and <italic>north</italic> of the city reported a negative impact on both sound-<italic>Pleasantness</italic> and visual-<italic>Liveability</italic> compared to those living in the <italic>south</italic>. These findings suggest that families living in these zones could be affected by the higher sound pressure level exposure in those areas, especially for households located in the <italic>centre</italic> of Quito, which has much higher commercial activity. In this line, <xref ref-type="bibr" rid="ref4">Arellana et al. (2019)</xref> have also argued that perceptions vary according to the residential location of the respondents.</p>
</sec>
<sec id="sec23" sec-type="conclusions">
<label>6.</label>
<title>Conclusion</title>
<p>This research provides evidence about the influence of explanatory variables such as auditory&#x2013;visual components, socio-demographics and residential location characteristics on three latent constructs in a residential location context. Using the SEM model estimates and the mediation analysis, we found a negative correlation between noise-<italic>Sensitivity</italic> and sound-<italic>Pleasantness</italic>, and a positive relationship between sound-<italic>Pleasantness</italic> and visual-<italic>Liveability</italic>. Note that a limitation of this study is that we considered only sound-<italic>Pleasantness</italic> whilst keeping a parsimony criterion of the model structure. Future research should include eventfulness and pleasantness analysis in the Latin American context.</p>
<p>The findings reported in this paper complement the understanding of complex relationships described in the literature on the knowledge gap between the perception of sound-visual components with the added value of being assessed in the residential context of Latin American cities. Therefore, this study calls for a more holistic understanding of the perception of sound and visual attributes of residential environments rather than just independently assessing auditory perceptions, traditionally noise-annoyance, and other visual concepts associated with livability when studying improvements to the residential environment.</p>
<p>The estimations of parameters calculated from path regressions using SEM demonstrated the influences of the mediation analysis. The estimation of the direct effect showed that noise-<italic>Sensitivity</italic> correlates negatively with socio-demographics such as gender, age, education, employment and income status. The estimations calculated of the total effects provided a better understanding of when sound-<italic>Pleasantness</italic> mediates under the specification of the set of acoustic measures, such as the A-weighted SPL, the equivalent C-weighted SPL and percentiles L<sub>10</sub>&#x2013;L<sub>90</sub>. Complementarily, estimates of the total effects calculated from the visual-<italic>Liveability</italic> path specification showed a heterogeneous variation across households according to their residential location in Quito&#x2019;s main districts (North, Centre and South).</p>
<p>Our methodology adds evidence in favour of future research using digital surveys containing 360&#x00B0; video and immersive sound reproduction and the application of perceptual questionnaires to capture perceptions of audio-visual attributes of residential environments. This alternative approach to administrating the experiment stimulated participants&#x2019; senses with a high level of reality and offered portability advantages for conducting the survey. These improvements allowed participants to reproduce the experiment under home conditions and evaluate multiple residential environments. The overall flexibility of the implemented methodology provided adequate conditions for experimental replicability.</p>
<p>Our prior statistical estimations support the idea of complementing the study of audio-visual perceptions using advanced econometric theory. Therefore, the collected information on stated preferences is appropriate as an analytical tool for analysing residential location preferences considering sound and visual factors and attributes. Thus, using advanced hybrid discrete choice models, the willingness-to-pay measures are estimated considering environmental improvements, such as <italic>noise reduction</italic> or <italic>enhanced urban amenities</italic>. Hence, the authors of this study are currently working on this line of research.</p>
</sec>
<sec id="sec24" 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="sec25">
<title>Ethics statement</title>
<p>Ethical review and approval was not required for the study involving human participants in accordance with the local legislation and institutional requirements. Written informed consent to participate in this study was not required from the participants in accordance with the national legislation and the institutional requirements.</p>
</sec>
<sec id="sec26">
<title>Author contributions</title>
<p>All authors listed have made a substantial, direct, and intellectual contribution to the work and approved it for publication.</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="sec100" 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>
<ack>
<p>This research was accomplished thanks to collaboration of the Universidad T&#x00E9;cnica del Norte and the co-funding project SOA.MCA.19.05- provided the Universidad de Las Am&#x00E9;ricas in Ecuador and the Civil Engineering programme at Universidad del Norte in Barranquilla, Colombia. JDO is grateful for the support of Instituto Sistemas Complejos de Ingenier&#x00ED;a (ISCI) through grant CONICYT PIA/BASAL AFB180003, and of the BRT+ Centre of Excellence.</p>
</ack>
<ref-list>
<title>References</title>
<ref id="ref1"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Ahmed</surname> <given-names>N.</given-names></name> <name><surname>El-Halafawy</surname> <given-names>A.</given-names></name></person-group> (<year>2019</year>). <article-title>A critical review of urban livability</article-title>. <source>Eur. J. Sustain. Dev.</source> <volume>8</volume>, <fpage>165</fpage>&#x2013;<lpage>182</lpage>. doi: <pub-id pub-id-type="doi">10.74207/ejsd.2079.v8n7p765</pub-id></citation></ref>
<ref id="ref2"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Aletta</surname> <given-names>F.</given-names></name> <name><surname>Kang</surname> <given-names>J.</given-names></name> <name><surname>Axelsson</surname> <given-names>&#x00D6;.</given-names></name></person-group> (<year>2016</year>). <article-title>Soundscape descriptors and a conceptual framework for developing predictive soundscape models</article-title>. <source>Landsc. Urban Plan.</source> <volume>149</volume>, <fpage>65</fpage>&#x2013;<lpage>74</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.landurbplan.2016.02.001</pub-id></citation></ref>
<ref id="ref3"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Amir</surname> <given-names>S.</given-names></name> <name><surname>Sadoway</surname> <given-names>D.</given-names></name> <name><surname>Dommaraju</surname> <given-names>P.</given-names></name></person-group> (<year>2021</year>). <article-title>Taming the noise: Soundscape and livability in a taming the noise. East Asian Sci</article-title>. <source>Technol. Soc. Annu. Int. J.</source> <volume>0</volume>, <fpage>1</fpage>&#x2013;<lpage>17</lpage>. doi: <pub-id pub-id-type="doi">10.1080/18752160.2021.1936749</pub-id></citation></ref>
<ref id="ref4"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Arellana</surname> <given-names>J.</given-names></name> <name><surname>Fuentes</surname> <given-names>L.</given-names></name> <name><surname>Cantillo</surname> <given-names>V.</given-names></name></person-group> (<year>2019</year>). <article-title>Multivariate analysis of user perceptions about the serviceability of urban roads: case of Barranquilla</article-title>. <source>Int. J. Pavement Eng.</source> <volume>22</volume>, <fpage>54</fpage>&#x2013;<lpage>63</lpage>. doi: <pub-id pub-id-type="doi">10.1080/10298436.2019.1577420</pub-id></citation></ref>
<ref id="ref5"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Arellana</surname> <given-names>J.</given-names></name> <name><surname>Garz&#x00F3;n</surname> <given-names>L.</given-names></name> <name><surname>Estrada</surname> <given-names>J.</given-names></name> <name><surname>Cantillo</surname> <given-names>V.</given-names></name></person-group> (<year>2020</year>). <article-title>On the use of virtual immersive reality for discrete choice experiments to modelling pedestrian behaviour</article-title>. <source>J. Choice Model.</source> <volume>37</volume>, <fpage>100251</fpage>&#x2013;<lpage>100218</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.jocm.2020.100251</pub-id></citation></ref>
<ref id="ref6"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Aulia</surname> <given-names>D. N.</given-names></name></person-group> (<year>2016</year>). <article-title>A framework for exploring livable community in residential environment. Case study: public housing in Medan</article-title>. <source>Indones. Proc. Soc. Behav. Sci.</source> <volume>234</volume>, <fpage>336</fpage>&#x2013;<lpage>343</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.sbspro.2016.10.250</pub-id></citation></ref>
<ref id="ref600"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Aumond</surname> <given-names>P.</given-names></name> <name><surname>Can</surname> <given-names>A.</given-names></name> <name><surname>De Coensel</surname> <given-names>B.</given-names></name> <name><surname>Botteldooren</surname> <given-names>D.</given-names></name> <name><surname>Ribeiro</surname> <given-names>C.</given-names></name> <name><surname>Lavandier</surname> <given-names>C.</given-names></name></person-group> (<year>2017</year>). <article-title>Modeling soundscape pleasantness using perceptual assessments and acoustic measurements along paths in urban context</article-title>. <source>Acta Acustica United with Acust.</source> <volume>103</volume>, <fpage>430</fpage>&#x2013;<lpage>443</lpage>. doi: <pub-id pub-id-type="doi">10.3813/AAA.919073</pub-id></citation></ref>
<ref id="ref7"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Axelsson</surname> <given-names>&#x00D6;.</given-names></name> <name><surname>Nilsson</surname> <given-names>M. E.</given-names></name> <name><surname>Berglund</surname> <given-names>B.</given-names></name></person-group> (<year>2010</year>). <article-title>A principal components model of soundscape perception</article-title>. <source>J. Acoust. Soc. Am.</source> <volume>128</volume>, <fpage>2836</fpage>&#x2013;<lpage>2846</lpage>. doi: <pub-id pub-id-type="doi">10.1121/1.3493436</pub-id>, PMID: <pub-id pub-id-type="pmid">21110579</pub-id></citation></ref>
<ref id="ref8"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Bonaiuto</surname> <given-names>M.</given-names></name> <name><surname>Aiello</surname> <given-names>A.</given-names></name> <name><surname>Perugini</surname> <given-names>M.</given-names></name> <name><surname>Bonnes</surname> <given-names>M.</given-names></name> <name><surname>Ercolani</surname> <given-names>A. P.</given-names></name></person-group> (<year>1999</year>). <article-title>Multidimensional perception of residential environment quality and neighborhood attachment in the urban environment</article-title>. <source>J. Environ. Psychol.</source> <volume>19</volume>, <fpage>331</fpage>&#x2013;<lpage>352</lpage>. doi: <pub-id pub-id-type="doi">10.1006/jevp.1999.0138</pub-id></citation></ref>
<ref id="ref9"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Bravo-Moncayo</surname> <given-names>L.</given-names></name> <name><surname>Ch&#x00E1;vez</surname> <given-names>M.</given-names></name> <name><surname>Puyana-Romero</surname> <given-names>V.</given-names></name> <name><surname>Lucio-Naranjo</surname> <given-names>J.</given-names></name> <name><surname>Garz&#x00F3;n</surname> <given-names>C.</given-names></name> <name><surname>Pav&#x00F3;n-Garc&#x00ED;a</surname> <given-names>I.</given-names></name></person-group> (<year>2019</year>). <article-title>A cost-effective approach to the evaluation of traffic noise exposure in the city of Quito</article-title>. <source>Ecuador. Case Stud. Transp. Policy</source> <volume>7</volume>, <fpage>128</fpage>&#x2013;<lpage>137</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.cstp.2018.12.006</pub-id></citation></ref>
<ref id="ref10"><citation citation-type="book"><person-group person-group-type="author"><name><surname>Campbell</surname> <given-names>A.</given-names></name> <name><surname>Converse</surname> <given-names>P. E.</given-names></name> <name><surname>Rodgers</surname> <given-names>W. L.</given-names></name></person-group> (<year>1976</year>). <source>The Quality of American Life</source>. <publisher-loc>New York,NY</publisher-loc>: <publisher-name>Russell Sage Foundation Press</publisher-name>.</citation></ref>
<ref id="ref11"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Cerny</surname> <given-names>B. A.</given-names></name> <name><surname>Kaiser</surname> <given-names>H. F.</given-names></name></person-group> (<year>1977</year>). <article-title>A study of a measure of sampling adequacy for factor-analytic correlation matrices</article-title>. <source>Multivar. Behav. Res.</source> <volume>12</volume>, <fpage>43</fpage>&#x2013;<lpage>47</lpage>. doi: <pub-id pub-id-type="doi">10.1207/s15327906mbr1201_3</pub-id>, PMID: <pub-id pub-id-type="pmid">26804143</pub-id></citation></ref>
<ref id="ref12"><citation citation-type="other"><person-group person-group-type="author"><name><surname>CoreTeam</surname> <given-names>R.</given-names></name></person-group> (<year>2018</year>). R: A language and environment for statistical computing. R Found. Stat. Comput. Available online at: <ext-link xlink:href="https://www.r-project.org/" ext-link-type="uri">https://www.r-project.org/</ext-link> (Accessed: August 3, 2021)</citation></ref>
<ref id="ref13"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Distefano</surname> <given-names>C.</given-names></name> <name><surname>Morgan</surname> <given-names>G. B.</given-names></name></person-group> (<year>2014</year>). <article-title>Structural equation modeling: a multidisciplinary a comparison of diagonal weighted least squares robust estimation techniques for ordinal data</article-title>. <source>Struct. Equa. Model. Multidiscip. J.</source> <volume>21</volume>, <fpage>425</fpage>&#x2013;<lpage>438</lpage>. doi: <pub-id pub-id-type="doi">10.1080/10705511.2014.915373</pub-id></citation></ref>
<ref id="ref14"><citation citation-type="other"><person-group person-group-type="author"><collab id="coll1">EEA</collab></person-group> (<year>2020</year>). Environmental noise in Europe &#x2212;2020. Technical report no. 22/2019. European Environmental Agency. Available at: <ext-link xlink:href="https://www.eea.europa.eu/publications/environmental-noise-in-europe" ext-link-type="uri">https://www.eea.europa.eu/publications/environmental-noise-in-europe</ext-link></citation></ref>
<ref id="ref15"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Fyhri</surname> <given-names>A.</given-names></name> <name><surname>Kl&#x00E6;boe</surname> <given-names>R.</given-names></name></person-group> (<year>2009</year>). <article-title>Road traffic noise, sensitivity, annoyance and self-reported health: a structural equation model exercise</article-title>. <source>Environ. Int.</source> <volume>35</volume>, <fpage>91</fpage>&#x2013;<lpage>97</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.envint.2008.08.006</pub-id>, PMID: <pub-id pub-id-type="pmid">18823662</pub-id></citation></ref>
<ref id="ref16"><citation citation-type="book"><person-group person-group-type="author"><name><surname>Hair</surname> <given-names>J. F.</given-names></name> <name><surname>Black</surname> <given-names>W. C.</given-names></name> <name><surname>Babin</surname> <given-names>B. J.</given-names></name> <name><surname>Anderson</surname> <given-names>E. A.</given-names></name></person-group> (<year>2018</year>). <source>Multivariate Data Analysis</source>. <edition>8th ed</edition>. <publisher-loc>Andover</publisher-loc>: <publisher-name>Cengage</publisher-name>.</citation></ref>
<ref id="ref17"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Hasegawa</surname> <given-names>Y.</given-names></name> <name><surname>Lau</surname> <given-names>S. K.</given-names></name></person-group> (<year>2022</year>). <article-title>Comprehensive audio-visual environmental effects on residential soundscapes and satisfaction: partial least square structural equation modeling approach</article-title>. <source>Landsc. Urban Plan.</source> <volume>220</volume>:<fpage>104351</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.landurbplan.2021.104351</pub-id></citation></ref>
<ref id="ref18"><citation citation-type="other"><person-group person-group-type="author"><name><surname>Heggie</surname> <given-names>C.</given-names></name> <name><surname>Smyrnova</surname> <given-names>J.</given-names></name> <name><surname>Smith</surname> <given-names>B.</given-names></name> <name><surname>Allen</surname> <given-names>M.</given-names></name> <name><surname>Klein</surname> <given-names>A.</given-names></name></person-group> (<year>2019</year>). "The practicalities of soundscape data collection by systematic approach according to ISO 12913-2" in <italic>48th International Congress and Conference Proceeding of Exhibition Noise Control Engineering</italic>. Institute of Noise Control Engineering, Madrid, 2995&#x2013;3992.</citation></ref>
<ref id="ref19"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Hong</surname> <given-names>J. Y.</given-names></name> <name><surname>He</surname> <given-names>J.</given-names></name> <name><surname>Lam</surname> <given-names>B.</given-names></name> <name><surname>Gupta</surname> <given-names>R.</given-names></name> <name><surname>Gan</surname> <given-names>W. S.</given-names></name></person-group> (<year>2017</year>). <article-title>Spatial audio for soundscape design: recording and reproduction</article-title>. <source>Appl. Sci.</source> <volume>7</volume>:<fpage>627</fpage>. doi: <pub-id pub-id-type="doi">10.3390/app7060627</pub-id></citation></ref>
<ref id="ref20"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Hong</surname> <given-names>J. Y.</given-names></name> <name><surname>Jeon</surname> <given-names>J. Y.</given-names></name></person-group> (<year>2015</year>). <article-title>Influence of urban contexts on soundscape perceptions: a structural equation modeling approach</article-title>. <source>Landsc. Urban Plan.</source> <volume>141</volume>, <fpage>78</fpage>&#x2013;<lpage>87</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.landurbplan.2015.05.004</pub-id></citation></ref>
<ref id="ref22"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Hong</surname> <given-names>J. Y.</given-names></name> <name><surname>Lam</surname> <given-names>B.</given-names></name> <name><surname>Ong</surname> <given-names>Z.</given-names></name> <name><surname>Ooi</surname> <given-names>K.</given-names></name> <name><surname>Gan</surname> <given-names>W.</given-names></name> <name><surname>Kang</surname> <given-names>J.</given-names></name> <etal/></person-group>. (<year>2020</year>). <article-title>Effects of contexts in urban residential areas on the pleasantness and appropriateness of natural sounds</article-title>. <source>Sustain. Cities Soc.</source> <volume>63</volume>:<fpage>102475</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.scs.2020.102475</pub-id></citation></ref>
<ref id="ref23"><citation citation-type="book"><person-group person-group-type="author"><name><surname>Iglesias</surname> <given-names>P.</given-names></name> <name><surname>Greene</surname> <given-names>M.</given-names></name> <name><surname>Ort&#x00FA;zar</surname> <given-names>J. D. D.</given-names></name></person-group> (<year>2013</year>). &#x201C;<article-title>On the perception of safety in low income neighbourhoods: using digital images in a stated choice experiment</article-title>&#x201D; in <source>Choice Modelling: The State of the Art and the State of Practice</source>. eds. <person-group person-group-type="editor"><name><surname>Hess</surname> <given-names>S.</given-names></name> <name><surname>Daly</surname> <given-names>A. J.</given-names></name></person-group> (<publisher-loc>Cheltenham</publisher-loc>: <publisher-name>Edward Elgar Publishing Ltd.</publisher-name>), <fpage>193</fpage>&#x2013;<lpage>210</lpage>.</citation></ref>
<ref id="ref24"><citation citation-type="other"><person-group person-group-type="author"><collab id="coll2">ISO</collab></person-group> (<year>2014</year>). 12913&#x2013;1: Data collection&#x2013;part 1: Definition and Conceptual Framework. International Standard Organization.</citation></ref>
<ref id="ref25"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Jo</surname> <given-names>H. I.</given-names></name> <name><surname>Jeon</surname> <given-names>J. Y.</given-names></name></person-group> (<year>2020</year>). <article-title>Effect of the appropriateness of sound environment on urban soundscape assessment</article-title>. <source>Build. Environ.</source> <volume>179</volume>:<fpage>106975</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.buildenv.2020.106975</pub-id></citation></ref>
<ref id="ref26"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Kishikawa</surname> <given-names>H.</given-names></name> <name><surname>Matsui</surname> <given-names>T.</given-names></name> <name><surname>Uchiyama</surname> <given-names>I.</given-names></name> <name><surname>Miyakawa</surname> <given-names>M.</given-names></name> <name><surname>Hiramatsu</surname> <given-names>K.</given-names></name> <name><surname>Stansfeld</surname> <given-names>S. A.</given-names></name></person-group> (<year>2006</year>). <article-title>The development of Weinstein's noise sensitivity scale</article-title>. <source>Noise Health</source> <volume>8</volume>, <fpage>154</fpage>&#x2013;<lpage>160</lpage>. doi: <pub-id pub-id-type="doi">10.4103/1463-1741.34703</pub-id>, PMID: <pub-id pub-id-type="pmid">17851220</pub-id></citation></ref>
<ref id="ref27"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Kogan</surname> <given-names>P.</given-names></name> <name><surname>Arenas</surname> <given-names>J. P.</given-names></name> <name><surname>Bermejo</surname> <given-names>F.</given-names></name> <name><surname>Hinalaf</surname> <given-names>M.</given-names></name> <name><surname>Turra</surname> <given-names>B.</given-names></name></person-group> (<year>2018</year>). <article-title>A green soundscape index (GSI): the potential of assessing the perceived balance between natural sound and traffic noise</article-title>. <source>Sci. Total Environ.</source> <volume>642</volume>, <fpage>463</fpage>&#x2013;<lpage>472</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.scitotenv.2018.06.023</pub-id>, PMID: <pub-id pub-id-type="pmid">29908505</pub-id></citation></ref>
<ref id="ref28"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Kogan</surname> <given-names>P.</given-names></name> <name><surname>Turra</surname> <given-names>B.</given-names></name> <name><surname>Arenas</surname> <given-names>J. P.</given-names></name> <name><surname>Hinalaf</surname> <given-names>M.</given-names></name></person-group> (<year>2017</year>). <article-title>A comprehensive methodology for the multidimensional and synchronic data collecting in soundscape</article-title>. <source>Sci. Total Environ.</source> <volume>580</volume>, <fpage>1068</fpage>&#x2013;<lpage>1077</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.scitotenv.2016.12.061</pub-id>, PMID: <pub-id pub-id-type="pmid">28007416</pub-id></citation></ref>
<ref id="ref29"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Kovacs-Gy&#x00F6;ri</surname> <given-names>A.</given-names></name> <name><surname>Cabrera-Barona</surname> <given-names>P.</given-names></name> <name><surname>Resch</surname> <given-names>B.</given-names></name> <name><surname>Mehaffy</surname> <given-names>M.</given-names></name> <name><surname>Blaschke</surname> <given-names>T.</given-names></name></person-group> (<year>2019</year>). <article-title>Assessing and representing livability through the analysis of residential preference</article-title>. <source>Sustain. For.</source> <volume>11</volume>, <fpage>1</fpage>&#x2013;<lpage>23</lpage>. doi: <pub-id pub-id-type="doi">10.3390/su11184934</pub-id></citation></ref>
<ref id="ref30"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Liebe</surname> <given-names>U.</given-names></name> <name><surname>Glenk</surname> <given-names>K.</given-names></name> <name><surname>Oehlmann</surname> <given-names>M.</given-names></name> <name><surname>Meyerhoff</surname> <given-names>J.</given-names></name></person-group> (<year>2015</year>). <article-title>Does the use of mobile devices (tablets and smartphones) affect survey quality and choice behaviour in web surveys?</article-title> <source>J. Choice Model.</source> <volume>14</volume>, <fpage>17</fpage>&#x2013;<lpage>31</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.jocm.2015.02.002</pub-id></citation></ref>
<ref id="ref31"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Lionello</surname> <given-names>M.</given-names></name> <name><surname>Aletta</surname> <given-names>F.</given-names></name> <name><surname>Kang</surname> <given-names>J.</given-names></name></person-group> (<year>2020</year>). <article-title>A systematic review of prediction models for the experience of urban soundscapes</article-title>. <source>Appl. Acoust.</source> <volume>170</volume>:<fpage>107479</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.apacoust.2020.107479</pub-id></citation></ref>
<ref id="ref32"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Liu</surname> <given-names>J.</given-names></name> <name><surname>Yang</surname> <given-names>L.</given-names></name> <name><surname>Xiong</surname> <given-names>Y.</given-names></name> <name><surname>Yang</surname> <given-names>Y.</given-names></name></person-group> (<year>2019</year>). <article-title>Effects of soundscape perception on visiting experience in a renovated historical block</article-title>. <source>Build. Environ.</source> <volume>165</volume>:<fpage>106375</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.buildenv.2019.106375</pub-id></citation></ref>
<ref id="ref33"><citation citation-type="book"><person-group person-group-type="author"><name><surname>Long</surname> <given-names>J. S.</given-names></name></person-group> (<year>1983</year>). &#x201C;<article-title>Confirmatory factor analysis</article-title>&#x201D; in <source>Quantitative Applications in the Social Sciences</source>. ed. <person-group person-group-type="editor"><name><surname>Long</surname> <given-names>J. S.</given-names></name></person-group> (<publisher-loc>Beverly Hills</publisher-loc>: <publisher-name>Sage Publications</publisher-name>), <fpage>1</fpage>&#x2013;<lpage>96</lpage>.</citation></ref>
<ref id="ref34"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Marans</surname> <given-names>R. W.</given-names></name></person-group> (<year>2012</year>). <article-title>Quality of urban life studies: an overview and implications for environment-behaviour research</article-title>. <source>Proc. Soc. Behav. Sci.</source> <volume>35</volume>, <fpage>9</fpage>&#x2013;<lpage>22</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.sbspro.2012.02.058</pub-id></citation></ref>
<ref id="ref35"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Miedema</surname> <given-names>H. M.</given-names></name> <name><surname>Vos</surname> <given-names>H.</given-names></name></person-group> (<year>2003</year>). <article-title>Noise sensitivity and reactions to noise and other environmental conditions</article-title>. <source>J. Acoust. Soc. Am.</source> <volume>113</volume>, <fpage>1492</fpage>&#x2013;<lpage>1504</lpage>. doi: <pub-id pub-id-type="doi">10.1121/1.1547437</pub-id>, PMID: <pub-id pub-id-type="pmid">12656384</pub-id></citation></ref>
<ref id="ref36"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Mouratidis</surname> <given-names>K.</given-names></name></person-group> (<year>2020</year>). <article-title>Commute satisfaction, neighborhood satisfaction, and housing satisfaction as predictors of subjective well-being and indicators of urban livability</article-title>. <source>Travel Behav. Soc.</source> <volume>21</volume>, <fpage>265</fpage>&#x2013;<lpage>278</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.tbs.2020.07.006</pub-id></citation></ref>
<ref id="ref37"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Mouratidis</surname> <given-names>K.</given-names></name> <name><surname>Yiannakou</surname> <given-names>A.</given-names></name></person-group> (<year>2022</year>). <article-title>What makes cities livable? Determinants of neighborhood satisfaction and neighborhood happiness in different contexts</article-title>. <source>Land Use Policy</source> <volume>112</volume>:<fpage>105855</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.landusepol.2021.105855</pub-id>, PMID: <pub-id pub-id-type="pmid">36540631</pub-id></citation></ref>
<ref id="ref38"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Nijland</surname> <given-names>H. A.</given-names></name> <name><surname>Hartemink</surname> <given-names>S.</given-names></name> <name><surname>Van Kamp</surname> <given-names>I.</given-names></name> <name><surname>van Wee</surname> <given-names>B.</given-names></name></person-group> (<year>2007</year>). <article-title>The influence of sensitivity for road traffic noise on residential location: does it trigger a process of spatial selection?</article-title> <source>J. Acoust. Soc. Am.</source> <volume>122</volume>, <fpage>1595</fpage>&#x2013;<lpage>1601</lpage>. doi: <pub-id pub-id-type="doi">10.1121/1.2756970</pub-id>, PMID: <pub-id pub-id-type="pmid">17927418</pub-id></citation></ref>
<ref id="ref39"><citation citation-type="book"><person-group person-group-type="author"><name><surname>Nunnally</surname> <given-names>J. C.</given-names></name> <name><surname>Bernstein</surname> <given-names>I. H.</given-names></name></person-group> (<year>1968</year>). <source>Psychometric Theory</source>. <edition>3rd ed.</edition> <publisher-loc>New York,NY</publisher-loc>: <publisher-name>McGraw-Hill Press</publisher-name>.</citation></ref>
<ref id="ref40"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Okulicz-Kozaryn</surname> <given-names>A.</given-names></name> <name><surname>Valente</surname> <given-names>R. R.</given-names></name></person-group> (<year>2019</year>). <article-title>Livability and subjective well-being across european cities</article-title>. <source>Appl. Res. Qual. Life</source> <volume>14</volume>, <fpage>197</fpage>&#x2013;<lpage>220</lpage>. doi: <pub-id pub-id-type="doi">10.1007/s11482-017-9587-7</pub-id></citation></ref>
<ref id="ref41"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Ortega</surname> <given-names>J.</given-names></name> <name><surname>Toth</surname> <given-names>J.</given-names></name> <name><surname>Peter</surname> <given-names>T.</given-names></name></person-group> (<year>2020</year>). <article-title>Mapping the catchment area of park and ride facilities within urban environments</article-title>. <source>Int. J. Geo-Inf.</source> <volume>9</volume>:<fpage>501</fpage>. doi: <pub-id pub-id-type="doi">10.3390/ijgi9090501</pub-id></citation></ref>
<ref id="ref42"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Puyana-Romero</surname> <given-names>V.</given-names></name> <name><surname>Maffei</surname> <given-names>L.</given-names></name> <name><surname>Brambilla</surname> <given-names>G.</given-names></name> <name><surname>Ciaburro</surname> <given-names>G.</given-names></name></person-group> (<year>2016</year>). <article-title>Modelling the soundscape quality of urban waterfronts by artificial neural networks</article-title>. <source>Appl. Acoust.</source> <volume>111</volume>, <fpage>121</fpage>&#x2013;<lpage>128</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.apacoust.2016.04.019</pub-id></citation></ref>
<ref id="ref43"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Ram&#x00ED;rez</surname> <given-names>T.</given-names></name> <name><surname>Hurtubia</surname> <given-names>R.</given-names></name> <name><surname>Lobel</surname> <given-names>H.</given-names></name> <name><surname>Rossetti</surname> <given-names>T.</given-names></name></person-group> (<year>2021</year>). <article-title>Measuring heterogeneous perception of urban space with massive data and machine learning: an application to safety</article-title>. <source>Landsc. Urban Plan.</source> <volume>208</volume>:<fpage>104002</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.landurbplan.2020.104002</pub-id></citation></ref>
<ref id="ref44"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Rey-Gozalo</surname> <given-names>G.</given-names></name> <name><surname>Barrig&#x00F3;n-Morillas</surname> <given-names>J. M.</given-names></name></person-group> (<year>2017</year>). <article-title>Perceptions and effects of the acoustic environment in quiet residential areas</article-title>. <source>J. Acoust. Soc. Am.</source> <volume>141</volume>, <fpage>2418</fpage>&#x2013;<lpage>2429</lpage>. doi: <pub-id pub-id-type="doi">10.1121/1.4979335</pub-id>, PMID: <pub-id pub-id-type="pmid">28464684</pub-id></citation></ref>
<ref id="ref45"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Rey-Gozalo</surname> <given-names>G.</given-names></name> <name><surname>Barrig&#x00F3;n-Morillas</surname> <given-names>J. M.</given-names></name> <name><surname>Montes-Gonzales</surname> <given-names>D.</given-names></name> <name><surname>Atanasio-Moraga</surname> <given-names>P.</given-names></name></person-group> (<year>2018</year>). <article-title>Relationships among satisfaction, noise perception, and use of urban green spaces</article-title>. <source>Sci. Total Environ.</source> <volume>624</volume>, <fpage>438</fpage>&#x2013;<lpage>450</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.scitotenv.2017.12.148</pub-id>, PMID: <pub-id pub-id-type="pmid">29268216</pub-id></citation></ref>
<ref id="ref46"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Rose</surname> <given-names>J. M.</given-names></name> <name><surname>Bliemer</surname> <given-names>M. C. J.</given-names></name> <name><surname>Hensher</surname> <given-names>D. A.</given-names></name> <name><surname>Collins</surname> <given-names>A. T.</given-names></name></person-group> (<year>2008</year>). <article-title>Designing efficient stated choice experiments in the presence of reference alternatives</article-title>. <source>Transp. Res. Part B. Method</source> <volume>42</volume>, <fpage>395</fpage>&#x2013;<lpage>406</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.trb.2007.09.002</pub-id></citation></ref>
<ref id="ref47"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Rosseel</surname> <given-names>Y.</given-names></name></person-group> (<year>2012</year>). <article-title>lavaan: AnRPackage for Structural Equation Modeling</article-title>. <source>J. Stat. Softw.</source> <volume>48</volume>, <fpage>1</fpage>&#x2013;<lpage>36</lpage>. doi: <pub-id pub-id-type="doi">10.18637/jss.v048.i02</pub-id></citation></ref>
<ref id="ref48"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Rossetti</surname> <given-names>T.</given-names></name> <name><surname>Lobel</surname> <given-names>H.</given-names></name> <name><surname>Rocco</surname> <given-names>V.</given-names></name> <name><surname>Hurtubia</surname> <given-names>R.</given-names></name></person-group> (<year>2019</year>). <article-title>Explaining subjective perceptions of public spaces as a function of the built environment: a massive data approach</article-title>. <source>Landsc. Urban Plan.</source> <volume>181</volume>, <fpage>169</fpage>&#x2013;<lpage>178</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.landurbplan.2018.09.020</pub-id></citation></ref>
<ref id="ref49"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Ryu</surname> <given-names>J. K.</given-names></name> <name><surname>Jeon</surname> <given-names>J. Y.</given-names></name></person-group> (<year>2011</year>). <article-title>Influence of noise sensitivity on annoyance of indoor and outdoor noises in residential buildings</article-title>. <source>Appl. Acoust.</source> <volume>72</volume>, <fpage>336</fpage>&#x2013;<lpage>340</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.apacoust.2010.12.005</pub-id></citation></ref>
<ref id="ref50"><citation citation-type="other"><person-group person-group-type="author"><name><surname>Sun</surname> <given-names>K.</given-names></name> <name><surname>Botteldooren</surname> <given-names>D.</given-names></name> <name><surname>De Coensel</surname> <given-names>B.</given-names></name></person-group> (<year>2018b</year>). &#x201C;Realism and immersion in the reproduction of audio-visual recordings for urban soundscape evaluation.&#x201D; in <italic>Inter-Noise and Noise-Con Congress and Conference Proceeding Internoise 2016</italic>. (Institute of Noise Control Engineering) (Chicago) 2984&#x2013;3995.</citation></ref>
<ref id="ref51"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Sun</surname> <given-names>K.</given-names></name> <name><surname>Sanchez-Echevarria</surname> <given-names>G. M.</given-names></name> <name><surname>De Coensel</surname> <given-names>B.</given-names></name> <name><surname>Van Renterghem</surname> <given-names>T.</given-names></name> <name><surname>Talsma</surname> <given-names>D.</given-names></name> <name><surname>Botteldooren</surname> <given-names>D.</given-names></name></person-group> (<year>2018a</year>). <article-title>Personal audio-visual aptitude influences the interaction between landscape and soundscape appraisal</article-title>. <source>Front. Psychol.</source> <volume>9</volume>, <fpage>1</fpage>&#x2013;<lpage>15</lpage>. doi: <pub-id pub-id-type="doi">10.3389/fpsyg.2018.00780</pub-id>, PMID: <pub-id pub-id-type="pmid">29910750</pub-id></citation></ref>
<ref id="ref52"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Tarlao</surname> <given-names>C.</given-names></name> <name><surname>Steffens</surname> <given-names>J.</given-names></name> <name><surname>Guastavino</surname> <given-names>C.</given-names></name></person-group> (<year>2021</year>). <article-title>Investigating contextual influences on urban soundscape evaluations with structural equation modeling</article-title>. <source>Build. Environ.</source> <volume>188</volume>:<fpage>107490</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.buildenv.2020.107490</pub-id></citation></ref>
<ref id="ref53"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Tillema</surname> <given-names>T.</given-names></name> <name><surname>Hamersma</surname> <given-names>M.</given-names></name> <name><surname>Sussman</surname> <given-names>J. M.</given-names></name> <name><surname>Arts</surname> <given-names>J.</given-names></name></person-group> (<year>2012</year>). <article-title>Extending the scope of highway planning: accessibility, negative externalities and the residential context</article-title>. <source>Transp. Rev.</source> <volume>32</volume>, <fpage>745</fpage>&#x2013;<lpage>759</lpage>. doi: <pub-id pub-id-type="doi">10.1080/01441647.2012.724726</pub-id></citation></ref>
<ref id="ref54"><citation citation-type="other"><person-group person-group-type="author"><collab id="coll3">Transportation Research Board</collab></person-group> (<year>2010</year>). <source>Highway Capacity Manual</source>. <edition>5th</edition> edn. Transportation Research Board, The National Academies of Science, Engineering and Medicine, Washington. D.C.</citation></ref>
<ref id="ref55"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>T&#x00FC;rko&#x011F;lu</surname> <given-names>H.</given-names></name> <name><surname>Fatih</surname> <given-names>T.</given-names></name> <name><surname>Tayfun</surname> <given-names>S.</given-names></name> <name><surname>Fulin</surname> <given-names>B.</given-names></name> <name><surname>G&#x00F6;k&#x00E7;er</surname> <given-names>O.</given-names></name></person-group> (<year>2019</year>). <article-title>Residential satisfaction in formal and informal neighborhoods: the case of Istanbul, Turkey</article-title>. <source>Archnet Int. J. Archit. Res.</source> <volume>13</volume>, <fpage>112</fpage>&#x2013;<lpage>132</lpage>. doi: <pub-id pub-id-type="doi">10.1108/ARCH-12-2018-0030</pub-id></citation></ref>
<ref id="ref56"><citation citation-type="book"><person-group person-group-type="author"><collab id="coll4">UN</collab></person-group> (<year>2022</year>). <source>World Economic Situation Prospects</source>. <publisher-loc>New York,NY</publisher-loc>: <publisher-name>United Nation publication</publisher-name>.</citation></ref>
<ref id="ref57"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Van Kamp</surname> <given-names>I.</given-names></name> <name><surname>Job</surname> <given-names>R. F. S.</given-names></name> <name><surname>Hatfield</surname> <given-names>J.</given-names></name> <name><surname>Haines</surname> <given-names>M.</given-names></name> <name><surname>Stellato</surname> <given-names>R. K.</given-names></name> <name><surname>Stansfeld</surname> <given-names>S. A.</given-names></name></person-group> (<year>2004</year>). <article-title>The role of noise sensitivity in the noise&#x2013;response relation: a comparison of three international airport studies</article-title>. <source>J. Acoust. Soc. Am.</source> <volume>116</volume>, <fpage>3471</fpage>&#x2013;<lpage>3479</lpage>. doi: <pub-id pub-id-type="doi">10.1121/1.1810291</pub-id>, PMID: <pub-id pub-id-type="pmid">15658698</pub-id></citation></ref>
<ref id="ref58"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Van Kamp</surname> <given-names>I.</given-names></name> <name><surname>Leidelmeijer</surname> <given-names>K.</given-names></name> <name><surname>Marsman</surname> <given-names>G.</given-names></name> <name><surname>De Hollander</surname> <given-names>A.</given-names></name></person-group> (<year>2003</year>). <article-title>Urban environmental quality and human well-being towards a conceptual framework and demarcation of concepts; a literature study</article-title>. <source>Landsc. Urban Plan.</source> <volume>65</volume>, <fpage>5</fpage>&#x2013;<lpage>18</lpage>. doi: <pub-id pub-id-type="doi">10.1016/S0169-2046(02)00232-3</pub-id></citation></ref>
<ref id="ref59"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Veenhoven</surname> <given-names>R.</given-names></name></person-group> (<year>2000</year>). <article-title>The four qualities of life</article-title>. <source>J. Happiness Stud.</source> <volume>1</volume>, <fpage>1</fpage>&#x2013;<lpage>39</lpage>. doi: <pub-id pub-id-type="doi">10.1023/A</pub-id></citation></ref>
<ref id="ref60"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Weber</surname> <given-names>W.</given-names></name> <name><surname>Dingerkus</surname> <given-names>F.</given-names></name> <name><surname>Fabrikant</surname> <given-names>S. I.</given-names></name> <name><surname>Zampa</surname> <given-names>M.</given-names></name> <name><surname>West</surname> <given-names>M.</given-names></name> <name><surname>Yildirim</surname> <given-names>O.</given-names></name></person-group> (<year>2022</year>). <article-title>Virtual reality as a tool for political decision-making? An empirical study on the power of immersive images on voting behavior</article-title>. <source>Front. Commun.</source> <volume>7</volume>, <fpage>1</fpage>&#x2013;<lpage>17</lpage>. doi: <pub-id pub-id-type="doi">10.3389/fcomm.2022.842186</pub-id></citation></ref>
<ref id="ref61"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Weinstein</surname> <given-names>N. D.</given-names></name></person-group> (<year>1978</year>). <article-title>Individual differences in reactions to noise: a longitudinal study in a college dormitory</article-title>. <source>J. Appl. Psychol.</source> <volume>63</volume>, <fpage>458</fpage>&#x2013;<lpage>466</lpage>. doi: <pub-id pub-id-type="doi">10.1037/0021-9010.63.4.458</pub-id>, PMID: <pub-id pub-id-type="pmid">701213</pub-id></citation></ref>
<ref id="ref62"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Yang</surname> <given-names>W.</given-names></name> <name><surname>Kang</surname> <given-names>J.</given-names></name></person-group> (<year>2005</year>). <article-title>Acoustic comfort evaluation in urban open public spaces</article-title>. <source>Appl. Acoust.</source> <volume>66</volume>, <fpage>211</fpage>&#x2013;<lpage>229</lpage>. doi: <pub-id pub-id-type="doi">10.1016/j.apacoust.2004.07.011</pub-id></citation></ref>
<ref id="ref63"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Yong</surname> <given-names>J.</given-names></name> <name><surname>In</surname> <given-names>H.</given-names></name> <name><surname>Lee</surname> <given-names>K.</given-names></name></person-group> (<year>2021</year>). <article-title>Potential restorative effects of urban soundscapes: personality traits, temperament, and perceptions of VR urban environments</article-title>. <source>Landsc. Urban Plan.</source> <volume>214</volume>:<fpage>104188</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.landurbplan.2021.104188</pub-id></citation></ref>
<ref id="ref64"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Zhao</surname> <given-names>W.</given-names></name> <name><surname>Kang</surname> <given-names>J.</given-names></name> <name><surname>Xu</surname> <given-names>H.</given-names></name> <name><surname>Zhang</surname> <given-names>Y.</given-names></name></person-group> (<year>2021</year>). <article-title>Relationship between contextual perceptions and soundscape evaluations based on the structural equation modelling approach</article-title>. <source>Sustain. Cities Soc.</source> <volume>74</volume>:<fpage>103192</fpage>. doi: <pub-id pub-id-type="doi">10.1016/j.scs.2021.103192</pub-id></citation></ref>
<ref id="ref65"><citation citation-type="journal"><person-group person-group-type="author"><name><surname>Zimmer</surname> <given-names>K.</given-names></name> <name><surname>Ellermeier</surname> <given-names>W.</given-names></name></person-group> (<year>1999</year>). <article-title>Psychometric properties of four measures of noise sensitivity: a comparison</article-title>. <source>J. Environ. Psychol.</source> <volume>19</volume>, <fpage>295</fpage>&#x2013;<lpage>302</lpage>. doi: <pub-id pub-id-type="doi">10.1006/jevp.1999.0133</pub-id></citation></ref></ref-list>
<fn-group><fn id="fn0004"><p><sup>1</sup>This refers to the streets conditions for trips measured by the vehicle level of service (LOS) type C defined in <xref ref-type="bibr" rid="ref54">Transportation Research Board (2010)</xref> for road transport at the average speed range of 50 (mph) and measured in flow range (1,100 vehicles/h/lane) or equivalent (18 vehicles/min/lane).</p></fn>
<fn id="fn0005"><p><sup>2</sup>The chi-square statistic () is used for large and normalised sample sizes. CFI compares the difference in fit with a null model; CFI&#x2009;&#x2265;&#x2009;0.95 is a good fit. TLI is the incremental fit index; TLI&#x2009;&#x2265;&#x2009;0.90 is a good fit. The Root Mean Square Error approximation (RMSEA) privileges models with more degrees of freedom and larger samples; RMSEA &#x2264;0.05 is a good fit. The Standardised Root Mean Square Residual (SRMR) measures the difference between implied and observed covariance matrices; SRMR &#x2264;0.05 is a good fit.</p></fn></fn-group>
</back>
</article>