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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Child Adolesc. Psychiatry</journal-id>
<journal-title>Frontiers in Child and Adolescent Psychiatry</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Child Adolesc. Psychiatry</abbrev-journal-title>
<issn pub-type="epub">2813-4540</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/frcha.2025.1506392</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Child and Adolescent Psychiatry</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Exploring the restorativeness of different hydrodynamic landscapes in world natural heritage sites</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" equal-contrib="yes"><name><surname>Zhang</surname><given-names>Ping</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="author-notes" rid="an1"><sup>&#x2020;</sup></xref><uri xlink:href="https://loop.frontiersin.org/people/2816545/overview"/><role content-type="https://credit.niso.org/contributor-roles/methodology/"/><role content-type="https://credit.niso.org/contributor-roles/project-administration/"/><role content-type="https://credit.niso.org/contributor-roles/resources/"/><role content-type="https://credit.niso.org/contributor-roles/writing-original-draft/"/><role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/></contrib>
<contrib contrib-type="author" equal-contrib="yes"><name><surname>Zhang</surname><given-names>Tongyao</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="author-notes" rid="an1"><sup>&#x2020;</sup></xref><role content-type="https://credit.niso.org/contributor-roles/methodology/"/><role content-type="https://credit.niso.org/contributor-roles/project-administration/"/><role content-type="https://credit.niso.org/contributor-roles/resources/"/><role content-type="https://credit.niso.org/contributor-roles/writing-original-draft/"/><role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/></contrib>
<contrib contrib-type="author" equal-contrib="yes"><name><surname>Chen</surname><given-names>Zexuan</given-names></name>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<xref ref-type="author-notes" rid="an1"><sup>&#x2020;</sup></xref><role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/><role content-type="https://credit.niso.org/contributor-roles/methodology/"/></contrib>
<contrib contrib-type="author"><name><surname>He</surname><given-names>Qianyi</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<role content-type="https://credit.niso.org/contributor-roles/methodology/"/><role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/><role content-type="https://credit.niso.org/contributor-roles/project-administration/"/><role content-type="https://credit.niso.org/contributor-roles/writing-original-draft/"/></contrib>
<contrib contrib-type="author"><name><surname>Luo</surname><given-names>Ke</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<uri xlink:href="https://loop.frontiersin.org/people/2772207/overview" />
<role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/><role content-type="https://credit.niso.org/contributor-roles/data-curation/"/></contrib>
<contrib contrib-type="author"><name><surname>Li</surname><given-names>Jinpeng</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref><role content-type="https://credit.niso.org/contributor-roles/formal-analysis/"/><role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/></contrib>
<contrib contrib-type="author"><name><surname>Yang</surname><given-names>Yanbin</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref><uri xlink:href="https://loop.frontiersin.org/people/2883743/overview" /><role content-type="https://credit.niso.org/contributor-roles/formal-analysis/"/><role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/></contrib>
<contrib contrib-type="author"><name><surname>Zhang</surname><given-names>Qingjie</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<role content-type="https://credit.niso.org/contributor-roles/methodology/"/><role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/></contrib>
<contrib contrib-type="author"><name><surname>Wang</surname><given-names>Xuan</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<role content-type="https://credit.niso.org/contributor-roles/data-curation/"/><role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/></contrib>
<contrib contrib-type="author"><name><surname>Han</surname><given-names>Limin</given-names></name>
<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
<role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/></contrib>
<contrib contrib-type="author"><name><surname>Chen</surname><given-names>Mingze</given-names></name>
<xref ref-type="aff" rid="aff4"><sup>4</sup></xref><uri xlink:href="https://loop.frontiersin.org/people/2552176/overview" /><role content-type="https://credit.niso.org/contributor-roles/formal-analysis/"/><role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/></contrib>
<contrib contrib-type="author"><name><surname>Zhao</surname><given-names>Fupei</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref><role content-type="https://credit.niso.org/contributor-roles/resources/"/><role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/></contrib>
<contrib contrib-type="author"><name><surname>He</surname><given-names>Xiaoqing</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref><role content-type="https://credit.niso.org/contributor-roles/resources/"/><role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/></contrib>
<contrib contrib-type="author"><name><surname>Cao</surname><given-names>Saixin</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref><role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/></contrib>
<contrib contrib-type="author"><name><surname>Xu</surname><given-names>Xiaoqing</given-names></name>
<xref ref-type="aff" rid="aff5"><sup>5</sup></xref><uri xlink:href="https://loop.frontiersin.org/people/1403509/overview" /><role content-type="https://credit.niso.org/contributor-roles/resources/"/><role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/></contrib>
<contrib contrib-type="author" corresp="yes"><name><surname>Wang</surname><given-names>Guangyu</given-names></name>
<xref ref-type="aff" rid="aff4"><sup>4</sup></xref>
<xref ref-type="corresp" rid="cor1">&#x002A;</xref><uri xlink:href="https://loop.frontiersin.org/people/961252/overview" /><role content-type="https://credit.niso.org/contributor-roles/formal-analysis/"/><role content-type="https://credit.niso.org/contributor-roles/funding-acquisition/"/><role content-type="https://credit.niso.org/contributor-roles/supervision/"/><role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/></contrib>
<contrib contrib-type="author" corresp="yes"><name><surname>Li</surname><given-names>Xi</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="corresp" rid="cor1">&#x002A;</xref><uri xlink:href="https://loop.frontiersin.org/people/2545512/overview" /><role content-type="https://credit.niso.org/contributor-roles/funding-acquisition/"/><role content-type="https://credit.niso.org/contributor-roles/resources/"/><role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/></contrib>
</contrib-group>
<aff id="aff1"><label><sup>1</sup></label><institution>College of Landscape Architecture, Sichuan Agricultural University</institution>, <addr-line>Chengdu</addr-line>, <country>China</country></aff>
<aff id="aff2"><label><sup>2</sup></label><institution>School of Architecture and Urban Planning, Chongqing University</institution>, <addr-line>Chongqing</addr-line>, <country>China</country></aff>
<aff id="aff3"><label><sup>3</sup></label><institution>School of International Education, Chengdu Agricultural College</institution>, <addr-line>Chengdu</addr-line>, <country>China</country></aff>
<aff id="aff4"><label><sup>4</sup></label><institution>Faculty of Forestry, Department of Forest and Resources Management, University of British Columbia</institution>, <addr-line>Vancouver, BC</addr-line>, <country>Canada</country></aff>
<aff id="aff5"><label><sup>5</sup></label><institution>Department of Landscape Architecture, School of Architecture and Urban Planning, Tongji University</institution>, <addr-line>Shanghai</addr-line>, <country>China</country></aff>
<author-notes>
<fn fn-type="edited-by"><p><bold>Edited by:</bold> Samuel Tomczyk, University of Greifswald, Germany</p></fn>
<fn fn-type="edited-by"><p><bold>Reviewed by:</bold> Angel Puig-Lagunes, Facultad de Medicina, Universidad Veracruzana, Mexico</p>
<p>Senhong Cai, Wuhan University, China</p></fn>
<corresp id="cor1"><label>&#x002A;</label><bold>Correspondence:</bold> Guangyu Wang <email>guangyu.wang@ubc.ca</email> Xi Li <email>lixi@sicau.edu.cn</email></corresp>
<fn fn-type="equal" id="an1"><label><sup>&#x2020;</sup></label><p>These authors have contributed equally to this work</p></fn>
</author-notes>
<pub-date pub-type="epub"><day>12</day><month>02</month><year>2025</year></pub-date>
<pub-date pub-type="collection"><year>2025</year></pub-date>
<volume>4</volume><elocation-id>1506392</elocation-id>
<history>
<date date-type="received"><day>05</day><month>10</month><year>2024</year></date>
<date date-type="accepted"><day>02</day><month>01</month><year>2025</year></date>
</history>
<permissions>
<copyright-statement>&#x00A9; 2025 Zhang, Zhang, Chen, He, Luo, Li, Yang, Zhang, Wang, Han, Chen, Zhao, He, Cao, Xu, Wang and Li.</copyright-statement>
<copyright-year>2025</copyright-year><copyright-holder>Zhang, Zhang, Chen, He, Luo, Li, Yang, Zhang, Wang, Han, Chen, Zhao, He, Cao, Xu, Wang and Li</copyright-holder><license license-type="open-access" xlink:href="http://creativecommons.org/licenses/by/4.0/">
<p>This is an open-access article distributed under the terms of the <ext-link ext-link-type="uri" xlink:href="http://creativecommons.org/licenses/by/4.0/">Creative Commons Attribution License (CC BY)</ext-link>. The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</p></license>
</permissions>
<abstract>
<p>Audiovisual environmental perception has been the focus of numerous empirical studies. This study employs virtual reality (VR) to explore how different hydrodynamic waterscapes in Jiuzhaigou World Natural Heritage Site affect physiological and psychological restoration in youth. According to the results, audiovisual interactions, particularly with water sounds and birdsongs, significantly enhance physiological restoration compared to visuals alone. High-intensity hydrodynamic landscapes, regardless of birdsongs, exhibit the highest physiological restoration. There is a linearly positive correlation between physiological restorativeness and hydrodynamic landscapes. Medium-intensity hydrodynamic landscapes with rich forms are most psychologically restorative. In low-medium-intensity settings, visuals contribute more to psychological restoration than soundscapes. It is further found that waterscapes rich in flora and fauna feature a higher level of biodiversity. In the waterscapes with both elements of vegetation and water, the restorativeness of plant and animal resources is greater than that of water. This work highlights the need to focus on the application of different hydrodynamic landscapes in urban areas and the conservation of World Heritage Sites.</p>
</abstract>
<kwd-group>
<kwd>audiovisual perception</kwd>
<kwd>hydrodynamic landscapes</kwd>
<kwd>restorative effect</kwd>
<kwd>virtual reality</kwd>
<kwd>Jiuzhaigou World Natural Heritage Site</kwd>
</kwd-group><contract-num rid="cn001">22GJHZ0142</contract-num><contract-sponsor id="cn001">Jiuzhaigou World Heritage Site</contract-sponsor><counts>
<fig-count count="6"/>
<table-count count="18"/><equation-count count="0"/><ref-count count="0"/><page-count count="22"/><word-count count="0"/></counts><custom-meta-wrap><custom-meta><meta-name>section-at-acceptance</meta-name><meta-value>Interventions for Adolescent Mental Health</meta-value></custom-meta></custom-meta-wrap>
</article-meta>
</front>
<body><sec id="s1" sec-type="intro"><label>1</label><title>Introduction</title>
<p>Under the significant pressure and high degree of sedentary work in modern life, individuals often have limited time and motivation for outdoor activities. This trend leads to an increased risk of physical and psychological ailments among youth, characterized by a rapidly declining attention span and accumulating mental fatigue. As a pivotal force driving social development and progress, factors that induce restorative effects on youth warrant comprehensive research.</p>
<p>Studies have shown that green spaces play a positive role in improving mood, alleviating work pressure, and preventing and managing mental illness (<xref ref-type="bibr" rid="B1">1</xref>). Among natural environments, blue spaces are considered the most favored, exerting a significant impact on enhancing mental health and psychological well-being (<xref ref-type="bibr" rid="B2">2</xref>). The broader utilization of blue&#x2013;green spaces to promote individuals&#x0027; health and well-being has become a key issue in creating current health-promoting environments (<xref ref-type="bibr" rid="B3">3</xref>). However, studies on the attraction of freshwater blue spaces are limited (<xref ref-type="bibr" rid="B4">4</xref>).</p>
<p>Loudness and the pressure level of water sounds, the two components of hydrodynamic intensity, are considered indicators for the restorativeness of water sounds. Water sounds, a significant factor in blue&#x2013;green spaces, have a remarkable influence on the restorativeness of the environment in terms of acoustic loudness (or sound pressure level) (<xref ref-type="bibr" rid="B5">5</xref>). Loudness refers to humans&#x0027; subjective auditory sensation of sounds and can be represented in decibel values (<xref ref-type="bibr" rid="B6">6</xref>). The sound pressure level (SPL) of water varies with water velocity, falling height, and impact material, among other factors (<xref ref-type="bibr" rid="B7">7</xref>), with changes in water sound source mainly affected by water velocity. Human auditory perception is reported to vary from enjoyment to like to dislike and then to complete aversion (<xref ref-type="bibr" rid="B8">8</xref>). Research on the effects of audiovisual interaction in urban environments has revealed that the availability of visual and auditory information significantly influences the perception of auditory and visual elements. When visual and auditory modalities are simultaneously engaged, individuals typically perceive communicative signals more intensively. Compared to a single sense, multisensory inputs can convey deeper and more comprehensive information, satisfying the human brain&#x0027;s need to integrate the external world through different sensory channels (<xref ref-type="bibr" rid="B9">9</xref>, <xref ref-type="bibr" rid="B10">10</xref>). Nature-related audiovisual stimuli are considered more beneficial to health compared to visual stimuli alone (<xref ref-type="bibr" rid="B11">11</xref>).</p>
<p>With natural habitats shrinking due to urbanization, restorative natural environments have become scarce resources in cities. In response to this, virtual reality (VR) technology is employed to bridge the gap between people and nature by providing simulated audiovisual landscapes. This allows individuals to conveniently experience nature, making virtual natural environments a valuable tool for alleviating various physical and mental ailments (<xref ref-type="bibr" rid="B12">12</xref>).</p>
<p>According to the United Nations Educational, Scientific, and Cultural Organization (UNESCO), World Natural Heritage Sites refer to natural areas that are considered to have &#x201C;outstanding universal value&#x201D; from an aesthetic or scientific perspective. These sites are recognized for their unique geological and ecological features, biodiversity or natural beauty that is considered important for the whole of humanity. As unspoiled natural environment offering visitors unique and wonderful experiences, World Natural Heritage Sites can relieve modern people from stress, tension and fatigue caused by decreased directed attention, and reduce the incidence of cardiovascular diseases (<xref ref-type="bibr" rid="B13">13</xref>). For depressed patients, mental stress level can be maintained at an ideal state in at least one month after returning to normal life (<xref ref-type="bibr" rid="B14">14</xref>).</p>
<p>Jiuzhaigou is a World Heritage Site characterized by its rich blue and green spaces. The study of such spaces aligns fully with the restorative environmental experiences of people (<xref ref-type="bibr" rid="B15">15</xref>). However, there are few studies that take Natural World Heritage Sites as a research object, most of which focus on environmental perception, place attachment, and visitor loyalty (<xref ref-type="bibr" rid="B16">16</xref>&#x2013;<xref ref-type="bibr" rid="B19">19</xref>). These studies on audiovisual interactions predominantly focus on urban environment. Few studies have examined World Heritage Sites from the perspective of restorative effects.</p>
<p>Therefore, this study aims to explore the blue&#x2013;green spaces of the Jiuzhaigou World Natural Heritage Site using virtual reality (VR) technology, with a focus on understanding the varying physiopsychological restorativeness of the different hydrodynamic waterscapes in Jiuzhaigou for youth. In particular, we examine differences in audiovisual interactions and pure visuals regarding their effects on promoting physiological restorativeness. Furthermore, we consider disparities in physiopsychological restorativeness among youth resulting from exposure to the different hydrodynamic waterscapes in Jiuzhaigou, and determine whether there exists a hydrodynamic landscape with optimal visual psychological restorativeness for youth within the Jiuzhaigou World Natural Heritage Site.</p>
</sec>
<sec id="s2"><label>2</label><title>Methodology</title>
<sec id="s2a"><label>2.1</label><title>Research area</title>
<p>Jiuzhaigou is situated in the central and southern parts of Jiuzhaigou County, Sichuan Province, China, covering a total area of about 620&#x2005;km<sup>2</sup>. Approximately 52&#x0025; of this area is comprised of virgin forests, boasting rich animal and plant resources, including rare species. This abundance is attributed to the presence of nine Tibetan villages in the valley. Jiuzhaigou Valley, characterized by its plateau traverse, Haizi groups, waterfall clusters, and flowing beaches, stands out as one of China&#x0027;s premier scenic spots for its water features. Springs, waterfalls, rivers, beaches, and 108 Haizi (a term used by locals to refer to the naturally formed, high-altitude lakes found in Jiuzhaigou) form a vibrant jade basin, cherished for its ecological significance, scientific value, aesthetic appeal, and tourism potential (<xref ref-type="fig" rid="F1">Figure&#x00A0;1</xref>).</p>
<fig id="F1" position="float"><label>Figure 1</label>
<caption><p>Map of the study area.</p></caption>
<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="frcha-04-1506392-g001.tif"/>
</fig>
</sec>
<sec id="s2b"><label>2.2</label><title>Research framework</title>
<p>The Jiuzhaigou Scenic Area, located in Aba Tibetan and Qiang Autonomous Prefecture, was chosen as the research site, with 23 image collection points selected according to the landscape environment in Jiuzhaigou for the collection of panoramic video images and two-dimensional water environment factor images. Based on the sound pressure level measured in the field, the collected waterscape points are divided into low, medium, and high hydrodynamic landscapes. Psychological data measurements and scale tests were conducted in the laboratory to explore the influence of different hydrodynamic landscapes on the restorativeness of youth. During the preliminary research process, we observed that low hydrodynamic landscapes (Haizi) feature more abundant waterscape elements, particularly biological habitats, compared to other hydrodynamic shoals and waterfalls. Further exploration was undertaken to investigate the restorative effects of the Haizi components, characteristics, and elements on youth and determine the presence of a hydrodynamic landscape with optimal visual psychological restorativeness for youth within the Jiuzhaigou World Natural Heritage Site (<xref ref-type="fig" rid="F2">Figure&#x00A0;2</xref>).</p>
<fig id="F2" position="float"><label>Figure 2</label>
<caption><p>Experimental framework used in this study.</p></caption>
<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="frcha-04-1506392-g002.tif"/>
</fig>
</sec>
<sec id="s2c"><label>2.3</label><title>Collection and processing of experimental data and materials</title>
<p>Before the experiment, panoramic and single-frame images and sounds were collected at 31 points located at lakes, waterfalls, and beaches in Shuzhenggou (Shuzheng Valley), Rizegou (Rize Valley), and Zechawagou (Zechawa Valley) from 26 to 31 July 2022. An Insta 360 (15&#x2013;20 megapixels and 4/3-in. sensor) and Canon m50 (20&#x2013;30 megapixels, APS-C sensor, LSO100-25600 standard ISO sensitivity) were employed to collect panoramic and single-frame images, respectively. Considering color, shooting climate, resolution, and representativeness, the panoramic videos and images were collected without people to ensure that the subject focused on the landscape (<xref ref-type="bibr" rid="B20">20</xref>). Images and videos were collected during 9&#x2013;11 a.m. and 2&#x2013;4 p.m. to ensure similar weather conditions (in July 2022, the average daytime temperature in Jiuzhaigou for the whole month was 30&#x00B0;C, with 85&#x0025; relative humidity). We selected the shooting locations based on the suggestions of Jiuzhaigou staff, tourists, and residents. For the acquisition of the 360&#x00B0; panoramic videos and images, the Insta 360 panoramic camera was placed on a tripod with the lens at the same height as the human eye (1.2&#x2005;m). A ZoomH5 recorder, outdoor directional microphone (RODE NTG4), and sound level meter (Aihua 6228) were used to collect natural sound data of water sounds and bird songs.</p>
<p>The minimum sound pressure that can be perceived by individuals with normal hearing is 0&#x2005;dB (1,000&#x2005;Hz). However, in general, sound with a stable sound pressure level within 10&#x2013;15&#x2005;dB is difficult to perceive. Therefore, this study defines low and medium hydrodynamic intensity underwater sound within the ranges of 30&#x2013;50&#x2005;dBA and 51&#x2013;70&#x2005;dBA, with high hydrodynamic intensity sounds exceeding 71&#x2005;dBA. Haizi in Jiuzhaigou are classified according to the hydrodynamic landscape (<xref ref-type="sec" rid="s10">Supplementary Map</xref>). By combining field investigation observations, network comparison, and test requirements, we selected four Haizi landscapes as representatives of low hydrodynamic landscapes, and Shuzheng Lakes and Nuorilang Waterfall as representatives of medium and high hydrodynamic landscapes, respectively. Water panoramic videos of these six landscapes with different hydrodynamics were employed as the test materials (<xref ref-type="table" rid="T1">Table&#x00A0;1</xref>).</p>
<table-wrap id="T1" position="float"><label>Table 1</label>
<caption><p>Description of the study sites.</p></caption>
<table frame="hsides" rules="groups">
<colgroup>
<col align="left"/>
<col align="left"/>
<col align="left"/>
<col align="left"/>
<col align="left"/>
<col align="left"/>
<col align="left"/>
</colgroup>
<thead>
<tr>
<th valign="top" align="left">Hydrodynamic landscape</th>
<th valign="top" align="center">Sound pressure level</th>
<th valign="top" align="center">Example</th>
<th valign="top" align="center">Meter test of original sound level</th>
<th valign="top" align="center">Landscape features</th>
<th valign="top" align="center">Image</th>
<th valign="top" align="center">Panoramic VR video</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left" rowspan="4">Low hydrodynamic andscape (Haizi)</td>
<td valign="top" align="left" rowspan="4">30&#x2013;50&#x2005;dBA</td>
<td valign="top" align="left">Wucaichi</td>
<td valign="top" align="left">32.7&#x2005;dBA&#x2009;&#x00B1;&#x2009;3.4</td>
<td valign="top" align="left">The scale of the water body is small, the color changes are rich, and the waterfront is composed of rocks.</td>
<td valign="top" align="left"><inline-graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="frcha-04-1506392-i001.tif"/></td>
<td valign="top" align="left"><inline-graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="frcha-04-1506392-i002.tif"/></td>
</tr>
<tr>
<td valign="top" align="left">Wuhua Lake</td>
<td valign="top" align="left">36.9&#x2005;dBA&#x2009;&#x00B1;&#x2009;3.8</td>
<td valign="top" align="left">The water body has high transparency, rich color changes, and abundant moist plants.</td>
<td valign="top" align="left"><inline-graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="frcha-04-1506392-i003.tif"/></td>
<td valign="top" align="left"><inline-graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="frcha-04-1506392-i004.tif"/></td>
</tr>
<tr>
<td valign="top" align="left">Luwei Lake</td>
<td valign="top" align="left">47.4&#x2005;dBA&#x2009;&#x00B1;&#x2009;3.8</td>
<td valign="top" align="left">Typical banded water body with high surrounding openness and abundant moist plants.</td>
<td valign="top" align="left"><inline-graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="frcha-04-1506392-i005.tif"/></td>
<td valign="top" align="left"><inline-graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="frcha-04-1506392-i006.tif"/></td>
</tr>
<tr>
<td valign="top" align="left">Mirror Lake</td>
<td valign="top" align="left">32.7&#x2005;dBA&#x2009;&#x00B1;&#x2009;3.4</td>
<td valign="top" align="left">The perception depth of the water body is deep, the reflection types in the water are rich, the reflection of complete clouds, mountains, and plants can be seen, and the environment is rich in bird songs.</td>
<td valign="top" align="left"><inline-graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="frcha-04-1506392-i007.tif"/></td>
<td valign="top" align="left"><inline-graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="frcha-04-1506392-i008.tif"/></td>
</tr>
<tr>
<td valign="top" align="left">
Medium hydrodynamic landscape (combined landscape)</td>
<td valign="top" align="left">51&#x2013;70&#x2005;dBA</td>
<td valign="top" align="left">Shuzheng Lakes</td>
<td valign="top" align="left">56.2&#x2005;dBA&#x2009;&#x00B1;&#x2009;0.8</td>
<td valign="top" align="left">The plant layer is rich; the water body is mainly blue; the water sound is clear.</td>
<td valign="top" align="left"><inline-graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="frcha-04-1506392-i009.tif"/></td>
<td valign="top" align="left"><inline-graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="frcha-04-1506392-i010.tif"/></td>
</tr>
<tr>
<td valign="top" align="left">
High hydrodynamic landscape (waterfall)</td>
<td valign="top" align="left">&#x2265;71&#x2005;dBA</td>
<td valign="top" align="left">Nuorilang Waterfall</td>
<td valign="top" align="left">71.1&#x2005;dBA&#x2009;&#x00B1;&#x2009;0.6</td>
<td valign="top" align="left">The plant level is rich, the water quantity is large, the flow rate is large, and the water sound is loud</td>
<td valign="top" align="left"><inline-graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="frcha-04-1506392-i011.tif"/></td>
<td valign="top" align="left"><inline-graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="frcha-04-1506392-i012.tif"/></td>
</tr>
</tbody>
</table>
</table-wrap>
<p>We collected 31 panoramic images, 56 soundscape data, and 1,086 single-frame images at 31 points. Among the single-frame images, we retained 100 after three rounds of screening (select images with high clarity, clear composition, and no obvious distracting elements). Following this, 15 graduate students and 10 teachers of landscape architecture determined 54 single-frame photographs as test materials according to the test requirements and subsequently conducted the necessary exposure processing based on maximizing the fidelity (<xref ref-type="fig" rid="F3">Figure&#x00A0;3</xref>). Note that single-frame photographs depict materials containing water bodies, plants at water edges, and animals such as fish and birds. For the collected soundscape materials, the members of the research team compared the external sounds with the embedded sounds, and selected the bird song soundscape in Wucaichi Forest with the most abundant and prosperous bird song ecological niche as the test materials. Adobe Audition 2022 was then used to complete the noise reduction and cleaning process. To ensure that the measured value (dBA value) was as close as possible to the participants&#x0027; subjective feelings, we introduced A-rate weighting.</p>
<fig id="F3" position="float"><label>Figure 3</label>
<caption><p>Examples of the 54 single-frame photographs for the perception restorativeness scale of the low hydrodynamic landscapes (Haizi).</p></caption>
<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="frcha-04-1506392-g003.tif"/>
</fig>
</sec>
<sec id="s2d"><label>2.4</label><title>Participant<bold>s</bold></title>
<p>A total of 64 Chinese youth (24 males and 40 females) were selected to participate in the experiment. Among them, 34 were university students and 30 were graduates (24 undergraduates and 10 postgraduates). All participants satisfied the following criteria: (1) they were aged from 19 to 26; (2) their majors covered the fields of landscape architecture, finance, environmental engineering, animal science, medicine, ecology and economics. Due to the nature of their professions, they all needed to spend extended time conducting experiments in sealed laboratories, engaging in physically demanding research of natural or social science, or spending hours engineering drawing in the office. As a result, they experienced high levels of learning pressure and both physical and mental fatigue.; (3) they generally had consistent vision, hearing, and color recognition abilities, good physical and mental health levels, and no history of drug abuse, alcoholism, or smoking; and (4) they visited green spaces one to three times per week, with the green spaces typically on campus or close to schools and homes (e.g., nearby parks). The study was conducted in accordance with the Declaration of Helsinki and was approved by the Human Research Ethics Committee of Sichuan Agricultural University.</p>
</sec>
<sec id="s2e"><label>2.5</label><title>Assessment procedures</title>
<p>We measured the differences in the physiological and psychological restorativeness of different hydrodynamic landscapes using physiological and psychological assessments and a questionnaire survey. The physiological assessment data was collected by recording the heart rate (HR), blood pressure (BP), and electroencephalogram (EEG). The psychological assessment data was collected by applying the perception restorativeness scale (PRS). The questionnaire survey was conducted using a PRS specifically designed for low hydrodynamic landscapes (Haizi) by the study group.</p>
<sec id="s2e1"><label>2.5.1</label><title>Physiological data measurements</title>
<p>The blood pressure [systolic (mmHg), diastolic (mmHg)] and heart rate of the participants were measured on the left arm using an electronic sphygmomanometer (OMRON HEM-7135) to indicate the relaxation degree of the body. The HR is considered a physiological response indicator to physiological stimuli and psychological stress (<xref ref-type="bibr" rid="B21">21</xref>). EEG is an oscillogram of electrophysiological signals that reflects the neurophysiological activities of brain neurons on the cerebral cortex or the scalp (<xref ref-type="bibr" rid="B22">22</xref>). It contains a large amount of information about brain activity that is closely related to human thinking, physical activity, mental state, and physical and mental health (<xref ref-type="bibr" rid="B23">23</xref>). Different wave bands can reflect different emotional states and cognitive abilities (<xref ref-type="bibr" rid="B24">24</xref>). The brain signals were measured in this study with a Wise Brain Instrument (Sichiray 03) at three waves (theta, alpha, and beta). Theta (<italic>&#x03B8;</italic>) waves range from approximately 4&#x2013;8&#x2005;Hz and are typically associated with deep relaxation, meditation, and mild sleep stages such as (rapid eye movement (REM) sleep. They are often considered as the brainwaves related to creativity and subconscious thinking. At this frequency, the abilities of memory, learning, and emotional integration may be enhanced as the brain enters a state of marginal consciousness, which is conducive to the formation of new ideas and concepts. Alpha (&#x03B1;) waves, which range from approximately 8&#x2013;12&#x2005;Hz, indicate relaxation in a state of consciousness and can often get intensified while sitting down with the eyes closed. They are associated with feelings of relaxation, tranquility, and a balance of physical and mental states. Enhanced alpha wave activity suggests that an individual may be in a state of idle thinking or enhanced creativity. Alpha wave activity often increases when individuals are in contact with nature, performing deep breathing exercises, or engaging in relaxation activities. Beta (&#x03B2;) waves range from approximately 12&#x2013;30&#x2005;Hz and are associated with daily alertness, concentration, decision-making, and problem-solving activities. High-frequency beta waves are related to states of anxiety, stress, or panic. However, moderate beta wave activity is healthy, indicating that the brain is in an alert and active state, capable of effective logical thinking and critical analysis.</p>
</sec>
<sec id="s2e2"><label>2.5.2</label><title>Psychological data measurements</title>
<p>Scales are typically used to measure psychological restorativeness, with PRS as the most representative (<xref ref-type="app" rid="app1">Appendix A</xref>). Developed by Hartig et al. (<xref ref-type="bibr" rid="B25">25</xref>), the PRS contains four items and 26 projects (<xref ref-type="bibr" rid="B20">20</xref>). Due to the cultural differences and different language habits in the semantics of different countries, Wang (<xref ref-type="bibr" rid="B26">26</xref>) applied the Chinese version of PRS to the restorativeness assessment of urban park landscapes, validating the reliability of the Chinese version of PRS (<xref ref-type="bibr" rid="B27">27</xref>, <xref ref-type="bibr" rid="B28">28</xref>). The PRS used for the psychological measurements in this study is based on the modified version of Huang et al. (<xref ref-type="bibr" rid="B29">29</xref>), consisting of 18 items in four dimensions (distance, extension, charisma, and compatibility), and modified according to the attention restorative theory by Kaplan et al. (<xref ref-type="bibr" rid="B27">27</xref>) (<xref ref-type="app" rid="app1">Appendix A</xref>).</p>
</sec>
<sec id="s2e3"><label>2.5.3</label><title>Questionnaire survey</title>
<p>This study further developed the PRS for low hydrodynamic landscapes (Haizi). Based on field investigations and literature reviews, the scale was ultimately determined to consist of three dimensions: the scale for the restorativeness of Haizi components; the characteristics of Haizi (<xref ref-type="app" rid="app2">Appendix B</xref>); and the elements of Haizi (<xref ref-type="app" rid="app3">Appendix C</xref>). The Haizi characteristics that vary continuously can generally be described by an interval, while the Haizi elements have discrete features. Each level is rated on a perception restorativeness scale from 1 to 7, where 7 represents the highest positive evaluation (considered the most restorative), and 1 represents the lowest evaluation (considered the least restorative).</p>
</sec>
</sec>
<sec id="s2f"><label>2.6</label><title>Experimental procedures</title>
<p>The experiment was performed from October 15 to November 17, 2023, during 7&#x2013;8:30 p.m. each day. The laboratory maintained a consistent physical environment, namely, it was quiet (noise below 25&#x2005;dB), clean (interior space of 10&#x2005;m<sup>2</sup> containing a set of desks and chairs and no windows), with appropriate light, temperature (20&#x00B0;C&#x2013;23&#x00B0;C) and relative humidity (about 45&#x0025;&#x2013;55&#x0025;), and without disturbances. The VR device (HTC VIVE Professional Version) was set up and debugged by staff in the laboratory before measurements. The device contained two positioners and a headset, with the following parameters: 90&#x2005;Hz refresh rate; 110&#x00B0; maximum field angle; 2,880&#x2009;&#x00D7;&#x2009;1,600 resolution; smooth and clear video-broadcasting; built-in high-resolution-certified headphones; and good audio sound quality. When watching the videos, the participants could freely turn their heads to simulate the real walking experience. The test lasted for approximately 45&#x2005;min.</p>
<p>Upon arriving at the laboratory, the participants were involved in three steps for the test procedure. The first step involved informing the participants about the test&#x0027;s purpose, procedure, and any necessary precautions by the staff. Participants filled out an informed consent form, which included consent for human image use. After the first step has been completed, participants then independently completed 1-min mental arithmetic tasks. For the second step, the blood pressure monitor was employed to test the participants&#x2019; blood pressure and heart rate, and an EEG then recorded brainwave data for 1&#x2005;min. Participants sequentially watched 1-min panoramic videos featuring landscapes with low, medium, and high hydrodynamic intensities (Mirror Lake, Shuzheng Lakes, and Nuorilang Waterfall) in quiet surroundings through VR headsets. The video comprises 30&#x2005;s of original sounds and 30&#x2005;s of original sounds with bird songs. During this process, staff members monitored and recorded the participants&#x0027; brainwave data in real-time. After viewing each hydrodynamic landscape through VR, participants removed the VR devices and completed a PRS. The VR devices were then worn again for the next test. Following this, participants took a 6-min rest to ensure that they experienced the same level of fatigue before the next stage of the test. For the third step, the participants had their blood pressure and heart rate monitored again using the blood pressure monitor, followed by the recording of brainwave data using the EEG for 1&#x2005;min. Participants then sequentially watched a 1-min visual panoramic video featuring low hydrodynamic landscapes (Mirror Lake, Wuhua Lake, Luwei Lake, and Wucaichi) in quiet surroundings through VR headsets. Staff members monitored and recorded the participants&#x0027; brainwave data in real-time during this process. After watching the video, the blood pressure and heart rate of the participants were measured, and they completed the PRS. The staff collected the completed scales, and participants were allowed a 2-min rest. Following this, participants viewed single-frame photographs presented in slides. The slide show began with a 60-s blank and then displayed 54 still, clear, and brightly colored images of landscapes. The size and layout of the photographs aimed to immerse the participants into the scene. During the viewing of the images, participants could freely navigate the slides. Finally, the participants completed the 15-min Haizi perception restorativeness scale (PRS) (<xref ref-type="fig" rid="F4">Figure&#x00A0;4</xref>).</p>
<fig id="F4" position="float"><label>Figure 4</label>
<caption><p>Experimental procedure experienced by the participants.</p></caption>
<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="frcha-04-1506392-g004.tif"/>
</fig>
</sec>
<sec id="s2g"><label>2.7</label><title>Statistical analysis</title>
<p>Statistical analysis was performed with SPSS 26.0 (IBM Corp.). Paired <italic>t</italic>-tests, repeated measures analysis of variance test (ANOVA), and the mean difference were applied to calculate the physiological and psychological state indicators. If large differences were observed among the test results, the least-significant difference (LSD) test was performed. In this study, a <italic>P</italic>-value less than 0.05 indicates statistical significance. A stepwise linear regression model was applied to test the perceptual restorativeness of the constituents, characteristics, and elements of Haizi. A VIF of multiple linear regression values exceeding 10 indicates collinearity among the independent variables and as a consequence, the unreliability of the generated equation model. The model fit is considered acceptable for goodness-of-fit values of the multiple regression greater than 30&#x0025;.</p>
</sec>
</sec>
<sec id="s3" sec-type="results"><label>3</label><title>Results</title>
<p>In this study, the maximum VIF value of the model is determined as 2.542, indicating that there is no collinearity and that the model is reliable. All dimensions of the model exhibited goodness-of-fit (<italic>R</italic>&#x00B2;) values exceeding 30&#x0025;, with many exceeding 50&#x0025;, and the highest reaching 81.5&#x0025;. Therefore, the model fit is considered acceptable. The results of this study on physiological and psychological data are as follows:</p>
<sec id="s3a"><label>3.1</label><title>Physiological data</title>
<sec id="s3a1"><label>3.1.1</label><title>Blood pressure and heart rate data</title>
<p>Following the audiovisual interaction test of the low hydrodynamic landscape (Haizi), participants exhibit a significant decrease in heart rate (79.22&#x2009;&#x00B1;<sans-serif>&#x2009;13</sans-serif>.30&#x2013;75.59&#x2009;&#x00B1;<sans-serif>&#x2009;10</sans-serif>.78, <italic>P</italic>&#x2009;&#x003C;<sans-serif>&#x2009;0</sans-serif>.01), systolic pressure (110.42&#x2009;&#x00B1;<sans-serif>&#x2009;9</sans-serif>.22&#x2013;103.81&#x2009;&#x00B1;<sans-serif>&#x2009;8</sans-serif>.55, <italic>P</italic>&#x2009;&#x003C;<sans-serif>&#x2009;0</sans-serif>.01), and diastolic pressure (70.16&#x2009;&#x00B1;<sans-serif>&#x2009;9</sans-serif>.47&#x2013;67.52&#x2009;&#x00B1;<sans-serif>&#x2009;7</sans-serif>.22, <italic>P</italic>&#x2009;&#x003C;<sans-serif>&#x2009;0</sans-serif>.05) (<xref ref-type="fig" rid="F4">Figure&#x00A0;4</xref>). Following the pure visual test of Haizi, participants present a significant reduction in heart rate (84.50&#x2009;&#x00B1;&#x2009;14.30&#x2013;79.37&#x2009;&#x00B1;<sans-serif>&#x2009;12</sans-serif>.03, <italic>P</italic>&#x2009;&#x003C;<sans-serif>&#x2009;0</sans-serif>.01), while systolic and diastolic blood pressure exhibit minimal changes (<xref ref-type="fig" rid="F5">Figure&#x00A0;5</xref>).</p>
<fig id="F5" position="float"><label>Figure 5</label>
<caption><p>Blood pressure and heart rate data.</p></caption>
<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="frcha-04-1506392-g005.tif"/>
</fig>
</sec>
<sec id="s3a2"><label>3.1.2</label><title>Brainwave data</title>
<p>After completing the audiovisual interaction of different hydrodynamic landscapes, the mean theta, alpha, and beta wave values are observed to increase greatly. Paired <italic>T</italic>-test results show marked differences (<italic>P</italic>&#x2009;&#x003C;<sans-serif>&#x2009;0</sans-serif>.05) between baseline and experimental theta, alpha, and beta wave data for the different hydrodynamic landscape tests. Moreover, the mean values of the three waves peak during the high hydrodynamic landscape (waterfall) test. However, no significant differences are observed in the corresponding ANOVA results (<xref ref-type="table" rid="T2">Table&#x00A0;2</xref>).</p>
<table-wrap id="T2" position="float"><label>Table 2</label>
<caption><p>Brainwave response to the audiovisual interaction of different hydrodynamic landscapes.</p></caption>
<table frame="hsides" rules="groups">
<colgroup>
<col align="left"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
</colgroup>
<thead>
<tr>
<th valign="top" align="left">Brainwave</th>
<th valign="top" align="center">Baseline value</th>
<th valign="top" align="center">Low hydrodynamic landscape (Haizi)</th>
<th valign="top" align="center">Medium hydrodynamic landscape (combined landscape)</th>
<th valign="top" align="center">High hydrodynamic landscape (waterfall)</th>
<th valign="top" align="center"><italic>P</italic>- value</th>
<th valign="top" align="center">Difference value</th>
<th valign="top" align="center"><italic>T</italic>-value</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">Theta wave</td>
<td valign="top" align="center">156,429.26</td>
<td valign="top" align="center">232,712.00</td>
<td valign="top" align="center">242,948.11</td>
<td valign="top" align="center">262,758.90</td>
<td valign="top" align="center">0.001&#x002A;&#x002A;<break/>0.000&#x002A;&#x002A;&#x002A;<break/>0.000&#x002A;&#x002A;&#x002A;</td>
<td valign="top" align="center">76,282.74<break/>86,515.85<break/>106,329.64</td>
<td valign="top" align="center">&#x2212;3.715<break/>&#x2212;4.672<break/>&#x2212;5.060</td>
</tr>
<tr>
<td valign="top" align="left">Alpha wave</td>
<td valign="top" align="center">66,721.13</td>
<td valign="top" align="center">101,320.11</td>
<td valign="top" align="center">109,653.13</td>
<td valign="top" align="center">116,431.77</td>
<td valign="top" align="center">0.002&#x002A;&#x002A;<break/>0.000&#x002A;&#x002A;&#x002A;<break/>0.000&#x002A;&#x002A;&#x002A;</td>
<td valign="top" align="center">34,598.98<break/>42,932.00<break/>49,710.64</td>
<td valign="top" align="center">&#x2212;3.340<break/>&#x2212;4.379<break/>&#x2212;4.295</td>
</tr>
<tr>
<td valign="top" align="left">Beta wave</td>
<td valign="top" align="center">45,957.34</td>
<td valign="top" align="center">62,915.66</td>
<td valign="top" align="center">68,214.69</td>
<td valign="top" align="center">73,131.74</td>
<td valign="top" align="center">0.015&#x002A;&#x002A;<break/>0.003&#x002A;&#x002A;<break/>0.002&#x002A;&#x002A;</td>
<td valign="top" align="center">16,958.32<break/>22,257.35<break/>27,174.40</td>
<td valign="top" align="center">&#x2212;2.575<break/>&#x2212;3.281<break/>&#x2212;3.350</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="table-fn1"><p>&#x002A;<italic>P</italic> &#x003C; 0.05, &#x002A;&#x002A;<italic>P</italic> &#x003C; 0.01, &#x002A;&#x002A;&#x002A;<italic>P</italic> &#x003C; 0.001.</p></fn>
</table-wrap-foot>
</table-wrap>
<p>After the audiovisual interaction test (first 30-s video) of the different hydrodynamic landscapes, the mean values of the theta, alpha, and beta waves are observed to increase greatly. The three paired <italic>t</italic>-test results exhibit significant differences (<italic>P</italic>&#x2009;&#x003C;<sans-serif>&#x2009;0</sans-serif>.05) between the baseline data and the experimental theta, alpha, and beta wave values for the three landscape tests. Moreover, the mean values of the three waves peak during the high hydrodynamic landscape (waterfall) test. However, no significant differences are observed in the corresponding ANOVA results (<xref ref-type="table" rid="T3">Table&#x00A0;3</xref>).</p>
<table-wrap id="T3" position="float"><label>Table 3</label>
<caption><p>Inter-group comparison of brain waves for the first 30&#x2005;s of the audiovisual interaction of different hydrodynamic landscapes (water sound&#x2009;&#x002B;&#x2009;no bird songs).</p></caption>
<table frame="hsides" rules="groups">
<colgroup>
<col align="left"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
</colgroup>
<thead>
<tr>
<th valign="top" align="left">Brainwave</th>
<th valign="top" align="center">Baseline value</th>
<th valign="top" align="center">Low hydrodynamic landscape (Haizi)</th>
<th valign="top" align="center">Medium hydrodynamic landscape (combined landscape)</th>
<th valign="top" align="center">High hydrodynamic landscape (waterfall)</th>
<th valign="top" align="center"><italic>P</italic>-value</th>
<th valign="top" align="center">Difference value</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">Theta wave</td>
<td valign="top" align="center">147,320.65</td>
<td valign="top" align="center">230,030.91</td>
<td valign="top" align="center">231,558.95</td>
<td valign="top" align="center">239,302.67</td>
<td valign="top" align="center">0.001&#x002A;&#x002A;<break/>0.000&#x002A;&#x002A;&#x002A;<break/>0.000&#x002A;&#x002A;&#x002A;</td>
<td valign="top" align="center">82,710.26<break/>84,238.30<break/>91,982.02</td>
</tr>
<tr>
<td valign="top" align="left">Alpha wave</td>
<td valign="top" align="center">66,314.41</td>
<td valign="top" align="center">108,476.33</td>
<td valign="top" align="center">106,088.06</td>
<td valign="top" align="center">108,970.82</td>
<td valign="top" align="center">0.004&#x002A;&#x002A;<break/>0.000&#x002A;&#x002A;&#x002A;<break/>0.000&#x002A;&#x002A;&#x002A;</td>
<td valign="top" align="center">42,161.92<break/>39,773.65<break/>42,656.41</td>
</tr>
<tr>
<td valign="top" align="left">Beta wave</td>
<td valign="top" align="center">46,391.11</td>
<td valign="top" align="center">67,237.53</td>
<td valign="top" align="center">67,611.53</td>
<td valign="top" align="center">67,863.10</td>
<td valign="top" align="center">0.035&#x002A;<break/>0.014&#x002A;<break/>0.017&#x002A;</td>
<td valign="top" align="center">20,846.42<break/>21,220.42<break/>21,471.99</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="table-fn2"><p>&#x002A;<italic>P</italic> &#x003C; 0.05, &#x002A;&#x002A;<italic>P</italic> &#x003C; 0.01, &#x002A;&#x002A;&#x002A;<italic>P</italic> &#x003C; 0.001.</p></fn>
</table-wrap-foot>
</table-wrap>
<p>The theta waves are observed to increase greatly for the second part of the audiovisual interaction test (second 30-s video) of the different hydrodynamic landscapes. The paired <italic>t</italic>-test results indicate significant differences (<italic>P</italic>&#x2009;&#x003C;<sans-serif>&#x2009;0</sans-serif>.05) between the baseline and experimental theta and alpha values for the three landscape tests, as well as between baseline and experimental beta wave values for the waterfall and combined landscape test. No significant differences are observed for Haizi. The mean values of the three waves also peak during the high hydrodynamic landscape (waterfall) test. Furthermore, there are no significant differences in the theta, alpha, and beta wave values for the three landscape tests (<xref ref-type="table" rid="T4">Table&#x00A0;4</xref>).</p>
<table-wrap id="T4" position="float"><label>Table 4</label>
<caption><p>Inter-group comparison of brain waves after 30&#x2005;s of the audiovisual interaction of different hydrodynamic landscapes (water sounds&#x2009;&#x002B;&#x2009;bird songs).</p></caption>
<table frame="hsides" rules="groups">
<colgroup>
<col align="left"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
</colgroup>
<thead>
<tr>
<th valign="top" align="left">Brainwave</th>
<th valign="top" align="center">Baseline value</th>
<th valign="top" align="center">Low hydrodynamic landscape (Haizi)</th>
<th valign="top" align="center">Medium hydrodynamic landscape (combined landscape)</th>
<th valign="top" align="center">High hydrodynamic landscape (waterfall)</th>
<th valign="top" align="center"><italic>P</italic>-value</th>
<th valign="top" align="center">Difference value</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">Theta wave</td>
<td valign="top" align="center">165,537.88</td>
<td valign="top" align="center">235,393.09</td>
<td valign="top" align="center">254,337.27</td>
<td valign="top" align="center">286,215.12</td>
<td valign="top" align="center">0.006&#x002A;&#x002A;<break/>0.000&#x002A;&#x002A;&#x002A;<break/>0.000&#x002A;&#x002A;&#x002A;</td>
<td valign="top" align="center">69,855.21<break/>88,799.39<break/>120,677.24</td>
</tr>
<tr>
<td valign="top" align="left">Alpha wave</td>
<td valign="top" align="center">67,127.84</td>
<td valign="top" align="center">94,163.88</td>
<td valign="top" align="center">113,218.19</td>
<td valign="top" align="center">123,892.73</td>
<td valign="top" align="center">0.011&#x002A;<break/>0.001&#x002A;&#x002A;<break/>0.000&#x002A;&#x002A;&#x002A;</td>
<td valign="top" align="center">27,036.04<break/>46,090.35<break/>56,764.89</td>
</tr>
<tr>
<td valign="top" align="left">Beta wave</td>
<td valign="top" align="center">45,523.56</td>
<td valign="top" align="center">58,593.78</td>
<td valign="top" align="center">68,817.85</td>
<td valign="top" align="center">78,400.39</td>
<td valign="top" align="center">0.093<break/>0.004&#x002A;&#x002A;<break/>0.001</td>
<td valign="top" align="center">13,070.22<break/>23,294.29<break/>32,876.83</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="table-fn3"><p>&#x002A;<italic>P</italic> &#x003C; 0.05, &#x002A;&#x002A;<italic>P</italic> &#x003C; 0.01, &#x002A;&#x002A;&#x002A;<italic>P</italic> &#x003C; 0.001.</p></fn>
</table-wrap-foot>
</table-wrap>
<p>Comparing the mean values of the theta, alpha, and beta waves between the first and second 30-s tests indicate that the values of the three waves in the Haizi test decrease after the addition of the bird songs, and increase in the waterfall and combined landscape tests (<xref ref-type="table" rid="T3">Tables&#x00A0;3</xref>, <xref ref-type="table" rid="T4">4</xref>).</p>
<p>In the tests focusing solely on the visual perception of Haizi, significant increases are observed in the mean values of the theta, alpha, and beta waves across the four Haizi landscapes (Mirror Lake, Wucaichi, Luwei Lake, and Wuhua Lake). Wucaichi exhibits the highest theta wave value, while the alpha and beta waves peak for Luwei Lake and Jing Hai, respectively. Paired <italic>t</italic>-test results reveal notable differences (<italic>P</italic>&#x2009;&#x003C;<sans-serif>&#x2009;0</sans-serif>.05) between the data in the baseline and experimental states for the three waves across the four Haizi landscapes. In contrast, the ANOVA results indicate no significant differences in theta, alpha, and beta waves among the four Haizi landscapes (<xref ref-type="table" rid="T5">Table&#x00A0;5</xref>).</p>
<table-wrap id="T5" position="float"><label>Table 5</label>
<caption><p>Brainwave responses to the pure visuals of haizi.</p></caption>
<table frame="hsides" rules="groups">
<colgroup>
<col align="left"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
</colgroup>
<thead>
<tr>
<th valign="top" align="left">Brainwave</th>
<th valign="top" align="center">Baseline value</th>
<th valign="top" align="center">Mirror Lake</th>
<th valign="top" align="center">Wucaichi</th>
<th valign="top" align="center">Luwei Lake</th>
<th valign="top" align="center">Wuhua Lake</th>
<th valign="top" align="center"><italic>P</italic>-value</th>
<th valign="top" align="center"><italic>T</italic>-value</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">Theta wave</td>
<td valign="top" align="center">127,432.8</td>
<td valign="top" align="center">235,020.6</td>
<td valign="top" align="center">242,362.22</td>
<td valign="top" align="center">235,035.89</td>
<td valign="top" align="center">230,796.22</td>
<td valign="top" align="center">0.000&#x002A;&#x002A;&#x002A;/0.001&#x002A;&#x002A;/<break/>0.006&#x002A;&#x002A;/0.003&#x002A;&#x002A;</td>
<td valign="top" align="center">&#x2212;3.996/&#x2212;3.790/<break/>&#x2212;2.978/&#x2212;3.191</td>
</tr>
<tr>
<td valign="top" align="left">Alpha wave</td>
<td valign="top" align="center">54,443.33</td>
<td valign="top" align="center">103,737.03</td>
<td valign="top" align="center">102,145.62</td>
<td valign="top" align="center">105,107.84</td>
<td valign="top" align="center">101,667.2</td>
<td valign="top" align="center">0.000&#x002A;&#x002A;&#x002A;/0.001&#x002A;&#x002A;/<break/>0.003&#x002A;&#x002A;/0.004&#x002A;&#x002A;</td>
<td valign="top" align="center">&#x2212;4.256/&#x2212;3.570/<break/>&#x2212;3.173/&#x2212;3.084</td>
</tr>
<tr>
<td valign="top" align="left">Beta wave</td>
<td valign="top" align="center">34,072.56</td>
<td valign="top" align="center">65,287.99</td>
<td valign="top" align="center">62,511.67</td>
<td valign="top" align="center">63,136.4</td>
<td valign="top" align="center">63,609.38</td>
<td valign="top" align="center">0.005&#x002A;&#x002A;/0.014&#x002A;/<break/>0.008&#x002A;&#x002A;/0.019&#x002A;</td>
<td valign="top" align="center">&#x2212;3.042/&#x2212;2.591/<break/>&#x2212;2.849/&#x2212;2.481</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="table-fn4"><p>&#x002A;<italic>P</italic> &#x003C; 0.05, &#x002A;&#x002A;<italic>P</italic> &#x003C; 0.01, &#x002A;&#x002A;&#x002A;<italic>P</italic> &#x003C; 0.001.</p></fn>
</table-wrap-foot>
</table-wrap>
<p>According to the physiological data, all low hydrodynamic landscapes exhibit significant physiological restorative effects under pure visual conditions, with no significant differences observed in physiological restorativeness among the four Haizi landscapes. The highest values of theta, alpha, and beta brain waves are found in different Haizi. This may be attributed to both the similarities and partial differences in the features and elements of the waterscape environment of Haizi.</p>
</sec>
</sec>
<sec id="s3b"><label>3.2</label><title>Subjective recovery data</title>
<p>According to the mean test value and standard deviation of the PRS, the different hydrodynamic landscapes can be ranked in terms of their restorative effects as follows (in descending order): combined landscape (Shuzheng Lakes), Haizi (Mirror Lake), and waterfall landscape (Nuorilang Waterfall). The combined landscape (Shuzheng Lakes) ranks number 1 in terms of Distance, Compatibility, and Extension. The top-ranking landscape in Charmingness is Haizi (Mirror Lake).The Haizi landscapes are ranked in terms of their restorative effects as follows (in descending order): Charmingness, Extension, Distance, and Compatibility (<xref ref-type="fig" rid="F6">Figure&#x00A0;6</xref>).</p>
<fig id="F6" position="float"><label>Figure 6</label>
<caption><p>Audiovisual interaction of PRS in different hydrodynamic landscapes. Validation was performed by paired <italic>T</italic>-tests. Data is expressed as mean&#x2009;&#x00B1;&#x2009;standard deviation. <italic>n</italic>&#x2009;&#x003D;&#x2009;64; &#x002A;<italic>P&#x2009;&#x003C;</italic>&#x2009;0.05; &#x002A;&#x002A;<italic>P&#x2009;&#x003C;</italic>&#x2009;0.01.</p></caption>
<graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="frcha-04-1506392-g006.tif"/>
</fig>
<p><xref ref-type="fig" rid="F6">Figure&#x00A0;6</xref> indicates that the Charmingness of the pure visuals of Haizi is significantly higher than that of distance and extensibility. Under audiovisual interaction, Haizi emerges as the most attractive landscape, with its overall psychological restorativeness ranking second, surpassing even that of the waterfall. Based on these findings, low hydrodynamic landscapes (Haizi) exhibit greater restorativeness and more abundant spatial elements, particularly biological habitats, compared to medium and high hydrodynamic landscapes. For low hydrodynamic landscapes, intense visual stimulation may bring about far greater restorativeness than sounds in the environment. Consequently, the low hydrodynamic Haizi landscapes, characterized by minimal disturbance of auditory stimulation, are selected to analyze the restorativeness of the landscape components, characteristics, and elements under pure visuals. This exploration aims to determine whether there exists a hydrodynamic landscape with optimal visual psychological restorativeness for youth within the Jiuzhaigou World Natural Heritage Site.</p>
</sec>
<sec id="s3c"><label>3.3</label><title>Multivariate linear regression analysis of the perceived restorativeness scale (PRS) of low hydrodynamic landscapes (Haizi)</title>
<sec id="s3c1"><label>3.3.1</label><title>Overall restorativeness of the components of Haizi</title>
<p><xref ref-type="table" rid="T6">Table&#x00A0;6</xref> reveals that all values of the four components are positive, with the plant and animal characteristics exhibiting the highest value (<italic>B</italic>&#x2009;&#x003D;&#x2009;0.362, <italic>P</italic>&#x2009;&#x003C;&#x2009;0.05). The overall restorativeness of Haizi can be calculated as &#x2212;0.044&#x2009;&#x002B;&#x2009;0.271&#x2009;&#x00D7;&#x2009;[water characteristics]&#x2009;&#x002B;&#x2009;0.362&#x2009;&#x00D7;&#x2009;[plant and animal characteristics]&#x2009;&#x002B;&#x2009;0.213&#x2009;&#x00D7;&#x2009;[water environment]&#x2009;&#x002B;&#x2009;0.202&#x2009;&#x00D7;&#x2009;[plant and animal environment]. The components of Haizi that contribute positively to overall restorativeness include animal and plant characteristics, water characteristics, water environments, and animal and plant environments, with animal and plant characteristics having the most significant influence on restorativeness. The other three components have similar effects (<xref ref-type="table" rid="T6">Table&#x00A0;6</xref>).</p>
<table-wrap id="T6" position="float"><label>Table 6</label>
<caption><p>Multiple linear regression analysis of the overall restorativeness regarding components of Haizi.</p></caption>
<table frame="hsides" rules="groups">
<colgroup>
<col align="left"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
</colgroup>
<thead>
<tr>
<th valign="top" align="left" rowspan="2">Model</th>
<th valign="top" align="center" colspan="2">Non-standard coefficient</th>
<th valign="top" align="center">Standard coefficient</th>
<th valign="top" align="center" rowspan="2"><italic>T</italic>-value</th>
<th valign="top" align="center" rowspan="2"><italic>P</italic>-value</th>
<th valign="top" align="center" colspan="2">95.0&#x0025; confidence interval for beta</th>
<th valign="top" align="center" colspan="2">Collinear statistics</th>
<th valign="top" align="center" rowspan="2"><italic>R</italic>&#x00B2;</th>
<th valign="top" align="center" rowspan="2">Adjusted <italic>R</italic>&#x00B2;</th>
</tr>
<tr>
<th valign="top" align="left">B</th>
<th valign="top" align="center">Standard error</th>
<th valign="top" align="center">Beta</th>
<th valign="top" align="center">Minimum value</th>
<th valign="top" align="center">Maximum value</th>
<th valign="top" align="center">Tolerance</th>
<th valign="top" align="center">VIF</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">(Constant)</td>
<td valign="top" align="center">&#x2212;.044</td>
<td valign="top" align="center">.758</td>
<td valign="top" align="center"/>
<td valign="top" align="center">&#x2212;.059</td>
<td valign="top" align="center">.954</td>
<td valign="top" align="center">&#x2212;1.610</td>
<td valign="top" align="center">1.521</td>
<td valign="top" align="center"/>
<td valign="top" align="center"/>
<td valign="top" align="center" rowspan="5">.776</td>
<td valign="top" align="center" rowspan="5">.738</td>
</tr>
<tr>
<td valign="top" align="left">Water characteristics</td>
<td valign="top" align="center">.271</td>
<td valign="top" align="center">.133</td>
<td valign="top" align="center">.233</td>
<td valign="top" align="center">2.048</td>
<td valign="top" align="center">.052</td>
<td valign="top" align="center">&#x2212;.002</td>
<td valign="top" align="center">.545</td>
<td valign="top" align="center">.724</td>
<td valign="top" align="center">1.382</td>
</tr>
<tr>
<td valign="top" align="left">Plant and animal characteristics</td>
<td valign="top" align="center">.362</td>
<td valign="top" align="center">.101</td>
<td valign="top" align="center">.479</td>
<td valign="top" align="center">3.571</td>
<td valign="top" align="center">.002&#x002A;&#x002A;</td>
<td valign="top" align="center">.153</td>
<td valign="top" align="center">.571</td>
<td valign="top" align="center">.520</td>
<td valign="top" align="center">1.924</td>
</tr>
<tr>
<td valign="top" align="left">Water environments</td>
<td valign="top" align="center">.213</td>
<td valign="top" align="center">.112</td>
<td valign="top" align="center">.214</td>
<td valign="top" align="center">1.911</td>
<td valign="top" align="center">.068</td>
<td valign="top" align="center">&#x2212;.017</td>
<td valign="top" align="center">.444</td>
<td valign="top" align="center">.745</td>
<td valign="top" align="center">1.341</td>
</tr>
<tr>
<td valign="top" align="left">Plant and animal environments</td>
<td valign="top" align="center">.202</td>
<td valign="top" align="center">.103</td>
<td valign="top" align="center">.272</td>
<td valign="top" align="center">1.949</td>
<td valign="top" align="center">.063</td>
<td valign="top" align="center">&#x2212;.012</td>
<td valign="top" align="center">.415</td>
<td valign="top" align="center">.480</td>
<td valign="top" align="center">2.082</td>
</tr>
<tr>
<td valign="top" align="left" colspan="12">Implicit variable: overall restorativeness of the Haizi components</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="table-fn5"><p>&#x002A;<italic>P</italic> &#x003C; 0.05, &#x002A;&#x002A;<italic>P</italic> &#x003C; 0.01, &#x002A;&#x002A;&#x002A;<italic>P</italic> &#x003C; 0.001.</p></fn>
</table-wrap-foot>
</table-wrap>
</sec>
<sec id="s3c2"><label>3.3.2</label><title>Restorativeness of water characteristics</title>
<p><xref ref-type="table" rid="A1">Appendix Table 7</xref> shows that all the water characteristic non-standard coefficient values are positive, with perceived depth exhibiting the highest value (<italic>B</italic>&#x2009;&#x003D;&#x2009;0.240, <italic>P</italic>&#x2009;&#x003C;&#x2009;0.05). The restorativeness of water characteristics can be calculated as 1.978&#x2009;&#x002B;&#x2009;0.046&#x2009;&#x00D7;&#x2009;[clearness]&#x2009;&#x002B;&#x2009;0.240&#x2009;&#x00D7;&#x2009;[perceived depth]&#x2009;&#x002B;&#x2009;0.178&#x2009;&#x00D7;&#x2009;[openness]&#x2009;&#x002B;&#x2009;0.084&#x2009;&#x00D7;&#x2009;[surface complexity]&#x2009;&#x002B;&#x2009;0.144&#x2009;&#x00D7;&#x2009;[color richness]. The characteristics that contribute to restorativeness include water transparency, perceived depth, openness, surface complexity, and color richness, with perceived depth having the greatest effect (<xref ref-type="table" rid="A1">Appendix Table 7</xref>).</p>
</sec>
<sec id="s3c3"><label>3.3.3</label><title>Restorativeness of plant and animal characteristics</title>
<p><xref ref-type="table" rid="A2">Appendix Table 8</xref> indicates the plant color richness value to be negative (<italic>B</italic>&#x2009;&#x003D;&#x2009;&#x2212;0.163, <italic>P</italic>&#x2009;&#x003E;&#x2009;0.05), while the other values are positive. Plant density and plant level richness exhibit the highest values (<italic>B</italic>&#x2009;&#x003D;&#x2009;0.419, 0.416, <italic>P</italic>&#x2009;&#x003C;&#x2009;0.05). The restorativeness of the plant and animal characteristics can be calculated as 0.934&#x2009;&#x002B;&#x2009;0.419&#x2009;&#x00D7;&#x2009;[plant density&#x2009;&#x002B;&#x2009;0.416]&#x2009;&#x00D7;&#x2009;[plant level richness]&#x2009;&#x002B;&#x2009;&#x2212;0.163&#x2009;&#x00D7;&#x2009;[plant color richness]&#x2009;&#x002B;&#x2009;0.091&#x2009;&#x00D7;&#x2009;plant form richness. Plant form richness, plant density, and plant level richness exhibit positive restorativeness, with the latter two exerting the greatest effects, while plant color richness has a negative restorative effect (<xref ref-type="table" rid="A2">Appendix Table 8</xref>).</p>
</sec>
<sec id="s3c4"><label>3.3.4</label><title>Restorativeness of water environments</title>
<p><xref ref-type="table" rid="A3">Appendix Table 9</xref> indicates that watercolor, waterfront elements, water shape, and reflection have positive effects on restorativeness, with watercolor and reflection exerting the strongest influence. In contrast, the component individual scene has a negative effect (<xref ref-type="table" rid="A3">Appendix Table 9</xref>). The restorativeness of the water environment can be calculated as 0.739&#x2009;&#x002B;&#x2009;0.348&#x2009;&#x00D7;&#x2009;[water color]&#x2009;&#x002B;&#x2009;0.347&#x2009;&#x00D7;&#x2009;[waterfront elements]&#x2009;&#x002B;&#x2009;0.052&#x2009;&#x00D7;&#x2009;[water shape]&#x2009;&#x002B; 0.373&#x2009;&#x00D7;&#x2009;[water reflection]&#x2009;&#x002B;&#x2009;&#x2212;0.219&#x2009;&#x00D7;&#x2009;[individual scene].</p>
<p>Further analysis was conducted on the components of water reflection, watercolor, and individual scenes. In terms of the water reflection components, <xref ref-type="table" rid="A4">Appendix Table 10</xref> shows that clouds have the most significant effect on restorativeness (<italic>B</italic>&#x2009;&#x003D;&#x2009;0.435, <italic>P</italic>&#x2009;&#x003C;&#x2009;0.05), while plants on the water have a negative effect (Beta&#x2009;&#x003D;&#x2009;&#x2212;0.023, <italic>P</italic>&#x2009;&#x003E;&#x2009;0.05). The restorativeness of water reflection can be calculated as 1.101&#x2009;&#x002B;&#x2009;&#x2212;0.023&#x2009;&#x00D7;&#x2009;[plants on the water]&#x2009;&#x002B;&#x2009;0.219&#x2009;&#x00D7;&#x2009;[waterfront plants]&#x2009;&#x002B;&#x2009;0.453&#x2009;&#x00D7;&#x2009;[clouds&#x2009;&#x002B;&#x2009;0.201]&#x2009;&#x00D7;&#x2009;mountains (<xref ref-type="table" rid="A4">Appendix Table 10</xref>). The watercolor components are observed to have a positive effect, with green having the greatest effect (<italic>B</italic>&#x2009;&#x003D;&#x2009;0.306, <italic>P</italic>&#x2009;&#x003C;&#x2009;0.05) (<xref ref-type="table" rid="A5">Appendix Table 11</xref>). The restorativeness of watercolor can be determined as 2.238&#x2009;&#x002B;&#x2009;0.222&#x2009;&#x00D7;&#x2009;[mainly blue]&#x2009;&#x002B;&#x2009;0.306&#x2009;&#x00D7;&#x2009;[mainly green]&#x2009;&#x002B;&#x2009;0.154&#x2009;&#x00D7;&#x2009;[mainly yellow]. Among the individual scene components, plank roads over water exert the greatest negative effect (<italic>B</italic>&#x2009;&#x003D;&#x2009;0.381, <italic>P</italic>&#x2009;&#x003C;&#x2009;0.05) (<xref ref-type="table" rid="A6">Appendix Table 12</xref>). Note that the values in <xref ref-type="table" rid="A6">Appendix Table 12</xref> indicate negative impacts of the individual scene components, and the higher the value, the greater the negative impact. The negative impact of the individual scene components is calculated as1.369&#x2009;&#x002B;&#x2009;0.236&#x2009;&#x00D7;&#x2009;[plank roads by the shore]&#x2009;&#x002B;&#x2009;0.381&#x2009;&#x00D7;&#x2009;[plank roads over water]&#x2009;&#x002B;&#x2009;0.065&#x2009;&#x00D7;&#x2009;[viewing platform with guardrails]&#x2009;&#x002B;&#x2009;0.051&#x00D7; [fallen trees in the water].</p>
<p>Analysis of the restorativeness of the plant and animal environments shows that both animal and plant species exert positive (and similar) effects (<italic>B</italic>&#x2009;&#x003D;&#x2009;0.547, 0.543, <italic>P</italic>&#x2009;&#x003C;&#x2009;0.05). The restorativeness of plant and animal environments can be calculated as &#x2212;0.674&#x2009;&#x002B;&#x2009;0.543&#x2009;&#x00D7;&#x2009;[plant species]&#x2009;&#x002B;&#x2009;0.547&#x2009;&#x00D7;&#x2009;[animal species] (<xref ref-type="table" rid="A7">Appendix Table 13</xref>). Through further analysis, it is revealed that submerged plants, emergent plants, wetland shrubs, and wetland trees have significant positive effects, with wetland shrubs exerting the strongest influence (<italic>B</italic>&#x2009;&#x003D;&#x2009;0.373, <italic>P</italic>&#x2009;&#x003C;&#x2009;0.05). The restorativeness of plant species can be calculated as 0.435&#x2009;&#x002B;&#x2009;0.044&#x2009;&#x00D7;&#x2009;[submerged plants]&#x2009;&#x002B;&#x2009;0.212&#x2009;&#x00D7;&#x2009;[emergent plants]&#x2009;&#x002B;&#x2009;0.373&#x2009;&#x00D7;&#x2009;[wetland shrubs]&#x2009;&#x002B;&#x2009;0.352&#x2009;&#x00D7;&#x2009;[wetland trees] (<xref ref-type="table" rid="A8">Appendix Table 14</xref>). Terrestrial and fish are observed to have remarkable effects on restorativeness, with terrestrial demonstrating the most significant influence (<italic>B</italic>&#x2009;&#x003D;&#x2009;0.455, <italic>P</italic>&#x2009;&#x003C;&#x2009;0.05). The restorativeness of animal species can be calculated as 0.760&#x2009;&#x002B;&#x2009;0.455&#x2009;&#x00D7;&#x2009;[terrestrial]&#x2009;&#x002B;&#x2009;0.433&#x2009;&#x00D7;&#x2009;[fish] (<xref ref-type="table" rid="A9">Appendix Table 15</xref>).</p>
</sec>
</sec>
</sec>
<sec id="s4" sec-type="discussion"><label>4</label><title>Discussion</title>
<sec id="s4a"><label>4.1</label><title>Physiological restorativeness of different hydrodynamic landscapes under audiovisual interaction</title>
<p>The above analysis indicates that all the hydrodynamic landscapes exhibit significant restorative effects under audiovisual interaction, regardless of whether there are bird songs or not. However, the differences between groups are not statistically significant. Notably, the highest values of theta, alpha, and beta brain waves consistently appear in waterfalls, indicating that high hydrodynamic landscapes (waterfalls) generally offer the greatest physiological restorativeness. In terms of audiovisually-perceived restorative effects of bird songs, the landscapes rank as follows (in descending order): high hydrodynamic landscape (waterfall), medium hydrodynamic landscape (combined landscape), and low hydrodynamic landscape (Haizi). Moreover, there is a linearly positive correlation between physiological restorativeness and hydrodynamic landscapes. Bird song represents one of nature&#x0027;s restorative sound sources, evoking associations with highly biodiverse environments and vitality (<xref ref-type="bibr" rid="B30">30</xref>, <xref ref-type="bibr" rid="B31">31</xref>), enhancing landscape experiences (<xref ref-type="bibr" rid="B32">32</xref>), and improving the overall impression and satisfaction with Jiuzhaigou&#x0027;s water environment (<xref ref-type="bibr" rid="B33">33</xref>). Hydrodynamic landscapes influence people&#x0027;s perception of bird songs. Higher-level hydrodynamic landscapes do not diminish the perception of bird song, rather they enrich and optimize the spatial ecological niche to some extent, resulting in a certain degree of soundscape richness. Compared to the rapid and orderly sounds of falling water as a background sound, the rich and varied bird songs are highly distinguishable (<xref ref-type="bibr" rid="B34">34</xref>). Therefore, when bird songs are added to the continuous water sounds of waterfalls and combined landscapes with high and medium hydrodynamic intensities, listeners are provided with a richer and more pleasant rhythm experience, enhancing their restorative experience in the soundscapes. Pleasant sounds added to a space can greatly enhance acoustic comfort, even if the original sound source is loud (<xref ref-type="bibr" rid="B35">35</xref>). Despite the addition of bird songs, the physiological restorativeness of Haizi remains weaker than that of waterfalls and combined landscapes, with its own restorativeness exhibiting a declining trend. Haizi features rich spatial elements, particularly biological habitats, and the reception and processing of visually perceived information are markedly intense. The contribution of bird songs to auditory stimulation is relatively weaker compared to that of visual simulation.</p>
</sec>
<sec id="s4b"><label>4.2</label><title>Physiological restorativeness of different hydrodynamic landscapes under pure visuals</title>
<p>According to the physiological brain waves data, distinctions in the restorativeness of various hydrodynamic landscapes persist between audiovisual interaction and purely visual experiences under pure visuals, all low hydrodynamic landscapes exhibit significant physiological restorative effects, with no significant differences observed in the physiological restorativeness among the four Haizi landscapes. The highest theta, alpha, and beta brain wave values vary across different Haizi. This may be attributed to similarities and partial differences in the features and elements of the waterscape environment. Compared to high and medium hydrodynamic landscapes, low hydrodynamic landscapes boast more abundant spatial elements, particularly biological habitats. The contribution of visually stimulating elements to psychological restorativeness may outweigh that of auditory stimulation, with visuals remaining the primary sensory input.</p>
</sec>
<sec id="s4c"><label>4.3</label><title>Psychological restorativeness of different hydrodynamic landscapes</title>
<p>According to the data of PRS (<xref ref-type="fig" rid="F6">Figure&#x00A0;6</xref>), we reveal that the Charmingness perceived in the pure visuals of Haizi significantly surpasses that of Distance and Extension. Under audiovisual interaction, Haizi emerges as the most attractive landscape, ranking second in overall psychological restorativeness, surpassing waterfalls. This suggests an inconsistency between physiological and psychological restorative effects, with the latter displaying a nonlinear relationship with hydrodynamic landscapes. When the visual features of waterscapes are prominently displayed, the perception of water sound loudness tends to decrease (<xref ref-type="bibr" rid="B36">36</xref>). In addition, Distance, Extension, Compatibility, and the overall perceptual restorativeness ratings of combined landscapes with medium hydrodynamic landscapes rank highest. These landscapes also exhibit the highest psychological restorative effects on youth, with physiological restorativeness following closely behind. This may be attributed to the abundance of visual stimuli, particularly the aesthetic beauty of water flow lines. In high hydrodynamic waterscapes, where visual stimulation is relatively scarce, the influence of water sounds and birdsongs on restorativeness may be decisive. Sounds can convey subjective emotions that visuals cannot express and can compensate for limitations resulting from reduced visuals (<xref ref-type="bibr" rid="B37">37</xref>). This aligns with the results presented by Evensen et al. (<xref ref-type="bibr" rid="B38">38</xref>), indicating that positive soundscapes can significantly improve psychological states and induce happiness when visual factors are disregarded in perception.</p>
</sec>
<sec id="s4d"><label>4.4</label><title>Pure visually-perceived restorativeness of low hydrodynamic landscapes (Haizi)</title>
<sec id="s4d1"><label>4.4.1</label><title>Restorativeness of the components of low hydrodynamic landscapes (Haizi)</title>
<p>The components of low hydrodynamic landscapes (Haizi) in Jiuzhaigou (animal and plant characteristics, water characteristics, water environment, and animal and plant environment) have a positive impact on restorativeness, with animal and plant characteristics exerting the most significant impact. In a comparison of the restorativeness between single-form natural visual elements, Ulrich et al. (<xref ref-type="bibr" rid="B39">39</xref>) found that water elements have more positive effects in terms of emotion regulation compared to vegetation elements. Low hydrodynamic landscapes (Haizi) in Jiuzhaigou are natural spaces containing rich flora and fauna and large areas of water. Plants and water can enhance mental restorativeness (<xref ref-type="bibr" rid="B40">40</xref>) as they can provide a comfortable environment by improving the microclimate, thus positively impacting the restorativeness of human health (<xref ref-type="bibr" rid="B41">41</xref>, <xref ref-type="bibr" rid="B42">42</xref>). Our results revealed that for low hydrodynamic landscapes (Haizi) with abundant vegetation and large-area water elements, the restorative effects of animals and plants are greater than those of water bodies. In nature, water cannot exist independently from other features, such as plants and animals. Therefore, even spaces with water as the main landscape type have differences in waterscape vision due to distinct near- and distant-view backgrounds, including color composition (<xref ref-type="bibr" rid="B43">43</xref>). Plants and wildlife associated with water can strongly affect individuals&#x0027; positive cognition of water spaces (<xref ref-type="bibr" rid="B44">44</xref>), with viewers feeling a sense of belonging and attachment (<xref ref-type="bibr" rid="B45">45</xref>, <xref ref-type="bibr" rid="B46">46</xref>), thus enhancing the attractiveness of water landscapes (<xref ref-type="bibr" rid="B47">47</xref>). This is in line with the Biophilia Hypothesis, which holds that humans have an inherent tendency to get close to and love natural life (plants and animals) during the long-term evolution process. This tendency is related to survival instinct. Environments with a great diversity of plants and animals by water (e.g., trees, shrubs, flowers, butterflies, and birds) have a higher level of biodiversity, which can reduce mental stress and improve the environmental restorative effects (<xref ref-type="bibr" rid="B48">48</xref>). Jiuzhaigou, a World Natural Heritage Site, is renowned for its rich biodiversity and the presence of rare species (<xref ref-type="bibr" rid="B49">49</xref>). The low hydrodynamic landscapes (Haizi) in Jiuzhaigou boast abundant animal and plant resources, a diverse ecosystem, and a superior natural environment, all of which contribute significantly to the restoration of youth with high stress levels.</p>
</sec>
<sec id="s4d2"><label>4.4.2</label><title>Restorativeness of the characteristics of low hydrodynamic landscapes (Haizi)</title>
<p>The perceived depth and openness of water, as well as the density and level richness of plants, have positive effects on landscape restorativeness. In contrast, plant color richness is considered to have a negative effect on landscape restorativeness. Acquired knowledge and experience play an important role in people&#x0027;s understanding of the environment (<xref ref-type="bibr" rid="B50">50</xref>). When people can clearly perceive the depth of water, they can then determine the danger level of the water body and whether it is suitable for recreation (<xref ref-type="bibr" rid="B51">51</xref>). An open space is likely to provide a sense of security and control due to a wide view (<xref ref-type="bibr" rid="B52">52</xref>), which is in line with the need for viewing and sheltering (<xref ref-type="bibr" rid="B53">53</xref>). Environments with a wider view and less sheltering induce greater restorativeness than suburban park environments with a narrower view and more sheltering (<xref ref-type="bibr" rid="B54">54</xref>). Furthermore, the more visible trees, the greater the restorativeness (<xref ref-type="bibr" rid="B40">40</xref>). The density of green plants and the richness of plant layers are both related to the number of plants. Both high-density vegetation and richly layered plant communities can attract attention and evoke positive emotions (<xref ref-type="bibr" rid="B55">55</xref>). Our study finds that the higher the perceived plant color richness in space, the lower its perceptual restorative effects. This may be because lower plant color richness makes it easier to create harmonious spatial colors that do not induce a sense of disorder (<xref ref-type="bibr" rid="B56">56</xref>). It also facilitates improved coordination of plants with the surrounding features, resulting in a more orderly environment that aids in reducing the need for directed attention and promotes relaxation in both physiological and psychological states. Consequently, plant color serves as a crucial indicator in enhancing public mental health (<xref ref-type="bibr" rid="B57">57</xref>).</p>
</sec>
<sec id="s4d3"><label>4.4.3</label><title>Restorativeness of environmental elements in low hydrodynamic landscapes (Haizi)</title>
<p>As a component of water reflection, clouds have a significant impact on restorativeness. Reflection in water is the embodiment of symmetrical beauty and form, placing minimal strain on the eyes of viewers. The comfortable and labor-saving perceptual experience can bring viewers pleasure. Moreover, due to the balanced rhythm among symmetrical objects, viewers can get a sense of order as well as a feeling of control during the perceptual experience. The pursuit of beauty in form by humans is based on a sense of order and security, which is also the most fundamental aesthetic consciousness of humans (<xref ref-type="bibr" rid="B58">58</xref>). For waterscapes, watercolor is a significant factor affecting the perceptual properties of water. According to neuroaesthetics, the optic nerve responds fastest to color in external stimuli, with responses reported as 30&#x2005;ms faster than those to motion (<xref ref-type="bibr" rid="B59">59</xref>). We identified green water bodies as having a greater perceptual restorativeness for youth. Blue and green are the universal color preferences among people due to genetic codes related to blue skies and green nature in human evolution. In particular, these two colors exert a sensory calming effect (<xref ref-type="bibr" rid="B60">60</xref>).</p>
<p>There is a negative correlation between plank roads over water and restorativeness. When people perceive the environment, they are more inclined to perceive the overall picture. However, plank roads over water destroy the integrity of the visual perception of landscapes for viewers at a distance. In addition, being exposed to remote viewing and becoming a member of the observed objects can reduce individuals&#x0027; sense of security, which goes against humans&#x0027; &#x201C;viewing&#x2013;sheltering&#x201D; needs. Plank roads over water may also impact the microbial environment and living habits of aquatic animals due to the materials and technology used to construct the roads (e.g., unpleasant smells). This may lower the level of biodiversity and even damage the ecological environment, further affecting the restorativeness of water spaces. Therefore, it is necessary to carefully use the facilities of key ecological environments such as the Jiuzhaigou World Natural Heritage Site to protect the long-term ecosystem value.</p>
<p>The species richness of animals and plants is a key indicator of general species richness. Parasympathetic nerve activity is stronger in environments with higher species richness, which can significantly reduce the anxiety level of youth (<xref ref-type="bibr" rid="B61">61</xref>) and improve the restorative effects for introverts (<xref ref-type="bibr" rid="B62">62</xref>). Enhancing the number of plant and animal species can increase human preferences and induce other positive perceptions. The greater the number of plant and animal species, the higher the perceived naturalness (<xref ref-type="bibr" rid="B56">56</xref>, <xref ref-type="bibr" rid="B63">63</xref>). Moreover, planting more vegetation in a space can increase its influence in reducing anxiety (<xref ref-type="bibr" rid="B64">64</xref>). In low hydrodynamic landscapes (Haizi), trees significantly increase people&#x0027;s preference for interacting with nature, effectively enhancing the restorativeness of the environment. Rich plant and animal species provide rich biodiversity and are associated with positive emotional effects, suggesting that higher biodiversity can lead to greater restorativeness and lower physiological stress (<xref ref-type="bibr" rid="B65">65</xref>).</p>
</sec>
</sec>
</sec>
<sec id="s5"><label>5</label><title>Research summary and prospects</title>
<p>This study investigates the restorative effects of different hydrodynamic landscapes in Jiuzhaigou World Natural Heritage Site on youth in terms of audiovisual perception. According to the results, natural blue&#x2013;green spaces with different hydrodynamic intensities are crucial to improving the health and well-being of the population. Moreover, hydrodynamic landscapes have an impact on the restorativeness of human physio-psychological health. In the same environments, different landscape elements of audiovisual perception have different restorative effects. This study identified the differences in the restorativeness of numerous hydrodynamic landscapes in Jiuzhaigou and determined the restorative components, characteristics, and elements of low hydrodynamic landscapes. Despite the progress made, this work is associated with several limitations. For example, the participants in this study were youth from China, yet it is necessary to take into consideration participants from a wider range of social, demographic, occupational, and cultural backgrounds, as well as those with different health conditions. In addition, the experimental material was collected in summer, with no data on the landscapes of the other three seasons. However, the landscapes in Jiuzhaigou vary with the season. Thus, further studies can explore whether the differences in season can induce variations in the psychological restorative effects of hydrodynamic landscapes on youth and other populations. Future work should also focus on the landscape optimization of blue&#x2013;green spaces such as Jiuzhaigou and other World Natural Heritage Sites by fully accounting for the hydrodynamic intensities of waterscapes, audiovisual interaction stimuli, and other aspects to enrich people&#x0027;s perceived experience. Furthermore, landscape elements can be improved through targeted optimization to create landscape spaces that enhance individuals&#x0027; restorative potential, which is conducive to creating a high-quality environment for the tourism industry. It is critical to determine effective measures to protect the natural environment of Jiuzhaigou and to define standards for new constructions that maintain an ecological balance. Pro-environmental behavior should also be advocated among the population, and cognitive attitudes and behavior toward protecting the environment should be encouraged and deepened for individuals.</p>
</sec>
</body>
<back>
<sec id="s6" sec-type="data-availability"><title>Data availability statement</title>
<p>The original contributions presented in the study are included in the article/<xref ref-type="sec" rid="s10">Supplementary Material</xref>, further inquiries can be directed to the corresponding authors.</p>
</sec>
<sec id="s7" sec-type="author-contributions"><title>Author contributions</title>
<p>PZ: Methodology, Project administration, Resources, Writing &#x2013; original draft, Writing &#x2013; review &#x0026; editing. TZ: Methodology, Project administration, Resources, Writing &#x2013; original draft, Writing &#x2013; review &#x0026; editing. ZC: Writing &#x2013; review &#x0026; editing, Methodology. QH: Methodology, Writing &#x2013; review &#x0026; editing, Project administration, Writing &#x2013; original draft. LK: Writing &#x2013; review &#x0026; editing, Data curation. JL: Formal Analysis, Writing &#x2013; review &#x0026; editing. YY: Formal Analysis, Writing &#x2013; review &#x0026; editing. QZ: Methodology, Writing &#x2013; review &#x0026; editing. XW: Data curation, Writing &#x2013; review &#x0026; editing. LH: Writing &#x2013; review &#x0026; editing. MC: Formal Analysis, Writing &#x2013; review &#x0026; editing. XH: Resources, Writing &#x2013; review &#x0026; editing. FZ: Resources, Writing &#x2013; review &#x0026; editing. SC: Writing &#x2013; review &#x0026; editing. XX: Resources, Writing &#x2013; review &#x0026; editing. GW: Formal Analysis, Funding acquisition, Supervision, Writing &#x2013; review &#x0026; editing. XL: Funding acquisition, Resources, Writing &#x2013; review &#x0026; editing.</p>
</sec>
<sec id="s8" sec-type="funding-information"><title>Funding</title>
<p>The author(s) declare financial support was received for the research, authorship, and/or publication of this article. This work was supported by Jiuzhaigou County in 2024 from the Central Finance (N5132252024000109), and Research on the constructing of multi-sensory perception system and its health effects in Jiuzhaigou World Heritage Site under the background of post-epidemic situation (22GJHZ0142).</p>
</sec>
<sec id="s9" 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>
<p>The author(s) declared that they were an editorial board member of Frontiers, at the time of submission. This had no impact on the peer review process and the final decision.</p>
</sec>
<sec id="s11" sec-type="disclaimer"><title>Publisher&#x0027;s note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
</sec>
<sec id="s10" sec-type="supplementary-material"><title>Supplementary material</title>
<p>The Supplementary Material for this article can be found online at: <ext-link ext-link-type="uri" xlink:href="https://www.frontiersin.org/articles/10.3389/frcha.2025.1506392/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/frcha.2025.1506392/full&#x0023;supplementary-material</ext-link></p>
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<app-group>
<app id="app1">
<title>Appendix A</title>
<table-wrap id="A10" position="float">
<table frame="hsides" rules="groups">
<colgroup>
<col align="left"/>
<col align="left"/>
<col align="left"/>
<col align="left"/>
<col align="left"/>
<col align="left"/>
<col align="left"/>
</colgroup>
<thead>
<tr>
<th valign="top" align="left" rowspan="2">Dimensions of perceptual restorativeness</th>
<th valign="top" align="center" rowspan="2">Question item</th>
<th valign="top" align="center" colspan="5">Agreement level</th>
</tr>
<tr>
<th valign="top" align="center">1</th>
<th valign="top" align="center">2</th>
<th valign="top" align="center">3</th>
<th valign="top" align="center">4</th>
<th valign="top" align="center"><bold>5</bold></th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left" rowspan="5">Remoteness</td>
<td valign="top" align="left">This place makes me feel vulgar</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
</tr>
<tr>
<td valign="top" align="left">This place provides me space to break from my everyday routine and allows me to rest</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
</tr>
<tr>
<td valign="top" align="left">I can fully relax here</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
</tr>
<tr>
<td valign="top" align="left">This place helps me relax my tense mood</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
</tr>
<tr>
<td valign="top" align="left">This place makes me feel free from the constraints of work and daily life</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
</tr>
<tr>
<td valign="top" align="left" rowspan="4">Extensibility</td>
<td valign="top" align="left">The surrounding scenes are harmonious</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
</tr>
<tr>
<td valign="top" align="left">I am curious about the unseen landscapes in the scenery here</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
</tr>
<tr>
<td valign="top" align="left">Here my imagination can be stretched</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
</tr>
<tr>
<td valign="top" align="left">The elements of the landscapes here are similar</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
</tr>
<tr>
<td valign="top" align="left" rowspan="4">Charmingness</td>
<td valign="top" align="left">The place is attractive</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
</tr>
<tr>
<td valign="top" align="left">I can visually explore and discover more here</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
</tr>
<tr>
<td valign="top" align="left">The visual scenes here are charming</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
</tr>
<tr>
<td valign="top" align="left">I would like to spend more time watching the scenes here</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
</tr>
<tr>
<td valign="top" align="left" rowspan="5">Compatibility</td>
<td valign="top" align="left">I can engage in the activities I like here</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
</tr>
<tr>
<td valign="top" align="left">I can quickly adapt to the scenes here</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
</tr>
<tr>
<td valign="top" align="left">This place brings me a sense of belonging</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
</tr>
<tr>
<td valign="top" align="left">I can find ways to enjoy myself here</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
</tr>
<tr>
<td valign="top" align="left">What I want to do here is consistent with the environment</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
<td valign="top" align="left">&#x3000;</td>
</tr>
</tbody>
</table>
</table-wrap></app>
<app id="app2"><title>Appendix B</title>
<table-wrap id="A11" position="float">
<table frame="hsides" rules="groups">
<colgroup>
<col align="left"/>
<col align="center"/>
<col align="left"/>
<col align="center"/>
<col align="left"/>
<col align="center"/>
</colgroup>
<thead>
<tr>
<th valign="top" align="left" rowspan="2">Research object</th>
<th valign="top" align="center" rowspan="2">Overall perceptual restorativeness</th>
<th valign="top" align="center" colspan="4">Characteristics of low hydrodynamic landscapes (Haizi)</th>
</tr>
<tr>
<th valign="top" align="center">Component</th>
<th valign="top" align="center">Perceptual restorativeness</th>
<th valign="top" align="center">Characteristic</th>
<th valign="top" align="center">Perceptual restorativeness</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left" rowspan="11">Low hydrodynamic landscapes (Haizi)</td>
<td valign="top" align="center" rowspan="11">1 2 3 4 5 6 7</td>
<td valign="top" align="left" rowspan="6">Water characteristics</td>
<td valign="top" align="center" rowspan="6">1 2 3 4 5 6 7</td>
<td valign="top" align="left">Water transparency (underwater visibility)<break/>(high/low)</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">&#x00A0;Perceived depth of water<break/>(deep/shallow)</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Proximity to people<break/>(high/low)</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Degree of openness<break/>(high/low)</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Water surface complexity<break/>(high/low)</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Color richness<break/>(high/low)</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left" rowspan="10">Plant and animal characteristics</td>
<td valign="top" align="center" rowspan="10">1 2 3 4 5 6 7</td>
<td valign="top" align="left">Plant density<break/>(high/low)</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Plant level richness<break/>(high/low)</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Plant color richness<break/>(high/low)</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Plant morphological richness<break/>(high/low)</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Animal species richness<break/>(high/low)</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
</tbody>
</table>
</table-wrap></app>
<app id="app3"><title>Appendix C</title>
<table-wrap id="A12" position="float">
<table frame="hsides" rules="groups">
<colgroup>
<col align="left"/>
<col align="center"/>
<col align="left"/>
<col align="center"/>
<col align="left"/>
<col align="center"/>
<col align="left"/>
<col align="center"/>
</colgroup>
<thead>
<tr>
<th valign="top" align="left" rowspan="2">Research object</th>
<th valign="top" align="center" rowspan="2">Overall perceptual restorativeness</th>
<th valign="top" align="center" colspan="6">Environment of Haizi</th>
</tr>
<tr>
<th valign="top" align="center">Component</th>
<th valign="top" align="center">Perceptual restorativeness</th>
<th valign="top" align="center">Element</th>
<th valign="top" align="center">Perceptual restorative-ness</th>
<th valign="top" align="center">Composition</th>
<th valign="top" align="center">Perceptual restorative-ness</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left" rowspan="28">Low hydrodynamic landscapes (Haizi)</td>
<td valign="top" align="center" rowspan="28">1 2 3 4 5 6 7</td>
<td valign="top" align="left" rowspan="22">Water environment</td>
<td valign="top" align="center" rowspan="22">1 2 3 4 5 6 7</td>
<td valign="top" align="left" rowspan="3">Water color</td>
<td valign="top" align="center" rowspan="3">1 2 3 4 5 6 7</td>
<td valign="top" align="left">Blue body</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Green body</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Yellow body</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left" rowspan="5">Waterfront elements</td>
<td valign="top" align="center" rowspan="5">1 2 3 4 5 6 7</td>
<td valign="top" align="left">Mountain stones</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Grassy slopes</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Dense Forest</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Trees</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Wooden plank road</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left" rowspan="6">Water shape</td>
<td valign="top" align="center" rowspan="6">1 2 3 4 5 6 7</td>
<td valign="top" align="left">Strip</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Rectangle</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Oval</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Peacock shape</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Irregular shape</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Bead net shape</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left" rowspan="4">Reflection</td>
<td valign="top" align="center" rowspan="4">1 2 3 4 5 6 7</td>
<td valign="top" align="left">Cloud</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Plants on the waterfront</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Plants in water</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Mountain</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left" rowspan="4">Individual-form scene</td>
<td valign="top" align="center" rowspan="4">1 2 3 4 5 6 7</td>
<td valign="top" align="left">Plank roads on the waterfront</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Plank roads over water</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Viewing platform (with guardrail)</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Fallen tree</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left" rowspan="6">Plant and animal environment</td>
<td valign="top" align="center" rowspan="6">1 2 3 4 5 6 7</td>
<td valign="top" align="left" rowspan="4">Plant species</td>
<td valign="top" align="center" rowspan="4">1 2 3 4 5 6 7</td>
<td valign="top" align="left">Aquatic plant</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Submerged plant</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Humidogene shrub</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Humidogene tree</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left" rowspan="2">Animal species</td>
<td valign="top" align="center" rowspan="2">1 2 3 4 5 6 7</td>
<td valign="top" align="left">Terrestrial</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
<tr>
<td valign="top" align="left">Fish</td>
<td valign="top" align="center">1 2 3 4 5 6 7</td>
</tr>
</tbody>
</table>
</table-wrap>
<table-wrap id="A1" position="float"><label>Appendix Table 7</label>
<caption><p>Multiple linear regression analysis of the restorativeness of water characteristics.</p></caption>
<table frame="hsides" rules="groups">
<colgroup>
<col align="left"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
</colgroup>
<thead>
<tr>
<th valign="top" align="left" rowspan="2">Model</th>
<th valign="top" align="center" colspan="2">Non-standard coefficient</th>
<th valign="top" align="center">Standard coefficient</th>
<th valign="top" align="center" rowspan="2"><italic>T</italic>-value</th>
<th valign="top" align="center" rowspan="2"><italic>P</italic>-value</th>
<th valign="top" align="center" colspan="2">95.0&#x0025; Confidence interval for beta</th>
<th valign="top" align="center" colspan="2">Collinear statistics</th>
<th valign="top" align="center" rowspan="2"><italic>R</italic>&#x00B2;</th>
<th valign="top" align="center" rowspan="2">Adjusted <italic>R</italic>&#x00B2;</th>
</tr>
<tr>
<th valign="top" align="center">B</th>
<th valign="top" align="center">Standard error</th>
<th valign="top" align="center">Beta</th>
<th valign="top" align="center">Minimum value</th>
<th valign="top" align="center">Maximum value</th>
<th valign="top" align="center">Tolerance</th>
<th valign="top" align="center">VIF</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">(Constant)</td>
<td valign="top" align="center">1.978</td>
<td valign="top" align="center">.785</td>
<td valign="top" align="center"/>
<td valign="top" align="center">2.520</td>
<td valign="top" align="center">.018&#x002A;</td>
<td valign="top" align="center">.365</td>
<td valign="top" align="center">3.591</td>
<td valign="top" align="center"/>
<td valign="top" align="center"/>
<td valign="top" align="center" rowspan="6">.489</td>
<td valign="top" align="center" rowspan="6">.390</td>
</tr>
<tr>
<td valign="top" align="left">Clearness</td>
<td valign="top" align="center">.046</td>
<td valign="top" align="center">.114</td>
<td valign="top" align="center">.066</td>
<td valign="top" align="center">.402</td>
<td valign="top" align="center">.691</td>
<td valign="top" align="center">&#x2212;.189</td>
<td valign="top" align="center">.281</td>
<td valign="top" align="center">.736</td>
<td valign="top" align="center">1.358</td>
</tr>
<tr>
<td valign="top" align="left">Perceived depth</td>
<td valign="top" align="center">.240</td>
<td valign="top" align="center">.104</td>
<td valign="top" align="center">.377</td>
<td valign="top" align="center">2.303</td>
<td valign="top" align="center">.030&#x002A;</td>
<td valign="top" align="center">.026</td>
<td valign="top" align="center">.454</td>
<td valign="top" align="center">.734</td>
<td valign="top" align="center">1.362</td>
</tr>
<tr>
<td valign="top" align="left">Openness</td>
<td valign="top" align="center">.178</td>
<td valign="top" align="center">.105</td>
<td valign="top" align="center">.281</td>
<td valign="top" align="center">1.699</td>
<td valign="top" align="center">.101</td>
<td valign="top" align="center">&#x2212;.037</td>
<td valign="top" align="center">.393</td>
<td valign="top" align="center">.721</td>
<td valign="top" align="center">1.387</td>
</tr>
<tr>
<td valign="top" align="left">Surface complexity</td>
<td valign="top" align="center">.084</td>
<td valign="top" align="center">.102</td>
<td valign="top" align="center">.130</td>
<td valign="top" align="center">.821</td>
<td valign="top" align="center">.419</td>
<td valign="top" align="center">&#x2212;.126</td>
<td valign="top" align="center">.294</td>
<td valign="top" align="center">.780</td>
<td valign="top" align="center">1.282</td>
</tr>
<tr>
<td valign="top" align="left">Color richness</td>
<td valign="top" align="center">.144</td>
<td valign="top" align="center">.119</td>
<td valign="top" align="center">.207</td>
<td valign="top" align="center">1.213</td>
<td valign="top" align="center">.236</td>
<td valign="top" align="center">&#x2212;.100</td>
<td valign="top" align="center">.388</td>
<td valign="top" align="center">.675</td>
<td valign="top" align="center">1.481</td>
</tr>
<tr>
<td valign="top" align="left" colspan="12">Implicit variable: restorativeness of the water characteristics</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="table-fn6"><p>&#x002A;<italic>P</italic> &#x003C; 0.05, &#x002A;&#x002A;<italic>P</italic> &#x003C; 0.01, &#x002A;&#x002A;&#x002A;<italic>P</italic> &#x003C; 0.001.</p></fn>
</table-wrap-foot>
</table-wrap>
<table-wrap id="A2" position="float"><label>Appendix Table 8</label>
<caption><p>Multiple linear regression analysis of the restorativeness of the plant and animal characteristics.</p></caption>
<table frame="hsides" rules="groups">
<colgroup>
<col align="left"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
</colgroup>
<thead>
<tr>
<th valign="top" align="left" rowspan="2">Model</th>
<th valign="top" align="center" colspan="2">Non-standard coefficient</th>
<th valign="top" align="center">Standard coefficient</th>
<th valign="top" align="center" rowspan="2"><italic>T</italic>-value</th>
<th valign="top" align="center" rowspan="2"><italic>P</italic>-value</th>
<th valign="top" align="center" colspan="2">95.0&#x0025; Confidence interval for beta</th>
<th valign="top" align="center" colspan="2">Collinear statistics</th>
<th valign="top" align="center" rowspan="2"><italic>R</italic>&#x00B2;</th>
<th valign="top" align="center" rowspan="2">Adjusted <italic>R</italic>&#x00B2;</th>
</tr>
<tr>
<th valign="top" align="center">B</th>
<th valign="top" align="center">Standard error</th>
<th valign="top" align="center">Beta</th>
<th valign="top" align="center">Minimum value</th>
<th valign="top" align="center">Maximum value</th>
<th valign="top" align="center">Tolerance</th>
<th valign="top" align="center">VIF</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">(Constant)</td>
<td valign="top" align="center">.934</td>
<td valign="top" align="center">1.026</td>
<td valign="top" align="center"/>
<td valign="top" align="center">.910</td>
<td valign="top" align="center">.371</td>
<td valign="top" align="center">&#x2212;1.172</td>
<td valign="top" align="center">3.039</td>
<td valign="top" align="center"/>
<td valign="top" align="center"/>
<td valign="top" align="center" rowspan="5">.462</td>
<td valign="top" align="center" rowspan="5">.382</td>
</tr>
<tr>
<td valign="top" align="left">Plant density</td>
<td valign="top" align="center">.419</td>
<td valign="top" align="center">.159</td>
<td valign="top" align="center">.477</td>
<td valign="top" align="center">2.635</td>
<td valign="top" align="center">.014&#x002A;</td>
<td valign="top" align="center">.093</td>
<td valign="top" align="center">.745</td>
<td valign="top" align="center">.608</td>
<td valign="top" align="center">1.644</td>
</tr>
<tr>
<td valign="top" align="left">Plant level richness</td>
<td valign="top" align="center">.416</td>
<td valign="top" align="center">.181</td>
<td valign="top" align="center">.376</td>
<td valign="top" align="center">2.293</td>
<td valign="top" align="center">.030&#x002A;</td>
<td valign="top" align="center">.044</td>
<td valign="top" align="center">.788</td>
<td valign="top" align="center">.740</td>
<td valign="top" align="center">1.352</td>
</tr>
<tr>
<td valign="top" align="left">Plant color richness</td>
<td valign="top" align="center">&#x2212;.163</td>
<td valign="top" align="center">.193</td>
<td valign="top" align="center">&#x2212;.178</td>
<td valign="top" align="center">&#x2212;.842</td>
<td valign="top" align="center">.407</td>
<td valign="top" align="center">&#x2212;.559</td>
<td valign="top" align="center">.234</td>
<td valign="top" align="center">.446</td>
<td valign="top" align="center">2.242</td>
</tr>
<tr>
<td valign="top" align="left">Plant form richness</td>
<td valign="top" align="center">.091</td>
<td valign="top" align="center">.181</td>
<td valign="top" align="center">.096</td>
<td valign="top" align="center">.503</td>
<td valign="top" align="center">.619</td>
<td valign="top" align="center">&#x2212;.281</td>
<td valign="top" align="center">.464</td>
<td valign="top" align="center">.545</td>
<td valign="top" align="center">1.836</td>
</tr>
<tr>
<td valign="top" align="left" colspan="12">Implicit variable: restorativeness of the plant and animal characteristics</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="table-fn7"><p>&#x002A;<italic>P</italic> &#x003C; 0.05, &#x002A;&#x002A;<italic>P</italic> &#x003C; 0.01, &#x002A;&#x002A;&#x002A;<italic>P</italic> &#x003C; 0.001.</p></fn>
</table-wrap-foot>
</table-wrap>
<table-wrap id="A3" position="float"><label>Appendix Table 9</label>
<caption><p>Multiple linear regression analysis of the restorativeness of water environments.</p></caption>
<table frame="hsides" rules="groups">
<colgroup>
<col align="left"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
</colgroup>
<thead>
<tr>
<th valign="top" align="left" rowspan="2">Model</th>
<th valign="top" align="center" colspan="2">Non-standard coefficient</th>
<th valign="top" align="center">Standard coefficient</th>
<th valign="top" align="center" rowspan="2"><italic>T</italic>-value</th>
<th valign="top" align="center" rowspan="2"><italic>P</italic>-value</th>
<th valign="top" align="center" colspan="2">95.0&#x0025; Confidence interval for beta</th>
<th valign="top" align="center" colspan="2">Collinear statistics</th>
<th valign="top" align="center" rowspan="2"><italic>R</italic>&#x00B2;</th>
<th valign="top" align="center" rowspan="2">Adjusted <italic>R</italic>&#x00B2;</th>
</tr>
<tr>
<th valign="top" align="center">B</th>
<th valign="top" align="center">Standard error</th>
<th valign="top" align="center">Beta</th>
<th valign="top" align="center">Minimum value</th>
<th valign="top" align="center">Maximum value</th>
<th valign="top" align="center">Tolerance</th>
<th valign="top" align="center">VIF</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">(Constant)</td>
<td valign="top" align="center">.739</td>
<td valign="top" align="center">.893</td>
<td valign="top" align="center"/>
<td valign="top" align="center">.828</td>
<td valign="top" align="center">.416</td>
<td valign="top" align="center">&#x2212;1.105</td>
<td valign="top" align="center">2.583</td>
<td valign="top" align="center"/>
<td valign="top" align="center"/>
<td valign="top" align="center" rowspan="6">.641</td>
<td valign="top" align="center" rowspan="6">.566</td>
</tr>
<tr>
<td valign="top" align="left">Water color</td>
<td valign="top" align="center">.348</td>
<td valign="top" align="center">.185</td>
<td valign="top" align="center">.300</td>
<td valign="top" align="center">1.884</td>
<td valign="top" align="center">.072</td>
<td valign="top" align="center">&#x2212;.033</td>
<td valign="top" align="center">.729</td>
<td valign="top" align="center">.591</td>
<td valign="top" align="center">1.691</td>
</tr>
<tr>
<td valign="top" align="left">Waterfront elements</td>
<td valign="top" align="center">.347</td>
<td valign="top" align="center">.145</td>
<td valign="top" align="center">.436</td>
<td valign="top" align="center">2.387</td>
<td valign="top" align="center">.025&#x002A;</td>
<td valign="top" align="center">.047</td>
<td valign="top" align="center">.647</td>
<td valign="top" align="center">.448</td>
<td valign="top" align="center">2.231</td>
</tr>
<tr>
<td valign="top" align="left">Water shape</td>
<td valign="top" align="center">.052</td>
<td valign="top" align="center">.120</td>
<td valign="top" align="center">.063</td>
<td valign="top" align="center">.432</td>
<td valign="top" align="center">.670</td>
<td valign="top" align="center">&#x2212;.195</td>
<td valign="top" align="center">.299</td>
<td valign="top" align="center">.702</td>
<td valign="top" align="center">1.425</td>
</tr>
<tr>
<td valign="top" align="left">Water reflection</td>
<td valign="top" align="center">.373</td>
<td valign="top" align="center">.121</td>
<td valign="top" align="center">.517</td>
<td valign="top" align="center">3.083</td>
<td valign="top" align="center">.005&#x002A;&#x002A;</td>
<td valign="top" align="center">.123</td>
<td valign="top" align="center">.622</td>
<td valign="top" align="center">.532</td>
<td valign="top" align="center">1.881</td>
</tr>
<tr>
<td valign="top" align="left">Individual scene</td>
<td valign="top" align="center">&#x2212;.219</td>
<td valign="top" align="center">.120</td>
<td valign="top" align="center">&#x2212;.330</td>
<td valign="top" align="center">&#x2212;1.827</td>
<td valign="top" align="center">.080</td>
<td valign="top" align="center">&#x2212;.466</td>
<td valign="top" align="center">.028</td>
<td valign="top" align="center">.460</td>
<td valign="top" align="center">2.174</td>
</tr>
<tr>
<td valign="top" align="left" colspan="12">Implicit variable: restorativeness of water environments</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="table-fn8"><p>&#x002A;<italic>P</italic> &#x003C; 0.05, &#x002A;&#x002A;<italic>P</italic> &#x003C; 0.01, &#x002A;&#x002A;&#x002A;<italic>P</italic> &#x003C; 0.001.</p></fn>
</table-wrap-foot>
</table-wrap>
<table-wrap id="A4" position="float"><label>Appendix Table 10</label>
<caption><p>Multiple linear regression analysis of the restorativeness of the water reflection components.</p></caption>
<table frame="hsides" rules="groups">
<colgroup>
<col align="left"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
</colgroup>
<thead>
<tr>
<th valign="top" align="left" rowspan="2">Model</th>
<th valign="top" align="center" colspan="2">Non-standard coefficient</th>
<th valign="top" align="center">Standard coefficient</th>
<th valign="top" align="center" rowspan="2"><italic>T</italic></th>
<th valign="top" align="center" rowspan="2"><italic>P</italic></th>
<th valign="top" align="center" colspan="2">95.0&#x0025; Confidence interval for beta</th>
<th valign="top" align="center" colspan="2">Collinear statistics</th>
<th valign="top" align="center" rowspan="2"><italic>R</italic>&#x00B2;</th>
<th valign="top" align="center" rowspan="2">Adjusted <italic>R</italic>&#x00B2;</th>
</tr>
<tr>
<th valign="top" align="center">B</th>
<th valign="top" align="center">Standard error</th>
<th valign="top" align="center">Beta</th>
<th valign="top" align="center">Minimum value</th>
<th valign="top" align="center">Maximum value</th>
<th valign="top" align="center">Tolerance</th>
<th valign="top" align="center">VIF</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">(Constant)</td>
<td valign="top" align="center">1.101</td>
<td valign="top" align="center">.885</td>
<td valign="top" align="center"/>
<td valign="top" align="center">1.244</td>
<td valign="top" align="center">.224</td>
<td valign="top" align="center">&#x2212;.715</td>
<td valign="top" align="center">2.917</td>
<td valign="top" align="center"/>
<td valign="top" align="center"/>
<td valign="top" align="center" rowspan="5">.585</td>
<td valign="top" align="center" rowspan="5">.523</td>
</tr>
<tr>
<td valign="top" align="left">Plants on the water</td>
<td valign="top" align="center">&#x2212;.023</td>
<td valign="top" align="center">.141</td>
<td valign="top" align="center">&#x2212;.028</td>
<td valign="top" align="center">&#x2212;.161</td>
<td valign="top" align="center">.873</td>
<td valign="top" align="center">&#x2212;.313</td>
<td valign="top" align="center">.267</td>
<td valign="top" align="center">.496</td>
<td valign="top" align="center">2.015</td>
</tr>
<tr>
<td valign="top" align="left">Waterfront plants</td>
<td valign="top" align="center">.219</td>
<td valign="top" align="center">.159</td>
<td valign="top" align="center">.258</td>
<td valign="top" align="center">1.377</td>
<td valign="top" align="center">.180</td>
<td valign="top" align="center">&#x2212;.107</td>
<td valign="top" align="center">.545</td>
<td valign="top" align="center">.439</td>
<td valign="top" align="center">2.280</td>
</tr>
<tr>
<td valign="top" align="left">Clouds</td>
<td valign="top" align="center">.435</td>
<td valign="top" align="center">.209</td>
<td valign="top" align="center">.438</td>
<td valign="top" align="center">2.083</td>
<td valign="top" align="center">.047&#x002A;</td>
<td valign="top" align="center">.007</td>
<td valign="top" align="center">.864</td>
<td valign="top" align="center">.348</td>
<td valign="top" align="center">2.870</td>
</tr>
<tr>
<td valign="top" align="left">Mountains</td>
<td valign="top" align="center">.201</td>
<td valign="top" align="center">.170</td>
<td valign="top" align="center">.233</td>
<td valign="top" align="center">1.178</td>
<td valign="top" align="center">.249</td>
<td valign="top" align="center">&#x2212;.149</td>
<td valign="top" align="center">.550</td>
<td valign="top" align="center">.393</td>
<td valign="top" align="center">2.542</td>
</tr>
<tr>
<td valign="top" align="left" colspan="12">Implicit variable: restorativeness of water reflection components</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="table-fn9"><p>&#x002A;<italic>P</italic> &#x003C; 0.05, &#x002A;&#x002A;<italic>P</italic> &#x003C; 0.01, &#x002A;&#x002A;&#x002A;<italic>P</italic> &#x003C; 0.001.</p></fn>
</table-wrap-foot>
</table-wrap>
<table-wrap id="A5" position="float"><label>Appendix Table 11</label>
<caption><p>Multiple linear regression analysis of the restorativeness of the watercolor components.</p></caption>
<table frame="hsides" rules="groups">
<colgroup>
<col align="left"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
</colgroup>
<thead>
<tr>
<th valign="top" align="left" rowspan="2">Model</th>
<th valign="top" align="center" colspan="2">Non-standard coefficient</th>
<th valign="top" align="center">Standard coefficient</th>
<th valign="top" align="center" rowspan="2">T-value</th>
<th valign="top" align="center" rowspan="2"><italic>P</italic>-value</th>
<th valign="top" align="center" colspan="2">95.0&#x0025; Confidence interval for beta</th>
<th valign="top" align="center" colspan="2">Collinear statistics</th>
<th valign="top" align="center" rowspan="2"><italic>R</italic>&#x00B2;</th>
<th valign="top" align="center" rowspan="2">Adjusted <italic>R</italic>&#x00B2;</th>
</tr>
<tr>
<th valign="top" align="center">B</th>
<th valign="top" align="center">Standard error</th>
<th valign="top" align="center">Beta</th>
<th valign="top" align="center">Minimum value</th>
<th valign="top" align="center">Maximum value</th>
<th valign="top" align="center">Tolerance</th>
<th valign="top" align="center">VIF</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">(Constant)</td>
<td valign="top" align="center">2.238</td>
<td valign="top" align="center">.698</td>
<td valign="top" align="center"/>
<td valign="top" align="center">3.208</td>
<td valign="top" align="center">.003&#x002A;&#x002A;</td>
<td valign="top" align="center">.809</td>
<td valign="top" align="center">3.667</td>
<td valign="top" align="center"/>
<td valign="top" align="center"/>
<td valign="top" align="center" rowspan="4">.487</td>
<td valign="top" align="center" rowspan="4">.432</td>
</tr>
<tr>
<td valign="top" align="left">Mainly blue</td>
<td valign="top" align="center">.222</td>
<td valign="top" align="center">.091</td>
<td valign="top" align="center">.341</td>
<td valign="top" align="center">2.451</td>
<td valign="top" align="center">.021&#x002A;</td>
<td valign="top" align="center">.036</td>
<td valign="top" align="center">.407</td>
<td valign="top" align="center">.948</td>
<td valign="top" align="center">1.055</td>
</tr>
<tr>
<td valign="top" align="left">Mainly green</td>
<td valign="top" align="center">.306</td>
<td valign="top" align="center">.091</td>
<td valign="top" align="center">.473</td>
<td valign="top" align="center">3.379</td>
<td valign="top" align="center">.002&#x002A;&#x002A;</td>
<td valign="top" align="center">.121</td>
<td valign="top" align="center">.492</td>
<td valign="top" align="center">.935</td>
<td valign="top" align="center">1.070</td>
</tr>
<tr>
<td valign="top" align="left">Mainly yellow</td>
<td valign="top" align="center">.154</td>
<td valign="top" align="center">.064</td>
<td valign="top" align="center">.332</td>
<td valign="top" align="center">2.409</td>
<td valign="top" align="center">.023&#x002A;</td>
<td valign="top" align="center">.023</td>
<td valign="top" align="center">.285</td>
<td valign="top" align="center">.966</td>
<td valign="top" align="center">1.035</td>
</tr>
<tr>
<td valign="top" align="left" colspan="12">Implicit variable: restorativeness of water color components</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="table-fn10"><p>&#x002A;<italic>P</italic> &#x003C; 0.05, &#x002A;&#x002A;<italic>P</italic> &#x003C; 0.01, &#x002A;&#x002A;&#x002A;<italic>P</italic> &#x003C; 0.001.</p></fn>
</table-wrap-foot>
</table-wrap>
<table-wrap id="A6" position="float"><label>Appendix Table 12</label>
<caption><p>Multiple linear regression analysis of the restorativeness of the individual scene components. Values indicate negative impacts of the individual scene components, and the higher the value, the greater the negative impact.</p></caption>
<table frame="hsides" rules="groups">
<colgroup>
<col align="left"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
</colgroup>
<thead>
<tr>
<th valign="top" align="left" rowspan="2">Model</th>
<th valign="top" align="center" colspan="2">Non-standard coefficient</th>
<th valign="top" align="center">Standard coefficient</th>
<th valign="top" align="center" rowspan="2">T-value</th>
<th valign="top" align="center" rowspan="2"><italic>P</italic>-value</th>
<th valign="top" align="center" colspan="2">95.0&#x0025; Confidence interval for beta</th>
<th valign="top" align="center" colspan="2">Collinear statistics</th>
<th valign="top" align="center" rowspan="2"><italic>R</italic>&#x00B2;</th>
<th valign="top" align="center" rowspan="2">Adjusted <italic>R</italic>&#x00B2;</th>
</tr>
<tr>
<th valign="top" align="center">B</th>
<th valign="top" align="center">Standard error</th>
<th valign="top" align="center">Beta</th>
<th valign="top" align="center">Minimum value</th>
<th valign="top" align="center">Maximum value</th>
<th valign="top" align="center">Tolerance</th>
<th valign="top" align="center">VIF</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">(Constant)</td>
<td valign="top" align="center">1.369</td>
<td valign="top" align="center">1.021</td>
<td valign="top" align="center"/>
<td valign="top" align="center">1.341</td>
<td valign="top" align="center">.191</td>
<td valign="top" align="center">&#x2212;.726</td>
<td valign="top" align="center">3.464</td>
<td valign="top" align="center"/>
<td valign="top" align="center"/>
<td valign="top" align="center" rowspan="5">.396</td>
<td valign="top" align="center" rowspan="5">.306</td>
</tr>
<tr>
<td valign="top" align="left">Plank roads by the shore</td>
<td valign="top" align="center">.236</td>
<td valign="top" align="center">.163</td>
<td valign="top" align="center">.239</td>
<td valign="top" align="center">1.452</td>
<td valign="top" align="center">.158</td>
<td valign="top" align="center">&#x2212;.098</td>
<td valign="top" align="center">.570</td>
<td valign="top" align="center">.828</td>
<td valign="top" align="center">1.208</td>
</tr>
<tr>
<td valign="top" align="left">Plank roads over water</td>
<td valign="top" align="center">.381</td>
<td valign="top" align="center">.172</td>
<td valign="top" align="center">.420</td>
<td valign="top" align="center">2.212</td>
<td valign="top" align="center">.036&#x002A;</td>
<td valign="top" align="center">.028</td>
<td valign="top" align="center">.735</td>
<td valign="top" align="center">.622</td>
<td valign="top" align="center">1.608</td>
</tr>
<tr>
<td valign="top" align="left">Viewing platform with guardrails</td>
<td valign="top" align="center">.065</td>
<td valign="top" align="center">.149</td>
<td valign="top" align="center">.076</td>
<td valign="top" align="center">.440</td>
<td valign="top" align="center">.663</td>
<td valign="top" align="center">&#x2212;.240</td>
<td valign="top" align="center">.371</td>
<td valign="top" align="center">.743</td>
<td valign="top" align="center">1.345</td>
</tr>
<tr>
<td valign="top" align="left">Fallen trees in the water</td>
<td valign="top" align="center">.051</td>
<td valign="top" align="center">.113</td>
<td valign="top" align="center">.073</td>
<td valign="top" align="center">.457</td>
<td valign="top" align="center">.652</td>
<td valign="top" align="center">&#x2212;.180</td>
<td valign="top" align="center">.282</td>
<td valign="top" align="center">.883</td>
<td valign="top" align="center">1.132</td>
</tr>
<tr>
<td valign="top" align="left" colspan="12">Implicit variable: restorativeness of individual scene components</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="table-fn11"><p>&#x002A;<italic>P</italic> &#x003C; 0.05, &#x002A;&#x002A;<italic>P</italic> &#x003C; 0.01, &#x002A;&#x002A;&#x002A;<italic>P</italic> &#x003C; 0.001.</p></fn>
</table-wrap-foot>
</table-wrap>
<table-wrap id="A7" position="float"><label>Appendix Table 13</label>
<caption><p>Multiple linear regression analysis of the restorativeness of plant and animal environments.</p></caption>
<table frame="hsides" rules="groups">
<colgroup>
<col align="left"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
</colgroup>
<thead>
<tr>
<th valign="top" align="left" rowspan="2">Model</th>
<th valign="top" align="center" colspan="2">Non-standard coefficient</th>
<th valign="top" align="center">Standard coefficient</th>
<th valign="top" align="center" rowspan="2">T-value</th>
<th valign="top" align="center" rowspan="2"><italic>P</italic>-value</th>
<th valign="top" align="center" colspan="2">95.0&#x0025; Confidence interval for beta</th>
<th valign="top" align="center" colspan="2">Collinear statistics</th>
<th valign="top" align="center" rowspan="2"><italic>R</italic>&#x00B2;</th>
<th valign="top" align="center" rowspan="2">Adjusted <italic>R</italic>&#x00B2;</th>
</tr>
<tr>
<th valign="top" align="center">B</th>
<th valign="top" align="center">Standard error</th>
<th valign="top" align="center">Beta</th>
<th valign="top" align="center">Minimum value</th>
<th valign="top" align="center">Maximum value</th>
<th valign="top" align="center">Tolerance</th>
<th valign="top" align="center">VIF</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">(Constant)</td>
<td valign="top" align="center">&#x2212;.674</td>
<td valign="top" align="center">.556</td>
<td valign="top" align="center"/>
<td valign="top" align="center">&#x2212;1.213</td>
<td valign="top" align="center">.236</td>
<td valign="top" align="center">&#x2212;1.815</td>
<td valign="top" align="center">.467</td>
<td valign="top" align="center"/>
<td valign="top" align="center"/>
<td valign="top" align="center" rowspan="3">.828</td>
<td valign="top" align="center" rowspan="3">.815</td>
</tr>
<tr>
<td valign="top" align="left">Plant species</td>
<td valign="top" align="center">.543</td>
<td valign="top" align="center">.085</td>
<td valign="top" align="center">.569</td>
<td valign="top" align="center">6.410</td>
<td valign="top" align="center">.000&#x002A;&#x002A;&#x002A;</td>
<td valign="top" align="center">.369</td>
<td valign="top" align="center">.716</td>
<td valign="top" align="center">.810</td>
<td valign="top" align="center">1.235</td>
</tr>
<tr>
<td valign="top" align="left">Animal species</td>
<td valign="top" align="center">.547</td>
<td valign="top" align="center">.096</td>
<td valign="top" align="center">.504</td>
<td valign="top" align="center">5.680</td>
<td valign="top" align="center">.000&#x002A;&#x002A;&#x002A;</td>
<td valign="top" align="center">.349</td>
<td valign="top" align="center">.744</td>
<td valign="top" align="center">.810</td>
<td valign="top" align="center">1.235</td>
</tr>
<tr>
<td valign="top" align="left" colspan="12">Implicit variable: restorativeness of plant and animal environments</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="table-fn12"><p>&#x002A;<italic>P</italic> &#x003C; 0.05, &#x002A;&#x002A;<italic>P</italic> &#x003C; 0.01, &#x002A;&#x002A;&#x002A;<italic>P</italic> &#x003C; 0.001.</p></fn>
</table-wrap-foot>
</table-wrap>
<table-wrap id="A8" position="float"><label>Appendix Table 14</label>
<caption><p>Multiple linear regression analysis of the restorativeness of plant species.</p></caption>
<table frame="hsides" rules="groups">
<colgroup>
<col align="left"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
</colgroup>
<thead>
<tr>
<th valign="top" align="left" rowspan="2">Model</th>
<th valign="top" align="center" colspan="2">Non-standard coefficient</th>
<th valign="top" align="center">Standard coefficient</th>
<th valign="top" align="center" rowspan="2">T-value</th>
<th valign="top" align="center" rowspan="2"><italic>P</italic>-value</th>
<th valign="top" align="center" colspan="2">95.0&#x0025; Confidence interval for beta</th>
<th valign="top" align="center" colspan="2">Collinear statistics</th>
<th valign="top" align="center" rowspan="2"><italic>R</italic>&#x00B2;</th>
<th valign="top" align="center" rowspan="2">Adjusted <italic>R</italic>&#x00B2;</th>
</tr>
<tr>
<th valign="top" align="center">B</th>
<th valign="top" align="center">Standard error</th>
<th valign="top" align="center">Beta</th>
<th valign="top" align="center">Minimum value</th>
<th valign="top" align="center">Maximum value</th>
<th valign="top" align="center">Tolerance</th>
<th valign="top" align="center">VIF</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">(Constant)</td>
<td valign="top" align="center">.435</td>
<td valign="top" align="center">.719</td>
<td valign="top" align="center"/>
<td valign="top" align="center">.605</td>
<td valign="top" align="center">.550</td>
<td valign="top" align="center">&#x2212;1.041</td>
<td valign="top" align="center">1.911</td>
<td valign="top" align="center"/>
<td valign="top" align="center"/>
<td valign="top" align="center" rowspan="5">.711</td>
<td valign="top" align="center" rowspan="5">.668</td>
</tr>
<tr>
<td valign="top" align="left">Submerged plants</td>
<td valign="top" align="center">.044</td>
<td valign="top" align="center">.090</td>
<td valign="top" align="center">.062</td>
<td valign="top" align="center">.483</td>
<td valign="top" align="center">.633</td>
<td valign="top" align="center">&#x2212;.142</td>
<td valign="top" align="center">.229</td>
<td valign="top" align="center">.642</td>
<td valign="top" align="center">1.558</td>
</tr>
<tr>
<td valign="top" align="left">Emergent plants</td>
<td valign="top" align="center">.212</td>
<td valign="top" align="center">.083</td>
<td valign="top" align="center">.305</td>
<td valign="top" align="center">2.546</td>
<td valign="top" align="center">.017&#x002A;</td>
<td valign="top" align="center">.041</td>
<td valign="top" align="center">.382</td>
<td valign="top" align="center">.749</td>
<td valign="top" align="center">1.335</td>
</tr>
<tr>
<td valign="top" align="left">Wetland shrubs</td>
<td valign="top" align="center">.373</td>
<td valign="top" align="center">.135</td>
<td valign="top" align="center">.415</td>
<td valign="top" align="center">2.753</td>
<td valign="top" align="center">.010&#x002A;&#x002A;</td>
<td valign="top" align="center">.095</td>
<td valign="top" align="center">.651</td>
<td valign="top" align="center">.472</td>
<td valign="top" align="center">2.119</td>
</tr>
<tr>
<td valign="top" align="left">Wetland trees</td>
<td valign="top" align="center">.352</td>
<td valign="top" align="center">.138</td>
<td valign="top" align="center">.328</td>
<td valign="top" align="center">2.545</td>
<td valign="top" align="center">.017&#x002A;</td>
<td valign="top" align="center">.068</td>
<td valign="top" align="center">.636</td>
<td valign="top" align="center">.644</td>
<td valign="top" align="center">1.554</td>
</tr>
<tr>
<td valign="top" align="left" colspan="12">Implicit variable: restorativeness of plant species</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="table-fn13"><p>&#x002A;<italic>P</italic> &#x003C; 0.05, &#x002A;&#x002A;<italic>P</italic> &#x003C; 0.01, &#x002A;&#x002A;&#x002A;<italic>P</italic> &#x003C; 0.001.</p></fn>
</table-wrap-foot>
</table-wrap>
<table-wrap id="A9" position="float"><label>Appendix Table 15</label>
<caption><p>Multiple linear regression analysis of the restorativeness of animal species.</p></caption>
<table frame="hsides" rules="groups">
<colgroup>
<col align="left"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
<col align="center"/>
</colgroup>
<thead>
<tr>
<th valign="top" align="left" rowspan="2">Model</th>
<th valign="top" align="center" colspan="2">Non-standard coefficient</th>
<th valign="top" align="center">Standard coefficient</th>
<th valign="top" align="center" rowspan="2">T-value</th>
<th valign="top" align="center" rowspan="2"><italic>P</italic>-value</th>
<th valign="top" align="center" colspan="2">95.0&#x0025; Confidence interval for beta</th>
<th valign="top" align="center" colspan="2">Collinear statistics</th>
<th valign="top" align="center" rowspan="2"><italic>R</italic>&#x00B2;</th>
<th valign="top" align="center" rowspan="2">Adjusted <italic>R</italic>&#x00B2;</th>
</tr>
<tr>
<th valign="top" align="center">B</th>
<th valign="top" align="center">Standard error</th>
<th valign="top" align="center">Beta</th>
<th valign="top" align="center">Minimum value</th>
<th valign="top" align="center">Maximum value</th>
<th valign="top" align="center">Tolerance</th>
<th valign="top" align="center">VIF</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="top" align="left">(Constant)</td>
<td valign="top" align="center">.760</td>
<td valign="top" align="center">.864</td>
<td valign="top" align="center"/>
<td valign="top" align="center">.880</td>
<td valign="top" align="center">.386</td>
<td valign="top" align="center">&#x2212;1.007</td>
<td valign="top" align="center">2.526</td>
<td valign="top" align="center"/>
<td valign="top" align="center"/>
<td valign="top" align="center" rowspan="3">.540</td>
<td valign="top" align="center" rowspan="3">.509</td>
</tr>
<tr>
<td valign="top" align="left">Terrestrial</td>
<td valign="top" align="center">.455</td>
<td valign="top" align="center">.113</td>
<td valign="top" align="center">.509</td>
<td valign="top" align="center">4.040</td>
<td valign="top" align="center">.000&#x002A;&#x002A;&#x002A;</td>
<td valign="top" align="center">.225</td>
<td valign="top" align="center">.686</td>
<td valign="top" align="center">.999</td>
<td valign="top" align="center">1.001</td>
</tr>
<tr>
<td valign="top" align="left">Fish</td>
<td valign="top" align="center">.433</td>
<td valign="top" align="center">.106</td>
<td valign="top" align="center">.516</td>
<td valign="top" align="center">4.094</td>
<td valign="top" align="center">.000&#x002A;&#x002A;&#x002A;</td>
<td valign="top" align="center">.216</td>
<td valign="top" align="center">.649</td>
<td valign="top" align="center">.999</td>
<td valign="top" align="center">1.001</td>
</tr>
<tr>
<td valign="top" align="left" colspan="12">Implicit variable: restorativeness of animal species</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn id="table-fn14"><p>&#x002A;<italic>P</italic> &#x003C; 0.05, &#x002A;&#x002A;<italic>P</italic> &#x003C; 0.01, &#x002A;&#x002A;&#x002A;<italic>P</italic> &#x003C; 0.001.</p></fn>
</table-wrap-foot>
</table-wrap></app>
</app-group>
</back>
</article>