Figures
Abstract
Urban soundscapes, particularly those experienced in green spaces, have been increasingly recognized as factors that influence human mental health. This scoping review explores the existing literature on soundscapes within urban green spaces and their associated mental health outcomes. It aims to classify the methodologies used in this domain, identify mental health outcomes related to urban green space soundscapes, and examine specific soundscape elements and their correlations with mental health. A systematic search of peer-reviewed studies was conducted. After screening titles, abstracts, and full texts, 22 studies met the inclusion criteria. Diverse methodological approaches were identified, with an emphasis on quantitative multi-method designs. Commonly studied mental health outcomes include stress reduction, mood enhancement, perceived restorativeness, and cognitive restoration. Standardized psychometric tools, such as the Perceived Stress Scale (PSS-14), Positive and Negative Affect Schedule (PANAS) and Perceived Restorativeness Soundscape Scale (PRSS) are frequently used as outcome measures. Natural soundscape elements such as birdsong, water sounds, and rustling leaves had a positive association with relaxation and perceived mental restoration throughout all studies, while mechanical sounds, such as traffic noise were linked to adverse mental health outcomes. These findings highlight that natural soundscapes in urban green spaces have a potential positive relationship with mental health by reducing stress and enhancing mood. However, the cross-sectional design and methodological heterogeneity of the included studies limit causal interpretation. Future research should explore multi-sensory experiences and examine soundscapes in diverse urban contexts to provide more robust insights into their relationship with mental health. The practical implications suggest that urban planners should prioritize integrating natural sound elements into urban areas to improve mental health. The study protocol of this scoping review had been registered at OSF (osf.io/4r7gd).
Citation: Ahmadi E, Baierl S, Voss S, Asenkerschbaumer I, Berndt U, Bernhard L, et al. (2026) Exploring the relationship between mental health and urban green space soundscapes: A scoping review. PLoS One 21(3): e0344125. https://doi.org/10.1371/journal.pone.0344125
Editor: Yuan Zhang, Shenyang Jianzhu University, CHINA
Received: September 3, 2025; Accepted: February 16, 2026; Published: March 3, 2026
Copyright: © 2026 Ahmadi et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Data Availability: All relevant data are within the paper and its Supporting Information files.
Funding: M.C.; S.V.: German Federal Ministry of Education and Research (BMBF) within the Research Initiative for the Conservation of Biodiversity (FEdA) under the funding code 16LW0385.
Competing interests: The authors have declared that no competing interests exist.
Introduction
In the past and present, the detrimental health effects of noise have been investigated and discussed thoroughly in various contexts and settings. Although a broad range of scientific literature on noise pollution and its various adverse health effects has been published, the scope of this research is predominantly limited to noise as a one-dimensional variable that focuses solely on negative health outcomes [1]. This narrow approach created a growing interest in investigating sound as a more holistic and subjective concept outside of mere noise-related considerations. The resulting paradigm shift emerged in the form of research which can be described by the umbrella term “soundscape”. First introduced by R. Murray Schaefer in The Tuning of the World (1977), the term conceptualizes the acoustic environment as perceived and experienced by individuals [2]. In soundscape research, the acoustic environment is considered as a resource with potential health benefits [3]. As a multidisciplinary field, it is characterized by its focus on the multi-layered acoustic perception of humans. Soundscape research emphasizes the contextual influence of sound sources, auditory perception, and cognitive processes, that impacts an individual’s response and outcomes [4]. Over the last ten years, the International Organization for Standardization (ISO) has developed and published a standardized framework for soundscape assessment using the ISO 12913 series. It collates definitions and guidance regarding data collection and analysis methods [4–6].
A prominent area of current soundscape research is the examination of different soundscape elements and their relationship with health in the context of urbanization. For instance, Aletta et al. systematically explored and identified associations between positive urban soundscapes (e.g., pleasant, calm and less annoying) and health. They reported a faster stress recovery associated with positive urban soundscapes [3]. The current rise in urban soundscape research could be related to a significant increase in the global urban population, from 0.75 billion in 1950 to 4.22 billion in 2018. It is estimated that by the mid-twenty-first century, 68% of the world’s population will reside in urban areas [7]. Urban soundscape research often involves an assessment of different sound sources and their association with health parameters. In recent years researchers have found that natural sounds can reduce stress [8] and improve mood and cognitive performance [9]. While evidence of the relationships between urban soundscapes and health is growing, only recent studies have examined the relationship between mental health and urban soundscapes in the context of urban green spaces. In the literature, exposure to urban green spaces has been associated with a wide array of beneficial health outcomes [10], although the influence of social determinants has not been fully explored [11].
Nonetheless, despite the growing importance of the field, there is no systematic overview of current urban soundscape research trends with an emphasis on green spaces and mental health currently. Therefore, this scoping review aims to map methodologies as well as the investigated associations between soundscape elements (e.g., birdsong, water sounds, traffic noise) and mental health outcomes in urban green spaces. The mapping of evidence could inform public health strategies and urban planning, supporting mental health through the intentional design of restorative green space soundscapes in cities.
Methods
Study design
This study follows the ISO 12913 definition of soundscapes as the perceived acoustic environment [4]. Accordingly, sound sources are categorized into sounds of technology (mechanical), nature (natural), or human beings (anthropogenic) [6,12]. No further restrictions were made to capture the full diversity in the literature.
Given that existing reviews only consider the relationship between soundscapes and health in clinical, rural, or urban contexts in a broader sense, a scoping review was identified as the most suitable type of review to provide an overview of the existing scientific landscape. To our knowledge, no review of this type has been conducted or published. The scoping review followed the guidance proposed by the Joanna Briggs Institute [13]. The study protocol had been registered at OSF (osf.io/4r7gd).
The scoping review is based on the methodological framework proposed by Arksey and O’Malley [14], considering later refinement suggestions by Levac et al. [15] and Daudt et al. [16], as well as the recommended enhancements by Westphaln et al. [17]. Furthermore, the preferred reporting items of the PRISMA checklist for scoping reviews were considered [18]. Initially, the framework was constructed using the following five steps: Step 1: Identifying and specifying the research questions, Step 2: Identifying relevant literature, Step 3: Selection of studies, Step 4: Extraction, mapping and charting the data, Step 5: Summarizing, synthesizing and reporting of the results.
Step 1: Identifying and specifying the research questions
After initially investigating the literature, attention was focused on the following research questions: (1) What methodologies and study designs are used in this domain? (2) What are the different soundscape elements studied? (3) Which mental health outcomes are being studied in connection with urban green space soundscapes? (4) How are the investigated soundscape elements associated with mental health outcomes?
According to the WHO, mental health refers to a state of psychological well-being in which individuals can manage life’s stresses, realize their potential, and function effectively at work and in their communities. It is a crucial aspect of overall health and well-being, embodying more than simply the absence of mental illness [19]. This broad definition of mental health aligns with the definition of mental health used in our scoping review approach, as our rationale is to map the current evidence in a multidisciplinary and integrated approach.
Step 2: Identifying relevant literature
To investigate the existing literature on the topic of soundscapes and their relationship with mental health, a “Population, Concept, Context” (PCC) framework was employed in order to adhere to the suggestions set out in the JBI Manual and to facilitate clarity in the subsequent stages of the scoping review process [20].
The PCC Framework was adjusted to another context, as the urban population can be described more appropriately with a second context rather than a population itself (Table 1). The search strategy was embedded in the PCC-Framework and was developed and further refined using a team-based approach. The following five databases were applied: MEDLINE, Embase, Web of Science, PsycINFO and LIVIVO. They were selected to ensure interdisciplinary coverage while avoiding redundancy in line with PRISMA-ScR guidelines. The search strategy was adapted to the respective syntax of the database and was identical for every database search (Table 1). The detailed search strings for all databases are provided in S1 Appendix. There were no restrictions regarding the time of publication. Furthermore, only peer-reviewed articles in English and German were considered for inclusion. Grey literature was excluded in advance, as it is more time consuming to find with systematic search strategies [21]. The search was conducted on the 17th of November 2024. All identified references were uploaded to the citation management software Endnote 21 (Clarivate; London, UK). Duplicates were removed using Endnote 21 and Rayyan (Cambridge, MA, USA) [22].
Step 3: Selection of studies
To develop the eligibility criteria, the PCC Framework was implemented. The model depicts the possible inclusion and exclusion criteria used for the screening. These include eligibility prerequisites for the population, concept and the two contexts (Table 2). Potential differences between studies in real words settings and laboratory studies were suspected; hence, it was decided post-hoc to include only on-site studies.
Screening was performed using Rayyan (Cambridge, MA, USA). An iterative and multi-step team approach was used to conduct the screening. Before the initial title and abstract screening, a test screening of 50 articles was carried out by all team members to revise the eligibility criteria through subsequent discussions within the team. After the test screening, all nine team members executed blinded title and abstract screening against the adjusted inclusion and exclusion criteria. The identified references for abstract screening were divided by nine; hence every team member screened the same proportion of references. The first author (EA) screened all references, as his assessment of inclusion and exclusion functioned as a reference point for discussions of conflicts. A similar approach was applied to the full-text screening. As before, the articles were divided proportionally between team members, with one member reading every article. The last author (MC) performed the final decision on resolving conflicts. To illustrate the selection process, we implemented a PRISMA flow chart with different screening steps.
Step 4: Extraction, mapping and charting the data
Data extraction was performed by the first author (EA) with a data charting table using Microsoft Excel (Redmond, WA, USA). The specific configuration of the extraction table was piloted iteratively through five test extractions, resulting in adjustments in comparison to the first proposed extraction tool in the first version of the study protocol. This corresponds with the recommendations of Pollock et al., who advocated the iterative process of data extraction [23]. The table captures (1) general information, such as authors, publication year, key findings, as well as (2) specific information such as primary mental health outcomes, types of urban green space, and studied soundscape elements.
An openness to emerging subcategories and further classifications was maintained. Thus, we added columns regarding cited theoretical frameworks as well as the seasonal period of the conducted study after the initial test-extraction.
Step 5: Summarizing, synthesizing and reporting of the results
Results were synthesized and organized in alignment with the research question and presented across three comprehensive extraction tables. The first table provides an overview of the preliminary study details, whereas the second describes more specific methodologies and population characteristics. The third table was dedicated to key findings, limitations and practical recommendations. The tabular data was further complemented by a narrative summary to provide context and highlight key observations made during extraction. Furthermore, the results were structured into four distinct parts to account for the specific aims (research questions; RQ) outlined in the scoping review: RQ (1) Study design and general methodology; RQ (2) Acoustic dimension and studied sound sources; RQ (3) Conceptualization and measurement of mental health outcomes and RQ (4) Soundscape elements and their associations with mental health. Figures were generated using Python [24]. Maps were created using Basemap 2.0.0 [25], which incorporates data from the Generic Mapping Tools (GMT) [26] and the Global Self-consistent, Hierarchical, High-resolution Geography Database (GSHHG) [27]. Both datasets are distributed under the GNU Lesser General Public License (LGPLv3) [28].
Results
A total of 3,892 articles were identified through the database searches. After removing duplicates with Endnote and Rayyan, 3,072 articles remained for title and abstract screening. Of these, a total of 159 articles were identified for the full-text screening. After full-text screening and resolving all conflicts, 22 articles remained (Fig 1).
Overview of included studies
With 14 of the 22 included studies, China accounted for nearly 70% of the conducted studies overall (Fig 2). Furthermore, the earliest study was conducted in 2018, whereas 17 studies were published after 2020 (Fig 3). The research settings predominantly involved urban parks (n = 13) and urban forests (n = 6). Further details of the included studies are shown in Table 3.
The investigated green spaces showed vast differences in size. For instance, “Dunbar’s Closed Garden” in Edinburgh, Scotland only encompasses 0.19 ha [29], whereas Sun Island Park in Harbin, China spans 3,800 ha in size [30] (Table 4).
The sample sizes displayed considerable differences, with small exploratory cohorts and larger population-based analyses (Table 4). The smallest sample yielded 20 participants [37], whereas the largest sample included 1,161 participants [39]. Most studies were conducted during the summer months (n = 15). Only two studies included both warm and cold seasons.
RQ (1): Study design and general methodology
The identified studies demonstrate the use of diverse techniques to capture objective sound metrics, subjective soundscape perception and psychometric parameters. All studies were based on a cross-sectional design, in which participant characteristics were analyzed at a single point in time. Nonetheless, data collection was conducted throughout multiple days and times of day, with an emphasis on mornings and afternoons [32,41,46]. Fifteen studies were conducted during summer/spring, while three were conducted during autumn/winter. Eleven studies examined more than one green space. Nineteen of the 22 studies implemented a quantitative multi-method approach, where the measurement of Sound Pressure Level (SPL) was combined with questionnaires regarding the subjective assessment of the acoustic environment as well as questions related to acoustic perception, mental health and well-being. Only three studies used a mixed-methods design. For instance, Jaszczak et al. employed qualitative interviews with participants and experts using a mixed-methods approach, to capture the nuances of individual soundscape experiences [45]. Payne and Bruce implemented qualitative content analysis to generate themes from their questionnaire with open-ended questions [29]. Furthermore, 21 studies collected data on sociodemographic characteristics. Table 4 further summarizes study methods and sociodemographic characteristics.
Statistical methods across the reviewed studies varied considerably, ranging from basic descriptive analyses (n = 22) to more advanced approaches, such as regression analyses (n = 8), ANOVA (n = 5) and structural equation modelling (SEM) (n = 7). For example, Y. L. Guo et al. combined Spearman’s rho, Kruskal–Wallis tests, and hierarchical multiple regression to link social and demographic factors with stress-related outcomes in park visitors [47]. Apart from that, X. Guo et al. used SEM with Confirmatory Factor Analysis (CFA) to examine how perceived pleasantness and eventfulness influence restorativeness [48]. Herranz-Pascual et al. and Payne and Bruce relied on ANOVA to compare mental health parameters across different urban environments [29,46].
RQ (2): Acoustic dimension and studied sound sources
Most of the authors of the included studies (n = 13) had a similar approach. They categorized sound sources into three overarching sound domains: natural (e.g., birdsong, water sounds), mechanical (e.g., traffic, construction noise), and anthropogenic or social (e.g., conversations, laughter), with slight adjustments in the scope of applied categories.
Four studies measured Sound Pressure Levels (SPL). Tian et al. additionally paired SPL with Geographical Information Systems (GIS) mapping to visualize soundscapes on a map [37]. Seven studies were based on soundwalks, while two studies implemented the Normalized Difference Soundscape Index (NDSI). The NDSI was used to measure the balance between acoustic biodiversity and anthropogenic disturbance [51]. Furthermore, the soundwalk method was applied as an empirical approach to identify soundscapes and their components. The fundamental objective of a soundwalk is to motivate participants to engage in attentive listening and formulate assessments of the auditory stimuli encountered [52]. It was also one of the more frequently applied method within the included studies (n = 7) to collect data for exploring areas of human response to an acoustic environment. The soundwalk method was standardized according to the International Organization for Standardization (ISO-12913–2). While plenty of the included studies implemented the ISO-12913–2 Guidelines (n = 6), most of the studies adjusted the methodological application specified in ISO/TS 12913−2. For example, Zhu et al. expanded sound source identification using a 5-point Likert scale with two additional points [31].
RQ (3): Conceptualization and measurement of mental health outcomes
A recurring theme in all studies is the recourse to similar theoretical frameworks. One of these theories is the highly influential Attention Restoration Theory (ART) introduced by Kaplan and Kaplan (n = 20). It states that mental focus can be restored by reducing fatigue through exposure to the natural environment. Restorative environments must provide four components: fascination (elements that effortlessly capture attention without cognitive strain), extent (an environment that feels immersive and expansive), compatibility (a match between the environment and an individual’s needs or preferences) and a sense of being away (a sense of psychological distance from routine or stressful environments) [53]. Another theoretical framework prevalent throughout a multitude of studies (n = 13) is the Stress Reduction Theory (SRT) by Ulrich. It proposes that humans have an inherent evolutionary-based preference for natural settings, which are perceived as safe and supportive for survival. According to the SRT, viewing or experiencing nature triggers a positive emotional response, leading to reduced stress levels and improved mood [54]. Furthermore, thirteen studies used both theories as their theoretical framework. Only one study referenced no theoretical framework.
To evaluate participants’ perceptions of the restorative potential of urban green spaces, Yue Ma et al. and Wu et al. implemented the Perceived Restorativeness Scale (PRS), with its items based on ART [36,39,55]. Another prominent tool for measuring restoration in natural environments was the Perceived Restorativeness Soundscape Scale (PRSS) developed by Payne (n = 4). Although it is also based on ART, it is more focused on adapting the concept to auditory environments [56].
Other standardized questionnaires and scales to measure stress reduction and emotional responses were also included. Zhang et al. used the Perceived Stress Scale (PSS-14) to screen participants for psychological stress before participating in the study, while also implementing the Positive and Negative Affect Schedule (PANAS) to measure short-term mood changes and emotional recovery during changes in the acoustic environment [34,57,58]. Furthermore, some studies (n = 3) introduced physiological methods to assess stress markers, such as heartrate monitoring and skin conductivity measurements [34,42,43].
RQ (4): Soundscape elements and their associations with mental health
Overall, the studies showed a high degree of heterogeneity in their investigated relationships between soundscape elements and mental health. A recurring pattern throughout the included studies was the consistency in reporting positive relationships of natural soundscapes with different mental health parameters, despite different strategies in study designs and investigated soundscape elements/mental health parameters (n = 13). This was the case for both direct and indirect variables associated with mental health. Tian et al. reported improved relaxation and pleasure perception [37], whereas Zhang et al. reported reduced heart rate and heart rate variability indicating mental stress relief through natural sounds [34]. Lee et al. further contributed to this by covering similar results for the relationship between urban park natural soundscapes and well-being in Kuala Lumpur and Putrajaya [41].
The most frequently examined natural sounds included birdsong, water sounds and wind sounds. There was an emphasis on birdsong, as numerous (n = 9) of the included studies associated birdsong as a crucial part of urban green space soundscapes. The positive relationship between mental health and birdsong was reported in a variety of studies, including associations with relaxation, mental stress relief and PRS [31,34,39,47,50]. Zhao et al. supplemented these findings with investigations regarding the association of different bird species with the PRS and the inclusion of seasonal variance. They found that woodpecker and sparrow sounds had high PRS scores throughout summer and winter, whereas crow sounds were rated the lowest during both seasons [30]. Furthermore, higher perceived bird species richness had a positive relationship with the PRS and higher well-being [50]. Correspondingly, positive mental health associations with water and wind sounds were also reported consistently within a large proportion of studies [31,32,34,39,44,47].
Anthropogenic soundscapes had mixed results, with some studies indicating positive and others reporting negative mental health associations. Tian et al. stated that the perceived occurrence of human activity sounds has a significant negative correlation with pleasure and relaxation [37]. In contrast, Zhou et al. indicated that living sounds such as activities, laughter, and children frolicking have a positive association with emotions [32]. Li and Liu reported that social sounds had a positive relationship with the PRS through sounds like playing children, while loud conversations had a negative relationship [39].
The results for the associations of mechanical sounds with mental health were uniform throughout the included literature. Negative relationships have been reported across multiple studies, through various direct and indirect mechanisms. Mechanical sounds were associated with impeded recovery from mental stress [34], reduced perceived restoration [39] and lower well-being [32]. This was especially the case for traffic sounds, which were rated negatively throughout the studies [34,35,41]. Fig 4 illustrates the reported relationships across the included studies.
For further information on population characteristics and specific methodologies as well as key findings of the included studies see S1 and S2 Tables.
Discussion
With this scoping review, the existing body of literature on the relationship between mental health and soundscapes embedded in an urban greenspace context was mapped. The different methods were illuminated and approaches the authors applied and gained a more comprehensive understanding of the different investigated soundscape elements and their associations on mental health.
Study design and general methodology
Although the initial exclusion of laboratory studies influenced the heterogeneity of the reviewed studies, there were still variations in the applied study design approaches. It was shown that the reviewed literature uses different methodologies, with an emphasis on cross-sectional [29,43,44] and multi-methods designs [38,39,50]. Only a small fraction of the studies took temporal changes into account; Zhao et al. and Zhou et al. postulated better mental health outcomes in the summer months compared to winter [30,32]. The lack of seasonal variance analysis could carry a risk of overestimating the restorative potential of urban green spaces, as summer months include conditions with a possible positive influence, such as favorable weather and higher levels of natural sounds [59].
Although the reviewed studies showed great varieties in statistical methods and sample sizes, some studies resorted to convenience samples [37], while other studies specifically aimed at recruiting university students [42] despite college students not necessarily being able to represent the general public [20]. Moreover, only three studies used a mixed-methods design. The lack of qualitative methods seems to be a missed opportunity, as they can reveal important contextual meanings, emotions, and personal experiences, giving urban citizens an opportunity for involvement in the research process [60]. This approach would also align more with the original soundscape paradigm description of Schaefer, which emphasizes the “individual” acoustic experience [2].
Most of the included studies were published in China and after 2020. This surge in health-related studies embedded in environmental contexts could be part of the “Healthy China 2030” national strategy, which aims to improve the overall health of the population by setting targets for sustainable development until 2030 [61]. This geographical bias poses a challenge for the generalization of the results of this review. Prior research has found that the socio-cultural context influences individual’s perception of auditory environments [62–65]. Cross-national studies have shown that participants from different nations vary in their preferences for human or natural sounds [66,67], in how they link pleasantness and vibrancy to these sound categories [66,68], and in how they associate sound levels with liveliness or noise [69,70]. Due to their multidimensionality and context-dependence the socio-cultural influences are difficult to quantify [63]. Along with the scarcity of research from other regions, particularly low-income countries, this poses a challenge for cross-cultural comparison and affects the generalizability of the associations found between soundscapes elements and mental health in this review.
It is not necessarily clear what qualifies as an “urban green space”, as there might be some fundamental differences in the definition of terms. While Chinese studies tend to refer to outer skirt, large-scale forest/park environments as “urban parks” [30,39], studies from Europe have applied the term to more small scaled green spaces within the city [29,46]. Additionally, most of the included studies investigated more than one green space, complicating comparability across studies [29,32,38–42,46,48–50]. Global geographical differences in the flora and fauna should also be considered, as they were not addressed in the included studies.
Acoustic dimension and studied sound sources
While most of the included studies categorized soundscape elements into similar categories (natural, anthropogenic and mechanical), it is not entirely clear how the specific categorization into different sound sources is justified. Such heterogeneity in classification has also been noted in broader soundscape literature. For example, Brown et al. and Kang et al., highlight how inconsistent category boundaries and labeling complicate direct comparisons across studies, limiting opportunities for meta-analyses and the development of shared theoretical frameworks [71,72]. While ISO 12913−1 through ISO 12913−3 offer guidelines for terminology and categorization, researchers often apply these methods to specific study contexts or participant populations, thereby creating subtle (and sometimes major) deviations in practice. The strict compliance with ISO/TS 12913−2 guidelines is therefore rather limited, which is also an observation Aletta and Torresin made within their literature overview regarding ISO/TS 12913−2 data collection compliance [73].
Moreover, the social and cultural contexts of a given location can further influence classification. What one group perceives as “pleasant anthropogenic” (e.g., children playing) may be deemed intrusive or mechanical by another, complicating attempts to develop a universal taxonomy. Jaszczak et al., who combined interviews with experts and park visitors, demonstrated how qualitative approaches can help uncover nuanced perceptions of sound [45]. Similarly, Payne and Bruce used qualitative content analysis to generate open-ended themes, suggesting that top-down categorizations (e.g., natural vs. anthropogenic) do not always capture the lived or contextual experiences of sound [29].
Conceptualization and measurement of mental health outcomes
The prominence of ART [53] and SRT [54] in the included studies highlights the consistent relevance of these foundational frameworks in explaining how urban green space soundscapes promote mental health. In line with Kaplan and Kaplan’s concept of cognitive restoration, the PRS [36,39,55] and PRSS [56] were used across multiple studies to quantify how specific auditory features, such as birdsong, wind, or running water, can provide fascination, a sense of being away, and other restorative components. These attributes align with broader systematic reviews suggesting that exposure to natural environments can have a positive impact on mental health outcomes [74,75].
Parallel to ART, the SRT has provided a foundation for understanding the affective and physiological pathways through which natural exposure reduces stress. Research within this review revealed increasing use of objective stress markers, including heart rate variability and skin conductance [34,42,43], suggesting a shift towards biopsychosocial approaches that capture complex mental health outcomes outside of psychometric instruments. Hume and Ahtamad also suggest that using physiological markers alongside subjective evaluations of individual sounds offers a more comprehensive, objective means of assessing soundscapes [76].
Nevertheless, both our review and the general body of literature reveal methodological heterogeneity: researchers deploy a range of measures (PRS, PSS, PANAS and PRSS), as well as various physiological measurements. This diversity is associated with the multidisciplinary nature of soundscape research (e.g., environmental psychology vs. public health vs. urban planning) and can complicate cross-study comparisons. Consequently, this echoes critiques in environmental psychology that call for standardized outcome measures or at least clearly documented assessment protocols [72].
Soundscape elements and their associations with mental health
The findings from this review underline the restorative potential of natural soundscape elements which are consistently associated with reduced stress, enhanced mood and greater perceived restorativeness [31,33,37]. This was especially the case for birdsong, although there may be differences in the restoration potential between bird species [30]. These differences were also observed by Ratcliffe et al., who found that not all birdsongs were regarded as restorative [77]. Similar results were reported for water- and wind- related sounds. Lan et al. additionally highlighted the “sound-masking” properties of urban forest waterfronts [42]. These results further contribute to a growing body of sound-masking literature, which focuses on noise mitigation through water sounds [78–81].
Overall, these reported outcomes align with broader evidence showing that natural sounds can facilitate stress recovery [82,83]. However, the exact mechanisms behind these benefits may differ across cultural contexts, as individual preferences and sociodemographic backgrounds may mediate these associations. To account for this potential bias, a substantial portion of the studies collected sociodemographic information [32,46,47]. While information on age and gender was omnipresent, only a few of the included studies collected information on income and education. Lee et al. found that age and education, followed by park distance, sensitivity of park users as well as gender and occupation might influence soundscape perception. Thus, sociodemographic information should be collected more rigorously [84]. We assume that it can be challenging to determine whether a person’s response stems directly from the environment or is partly shaped by existing vulnerabilities or underlying health conditions. Moreover, the observed associations may not result solely from the sound itself; instead, it could be influenced by intervening factors such as overall health status or sleep disturbance [85].
Anthropogenic and mechanical soundscape elements yield mixed or negative results, with loud traffic consistently undermining psychological restoration [39,81]. These findings align with concerns raised by the WHO regarding chronic noise exposure and mental well-being [86]. Further classification of the relationship between traffic noise and mental health seems challenging, as the associated body of literature does not provide clarity. For instance, Hegewald et al. found no significant relationship between road noise and anxiety/depression [87], whereas Dzhambov and Lercher pointed out a potential link [88]. Notably, the current trend in soundscape research is to consider soundscape elements and their associated health parameters individually. Bai and Zhang expanded this narrow approach by introducing multi-element natural soundscapes, indicating that combined natural soundscapes have a higher restorative effect than single-element natural soundscapes [89]. Therefore, future research should advance the multi-element soundscape approach to gain a more holistic understanding of urban green space soundscapes.
Although our review focused primarily on auditory aspects, several studies indicated that integrating multisensory elements, combining visual with auditory inputs, can improve our understanding of soundscape experiences [35,42,44,48]. The corresponding body of literature suggests that early crossmodal interactions, particularly when emotional cues are present, may heighten attention and arousal, offering more differentiated insights than auditory data alone [90,91]. Shao et al. identified multiple correlations between visual attributes, aural attributes and sound sources, influencing perceived soundscape comfort [92]. According to experimental studies, soundscapes are rated more positively when accompanied by visual stimuli and audiovisual stimuli are more beneficial to mental health than auditory or visual stimuli alone, particularly when the visual and auditory components are congruent [93,94]. These findings highlight the need for research on multisensory or multimodal environmental perception to comprehensively understand the pathways through which urban green spaces influence mental health.
Strengths and limitations
One of the strengths of this scoping review is the team-based approach during the screening phase of the literature as well as the inclusion of multiple databases due to the multidisciplinary character of soundscape research. Another strength is the broad research strategy, as studies from different disciplines were included, thus allowing for a multidisciplinary scope. The compliance with Arksey and O’Malley’s framework as well as the use of the PRISMA-ScR-Checklist is considered as a strength as well.
However, this study had some limitations. Both the pilot testing of the data extraction and the original data extraction were conducted by only one person, thus deviating from the JBI recommendations regarding data extraction [23]. Although a broad search strategy was employed, limiting the language to English and German might have introduced bias. We also did not include grey literature, which could have provided additional perspectives for this review. The lack of stakeholder inclusion may also have reduced the depth of contextual insights, as local expertise in acoustic environments can signify specific knowledge about certain areas [95]. Conclusively, heterogeneity in methodologies posed a challenge for drawing firm conclusions across studies.
Conclusion
This scoping review provides the first comprehensive overview of current research on the associations between urban green space soundscapes and mental health. Most studies assessed soundscapes through both SPL and subjective evaluations, yet only a subset adhered to the methods and sound specifications of the ISO 12913 standard. A variety of mental health outcomes, based on frameworks such as ART or SRT, was examined, including stress reduction, perceived restoration, and affect, using instruments such as PRS, PRSS, PANAS, and physiological stress markers. The model presented in this review provides an overview of the observed relationships between urban green space soundscapes and mental health outcomes, contributing to a more structured understanding of the current evidence in this emerging research area.
We found that natural soundscape elements, particularly birdsong, were consistently associated with improved mental health outcomes (reduced stress, enhanced restoration and better overall mental well-being). The results for anthropogenic sounds were mixed, whereas mechanical sounds were rated negatively. However, the cross-sectional design and methodological heterogeneity of the studies limit comparability and preclude causal inference. The predominance of studies conducted in China further highlights a geographic imbalance and limits generalizability. The scarcity of research from low-income countries reveals an evidence gap, indicating the need for further studies in these regions to draw broader conclusions about the relationships between soundscapes and mental health.
The findings underscore the need for applying standardized soundscape classification and assessment procedures to improve comparability across studies. Contextual factors such as seasonal variation, cultural influences, and spatial characteristics could play critical roles in shaping how urban soundscapes affect mental health, emphasizing the importance of longitudinal and multisensory research approaches that capture temporal and contextual variation.
Understanding the links between acoustic environments in urban green spaces and mental health is increasingly relevant as urbanization progresses. By mapping existing evidence and highlighting methodological gaps, this review provides a foundation for more comprehensive, interdisciplinary research on this topic. The insights inform public health strategies and urban planning policies aimed at designing restorative urban green spaces that support mental health.
Supporting information
S1 Appendix. Detailed search strategy for all databases.
https://doi.org/10.1371/journal.pone.0344125.s001
(DOCX)
S1 Table. Population characteristics and specific methodologies of included studies (n = 22).
https://doi.org/10.1371/journal.pone.0344125.s002
(PDF)
S2 Table. Key findings, limitations and practical recommendations of included studies (n = 22).
https://doi.org/10.1371/journal.pone.0344125.s003
(PDF)
S2 File. Preferred Reporting Items for Systematic reviews and Meta-Analyses extension for Scoping Reviews (PRISMA-ScR) Checklist.
https://doi.org/10.1371/journal.pone.0344125.s005
(PDF)
References
- 1.
Schulte-Fortkamp B, Fiebig A, Sisneros JA, Popper AN, Fay RR. Soundscape: The development of a new discipline. Soundscapes: Humans and their acoustic environment. Cham: Springer International Publishing. 2023. 1–21.
- 2.
Schafer RM. The soundscape: our sonic environment and the tuning of the world. Rochester, Vermont: Destiny Books. 1977.
- 3. Aletta F, Oberman T, Kang J. Associations between positive health-related effects and soundscapes perceptual constructs: A systematic review. Int J Environ Res Public Health. 2018;15(11):2392. pmid:30380601
- 4.
International Organization for Standardization. ISO 12913-1:2014 Acoustics — Soundscape — Part 1: Definition and Conceptual Framework. Geneva: ISO. 2014.
- 5.
International Organization for Standardization. ISO/TS 12913-3:2019 Acoustics — Soundscape — Part 3: Data Analysis. Geneva: ISO. 2019.
- 6.
International Organization for Standardization. ISO/TS 12913-2:2018 Acoustics — Soundscape — Part 2: Data Collection and Reporting Requirements. Geneva: ISO. 2018.
- 7.
Kundu D, Pandey AK. World urbanisation: Trends and patterns. Kundu D, Sietchiping R, Kinyanjui M. Developing national urban policies: ways forward to green and smart cities. Singapore: Springer Nature Singapore. 2020. 13–49.
- 8. Fan L, Baharum MR. The effect of exposure to natural sounds on stress reduction: A systematic review and meta-analysis. Stress. 2024;27(1):2402519. pmid:39285764
- 9. Ratcliffe E. Sound and soundscape in restorative natural environments: A narrative literature review. Front Psychol. 2021;12:570563. pmid:33981262
- 10. Twohig-Bennett C, Jones A. The health benefits of the great outdoors: A systematic review and meta-analysis of greenspace exposure and health outcomes. Environ Res. 2018;166:628–37. pmid:29982151
- 11. Lee ACK, Maheswaran R. The health benefits of urban green spaces: A review of the evidence. J Public Health (Oxf). 2011;33(2):212–22. pmid:20833671
- 12. Brown AL, Kang J, Gjestland T. Towards standardization in soundscape preference assessment. Applied Acoustics. 2011;72(6):387–92.
- 13.
Peters MDJ, Godfrey C, McInerney P, Munn Z, Tricco AC, Khalil H. Scoping reviews. Aromataris E, Lockwood C, Porritt K, Pilla B, Jordan Z. JBI Manual for Evidence Synthesis. JBI: JBI. 2024.
- 14. Arksey H, O’Malley L. Scoping studies: Towards a methodological framework. International Journal of Social Research Methodology. 2005;8(1):19–32.
- 15. Levac D, Colquhoun H, O’Brien KK. Scoping studies: Advancing the methodology. Implement Sci. 2010;5:69. pmid:20854677
- 16. Daudt HML, van Mossel C, Scott SJ. Enhancing the scoping study methodology: A large, inter-professional team’s experience with Arksey and O’Malley’s framework. BMC Med Res Methodol. 2013;13:48. pmid:23522333
- 17. Westphaln KK, Regoeczi W, Masotya M, Vazquez-Westphaln B, Lounsbury K, McDavid L, et al. From Arksey and O’Malley and Beyond: Customizations to enhance a team-based, mixed approach to scoping review methodology. MethodsX. 2021;8:101375. pmid:34430271
- 18. Tricco AC, Lillie E, Zarin W, O’Brien KK, Colquhoun H, Levac D, et al. PRISMA Extension for Scoping Reviews (PRISMA-ScR): Checklist and explanation. Ann Intern Med. 2018;169(7):467–73. pmid:30178033
- 19.
World Health Organization. World Mental Health Report: Transforming Mental Health for All. Geneva: World Health Organization. 2022.
- 20. Peters MDJ, Marnie C, Tricco AC, Pollock D, Munn Z, Alexander L, et al. Updated methodological guidance for the conduct of scoping reviews. JBI Evid Synth. 2020;18(10):2119–26. pmid:33038124
- 21. Paez A. Gray literature: An important resource in systematic reviews. J Evid Based Med. 2017;10(3):233–40. pmid:28857505
- 22. Ouzzani M, Hammady H, Fedorowicz Z, Elmagarmid A. Rayyan-a web and mobile app for systematic reviews. Syst Rev. 2016;5(1):210. pmid:27919275
- 23. Pollock D, Peters MDJ, Khalil H, McInerney P, Alexander L, Tricco AC, et al. Recommendations for the extraction, analysis, and presentation of results in scoping reviews. JBI Evid Synth. 2023;21(3):520–32. pmid:36081365
- 24.
Van Rossum G, Drake FL. Python reference manual. Amsterdam: Centrum voor Wiskunde en Informatica Amsterdam. 1995.
- 25. Whitaker J. Basemap 2.0.0: Matplotlib. https://matplotlib.org/basemap/stable/index.html. Accessed 2025 November 21.
- 26. Wessel P, Luis JF, Uieda L, Scharroo R, Wobbe F, Smith WHF, et al. The generic mapping tools version 6. Geochem Geophys Geosyst. 2019;20(11):5556–64.
- 27. Wessel P, Smith WHF. A global, self‐consistent, hierarchical, high‐resolution shoreline database. J Geophys Res. 1996;101(B4):8741–3.
- 28. Free Software Foundation Inc. GNU Lesser General Public License. https://www.gnu.org/licenses/lgpl-3.0.html#license-text. 2007. Accessed 2025 November 21.
- 29. Payne SR, Bruce N. Exploring the relationship between urban quiet areas and perceived restorative benefits. Int J Environ Res Public Health. 2019;16(9):1611. pmid:31071957
- 30. Zhao W, Li H, Zhu X, Ge T. Effect of birdsong soundscape on perceived restorativeness in an urban park. Int J Environ Res Public Health. 2020;17(16):5659. pmid:32764453
- 31. Zhu Y, Huang N, Weng Y, Tong H, Wang X, Chen J, et al. Does soundscape perception affect health benefits, as mediated by restorative perception?. Forests. 2023;14(9):1798.
- 32. Zhou Y, Dai P, Zhao Z, Hao C, Wen Y. The Influence of urban green space soundscape on the changes of citizens’ emotion: A case study of beijing urban parks. Forests. 2022;13(11):1928.
- 33. Zhang T, Liu J, Li H. Restorative effects of multi-sensory perception in urban green space: A case study of urban park in Guangzhou, China. Int J Environ Res Public Health. 2019;16(24):4943. pmid:31817595
- 34. Zhang J, Yan H, Wang D. Effects of acoustic environment types on stress relief in urban parks. Int J Environ Res Public Health. 2023;20(2):1082. pmid:36673837
- 35. Yin Y, Shao Y, Meng Y, Hao Y. The effects of the natural visual-aural attributes of urban green spaces on human behavior and emotional response. Front Psychol. 2023;14:1186806. pmid:37564319
- 36. Wu Y, Liu J, Quevedo JMD, Cheng H, Yu K, Kohsaka R. Critical factors influencing visitor emotions: Analysis of “restorativeness” in urban park visits in Fuzhou, China. Front Public Health. 2023;11:1286518. pmid:38074738
- 37. Tian L, Winterbottom D, Liu J. Soundscape optimization strategies based on landscape elements in urban parks: A case study of greenlake park in kunming. Sustainability. 2023;15(13):10155.
- 38. Marafa LM, Tsang F, Watts G, Yuan X. Perceived tranquility in green urban open spaces. World Leisure Journal. 2018;60(3):221–34.
- 39. Li W, Liu Y. Predicting the impact of integrated audio-visual environments on perceived restorative benefits across different park types: A field study based on seven parks in Hangzhou, China. Urban Forestry & Urban Greening. 2024;101:128517.
- 40. Li S, Chen T, Chen F, Mi F. How does the urban forest environment affect the psychological restoration of residents? A natural experiment in environmental perception from Beijing. Forests. 2023;14(10):1986.
- 41. Siaw Ling Lee J, Hosni N, Rusli N, Abdul Ghani N. Influence of perceived soundscape and sound environment on subjective well-being of park visitors. JSSH. 2023;31(4):1621–48.
- 42. Lan Y, Tang Y, Liu Z, Yao X, Zhu Z, Liu F, et al. Combined effects of the visual–acoustic environment on public response in urban forests. Forests. 2024;15(5):858.
- 43. Korpilo S, Nyberg E, Vierikko K, Ojala A, Kaseva J, Lehtimäki J, et al. Landscape and soundscape quality promote stress recovery in nearby urban nature: A multisensory field experiment. Urban Forestry & Urban Greening. 2024;95:128286.
- 44. Jin T, Lu J, Shao Y. Exploring the impact of visual and aural elements in urban parks on human behavior and emotional responses. Land. 2024;13(9):1468.
- 45. Jaszczak A, Pochodyła E, Kristianova K, Małkowska N, Kazak JK. Redefinition of park design criteria as a result of analysis of well-being and soundscape: The case study of the kortowo park (Poland). Int J Environ Res Public Health. 2021;18(6):2972. pmid:33799383
- 46. Herranz-Pascual K, Aspuru I, Iraurgi I, Santander Á, Eguiguren JL, García I. Going beyond quietness: Determining the emotionally restorative effect of acoustic environments in urban open public spaces. Int J Environ Res Public Health. 2019;16(7):1284. pmid:30974811
- 47. Guo Y, Jiang X, Zhang L, Zhang H, Jiang Z. Effects of sound source landscape in urban forest park on alleviating mental stress of visitors: Evidence from huolu mountain forest park, Guangzhou. Sustainability. 2022;14(22):15125.
- 48. Guo X, Liu J, Albert C, Hong X-C. Audio-visual interaction and visitor characteristics affect perceived soundscape restorativeness: Case study in five parks in China. Urban Forestry & Urban Greening. 2022;77:127738.
- 49. Guo X, Jiang S-Y, Liu J, Chen Z, Hong X-C. Understanding the role of visitor behavior in soundscape restorative experiences in urban parks. Forests. 2024;15(10):1751.
- 50. Fisher JC, Irvine KN, Bicknell JE, Hayes WM, Fernandes D, Mistry J, et al. Perceived biodiversity, sound, naturalness and safety enhance the restorative quality and wellbeing benefits of green and blue space in a neotropical city. Sci Total Environ. 2021;755(Pt 2):143095. pmid:33139002
- 51. Kasten EP, Gage SH, Fox J, Joo W. The remote environmental assessment laboratory’s acoustic library: An archive for studying soundscape ecology. Ecological Informatics. 2012;12:50–67.
- 52. Jeon JY, Hong JY, Lee PJ. Soundwalk approach to identify urban soundscapes individually. J Acoust Soc Am. 2013;134(1):803–12. pmid:23862886
- 53.
Kaplan R, Kaplan S. The experience of nature: A psychological perspective. Cambridge: Cambridge University Press. 1989.
- 54. Ulrich RS, Simons RF, Losito BD, Fiorito E, Miles MA, Zelson M. Stress recovery during exposure to natural and urban environments. Journal of Environmental Psychology. 1991;11(3):201–30.
- 55. Hartig T, Korpela K, Evans GW, Gärling T. A measure of restorative quality in environments. Scandinavian Housing and Planning Research. 1997;14(4):175–94.
- 56. Payne SR. The production of a perceived restorativeness soundscape scale. Applied Acoustics. 2013;74(2):255–63.
- 57. Cohen S, Kamarck T, Mermelstein R. A global measure of perceived stress. Journal of Health and Social Behavior. 1983;24(4):385.
- 58. Watson D, Clark LA, Tellegen A. Development and validation of brief measures of positive and negative affect: The PANAS scales. J Pers Soc Psychol. 1988;54(6):1063–70. pmid:3397865
- 59. Sun Y, Wang S, Feng J, Wang T. Diel and seasonal variability of the forest soundscape in the Northeast China Tiger and Leopard National Park. Biodiversity Science. 2023;31(1):22523.
- 60. Silva JP, Ribeiro AI. Using qualitative methods to understand the interconnections between cities and health: A methodological review. Public Health Rev. 2024;45:1606454. pmid:38651134
- 61.
Li B, Ma X, Yu Y, Wang G, Zhuang N, Liu H, et al. Healthy China 2030: Promoting health and longevity of the whole nation. Li B. Tutorial for outline of the Healthy China 2030 Plan. Singapore: Springer Singapore. 2020. 1–9.
- 62. Kim S. Do we hear differently? Comparing spatial hearing between East-Asian and North-American listeners. Acoust Sci & Tech. 2020;41(1):129–33.
- 63. Zhang Y, Wu D, Kang J. Beyond translation: Rethinking soundscape emotion assessments from a cultural perspective. Nexus. 2025;2(2):100071.
- 64. Zhang R, Ma H, Wang C, Zhang Y, Kang J. Soundscape and its context: A framework based on a systematic review. J Acoust Soc Am. 2025;157(6):4417–36. pmid:40525832
- 65. Aletta F, Lam B, Tarlao C, Oberman T, Mitchell A. Introduction to the special issue on: Advances in soundscape: Emerging trends and challenges in research and practice. J Acoust Soc Am. 2025;157(6):4411–6. pmid:40526448
- 66. Jeon JY, Hong JY, Lavandier C, Lafon J, Axelsson Ö, Hurtig M. A cross-national comparison in assessment of urban park soundscapes in France, Korea, and Sweden through laboratory experiments. Applied Acoustics. 2018;133:107–17.
- 67. Yu C-J, Kang J. Soundscape in the sustainable living environment: A cross-cultural comparison between the UK and Taiwan. Sci Total Environ. 2014;482–483:501–9. pmid:24290144
- 68. Aletta F, Oberman T, Mitchell A, Erfanian M, Kang J. Soundscape experience of public spaces in different world regions: A comparison between the European and Chinese contexts via a large-scale on-site surveya). J Acoust Soc Am. 2023;154(3):1710–34. pmid:37712752
- 69. Nguyen T, Nagahata K, Morinaga M, Ma H. Cross-cultural comparison of soundscape evaluation between Japanese and Vietnamese using standardized attributes. Applied Acoustics. 2023;213:109627.
- 70. Manohare M, Aletta F, Oberman T, Elangovan R, Parida M, Kang J. Cross-country variation in psychophysiological responses to traffic noise exposure: Laboratory experiments in India and the UKa). J Acoust Soc Am. 2024;156(5):3067–79. pmid:39499043
- 71.
Brown AL, Gjestland T, Dubois D. Acoustic environments and soundscapes. Soundscape and the Built Environment. Boca Raton: CRC Press. 2015. 1–16.
- 72. Kang J, Aletta F, Gjestland TT, Brown LA, Botteldooren D, Schulte-Fortkamp B, et al. Ten questions on the soundscapes of the built environment. Building and Environment. 2016;108:284–94.
- 73. Aletta F, Torresin S. Adoption of ISO/TS 12913-2:2018 protocols for data collection from individuals in soundscape studies: An overview of the literature. Curr Pollution Rep. 2023;9(4):710–23.
- 74. Bowler DE, Buyung-Ali LM, Knight TM, Pullin AS. A systematic review of evidence for the added benefits to health of exposure to natural environments. BMC Public Health. 2010;10:456. pmid:20684754
- 75. Jimenez MP, DeVille NV, Elliott EG, Schiff JE, Wilt GE, Hart JE, et al. Associations between nature exposure and health: A review of the evidence. Int J Environ Res Public Health. 2021;18(9):4790. pmid:33946197
- 76. Hume K, Ahtamad M. Physiological responses to and subjective estimates of soundscape elements. Applied Acoustics. 2013;74(2):275–81.
- 77. Ratcliffe E, Gatersleben B, Sowden PT. Bird sounds and their contributions to perceived attention restoration and stress recovery. Journal of Environmental Psychology. 2013;36:221–8.
- 78. Li J, Maffei L, Pascale A, Masullo M. Effects of spatialized water-sound sequences for traffic noise masking on brain activities. J Acoust Soc Am. 2022;152(1):172. pmid:35931502
- 79. Jeon JY, Lee PJ, You J, Kang J. Acoustical characteristics of water sounds for soundscape enhancement in urban open spaces. J Acoust Soc Am. 2012;131(3):2101–9. pmid:22423706
- 80. Wang Q, Hongwei W, He X, Huang Z, Yang C. Evaluating the mitigating effects of water sounds on multi-dimensional negative reactions due to secondary radiation noise. Acta Acust. 2024;8:30.
- 81. Zhang S, Chen L. Acoustic information masking effects of natural sounds on traffic noise based on psychological health in open urban spaces. Front Public Health. 2023;11:1031501. pmid:36935713
- 82. Alvarsson JJ, Wiens S, Nilsson ME. Stress recovery during exposure to nature sound and environmental noise. Int J Environ Res Public Health. 2010;7(3):1036–46. pmid:20617017
- 83. Buxton RT, Pearson AL, Allou C, Fristrup K, Wittemyer G. A synthesis of health benefits of natural sounds and their distribution in national parks. Proc Natl Acad Sci U S A. 2021;118(14):e2013097118. pmid:33753555
- 84. Ling Lee JS, Hosni N, Rusli N, Ghani NA. Soundscape perception and preference in the context of Malaysian Urban Parks. IOP Conf Ser: Earth Environ Sci. 2023;1274(1):012022.
- 85.
Lercher P, Dzhambov AM. Soundscape and health. Schulte-Fortkamp B, Fiebig A, Sisneros JA, Popper AN, Fay RR. Soundscapes: humans and their acoustic environment. Cham: Springer International Publishing. 2023. 243–76.
- 86.
World Health Organization. Environmental noise guidelines for the European Region. Copenhagen: World Health Organization. 2018.
- 87. Hegewald J, Schubert M, Freiberg A, Romero Starke K, Augustin F, Riedel-Heller SG, et al. Traffic noise and mental health: A systematic review and meta-analysis. Int J Environ Res Public Health. 2020;17(17):6175. pmid:32854453
- 88. Dzhambov AM, Lercher P. Road traffic noise exposure and depression/anxiety: An updated systematic review and meta-analysis. Int J Environ Res Public Health. 2019;16(21):4134. pmid:31717834
- 89. Bai Z, Zhang S. Effects of different natural soundscapes on human psychophysiology in national forest park. Sci Rep. 2024;14(1):17462. pmid:39075109
- 90. Wu C, Stefanescu RA, Martel DT, Shore SE. Listening to another sense: somatosensory integration in the auditory system. Cell Tissue Res. 2015;361(1):233–50. pmid:25526698
- 91. Gerdes ABM, Wieser MJ, Alpers GW. Emotional pictures and sounds: A review of multimodal interactions of emotion cues in multiple domains. Front Psychol. 2014;5:1351. pmid:25520679
- 92. Shao Y, Hao Y, Yin Y, Meng Y, Xue Z. Improving soundscape comfort in urban green spaces based on aural-visual interaction attributes of landscape experience. Forests. 2022;13(8):1262.
- 93. Xu X, Wu H. Audio-visual interactions enhance soundscape perception in China’s protected areas. Urban Forestry & Urban Greening. 2021;61:127090.
- 94. Kong P-R, Han K-T. Psychological and physiological effects of soundscapes: A systematic review of 25 experiments in the English and Chinese literature. Sci Total Environ. 2024;929:172197. pmid:38582113
- 95.
Schulte-Fortkamp B, Jordan P. Soundscape: the holistic understanding of acoustic environments. Schulte-Fortkamp B, Fiebig A, Sisneros JA, Popper AN, Fay RR. Soundscapes: humans and their acoustic environment. Cham: Springer International Publishing. 2023. 49–79.