Skip to content

Brief Research Report

Frontiers in Bird Science ·

Volume 5 - 2026 | https://doi.org/10.3389/fbirs.2026.1740187

Bird species traits in recreational areas – building a human restoration value of bird species and connecting it to the mental well-being of recreationists in Germany

  • Janina Vanhöfen1*corresponding author
  • Nadine Kalb1
  • Christoph Randler1
  1. Didactics of Biology, Department of Biology, Eberhard Karls University Tübingen, Tübingen, Germany
Article metrics0 viewsView details

Abstract

Preferences for animal species and their popularity vary significantly between species, even within a taxonomic group such as birds. Understanding which characteristics influence human preferences for certain bird species can help to promote targeted conservation measures and define so-called ‘flagship species’ for conservation programs. However, the extent to which such species-specific characteristics also affect human psychological well-being remains largely unclear. The positive impact of interacting with birds on the human psyche is currently being researched. However, a grey goose could potentially have a different impact on the human experience of nature and, thus, also on psychological well-being in local recreation areas than, for example, a blue tit or a nightingale. Which species-specific characteristics play a role in this is still largely unclear. We therefore compiled data on species-specific characteristics for 118 bird species that were mapped in 40 different areas in southwest Germany. One factor was summarized from four species traits in a principal component analysis, building the human restoration value. An index was calculated for each location (HRV = human restoration value of bird species). In a second step, these indices were then correlated with the mental well-being and place attachment of 1,184 people in the 40 project areas. The results show a positive correlation between the HRV and satisfaction. Compiling species-specific characteristics relevant to human well-being into one factor, such as the HRV presented here, might enable future projects to investigate the recreational value of nature areas based on bird abundance.

Keywords

1 Introduction

Well-being and mental health research is a rapidly growing field of study within the area of birds and ecology. One of the prominent ideas is that being outside in nature often leads to increased mental well-being among recreationists, with research typically focusing on the characteristics of the area or landscape. Earlier studies have also theorized that biodiversity is one of the main drivers of this phenomenon [see, for example, but not exclusively, Adjei and Agyei (2015); De Vries and Snep (2019); Houlden et al. (2021)]. Research has shown mixed results between the effects of biodiversity, perceived biodiversity, and experimentally increased biodiversity. We propose here that birds, as a key component of an area’s characteristics, play an important role in this. Birds can be perceived both directly and unconsciously. They are a taxonomic group that is easily recognised and observed by people (Cox and Gaston, 2015), regardless of ornithological knowledge. Additionally, they are a common and well-studied taxon, sensitive to anthropogenic influences (Gregory et al., 2008) and therefore valuable indicators of biological diversity, ecological conditions, and environmental status (Randler and Koch, 2025). Their species characteristics are closely linked to their habitat and ecosystem services (Sekercioglu, 2006), and they are well-suited to connect urban residents with nature (Belaire et al., 2015). In contrast to many mammals and reptiles, birds are mostly diurnal, and many are found in urban areas. Some are also extremely common in city settings.

Birds have been linked to increased happiness (White et al., 2023) and improved mental health (Xie et al., 2023) in people. Their sounds play a crucial role (Chen et al., 2022) in stress relief, though not all bird sounds are equally beneficial (Ratcliffe et al., 2013). Earlier studies often focused on bird species richness (Methorst et al., 2021). Some also looked at the effects of bird observation (Cox and Gaston, 2015), or bird song (Stobbe et al., 2022), sometimes even attempting to artificially increase bird song to foster well-being (Ferraro et al., 2020). However, some research has found no association of bird species richness with people’s mental well-being (Cox et al., 2017; Taylor et al., 2018). Some only found a relationship with perceived bird diversity instead of actual biodiversity measures (Dallimer et al., 2012). This inconsistent relationship between bird diversity, perceived bird diversity, and human mental health (Lovell et al., 2014) renders it difficult to measure if and how conservation efforts in nature could boost mental well-being. Since experiencing biodiverse urban green spaces can evidently bring joy (Douglas and Evans, 2021) and generally has positive effects (Carrus et al., 2015), it’s important to look beyond general assessments of bird diversity and maybe look at the composition of bird species in an area.

To our knowledge, no studies have yet assessed the bird species characteristics and traits that may be responsible for the mental well-being of recreationists. Additionally, only a few studies have considered that not all bird species equally affect people [see, for example, Fisher et al. (2023); Garnett et al. (2018); Randler and Koch (2025); Randler et al. (2023); Ratcliffe et al. (2013)]. This might be important because there is a large variation in the perception, likeability, and preferences of bird species (Albert et al., 2018; Veríssimo et al., 2014; White et al., 2023) as well as in the bird species themselves. Aesthetically pleasing animals are often considered charismatic (Prokop et al., 2025; Veríssimo et al., 2014), and small and vividly colored birds are often perceived as more beautiful (Haukka et al., 2023; Santangeli et al., 2023). Most people also share a preference for birdsong (Chen et al., 2022), but some songs and calls can also annoy urban residents (Belaire et al., 2015; Pejchar et al., 2025). Some bird species, such as the hooded crow, for example, are also associated with problems such as trash scattering, noise disturbance, and aggressive behavior (Kövér et al., 2022). Lišková and Frynta (2013) have already emphasized that finding the traits that determine human preference towards birds may help promote conservation programs. Earlier studies on flagship species have suggested certain species characteristics of liked animal species, with a high body mass (Santarém et al., 2019; Smith et al., 2012), and a large body size often being linked to charisma (Albert et al., 2018; Callaghan et al., 2021).

Finding the species traits important for human mental well-being may explain the discrepancies between studies, since not all birds are present in all study areas similarly. The study by Garnett et al. (2018), for example, found a preference for small colorful birds with melodious song, but participants then nominated mostly large and well-known species as most attractive. According to Haukka et al. (2023), aesthetic attraction is dependent on a set of features that make something interesting or likable, usually composed of visual and emotional cues. This is why many liked species exhibit a bright appearance, colors, or color patterns (Santarém et al., 2019; Veríssimo et al., 2014). Aesthetic attraction seems to be highest for smaller birds, with vivid colors and extreme ornaments (Santangeli et al., 2023). Other factors seemingly playing a role are visibility, rarity, familiarity, or encounter rate (Santangeli et al., 2023; Schlegel and Rupf, 2010; Veríssimo et al., 2014). Some charismatic species are also considered “sweet” or “cute” (Albert et al., 2018; Borgi et al., 2014). The concept of cuteness is based on the baby schema by Lorenz (1943), which sums up characteristics that are supposed to trigger an innate caring behavior in humans. These characteristics consist of a large head in relation to body size, short and thick extremities, a large set of eyes, a large, rounded forehead, and round, protruding, chubby cheeks (Lorenz, 1943). Animals exhibiting the baby schema are often perceived as cute and draw the viewer’s attention (Albert et al., 2018). Bird species perceived as cute elicited a higher willingness to protect, as well as a bright coloration (Randler and Koch, 2025).

We hypothesize that the human perception of birds is strongly linked to mental well-being, and therefore, the species composition in an area may determine the mental well-being benefits received when visiting. In this study, we investigate the link between human perception of bird traits and well-being to determine if and how species composition in recreational areas affects place attachment and well-being of visitors.

2 Method

This study consists of two parts. First, a survey was conducted among people in recreational areas to assess their mental well-being. In the same areas, the bird species were recorded. In a second step, the well-being data were related to the bird species characteristics.

2.1 Mental well-being

The pen-and-paper survey took place in May-June 2022 in 40 recreational areas between Rottenburg am Neckar and Stuttgart in Baden-Württemberg, southwest Germany.

Using voluntary response sampling, pedestrians over the age of 18 were invited to participate in the questionnaire if they had already been in the respective area for a while. They answered the survey once, for a situational assessment after being in the study area. The study had 1184 participants. 54.9% of them identified as female, 44.1% as male (0.2% identified as diverse, 0.8% preferred not to answer the question). The age ranged from 18 to 89 years old (1.9% did not answer), with the mean age being 43.34 ± 17.75 years. For more details on the questionnaire, see Table 1 and Vanhöfen et al. (2025).

Table 1. Mental well-being items for the biodiversity and health survey.

ConceptItemSource
Satisfaction(5-point Likert scale)Overall, how satisfied were you with your visit today?Arlinghaus (2006)
Emotions(5-point Likert scale)I feel…Calm and relaxedPeacefulRefreshedWhite et al. (2013)Wyles et al. (2019)
Recalled Restoration(5- point Likert scale)How refreshed do you feel now compared to before your visit?Young et al. (2020)
Place attachment - Identity(5-point Likert scale)I feel very connected to this area hereThis area is very special to me.I can identify well with this area.Boley et al. (2021)
Place attachment - Recovery(5-point Likert scale)Visiting this place gives me a feeling of freedom.I can clear my head here.Being here helps me to feel healthy.Bryce et al. (2016)

For more information on the survey, see also Vanhöfen et al. (2025).

Three subjective measures for assessing mental well-being were used: recalled restoration, emotions, and satisfaction.

Recalled restoration after the visit was asked for with one item, on a categorical scale with 6 categories adapted from Young et al. (2020). For better comparability between the scales in our study, we recoded the recalled restoration Scale into a 0 (“cannot say”) to 5 (“significantly more recovered”) Likert scale, with 0 being considered as missing data.

Emotions or self-reported restoration were measured with three items on a 5-point Likert scale, adapted from White et al. (2020); Wyles et al. (2019). Items included questions for a situational positive state of mind. The scale had a Cronbach’s alpha of 0.77 in our study.

Satisfaction was asked for with one item (Overall, how satisfied were you with your visit today)? on a categorical 5-point Likert scale adapted from Arlinghaus (2006).

Additionally, we asked for place attachment on a 5-point Likert scale (full scale with a Cronbach’s alpha = 0.88, Vanhöfen et al. (2025)). Place attachment is the emotional bond humans form with a place. It has been influenced by visit satisfaction in earlier studies (Prayag and Ryan, 2011). Bryce et al. (2016) identified constructs of place identity and therapeutic value as cultural ecosystem services, benefitting people’s well-being. According to them, most benefits associated with visiting nature can depend on specific habitats and landscapes. It could also possibly be connected to the bird species present in the area and their traits. According to factor analysis, the place attachment scale can be split into two variables, namely place attachment identity and place attachment recovery. The recovery scale (Cronbach’s alpha = 0.86) is derived from the therapeutic value by the place attachment assessment of Bryce et al. (2016). The identity scale (Cronbach’s alpha = 0.87) is derived from the abbreviated three-item place identity scale of Boley et al. (2021).

2.2 Bird species traits

2.2.1 Bird species selection

The avifauna of Germany is typical of central Europe. The total list of bird species for Germany contains 527 bird species (including vagrants), of which about 250 are regular breeders. In addition, there are about 20 non-native breeding species (Barthel and Krüger, 2019). Since only birds present in a respective area can be experienced by people, bird species and their abundance were recorded by ornithologists via the standard procedure of Bibby et al. (2000). Bird surveys were carried out two times in the morning and once in the afternoon, with each morning survey having at least 3 weeks in between. In a 250m radius on footpaths, all individuals seen and heard in the span of 15 minutes were recorded. Data was then compiled into a list of all species recorded at each site, and the highest species frequency present was used further.

This data resulted in a total of 118 species present in the 40 study areas during the duration of the pen-and-paper survey (Vanhöfen et al., 2025), for which the trait data were collected.

2.2.2 Variable selection and data collection

Cuteness data were taken from the study by Randler and Koch (2025), in which the participants were asked to rate the cuteness of bird pictures on a 5-point Likert-type scale, following Borgi et al. (2014).

Brightness data were taken from Randler et al. (2023). In this study, 769 people estimated the brightness of the male breeding plumage on a scale from 0 to 100.

In another survey study (Lukanowski, 2023), participants were asked to rate bird song on their beauty on a Likert-type scale from 1 to 5, resulting in the data for the beauty of song. The audio was taken from Bergmann et al. (2020).

Lastly, data on visual attractiveness were taken from the iRateBirds study by Haukka et al. (2023), using the iRateBirds database. In this study, respondents (n = 6,212) were asked to rate the appearance of bird species on a scale from 1 (low) to 10 (high) based on photographs from the Cornell Lab of Ornithology’s Macaulay Library.

2.3 Statistical procedure

Statistical procedures and analyses were performed using SPSS (version 29.0.2.0) and Excel. For assessing internal consistency, we used Cronbach’s α. For the exploratory factor analysis, we used a principal component analysis with a varimax extraction. And finally, for the correlation of factor scores with mental well-being data, we used Spearman’s rho correlations.

2.3.1 Factor analysis of variables

Based on a principal component analysis, the variables visual attractiveness, brightness, cuteness, and beauty of song were combined into a single factor, which was then saved as a standardized regression score, now labeled HRVspecies = human restoration value of the respective bird species.

All variables load strongly on one factor (see Table 2), allowing for continuing with only one component extracted.

Table 2. Component matrix. extraction method: principal component analysis.

VariablesComponent 1 = HRVspecies
Cuteness.855
Brightness.618
iRateBirds (visual attractiveness).599
Beauty of song.552

2.3.2 Value per place

The factor was then used to calculate values for each study area. For this value on the place level, the frequency of the respective bird species was used as well to account for mass or rarity occurrences of specific species. Every study area, therefore, receives a specific value for the HRVplace.

HRVPlace=Mean(∑species=1118(HRVspecies*frequencyspecies))

2.3.3 Correlation with mental well-being

Finally, the HRVplace was correlated with the mental well-being of people at the place level using a non-parametric Spearman-rho correlation analysis.

3 Results

The factor values for the HRV of the respective bird species are shown in Table 3. The bird species are ranked from highest to lowest by their HRVspecies score. A high HRVspecies score means a positive evaluation of species traits.

Table 3. Bird species ranked according to their factor values of the HRVspecies.

Nr.SpeciesHRVspeciesNr.SpeciesHRVspecies
1Erithacus rubecula2.7160Motacilla alba0.03
2Cyanistes caeruleus2.6961Picus canus0.00
3Parus major2.0562Tadorna tadorna0.00
4Regulus ignicapilla1.8763Acrocephalus arundinaceus0.00
5Pyrrhula pyrrhula1.7064Larus michahellis0.00
6Emberiza citrinella1.4765Muscicapa striata-0.01
7Poecile montanus1.4666Certhia brachydactyla-0.03
8Carduelis carduelis1.4367Mergus merganser-0.03
9Alcedo atthis1.3168Aythya fuligula-0.05
10Regulus regulus1.2769Fringilla montifringilla-0.07
11Hirundo rustica1.2670Lullula arborea-0.07
12Fringilla coelebs1.2471Milvus migrans-0.08
13Periparus ater1.1572Tadorna ferruginea-0.08
14Oriolus oriolus1.0873Passer domesticus-0.12
15Poecile palustris0.9974Acrocephalus scirpaceus-0.15
16Aegithalos caudatus0.9275Circus aeruginosus-0.18
17Picus viridis0.9176Coturnix coturnix-0.22
18Aix galericulata0.9177Turdus merula-0.22
19Coccothraustes coccothraustes0.9178Falco subbuteo-0.24
20Phoenicurus phoenicurus0.8979Accipter nisus-0.24
21Ficedula hypoleuca0.8180Pernis apivorus-0.26
22Phylloscopus trochilus0.8181Garrulus glandarius-0.29
23Dendrocopos major0.8082Sturnus vulgaris-0.30
24Falco tinnunculus0.7983Prunella modularis-0.33
25Leiopicus medius0.7784Sylvia atricapilla-0.34
26Saxicola rubicola0.7685Anthus spinoletta-0.36
27Delichon urbicum0.6886Turdus pilaris-0.39
28Sitta europaea0.6687Anas crecca-0.41
29Vanellus vanellus0.6388Tachybaptus ruficollis-0.46
30Spinus spinus0.6389Cuculus canorus-0.46
31Troglodytes troglodytes0.5890Aythya ferina-0.49
32Motacilla flava0.5391Passer montanus-0.51
33Lophophanes cristatus0.5192Acrocephalus palustris-0.51
34Certhia familiaris0.4993Anas platyrhynchos-0.61
35Turdus viscivorus0.3794Streptopelia decaocto-0.66
36Anser indicus0.3695Anthus pratensis-0.67
37Motacilla cinerea0.3396Milvus milvus-0.69
38Serinus serinus0.3397Alauda arvensis-0.73
39Phylloscopus collybita0.3298Cygnus olor-0.77
40Asio otus0.2899Dryocopus martius-0.79
41Phalacrocorax carbo0.28100Pica pica-0.85
42Phylloscopus sibilatrix0.27101Ciconia ciconia-1.00
43Sylvia borin0.27102Fulica atra-1.04
44Emberiza schoeniclus0.25103Gallinula chloropus-1.11
45Netta rufina0.21104Chroicocephalus ribibundus-1.13
46Ficedula albicollis0.21105Apus apus-1.22
47Sylvia curruca0.20106Columba oenas-1.33
48Chloris chloris0.15107Jynx torquilla-1.34
49Phoenicurus ochruros0.14108Buteo buteo-1.40
50Lanius collurio0.12109Alopochen aegyptiaca-1.41
51Sylvia communis0.10110Anser anser-1.71
52Ardea alba0.10111Columba palumbus-1.76
53Emberiza hortulana0.10112Corvus corone-1.82
54Anthus trivialis0.10113Columba livia-2.15
55Linaria cannabina0.10114Ardea cinerea-2.15
56Charadrius dubius0.08115Corvus corax-2.17
57Luscinia megarhynchos0.08116Circus cyaneus-2.32
58Turdus philomelos0.07117Coloeus monedula-2.43
59Podiceps cristatus0.06118Corvus frugilegus-2.45

For the correlation with mental well-being, the HRV significantly correlated with satisfaction (Table 4). However, the other correlations falied significance only marginally.

Table 4. Spearman´s rho correlation of the mental well-being variables with the subjective HRV on the place level (N = 40).

HRVplace
EmotionsCorrelation Coefficient.289
Sig. (2-tailed).071
SatisfactionCorrelation Coefficient.357*
Sig. (2-tailed).024
RestorationCorrelation Coefficient.283
Sig. (2-tailed).076
Place Attachment IdentityCorrelation Coefficient.127
Sig. (2-tailed).433
Place Attachment RecoveryCorrelation Coefficient.269
Sig. (2-tailed).093

*Correlation is significant at the 0.05 level (2-tailed).

Bold text indicates significant values.

With increasing HRVplace, satisfaction with the visit increased significantly (Figure 1). This also means that bird species with a high HRVspecies (for example, Erithacus rubecula or Cyanistes caeruleus) have a positive effect on satisfaction after the visit. In contrast, species like Carrion Crow (Corvus corone) or Feral Pigeon (Columba livia f. domestica) negatively affect the satisfactory value of a given place. By using the species frequency in the HRVplace calculation, we were able to account for mass aggregations, which are often found in geese, pigeons, or crows, and which are a reality for urban parks.

Scatter plot of the positive relationship between HRV<sub>place</sub> and satisfaction.
Figure 1. Scatter plot of the positive relationship between HRVplace and satisfaction.

4 Discussion

We here propose a new measure, the Human Restoration Value, to assess the beneficial influence of birds on human well-being. For this value, bird species traits were combined into one value and then related to the mental well-being of humans. This method could potentially be used for many other conservation questions, as discussed below. Each bird species was assigned a value that is based on previous studies on likeability, pleasantness, and attractiveness. Thus, more likable species receive a higher value. This factor can now be used to determine which bird species are perceived favorably by people.

Moreover, based on field work on 40 different places, we were able to assign a well-being value based on the species traits and the bird diversity to each of the areas. This value has been connected to on-site data of well-being in human participants to investigate how species composition affects mental well-being.

Bird species receiving a higher HRV score are mostly species commonly rated as cute, colorful, visually attractive, and with a nice song. Therefore, it is not surprising that this factor significantly correlates with satisfaction. High biodiversity levels are theorized to help with psychophysiological stress recovery, according to the Stress Reduction Theory [= SRT (Ulrich, 1983; Ulrich et al., 1991)]. Additionally, spending time in nature, according to the Attention Restoration Theory (ART), facilitates recovery from attentional fatigue (Kaplan and Kaplan, 1989; Kaplan, 1995). Areas with more beneficial bird species could therefore help with stress reduction and restoration.

Bird song has been associated with stress reduction (Ratcliffe et al., 2013), being able to buffer the negative effects of traffic noise (Uebel et al., 2022), and improving anxiety (Stobbe et al., 2022), making them a very important part of urban soundscapes. A perceptively beautiful bird song is important for the HRV and mental well-being of people, since sounds are one of the most important factors for stimulating well-being responses (Fisher et al., 2023), underscoring the notion that birds singing beautifully have a positive impact and birds screaming or warning have a more negative one. Bird diversity is also often perceived by humans in the form of bird song (Ferraro et al., 2020).

The appearance of a bird species, on the other hand, is also very important as the second way in which people mostly perceive birds: visually. In the study by Fisher et al. (2023), colors and behavior followed behind sound as a determinant of well-being. Attractive birds are colorful, with a bright appearance, and big ornaments (Santangeli et al., 2023; Santarém et al., 2019; Veríssimo et al., 2014). Bigger birds, on the other hand, are often seen as less attractive (Santangeli et al., 2023). These differing factors have to be kept in mind when looking at the “attractiveness” of birds, since attractiveness is a subjective feeling. This is why we added cuteness, brightness, and the beauty of song as variables. All of them are variables, which are subjectively perceived by people experiencing birds.

The HRV is correlated with the well-being variable satisfaction. Emotions, on the other hand, as well as recalled restoration, and the two place-attachment scales are not. Place attachment is strongly linked to perceived restorativeness and perceived restorative potential of an area (Menatti et al., 2019). It consists of two constructs: place attachment identity and place attachment recovery, with the place attachment recovery scale asking for feelings of freedom, clear head, and health (Bryce et al., 2016). Differing to that, recalled restoration asked for feelings of being refreshed (Young et al., 2020). Therefore, beautiful bird song, visual attractivity, cuteness, and brightness do not actually influence refreshment or positive emotions, but satisfaction with a visit. Therefore, bird species like Erithacus rubecula or Cyanistes caeruleus may themselves have a positive impact, or they go together with positively connoted habitats or structures. This could be since people do not consciously experience bird diversity in the study areas but more unconsciously (Vanhöfen et al., 2025, Vanhöfen et al., 2022), and needs to be studied further. Also, the sheer amount of positively perceived birds present in the area could play a role, since areas with high numbers of bird species are also more satisfying to live in, which is an unconscious mechanism (Hepburn et al., 2021).

As can be seen in Figure 1, two areas especially have a negative impact. These two parks especially present with large aggregations of “negative” species, resulting in a very low HRVplace. One location, for example, had more than 100 greylag geese (Anser anser) aggregating, and another had a flock of more than 100 feral pigeons (Columba livia f. domestica). This is important to note, since birds accumulating in large groups could also be perceived as threatening, especially if they are big and noisy. Many abundant species that form large aggregations, like geese, pigeons, and corvids, are associated with aggression (Belaire et al., 2015), dirt/defecation (Leong et al., 2020), and disease transmission (Pejchar et al., 2025). Especially large birds, like greylag geese, egyptian geese (Alopochen aegyptiaca), mute swans (Cygnus olor), and great cormorants (Phalacrocorax carbo), are often perceived as a nuisance since they are loud, do not sing beautifully (Lukanowski, 2023), and oftentimes, people are even scared of them. These accumulations of birds need to be considered, which is why we used the species frequency in calculating our factor. But this is also one of the limitations of this analysis, since these two parks have a high impact on our analysis and therefore need not be overlooked.

The large body size of birds has not been connected to a higher willingness to protect in earlier studies on birds (Randler and Koch, 2025), which is probably why birds with a low factor score are less beneficial for our mental well-being. On the other hand, colorful, cute birds increase positive feelings, especially in combination with beautiful bird song.

To conclude, attractive birds have a positive effect on people’s mental well-being, namely satisfaction. This is important to know for improving human mental health and biodiversity conservation. Protecting aesthetically attractive and nicely singing species helps not only nature but also society. These birds can possibly function as a flagship or umbrella species, leading to conservation benefits for their whole habitat. It has been shown before that charisma and aesthetic attractiveness of species impact the allocation of conservation funding and efforts (Garnett et al., 2018; Lišková and Frynta, 2013). But also, some important flagship species, especially with birds, are dull-looking, small species, strongly impacted by humans. The HRV, as we propose it, is probably not a useful measure for these species. It is a tool for urban species, able to enhance people’s awareness of the benefits of biodiversity. If a bird species has as high HRV as we propose it, it is aesthetically attractive, has a beautiful song, is cute, and colorful. They are species that are able to elicit interest in people, even without a strong conservation background, and are a gateway into conservation and biodiversity awareness. It can also be a reason for planners to improve urban green spaces to attract these species and, therefore, not only create habitat for birds but also improve human mental well-being. But the method of calculating the HRV can surely be used for other applications as well. Using more or other variables in the calculation could help explore other patterns. For example, habitat affinity, foraging strategy, and nest types could be tested for differences between groups, conservation success, among other things. Future studies might therefore investigate a relationship between the HRV and other metrics, including population status, IUCN ranking of certain species, or shed light on relationships between conservation and HRV.

In the context of this study, it is essential to acknowledge that there is also a widely recognized connection between culture and the perceived value or awareness of biodiversity (Ladle et al., 2019; Millard et al., 2021). In many cultures, birds are connected to religion/folklore. This means that one species could be perceived as positive in one country and negative in another. Hummel et al. (2015), for example, found that there are significant differences between countries regarding the presence of myths surrounding birds.

This is why the present results need to be taken to a larger scale in further studies, in addition to being carefully interpreted in a cultural context. Right now, this study presents a method of analyzing bird species traits and connecting them with the well-being of recreationists, based in south-west Germany. Expanding the survey to other countries would result in more robust results regarding the connection of the HRV to human well-being. Nevertheless, our results are a promising start, showing that species traits of birds are indeed related to the human experience in recreational areas.

Generative AI statement

The author(s) declared that generative AI was not used in the creation of this manuscript.

Any alternative text (alt text) provided alongside figures in this article has been generated by Frontiers with the support of artificial intelligence and reasonable efforts have been made to ensure accuracy, including review by the authors wherever possible. If you identify any issues, please contact us.

Publisher’s note

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.

Footnotes

Edited by: Seunguk Shin, University of Missouri, United States

Reviewed by: Barbara Kus, United States Geological Survey (USGS), United States

Rosa Patricia Román Reyes, Universidad Autónoma del Estado de México, Mexico

Statements

Conflict of interest

The author(s) declared that this work was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

The author CR 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.

Funding

The author(s) declared that financial support was not received for this work and/or its publication.

Data availability

The raw data supporting the conclusions of this article will be made available by the authors, without undue reservation. For questions contact the corresponding author.

Ethics approval

The studies involving humans were approved by Ethics committee of the Faculty of Social Sciences and Economics of the University of Tübingen (AZ: A2.5.4-219_ns). The studies were conducted in accordance with the local legislation and institutional requirements. The participants provided their written informed consent to participate in this study.

Author contributions

JV: Conceptualization, Data curation, Formal analysis, Investigation, Methodology, Validation, Visualization, Writing – original draft, Writing – review & editing. NK: Investigation, Methodology, Writing – review & editing. CR: Conceptualization, Data curation, Investigation, Methodology, Project administration, Resources, Supervision, Writing – review & editing.

Acknowledgements

We would like to thank Talia Härtel for her scientific input regarding the analysis and formulation of the factor.

References

  1. Adjei P. O.-W., Agyei F. K. (2015). Biodiversity, environmental health and human well-being: analysis of linkages and pathways. Environment Dev. sustainability 17, 1085 – 1102. doi: doi:10.1007/s10668-014-9591-0
  2. Albert C., Luque G. M., Courchamp F. (2018). The twenty most charismatic species. PLoS One 13, e0199149. doi:, PMID: doi:10.1371/journal.pone.0199149
  3. Arlinghaus R. (2006). On the apparently striking disconnect between motivation and satisfaction in recreational fishing: the case of catch orientation of German anglers. North Am. J. Fisheries Manage. 26, 592 – 605. doi: doi:10.1577/M04-220.1
  4. Barthel P. H., Krüger T. (2019). Liste der Vögel Deutschlands: Version 3.2 (Radolfzell, Germany: Deutsche Ornithologische Gesellschaft).
  5. Belaire J. A., Westphal L. M., Whelan C. J., Minor E. S. (2015). Urban residents’ perceptions of birds in the neighborhood: Biodiversity, cultural ecosystem services, and disservices. Condor 117, 192 – 202. doi: doi:10.1650/condor-14-128.1
  6. Bergmann H.-H., Engländer W., Baumann S. (2020). Die Stimmen der Vögel Europas auf DVD, AULA-Verlag. Wiebelsheim, Germany
  7. Bibby C. J., Burgess N. D., Ecologists E. A., Hillis D. M., Hill D. A., Ornithology B. T. F.. (2000). Bird Census Techniques (Great Britain: Elsevier Science).
  8. Boley B. B., Strzelecka M., Yeager E. P., Ribeiro M. A., Aleshinloye K. D., Woosnam K. M.. (2021). Measuring place attachment with the abbreviated place attachment scale (APAS). J. Environ. Psychol. 74, 101577. doi: doi:10.1016/j.jenvp.2021.101577
  9. Borgi M., Cogliati-Dezza I., Brelsford V., Meints K., Cirulli F. (2014). Baby schema in human and animal faces induces cuteness perception and gaze allocation in children. Front. Psychol. 5, 411. doi:, PMID: doi:10.3389/fpsyg.2014.00411
  10. Bryce R., Irvine K. N., Church A., Fish R., Ranger S., Kenter J. O. (2016). Subjective well-being indicators for large-scale assessment of cultural ecosystem services. Ecosystem Serv. 21, 258 – 269. doi: doi:10.1016/j.ecoser.2016.07.015
  11. Callaghan C. T., Poore A. G. B., Hofmann M., Roberts C. J., Pereira H. M. (2021). Large-bodied birds are over-represented in unstructured citizen science data. Sci. Rep. 11, 19073. doi:, PMID: doi:10.1038/s41598-021-98584-7
  12. Carrus G., Scopelliti M., Lafortezza R., Colangelo G., Ferrini F., Salbitano F.. (2015). Go greener, feel better? The positive effects of biodiversity on the well-being of individuals visiting urban and peri-urban green areas. Landscape Urban Plann. 134, 221 – 228. doi: doi:10.1016/j.landurbplan.2014.10.022
  13. Chen Z., Hermes J., Liu J., von Haaren C. (2022). How to integrate the soundscape resource into landscape planning? A perspective from ecosystem services. Ecol. Indic. 141, 109156. doi: doi:10.1016/j.ecolind.2022.109156
  14. Cox D. T., Gaston K. J. (2015). Likeability of garden birds: Importance of species knowledge & richness in connecting people to nature. PLoS One 10, e0141505. doi:, PMID: doi:10.1371/journal.pone.0141505
  15. Cox D. T., Hudson H. L., Shanahan D. F., Fuller R. A., Gaston K. J. (2017). The rarity of direct experiences of nature in an urban population. Landscape Urban Plann. 160, 79 – 84. doi: doi:10.1016/j.landurbplan.2016.12.006
  16. Dallimer M., Irvine K. N., Skinner A. M., Davies Z. G., Rouquette J. R., Maltby L. L.. (2012). Biodiversity and the feel-good factor: understanding associations between self-reported human well-being and species richness. BioScience 62, 47 – 55. doi: doi:10.1525/bio.2012.62.1.9
  17. De Vries S., Snep R. (2019). Biodiversity in the context of ‘biodiversity–mental health’research (Biodiversity and health in the face of climate change), Switzerland: Springer Nature. 159 – 173.
  18. Douglas J. W., Evans K. L. (2021). An experimental test of the impact of avian diversity on attentional benefits and enjoyment of people experiencing urban green-space. People Nat. 4 (1), 243–259.
  19. Ferraro D. M., Miller Z. D., Ferguson L. A., Taff B. D., Barber J. R., Newman P.. (2020). The phantom chorus: birdsong boosts human well-being in protected areas. Proc. R. Soc. B: Biol. Sci. 287, 20201811. doi:, PMID: doi:10.1098/rspb.2020.1811
  20. Fisher J. C., Dallimer M., Irvine K. N., Aizlewood S. G., Austen G. E., Fish R. D.. (2023). Human well-being responses to species’ traits. Nat. Sustainability 6, 1219 – 1227. doi: doi:10.1038/s41893-023-01151-3
  21. Garnett S. T., Ainsworth G. B., Zander K. K. (2018). Are we choosing the right flagships? The bird species and traits Australians find most attractive. PLoS One 13, e0199253. doi:, PMID: doi:10.1371/journal.pone.0199253
  22. Gregory R. D., Vořišek P., Noble D. G., Van Strien A., Klvaňová A., Eaton M.. (2008). The generation and use of bird population indicators in Europe. Bird Conserv. Int. 18, S223 – S244. doi: doi:10.1017/S0959270908000312
  23. Haukka A., Lehikoinen A., Mammola S., Morris W., Santangeli A. (2023). The iratebirds citizen science project: A dataset on birds’ visual aesthetic attractiveness to humans. Sci. Data 10, 297. doi: https://doi.org/, PMID: doi:10.1038/s41597-023-02169-0
  24. Hepburn L., Smith A. C., Zelenski J., Fahrig L. (2021). Bird diversity unconsciously increases people’s satisfaction with where they live. Land 10, 153. doi: doi:10.3390/land10020153
  25. Houlden V., Jani A., Hong A. (2021). Is biodiversity of greenspace important for human health and wellbeing? A bibliometric analysis and systematic literature review. Urban Forestry Urban Greening 66, 127385. doi: doi:10.1016/j.ufug.2021.127385
  26. Hummel E., Fancovicová J., Randler C., Ozel M., Usak M., Medina-Jerez W.. (2015). Interest in birds and its relationship with attitudes and myths: A cross-cultural study in countries with different levels of economic development. Educ. Sciences: Theory Pract. 15, 285 – 296. doi: doi:10.12738/estp.2015.1.2242
  27. Kaplan R., Kaplan S. (1989). The experience of nature: A psychological perspective (Great Britain: Cambridge university press).
  28. Kaplan S. (1995). The restorative benefits of nature: Toward an integrative framework. J. Environ. Psychol. 15, 169 – 182. doi: doi:10.1016/0272-4944(95)90001-2
  29. Kövér L., Paládi P., Benmazouz I., Šorgo A., Špur N., Juhász L.. (2022). Is the Hitchcock story really true? Public opinion on hooded crows in cities as input to management. Animals 12, 1207. doi:, PMID: doi:10.3390/ani12091207
  30. Ladle R. J., Jepson P., Correia R. A., Malhado A. C., Gould R. (2019). A culturomics approach to quantifying the salience of species on the global internet. People Nat. 1, 524 – 532. doi: doi:10.1002/pan3.10053
  31. Leong R. A., Fung T. K., Sachidhanandam U., Drillet Z., Edwards P. J., Richards D. R. (2020). Use of structural equation modeling to explore influences on perceptions of ecosystem services and disservices attributed to birds in Singapore. Ecosystem Serv. 46, 101211. doi: doi:10.1016/j.ecoser.2020.101211
  32. Lišková S., Frynta D. (2013). What determines bird beauty in human eyes ? Anthrozoös 26, 27 – 41. doi: doi:10.2752/175303713X13534238631399
  33. Lorenz K. (1943). Die angeborenen formen möglicher erfahrung. Z. für Tierpsychologie 5, 235 – 409. doi: doi:10.1111/j.1439-0310.1943.tb00655.x
  34. Lovell R., Wheeler B. W., Higgins S. L., Irvine K. N., Depledge M. H. (2014). A systematic review of the health and well-being benefits of biodiverse environments. J. Toxicol. Environ. Health Part B 17, 1 – 20. doi:, PMID: doi:10.1080/10937404.2013.856361
  35. Lukanowski J. (2023). Das Geschlecht und die persönliche Einstellung haben einen Einfluss auf die Wahrnehmung der Schönheit von Vögeln. Eberhard Karls University Tübingen, Tübingen, Germany: B.Sc. Graduation Thesis. 23 (5).
  36. Menatti L., Subiza-Pérez M., Villalpando-Flores A., Vozmediano L., San Juan C. (2019). Place attachment and identification as predictors of expected landscape restorativeness. J. Environ. Psychol. 63, 36 – 43. doi: doi:10.1016/j.jenvp.2019.03.005
  37. Methorst J., Bonn A., Marselle M., Böhning-Gaese K., Rehdanz K. (2021). Species richness is positively related to mental health – A study for Germany. Landscape Urban Plann. 211, 104084. doi: doi:10.1016/j.landurbplan.2021.104084
  38. Millard J. W., Gregory R. D., Jones K. E., Freeman R. (2021). The species awareness index as a conservation culturomics metric for public biodiversity awareness. Conserv. Biol. 35, 472 – 482. doi:, PMID: doi:10.1111/cobi.13701
  39. Pejchar L., Rega-Brodsky C. C., Vázquez L. B., MacGregor-Fors I. (2025). Bird-mediated ecosystem services and disservices in cities and towns. Front. Ecol. Environ., 23: e2835. doi: doi:10.1002/fee.2835
  40. Prayag G., Ryan C. (2011). Antecedents of tourists’ Loyalty to Mauritius: the role and influence of destination image, place attachment, personal involvement, and satisfaction. J. Travel Res. 51, 342 – 356. doi: doi:10.1177/0047287511410321
  41. Prokop P., Masarovič R., Vranovský T. (2025). Human preferences for animals on youTube. Diversity 17, 720. doi: doi:10.3390/d17100720
  42. Randler C., Koch S. (2025). Willingness to protect bird species depends on individual respondents’ demographic and species traits. Conserv. Sci. Pract. 7, e13277. doi: doi:10.1111/csp2.13277
  43. Randler C., Staller N., Kalb N., Tryjanowski P. (2023). Charismatic species and birdwatching: Advanced birders prefer small, shy, dull, and rare species. Anthrozoös 36, 427 – 445. doi: doi:10.1080/08927936.2023.2182030
  44. Ratcliffe E., Gatersleben B., Sowden P. T. (2013). Bird sounds and their contributions to perceived attention restoration and stress recovery. J. Environ. Psychol. 36, 221 – 228. doi: doi:10.1016/j.jenvp.2013.08.004
  45. Santangeli A., Haukka A., Morris W., Arkkila S., Delhey K., Kempenaers B.. (2023). What drives our aesthetic attraction to birds ? NPJ Biodiversity 2, 20. doi:, PMID: doi:10.1038/s44185-023-00026-2
  46. Santarém F., Pereira P., Saarinen J., Brito J. C. (2019). New method to identify and map flagship fleets for promoting conservation and ecotourism. Biol. Conserv. 229, 113 – 124. doi: doi:10.1016/j.biocon.2018.10.017
  47. Schlegel J., Rupf R. (2010). Attitudes towards potential animal flagship species in nature conservation: A survey among students of different educational institutions. J. Nat. Conserv. 18, 278 – 290. doi: doi:10.1016/j.jnc.2009.12.002
  48. Sekercioglu C. H. (2006). Increasing awareness of avian ecological function. Trends Ecol. Evol. 21, 464 – 471. doi:, PMID: doi:10.1016/j.tree.2006.05.007
  49. Smith R. J., Veríssimo D., Isaac N. J., Jones K. E. (2012). Identifying Cinderella species: uncovering mammals with conservation flagship appeal. Conserv. Lett. 5, 205 – 212. doi: doi:10.1111/j.1755-263X.2012.00229.x
  50. Stobbe E., Sundermann J., Ascone L., Kühn S. (2022). Birdsongs alleviate anxiety and paranoia in healthy participants. Sci. Rep. 12, 16414. doi:, PMID: doi:10.1038/s41598-022-20841-0
  51. Taylor L., Hahs A. K., Hochuli D. F. (2018). Wellbeing and urban living: nurtured by nature. Urban Ecosyst. 21, 197 – 208. doi: doi:10.1007/s11252-017-0702-1
  52. Uebel K., Rhodes J. R., Wilson K., Dean A. J. (2022). Urban park soundscapes: Spatial and social factors influencing bird and traffic sound experiences. People Nat. 4, 1616 – 1628. doi: doi:10.1002/pan3.10409
  53. Ulrich R. S. (1983). “ Aesthetic and affective response to natural environment,” in Behavior and the natural environment (Boston, MA: Springer US), 85 – 125.
  54. Ulrich R. S., Simons R. F., Losito B. D., Fiorito E., Miles M. A., Zelson M. (1991). Stress recovery during exposure to natural and urban environments. J. Environ. Psychol. 11, 201 – 230. doi: doi:10.1016/S0272-4944(05)80184-7
  55. Vanhöfen J., Härtel T., Reichert G., Randler C. (2025). The relationship between perception and landscape characteristics of recreational places with human mental well-being. Sci. Rep. 15, 4245. doi:, PMID: doi:10.1038/s41598-025-88414-5
  56. Vanhöfen J., Schöffski N., Härtel T., Randler C. (2022). Are lay people able to estimate breeding bird diversity ? Animals 12, 3095. doi:, PMID: doi:10.3390/ani12223095
  57. Veríssimo D., Pongiluppi T., Santos M. C. M., Develey P. F., Fraser I., Smith R. J.. (2014). Using a systematic approach to select flagship species for bird conservation. Conserv. Biol. 28, 269 – 277. doi:, PMID: doi:10.1111/cobi.12142
  58. White M. P., Alcock I., Wheeler B. W., Depledge M. H. (2013). Would you be happier living in a greener urban area? A fixed-effects analysis of panel data. psychol. Sci. 24, 920 – 928. doi:, PMID: doi:10.1177/0956797612464659
  59. White M. P., Elliott L. R., Gascon M., Roberts B., Fleming L. E. (2020). Blue space, health and well-being: A narrative overview and synthesis of potential benefits. Environ. Res. 191, 110169. doi:, PMID: doi:10.1016/j.envres.2020.110169
  60. White M. E., Hamlin I., Butler C. W., Richardson M. (2023). The Joy of birds: the effect of rating for joy or counting garden bird species on wellbeing, anxiety, and nature connection. Urban Ecosyst. 26 (3), 755–765. doi: doi:10.1007/s11252-023-01334-y
  61. Wyles K. J., White M. P., Hattam C., Pahl S., King H., Austen M. (2019). Are some natural environments more psychologically beneficial than others? The importance of type and quality on connectedness to nature and psychological restoration. Environ. Behav. 51, 111 – 143. doi: doi:10.1177/0013916517738312
  62. Xie S., Pan Q., Zheng H., Xiao N., Li J. (2023). Key factors strengthening residents’ Psychological well-being and critical human-nature connections within the living spaces—An example from Beijing. Diversity 15, 438. doi: doi:10.3390/d15030438
  63. Young C., Hofmann M., Frey D., Moretti M., Bauer N. (2020). Psychological restoration in urban gardens related to garden type, biodiversity and garden-related stress. Landscape Urban Plann. 198, 103777. doi: doi:10.1016/j.landurbplan.2020.103777

Citation

Vanhöfen, J., et al. (2026). Bird species traits in recreational areas – building a human restoration value of bird species and connecting it to the mental well-being of recreationists in Germany. Frontiers in Bird Science, Volume 5. https://doi.org/
Received
Accepted
Published
Volume
5 - 2026

Copyright

Copyright © 2026 Vanhöfen, Kalb and Randler.

License: https://creativecommons.org/licenses/by/4.0/

*Correspondence: Janina Vanhöfen

Article metrics

Views
0
Downloads
0
Citations
0
Shares
0