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Article

From Planting to Participation: Early-Phase Resident Attachment in an Urban Fruit Orchard

1
INESAN (Institute for Evaluations and Social Analyses), 18600 Prague, Czech Republic
2
Research and Breeding Institute of Pomology Holovousy Ltd., 508 01 Hořice, Czech Republic
*
Author to whom correspondence should be addressed.
Urban Sci. 2025, 9(12), 492; https://doi.org/10.3390/urbansci9120492
Submission received: 1 October 2025 / Revised: 7 November 2025 / Accepted: 19 November 2025 / Published: 21 November 2025

Abstract

Urban edible greening initiatives, such as urban orchards and community fruit gardens, can deliver ecological and social benefits, but their long-term success depends on community acceptance. This study examines the establishment phase of a newly planted orchard in a housing estate in a mid-sized Czech city and operationalizes esthetic fit over time, i.e., the extent to which early-phase design is perceived as orderly, suitable, and promising using targeted items on design legibility, species–site suitability, and perceived promise. Data were collected through standardized face-to-face interviews with 150 residents, using a stratified sampling strategy. The survey elicited anticipated burdens and benefits, current and future evaluations of the orchard, and attitudes toward its care. Attitudes were measured with an adapted Urban Green Attachment Scale (UGAS). Descriptive and inferential analyses, including logistic regression and non-parametric tests, were conducted. Findings reveal that residents credited the orchard with design legibility, beauty, and ecological promise, while pragmatic concerns focused on maintenance tasks (leaf litter, watering) and questions of fruit access. Window views of the orchard and general satisfaction with the residential environment significantly increased the odds of higher attachment, while gender differences suggested varied engagement pathways. Importantly, attachment was strongly associated with stewardship intentions; residents with higher UGAS scores were more likely to defend the orchard, taste the fruit, participate in maintenance, and even support its preservation through higher property taxes. The results underscore that attachment is measurable before full ecological performance emerges, arising from a combination of design legibility and daily visibility. Practically, visible routines of care can pace expectations and sustain legitimacy. Conceptually, the study demonstrates that early-phase esthetic fit spans installation with stewardship, providing a foundation for long-term resilience and co-stewardship of edible urban greening.

1. Introduction

Cities across the world are experimenting with edible greening, especially urban orchards, community fruit gardens, and mixed productive plantings to integrate ecological performance with everyday social life [1]. This practice builds on a decade of advances that have mapped typologies of edible landscapes, identified enabling governance arrangements, and documented system-level benefits, including microclimate moderation, shade provision, biodiversity support, and air-quality co-benefits [2]. These achievements reflect a broader shift from purely ornamental urban greenery to multi-functional plantings that embed food species in the ordinary spaces of housing estates, courtyards, and neighborhood streets [3,4].
Alongside these environmental and governance advances, previous research has clarified how social sustainability depends on the legibility of landscape design and the meanings people ascribe to new plantings in their daily routines. In this respect, environmental psychology has connected esthetic judgment, preference, and use [5], while urban health and landscape studies show that everyday visibility, such as window views of greenery, supports well-being and can shape attitudes and behaviors [6,7]. In parallel, urban forestry has moved beyond benefits-only narratives to include ecosystem disservices, calling for evaluation tools that register perceived burdens alongside benefits [8,9,10]. These strands point to the importance of early interpretation: how residents perceive a planting’s order, purpose, and likely trajectory in its first seasons.
Within this broader turn to productive landscapes, edible plantings present distinctive visual and symbolic cues compared with ornamental plantings. Staking, guards, seasonal variability, and the prospect of fruit harvest signal future utility yet can also introduce ambiguity about order, care, and intent [11,12]. These attributes heighten the stakes for early community acceptance, and residential settings offer a particularly revealing context for examining these dynamics. In dense housing estates, apartment windows overlook shared grounds, movement patterns are local and routine, and small design decisions, for instance, spacing, edge conditions, or the presence of protective guards, carry outsized interpretive consequences.
Despite the rapid growth of research on edible urban greening [1,8,9,12], important gaps remain. Early-phase social acceptance is under-examined as a design problem; we know less about how residents interpret the appearance of newly planted edible landscapes and how esthetic legibility shapes legitimacy during establishment [13]. Insights from environmental psychology are rarely applied directly to edible plantings, leaving open questions about whether having a window view of an edible planting predicts attachment to it [7,14,15,16,17]. While calls to account for disservices have grown [18,19], design-sensitive instruments that capture both perceived benefits and burdens are still scarce [20]. Moreover, much of the literature addresses governance at the system level, with fewer studies on residential-scale orchards in dense estates where design choices are most visible and stewardship demands most immediate [4,7,14].
Against this backdrop, this study pursues three aims. Firstly, to assess residents’ early-phase appraisals of design legibility and situational suitability based on our operationalization of esthetic fit over time [5,6,7,8]. Secondly, to test whether everyday visibility (i.e., window views) and place satisfaction are associated with attachment to urban green [7,14,15,16,17]. Thirdly, to examine whether attachment aligns with stewardship-relevant orientations (especially, willingness to help maintain, willingness to pay higher tax, and willingness to participate) [21,22]. By focusing on a highly visible residential orchard and employing design-sensitive, benefit-and-burden measures linked to attachment, the study contributes practice-proximate evidence on how esthetic judgments during establishment can lay the groundwork for co-stewardship and the long-term legitimacy of edible urban greening [18,19,20].

2. Materials and Methods

2.1. Study Design and Setting

The study was designed as a cross-sectional social survey conducted during the early phase of an urban greening intervention specifically oriented toward fruit crops. The intervention consisted of the establishment of an orchard in a housing estate of a mid-sized city in Czechia (approx. 100,000 inhabitants) called Hradec Králové. It is located in the temperate climate zone of Central Europe within the predominantly flat Polabí lowland region characterized by distinct seasonal variations. The city experiences a moderate continental climate with warm summers and cold winters. Mean annual temperature ranges from 8–9 °C. Annual precipitation totals approximately 600–650 mm, distributed relatively evenly throughout the year with a slight peak during the summer months. The growing season typically extends from mid-April to mid-October, providing favorable conditions for fruit tree and shrub cultivation. These climatic conditions are well-suited for the establishment of urban orchards featuring apples, cherries, plums, pears, and various berry shrubs.
The housing estate itself is home to about 5000 residents, largely accommodated in blocks of flats. At the time of data collection, the orchard consisted of 58 fruit trees and 114 fruiting shrubs. Trees included apples, cherries, plums, and pears, while shrubs comprised currants, gooseberries, aronia berries, honeyberries, mulberries, and hazelnuts. Weaker-growing apple and plum varieties were planted as quarter-stem forms with a stem height of 0.9 m. Vigorous-growing cherry and pear trees were planted as high-stem forms with stem heights ranging from 1.7 to 2.0 m. The trees were planted with 4 to 5 scaffold branches and one terminal. The shrubs were planted with 4 to 6 scaffold branches branching out at ground level (see Figure 1 and Figure 2).
All newly planted trees and shrubs received initial establishment pruning according to standard agronomic practice. Approximately 50 percent of the previous year’s growth was removed to balance the partially reduced root system with the above-ground portion. All pruning cuts were treated with acrylic dispersion-based tree wound sealant. During the subsequent growing season, only sanitary maintenance pruning was performed, which involved the removal of mechanically damaged branches as needed.
The actual setting of the orchard is obvious from Figure 1 and Figure 2. Data collection was undertaken six months after planting, when the first visible green cover effects of the intervention were present, but before the orchard had reached the fruiting phase.

2.2. Participants and Sampling

The target population was defined as current residents of the housing estate. Non-resident users of the area were excluded. Data collection was implemented through standardized face-to-face interviews, carried out in respondents’ households. Prior to fieldwork, the questionnaire was prepared, pilot-tested, and refined to ensure clarity and feasibility [23].
Sampling followed a combined approach. A stratified probability design was applied across specific blocks of flats to ensure geographic coverage within the estate. Within strata, time-location sampling was employed to capture residents with different daily routines and working hours. Finally, convenience elements were inevitably applied, as participation depended on respondents being present at home and willing to take part. This combination of strategies resulted in a balanced sample that achieved broad coverage, but results should be interpreted as analytically generalizable to similar estates rather than statistically representative.
A total of 267 residents were approached. Of these, 158 consented to participate, yielding a response rate of 59%. After data cleaning, eight incomplete cases were excluded, resulting in a final analytical sample of 150 respondents. Such a sample size is adequate with respect to the intended analyses [24,25,26,27,28,29,30].
Informed consent was obtained from all participants prior to the interviews. Participation was voluntary and the confidentiality of responses was assured; no personally identifying data were collected. Fieldwork procedures complied with the ethical principles of the Helsinki Declaration. Ethical approval was obtained from the INESAN Ethical Committee prior to data collection (IREBA/2025/425 from 8 April 2025).

2.3. Measures

Building on work that links perceived order and suitability to acceptance, we articulated the concept of esthetic fit over time as a dynamic property: residents’ early-phase appraisal of order, situational suitability, and credible promise of growth [5,6,7]. We operationalized esthetic fit over time through three sub-dimensions: (1) design legibility (e.g., spacing, edges, guards) [7,31]; (2) species–site suitability [8]; and (3) perceived promise (anticipated canopy development and fruiting schedule) [9,10]. These map directly onto the two eight-item benefit sets used in the survey.

2.3.1. Perceived Benefits

The first eight-item set captured benefits already observable at the time of data collection and instantiated legibility and suitability (e.g., “This planting is well designed.” (design legibility) and “The selection of trees and shrubs is suitable for this location” (species–site suitability) alongside near-term benefits already noticeable during establishment “Trees and shrubs planted here clean the air.”); all measured on a 4-point agreement scale (1 = definitely disagree; 4 = definitely agree). The second eight-item set of benefits captured expected future benefits, which instantiated perceived promise (e.g., “Planted trees and shrubs will cool the area in summer.”, “Planted trees will provide much-needed shade.”); measured on a 4-point agreement scale as well.

2.3.2. Anticipated Burdens and Perceived Risks

Respondents were presented with a list of potential problems and risks associated with the orchard [4,5,32]. The items were developed from issues raised during a public hearing and resulting discussions held prior to the orchard’s establishment. Example statements include “Planted trees will cast shadows and obstruct the view” and “Fruit on the trees and shrubs will attract insects”. Agreement with each statement was measured on a 4-point Likert-type scale.

2.3.3. Urban Green Attachment Scale

Attitudinal background was assessed using the adapted Urban Green Attachment Scale (UGAS) originally developed by Haluza et al. [21]. The UGAS was translated from the English version into Czech and confirmed by back-translation [33]. Then, cognitive interviews (n = 12) were performed to test the clarity and relevance of the items. Based on the cognitive interviews, no changes in the wording of scale items were necessary due to vagueness or lack of specificity. However, we made minor changes in terminology when we replaced “trees” with “trees and shrubs” to better reflect the given setting. The scale captures emotional, cognitive, and evaluative aspects of attachment to newly introduced urban greenery. In its original form, it encompassed three factors, namely attachment, discontent, and availability; however, in this study, we deployed only the attachment dimension, which comprises five items. Items such as “These trees and shrubs are important to me” or “I would protect these trees if someone wants to remove them” were rated on a 4-point scale (1 = strongly disagree; 4 = strongly agree) instead of a 5-point scale due to sample characteristics [34,35,36]. The original scale has demonstrated high reliability (Cronbach’s α was 0.929) [21], which was confirmed in this study (Cronbach’s α was 0.869).

2.3.4. Additional Variables

Additional independent variables included satisfaction with living in the location, length of residence, and whether respondents had a direct view of the orchard from their window [31,32,37]. These variables were included to explore predictors of attachment.

2.3.5. Civic Dispositions and Stewardship Intentions

Respondents were also asked about their willingness to engage in activities related to the stewardship and governance of green spaces with fruit trees and shrubs. This included willingness to participate in orchard maintenance (“Would you be willing to participate in the maintenance of green spaces here in this location?”), willingness to pay higher property taxes to preserve greenery (“Would you be willing to pay higher property taxes to preserve the existing green spaces here?”), and willingness to participate in improving the local greenery when being better informed (“Would you be willing to participate more in green spaces maintenance if you would have more information about the orchard?”), inspired by Balram and Dragićević [38]. These items allowed analysis of how attachment to the orchard relates to broader pro-environmental and civic orientations [39,40].

2.4. Data Analysis

Data were analyzed in several stages. Firstly, descriptive statistics (means, standard deviations, frequencies) were calculated for all items [41,42]. The key properties of the UGAS were assessed through internal consistency indices (Cronbach’s α, McDonald’s ω), item-total correlations, and inspection of floor and ceiling effects [43]. Secondly, inferential analyses were conducted to examine relationships among variables. Logistic regression was used to model predictors of high attachment (defined as scoring above the median on the UGAS), with satisfaction with living in the place, window view, and gender as independent variables. Model fit was evaluated using omnibus tests, pseudoR2 indices, classification accuracy, and the Hosmer–Lemeshow test. Thirdly, associations between UGAS scores and engagement were examined using non-parametric tests (Mann–Whitney U and Kruskal–Wallis H tests) due to the non-normal distribution of some variables. Finally, exploratory ANOVA was used to examine subgroup differences in perceived benefits and burdens by socio-demographic strata. For non-normal outcomes, we used Kruskal–Wallis; parametric ANOVA results are included in sensitivity checks and led to identical conclusions. All analyses were performed using IBM SPSS Statistics, Version 26 (IBM Corp., Armonk, NY, USA). Significance was assessed at the conventional levels (p < 0.05; p < 0.01).

3. Results

3.1. Sample Characteristics

The socio-demographic profile of the sample is summarized in Table 1. Women represented 60% of respondents, while 40% were men. Age distribution was broad, with 24% under 30 years, 20% aged 30–39, 16% aged 40–49, 14% aged 50–59, and 26% aged 60 or older. Educational attainment was concentrated at the secondary level (51.3%), with vocational education at 22.7%, university education at 21.3%, and elementary education at 4.7%.
Two contextual variables were of particular importance. Firstly, 64.7% of respondents reported having a direct view of the orchard from their windows, providing them with everyday visual exposure to the intervention. Secondly, the length of residence differed between long-term residents (≥15 years, 46.7%) and newcomers (<15 years, 53.3%), allowing the exploration of how place memory shapes perceptions of the orchard.

3.2. Expected Burdens and Risks

The anticipated burdens associated with the newly established orchard are both practical and clearly expressed by respondents. Table 2 shows that concerns related to maintenance score are the highest; the necessity of clearing fallen leaves (M = 3.44, SD = 0.585) and the general perception that “Someone will have to take care of the planted trees and shrubs” (M = 3.84, SD = 0.368) were the strongest concerns. Regular watering (M = 3.61, SD = 0.541) and the potential for leaf litter to create a mess (M = 3.44, SD = 0.585) also rank highly. Ecological concerns are reflected in the expectation that the fruit will attract insects (M = 3.41, SD = 0.615).
Beyond operations, respondents also register social concerns. The expectation that “Fruit will attract homeless people.” (M = 3.57, SD = 0.536) is as salient as the need for regular watering and exceeds many ecological or visual issues. By contrast, visual impacts are evaluated as relatively minor (“Planted trees will cast shadows and obstruct the view.” M = 2.47, SD = 0.662), and potential allergy aggravation is moderate (M = 2.93, SD = 0.435).

3.3. Perceived Current Benefits

Whereas the previous section focused on expected problems, Table 3 demonstrates that several benefits are already recognized in situ. Using a 1–4 Likert-type scale where 1 = definitely disagree and 4 = definitely agree, respondents reported the strongest perceptions of environmental functions, particularly air cleaning (M = 3.47, SD = 0.642). Esthetic benefits were also highly valued, including the perception that the planting is well designed (M = 3.34, SD = 0.600) and that the selection of trees and shrubs is suitable for the location (M = 3.23, SD = 0.523). The orchard is also perceived to enhance social ambience, making it more pleasant to meet other people (M = 3.15, SD = 0.679).
An important finding is the relatively high agreement with the statement that the orchard reduces the risk of future construction at the site (M = 3.17, SD = 0.528). This suggests that residents view the orchard as a form of “defensive urbanism” where greenery functions not only as an amenity but also as a barrier against development pressures.
By contrast, noise reduction (M = 2.30, SD = 0.502) and stimulation of interest in gardening (M = 2.22, SD = 0.633) received the lowest mean scores. Notably, the fear that the orchard blocks views from windows was strongly rejected (M = 1.25, SD = 0.558).

3.4. Expected Future Benefits

The results presented in Table 4 show that residents hold consistently high expectations regarding the orchard’s future contributions. On a four-point agreement scale, the strongest endorsements concern the orchard’s role in microclimate regulation and esthetic enhancement. Anticipated cooling during summer (M = 3.63, SD = 0.485) and provision of shade (M = 3.63, SD = 0.497) both approach the scale’s upper limit, underscoring the salience of thermal comfort in residents’ perceptions. Closely following are expectations that the planting will improve the area’s appearance (M = 3.58, SD = 0.495), make breathing easier (M = 3.47, SD = 0.501), and contribute to biodiversity (M = 3.42, SD = 0.522). These evaluations suggest that residents are projecting a wide service envelope onto the orchard, attributing to it both regulating functions (shade, air, biodiversity) and cultural services (esthetics, quality of life).
Other benefits were evaluated positively but at slightly lower levels, notably access to fresh fruit (M = 3.37, SD = 0.755) and wind-speed reduction (M = 2.89, SD = 0.545). The relatively modest expectation of fruit access may reflect uncertainties about rules of use and equitable distribution, issues commonly noted in edible landscape governance. Similarly, the less emphatic rating for wind reduction reflects lay intuitions about the physical limitations of young plantings in providing shelter. Taken together, the pattern indicates that while residents anchor their expectations in tangible, easily legible services such as shade, cooling, and esthetics, they also anticipate broader ecological and social benefits. Importantly, the uniformly high scores confirm that optimism around the orchard’s future performance is strong, providing a fertile basis for cultivating long-term attachment and stewardship—provided that expectations are carefully managed in line with the orchard’s growth trajectory.

3.5. Attitudinal Background Measured by UGAS

UGAS was employed to contextualize the perceptions of local residents. Table 5 shows that the mean score was 15.67 (SD = 2.401) across five items, with negligible floor effects (0.0%) and modest ceiling effects (5.3%) [43]. Internal consistency was very good (Cronbach’s α = 0.882, McDonald’s ω = 0.890) [44,45,46,47]. Skewness was –0.475 and kurtosis −0.366 [48,49].
Item means clustered toward agreement for positive evaluations: beauty (M = 3.31, SD = 0.590), contribution to well-being (M = 3.27, SD = 0.609), perceived importance (M = 3.12, SD = 0.634), and willingness to protect trees from removal (M = 3.07, SD = 0.545).

3.6. Predictors of Attachment

A logistic regression model was estimated to identify predictors of higher attachment (Table 6). The model exhibited good fit χ2 (df = 5) = 45.381, p < 0.001; Hosmer–Lemeshow χ2 (df = 6) = 6.765, p = 0.343 and satisfactory explanatory power (Nagelkerke R2 = 0.350), with a classification accuracy of 75.3%. Outcome balance is adequate (84 higher vs. 66 lower), and with 5 model df, the events-per-variable are 84/5 = 16.8, i.e., above common rules of thumb (≥10). Education group sizes (41/77/32) are modest but not sparse; the wider CI for the secondary education category reflects sampling variability rather than model failure.
Four predictors emerged as significant. First, satisfaction with living at the place was strongly associated with higher attachment (OR = 3.548, p < 0.05). Second, having a direct view of the orchard from the window increased the odds of higher attachment (OR = 2.870, p < 0.01), suggesting that everyday visual exposure reinforces the sense of connection. Third, gender differences were evident; male respondents had lower odds of high attachment compared to female respondents (OR = 0.248, p < 0.01). Fourth, education differences were evident; respondents with elementary/vocational education had lower odds of high attachment compared to respondents with university education (OR = 0.274, p < 0.05). Compared with university education (reference), elementary/vocational respondents had significantly lower odds of high attachment (OR = 0.274, p = 0.024), whereas secondary education did not differ from university (OR = 1.060, p = 0.907), indicating a threshold rather than a monotonic, linear stepwise gradient.

3.7. Attachment and Pro-Stewardship Orientations

Bivariate analyses in Table 7 confirm that higher levels of attachment are strongly associated with pro-stewardship intentions and broader civic dispositions. Respondents with higher UGAS scores were significantly more likely to wish that the orchard remain in the future (M = 16.20 vs. 12.92, p < 0.001) and to express interest in tasting the fruit (M = 16.17 vs. 13.84, p < 0.001).
Similarly, willingness to engage in maintenance followed a clear gradient; respondents who were willing to help reported higher attachment (M = 16.89), while those unwilling to participate reported significantly lower attachment (M = 15.01). Willingness to pay higher property taxes to preserve green spaces and willingness to participate if more information was available were also associated with higher attachment.

4. Discussion

The results indicate that esthetic legibility is a critical driver of residents’ acceptance in the establishment phase. Although the orchard is visually “young,” respondents already attribute beauty, well-being, and design suitability to it. These positive evaluations are not yet grounded in deep place identity; rather, they arise from the planting’s capacity to signal order, purpose, and promise. Consistent with theories of environmental legibility, residents appear able to understand intentionality in spatial arrangement, species choice, and edge conditions, even before biophysical functions mature.
The orchard has not yet entered the estate’s entrenched mental map, which is unsurprising when canopy, understory, and seasonal dramaturgy are only beginning. In this early window, attachment reflects surface-level appraisal rather than fully sedimented place meanings, which underscores the importance of design cues and temporal communication.
Multivariate results show that everyday visibility (a direct window view) substantially increases the odds of higher attachment, translating the orchard from abstract amenity to a familiar element of daily life [50]. General satisfaction with the residential setting further strengthens this pathway, suggesting a reinforcing loop in which positive baseline evaluations color interpretations of new interventions [51]. Together, these mechanisms support a theory of change in which esthetic legibility, visibility, and place satisfaction jointly foster early attachment [52,53].
Gender differences (higher attachment among women) invite targeted engagement strategies. Equally important is the finding that respondents with elementary/vocational education show lower odds of high attachment than their university-educated peers, which can indicate a green attachment divide. Two mechanisms are plausible in this respect: (i) technical language or low-salience cues are harder for individuals with lower levels of education to decode and (ii) edible plantings align differently with habits and perceived obligations. Design and programming should therefore pair legible form with customized information delivery and diverse participation modes, co-produced with local schools, vocational centers, and resident associations.
The benefit profile shows strong endorsement of symbolic ecological services (cleaner air, improved appearance, conviviality) despite limited early biophysical capacity; expectations for noise abatement, wind attenuation, or gardening stimulation are modest. These symbolic attributions are not trivial; they constitute the symbolic value that bridges the time gap between installation and delayed physical performance, sustaining attachment during the period when measurable impacts are nascent.
Residents’ expectations for future benefits, especially shade, biodiversity, quality of life, and fruit, are high. Without coordination, the gap between current reality and projected benefits risks disappointment [54,55]. Temporal communication in the form of growth charts, phenology boards, first-blossom and first-harvest events, and participatory pruning days can render maturation timelines visible and align expectations with growth rates, reinforcing the symbolic bridge.
Predictable concerns focused on leaf litter, watering, and routine care are amenable to pre-emptive organization. Turning these tasks into visible, scheduled, participatory routines reframes burdens as rituals, strengthening stewardship. Clear, fair, and widely communicated harvest norms, e.g., “take-what-you-need” guidance, ripeness windows, or shared tasting days, can legitimize use while minimizing perceived disorder.
The concern that “Fruit will attract homeless people” should be understood as a perceived social disservice implicating safety, occupancy, and governance of shared goods beyond simple fruit access. In early stages, such anxieties can erode the symbolic value that sustains attachment before performance is visible. Responses should combine initial legibility with inclusive communication about use, harvest, and care; co-produced norms; communal harvest events; gleaning/donation partnerships with shelters/food banks; routine visible maintenance; and situational design cues (such as clear sightlines, lighting, tidy edges, or wayfinding) [50]. Collaboration with local social service organizations can pre-empt conflict while preserving an inclusive ethos. By stabilizing symbolic value, these measures can protect the attachment that underwrites co-maintenance.
Bivariate patterns show that residents with higher attachment (i.e., higher UGAS score) are more willing to defend the orchard, taste fruit, contribute to maintenance, and even support preservation through higher taxes [56]. Attachment thus functions as a practical orientation toward co-stewardship, not merely an affective state.
Several limitations must be acknowledged. First, the study is cross-sectional and captures perceptions at a single point in time shortly after the orchard’s establishment. Longitudinal research is necessary to examine how attachment evolves as the orchard matures and as ecological functions become more tangible. Second, the study focused on a single housing estate in a mid-sized Czech municipality; while socio-demographically varied, the findings cannot be generalized without caution to other urban contexts with different cultural, ecological, or governance settings. Third, reliance on self-reported perceptions introduces potential biases, including social desirability and projection effects. Fourth, results may be affected by common-method variance and unmeasured confounding (e.g., prior pro-environmental attitudes). Finally, single-site design limits external validity; multi-site longitudinal replication is warranted.
Future studies should employ longitudinal and comparative designs, integrating both perceptual data and ecological monitoring to assess how symbolic attributions interact with actual biophysical performance. Further attention to social segmentation (e.g., by gender, age, or length of residence) could also refine engagement strategies tailored to different resident groups.
In spite of those limitations, the study makes four contributions. Firstly, it proposes a way to measure an early-phase design legibility. We adapted and extended the esthetic–legibility tradition to edible plantings, capturing perceptions of order, suitability, and fit in the establishment stage. Secondly, it demonstrates the use of indicators quantifying the everyday visibility. We tested whether having a window view of the orchard significantly predicts attachment, thereby moving from generic studies of “views of nature” to a situated mechanism of social assimilation. Thirdly, it validates attachment and links it to stewardship. Using the UGAS, we assess attachment as a robust psychometric construct and examine its association with orientations toward co-stewardship, neighborhood participation, and willingness to underwrite care. Fourthly, it is balancing services and disservices. We elicited both perceived benefits (e.g., cooling, biodiversity, quality of life) and anticipated burdens (e.g., maintenance load, insects, social frictions), treating them as part of the governance locus where design, perception, and equity intersect. For planners and designers, visibility and communication of seasonal change should be treated as universal design elements, not optional outreach. Careful spacing, grouping, and species selection can accelerate assimilation; communicative devices and participatory routines convert novelty into belonging. From a governance perspective, co-produced care routines and transparent harvest norms can transform predictable frictions into shared rituals. Ultimately, the orchard’s legitimacy will depend not only on ecological performance but also on its capacity to enter residents’ mental maps and daily narratives.

5. Conclusions

Urban edible greening is intrinsically temporal; in the first seasons, trees are small, protections are conspicuous, and ecological performance is nascent. Under these conditions, symbolic value operates as a bridge carrying resident attachment across the gap between installation and delayed benefits. Our results indicate that this bridge forms when early design legibility is paired with communication that makes the future intelligible, and when plantings are visibly present in residents’ daily routines.
Empirically, the logistic model showed that place satisfaction and everyday visibility significantly increased the likelihood of higher attachment, while gender differences suggested the need for tailored engagement. Residents anticipated cooling, shade, air quality, biodiversity, and quality-of-life benefits; their concerns were pragmatic and seasonal (e.g., leaf litter, watering, insects, fair fruit access). These concerns can be addressed through visible care routines and clear norms. Temporal communication tools such as growth charts, phenology boards, and first-harvest events convert abstract promise into concrete milestones, reinforcing the symbolic bridge that sustains attachment before performance fully materializes.
Conceptually, we argue that early-phase esthetic fit mediates between installation and stewardship by aligning form (legibility, proportion, edges), narrative (credible signals of canopy and fruiting), and salience (window and pathway visibility). Practically, this implies siting for benign visibility, detailing that reads as intentional rather than temporary, and communication that invites residents into the orchard’s unfolding story. Because attachment coheres with willingness to participate and underwrite care, investments in early-phase legibility and communication yield downstream governance capacity.
Limitations include the cross-sectional design and early-phase focus; causal pathways require longitudinal follow-up. Nonetheless, the alignment across design appraisals, visibility, attachment, and stewardship orientations provides a coherent account of how edible greening gains legitimacy in dense residential estates. If cities want orchards that endure, the first seasons must be curated as much for meaning as for biology; making the future legible is not cosmetic, but foundational.

Author Contributions

Conceptualization, J.R. and J.S.; methodology, J.R.; formal analysis, J.R.; field research, J.R.; resources, J.R. and J.S.; data curation, J.R.; writing—original draft preparation, J.R. and J.S.; writing—review and editing, J.R.; visualization, J.R. and J.S.; funding acquisition, J.S. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by TA ČR, grant number SS07020449—Mitigation of the negative impacts of weather extremes (temperature, wind, and precipitation) on the public health and environment in large agglomerations.

Institutional Review Board Statement

The study was conducted in accordance with the Declaration of Helsinki of 1975 (https://www.wma.net/what-we-do/medical-ethics/declaration-of-helsinki/, accessed on 30 September 2025) and followed the AAPOR ethical code (https://aapor.org/standards-and-ethics/#aapor-code-of-professional-ethics-and-practices, accessed on 30 September 2025). The research design and the research instrument (the questionnaire) were approved in INESAN by the Research Ethics Board (IREBA/2025/425) on 8 April 2025. All links were accessed on 30 September 2025.

Informed Consent Statement

Informed consent was obtained from all subjects involved in the study. This study involved data collected from anonymous respondents. All subjects gave their informed consent for inclusion before their participation in the survey.

Data Availability Statement

The data used to support the findings of this study will be available from the authors upon reasonable request.

Acknowledgments

The authors would like to thank all respondents and interviewers who engaged in this study, and all members of the supportive research team.

Conflicts of Interest

Author Jiří Sedlák was employed by the company Research and Breeding Institute of Pomology Holovousy Ltd. The remaining authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Abbreviations

The following abbreviations are used in this manuscript:
UGASUrban Green Attachment Scale

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Figure 1. Residential environment. Note: Photograph taken by co-author J.S.
Figure 1. Residential environment. Note: Photograph taken by co-author J.S.
Urbansci 09 00492 g001
Figure 2. Orchard layout. Note: Photograph taken by co-author J.S.
Figure 2. Orchard layout. Note: Photograph taken by co-author J.S.
Urbansci 09 00492 g002
Table 1. Selected socio-demographic characteristics.
Table 1. Selected socio-demographic characteristics.
Variables
Sample
GenderMale40.0%
Female60.0%
Total100.0%
Ageless than 30 years24.0%
30–39 years20.0%
40–49 years16.0%
50–59 years14.0%
60 and more years26.0%
Total100.0%
Highest achieved educationElementary4.7%
Vocational22.7%
Secondary51.3%
University21.3%
Total100.0%
View of the orchard from the windowYes64.7%
No35.3%
Total100.0%
Length of residenceNewcomers (less than 15 years)53.3%
Long-time residents (15 years and longer)46.7%
Total100.0%
Table 2. Descriptive statistics—expected issues, problems, fears.
Table 2. Descriptive statistics—expected issues, problems, fears.
NMeanSD
There will be a mess from fallen leaves.1503.440.585
Planted trees will cast shadows and obstruct the view.1502.470.662
Fruit on the trees and shrubs will attract insects.1503.410.615
Someone will have to take care of the planted trees and shrubs.1503.840.368
Planted trees and shrubs may aggravate the allergies of local residents.1502.930.435
In the fall, it will be necessary to clear away leaves that have fallen from the trees.1503.850.355
Planted trees and shrubs will need to be watered regularly.1503.610.541
Fruit will attract homeless people.1503.570.536
Table 3. Descriptive statistics—identified benefits.
Table 3. Descriptive statistics—identified benefits.
NMeanSD
Trees and shrubs planted here block my view from the window.1501.250.558
Trees and shrubs planted here reduce street noise.1502.300.502
Trees and shrubs planted here clean the air.1503.470.642
This planting is well designed.1503.340.600
The selection of trees and shrubs is suitable for this location.1503.230.523
Trees and shrubs planted here make it more pleasant to meet other people.1503.150.679
Trees and shrubs planted here reduce the risk of construction taking place here.1503.170.528
Trees and shrubs planted here have led me to take a greater interest in gardening.1502.220.633
Table 4. Descriptive statistics—expected benefits.
Table 4. Descriptive statistics—expected benefits.
NMeanSD
Local residents will have access to fresh fruit.1503.370.755
Planted trees and shrubs will cool the area in summer.1503.630.485
Planted trees and shrubs will increase biodiversity in the area.1503.420.522
Planted greenery will improve the appearance of the area.1503.580.495
Planted trees and shrubs will improve the quality of life.1503.400.505
Planted trees will provide much-needed shade.1503.630.497
Planted trees will help reduce wind speed.1502.890.545
Thanks to the planted trees and shrubs, it will be easier to breathe here.1503.470.501
Table 5. Descriptive statistics of UGAS and its items.
Table 5. Descriptive statistics of UGAS and its items.
NMeanSDItem-Total CorrelationAlpha if Item Deleted
These trees and shrubs are important to me.1503.120.6340.7730.820
These trees and shrubs contribute to my well-being.1503.270.6090.7330.831
I would miss something in this neighborhood if these trees were gone.1502.910.5830.6240.858
I would protect these trees if someone wants to remove them.1503.070.5450.7030.840
These trees and shrubs are beautiful.1503.310.5900.6350.855
UGA Scale15015.672.401
Note: In this study, the scale has a median of 15.
Table 6. Description of dependent variable and predictors.
Table 6. Description of dependent variable and predictors.
VariablesDescriptionFrequency
DEPENDENT VARIABLE
Urban Green Attachment (UGA)Higher84
Lower66
PREDICTORS
Satisfaction with living at the given placeSatisfied130
Others20
View of the orchard from the windowYes97
No53
Educationelementary/vocational41
secondary77
university32
GenderMale60
Female90
Regression modelBS.E.OR95% CIp-value
Constant−0.6290.8030.533 0.434
Satisfaction with living at the given placeSatisfied1.2660.6253.548(1.042–12.076)0.043
Others
View of the orchard from the windowYes1.0540.4012.870(1.307–6.304)0.009
No
Educationelementary/vocational−1.2930.5720.274(0.089–0.842)0.024
secondary0.0590.5021.060(0.396–2.838)0.907
university
GenderMale−1.3930.3940.248(0.115–0.538)<0.001
Female
Note: category “lower” is the reference category; Omnibus χ2 (df = 5) = 45.381, p < 0.001; Hosmer and Lemeshow χ2 (df = 6) = 6.765, p = 0.343; Nagelkerke (pseudo R2) = 0.350; 75.3% of cases are correctly classified. Age and length of residence at place of living are insignificant predictors.
Table 7. UGAS with other indicators.
Table 7. UGAS with other indicators.
n%MeanMedianSDU/Hp-Value
Would you like the trees and shrubs planted here to remain in the future? 360.000<0.001
Yes1268416.20162.113
No241612.92131.909
Would you like to taste the fruit from the trees and shrubs planted here? 938.500<0.001
Yes1187916.17162.105
No322113.84152.567
Would you be willing to participate in the maintenance of green spaces here in this location? 1447.000<0.001
Agree (+definitely agree)533516.89171.948
Disagree (+definitely disagree)976515.01152.374
Would you be willing to pay higher property taxes to preserve the existing green spaces here? 1422.500<0.001
Agree (+definitely agree)453016.89171.991
Disagree (+definitely disagree)1057015.15152.381
Would you be willing to participate more in green spaces maintenance if you would have more information about the orchard? 1409.000<0.001
Agree (+definitely agree)654316.85171.938
Disagree (+definitely disagree)855714.78152.342
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Remr, J.; Sedlák, J. From Planting to Participation: Early-Phase Resident Attachment in an Urban Fruit Orchard. Urban Sci. 2025, 9, 492. https://doi.org/10.3390/urbansci9120492

AMA Style

Remr J, Sedlák J. From Planting to Participation: Early-Phase Resident Attachment in an Urban Fruit Orchard. Urban Science. 2025; 9(12):492. https://doi.org/10.3390/urbansci9120492

Chicago/Turabian Style

Remr, Jiri, and Jiri Sedlák. 2025. "From Planting to Participation: Early-Phase Resident Attachment in an Urban Fruit Orchard" Urban Science 9, no. 12: 492. https://doi.org/10.3390/urbansci9120492

APA Style

Remr, J., & Sedlák, J. (2025). From Planting to Participation: Early-Phase Resident Attachment in an Urban Fruit Orchard. Urban Science, 9(12), 492. https://doi.org/10.3390/urbansci9120492

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