Abstract
We present a multi-country and multilingual dataset on garden characteristics, gardening practices, and gardeners’ environmental attitudes based on a questionnaire survey conducted across nine Central and Eastern European countries: Croatia, Czechia, Estonia, Hungary, Latvia, Poland, Romania, Slovakia, and Slovenia. The survey was collaboratively designed and translated into ten languages by native speakers to ensure cultural and linguistic accuracy. It was distributed online through diverse channels, yielding 5511 responses. The dataset enables exploration of relationships between gardening practices and socio-cultural factors at local, national, and regional scales. The questionnaire covered topics such as garden characteristics, management practices, pesticide use, biodiversity-supporting actions, and environmental awareness, offering a comprehensive overview of gardening in the region. The dataset is suitable for cross-country comparisons, machine learning analyses, and the development of indices that quantify ecological value or management intensity. The multilingual questionnaire supports reuse in future studies, facilitating replication or adaptation elsewhere. By making the dataset openly available, we provide a resource for researchers and practitioners interested in urban biodiversity, sustainability, and human–nature interactions.
Background & Summary
Urbanisation is a major driver of biodiversity loss worldwide1,2, contributing to habitat fragmentation3, the disruption of ecological interactions4, and the decline of ecosystem services essential for human well-being, such as pollination and natural pest control5. To mitigate these impacts, attention has increasingly turned to enhancing the ecological quality of urban green spaces, especially in densely human-modified environments like cities6,7. While public parks and other green infrastructure are often prioritised in conservation planning8,9, private domestic gardens and allotments also represent a substantial proportion of urban land cover in Europe — estimated between 16 and 36% depending on the country10,11 — and therefore their role in urban biodiversity and ecosystem services should not be overlooked. These privately or small community managed spaces can provide habitats and stepping stones for wildlife, improve ecological connectivity, and deliver multiple benefits for biodiversity and people alike12,13.
The conservation potential of private gardens and allotments depends strongly on how they are managed14–16. Practices such as frequent mowing, pesticide use, or the removal of microhabitats reduce biodiversity, while creating undisturbed patches, planting native species, or maintaining ponds can significantly enhance it15,17. Consequently, understanding garden management practices is key to evaluating gardens’ contribution to the biodiversity of urban ecosystems16.
Research into the biodiversity of private gardens and allotments has expanded considerably in Western Europe and North America since the 1990s, with studies showing that even small gardens can support high levels of species richness18 and act as habitat refuges and stepping stones in urban ecological networks19. In contrast, comparable research in Central and Eastern Europe (CEE) remains limited, despite the region’s distinctive socio-economic context and gardening traditions16,20.
In Central and Eastern Europe, gardening—traditionally a means of food self-provisioning during economic hardship—has only recently shifted toward recreational and biodiversity-oriented forms, yet limited access to ecological knowledge and continued reliance on conventional, pesticide-based practices indicate slower adoption of biodiversity-friendly approaches16. These shifts highlight the need for CEE-specific data to better understand how cultural and historical background, gardening motivations, and socio-economic drivers shape garden management and ecological outcomes in the region and in countries showing similar trajectories.
This dataset21, available through the Figshare repository, aims to fill this information gap and gathers structured data on the gardening practices and gardening motivation of CEE countries. It provides anonymised data from a cross-national questionnaire survey of nine CEE countries. The survey, containing 59 questions, designed to collect detailed information about respondents’ socio-demographic background, personal motivations for gardening, and the characteristics of their gardens (e.g. its size, how much area was occupied by different types of plants, such as fruit trees, ornamental plants, and lawn, and what was the adjacent land use), as well as their plant protection and -growing practices. In addition, the survey recorded information on pesticide use habits (types of products used, target organisms, perceived importance of pesticide use, and purchasing habits, etc.), mowing frequency, biodiversity-supporting practices (especially for insect pollinators) and their practical implementation (e.g. creating supporting habitats), as well as on the degree of environmental awareness of the gardeners (e.g. opinions about threats to pollinators and knowledge of risks associated with synthetic pesticides, like neonicotinoids). Respondents were also asked about their familiarity with the biodiversity present in their gardens and the tools they use for species identification (e.g. whether they use mobile applications), as well as whether they apply spot-on insecticide treatments on their pets that are allowed outdoors in the garden.
A total of 5511 gardeners responded to the questionnaire, representing a wide range of cultural backgrounds and gardening practices. The data provide a valuable resource for investigating the interplay between socio-demographic factors, garden management practices, and gardener attitudes in maintaining biodiversity-friendly gardens across multiple scales and allows for investigations using a variety of analytical approaches, including complex statistical modelling, machine learning, and network analysis. Indeed, subsets of this dataset have already been used to investigate CEE gardeners’ attitudes towards biodiversity-friendly gardening and small-scale variation in these attitudes15,16. However, while the datasets underlying those studies partially overlap with the dataset described here, the present data descriptor provides the complete questionnaire and associated responses, including survey questions not analysed previously, as well as responses from participants who were excluded from the earlier studies. In addition, the entire questionnaire, including all questions and structure, is available in ten languages, enabling its reuse either in full or on a question-by-question basis.
Methods
Study area and data collection
The questionnaire was distributed in nine CEE countries (Croatia, Czechia, Estonia, Hungary, Latvia, Poland, Romania, Slovakia, and Slovenia), all of which were formerly part of the Eastern Block and are currently members of the European Union.
The questions were developed in Hungarian and translated first to English and then from English to Croatian, Czech, Estonian, Latvian, Polish, Romanian, Slovak, and Slovenian languages by native-speaking collaborators to ensure linguistic and cultural accuracy. Thus, the participants could choose from the ten languages in which they wanted to complete the questionnaire. The wording of all questions was kept deliberately neutral and simple to avoid bias and respondents were also able to contact local collaborators for clarification in their own language.
The questionnaire was distributed exclusively online and was made accessible in two ways: through a direct link to the Google Form(s), and via a dedicated website (https://vargaszilay.hu/questionnaire/) where respondents could select their preferred language from the available translations before completing the survey. The questionnaire was actively distributed for a 90-day period in each of the nine participating countries between 26 October 2022 and 18 May 2023, with the start and end dates slightly varying by country. Following this period, the survey remained accessible online but was no longer actively promoted. The released dataset contains responses from 26 October 2022 to 13 June 2023 time window. The questionnaire was disseminated through a broad variety of channels to reduce the risk of bias towards particular respondent groups. These channels included gardening-oriented websites, and various online social media platforms (for instance Facebook groups and pages) where QR codes and hashtags were used to increase the sharing efficiency. Moreover, through targeted email distributions, outreach efforts extended to professional associations, non-governmental organisations, foundations, and societies dedicated to gardening and environmental conservation. To standardise dissemination, a document with ‘Tips and Tricks’ was provided to collaborators, together with an English template text for social media sharing, which could be translated into their respective languages.
Ethics statement
Ethical approval for this study, including the study protocol and data sharing, was granted by the Daugavpils University Biology and Medical Research Ethics Committee (No. 107). According to the European GDPR regulation, a Data Protection and Privacy Statement was available alongside the questionnaire in all languages. Thus ethical considerations were minimal and aligned with institutional protocols and the principles of the Declaration of Helsinki. Although, to a certain degree, our study involved humans, it did not constitute an experimental setting and did not involve the use of human tissue. Our online questionnaire was entirely voluntary and anonymous, and by completing the questionnaire, respondents consented to the use of their answers for research purposes. No personal data were collected, and before beginning, participants were informed about the aim of the study. The Form did not automatically store respondents’ email addresses; however, participants had the option to provide it at the end of the questionnaire or input personal information in the free text fields. This, and all other, potentially sensitive information was removed and pseudonymised (e.g. grouping participants within broad age groups rather than giving specific ages) prior to data release, ensuring that no respondent can be identified from the dataset in any form. Based on these, the Daugavpils University Biology and Medical Research Ethics Committee has thus approved a waiver of consent for the publication of the dataset (No. 107).
Questionnaire structure
The questionnaire gathered information about the coarse location and the main characteristics of the garden, the sociodemographic parameters, the garden owners’ motivations, cultivation habits, pesticide usage, environmental awareness, and pollinator-friendly practices. The questions were organised into nine sections (1. Location of the garden; 2. Sociodemographic parameters; 3. ‘What is your garden like?’; 4. Motivation; 5. Gardening habits; 6. Plants growing in the garden; 7. Pesticides in the garden; 8. Pollinators in the garden; 9. Final questions, e.g. ‘How did you learn about this questionnaire?’ or ‘How do you learn/gather knowledge/information about gardening?’) (Fig. 1).
Fig. 1.

Structure of the multilingual, multi-country questionnaire. The numbers in parentheses after each of the nine section titles indicate the number of questions included in that section. Section 7 was available only to respondents who reported using pesticides at the last question of Section 6.
The questionnaire was designed in Google Forms, one form for each language, divided into separate pages to make completion easier for respondents, and took a maximum of 15 minutes to complete. It was mandatory to respond to 55 of the total 59 questions (see in the questionnaire.xlsx). Overall, we aimed to formulate the questions in a concise and straightforward manner. To facilitate easier data processing, free-text responses were not allowed, with the exception of two questions at the end of the questionnaire (‘Please describe in a few words/one sentence what your garden means to you.’; ‘Please describe briefly what you like the most in your garden.’). Thus, depending on the type of question, six different formats were used: checkbox (10), linear scale (5), multiple choice (26), multiple choice grid (14), paragraph (2), and short answer (1) (see details in the questionnaire.xlsx).
In the first two questions, the respondents could choose in which country and lower-level administrative units (respectively) their garden was located. The second section was country-specific: only administrative units of the previously chosen country were listed. We recorded the finer scale of residency according to the Nomenclature of Territorial Units for Statistics (henceforth NUTS22). Because of the large number of NUTS-3 regions in Poland, to simplify the questionnaire, here, residencies were recorded at NUTS-2 levels, while the other eight participating countries were recorded at NUTS-3 levels. After these, the questions were the same for everyone. However, section seven (Pesticides in the garden), which focused on pesticide-use habits, was shown only to respondents who answered ‘Yes’ to the question ‘Do you use pesticides?’. Respondents answering ‘No’ were automatically directed to Section 8 (Pollinators in the garden) (Fig. 1).
For the question ‘What pollinators do you regularly observe/see in your garden?’, photos were provided to illustrate insect pollinator groups (butterflies, bumblebees, honeybees, other wild bees, wasps, ants, hoverflies, other flies, and beetles). For the question listing potential threat factors and asking ‘To what level do you think the factors below threaten wild pollinators?’, respondents were explicitly informed that the domestic honeybee is not considered a wild pollinator.
Data processing
The data were downloaded from the Google Forms as plain coma-separated text (.csv) files in each language by the first author, then, to improve the usability of the dataset and to allow future reuse, formatting and harmonisation processes were carried out in Python and R environments.
The data cleaning was performed in a Python environment23 using the ‘pandas’24 package. The figures in this paper were produced in an R environment25, using the ‘sf’26, ‘ggspatial’27, ‘rnaturalearth’28, and ‘ggplot2’27 packages. In addition, two shapefiles29,30 were used to support the spatial visualisations.
After selecting their country, respondents could choose the administrative unit where their garden is located (Fig. 1), as displayed in their respective language, including special characters, where applicable. Since these administrative unit names often contained special characters, we matched them to the corresponding NUTS categories for standardisation (see in the dictionary.xlsx).
To facilitate cross-linguistic comparability, and to avoid encoding incompatibility issues with special characters, both the survey questions and response options were translated into English using a dictionary that aligns the multilingual content with standardised English terminology. The English language datasets were then merged and converted into comma-separated values (.csv; see in the main_dataset.csv). The data dictionary and the list of questions and answers are available in Excel (.xlsx) format. All files follow a consistent naming convention and UTF-8 encoding to ensure accessibility and interoperability across systems.
Data Records
Data structure, description of data and documentation files
The released dataset (main_dataset.csv) is available in the Figshare repository21. It consists of 5512 rows (one header row and 5511 respondent records) and 101 columns (questions), values separated by commas. It includes only the core questions; optional items such as the respondent’s email address and open-ended, free-text questions were excluded. Except for the first two columns, which are named as ‘ID’ and ’Country_code’, the columns in the dataset (main_dataset.csv) are labelled with question identifiers ranging from ‘Q_1’ to ‘Q_99’ (since the answers to multiple choice grid were recorded as separate columns, the number of columns exceeds those of the questions). For questions that allowed multiple answers, the responses are listed in one value field, separated by semicolons.
In addition, a separate dictionary file (dictionary.xlsx) is provided for the translations of the questions and answers to all languages, along with a list of the questions and possible answer options in English (questionnaire.xlsx). These files are cross-referenced with each other and with the main dataset through common identifiers (e.g. ‘Main_dataset_ID’ column). The questionnaire.xlsx file indicates the structure of the questionnaire, showing which of the nine sections each question belongs to, the question type (e.g. multiple choice), and whether answering the question was mandatory.
Data Overview
Characteristics of the sample population
Across all countries, the proportion of female respondents was generally higher than that of males (Table 1). Most participants were between 26 and 55 years of age and held middle-level (secondary or high school) or postsecondary education (college or university level). The majority of respondents lived in towns or rural areas, while smaller proportions resided in capital cities or large urban settlements. Approximately half of the respondents reported having children.
Table 1.
Sociodemographic characteristics of the study population (n = 5511).
| Country ISO code | |||||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| CZ | EE | HR | HU | LV | PL | RO | SI | SK | |||||||||||
| Variables | Levels | n | % | n | % | n | % | n | % | n | % | n | % | n | % | n | % | n | % |
| Gender | Female | 531 | 79.85 | 664 | 93.26 | 389 | 80.21 | 915 | 72.68 | 350 | 88.38 | 538 | 71.45 | 300 | 67.42 | 292 | 83.19 | 303 | 68.09 |
| Male | 129 | 19.4 | 46 | 6.46 | 96 | 19.79 | 343 | 27.24 | 46 | 11.62 | 212 | 28.15 | 144 | 32.36 | 59 | 16.81 | 140 | 31.46 | |
| Other | 5 | 0.75 | 2 | 0.28 | 0 | 0 | 1 | 0.08 | 0 | 0 | 3 | 0.4 | 1 | 0.22 | 0 | 0 | 2 | 0.45 | |
| Age | 18–25 | 34 | 5.11 | 4 | 0.56 | 17 | 3.51 | 50 | 3.97 | 7 | 1.77 | 105 | 13.94 | 29 | 6.52 | 10 | 2.85 | 10 | 2.25 |
| 26–35 | 179 | 26.92 | 89 | 12.5 | 70 | 14.43 | 196 | 15.57 | 43 | 10.86 | 91 | 12.08 | 75 | 16.85 | 49 | 13.96 | 60 | 13.48 | |
| 36–45 | 216 | 32.48 | 181 | 25.42 | 132 | 27.22 | 334 | 26.53 | 63 | 15.91 | 213 | 28.29 | 163 | 36.63 | 95 | 27.07 | 137 | 30.79 | |
| 46–55 | 131 | 19.7 | 217 | 30.48 | 154 | 31.75 | 334 | 26.53 | 130 | 32.83 | 187 | 24.83 | 95 | 21.35 | 90 | 25.64 | 113 | 25.39 | |
| 56–65 | 59 | 8.87 | 166 | 23.31 | 85 | 17.53 | 180 | 14.3 | 120 | 30.3 | 82 | 10.89 | 51 | 11.46 | 67 | 19.09 | 80 | 17.98 | |
| Over 65 | 46 | 6.92 | 55 | 7.72 | 27 | 5.57 | 165 | 13.11 | 33 | 8.33 | 75 | 9.96 | 32 | 7.19 | 40 | 11.4 | 45 | 10.11 | |
| Education level | Elementary | 8 | 1.2 | 11 | 1.54 | 0 | 0 | 7 | 0.56 | 4 | 1.01 | 8 | 1.06 | 2 | 0.45 | 4 | 1.14 | 4 | 0.9 |
| Middle | 237 | 35.64 | 178 | 25 | 172 | 35.46 | 346 | 27.48 | 78 | 19.7 | 177 | 23.51 | 123 | 27.64 | 92 | 26.21 | 135 | 30.34 | |
| Postsecondary | 315 | 47.37 | 459 | 64.47 | 258 | 53.2 | 822 | 65.29 | 278 | 70.2 | 514 | 68.26 | 244 | 54.83 | 232 | 66.1 | 267 | 60 | |
| Postgraduate | 105 | 15.79 | 64 | 8.99 | 55 | 11.34 | 84 | 6.67 | 36 | 9.09 | 54 | 7.17 | 76 | 17.08 | 23 | 6.55 | 39 | 8.76 | |
|
Type of the urban settlement Having children |
Capital | 60 | 9.02 | 42 | 5.9 | 83 | 17.11 | 154 | 12.23 | 22 | 5.56 | 128 | 17 | 6 | 1.35 | 26 | 7.41 | 86 | 19.33 |
| City | 68 | 10.23 | 28 | 3.93 | 71 | 14.64 | 238 | 18.9 | 41 | 10.35 | 106 | 14.08 | 80 | 17.98 | 21 | 5.98 | 22 | 4.94 | |
| Town | 126 | 18.95 | 122 | 17.13 | 130 | 26.8 | 342 | 27.16 | 56 | 14.14 | 279 | 37.05 | 61 | 13.71 | 52 | 14.81 | 62 | 13.93 | |
| Countryside | 400 | 60.15 | 279 | 39.19 | 193 | 39.79 | 511 | 40.59 | 206 | 52.02 | 231 | 30.68 | 293 | 65.84 | 206 | 58.69 | 265 | 59.55 | |
| Farmland | 11 | 1.65 | 241 | 33.85 | 8 | 1.65 | 14 | 1.11 | 71 | 17.93 | 9 | 1.2 | 5 | 1.12 | 46 | 13.11 | 10 | 2.25 | |
| Yes | 385 | 57.89 | 378 | 53.09 | 248 | 51.13 | 615 | 48.85 | 229 | 57.83 | 396 | 52.59 | 251 | 56.4 | 187 | 53.28 | 267 | 60 | |
| No | 280 | 42.11 | 334 | 46.91 | 237 | 48.87 | 644 | 51.15 | 167 | 42.17 | 357 | 47.41 | 194 | 43.6 | 164 | 46.72 | 178 | 40 | |
| Total number of respondents | 665 | 712 | 485 | 1259 | 396 | 753 | 445 | 351 | 445 | ||||||||||
The largest number of respondents were from Hungary, and Estonia was the most represented country in proportion to its population size. Gardeners from certain regions in Romania and Poland showed relatively low willingness to participate in the survey (Fig. 2).
Fig. 2.

Number of respondents in the nine participating countries by NUTS-2 regions (thick black lines indicate national borders). The colour intensity of the maps represents the number of respondents per 100000 inhabitants in each NUTS-2 region and is displayed on a logarithmic scale. The pie charts within countries illustrate mowing frequency during the growing season (April–September). Different colours indicate the mowing frequency categories as follows: salmon – ‘Several times a month’, blue – ‘Once a month’, gold – ‘Every two months’, grey – ‘Twice during the growing season’, green – ‘Once during the growing season’, and pale yellow – ‘I do not mow the lawn at all’.
In terms of mowing practices, respondents from the two northernmost countries (Estonia and Latvia) reported mowing their lawns very frequently (several times per month) whereas in Croatia and Romania a notable share of respondents stated that they do not mow their lawns at all. Overall, mowing once a month was the most common frequency during the growing season, from April to September (Fig. 2).
In most countries, respondents who reported supporting insect pollinators in their garden were more prevalent than those who did not (Fig. 3). However, a relatively high proportion of pollinator supporters also reported using pesticides, and their pesticide use rate was higher compared to respondents who did not support pollinators. In contrast, respondents who did not support pollinators showed a higher proportion of synthetic pesticide use within the pesticide-user group.
Fig. 3.

Relative frequency of respondents (gardeners) by whether they support pollinators (Y – Yes, N – No) and whether they use pesticides (No: light green, Yes: light yellow). Numbers within bars indicate the absolute number of respondents. The dark orange segments indicate the proportions of synthetic pesticides users within the pesticide-user groups.
Technical Validation
The questionnaire was translated into the target languages by collaborators who were native speakers. To ensure that no differences occurred across the questionnaires other than language, all forms were initially created by the project leader. Editing rights were then granted to collaborators so that they could thoroughly review the wording. Where necessary, they adapted questions by adding country-specific examples to ensure cultural relevance. For clarifications regarding terminology, collaborators consulted with the project coordinator to agree on the most appropriate translation of technical terms. Prior to dissemination, editing rights were restricted to the project leader alone. This procedure was essential to maintain standardisation across all versions, as Google Forms can be modified at any time, potentially resulting in unintended alterations. By exporting each questionnaire from Google Forms according to its language, the surveys were suitable for centralised data management.
All data exported directly from Google Forms were automatically saved into text-based tables (.txt) that preserved both the original submission order and the exact timestamps of responses.
Data quality was assessed through a series of automated and manual validation procedures. For each variable, data type, allowable values, missing values, and consistency across language versions were verified. Categorical variables were checked against the predefined response options, while numerical variables were screened for implausible values and outliers. The merged dataset was then compared with the original exports from Google Forms to confirm that all records and variables had been transferred correctly. Since the termination of the survey, the data were analysed in a variety of ways and used in publications (e.g. Varga-Szilay, et al., 2024; Varga-Szilay & Pozsgai, 202215,17 with no obvious data-related weaknesses.
Usage Notes
Our database provides a unique resource for investigating gardeners’ attitudes, motivations, knowledge, and management practices across nine European countries, where no comparable survey at this scale has previously been conducted. Combined methods of machine learning and network analysis can be applied to explore associations between gardening practices and socio-demographic characteristics (e.g. Varga-Szilay, et al., 202415). The data can be reused for cross-country comparisons across the nine participating countries, but it is also possible to extract country-specific subsets, enabling in-depth analyses at the country level as well as pinpointing national characteristics of garden structures, gardening habits or pesticide use. Potential applications also include analyses focusing on pesticide-related gardening practices, which may contribute to a better understanding of usage patterns and support the promotion of alternatives that reduce the reliance on widely available synthetic plant protection products. The dataset also allows researchers or policy makers to identify broader gardeners’ behavioural and attitudinal patterns that may inform future interventions aimed at engaging gardeners and encouraging biodiversity-friendly practices.
Furthermore, population statistics (e.g. Eurostat, 2022, 202431,32) can be integrated with this dataset, enabling normalisation of responses by national or regional population size; for instance, by expressing respondent numbers per 100000 inhabitants in each NUTS-2 region16. This compatibility facilitates the inclusion of our dataset both in large-scale comparative analyses and NUTS-level regional studies.
By providing translations of all questions and answer options into the official languages of the nine surveyed CEE countries, in addition to the English version, we ensured that the questionnaire can be readily reused in future studies. This approach facilitates direct replication or partial reuse of the survey in other European regions, including Western and Central-Eastern European regions or the Balkans, in a fully comparable form. Such harmonisation enables cross-country comparisons and supports the development of a unified framework for studying gardening practices and biodiversity-friendly behaviours across Europe.
The dataset does not include precise geographical coordinates of individual gardens and is therefore not suitable for fine-scale spatial analyses. In addition, it does not contain direct measurements of garden biodiversity. Future studies could combine similar questionnaire-based datasets with citizen science initiatives or standardised biodiversity surveys to link gardening practices with observed patterns of biodiversity.
Acknowledgements
We are grateful to all respondents and all people who helped to distributed the questionnaire.
Author contributions
Z.V.S. and G.P. conceived the idea of the project, designed the study and created the first version of the questionnaire in Hungarian. Z.V.S., G.P., K.G.F. and G.S. finalised the questions. Z.V.S. and G.P. translated and specialised the questionnaire into English, and L.S.J., S.V., A.B., K.B., D.B., A.K., J.R., E.V. translated it into the eight target languages. All authors participated in data collection and project administration. Analysis was performed by Z.V.S. and G.P. The draft of the manuscript was written by Z.V.S. and G.P. All authors read and approved the final manuscript.
Funding
SV was supported by the Estonian Research Council (PUTJD1307). DB was supported by the Slovenian Research Agency (research core funding No.P1-0255) and FRACTAL (Interreg Alpine Space). AK was supported by the Slovak Scientific Grant Agency VEGA 2/0097/23. EV was supported by the Estonian Research Council grant PRG1056. LSJ was supported by the Croatian Science Foundation, MEDITERATRI project (HRZZ UIP 2017-05-1046). GP was supported by the project Open Access FCT-UIDP/00329/2020-2024 (Thematic Line 1 – integrated ecological assessment of environmental change on biodiversity, https://doi.org/10.54499/UIDB/00329/2020) and by the Azores DRCT Pluriannual Funding (M1.1.A/FUNC.UI&D/010/2021-2024). Open access funding provided by University of Pannonia.
Data availability
All data are openly available in the Figshare repository21, under a CC-BY 4.0 Licence. All related computer code is also available on the project’s GitHub repository: https://github.com/zsvargaszilay/Central_Eastern_Europe_Gardening_Dataset.
Code availability
The computer codes (Python and R) and packages used to clean the dataset and generate the table and the figures in this paper are openly available in the https://github.com/zsvargaszilay/Central_Eastern_Europe_Gardening_Dataset GitHub repository.
Competing interests
The authors declare no competing interests.
Footnotes
Publisher’s note Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Contributor Information
Zsófia Varga-Szilay, Email: zsofia@vargaszilay.hu, Email: varga.zsofia@mk.uni-pannon.hu.
Arvīds Barševskis, Email: arvids.barsevskis@du.lv.
Gábor Pozsgai, Email: pozsgaig@coleoptera.hu.
References
- 1.Fenoglio, M. S., Calviño, A., González, E., Salvo, A. & Videla, M. Urbanisation drivers and underlying mechanisms of terrestrial insect diversity loss in cities. Ecological Entomology46, 757–771 (2021). [Google Scholar]
- 2.Sánchez-Bayo, F. & Wyckhuys, K. A. G. Worldwide decline of the entomofauna: A review of its drivers. Biological Conservation232, 8–27 (2019). [Google Scholar]
- 3.Concepción, E. D., Moretti, M., Altermatt, F., Nobis, M. P. & Obrist, M. K. Impacts of urbanisation on biodiversity: the role of species mobility, degree of specialisation and spatial scale. Oikos124, 1571–1582 (2015). [Google Scholar]
- 4.Theodorou, P. The effects of urbanisation on ecological interactions. Current Opinion in Insect Science52, 100922 (2022). [DOI] [PubMed] [Google Scholar]
- 5.Eigenbrod, F. et al. The impact of projected increases in urbanization on ecosystem services. Proceedings of the Royal Society B: Biological Sciences278, 3201–3208 (2011). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 6.Castelli, K. R., Silva, A. M. & Dunning, J. B. Improving the biodiversity in urban green spaces: A nature based approach. Ecological Engineering173, 106398 (2021). [Google Scholar]
- 7.Lepczyk, C. A. et al. Biodiversity in the City: Fundamental Questions for Understanding the Ecology of Urban Green Spaces for Biodiversity Conservation. BioScience67, 799–807 (2017). [Google Scholar]
- 8.Climate ADAPT. Urban green and blue infrastructure planning. https://climate-adapt.eea.europa.eu/en/metadata/adaptation-options/green-spaces-and-corridors-in-urban-areas (2021).
- 9.Minor, E. S., Anderson, E. C., Belaire, J. A., Garfinkel, M. & Smith, A. D. Urban green infrastructures and ecological networks for urban biodiversity conservation. in Urban Biodiversity (Routledge, 2017).
- 10.Cameron, R. W. F. et al. The domestic garden – Its contribution to urban green infrastructure. Urban Forestry & Urban Greening11, 129–137 (2012). [Google Scholar]
- 11.Goddard, M. A., Dougill, A. J. & Benton, T. G. Scaling up from gardens: biodiversity conservation in urban environments. Trends in Ecology & Evolution25, 90–98 (2010). [DOI] [PubMed] [Google Scholar]
- 12.Delahay, R. J., Sherman, D., Soyalan, B. & Gaston, K. J. Biodiversity in residential gardens: a review of the evidence base. Biodivers Conserv32, 4155–4179 (2023). [Google Scholar]
- 13.Seitz, B. et al. Land sharing between cultivated and wild plants: urban gardens as hotspots for plant diversity in cities. Urban Ecosyst25, 927–939 (2022). [Google Scholar]
- 14.Quistberg, R. D., Bichier, P. & Philpott, S. M. Landscape and local correlates of bee abundance and species richness in urban gardens. Environmental Entomology45, 592–601 (2016). [DOI] [PubMed] [Google Scholar]
- 15.Varga-Szilay, Z., Fetyko, K. G., Szovenyi, G. & Pozsgai, G. Bridging biodiversity and gardening: Unravelling the interplay of socio-demographic factors, garden practices, and garden characteristics. Urban Forestry & Urban Greening97 (2024).
- 16.Varga-Szilay, Z. et al. Improving biodiversity in Central and Eastern European gardens needs regionally scaled strategies. Urban Forestry & Urban Greening113 (2025).
- 17.Varga-Szilay, Z. & Pozsgai, G. Plant growers’ environmental consciousness may not be enough to mitigate pollinator declines: a questionnaire-based case study in Hungary. Pest Management Science79, 1284–1294 (2022). [DOI] [PubMed] [Google Scholar]
- 18.Griffiths-Lee, J., Nicholls, E. & Goulson, D. Sown mini-meadows increase pollinator diversity in gardens. J Insect Conserv26, 299–314 (2022). [Google Scholar]
- 19.Marín, L., Martínez-Sánchez, M. E., Sagot, P., Navarrete, D. & Morales, H. Floral visitors in urban gardens and natural areas: Diversity and interaction networks in a neotropical urban landscape. Basic and Applied Ecology43, 3–15 (2020). [Google Scholar]
- 20.Coisnon, T., Rousselière, D. & Rousselière, S. Information on biodiversity and environmental behaviors: A European study of individual and institutional drivers to adopt sustainable gardening practices. Social Science Research84, 102323 (2019). [DOI] [PubMed] [Google Scholar]
- 21.Varga-Szilay, Z. et al. Central Eastern Europe Gardening Dataset 10.6084/m9.figshare.30804422 (2025). [DOI]
- 22.Eurostat. NUTS - Nomenclature of territorial units for statistics - Overview. https://ec.europa.eu/eurostat/web/nuts (2021).
- 23.Python Software Foundation. Python Language Reference (2019).
- 24.The pandas development team. pandas-dev/pandas: Pandas. Zenodo, 10.5281/zenodo.7344967 (2022). [DOI]
- 25.R Core Team. R: A language and environment for statistical computing (2021).
- 26.Pebesma, E. Simple features for r: Standardized support for spatial vector data. The R Journal10, 439–446 (2018). [Google Scholar]
- 27.Dunnington, D., Thorne, B. & Hernangómez, D. ggspatial: Spatial Data Framework for ggplot2, (2025).
- 28.Introduction to rnaturalearth. https://cran.r-project.org/web/packages/rnaturalearth/vignettes/rnaturalearth.html.
- 29.GISCO. GISCO data distribution API - Countries 2024. https://gisco-services.ec.europa.eu/distribution/v1/countries-2024.html (2024).
- 30.ArcGIS Data and Maps. Europe NUTS 3 Demographics and Boundaries - Overview. https://www.arcgis.com/home/item.html?id=5eb88decbff54520b49c785241c07bf4 (2022).
- 31.Eurostat. Population on 1 January. Eurostat, 10.2908/TPS00001 (2022). [DOI]
- 32.Eurostat. Rural development - Methodology https://ec.europa.eu/eurostat/web/rural-development/methodology (2024).
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Data Availability Statement
All data are openly available in the Figshare repository21, under a CC-BY 4.0 Licence. All related computer code is also available on the project’s GitHub repository: https://github.com/zsvargaszilay/Central_Eastern_Europe_Gardening_Dataset.
The computer codes (Python and R) and packages used to clean the dataset and generate the table and the figures in this paper are openly available in the https://github.com/zsvargaszilay/Central_Eastern_Europe_Gardening_Dataset GitHub repository.
