Sec. Urban Ecology
Volume 10 - 2022 | https://doi.org/10.3389/fevo.2022.1032022
Editorial: Urban ecology and human health
- 1School of Natural Sciences, University of Tasmania, Hobart, TAS, Australia
- 2School of Public Health Studies, University of Wolverhampton, Wolverhampton, United Kingdom
- 3School of Environment, Education and Development, The University of Manchester, Manchester, United Kingdom
Editorial on the Research Topic
Urban ecology and human health
The character, design and biodiversity of urban ecosystems have both beneficial and negative impacts on human health and wellbeing (Flies et al., 2019). However, the ways in which urban ecosystems influence human health—positively and negatively—remain unclear. Current knowledge is dominated by research in large cities and the global north, and therefore is incomplete and biased (Kendal et al., 2020). The diverse chapters in this special issue contribute to the “Urban One Health” and “Ecology with Cities” frameworks (de Leeuw, 2021; Ellwanger et al., 2022) that bring together the ecological, social, political, and community engagement aspects of ensuring public health among the intricacy of interactions, both between organisms and within complex, changing, and diverse urban environments.
Greenspace ecosystem services and disservices
Urban green and blue spaces provide many diverse beneficial ecosystem services (ES; Flies et al., 2017; Lai et al., 2019; Mavoa et al., 2019). They play an important role in mitigating air pollution from exhaust and industrial emissions, and health-impacting haze from wildfires, as in Malaysia (Jaafar et al.). An examination of urban ES in China found that urban agglomerations typically had lower ES than their surroundings (Shao et al.), but among other variables, the presence of green infrastructure (GI), like woodlands increased urban ES.
Urban greenspaces and GI nevertheless can also provide ecosystem disservices (Lyytimäki and Sipilä, 2009) for example, as a mixing ground for native and introduced species and between human and non-human animals. These novel urban interactions may change disease patterns and adaptation by vector species and their pathogens. The Chagas disease vector, Triatoma dimidiate, may have adapted to the urban environment (de Oca-Aguilar et al.) as indicated by changes in the thorax and antennal phenotype of this species between urban and rural areas, suggesting adaptation leading to altered sensory and locomotion performance. However, as these differences seem not to have altered the insect's fecundity/fitness, the impact of the insect's urban adaptation on human health is unclear.
Urban sustainability, urban greening, and human wellbeing
Less tangible are the impacts of urban environments on human mental health and subjective wellbeing. For example, biodiversity can be supportive of human health and wellbeing (Taylor and Hochuli, 2014; Flies et al., 2017; Mavoa et al., 2019; Schebella et al., 2019) and urbanization can homogenize animal and microbial biodiversity (Johnston et al., 2014; Morelli et al., 2016; Flies et al., 2020). However, the biodiversity-wellbeing mechanisms and how they impact urban greenspace benefits remain unclear (Lai et al., 2019). Untangling the role of biodiversity in the greenspace-wellbeing connection will require the type of interdisciplinary effort for which Hedin et al. make a plea and provide a framework.
Further exploration of the relationship between greenspace and wellbeing in two cities in Kenya and Thailand found wellbeing was most strongly influenced by availability of basic infrastructure (waste removal, accessible clean water; Cinderby et al.). Once these amenities were in place, social (crime and tenure) and environmental (noise and air quality) issues became important for community wellbeing. Spending time in urban greenspaces could mitigate city-living stresses even for residents of informal neighborhoods. Cinderby et al. demonstrate the need for diversity and equity in public realm space provision to ensure social and spatial justice.
The COVID-19 pandemic lockdowns and restrictions changed most people's use of urban greenspace. During a COVID-19 lockdown in Brisbane, Australia, greenspace use patterns changed, varying by both individual and greenspace characteristics (Berdejo-Espinola et al.). Places with access to blue spaces and good accessibility (carparks/public transport) experienced increased use; but places with foliage height diversity had decreased use. More females than males changed their greenspace visitation frequency during COVID-19. Females had increased reliance on greenspaces for social and family interactions and spiritual reasons, while males for nature interactions and mental health benefits during COVID lockdowns. Clearly, different times of stress and national crisis lead to major behavioral changes during which urban greenspace is a great asset for human wellbeing and morale. Understanding such changes during crises will help develop more resilient urban greenspace planning and policies.
Private and community vegetable gardens were a refuge for many during COVID lockdowns (Marsh et al., 2021) are key parts of urban greenery. Community gardens support social, physical and dietary health (Egli et al., 2016) and urban agriculture is a possible nature-based solution to socio-ecological challenges in cities (Kingsley et al., 2021). The ways people interact with gardens differ between countries, with few studies in the global south. In a South Africa, Du Toit et al. examined food security in a community garden scheme designed to encourage small garden plots in a community where 39% of participants reported hunger affecting the entire household and 51% were at risk of hunger. Although 72% participants planted fruits and vegetables, the gardens contributed little to food security; Du Toit et al. explore the reasons, including cultural and food-purchasing practices.
Planning and design for urban nature to improve health and wellbeing
Understanding the ways different communities, ethnic groups, and age cohorts use urban greenspaces is an interdisciplinary effort helping toward Urban One Health. Children's views are seldom sought when designing greenspaces (Vidal and Seixas). Often urban children would rather play in a seminatural local creek area than in a formal municipal park playground. Vidal and Seixas argue that community plans ought to include special “Children Green Infrastructure” designed to link children to nature where they live, learn, and play.
Such provision for individual and groups extends into the design of other green infrastructure (GI) like green roofs and walls. Adequate planning, design, and management, especially for water in changing climates, can maximize ES health benefits of GI (Sang et al.). Sometimes trade-offs occur in planting decisions: aesthetic choices aligning with human preferences can result in greater wellbeing benefits, while opting for native species or biodiverse combinations may result in greater ES. This trade-off may be circumvented by using color theory to create aesthetically pleasing, biodiverse designs for living walls (Thorpert et al.).
Urban greenspace and the resultant ecosystem services benefit human health everywhere, but values, perceptions, uses and risks remain diverse, between and within nations and communities. The more we learn about them, the more we can help communities and individuals prosper and enjoy urban GI.
ID wrote the initial draft of this Editorial summarizing the Research Topic articles. EF revised the draft and contextualizing the Research Topic articles in the broader literature. All authors revised subsequent drafts and finalized the article for submission. All authors contributed to the article and approved the submitted version.
We would like to thank all the reviewers who contributed to ensuring the manuscripts in this Research Topic are of high quality and readability.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
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.
Ellwanger, J. H., Byrne, L. B., and Chies, J. A. B. (2022). Examining the paradox of urban disease ecology by linking the perspectives of Urban One Health and Ecology with Cities. Urban Ecosyst. 22, 5. doi: 10.1007/s11252-022-01260-5
Flies, E. J., Clarke, L. J., Brook, B. W., and Jones, P. (2020). Urbanisation reduces the abundance and diversity of airborne microbes - but what does that mean for our health? A systematic review. Sci. Tot. Environ. 738, 140337. doi: 10.1016/j.scitotenv.2020.140337
Flies, E. J., Mavoa, S., Zosky, G. R., Mantzioris, E., Williams, C., Eri, R., et al. (2019). Urban-associated diseases: candidate diseases, environmental risk factors, and a path forward. Environ. Int. 133, 105187. doi: 10.1016/j.envint.2019.105187
Flies, E. J., Skelly, C., Negi, S. S., Prabhakaran, P., Liu, Q., Liu, K., et al. (2017). Biodiverse green spaces: a prescription for global urban health. Front. Ecol. Environ. 15, 1630. doi: 10.1002/fee.1630
Johnston, E., Weinstein, P., Slaney, D., Flies, A. S., Fricker, S., Johnston, E., et al. (2014). Mosquito Communities with Trap Height and Urban-Rural Gradient in Adelaide, South Australia: implications for disease vector surveillance mosquito communities with trap height and urban-rural gradient in Adelaide, South Australia implications for dis. J. Vector Ecol. 39, 48–55. doi: 10.1111/j.1948-7134.2014.12069.x
Kendal, D., Egerer, M., Byrne, J., Jones, P., Marsh, P., Threlfall, C., et al. (2020). City-size bias in knowledge on the effects of urban nature on people and biodiversity. Environ. Res. Lett. 2020, abc5e4. doi: 10.1088/1748-9326/abc5e4
Kingsley, J., Egerer, M., Nuttman, S., Keniger, L., Pettitt, P., Frantzeskaki, N., et al. (2021). Urban agriculture as a nature-based solution to address socio-ecological challenges in Australian cities. Urban For. Urban Green. 60, 127059. doi: 10.1016/j.ufug.2021.127059
Marsh, P., Diekmann, L. O., Egerer, M., Lin, B., Ossola, A., and Kingsley, J. (2021). Where birds felt louder: the garden as a refuge during COVID-19. Wellbeing Space Soc. 2, 100055. doi: 10.1016/j.wss.2021.100055
Mavoa, S., Davern, M., Breed, M., and Hahs, A. (2019). Higher levels of greenness and biodiversity associate with greater subjective wellbeing in adults living in Melbourne, Australia. Health Place 57, 321–329. doi: 10.1016/j.healthplace.2019.05.006
Morelli, F., Benedetti, Y., Ibáñez-Álamo, J. D., Jokimäki, J., Mänd, R., Tryjanowski, P., et al. (2016). Evidence of evolutionary homogenization of bird communities in urban environments across Europe. Glob. Ecol. Biogeogr. 25, 1284–1293. doi: 10.1111/geb.12486
Schebella, M. F., Weber, D., Schultz, L., and Weinstein, P. (2019). The wellbeing benefits associated with perceived and measured biodiversity in Australian Urban Green Spaces. Sustainability 11, 802. doi: 10.3390/su11030802
Keywords: nature, wellbeing, greenspace, ecosystem services, sustainability, ecosystem disservice, vector-borne disease, global south
Citation: Flies EJ, Lim JNW and Douglas I (2022) Editorial: Urban ecology and human health. Front. Ecol. Evol. 10:1032022. doi: 10.3389/fevo.2022.1032022
Received: 30 August 2022; Accepted: 06 October 2022;
Published: 13 October 2022.
Edited and reviewed by: Jose Artur Chies, Federal University of Rio Grande Do Sul, Brazil
Copyright © 2022 Flies, Lim and Douglas. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Emily J. Flies, firstname.lastname@example.org