Workshop report outlines global urban tree ecophysiology monitoring, highlighting climate resilience.
From 26 March to 29 March 2023, at the Georgia Center in Athens, GA, USA, a workshop on urban trees gathered 40 specialists from a wide array of disciplines, including tree physiology, forest ecology, arboriculture, urban tree ecology, urban forestry, soil science, ecohydrology, vegetation modelling, computer vision, and industrial design. With 28 attendees from four continents, and seven countries physically present, and a further 12 participants joining virtually, the workshop brought together an international team aiming to better understand the physiological functioning of urban trees. The Urban Trees Ecophysiology Network (UTEN) inaugural workshop sought to address the questions of how the urban environment impacts tree functioning and health, and how trees alter the microclimate of cities. Assessing tree health, performance, and survival in urban forests is a complex task that requires a deeper understanding of the physiological functioning of trees in relation to the biophysical, climatic, and social factors shaping urban environments. Confronting these complexities, the workshop brought together scientists and experts covering different aspects of biotic and abiotic stressors affecting tree health, performance, and mortality, as well as urban practitioners and managers, to encourage interdisciplinary thinking, align protocols, design/share new tools, and discuss the dissemination of findings to the public. Thus, the workshop aimed to uncover predictable patterns leading to rapid assessment of tree health and the influence of trees on the microclimate of the cities in contrasting urban environments across the globe amid climate change. The vulnerability of cities and their populations to further climate change may increase due to rapid urbanization, with 70% of Earth's population expected to live in cities by 2050 (Salbitano et al., 2016). Urban trees play a crucial role in creating liveable and sustainable communities in densely populated areas (Turner-Skoff & Cavender, 2019). They have been associated with lower air pollution (Nowak et al., 2006), improved mental health (Faber Taylor & Kuo, 2009), and lower temperatures (Baró et al., 2019; Wang et al., 2019). Particularly, their presence reduces the phenomenon of urban heat islands by providing shaded areas and actively cooling the air via transpiration (Fig. 1; Armson et al., 2012; Rahman et al., 2019), helping relieve financial strain on citizens and municipalities by reducing reliance on expensive air-cooling systems (Tsoka et al., 2021). They can also help to decrease costs associated with water pollution, runoff, and water treatment. Even though urban trees can sometimes be considered threats to infrastructure (Ossola et al., 2023), their benefits generally outweigh their risks for example by reducing road maintenance expenses and extending road lifespan through reduced UV radiation exposure (McPherson & Muchnick, 2005). On another scale, urban trees play a key role in ecosystems by providing food and habitat for birds, invertebrates, mammals, and epiphytes, thus helping with biodiversity conservation in cities (Fig. 1). They also serve the environment by mitigating climate change, actively capturing and sequestering carbon. In 2021, urban trees contributed, along with agricultural soils in the USA, to offsetting 13.1% of total gross emissions (EPA, 2023). However, trees, and therefore their benefits, are not equitably distributed (Nyelele & Kroll, 2020) and multiple studies found that urban canopy cover decreases along multiple social dimensions such as the poverty rate, minority population proportion, and low educational attainment (outlined in Riley & Gardiner, 2020). This has cascading implications for the positive services trees provide, with low-income areas presenting 15% less tree cover and being 1.5°C hotter than those areas with higher income (McDonald et al., 2021). This bias was even more extreme in the Northeastern USA, with low-income areas experiencing up to 30% less tree cover and up to 4.0°C warming relative to high-income areas. Recognizing these disparities, the network is seeking to move forward and design our projects with an eye toward equity. During breakout sessions, regional working groups were created to: (1) identify the species of interest; (2) characterize dominant stressor(s) in specific climate region; and (3) connect rapidly with local land managers to find out whether tree inventories existed and what data were already available for use. Workshop participants were divided into three climatically themed groups (Fig. 2): Hot and Wet, including scientists from Gainesville (Florida, USA) and Athens (Georgia, USA); Cool and Wet, including scientists from Montreal (Canada), Cambridge and Northampton (Massachusetts, USA), and Minneapolis–Saint Paul (Minnesota, USA); and Hot and Dry including scientists from Sydney (Australia), Tel-Aviv (Israel), Sacramento (California, USA), and Johannesburg (South Africa). Each group raised the global and regional most urgent questions and highlighted the specific needs of each region. Data collected from all cities will help tackle common questions concerning tree health and stress in the face of changing climate across biomes, as well as leveraging institutional knowledge to investigate research questions and hypotheses particular to the locality of each network node. Breakout groups echoed concepts from keynote talks highlighting the potential for public engagement. By leveraging public curiosity surrounding equipment installation and tissue collection in high-traffic public areas, research in urban environments can inspire both science communication and education. Keynotes by Jason Gordon (University of Georgia USA) and Kaisa Rissanen (Université de Québec à Montréal, Canada) highlighted the challenge of preserving scientific equipment from any human or animal-induced degradations in urban settings. To simultaneously maximize educational opportunities and discourage vandalism, workshop participants proposed installing informative panels in front of monitored trees, including a QR code for near-real-time web-based tree health information (Fig. 1). Subsequent discussions explored methods of protecting apparatus from tampering, including suggesting the use of decoy devices (Fig. 1). Keynote talks by Yakir Preisler (Harvard University, USA and ARO, Israel), Erez Feuer (Hebrew University, Israel) and Bill Miller (Licor Ltd, USA), showcased novel tools helpful for long-term monitoring of urban trees. Workshop participants decided that each city node would build and deploy a 'Trumpet' datalogger designed by Erez Feuer utilizing the Global System for Mobile (GSM) communication network for real-time data collection across multiple remote sites (Fig. 1). Upon database launch, the 'Trumpet' would be deployed on urban trees distributed to c. 30 trees per participating city, to measure air temperature, humidity, and trunk diameter variations using band dendrometers (EMS Brno Ltd, Brno, Czechia). Emphasizing the need for real-time monitoring across cities, representatives from each UTEN node agreed to monitor ecophysiological processes (e.g. sap flow, stem diameter, and water potential) and meteorological measurements (air temperature, humidity, solar radiation, and wind) using this design over the coming year(s). Participants of the workshop agreed on a platform for consistent measurement and quality control of data collection and communication from urban trees to UTEN. Thus, these data will be aggregated in a shared UTEN research database (Fig. 1), which UTEN intends to create and implement in close collaboration with municipalities for exchanging critical information on urban forest health (see arrows in Fig. 1). Following Dr Tim Rademacher's Université du Québec en Outaouais keynote talk that presented the concept of a 'witness tree', that is a tree on which different apparatus communicate their results to the general public through social media, workshop participants agreed to install one witness tree per city to enhance public and municipal engagement. Future actions will consist of selecting and establishing one witness tree per city and establishing a social media presence (X, Instagram, etc.) for it (Fig. 1). Establishing a global urban tree monitoring network is challenging in practice and will require several years of commitment to the project. However, workshop participants were eager to trial measurements and deploy sensors. The group's primary focus lies in establishing a foundational ecophysiological database, ready to benefit both the scientific community (addressing climate change responses, mechanisms, and biophysical interactions) and municipal decision-makers (in matters of species selection, cooling efficiency, treatments, etc.). While the group will encounter scientific and logistical obstacles, UTEN has the interdisciplinary expertise necessary to overcome a wide array of challenges. Future steps, including ongoing virtual meetings (which have been running monthly since December 2022), include establishing an annual in-person meeting to discuss the data collected and the future of the network, such as recruiting representatives from new nodes to aid the progressive expansion of the network into currently under-represented biogeographic and climatic regions. The integration of nodes in Europe (Clermont-Ferrand, France, and Helsinki, Finland), and South America (Bogotá, Colombia) is currently underway; however, participation of more sites in areas of the world that lack UTEN nodes (particularly in the southern hemisphere) is encouraged. Those interested in establishing a node of UTEN in their city should join the group on X at @Global_UTEN, and visit our website and complete the 'join us' form. Funding for the workshop was provided by the Georgia Forestry Commission, the Warnell School of Forestry and Natural Resources, and the Office of the Vice President for Research at the University of Georgia. YP planned and designed the UTEN workshop. MM wrote the first draft of the manuscript. WMH, DMJ, YP, RM, MB, GPJ, JG and AO contributed substantially to improving the first draft. All the other authors contributed equally to improving the final version of the manuscript. Data sharing is not applicable as no new data were generated.
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