EDITORIAL article
Front. Plant Sci.
Sec. Functional Plant Ecology
This article is part of the Research TopicClimate Adaptations and Challenges of Non-native Tree Species in Forest EcosystemsView all 10 articles
Editorial: Climate Adaptations and Challenges of Non-native Tree Species in Forest Ecosystems
Provisionally accepted- 1Dendrolab IBL, Department of Silviculture and Genetics, Forest Research Institute, Sekocin Stary, Poland
- 2Department Environmental, Biological and Pharmaceutical Sciences and Technologies, University of Campania Luigi Vanvitelli, Caserta, Italy
- 3Silviculture Group, Institute of Terrestrial Ecosystems, ETH Zurich, Zurich, Switzerland
- 4Département de Sciences fondamentales, Université du Québec à Chicoutimi, Quebec, Canada
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conditions (Bouteiller et al., 2021;Klisz et al., 2025). In particular, there is a need for retrospective approaches to quantify the physiological processes of NNTs, which can be achieved through long-term monitoring on permanent plots (Hoffmann et al., 2020;Gręda et al., 2022). Common garden experiments are especially valuable, as they enable the disentanglement of inter-and intraspecific variation in phenotypic traits (Alizoti et al., 2022). These approaches should be complemented by experiments conducted under controlled conditions that simulate the climatic regimes projected for the coming decades (Medina et al., 2024). Intraspecific variation in adaptive potential, especially in species with a wide ecological range, requires consideration of populations from both the edge and the core of the distribution. This research topic includes studies addressing the acclimatisation and the adaptive potential of nonnative woody species to changing climatic conditions, covering a wide range of climate zones, various taxonomic groups, plant developmental phases, and physiological processes. This collection of scientific papers aims to encourage scientists from various disciplines to present innovative, cuttingedge research on the broadly understood climate change adaptation of NNTs. In response to the call for papers, we published nine high-quality submissions from 35 leading researchers representing nine countries across three continents (Table 1). We are pleased to present a collection of high-quality publications on the Research Topic. Introduced tree species with high invasive potential develop complex interactions with the components of the host environment, whether the atmosphere, soil, or biotope. These plants can strongly modify soil conditions, while global warming, atmospheric nitrogen deposition, and elevated CO2 concentration can modify their photosynthetic efficiency or increase nitrogen concentration in plant tissue. As part of this compilation, (Ali et al., 2024) found that Prosopis juliflora (Sw.) DC., an invasive species in the Middle East, significantly alters soil properties significantly, mainly affecting soil organic carbon and soil total nitrogen. This leads to positive plant-soil feedback (PSF) in this species, whereas negative PSF was observed in the native Prosopis cineraria (L.) Druce. This undesired interaction between an alien and invasive species and soil conditions raises concerns about whether the restoration of native P. cineraria is at risk. The strategy of adaptation to climate change, expressed in high efficiency of resource acquisition, photosynthesis rate, and consequently faster investment returns, may indicate high plasticity of invasive species. The increase in atmospheric CO2 concentration, predicted in many climate change scenarios, is likely to promote higher photosynthetic efficiency, stomatal conductance, and, as a result, increased biomass production in two invasive maple species in Europe, Acer ginnala (Maxim.) Wesm. and Acer negundo L. On the other hand, increased nitrate deposition observed in many regions, unlike ammonium fertilisation, may significantly limit photosynthetic efficiency and thus reduce the invasive potential of these two introduced maple species (Wang and Dang, 2024). Assisted colonisation of tree species outside their natural range often aims to introduce species into areas that lie within their fundamental niches but are impossible to colonise due to geographical or anthropogenic barriers (e.g., deforested areas) (Gardner and Bullock, 2025). In such situations, it is assumed that the adaptive plasticity of species will enable them to acclimatise to new conditions.Performance under new conditions depends on the adaptive strategies adopted by NNTs. In this Research Topic, (Camarero et al., 2024) found that it result in a survival-at-any-cost approach under stressful conditions, but may also lead to competing strategy with local species when resources are unlimited. With adverse growth conditions arising from severe drought episodes, Larix decidua Mill. prioritises hydraulic safety over hydraulic efficiency. This strategy, however, leads to reduced growth and, consequently, reduced competitiveness with native species. Although this strategy may facilitate tree establishment and persistence under current climatic conditions, it does not ensure long-term success as environmental conditions become increasingly unfavourable and potentially exceed speciesspecific ecological tolerance limits. However, assisted range expansion may lead to increased productivity and even effective competition with local species. (Griesbauer et al., 2025) suggested in this issue that certain species may still have unrealised niche space, which should be addressed when projecting their potential ranges under a changing climate. The increasing sensitivity to climate change observed in Central European conifers has triggered interest in NNTs as potential alternatives. Pseudotsuga menziesii (Mirbel) Franco, the most common NNT in Central Europe due to its drought tolerance, is now in focus. Resistance to adverse growing conditions applies to all stages of ontogenetic development; therefore, early-life history traits under differing resource availability conditions provide key information about the potential of seedlings to cope with unfavourable conditions and compete with native species. In this Research Topic, (Moser et al., 2025) pointed out that under reduced water availability and limited nutrients, seedlings of P. menziesii are able to establish effectively and grow vigorously due to their high phenotypic plasticity, thus successfully competing with native conifers P. abies, P. sylvestris, and A. alba Mill. In its mature phase, the deep and dense root system of P. menziesii plays a key role in its ability to endure drought. However, (Spangenberg et al., 2024) note in the same compilation that these species-specific abilities determined by the root system may be limited by soil texture. Therefore, P. menziesii may be vulnerable to soil water deficit under prolonged drought and deeper soil desiccation. On the other hand, (Niessner et al., 2024) point out that P. menziesii's specific ability to cope with drought gives it an advantage over P. abies. Under soil drought, this species is forced to reduce effective water transport in the trunk and xylem production to avoid cavitation and xylem dysfunction at critical xylem water potential. This tendency follows the soil moisture gradient, indicating that P. menziesii has already acclimatised to local conditions in Europe, as evidenced for other coniferous NNTs (Klisz et al., 2023). Assisted acclimatisation of North American tree species utilised diverse seed sources, reflecting the natural genetic variability of native populations and thus increasing the chances of successful acclimatisation to new conditions (Neophytou et al., 2020). A reliable assessment of provenancespecific variation in the adaptation of NNTs requires unified growing conditions in which populations are tested, i.e., common-garden experiments. Such experiments are remarkably rare for species introduced in Europe, and therefore constitute an exceptionally valuable source of knowledge not only about intraspecific diversity but also about their adaptive potential to climate change (Alizoti et al., 2022). Due to the long history of introducing tree species to Europe (Bucharova and Van Kleunen, 2009), European populations of NNTs have evolved under new climatic and ecological conditions over centuries, adapting to new growing conditions. Common gardens with NNTs were established to assess intraspecific variation in growth performance under local climatic conditions, yet among factors impeding tree species performance and growth are climate change-driven anomalies (e.g., severe droughts, late frosts), which are becoming more frequent (Vitasse et al., 2019). Therefore, assessing provenance-specific growth performance in the context of their drought and frost hardiness provides key insights into their adaptive potential. Writing for this issue (Kormann et al., 2024) compared native and introduced populations of Quercus rubra L. and found that populations acclimatised to central European conditions were better adapted to extreme droughts and late frosts (namely, they have greater growth and resistance to droughts and frosts) than native populations from North America. NNTs -solution to the decline in ecosystem service provision?Ongoing climate change is disrupting the provision of ecosystem services by native tree species; therefore, the role of NNTs as alternative tree species is becoming particularly important. However, itis not yet certain whether promoting NNTs in forests will reverse the decline in the provision of ecosystem services. In this issue Konic et al. (2024) highlighted that mixed stands, with native and introduced species, can improve productivity and tree species richness under Central European conditions; however, they are not an adequate solution for maintaining a sufficient level of protection against gravitation hazards in mountainous areas. Therefore, planning the use of NNTs should be tailored to the region-specific ecosystem service needs they are intended to support. Climate change will likely shift the climatic niches of NNTs, thereby causing a contraction of their climatic optima or an expansion beyond their secondary ranges, with unknown consequences (Nicolescu et al., 2026). Therefore, it is essential to determine the direction and rate of these changes under projected climate change scenarios (Puchałka et al., 2023). However, research on the ecological niche dynamics of NNTs requires complete and up-to-date data on their present distribution. The most effective approach to obtaining up-to-date distribution data appears to be combining multiple distribution data sources, such as biodiversity, forest inventory and citizen science databases (Heberling and Isaac, 2018;Jaric et al., 2020). As data on NNTs distribution become more complete, the stability of models and the reliability of forecasts will improve. Including additional ecological niche parameters, such as soil properties and stand parameters, alongside high-resolution climate data would enhance the robustness of the models (Thuiller et al., 2019). Furthermore, most current species distribution models (SDMs) for NNTs ignore the ontogenetic development of trees, so addressing both adults (reproducing trees) and juveniles (natural regeneration) would allow verification of the overlap between reproduction and regeneration niches, hence increasing the robustness of SDMs.
Keywords: acclimatisation, Climate Change, Growth, Introduced tree species, woody species
Received: 15 Dec 2025; Accepted: 10 Feb 2026.
Copyright: © 2026 Klisz, Battipaglia, Lévesque and Rossi. 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) or licensor 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: Marcin Klisz
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