Abstract
Pinus radiata has been characterized as strongly isohydric, which means that it tends to close stomata to maintain leaf water potential relatively constant under changing environmental conditions. However, under high temperatures, where leaf cooling may be necessary to prevent overheating, the ability to maintain this isohydric behaviour remains unexplored. Here, we examined the impact of increasing temperature (and associated needle-to-air vapour pressure deficit, VPDneedle) on whole plant stomatal conductance (gc), canopy transpiration (Ec), minimal conductance (gmin), and stem water potential (ψstem) in well-watered Pinus radiata plants. A decline in gc was observed as temperature increased from 22 °C to 32 °C resulting in 27% stomatal closure, followed by levelling off at further higher temperatures. However, this stomatal closure was not enough to prevent an exponential rise in Ec and pronounced declines in ψstem. gmin contributed 18% of gc at 42 °C and showed an exponential rise at temperatures higher than 42 °C. Our findings suggests that high temperatures may lead to a drop in isohydry in Pinus radiata. This shift may be crucial to avoid overheating and damage of plant tissues but at the same time leads to more negative ψstem, thereby increasing the chances of xylem embolism. The observed shift in stomatal response reveals that even in water-conservative species like Pinus radiata, high temperatures may compromise stomatal regulation of water potential.
Keywords: Evaporative cooling, heat stress, isohydry, minimal conductance, stem water potential, stomatal conductance
High temperatures result in large transpiration rates due to suppressed stomatal control, leading to large declines in stem water potential in Pinus radiata, a strongly isohydric species.
Introduction
Climate change is one of the biggest challenges, imposing far-reaching effects on the ecological system. Based on World Meteorological Organization (2024) reports, the global temperature record was broken in the year 2023, with the highest rise of 1.45±0.12 °C above the long term mean since the pre-industrial era (Dunstone et al., 2024). In this context, it is surprising that among the many studies documenting the aftermath of drought (Sanchez-Martinez et al., 2023), or the combined impact of drought–heat stress (Zhao et al., 2013; Birami et al., 2020; Gong and Hao, 2023; Gauthey et al., 2024; Hankin et al., 2024), very little is known about the distinct consequences of heat waves on plant survival (Allen et al., 2015; Margalef-Marrase et al., 2020; Breshears et al., 2021; Hartmann et al., 2022; Klein et al., 2022). As temperature continues to rise under climate change, characterizing the effects of heat on tree function is critical for predicting future ecosystem dynamics.
Most studies of heat effects on plant function have focussed on the photosynthetic response (Teskey et al., 2015; Guha et al., 2018; Bennett et al., 2024) with a very few exploring the stomatal response especially in terms of water potential regulation. Water potential is highly dynamic in plants and is largely influenced by transpiration rate, and hence vapour pressure deficit (VPD). Plants close stomata at high VPD, stabilizing water loss and thus attenuating the decline in water potential that could lead to xylem cavitation and damage the plant (Choat et al., 2018). Changes in VPD can be caused by air moisture content and temperature. Without a change in water content of the air, rising temperatures cause VPD to increase. However, the influence of high VPD driven by elevated temperature on stomatal regulation and its consequences for water potential regulation are still not well characterized (Moore et al., 2021). The few existing studies have reported contradictory findings, with some showing stronger stomatal regulation under high temperature prioritizing hydraulic safety (Zhang et al., 2022; Gong et al., 2023), while others show reduced control to enable leaf cooling (Urban et al., 2017; Drake et al., 2018; Chen et al., 2019). This means that the plants face a trade-off between water conservation and evaporative cooling required under high temperatures (Chaves et al., 2016; Sadok et al., 2021). Plants are often classified as isohydric (tight regulation of leaf water potential via stomatal closure) or anisohydric (looser regulation, allowing leaf water potential to decline as stomata stay open) (Tardieu and Simonneau, 1998; Klein, 2014), and these modes of regulation are often assumed to remain consistent within a species across varying environmental conditions. Yet this assumption remains largely untested under increasing temperature, where the need to maintain transpirational cooling to avoid overheating may shift stomatal behaviour within the same species. A strong stomatal closure is observed as a response mechanism to increasing VPD in isohydric species like Pinus radiata, but there is still a potential of losing water through partially closed stomata (Brodribb et al., 2014) or via the cuticle (Kane et al., 2020). Cuticular conductance can vary with temperature and between different species (Bueno et al., 2019; Slot et al., 2021; Garen and Michaletz, 2025). Studies have reported moderate rise in cuticular permeability at low temperatures and substantial increase at temperatures higher than 35 °C (Riederer, 2006; Slot et al., 2021; Garen and Michaletz, 2025) making it a key factor to consider while evaluating plant response under heat waves.
Pines are evergreen conifers and therefore more likely to invest resources in strategies like evaporative cooling that maintain leaf integrity. However, given the characterization of Pinus radiata as strongly isohydric (Brodribb and McAdam, 2013), the sustainability of this strategy at higher temperatures remains an important question. Most of the studies reporting isohydry in Pinus (Rodríguez-Gamir et al., 2019; Sharma et al., 2025) have been performed under a narrow range of temperature leaving uncertainty about how isohydric plants behave under heat stress when water is abundant (Bucholz et al., 2020). So, the question remains: will an isohydric species exposed to high temperature exhibit a decline in the stomatal conductance to maintain isohydry, or maintain isohydry and lose water through the cuticle, or sacrifice isohydry by keeping stomata open to maintain leaf temperature? Here we examine whether Pinus radiata, a strongly isohydric species, maintains its isohydric behaviour under elevated temperatures, which can give us a more accurate understanding of survival of this species in extremely hot environments.
Materials and methods
Plant material and growing conditions
The study was carried out on 19-month-old Pinus radiata plants cultivated from an open pollinated seedlot (‘Seed Energy Blackwood 8’) procured from Woodlea Nursery (Springfield, Tasmania). The procured seedlings were potted in Lannen 81 trays using a potting mix comprising pine bark, controlled-release fertilizer, micronutrients and MycoApply mycorrhizal inoculation. After 2 months, seedlings were re-potted in 5 litre pots in potting mix comprising 7:4 parts of fine pine bark and coarse-washed river sand along with controlled-release fertilizer. All the plants were grown under unfiltered natural light in a controlled glasshouse cell at 25/15 °C day/night temperature and 40/80% day/night relative humidity (RH) and were watered daily to the maximum field capacity during the entire growing period.
Experimental set-up
Five healthy plants of a similar age (19 months) and size (77.9±6.1 cm) were chosen for the experiment (Supplementary Fig. S1A–C). The plants were placed in a well-ventilated customized growth chamber (with internal dimensions of 3.4×2.4×2.3 m) 2 d prior to the experiment to give them sufficient time to acclimate to the temperature and new light conditions. During these 2 d, the growth chamber was kept at 20±1 °C temperature with 10 h of light of intensity 800 μmol m−2 s−1 at the plant canopy level using an air conditioner (5KW Daikin Inverter Split System L-Series FTXS50LVMA, Osaka, Japan) and a LED lighting fixture (Lumatek, ZEUS 1000W Pro) with coverage area of 1.5×1.5 m. This photoperiod comprising 10 h day (from 07.00 h until 17.00 h) and 14 h night was followed throughout the experiment while achieving different target temperatures. A temperature/humidity probe (HMP45AC; Vaisala Inc., Helsinki, Finland) was placed at the canopy level of plants to record relative humidity and air temperature at every 1 min interval using a datalogger (CR850, Campbell Scientific, Logan, UT, USA). A soil thermocouple was employed to measure soil temperature and soil–stem hydraulic conductivity measurements (Ks–s) were corrected for viscosity. Plants were exposed to five different target temperatures (22, 27, 32, 37, and 42 °C). Each of these temperature treatments were given on consecutive days starting in the morning raising temperatures from 20 °C to required temperature treatment over a period of 2–3 h. The target temperatures were achieved using an air conditioner (5KW Daikin Inverter Split System L-Series FTXS50LVMA), a heater, and a small table fan (used to circulate air). Each target temperature was maintained for at least 1–2 h until stem water potential (ψstem) and canopy transpiration (Ec) achieved a steady-stable state. Relative humidity was kept almost constant in the range of 30–40% at each target temperature. The plants were watered every day to full capacity throughout the experiment making sure that soil was not limiting even at higher temperatures. Soil surface was covered with aluminium foil to prevent evaporation from soil.
For each temperature treatment, ψstem and Ec were monitored simultaneously and continuously on each Pinus radiata plant. ψstem was monitored using needle width variation as a proxy, measured continuously every 5 min with optical dendrometers (Cavicam Co, Hobart, Tasmania, Australia) that were attached to mature needle(s) (Bourbia et al., 2021; Bourbia and Brodribb, 2023; Sharma et al., 2025). The needle width obtained was calibrated against the Ψstem measured at every target temperature using a Scholander chamber (PMS Instrument Co., Albany, OR, USA) (Supplementary Fig. S2A). The Scholander chamber Ψstem used for calibration was measured on mature non-transpiring needles covered with damp tissue paper and aluminium foil for at least an hour before measurements to prevent transpiration and allow xylem–leaf water potential equilibrium. The relationship between needle width and ψstem was always linear across all replicates (Supplementary Fig. S2A). Every morning, a measurement was taken before turning on lights (pre-dawn water potential) followed by another measurement at target temperature. The Ψstem measurement at each temperature was taken when needle width reached steady state. Steady state pertains to a condition when both Ec and the corresponding Ψstem remain steady for at least 40 min (less than 5% change) under constant target temperature, with insignificant impact from plant capacitance.
E c of each individual plant was monitored continuously at 5 min intervals using computer-interfaced balances (model PG5002-S, Mettler Toledo) with ±0.01 g accuracy. Each pot was watered to full capacity, and excess water was drained before placing on the balances. Aluminium foil was used to cover the soil surface to prevent evaporation from soil. Ec from each plant was normalized by the projected total leaf area (m2). Given that there was little needle length variation (13% coefficient of variation; averaged over all plants), the total canopy area was measured using total needle count and random sampling of five needles for average leaf area. The needles were scanned using a flatbed scanner and area was calculated using ImageJ (NIH, Bethesda, MD, USA). Note that the same five plants were assessed at each temperature treatment.
Needle temperature was measured using a portable photosynthesis system, LI-6800 (Li-Cor, Lincoln, NE, USA). During measurements, the conditions in the cuvette of the LI-6800 were very carefully aligned to match the ambient conditions of light, temperature, and VPD in the growth chamber. Given the very insignificant difference in the measured needle temperature and air temperature (0.2 °C; averaged over all the temperature treatments; Supplementary Fig. S2B), needle temperature was taken as equal to the air temperature.
The Buck equation (Buck, 1981) was then used to calculate needle-to-air vapour pressure deficit (VPDneedle) as follows:
| (1) |
where RH is the relative humidity (in %) and T is needle temperature (in °C).
Water potential gradient (ΔΨ) was calculated using difference of soil water potential (Ψsoil; in MPa) and stem water potential (Ψstem; in MPa), inferred from needle width variations using optical dendrometers. Ψsoil was assumed to be equal to the predawn water potential as the plants were well watered and under maximum humidity.
Whole canopy diffusive conductance
E c and VPDneedle measured at each target temperature were used to calculate canopy diffusive conductance (gc) in each replicate as follows:
| (2) |
where Ec (mmol m−2 s−1) refers to the normalized steady state gravimetrically measured canopy transpiration at each target temperature in individual replicate, Patm is atmospheric pressure i.e. 101.3 kPa.
Soil–stem hydraulic conductivity dynamics measurements
E c measured at each steady state temperature (and VPDneedle) and corresponding daytime ψstem in each replicate were used to calculate soil-to-stem hydraulic conductance (Ks–s, mmol m−2 s−1 MPa−1) employing Darcy’s law:
| (3) |
where Ψsoil is the soil water potential which was assumed to be equal to the predawn water potential as the soil was kept well hydrated throughout the day.
A soil thermocouple was placed at almost 10 cm depth to measure soil temperature. Across all treatment temperatures, which ranged from 22 °C to 42 °C, soil temperature for all the replicates only varied between 21 °C and 29 °C (Supplementary Fig. S2C). Therefore, Ks–s measurements were normalized to the viscosity of water at 20 °C (Korson et al., 1969), shown in Supplementary Fig. S3A.
Minimal needle diffusive conductance at different temperatures
Minimal needle diffusive conductance (gmin) was measured at seven different temperatures as follows: 25, 32, 37, 40, 42, 44 and 47 °C. For the measurements, five Pinus radiata plants used as replicates in the main experiment were watered to maximum capacity and kept in the dark overnight to ensure full stomatal closure. The next morning, three to four fully mature hydrated needles from different fascicles were taken before turning on lights, and turgid weight was measured using a precision balance followed by scanning and measuring area using a flatbed scanner and ImageJ. These were then immediately tied in a group of three to four and cut ends were sealed using paraffin wax and labelled as per replicates. A dehydrating oven (Thermoline Scientific, NSW, Australia) was set at each target temperature 30 min before starting the treatment. Air temperature and relative humidity inside the dehydrating oven were monitored every minute using a temperature/humidity probe (HMP45AC; Vaisala Inc.) and data were recorded on a logger (CR850, Campbell Scientific). The needle groups were then hung in the dehydrating oven on a string with the help of clothes pegs. The rate of water loss was determined using difference in the weights measured at regular intervals on a precision balance. The time interval between each measurement was between 2 min (at higher temperatures) and 1 h (at lower temperatures) depending upon the target temperature. The time interval between the measurements at high temperatures was significantly reduced to avoid any damage due to excessive dehydration. VPD was calculated using temperature and relative humidity measured at each target treatment (Equation 1). Relative needle water content (RWC; %) was calculated using (Barrs and Weatherley, 1962):
| (4) |
g min (mmol m−2 s−1) was then calculated using slope of the linear part of the needle mass–time relationship, measured needle area (m2) and VPD (mol mol−1) in each replicate (Sack and Scoffoni, 2010; Slot et al., 2021; Wang et al., 2024). This linear part was selected in relative needle water content range of 80–60% where stomata were closed and water loss occurred primarily through the cuticle, allowing accurate calculation of gmᵢn.
g min was calculated as:
| (5) |
Here, dw/dt is the linear slope of needle mass change over time (g s−1) within the selected RWC interval, Aneedle is the total needle area (m2), VPD is the vapour mole fraction deficit (mol mol−1), 18 is the gram molar mass of water (g mol−1) and 1000 converts mol to mmol.
Measurement of maximum quantum yield of photosystem II
Maximum quantum yield of photosystem II (Fv/Fm) was used as an indicator of damage to photosystem II under increasing temperature from 25 °C to 52 °C. The Fv/Fm ratio was evaluated by measuring chlorophyll fluorescence using a portable leaf clip MINI-PAM-II Photosynthesis Yield Analyzer (Heinz Walz GmbH, Effeltrich Germany) (Supplementary Fig. S3B). A fascicle with three to four needles sampled from each of the five replicates was kept in dark in the dehydrating oven (Thermoline Scientific) under each temperature treatment for approximately 1 h and an average from three measurements taken on same needles was used for calculations.
Measurement of morphological traits
Morphological traits like plant height (cm), total leaf area (cm2) and leaf mass per area (LMA; mg cm−2) were measured from all the replicates after completing the experiment. Five randomly sampled needles were scanned and area was measured using a flatbed scanner and ImageJ and oven-dried (Thermoline Scientific) at 70 °C to procure dry weight. LMA was calculated as a ratio of dry weight of five sampled needles to the total surface area of needles. Total needle count and average needle area from each plant were used to calculate the total leaf area (cm2).
Statistical analysis
The study analysis was done using RStudio 2024.12.0+467. Differences in ψstem, Ec, gc, and Ks–s at different target temperature treatments were assessed using analysis of variance (ANOVA). A post-hoc Tukey multiple comparison of means test was employed in cases of significant differences (when P<0.05). Results are presented as mean values ±SD.
Various models like linear, quadratic, exponential, and cubic were deployed to study the relationship of average gc and gmin (calculated over for all replicates) with temperature over the entire temperature treatment range (22 °C to 42 °C). A cubic polynomial model was found to be the best fit (the highest R2 and lowest Akaike information criterion values) for evaluating the relationship between gc and temperature while an exponential model best described the relationship between gmin and temperature.
We modelled stomatal responses to determine the degree of stomatal closure required to maintain constant ψstem under rising VPD driven by increasing temperature, thereby maintaining near-isohydric behaviour, and compared this to the observed stomatal closure. We quantified how much gc would need to be reduced to maintain a constant ψstem (hence a constant soil-to-stem water potential gradient, Δψ) set to the value observed at low temperature (22 °C) in each replicate using the following equation:
| (6) |
Here we used the average Ks–s (normalized to the viscosity of water at 20 °C) observed across all the temperature treatments, and Δψ22°C is the difference between Ψsoil (soil water potential, which was assumed to be equal to the predawn water potential as the soil was kept well hydrated throughout the day) and Ψstem at 22 °C.
Results
Temperature-induced decline in stem water potential
Each Pinus radiata plant was subjected to five temperature treatments from 22 °C to 42 °C and corresponding VPDneedle ranging from 1.4 kPa to 6.1 kPa (Fig. 1). During the temperature treatments, the mean ψstem from all the replicates declined from −0.4±0.1 MPa at 22 °C to −0.8±0.0 MPa at 42 °C (Fig. 2A). We observed a consistent decline in mean ψstem over the entire range of temperature treatments.
Fig. 1.

Series of temperature (°C) and corresponding needle-to-air vapour pressure deficit (VPDneedle) (kPa) employed as five different treatments in the study. Different colours represent the replicates used.
Fig. 2.

Response of mean stem water potential (ψstem, MPa) (A), mean canopy transpiration (Ec) (B), and mean canopy diffusive conductance (gc, mmol m−2s−1), modelled canopy diffusive conductance (gmodel, mmol m−2s−1), and minimal conductance (gmin, mmol m−2s−1) (C) to different temperature treatments in all Pinus radiata replicates (represented by different colours). The black circle represents the mean of ψstem, Ec, and gc and error bars show the standard deviation among all the replicates at each temperature treatment. In (B), the black solid line represents the exponential fit of response of Ec to different temperature treatments. In (C), the solid black line represents the cubic polynomial fit of the response of gc to all temperature treatments and the blue solid line represents gmodel.
Response of transpiration and canopy diffusive conductance to different temperature treatments
We observed an exponential rise in transpiration (Ec) with increase in temperature (Fig. 2B). The mean Ec ranged from 2.3±0.4 mmol m−2 s−1 at 22 °C to 4.8±0.8 mmol m−2 s−1 at 42 °C.
Stomatal response at all the temperature treatments was found to be the same among all the well-watered replicates (ANOVA, P > 0.05) (Fig. 2C). We observed that the overall canopy diffusive conductance (gc) declined by 27% between 22 °C and 32 °C followed by levelling off at higher temperature treatments. However, this was insufficient to prevent the continuous decline in ψstem with increasing temperatures. Based on the gmodel (calculated using Equation 6), 70% reduction in gc is required to maintain a constant ψstem as the temperature increases between 22 °C and 42 °C (Fig. 2C). An exponential rise in gmin was observed with increasing temperature (R2=0.85), increasing from 1% at 22 °C to 18.2% of gc at 42 °C (Figs 2C, 3).
Fig. 3.

Increasing minimal conductance (gmin, mmol m−2s−1) with rising temperature treatments in Pinus radiata replicates. The error bars represent standard deviation over all the replicates at each temperature treatment. The solid line represents the exponential fit over the response of gmin to all temperature treatments.
Discussion
Pinus radiata is one of the most widely planted softwood conifer species in the southern hemisphere, valued for its fast growth and high-quality wood production. Due to increasing numbers of hot and dry days, large scale mortality has been observed in Pinus radiata growing areas of Australia, New Zealand, Africa, Chile, and USA (Carnegie et al., 2022). Therefore, there is an increasing need to evaluate the stomatal response under high temperatures. Pinus radiata has been characterized as strongly isohydric (Martínez-Vilalta et al., 2004), which means it maintains its daytime minimum leaf water potential relatively constant under increasing VPD or drying soil conditions due to stomatal closure (Brodribb and McAdam, 2013; Rodríguez-Gamir et al., 2019; Sharma et al., 2025). But the question that remains unanswered is whether this isohydric behaviour is maintained under conditions of high temperature where demands to maintain leaf cooling might require non-isohydric behaviour. To answer this question, we examined the impact of increasing temperature (and associated VPDneedle) on stem water potential and stomatal conductance of Pinus radiata saplings. We found that stomatal conductance was not sufficiently regulated to maintain isohydry under increasing temperature, resulting in constantly rising transpiration and declining ψstem.
The observed stomatal closure between 22 °C and 32 °C is consistent with the high sensitivity observed in Pinus radiata in previous studies (Weston and Bauerle, 2007; Brodribb and McAdam, 2013; Lahr et al., 2015; Sharma et al., 2025) and is also consistent with our study results where stomata closed by 27% as temperature increased from 22 °C to 32 °C (Fig. 2C). This stomatal control is typically observed under increasing temperature and VPD to maintain homeostasis (Weston and Bauerle, 2007; Lahr et al., 2015; Sharma et al., 2025). However, further increase in temperature to 42 °C did not lead to any additional decline in gc, resulting in a further decline in ψstem. Our results are consistent with the study reporting a shift in isohydric behaviour in young apple trees in response to increasing drought stress (Zhao et al., 2023). Stomatal behaviour has often been interpreted through a simplified isohydric-anisohydric framework (Tardieu and Simonneau, 1998), which is often assumed to be constant within a species across conditions. However, our data suggests that isohydric and anisohydric behaviour may not be fixed, enabling species to shift water use regulation under specific conditions, such as high temperature (Guo et al., 2020).
A plausible explanation for the breakdown of isohydric regulation under high temperature may reflect a difference between long-term drought-induced stomatal closure and short-term stomatal responses to acute heat stress. Previous studies showing extreme isohydry in Pinus radiata have been performed under slow and long-term exposure to drought, where plants had enough time for abscisic acid (ABA) synthesis to reach levels sufficient to induce strong stomatal closure (Brodribb and McAdam, 2013; Rodríguez-Gamir et al., 2019). By contrast, in our experiment, plants were exposed to high temperature for short time period, which may not have allowed sufficient time for ABA to accumulate to levels capable of inducing near-complete stomatal closure (Mitchell et al., 2017; Rizzuto et al., 2024). These short-term diurnal temperature variations are very common under field settings where the temperature can ramp up very quickly on hot days during a heatwave. Under these conditions, stomatal behaviour may be governed more by passive hydraulic responses to declining water potential than by strong hormonal control.
Some studies have reported that stomata remain partially open at high temperatures (Weston and Bauerle, 2007), which helps to mitigate overheating of the leaves via evaporative cooling especially under well-hydrated conditions (Aparecido et al., 2020; Gommers, 2020). But this comes at the cost of declining water potential in the plant. The decline in ψstem shows the inability of Pinus radiata to hold its water potential from dropping at high temperatures, which could eventually lead to xylem embolism (Tyree and Sperry, 1989). The ψstem in our study declined from −0.4±0.1 MPa at 22 °C to −0.8±0.1 MPa at 42 °C (Fig. 2A); however, the xylem embolism observed in Pinus radiata roots and stem parts does not start until water potential reaches around −2 MPa (Harrison Day et al., 2024). This implies that there is still some space for Pinus radiata to keep its stomata open at the expense of declining water potential before it reaches the point of xylem embolism.
After stomatal closure, plants may use water loss via cuticle and incompletely closed or leaky stomata, together accounting for increased minimal conductance (gmin) (Machado et al., 2021; Slot et al., 2021; Garen and Michaletz, 2025). Minimal conductance can vary with temperature and between different species (Duursma et al., 2019). Our results are consistent with studies reporting a steep rise in minimal conductance at high temperatures (Bueno et al., 2019; Billon et al., 2020; Wang et al., 2024), which makes it a key factor to consider when evaluating plant response under heat waves (Fig. 3). The rising evaporation rates and water loss via cuticle and leaky stomata might have prevented tissue damage at high temperature by buffering the high needle temperatures (Rehschuh and Ruehr, 2022).
Maintaining high transpiration and non-cavitating ψstem at high temperatures requires a high and constant hydraulic supply. In this species, Ks–s remained stable despite increasing air temperature (Supplementary Fig. S3A). This is in agreement with previous studies reporting constant soil–stem hydraulic conductance under well-watered conditions in different species (Hailey et al., 1973; Dubé et al., 1975; Bourbia et al., 2022). A small decline was observed in Ks–s value (without accounting for viscosity effect) at 42 °C but was not sufficient to induce further stomatal closure or excessive decline in ψstem, as Ks–s remained high (6.8±1.3 mmol m−2 s−1 MPa−1; Supplementary Fig. S3A). The constancy of Ks–s as gc declines by 36% with increasing temperature also confirms that in this species, stomatal closure is not driven by any decline in Ks–s when soil is wet (Bourbia and Brodribb, 2024).
Conclusion
Our study suggests that high temperatures are capable of shifting the isohydric behaviour in Pinus radiata. This shift may be associated with lack of rapid ABA biosynthesis under short-term temperature stress, thereby avoiding overheating of plant tissue but at the cost of declining stem water potentials to levels that could increase the risk of embolism if not properly regulated. The observed shift in isohydric response provides an opportunity to understand that even species like Pinus radiata, which are characterized as strongly isohydric, might lose their stomatal control at higher negative water potentials. This also implies that high temperatures may accelerate mortality in all other less isohydric species, especially under soil drought conditions. Therefore, there is a need to re-evaluate the characterized response at temperatures corresponding to heatwaves to predict the repercussions of future heatwaves on the survival and growth in different plant species.
Supplementary Material
Contributor Information
Kritika Sharma, School of Natural Sciences, University of Tasmania, Sandy Bay, Hobart, Tasmania 7001, Australia.
Ibrahim Bourbia, School of Natural Sciences, University of Tasmania, Sandy Bay, Hobart, Tasmania 7001, Australia.
Faustino Rubio Pérez, Departamento de Sistemas y Recursos Naturales, ETSI Montes, Forestal y del Medio Natural Universidad Politécnica de Madrid, Madrid 28040, Spain.
Timothy Brodribb, School of Natural Sciences, University of Tasmania, Sandy Bay, Hobart, Tasmania 7001, Australia.
Tracy Lawson, University of Illinois Urbana-Champaign, USA.
Supplementary data
The following supplementary data are available at JXB online.
Fig. S1. Morphological measurements of Pinus radiata plants.
Fig. S2. Variations in stem water potential (ψstem), average needle temperature and soil temperature across temperature treatments.
Fig. S3. Response of mean soil-to-stem hydraulic conductance (Ks–s, mmol m−2 s−1 MPa−1), mean Ks–s normalized to 20°C and maximum quantum yield of photosystem II (Fv/Fm ratio) across temperature treatments.
Author contributions
TB and KS: conceptualization; TB, KS, IB and FRP: design of the experiment; KS and FRP: data collection; KS: data analysis; KS: writing, with revisions by TB and IB.
Funding
This research was supported by the NZ Ministry of Business, Innovation and Employment (MBIE) programme entitled ‘Seeing the forest for the trees: transforming tree phenotyping for future forests’ (programme grant number C04X2101). We thank the ARC Centre of Excellence for Plant Success in Nature and Agriculture.
Data availability
The primary data supporting this study were not made publicly available at the time of publication. The data that support the findings of this study are available from the corresponding author upon request.
References
- Allen CD, Breshears DD, McDowell NG. 2015. On underestimation of global vulnerability to tree mortality and forest die-off from hotter drought in the Anthropocene. Ecosphere 6, 1–55. [Google Scholar]
- Aparecido LM, Woo S, Suazo C, Hultine KR, Blonder B. 2020. High water use in desert plants exposed to extreme heat. Ecology Letters 23, 1189–1200. [DOI] [PubMed] [Google Scholar]
- Barrs H, Weatherley P. 1962. A re-examination of the relative turgidity technique for estimating water deficits in leaves. Australian Journal of Biological Sciences 15, 413–428. [Google Scholar]
- Bennett AC, Knauer J, Bennett LT, Haverd V, Arndt SK. 2024. Variable influence of photosynthetic thermal acclimation on future carbon uptake in Australian wooded ecosystems under climate change. Global Change Biology 30, e17021. [DOI] [PubMed] [Google Scholar]
- Billon LM, Blackman CJ, Cochard H, Badel E, Hitmi A, Cartailler J, Souchal R, Torres-Ruiz JM. 2020. The DroughtBox: a new tool for phenotyping residual branch conductance and its temperature dependence during drought. Plant, Cell & Environment 43, 1584–1594. [DOI] [PubMed] [Google Scholar]
- Birami B, Nägele T, Gattmann M, Preisler Y, Gast A, Arneth A, Ruehr NK. 2020. Hot drought reduces the effects of elevated CO2 on tree water-use efficiency and carbon metabolism. New Phytologist 226, 1607–1621. [DOI] [PubMed] [Google Scholar]
- Bourbia I, Pritzkow C, Brodribb TJ. 2021. Herb and conifer roots show similar high sensitivity to water deficit. Plant Physiology 186, 1908–1918. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Bourbia I, Lucani C, Brodribb TJ. 2022. Constant hydraulic supply enables optical monitoring of transpiration in a grass, a herb, and a conifer. Journal of Experimental Botany 73, 5625–5633. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Bourbia I, Brodribb TJ. 2023. A new technique for monitoring plant transpiration under field conditions using leaf optical dendrometry. Agricultural and Forest Meteorology 331, 109328. [Google Scholar]
- Bourbia I, Brodribb TJ. 2024. Stomatal response to VPD is not triggered by changes in soil–leaf hydraulic conductance in Arabidopsis or Callitris. New Phytologist 242, 444–452. [DOI] [PubMed] [Google Scholar]
- Breshears DD, Fontaine JB, Ruthrof KX, Field JP, Feng X, Burger JR, Law DJ, Kala J, Hardy GESJ. 2021. Underappreciated plant vulnerabilities to heat waves. New Phytologist 231, 32–39. [DOI] [PubMed] [Google Scholar]
- Brodribb TJ, McAdam SA. 2013. Abscisic acid mediates a divergence in the drought response of two conifers. Plant Physiology 162, 1370–1377. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Brodribb TJ, McAdam SA, Jordan GJ, Martins SC. 2014. Conifer species adapt to low-rainfall climates by following one of two divergent pathways. Proceedings of the National Academy of Sciences, USA 111, 14489–14493. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Bucholz ER, Waring KM, Kolb TE, Swenson JK, Whipple AV. 2020. Water relations and drought response of Pinus strobiformis. Canadian Journal of Forest Research 50, 905–916. [Google Scholar]
- Buck AL. 1981. New equations for computing vapor pressure and enhancement factor. Journal of Applied Meteorology 20, 1527–1532. [Google Scholar]
- Bueno A, Alfarhan A, Arand K, Burghardt M, Deininger A-C, Hedrich R, Leide J, Seufert P, Staiger S, Riederer M. 2019. Effects of temperature on the cuticular transpiration barrier of two desert plants with water-spender and water-saver strategies. Journal of Experimental Botany 70, 1613–1625. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Carnegie A, Kathuria A, Nagel M, Mitchell P, Stone C, Sutton M. 2022. Current and future risks of drought-induced mortality in Pinus radiata plantations in New South Wales, Australia. Australian Forestry 85, 161–177. [Google Scholar]
- Chaves M, Costa JM, Zarrouk O, Pinheiro C, Lopes C, Pereira JS. 2016. Controlling stomatal aperture in semi-arid regions—the dilemma of saving water or being cool? Plant Science 251, 54–64. [DOI] [PubMed] [Google Scholar]
- Chen X, Zhao P, Hu Y, Ouyang L, Zhu L, Ni G. 2019. Canopy transpiration and its cooling effect of three urban tree species in a subtropical city—Guangzhou, China. Urban Forestry & Urban Greening 43, 126368. [Google Scholar]
- Choat B, Brodribb TJ, Brodersen CR, Duursma RA, López R, Medlyn BE. 2018. Triggers of tree mortality under drought. Nature 558, 531–539. [DOI] [PubMed] [Google Scholar]
- Drake JE, Tjoelker MG, Vårhammar A, Medlyn BE, Reich PB, Leigh A, Pfautsch S, Blackman CJ, López R, Aspinwall MJ. 2018. Trees tolerate an extreme heatwave via sustained transpirational cooling and increased leaf thermal tolerance. Global Change Biology 24, 2390–2402. [DOI] [PubMed] [Google Scholar]
- Dubé P, Stevenson K, Thurtell G, Neumann H. 1975. Steady state resistance to water flow in corn under well watered conditions. Canadian Journal of Plant Science 55, 941–948. [Google Scholar]
- Dunstone NJ, Smith DM, Atkinson C, Colman A, Folland C, Hermanson L, Ineson S, Killick R, Morice C, Rayner N. 2024. Will 2024 be the first year that global temperature exceeds 1.5 °C? Atmospheric Science Letters 25, e1254. [Google Scholar]
- Duursma RA, Blackman CJ, Lopéz R, Martin-StPaul NK, Cochard H, Medlyn BE. 2019. On the minimum leaf conductance: its role in models of plant water use, and ecological and environmental controls. New Phytologist 221, 693–705. [DOI] [PubMed] [Google Scholar]
- Garen JC, Michaletz ST. 2025. Temperature governs the relative contributions of cuticle and stomata to leaf minimum conductance. New Phytologist 245, 1911–1923. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Gauthey A, Kahmen A, Limousin JM, Vilagrosa A, Didion-Gency M, Mas E, Milano A, Tunas A, Grossiord C. 2024. High heat tolerance, evaporative cooling, and stomatal decoupling regulate canopy temperature and their safety margins in three European oak species. Global Change Biology 30, e17439. [DOI] [PubMed] [Google Scholar]
- Gommers C. 2020. Keep cool and open up: temperature-induced stomatal opening. Plant Physiology 182, 1188–1189. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Gong X-W, Hao G-Y. 2023. The synergistic effect of hydraulic and thermal impairments accounts for the severe crown damage in Fraxinus mandshurica seedlings following the combined drought-heatwave stress. The Science of the Total Environment 856, 159017. [DOI] [PubMed] [Google Scholar]
- Gong X-W, Leigh A, Guo J-J, Fang L-D, Hao G-Y. 2023. Sand dune shrub species prioritize hydraulic integrity over transpirational cooling during an experimental heatwave. Agricultural and Forest Meteorology 336, 109483. [Google Scholar]
- Guha A, Han J, Cummings C, McLennan DA, Warren JM. 2018. Differential ecophysiological responses and resilience to heat wave events in four co-occurring temperate tree species. Environmental Research Letters 13, 065008. [Google Scholar]
- Guo JS, Hultine KR, Koch GW, Kropp H, Ogle K. 2020. Temporal shifts in iso/anisohydry revealed from daily observations of plant water potential in a dominant desert shrub. New Phytologist 225, 713–726. [DOI] [PubMed] [Google Scholar]
- Hailey JL, Hiler EA, Jordan WR, Van Bavel C. 1973. Resistance to water flow in Vigna sinensis L.(Endl.) at high rates of transpiration 1. Crop Science 13, 264–267. [Google Scholar]
- Hankin LE, Barrios-Masias FH, Urza AK, Bisbing SM. 2024. Lethal combination for seedlings: extreme heat drives mortality of drought-exposed high-elevation pine seedlings. Annals of Botany 135, mcae064. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Harrison Day BL, Brodersen CR, Brodribb TJ. 2024. Weak link or strong foundation? Vulnerability of fine root networks and stems to xylem embolism. New Phytologist 244, 1288–1302. [DOI] [PubMed] [Google Scholar]
- Hartmann H, Bastos A, Das AJ, Esquivel-Muelbert A, Hammond WM, Martínez-Vilalta J, McDowell NG, Powers JS, Pugh TA, Ruthrof KX. 2022. Climate change risks to global forest health: emergence of unexpected events of elevated tree mortality worldwide. Annual Review of Plant Biology 73, 673–702. [DOI] [PubMed] [Google Scholar]
- Kane CN, Jordan GJ, Jansen S, McAdam SA. 2020. A permeable cuticle, not open stomata, is the primary source of water loss from expanding leaves. Frontiers in Plant Science 11, 774. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Klein T. 2014. The variability of stomatal sensitivity to leaf water potential across tree species indicates a continuum between isohydric and anisohydric behaviours. Functional Ecology 28, 1313–1320. [Google Scholar]
- Klein T, Torres-Ruiz JM, Albers JJ. 2022. Conifer desiccation in the 2021 NW heatwave confirms the role of hydraulic damage. Tree Physiology 42, 722–726. [DOI] [PubMed] [Google Scholar]
- Korson L, Drost-Hansen W, Millero FJ. 1969. Viscosity of water at various temperatures. The Journal of Physical Chemistry 73, 34–39. [Google Scholar]
- Lahr EC, Schade GW, Crossett CC, Watson MR. 2015. Photosynthesis and isoprene emission from trees along an urban–rural gradient in Texas. Global Change Biology 21, 4221–4236. [DOI] [PubMed] [Google Scholar]
- Machado R, Loram-Lourenço L, Farnese FS, Alves RDFB, de Sousa LF, Silva FG, Filho SCV, Torres-Ruiz JM, Cochard H, Menezes-Silva PE. 2021. Where do leaf water leaks come from? Trade-offs underlying the variability in minimum conductance across tropical savanna species with contrasting growth strategies. New Phytologist 229, 1415–1430. [DOI] [PubMed] [Google Scholar]
- Margalef-Marrase J, Pérez-Navarro MÁ, Lloret F. 2020. Relationship between heatwave-induced forest die-off and climatic suitability in multiple tree species. Global Change Biology 26, 3134–3146. [DOI] [PubMed] [Google Scholar]
- Martínez-Vilalta J, Sala A, Piñol J. 2004. The hydraulic architecture of Pinaceae—a review. Plant Ecology 171, 3–13. [Google Scholar]
- Mitchell PJ, McAdam SA, Pinkard EA, Brodribb TJ. 2017. Significant contribution from foliage-derived ABA in regulating gas exchange in Pinus radiata. Tree Physiology 37, 236–245. [DOI] [PubMed] [Google Scholar]
- Moore CE, Meacham-Hensold K, Lemonnier P, Slattery RA, Benjamin C, Bernacchi CJ, Lawson T, Cavanagh AP. 2021. The effect of increasing temperature on crop photosynthesis: from enzymes to ecosystems. Journal of Experimental Botany 72, 2822–2844. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Rehschuh R, Ruehr NK. 2022. Diverging responses of water and carbon relations during and after heat and hot drought stress in Pinus sylvestris. Tree Physiology 42, 1532–1548. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Riederer M. 2006. Thermodynamics of the water permeability of plant cuticles: characterization of the polar pathway. Journal of Experimental Botany 57, 2937–2942. [DOI] [PubMed] [Google Scholar]
- Rizzuto G, Wang D, Chen J, Hung TH, Fitzky AC, Flashman E, MacKay JJ. 2024. Contrasted NCED gene expression across conifers with rising and peaking abscisic acid responses to drought. Plant Stress 14, 100574. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Rodríguez-Gamir J, Xue J, Clearwater MJ, Meason DF, Clinton PW, Domec JC. 2019. Aquaporin regulation in roots controls plant hydraulic conductance, stomatal conductance, and leaf water potential in Pinus radiata under water stress. Plant, Cell & Environment 42, 717–729. [DOI] [PubMed] [Google Scholar]
- Sack L, Scoffoni C. 2010. Minimum epidermal conductance (gmin, a.k.a. cuticular conductance) protocol. PROMETHEUS. https://prometheusprotocols.net/function/gas-exchange-and-chlorophyll-fluorescence/stomatal-and-non-stomatal-conductance-and-transpiration/minimum-epidermal-conductance-gmin-a-k-a-cuticular-conductance/. [Google Scholar]
- Sadok W, Lopez JR, Smith KP. 2021. Transpiration increases under high-temperature stress: potential mechanisms, trade-offs and prospects for crop resilience in a warming world. Plant, Cell & Environment 44, 2102–2116. [DOI] [PubMed] [Google Scholar]
- Sanchez-Martinez P, Mencuccini M, García-Valdés R, Hammond WM, Serra-Diaz JM, Guo W-Y, Segovia RA, Dexter KG, Svenning J-C, Allen C. 2023. Increased hydraulic risk in assemblages of woody plant species predicts spatial patterns of drought-induced mortality. Nature Ecology & Evolution 7, 1620–1632. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Sharma K, Bourbia I, Freeman J, Jones R, Brodribb T. 2025. Stomatal plasticity maintains water potential homeostasis in Pinus radiata needles. Plant, Cell & Environment 48, 3225–3235. [DOI] [PubMed] [Google Scholar]
- Slot M, Nardwattanawong T, Hernández GG, Bueno A, Riederer M, Winter K. 2021. Large differences in leaf cuticle conductance and its temperature response among 24 tropical tree species from across a rainfall gradient. New Phytologist 232, 1618–1631. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Tardieu F, Simonneau T. 1998. Variability among species of stomatal control under fluctuating soil water status and evaporative demand: modelling isohydric and anisohydric behaviours. Journal of Experimental Botany 49, 419–432. [Google Scholar]
- Teskey R, Wertin T, Bauweraerts I, Ameye M, McGuire MA, Steppe K. 2015. Responses of tree species to heat waves and extreme heat events. Plant, Cell & Environment 38, 1699–1712. [DOI] [PubMed] [Google Scholar]
- Tyree MT, Sperry JS. 1989. Vulnerability of xylem to cavitation and embolism. Annual Review of Plant Physiology and Plant Molecular Biology 40, 19–36. [Google Scholar]
- Urban J, Ingwers M, McGuire MA, Teskey RO. 2017. Stomatal conductance increases with rising temperature. Plant Signaling & Behavior 12, e1356534. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Wang S, Hoch G, Grun G, Kahmen A. 2024. Water loss after stomatal closure: quantifying leaf minimum conductance and minimal water use in nine temperate European tree species during a severe drought. Tree Physiology 44, tpae027. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Weston DJ, Bauerle WL. 2007. Inhibition and acclimation of C3 photosynthesis to moderate heat: a perspective from thermally contrasting genotypes of Acer rubrum (red maple). Tree Physiology 27, 1083–1092. [DOI] [PubMed] [Google Scholar]
- World Meteorological Organization . 2024. WMO confirms that 2023 smashes global temperature record. https://wmo.int/media/news/wmo-confirms-2023-smashes-global-temperature-record
- Zhang P, Yang X, Manevski K, Li S, Wei Z, Andersen MN, Liu F. 2022. Physiological and growth responses of potato (Solanum tuberosum L.) to air temperature and relative humidity under soil water deficits. Plants 11, 1126. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Zhao J, Hartmann H, Trumbore S, Ziegler W, Zhang Y. 2013. High temperature causes negative whole-plant carbon balance under mild drought. New Phytologist 200, 330–339. [DOI] [PubMed] [Google Scholar]
- Zhao L, Gao X, An Q, Ren X, Zhang Y, Luo L, Ma N, Song X, Cai Y, Zhao X. 2023. A shift from isohydric to anisohydric water-use strategy as a result of increasing drought stress for young apple trees in a semiarid agroforestry system. Agricultural and Forest Meteorology 336, 109484. [Google Scholar]
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Data Availability Statement
The primary data supporting this study were not made publicly available at the time of publication. The data that support the findings of this study are available from the corresponding author upon request.
