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ARTICLE   Open Access    

Divergence in isoprenoid emissions among subtropical broadleaf trees: linking photosynthesis, leaf economics, and volatile defense for forest management

  • # Authors contributed equally: Yimiao Mao, Hang Yao

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  • Received: 19 January 2026
    Revised: 25 April 2026
    Accepted: 08 June 2026
    Published online: 29 July 2026
    Forestry Research  6 Article number: e024 (2026)  |  Cite this article
  • Biogenic volatile organic compound (BVOC) emissions are pivotal in plant–environment interactions, yet their intrinsic linkages with photosynthesis and leaf economics across diverse tree species remain poorly integrated. This study investigated seven subtropical broadleaf species spanning distinct lineages to unravel how BVOC chemotypes (isoprene- vs. monoterpene-dominance) align with photosynthetic energy use and leaf structural traits. Using controlled measurements on excised branches to isolate physiological relationships, we combined TD-GC-MS, gas-exchange, and leaf trait analyses. The results revealed strong divergence in BVOC chemotypes that was broadly coherent with species phylogeny and ecological strategy. Isoprene-dominant (ISO) species exhibited higher photosynthetic rates (A), greater electron transport capacity (Jmax), and elevated Jmax/Vcmax ratios, consistent with the hypothesis that isoprene synthesis functions as a photosynthetic overflow mechanism for energy dissipation. In contrast, monoterpene-dominant (MTS) species displayed higher specific leaf weight (SLW) and relied on stored and induced emissions, reflecting a conservative, defense-oriented strategy. BVOC profiles were strongly correlated with SLW and photosynthetic capacity, highlighting a coordinated 'structure–function–volatile' adaptive syndrome. These findings suggest that BVOC emissions may be embedded within leaf economic strategies and photosynthetic networks, providing a basis to help refine next-generation BVOC models by integrating leaf structural traits (e.g., SLW) and photosynthetic electron transport capacity (Jmax) into model parameterization.
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  • Supplementary Table S1 BVOCs emission rates and composition for the seven species.
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  • Cite this article

    Mao Y, Yao H, Yuan Y, Yu C, Wang M, et al. 2026. Divergence in isoprenoid emissions among subtropical broadleaf trees: linking photosynthesis, leaf economics, and volatile defense for forest management. Forestry Research 6: e024 doi: 10.48130/forres-0026-0023
    Mao Y, Yao H, Yuan Y, Yu C, Wang M, et al. 2026. Divergence in isoprenoid emissions among subtropical broadleaf trees: linking photosynthesis, leaf economics, and volatile defense for forest management. Forestry Research 6: e024 doi: 10.48130/forres-0026-0023

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ARTICLE   Open Access    

Divergence in isoprenoid emissions among subtropical broadleaf trees: linking photosynthesis, leaf economics, and volatile defense for forest management

Forestry Research  6 Article number: e024  (2026)  |  Cite this article

Abstract: Biogenic volatile organic compound (BVOC) emissions are pivotal in plant–environment interactions, yet their intrinsic linkages with photosynthesis and leaf economics across diverse tree species remain poorly integrated. This study investigated seven subtropical broadleaf species spanning distinct lineages to unravel how BVOC chemotypes (isoprene- vs. monoterpene-dominance) align with photosynthetic energy use and leaf structural traits. Using controlled measurements on excised branches to isolate physiological relationships, we combined TD-GC-MS, gas-exchange, and leaf trait analyses. The results revealed strong divergence in BVOC chemotypes that was broadly coherent with species phylogeny and ecological strategy. Isoprene-dominant (ISO) species exhibited higher photosynthetic rates (A), greater electron transport capacity (Jmax), and elevated Jmax/Vcmax ratios, consistent with the hypothesis that isoprene synthesis functions as a photosynthetic overflow mechanism for energy dissipation. In contrast, monoterpene-dominant (MTS) species displayed higher specific leaf weight (SLW) and relied on stored and induced emissions, reflecting a conservative, defense-oriented strategy. BVOC profiles were strongly correlated with SLW and photosynthetic capacity, highlighting a coordinated 'structure–function–volatile' adaptive syndrome. These findings suggest that BVOC emissions may be embedded within leaf economic strategies and photosynthetic networks, providing a basis to help refine next-generation BVOC models by integrating leaf structural traits (e.g., SLW) and photosynthetic electron transport capacity (Jmax) into model parameterization.

    • Plant-derived biogenic volatile organic compounds (BVOCs) are a diverse group of low-molecular-weight organic compounds emitted during plant growth and development. The major classes of BVOCs, categorized according to their biosynthesis pathways, include terpenoids (such as isoprene, monoterpenes, and sesquiterpenes), compounds derived from fatty acid metabolism (so-called green leaf volatiles [GLVs]), and aromatic compounds[13]. Terrestrial ecosystems emit about 1 billion tons of carbon equivalent in BVOCs annually, accounting for over 90% of global VOC emissions[4]. Among these, isoprenoids, particularly isoprene and monoterpenes, constitute more than 75% of the total BVOC emissions[5,6]. These compounds play key roles in ecological processes and influence ecosystem structure and function through biogeochemical feedbacks[69].

      Throughout their life cycle, plants face a multitude of biotic and abiotic stresses, including herbivory, pathogens, drought, extreme temperatures, and salinity. BVOCs serve key functions in mitigating these stresses and facilitating reproduction[6,10]. In response to biotic stress, BVOCs operate through direct and indirect defenses. Plants can directly emit terpenoids and GLVs to effectively deter pests and pathogens. For instance, monoterpenes such as limonene and eucalyptol exhibit insecticidal and repellent properties by inhibiting insect and microbial activity[5,11,12]. Similarly, GLVs such as cis-3-hexenol exhibit strong antimicrobial effects against bacteria and fungi, while trans-2-hexenal repels insect larvae to reduce herbivory[13]. Some phenylpropanoids, including eugenol, also exhibit broad-spectrum antimicrobial activity, inhibiting mycelial growth[14]. For indirect defense, plants release specific BVOCs for chemical signaling. For example, maize attacked by Ostrinia furnacalis emits cis-3-hexenyl acetate and terpenoids to attract parasitic wasps (Trichogramma)[15]. Wounded Arabidopsis thaliana releases cis-3-hexenol, which primes neighboring plants via jasmonic acid and ethylene pathways, inducing early defense gene expression and forming a 'group immune' response[16]. BVOCs also enhance reproduction by attracting pollinators such as bees and butterflies[17,18].

      Under abiotic stress, BVOCs play critical protective roles in plants. For instance, many tree species (e.g., poplar, oak) emit substantial amounts of isoprene in response to high temperature or intense light[2,19]. Beyond its well-established function in stabilizing chloroplast membranes, emerging evidence suggests that isoprene may also act as a hormone-like signal, modulating cellular metabolism and stress-response pathways to enhance the resilience of photosynthetic tissues[2022]. Meanwhile, certain monoterpenes function as effective lipophilic antioxidants and can act as defense primers by inducing the expression of stress-related genes, with some even facilitating interplant communication[21,23]. Additionally, sesquiterpenes and aromatic compounds contribute to drought tolerance by modulating osmotic potential, stabilizing membranes, and reducing evaporative water loss[24,25].

      BVOC biosynthesis is an integral part of plant secondary metabolism. Terpenoid synthesis occurs mainly via two pathways: the mevalonic acid (MVA) pathway in the cytoplasm and the methylerythritol phosphate (MEP) pathway in plastids, both producing the universal five-carbon precursors, isopentenyl diphosphate (IPP) and dimethylallyl diphosphate (DMAPP)[1,26]. The MVA pathway predominantly synthesizes sesquiterpenes, triterpenes, sterols, and others, whereas the MEP pathway yields isoprene, monoterpenes, diterpenes, and carotenoids[2,27]. Aromatic compounds are derived from phenylalanine via phenylalanine ammonia-lyase (PAL), leading to volatiles such as benzaldehyde, phenethyl alcohol, and methyl salicylate[28]. GLVs are generated through the lipoxygenase (LOX) pathway, which oxidizes and cleaves fatty acids into C6–C9 aldehydes, alcohols, and esters, often released rapidly upon damage[29,30].

      Rather than representing mere carbon loss, BVOCs reflect a metabolic investment by plants. Their synthesis and emission are tightly coupled to photosynthetic carbon fixation, which supplies necessary substrates and energy (ATP, NADPH)[31]. Thus, BVOC emission constitutes a consumptive allocation of photosynthetically fixed carbon, revealing strategic trade-offs in resource use[31,32]. Although all three major classes of BVOCs are widespread, emission profiles (composition, rates, and inducibility) are highly species-specific and phylogenetically conserved[7,33]. For example, Pinaceae species are high monoterpene emitters (e.g., α-pinene); Salicaceae (Populus), Fabaceae, Moraceae (Ficus), and Fagaceae (Quercus) typically emit high levels of isoprene; and Magnoliaceae and Lauraceae chiefly release monoterpenes[33,34]. These traits ultimately underscore the tight coupling between BVOC emission and photosynthetic carbon fixation[2].

      Environmental selection can drive convergent evolution in BVOC emissions across disparate lineages. For instance, in Mediterranean ecosystems characterized by drought and high irradiance, distantly related families (e.g., Oleaceae, Myrtaceae) have independently evolved high-light-induced isoprene emission, leveraging its thermotolerance properties[2,35]. Similar adaptive elevations in isoprenoid emissions are observed in lineages inhabiting hot, arid savannas[33,36]. Conversely, at the interspecific level, BVOC emission patterns are often phylogenetically conserved and reflect long-term ecological adaptation[37]. However, the physiological mechanisms linking these macro-evolutionary patterns to underlying photosynthetic performance and leaf economic strategies remain fragmented. Specifically, how the coordinated interplay of photosynthetic energy allocation, leaf structural investment, and BVOC chemistry coalesces into distinct adaptive syndromes remains to be fully elucidated[18,38].

      To bridge this gap, we selected seven subtropical broadleaf woody species spanning diverse families and ecological habits. By integrating measurements of BVOC emission profiles, photosynthetic gas-exchange parameters, and key leaf structural traits under controlled conditions, this study aimed to: (1) uncover the intrinsic linkages between BVOC chemotypes (isoprene- vs. monoterpene-dominance) and core physiological traits; and (2) synthesize these relationships into a coherent 'structure–function–volatile' framework explaining divergent adaptive strategies in forest trees. These findings provide a mechanistic basis for incorporating plant functional traits into predictions of forest-atmosphere interactions under environmental change.

    • This study employed a mechanism-focused comparative approach to elucidate the intrinsic relationships between BVOC emission profiles and core plant functional traits. We selected seven common, co-occurring subtropical woody species from diverse families (Machilus leptophylla, Carya illinoinensis, Choerospondias axillaris, Liriodendron chinense, Edgeworthia chrysantha, Wisteria sinensis, and Ormosia hosiei) to capture broad variation in phylogeny, growth form, and leaf economic strategy (Table 1). Critically, the chosen species are characterized as low-to-moderate BVOC emitters, based on the emission rate classifications reported in the MEGAN2.1 model framework[4] and supported by empirical data from diverse regional studies[3941]. By focusing on this range, we aimed to reveal fundamental trait-emission linkages that might be obscured by the disproportionately high metabolic flux of hyper-emitters (e.g., some Populus or Quercus species), thereby addressing a knowledge gap for non-extreme emitters.

      Table 1.  Leaf functional traits and ecological characteristics of seven woody species.

      SpeciesFamilyGenusLeaf water content (LWC, %)Specific leaf dry weight (SLW, g·m−2)Specific leaf area (SLA, cm2·g−1)Ecological niche
      Machilus leptophyllaLauraceaeMachilus59.945 ± 0.743e95.138 ± 3.69a105.883 ± 3.993cST, CT; evergreen understory tree in subtropical forests; prefers moist, well-drained soils
      Carya illinoinensisJuglandaceaeCarya59.331 ± 0.623e67.961 ± 4.007bc149.701 ± 8.718bCT; introduced deciduous tree, cultivated, adapted to full sun and deep soils
      Choerospondias axillarisAnacardiaceaeChoerospondias59.1 ± 1.043e73.674 ± 4.081b137.784 ± 7.432bcLT, ST; light-demanding and fast-growing deciduous tree, common on forest margins and open slopes
      Liriodendron chinenseMagnoliaceaeLiriodendron71.424 ± 1.076b57.852 ± 4.23c177.605 ± 13.222bLT, HT, CT; fast-growing, pioneer deciduous tree of valleys and moist mountainous forests
      Edgeworthia chrysanthaThymelaeaceaeEdgeworthia81.657 ± 0.346a39.692 ± 2.254d255.901 ± 14.084aLT, ST; deciduous understory shrub, tolerates semi-shade; often found along streams or in moist ravines
      Wisteria sinensisFabaceaeWisteria67.593 ± 0.975c36.846 ± 3.01d281.382 ± 24.679aLT, ST, CT, DT, WT; light-demanding deciduous liana, climbing on forest edges, open areas, and riparian zones
      Ormosia hosieiFabaceaeOrmosia63.953 ± 1.604d70.813 ± 5.667b145.939 ± 11.994bcLT, ST, CT; semi-evergreen tree of mixed broadleaf forests, tolerating partial shade
      LT, light-tolerant; ST, shade-tolerant; HT, heat-tolerant; CT, cold-tolerant; DT, drought-tolerant; WT, waterlogging-tolerant. Values are mean ± SE (n = 6). Different lowercase letters with a column indicate significant differences (Tukey's test, p < 0.05).
    • All plant materials were obtained from the Donghu Campus of Zhejiang A&F University (119°43' E, 30°15' N). Sampling was conducted in July 2023 (peak growing season) from three healthy, mature individuals per species. From each individual, two sun-exposed branches were excised, yielding six replicates per species (n = 6). This hierarchical design, with individual trees included as a random factor in all statistical analyses, follows established protocols for comparative BVOC and leaf physiology studies[42,43].

      To standardize conditions for rigorous physiological comparison, we used excised branches under controlled laboratory settings[42,43]. Immediately after excision, healthy sun-exposed branches (> 60 cm) were recut underwater to 10–15 cm to prevent xylem embolism and transported with stems submerged. This procedure maintains xylem integrity and preserves key physiological functions, including photosynthetic rates, stomatal conductance, and isoprene emissions, at levels comparable to intact attached branches[4447]. A 30-min acclimation period was selected based on preliminary tests showing that this duration allowed stomatal stabilization after excision while minimizing detachment stress, consistent with established excised-branch protocols[42,43].

      For species with pressurized storage structures, excision may transiently elevate emissions. We controlled this potential bias through uniform handling across species, randomizing any artifacts and mixed-effects models with individual trees as a random factor, ensuring valid comparative inference.

    • All BVOC sampling was conducted indoors under strictly controlled and monitored environmental conditions: temperature (28 °C), relative humidity (65%−75%), CO2 concentration (ambient, ~420 μmol·mol−1), and a saturating photosynthetic photon flux density (PPFD of 1,050 μmol·m−2·s−1) provided by a calibrated LED plant growth light (model C21GL-AE26-15W-A, SanSi, China).

      A custom-made semi-open transparent glass chamber (diameter 10.5 cm, length 15 cm, 95% quartz glass) was used for sampling. The chamber featured inlet and outlet ports at its base, with one port left open to maintain stable internal pressure. It was positioned 20 cm beneath the LED light source.

    • Ambient air was drawn by a calibrated pump (SB-948, Beijing Institute of Labor Protection Science) at a constant flow rate of 900 ml·min1. The air stream was passed through a trapping column packed with molecular sieve and charcoal (Supelpure HC) to remove ambient VOCs and moisture, ensuring a clean, hydrocarbon-free supply before entering the chamber via Teflon tubing.

    • Volatiles emitted from enclosed leaves were drawn from the outlet port at 100 ml·min1 using a portable mini-sampler (Beijing Institute of Labor Protection) and trapped onto a BVOC-specific adsorption tube (Tenax TA, Markes, UK). Each sampling event lasted 30 min. Daily blank samples (empty chamber) were collected under identical conditions for background correction. Adsorption tubes were sealed and stored at 4 °C in the dark, with all samples analyzed within 48 h. The enclosed leaf area was determined by scanning after sampling for accurate emission-rate calculation.

    • BVOCs were analyzed using thermal desorption-gas chromatography-mass spectrometry (TD-GC-MS) with a TD-100 unit (Markes, UK), GC-7890B, and MS-5977B (Agilent, USA). The detailed procedures and operational parameters are described in three steps below. (1) Thermal desorption: The adsorption tube was desorbed at 320 °C for 5 min. Volatile compounds were focused in a cold trap held at −10 °C, then rapidly heated for transfer to the GC. (2) Gas chromatographic separation: The separation was performed using a DB-Select 624 Ultra Inert capillary column (30 m × 250 μm × 1.4 μm) with helium carrier gas at a flow rate of 1.2 ml·min−1. The oven temperature program was as follows: 40 °C (hold 5 min), ramp up to 80 °C at 8 °C min−1 (hold 2 min), to 160 °C at 5 °C min−1 (hold 3 min), to 200 °C at 6 °C min−1 (hold 8 min), and post-run at 220 °C for 10 min. (3) MS spectrometric detection: An electron impact (EI) ion source was employed with the ion source temperature set at 230 °C and the quadrupole temperature at 150 °C. The mass scanning range was 45 to 350 m/z.

    • Qualitative identification was performed using MassHunter Qualitative Analysis software (Agilent, USA) with the NIST20.L mass spectral library (National Institute of Standards and Technology, USA) and chromatographic-grade standard alkane mixtures (Sigma). Identification was based on comparisons of mass spectra and retention indices (for details, see[43]).

      Quantification used an external standard method with a certified gas mixture (Dalian Specialty Gases Co., China) containing 14 target compounds: methanol, acetaldehyde, isoprene, benzene, toluene, xylene, chlorobenzene, dichlorobenzene, acetonitrile, acrolein, crotonaldehyde, α-pinene, acetone, and 2-butanone. The original concentration of each compound was 1,000 ± 5 μmol·mol−1, v/v. Primary standards were dynamically diluted with high-purity N2 to generate a working concentration of 200 μmol·mol−1, v/v. To construct calibration curves, the diluted standard gas was sampled onto adsorption tubes at the same flow rate (100 ml·min−1) for different durations (10, 20, 30, and 40 min), yielding a series of absolute amounts (nmol) for each target compound. Calibration curves were established by plotting peak area against absolute amount (nmol), with R2 > 0.99 for all compounds. Emission rates were calculated based on the quantified amount, leaf area, sampling time, and flow rate. Daily blank samples (empty chamber) were analyzed under identical conditions, and their corresponding peak areas were subtracted from all sample measurements to correct for background contamination. All emission rates were expressed on a leaf area basis (nmol·m−2·s−1) to facilitate comparison with previous studies.

    • Measurements of photosynthetic parameters were conducted using a portable photosynthesis system (GFS-300, WALZ, Germany). Healthy mature leaves were selected for measurements.

    • After 30 min of instrument warm-up and zeroing, baseline conditions were set: flow rate of 750 μmol·s−1, leaf chamber temperature of 28 °C, relative humidity of 60%−70%, CO2 concentration of 420 μmol·mol−1, and photosynthetic photon flux density (PPFD) of 800 μmol·m−2·s−1.

      Leaves were equilibrated until stomatal conductance and net photosynthetic rate stabilized. The photosynthetic gas-exchange parameters recorded included net assimilation rate (A, μmol·m−2·s−1), transpiration rate (E, mmol·m−2·s−1), stomatal conductance (Gs, mmol·m−2·s−1), and intercellular CO2 concentration (Ci, μmol·mol−1). Water use efficiency (WUE) was calculated as WUE = A/E.

    • After baseline measurements, light response measurements were conducted. The PPFD (μmol·m−2·s−1) levels were set according to[19], following the sequence: 800, 1,200, 1,600, 800, 400, 200, 100, 50, and 0. Each PPFD level was maintained for 3–5 min until a steady state. The light response curves were fitted using Ye Zipiao's modified rectangular hyperbola model[48]:

      $ A_{}=\alpha _{\mathrm{p}}\frac{1-\beta _{\mathrm{p}}I}{1+\gamma _{\mathrm{p}}I}I-R_{\mathrm{d}} $ (1)

      where, A is net assimilation rate, I is PPFD, αp is the initial slope, βp is the photoinhibition coefficient, γp is the light saturation coefficient, Rd is the dark respiration rate. The light saturation point Isat and the maximum net assimilation rate Amax were calculated using Eqs. (2) and (3), respectively:

      $ I_{\mathrm{sat}}=\frac{\sqrt{\left( \beta _{\mathrm{p}}+\gamma _{\mathrm{p}} \right) /\beta _{\mathrm{p}}}-1}{\gamma _{\mathrm{p}}} $ (2)
      $ A_{\max}=\alpha _{\mathrm{p}}\left( \frac{\sqrt{\beta _{\mathrm{p}}+\gamma _{\mathrm{p}}}-\sqrt{\beta _{\mathrm{p}}}}{\gamma _{\mathrm{p}}} \right) ^2-R_{\mathrm{d}} $ (3)
    • After the base state stabilized and the stomata were fully open, CO2 concentrations were set as follows: 420, 200, 120, 60, 30, 15, 420, 600, 800, 1,200, and 1,600 μmol·mmol−1. Measurements were taken after stabilization at each concentration. A-Ci response biochemical model established by Farquhar et al.[49] was employed for curve fitting. The model was expressed as follows:

      $ A=\min \left\{ A_{\mathrm{c}},A_{\mathrm{j}} \right\} \left( 1-\frac{\varGamma ^*}{C_{\mathrm{i}}} \right) -R_{\mathrm{p}} $ (4)

      where, A is net assimilation rate, Ac represents the CO2 assimilation rate limited by Rubisco activity, Aj indicates the CO2 assimilation rate constrained by the regeneration rate of ribulose-1,5-bisphosphate (RuBP), Г* refers to the CO2 compensation point in the absence of dark respiration, Ci stands for the intercellular CO2 concentration, and Rp represents the rate of respiration under light conditions. The mathematical expressions for Ac and Aj were given as follows:

      $ A_{\mathrm{c}}=\frac{V_{\mathrm{c}\max}C_{\mathrm{i}}}{C_{\mathrm{i}}+K_{\mathrm{c}}\left( 1+O/K_{\mathrm{o}} \right)} $ (5)
      $ A_{\mathrm{j}}=\frac{JC_{\mathrm{i}}}{4.5C_{\mathrm{i}}+10.5\varGamma ^*} $ (6)

      where, Vcmax is the maximum rate of Rubisco carboxylation, Kc and Ko are the Michaelis–Menten constants for carboxylation and oxygenation, respectively, O is the oxygen partial pressure inside the stomata, and J is the electron transport rate at light saturation for RuBP regeneration.

    • After the base state stabilized and the stomata were fully open, temperature response curves were measured. Leaf chamber temperature (°C) was set in the sequence: 28, 23, 33, 38, 43, and 48. Each temperature was maintained for 5 min to ensure leaf temperature equilibrium. The curves were fitted using Ye-Zipiao's temperature response model (Eq. 7):

      $ A=\alpha _{\mathrm{t}}\frac{1-\beta _{\mathrm{t}}t}{1+\gamma _{\mathrm{t}}t}t+R_{\mathrm{to}} $ (7)

      where, A is net assimilation rate, αt is the initial slope of the temperature response curve, βt is the inhibition coefficient, γt is the saturation rate, t is the temperature, and Rto is the photorespiration rate. The optimum temperature (Topt) and the corresponding maximum net assimilation rate (Atmax) were calculated using Eqs. (8) and (9):

      $ T_{\mathrm{opt}}=\frac{\sqrt{\left( \beta _{\mathrm{t}}+\gamma _{\mathrm{t}} \right) /\beta _{\mathrm{t}}}-1}{\gamma _{\mathrm{t}}} $ (8)
      $ A_{\mathrm{t}\max }=\alpha _{\mathrm{t}}\left( \frac{\left( \sqrt{\beta _{\mathrm{t}}+\gamma _{\mathrm{t}}}-\sqrt{\beta _{\mathrm{t}}}\right)}{\gamma_{t}}\right)^2+R_{{\rm{to}}} $ (9)
    • After BVOCs were collected, leaf fresh weight (FW) was determined, and leaf area (LA) was scanned using an HP Scanjet 4890 scanner. Subsequently, the leaves were oven-dried at 80 °C until a constant weight was reached (difference between two consecutive measurements < 0.001 g), and dry weight (DW, g) was recorded. Leaf water content (LWC), specific leaf weight (SLW, defined as leaf dry weight per unit area), and specific leaf area (SLA, expressed as leaf area per unit dry weight) were then calculated using the following equations:

      $ {\mathrm{LWC}}=100*({\mathrm{FW}}-{\mathrm{DW}})/{\mathrm{FW}} $ (10)
      $ {\mathrm{SLW}}={\mathrm{DW}}/({\mathrm{LA}}\cdot 10^{-4}) $ (11)
      $ \mathrm{SLA=LA/DW} $ (12)

      where, LWC is expressed in %, FW is leaf fresh weight (g), DW is leaf dry weight (g), SLW is in g·m2, LA is leaf area (cm2), and SLA is in cm2·g1.

    • Microsoft Excel was used for the organization and preprocessing of raw data. The photosynthetic light response curves and temperature response curves were fitted using the Photosynthesis Model Simulation Software (PMSS) developed by Ye-Zhipiao to obtain the key parameters of the model. The photosynthetic CO2 response curves were fitted using the plantecophys package in R language to calculate relevant physiological and biochemical indicators.

      Statistical analysis was performed using SPSS statistical software (v27): one-way or multi-way analysis of variance (ANOVA) and post hoc tests (Tukey's test) were used to evaluate significant differences among the seven species. For these comparisons, all six technical replicates per species (n = 6) were included as independent data points. The independent samples t-test was used to compare the mean differences between two BVOC chemotype groups (monoterpene-dominant, MTS, n = 4 species; isoprene-dominant, ISO, n = 3 species). For this between-group comparison, species averages (each derived from six technical replicates) were used as the unit of analysis, with degrees of freedom = 5. Spearman correlation analysis was carried out to explore the relationships among variables. All graphs were drawn using OriginPro 2024 software.

    • The seven species selected, representing different families and genera (Table 1), exhibited substantial variations in life form, leaf water content (LWC), specific leaf weight (SLW), specific leaf area (SLA), and ecological habit. In terms of life form, Machilus leptophylla was evergreen, Ormosia hosiei was semi-evergreen, and the remaining species were deciduous. With the exception of Edgeworthia chrysantha, which was a shrub, the other species are woody trees.

      Considerable interspecific variation was observed in leaf functional traits. LWC ranged from 59% to 81%, SLW from 36.8 to 95.1 g·m−2, and SLA from 105 to 255 cm2·g−1. Among these, the shrub E. chrysantha exhibited the highest LWC (81.7%) and the lowest SLW (39.7 g·m−2), consistent with adaptation to semi-shaded and humid environments. The evergreen tree M. leptophylla displayed the highest SLW (95.1 g·m−2), indicative of denser leaf tissue and greater shade tolerance, which may reflect a carbon investment strategy favoring extended leaf lifespan under low light. By contrast, W. sinensis had the lowest SLW (36.8 g·m−2), suggesting relatively thin leaves that were consistent with its climbing habit and a strategy prioritizing rapid light capture and high photosynthetic turnover via expanded leaf area and reduced leaf mass.

    • The seven plant species exhibited marked divergence in BVOC emission profiles (detailed in Supplementary Table S1, with key data summarized in Fig. 1). Based on the dominant compounds, the species were grouped into two dominant types: a monoterpene-dominant type (MTS, monoterpenes > 60% of total emissions) and an isoprene-dominant type (ISO, isoprene > 70%). Green leaf volatiles and aromatic compounds were emitted at low rates by both types, though their compositional profiles differed, suggesting potential divergence in metabolic pathways and ecological function.

      Figure 1. 

      BVOC emission profiles of seven plant species. (a) Total BVOC emission rates. (b) Relative compositional proportion of BVOCs for each species. (c) Compositional proportion of isoprene-dominant emitters (ISO). (d) Compositional proportion of monoterpene-dominant emitters (MTS). BVOC emission rates (nmol·m−2·s−1) for individual compounds and total emissions are provided in Supplementary Table S1. Different lowercase letters indicate significant differences among species (Tukey's test, p < 0.05). 'ns' denotes no significant difference between ISO and MTS groups (independent samples t-test, p > 0.05). Values are mean ± SE (n = 6).

      The MTS species, Machilus leptophylla, Carya illinoinensis, Choerospondias axillaris, and Liriodendron chinense emitted primarily α-pinene, β-phellandrene, and β-pinene. Among these, C. axillaris was notable for its high emissions of β-ocimene and for having a significantly higher total BVOCs emission rate than other monoterpene emitters. The ISO species included Edgeworthia chrysantha, Wisteria sinensis, and Ormosia hosiei. W. sinensis exhibited the highest isoprene emission rate at 6.487 nmol·m−2·s−1, which was significantly greater than that of E. chrysantha and O. hosiei.

      Although the mean total BVOC emission rate was higher in isoprene-dominant species than in monoterpene-dominant ones, the difference was not statistically significant.

    • Under baseline conditions (PPFD 800 μmol·m−2·s−1, CO2 420 μmol·mol−1, and 28 °C), significant interspecific differences and emission-type-specific patterns were observed in net assimilation rate (A), transpiration rate (E), stomatal conductance (Gs), intercellular CO2 concentration (Ci), and water use efficiency (WUE) (Fig. 2). ISO species (particularly W. sinensis) exhibited higher A, E, and Gs, whereas MTS species (such as Machilus leptophylla and Carya illinoinensis) showed higher WUE, suggestive of a more conservative water use strategy. The absence of significant differences in Ci between the two groups suggested that divergence in stomatal behavior primarily underlies the differences in transpiration and water use efficiency.

      Figure 2. 

      Photosynthetic parameters under baseline conditions (PPFD 800 μmol·m−2·s−1, CO2 420 μmol·mol−1, 28 °C). MTS-average and ISO-average denote pooled values for monoterpene-dominant and isoprene-dominant types, respectively. Lowercase letters indicate significant differences among the seven species (Tukey's test, p < 0.05). Asterisks indicate significant differences between MTS and ISO groups (* p < 0.05, ** p < 0.01; independent samples t-test); 'ns' indicates no significant difference. Values are mean ± standard error (SE) (n = 6).

      Light response curves were fitted using the modified rectangular hyperbola model[48]. The model fitted all species well, with coefficient of determination (R2) ranging from 0.995 to 0.998 across the seven species (Table 2; Fig. 3). While no significant differences were found in maximum net assimilation rate (Amax) among species, the light saturation point (Isat) was highest in O. hosiei (1,877 μmol·m−2·s−1), and the light compensation point (Ic) was lowest in E. chrysantha (14.4 μmol·m−2·s−1). The lowest apparent quantum efficiency (αp) was observed in M. leptophylla (Fig. 3; Table 2).

      Table 2.  Photosynthetic parameters derived from the response curves to light (A-L), CO2 (A-Ci) and temperature (A-T.) in seven woody species.

      Species Machilus leptophylla Carya illinoinensis Choerospondias axillaris Liriodendron chinense Edgeworthia chrysantha Wisteria sinensis Ormosia hosiei
      Fitting parameters of the light response curve Amax 11.118 ± 1.156a 12.61 ± 0.876a 12.117 ± 0.602a 10.85 ± 0.381a 12.154 ± 0.378a 12.333 ± 0.592a 13.1 ± 0.691a
      Isat 1,309.962 ± 67.986b 1,351.746 ± 28.021b 1,325.645 ± 67.633b 1,269.557 ± 82.395b 1,474.862 ± 47.225b 1,429.707 ± 116.537b 1,877.378 ± 166.234a
      Ic 23.599 ± 2.874a 18.335 ± 0.856a 17.051 ± 1.956a 16.578 ± 2.646a 14.387 ± 1.131a 16.335 ± 4.216a 18.709 ± 4.339a
      αp 0.046 ± 0.002c 0.058 ± 0.005ab 0.056 ± 0.004abc 0.05 ± 0.003bc 0.057 ± 0.002ab 0.06 ± 0.006ab 0.066 ± 0.004a
      Rd 1.031 ± 0.143a 1.005 ± 0.097a 0.895 ± 0.095a 0.776 ± 0.124a 0.784 ± 0.063a 0.932 ± 0.233a 1.113 ± 0.208a
      R2 0.998 0.997 0.998 0.998 0.997 0.998 0.995
      Fitting parameters of CO2 response curve Vcmax 57.66 ± 4.595a 60.462 ± 4.331a 65.766 ± 5.802a 67.173 ± 3.386a 56.394 ± 2.309a 67.213 ± 1.684a 62.018 ± 4.381a
      Jmax 75.331 ± 8.063e 81.705 ± 5.382de 87.955 ± 4.147cde 110.347 ± 8.418abc 103.649 ± 6.705bcd 130.073 ± 6.155a 117.24 ± 8.541ab
      Rp 0.99 ± 0.111ab 0.798 ± 0.114ab 1.134 ± 0.195ab 1.328 ± 0.305a 0.714 ± 0.073b 0.74 ± 0.042ab 0.778 ± 0.109ab
      Γ* 68.527 ± 3.059ab 64.978 ± 2.238ab 67.686 ± 3.06ab 70.201 ± 4.286a 62.787 ± 1.173ab 59.053 ± 0.322b 63.008 ± 2.015ab
      Jmax/Vcmax 1.299 ± 0.061b 1.366 ± 0.082b 1.393 ± 0.139b 1.637 ± 0.073ab 1.828 ± 0.055a 1.94 ± 0.123a 1.941 ± 0.186a
      R2 0.996 0.995 0.989 0.997 0.997 0.999 0.997
      Fitting parameters of temperature response curve αt 0.594 ± 0.214b 0.364 ± 0.054b 0.407 ± 0.053b 0.473 ± 0.12b 1.403 ± 0.872a 0.493 ± 0.064b
      Atmax 13.359 ± 0.815a 12.465 ± 0.411ab 10.262 ± 0.285c 10.963 ± 0.662bc 11.868 ± 0.15abc 12.129 ± 0.626abc
      Topt 35.2 ± 0.43a 37.086 ± 0.965a 34.39 ± 0.85a 37.593 ± 1.078a 31.024 ± 1.89b 37.282 ± 0.636a
      R2 0.985 0.988 0.995 0.972 0.975 0.967
      Note: abbreviations: Amax: maximum net assimilation rate (μmol·m−2·s−1); Isat: light saturation point (μmol·m−2·s−1); Ic: light compensation point (μmol·m−2·s−1); αp: initial quantum efficiency (μmol CO2 μmol–1 photons); Rd: dark respiration rate (μmol·m-2·s−1); Vcmax: maximum carboxylation rate of Rubisco enzyme (μmol·m−2·s−1); Jmax: maximum electron transfer rate (μmol·m−2·s−1); Rp: respiratory rate under light (μmol·m−2·s−1); Γ*: CO2 compensation point (μmol·mol−1); Jmax/Vcmax: the ratio of Jmax to Vcmax (μmol electrons [μmol CO2]−1); αt: initial slope (μmol·m−2·s−1); Atmax: maximum net assimilation rate in temperature response curve (μmol·m−2·s−1); Topt: optimal temperature (°C) corresponding to maxima net assimilation rate; R2: fitting coefficient. Values are mean ± SE (n = 6). Different letters within a row indicate significant differences (LSD test, p < 0.05).

      Figure 3. 

      Photosynthetic response curves. (a)−(g) Light response curves (A-L). (h)−(n) CO2 response curves (A-Ci). (o)−(t) Temperature response curves (A-T). A, net assimilation rate. Ac and Aj donate Rubisco activity-limited and RuBP regeneration-limited stages, respectively, derived from A-Ci curves. Curve fitting statistics are provided in Table 2 (R2 > 0.98, p < 0.05 for all fits).

      CO2 response curves were fitted using Farquhar's biochemical model[49]. The model provided an excellent fit for all species, with R2 values ranging from 0.989 to 0.997 (Table 2; Fig. 3). Among the fitted parameters, the maximum carboxylation rate (Vcmax) did not differ significantly among species, whereas the maximum electron transport rate (Jmax) was highest in W. sinensis and lowest in M. leptophylla. The higher Jmax/Vcmax ratio observed in ISO species suggested a greater capacity for photosynthetic electron transport. Overall, isoprene emitters exhibited higher Jmax and Jmax/Vcmax values, but lower respiration in light (Rp) and CO2 compensation point (Γ*), compared to monoterpene emitters.

      Temperature response curves were fitted using the temperature response model[48]. The model provided a good fit for all species, with R2 values ranging from 0.967 to 0.995 (Table 2; Fig. 3). The optimal photosynthetic temperature (Topt) ranged from 31.024 to 37.593 °C. C. illinoinensis and W. sinensis exhibited higher Topt values, while M. leptophylla showed the lowest, indicating higher sensitivity to elevated temperature. The maximum net assimilation rate at Topt (Atmax) was highest in C. illinoinensis and relatively low in Liriodendron chinense and E. chrysantha.

      These results reveal interspecific differentiation and emission-type-specific patterns in photosynthetic traits, reflecting distinct photosynthetic adaptation strategies associated with different BVOC chemotypes.

    • Spearman correlation and regression analyses (Fig. 4) revealed systematic relationships between BVOC emission rates and photosynthetic parameters and leaf structural traits, with distinct patterns observed between MTS and ISO plants.

      Figure 4. 

      Correlations among leaf traits, photosynthetic parameters, and BVOC emissions. (a)–(d) Leaf traits vs photosynthetic parameters; (e)–(h) BVOC emissions vs photosynthetic parameters. Correlation coefficients (R2) and significance levels are shown for each relationship (ns, p > 0.05; * p < 0.05; ** p < 0.01). Abbreviations: SLW, specific leaf weight; LWC, leaf water content; other parameters defined in Table 2.

      Specific leaf weight (SLW) was strongly negatively correlated with net assimilation rate (A) under baseline conditions (R2 = 0.657, p < 0.05) and strongly positively correlated with the light compensation point (Ic) (R2 = 0.901, p < 0.05). Leaf water content (LWC) was positively correlated with transpiration rate (E) (R2 = 0.417, p < 0.05) and negatively correlated with the net photosynthetic rate at optimum temperature (Atmax) (R2 = 0.562, p > 0.05).

      Isoprene emission was strongly positively correlated with net assimilation rate (R2 = 0.901, p < 0.01), Jmax (R2 = 0.956, p < 0.01). These correlations were stronger for isoprene than for monoterpenes, with monoterpene emission showing no significant correlation with these parameters (p > 0.05 for all). Moreover, isoprene emission showed a stronger correlation with Jmax than with Jmax/Vcmax, suggesting that its emission is more closely linked to photosynthetic electron transport capacity. These findings indicated divergent regulatory mechanisms between monoterpene- and ISO-type plants.

      Furthermore, significant intrinsic correlations were identified among photosynthetic parameters (Fig. 5). Net photosynthetic rate was strongly positively correlated with stomatal conductance and transpiration rate (r = 0.68); light saturation point (Isat) was significantly correlated with maximum net photosynthetic rate (Amax) (r = 0.86); light compensation point (Ic) was negatively correlated with apparent quantum efficiency (αp) (r = −0.79); and CO2 compensation point (Γ*) was negatively correlated with the Jmax/Vcmax ratio (r = −0.64). Together, these relationships reflect key trade-offs and synergies within the photosynthetic apparatus pertaining to light capture, carbon assimilation, and water-use strategies.

      Figure 5. 

      Spearman correlation matrix of photosynthetic parameters. E, Transpiration rate, Gs: Stomatal conductance, A: Net assimilation rate, Ci: Intercellular CO2 concentration; other parameters (αp, Rd, Amax, Isat, Ic, Vcmax, Jmax, Rp, Γ*, Jmax/Vcmax, αt, Atmax, and Topt) defined in Table 2. Color scale indicates correlation coefficient (r). * p < 0.05, ** p < 0.01.

    • This study systematically examined variations and synergies in BVOC emissions, photosynthetic characteristics, and leaf structural traits among seven common subtropical woody plants. By deliberately focusing on moderate emitters from diverse lineages, we aimed to elucidate the intrinsic 'structure–function–volatile' relationships without the potential confounding effects of hyper-emission, which can disproportionately dominate both metabolic budgets and functional interpretations. The results revealed significant functional differentiation and intrinsic correlations among BVOC chemotypes, photosynthetic energy-use strategies, and leaf structural traits. The following sections integrate and discuss these findings from three perspectives: species-specific metabolic strategies, the driving role of photosynthetic energy and carbon supply, and the long-term evolutionary adaptations underpinning these coordinated traits.

    • The seven studied species, representing seven different genera and diverse life forms (evergreen/deciduous trees, shrubs, and lianas), exhibited pronounced differences in BVOC composition and emission rates (Supplementary Table S1; Table 1). Crucially, this chemical divergence was not random but aligned with and reinforced their positions along the Leaf Economics Spectrum (LES) and within the fundamental growth-defense trade-off, reflecting evolutionary adaptations to distinct ecological niches[8,18,20,50].

      Monoterpene-dominant emitters (MTS: M. leptophylla, C. illinoinensis, C. axillaris, and L. chinense) exhibited monoterpene proportions of 60%–87%, with α-pinene, β-pinene, and D-limonene as major constituents. These compounds are well-documented for their roles in direct insect resistance, antimicrobial activity, and plant-plant signaling[8,50]. This strategy epitomizes the 'Conservative-Storage' syndrome[5,50], characterized by high investment in stored volatiles as part of a broader resource allocation toward durable defense and long-lived leaves (high SLW, Table 1)[51].

      Among the MTS species, M. leptophylla represented the most extreme expression of this conservative strategy: it was an evergreen tree with the highest SLW (95.1 g·m−2) and the lowest leaf water content (59%) among all studied species (Table 1), reflecting dense leaf tissues optimized for long-term carbon retention and stress resistance. Its monoterpene profile was dominated by α-pinene and β-pinene, with minimal sesquiterpene diversity, suggesting a streamlined, constitutive chemical defense arsenal typical of shade-tolerant, slow-growing evergreens[52]. In contrast, C. illinoinensis produced a diverse array of sesquiterpenes (e.g., caryophyllene, germacrene D, and β-cadinene), which typically function in long-term defense due to their lower volatility and higher molecular stability[17]. L. chinense, while sharing the basic MTS profile, exhibited relatively higher light respiration rates (Table 2), suggesting a greater diversion of photosynthetic carbon to maintenance processes that might compete with de novo monoterpene synthesis.

      A notable specialization within the MTS syndrome was observed in C. axillaris, which emitted high levels of the light-dependent monoterpene β-ocimene (constituting 75% of its total monoterpenes). Unlike the stored monoterpenes typical of MTS species, β-ocimene biosynthesis relied on recently fixed photosynthetic carbon via the plastidal MEP pathway, and its synthase shared high sequence homology with isoprene synthase, suggesting a common evolutionary origin. Ecologically, β-ocimene acted as a herbivore-induced plant volatile (HIPV) that can directly activate plant defense, prime neighboring plants, attract natural enemies, and facilitate pollinator attraction[7,53,54]. Within the high-light, high-temperature canopy environment where C. axillaris thrived, rapid de novo synthesis of β-ocimene allowed for immediate stress signaling without requiring constitutive storage. Thus, C. axillaris represented an intermediate strategy within the MTS continuum: it retained the core 'conservative' leaf traits (high SLW, Table 1) and stored a monoterpene pool, but had evolved a light-triggered, rapidly inducible β-ocimene channel for dynamic ecological communication. This flexibility suggested that the ISO–MTS distinction represented endpoints along a continuum rather than a strict dichotomy, illustrating that volatile strategies were better understood as a spectrum shaped by species-specific niches and phylogenetic history.

      Additionally, certain sesquiterpenes were detected in both C. illinoinensis (e.g., caryophyllene, trans-α-bergamotene, [Z,Z]-α-farnesene, germacrene D, and β-cadinene) and C. axillaris (e.g., [E]-β-farnesene and caryophyllene), which typically functioned in long-term defense due to their higher molecular stability and lower volatility[17]. Recent breakthroughs further highlighted that sesquiterpenes like (−)-germacrene D were specifically perceived by the karrikin signaling receptor KAI2, triggering developmental cascades critical for reproductive organ maturation[55], implying unrecognized ecological functions of these emissions in our study species.

      Isoprene-dominant emitters (ISO: E. chrysantha, W. sinensis, O. hosiei) demonstrated high isoprene emission capacities, aligning with the 'Acquisitive-Overflow' syndrome[33,50]. This pattern was consistent with a strategy characterized by rapid carbon acquisition and growth, as reflected in their lower SLW and higher SLA (Table 1)[56]. Isoprene emission functioned as a real-time metabolic sink for excess photosynthetic energy, crucial for plants maintaining high metabolic flux[20,57]. The shared high isoprene emission in W. sinensis and O. hosiei suggested a phylogenetically conserved trait, consistent with observations that Fabaceae trees in subtropical regions frequently adopt isoprene emission-type strategies[7]. W. sinensis, as a liana, also exhibited relatively high emissions of GLVs, reflecting its biotic stress protection needs under high growth rates[30,58]. O. hosiei, as a semi-evergreen tree, retained some capacity for monoterpene emission, suggesting greater flexibility in chemical response to seasonal changes in temperature and herbivory pressure[34].

      E. chrysantha presents a specialized case, emitting almost exclusively isoprene with an elevated Jmax/Vcmax ratio, demonstrating that the ISO syndrome is not exclusive to Fabaceae. We acknowledge that two of the three ISO species belong to Fabaceae, whose high nitrogen fixation capacity could partly contribute to the observed physiological differences between ISO and MTS groups. However, the similar high-isoprene, high- Jmax/Vcmax traits in E. chrysantha suggest the acquisitive-overflow syndrome is not restricted to Fabaceae. Given the limited sample size (n = 7), we cannot fully disentangle phylogenetic effects from emission strategy; future studies with larger species sets and phylogenetic independent contrasts are needed. This point is further discussed in the context of the strategy continuum below.

      Critically, these divergent BVOC profiles are integral components of coherent functional syndromes[33,50,59]. MTS chemistry is embedded within a 'slow-return' strategy emphasizing preemptive investment in defense and structure, often accompanied by other costly, stored secondary metabolites (e.g., phenolics, alkaloids)[52,60]. In contrast, ISO chemistry was a hallmark of a 'fast-return' strategy that minimized fixed defense investment, favoring dynamic, energy-dependent protection and resulting in generally lower concentrations of other constitutive secondary metabolites[32,61]. Thus, BVOC chemotypes were robust indicators of a plant's fundamental position on the axis of resource acquisition vs. conservation.

      It should be noted that the monoterpene and sesquiterpene emission rates reported here, measured from excised branches, might overestimate constitutive baseline levels for species with pressurized storage structures due to potential release upon cutting. Nonetheless, while excision may influence absolute emission rates, the relative relationships remained robust between the MTS emission profile[62], representing a storage-based strategy, and its associated suite of conservative leaf traits[43]. These integrated relationships were consistent with the 'Conservative-Storage' syndrome as a coherent evolutionary strategy.

    • BVOC synthesis is intrinsically linked to photosynthetic carbon and energy metabolism. The MEP pathway, localized in chloroplasts, serves as a critical bridge between photosynthesis and isoprene/monoterpene formation, directly generating DMAPP and IPP, the precursors for isoprene and most monoterpenes[1,20,26,63].

      Our data revealed a fundamental dichotomy in this coupling between the two chemotypes. ISO species showed higher net assimilation rates than monoterpene emitters (Fig. 2), and isoprene emission correlated strongly with instantaneous photosynthetic rate (Fig. 4). This tight linkage indicated that isoprene synthesis likely acted as a real-time metabolic sink, directly dependent on substrates and energy (ATP, NADPH) derived from concurrent light reactions and carbon fixation[2,64]. Under high light, ISO species possessed high light saturation points that likely channeled excess photosynthetic electrons and carbon into the MEP pathway[2,8,50,65]. This process was widely proposed to function as an ‘overflow metabolism' that helped mitigate photodamage. Recent evidence suggested that the photoprotective effect was achieved primarily through the stabilization of chloroplast membranes under thermal and oxidative stress, rather than via direct ROS scavenging[21,66].

      In contrast, monoterpene emissions were weakly correlated with instantaneous photosynthetic rates. This decoupling stemmed from a distinct storage-based strategy[64]. Monoterpenes are often synthesized during periods of high photosynthetic activity and sequestered in specialized structures (e.g., resin ducts, glandular trichomes), with emission being induced later by external stimuli such as herbivory or mechanical damage, rather than by real-time photosynthetic flux[5,62]. This represented a 'pre-formed defense' strategy, prioritizing resource allocation to durable chemical pools over continuous, energy-intensive synthesis.

    • The divergence in BVOC emission strategies appeared to be largely associated with how plants manage photosynthetic electron flow and energy partitioning. ISO plants exhibited higher Jmax and elevated Jmax/Vcmax ratios compared to MTS-type emitters (Fig. 2). An increased Jmax reflected a greater capacity for light harvesting, whereas a higher Jmax/Vcmax ratio indicates that the capacity for light harvesting and electron transport (light reaction) could exceed the downstream demand for carbon fixation by the Calvin cycle (dark reactions), particularly under high light. This imbalance created a surplus of reducing equivalents (NADPH) and ATP[2,8,64].

      Our data strongly suggested that isoprene synthesis acted as a critical electron shunt under these conditions. The strong positive correlation between isoprene emission and Jmax (Fig. 4e), and its direct dependence on electron transport capacity suggested that isoprene biosynthesis might consume excess reductants through the MEP pathway, thereby mitigating electron overflow and protecting photosystems from photoinhibition[8,67,68].

      In contrast, monoterpene emitters showed lower Jmax/Vcmax ratios but higher light respiration rates (Rp, Table 2). This physiological profile indicated a strategy geared toward carbon conservation and efficient resource investment. Higher Rp suggested significant diversion of photosynthetic products into photorespiration and maintenance processes, which might compete with the MEP pathway for carbon skeletons and energy, limiting immediate de novo terpene synthesis[69]. This further explained the weaker link between monoterpene emission and instantaneous photosynthetic parameters (Fig. 4), emphasizing a reliance on mobilized storage rather than real-time production[5].

      Collectively, these findings supported the existence of two dominant adaptive syndromes linked to photosynthetic energy management. ISO-type plants prioritized rapid light capture and carbon assimilation, utilizing isoprene synthesis as a dynamic electron shunt to manage photosynthetic overflow and conferred immediate stress tolerance[32,68]. In contrast, the prevailing MTS-type strategy emphasized carbon economy and investment in storage-based defenses, uncoupling defense deployment from instantaneous metabolic flux to ensure persistent protection[5].

    • The ISO–MTS framework delineated dominant adaptive peaks in plant volatile strategies. However, the precise position of a species along this strategic continuum was shaped by the integration of its ecological context, phylogenetic history, and multifunctional traits. The cases of C. axillaris and E. chrysantha refined the simple dichotomy and demonstrated that these strategies represented a physiologically plastic spectrum of photosynthetic energy allocation and defense investment.

      C. axillaris, classified within the MTS group due to its high monoterpene proportion, exemplified a hybrid strategy. Unlike typical MTS emitters, it lacked typical storage structures and emitted high levels of β-ocimene, a monoterpene known for light-dependent de novo synthesis[5,70]. This photosynthetically coupled volatile production reflected a physiological linkage characteristic of the ISO syndrome, likely reflecting adaptation to its high-light, canopy-gap niche where rapid, inducible aerial signaling for pollinator attraction or indirect defense was advantageous[7,53]. Thus, C. axillaris occupied an intermediate position, blending storage-oriented defense with a photosynthetically coupled, rapid-response volatile channel.

      Conversely, E. chrysantha, a strong isoprene emitter representing the ISO type, exhibits a more nuanced energy allocation pattern. Despite possessing an acquisitive physiological base (high Jmax/Vcmax) conducive to channeling excess energy into isoprene, its concurrently high Rp, presence of glandular structures, and the accumulation of flavonoids suggest that a substantial portion of the excess energy is instead allocated to secondary metabolism and defense, rather than being fully committed to isoprene production[71]. These traits suggested significant resource partitioning toward photorespiratory maintenance and non-volatile chemical defenses. This pattern implied a strategic trade-off in which maximizing isoprene yield was secondary to maintaining a diversified defense portfolio, likely an adaptation to an ecological context where multiple abiotic and biotic stresses co-occur.

      These variations did not invalidate the core ISO–MTS framework but confirmed it as a physiologically plastic continuum. They highlighted that a plant's volatile emission strategy was an integrated component of its overall ecological strategy, subject to fine-tuning in response to habitat-specific selection pressures. Intra-group variations, such as the elevated Rp in L. chinense potentially limiting monoterpene synthesis, further illustrated the continuous nature of trait coordination within these broad syndromes.

    • The integrated 'structure–function–volatile' patterns observed in this study (Fig. 6) were not merely correlative but represent evolutionary adaptations shaped by long-term natural selection[50,72,73]. They arose from divergent solutions to the universal growth-defense trade-off, as conceptualized within the Leaf Economics Spectrum (LES), wherein plants optimized the allocation of finite resources[56,60,61].

      Figure 6. 

      Conceptual model of structure–function–volatile syndromes in subtropical woody species. Solid arrows indicate environmental drivers; dotted arrows indicate functional feedbacks; dashed box represent intermediate trait states; and solid boxes represent classical ISO/MTS emission traits. Abbreviations: ISO, isoprene-dominant; MTS, monoterpene-dominant; others defined in Tables 1 and 2.

    • BVOC chemotypes appeared to reflect core ecological strategies. ISO species (e.g., W. sinensis, E. chrysantha) aligned with the 'fast-return' end of the LES. Their traits, including low specific leaf weight (SLW), high specific leaf area (SLA, expressed as leaf area per unit dry weight), high Jmax, and high stomatal conductance, were hallmarks of a strategy prioritizing rapid carbon acquisition and high metabolic flux[50,56]. This 'acquisitive' resource allocation minimized investment in long-lived structural components like cell walls, allowing greater allocation to the photosynthetic apparatus[20,74]. Consequently, these plants frequently faced a transient excess of photosynthetic energy (high Jmax/Vcmax ratio). The real-time, energy-dependent synthesis of isoprene acted as a dynamic 'metabolic overflow valve', consuming excess reductants and providing immediate membrane stabilization and thermotolerance[21,32,66]. This strategy was metabolically costly but allowed for rapid growth and is likely underpinned by a physiological state where growth-promoting signals were predominant[61]. It represented a high-investment, high-reward strategy advantageous in environments with abundant light and water but fluctuating conditions (e.g., forest edges, gaps). Accordingly, ISO-type leaves typically contain lower concentrations of other costly, stored secondary metabolites (e.g., complex phenolics).

    • In contrast, MTS species align with the 'slow-return, conservative' end of the LES. Their high SLW, higher water-use efficiency (WUE), and lower Jmax/Vcmax ratio indicated substantial investment in durable leaf structures (e.g., thickened cell walls) and resource conservation[51]. This enhanced leaf longevity and stress resilience at the cost of maximum photosynthetic throughput. Within this framework, defense was achieved through pre-emptive investment in stored compounds in resource-limited or stable environments (e.g., forest understories). Monoterpenes were synthesized and sequestered in specialized structures (e.g., resin ducts), constituting a 'standing defense' pool[5]. This pool was often part of a broader defensive arsenal.

      In our study, typical MTS species like M. leptophylla and C. illinoinensis not only possessed secretory structures for monoterpene storage but also likely accumulated non-volatile defensive compounds such as phenolics, reflecting a comprehensive, capital-intensive investment in durable leaf defense and extended leaf lifespan. Their core function involved preferential carbon investment into structural/storage substances and the synergistic enhancement of physical and chemical defense. This strategy uncoupled defense readiness from instantaneous photosynthetic yield, minimizing metabolic opportunity costs. It suggests a physiological bias towards defense-signaling pathways[61] and was a bet-hedging strategy well-suited to stable, resource-limited, or herbivore-rich environments like forest understories. This suite of traits often co-occurred with other stored defenses (e.g., tannins, alkaloids), forming a diversified defense portfolio.

      It was noteworthy that our measurements of these stored volatiles were conducted on excised branches, a standard approach for comparative physiology. For species with pressurized secretory structures (e.g., resin ducts), excision might potentially lead to an overestimation of constitutive baseline emissions by releasing stored pools. However, this potential methodological effect did not undermine the core finding of strong integration between the MTS emission strategy (whether measured as stored capacity or induced release) and conservative leaf traits (e.g., high SLW). These correlations robustly reflected the long-term, 'slow-return' investment syndrome. Future in situ studies would be valuable to precisely quantify emission fluxes from intact plants in their natural context.

    • Therefore, the ISO–MTS divergence in BVOC emissions was a core component of broader, genetically correlated trait syndromes arising from adaptive optimization to different environmental selection pressures[60]. While our study established strong phenotypic integration, the direction of causality was best interpreted through an evolutionary lens. Habitats favoring rapid growth and high productivity selected for the integrated 'Acquisitive-Overflow' syndrome, where isoprene emission was a co-adapted trait for managing energy surplus. Conversely, habitats favoring persistence under chronic stress selected for the 'Conservative-Storage' syndrome, where volatile storage was part of a durable, pre-formed defense package. Thus, the observed correlations emerged from divergent evolutionary optima. This framework posited that the demonstrated physiological linkages (e.g., high Jmax driving isoprene synthesis) were the proximate mechanisms underlying ultimate evolutionary strategies shaped by environmental filtering. This provided a mechanistic, adaptive explanation for the diversity of plant volatile strategies and their embeddedness within the fundamental axes of plant ecological variation.

      The framework also generates testable hypotheses. For example, manipulating photosynthetic electron flow could test whether Jmax drives isoprene emission in ISO species (with negligible impact on stored pools in MTS species). Extending the framework to hyper-emitters and diverse biomes would clarify its generality. These are essential steps toward integrating functional traits into next-generation models.

    • While this study integrates BVOC emissions within the leaf economics and growth-defense trade-off framework, providing a mechanistic, trait-based understanding of plant volatile diversity, several limitations point to valuable future directions.

    • We acknowledge that the current study includes only seven species, which precluded rigorous phylogenetic independent contrasts (PIC) analysis. Consequently, we could not fully separate the effects of shared ancestry from adaptive convergence in the observed trait correlations. The ISO group includes two Fabaceae species and one Thymelaeaceae species (E. chrysantha), and the similar physiological traits among them might partly reflect phylogenetic relatedness rather than solely the isoprene emission strategy. Future studies with a larger and phylogenetically more diverse species set, ideally enabling PIC analysis, are needed to strengthen causal inference regarding ISO–MTS syndromes.

    • Our focused experimental design with seven subtropical species clearly delineated the core ISO and MTS syndromes, including intermediates such as C. axillaris. Future work should test this 'structure–function–volatile' framework across a wider taxonomic and functional range, including hyper-emitters (e.g., Populus, Quercus), temperate broadleaf trees (e.g., Fagus, Acer), tropical shrubs (e.g., Piper, Psychotria), herbaceous plants, and species from diverse biomes, to determine whether these syndromes represent universal adaptive peaks or are regionally filtered.

    • Measurements on excised branches under controlled conditions enabled precise physiological comparisons. To understand how these trait networks operate in natural settings, future in situ monitoring of intact plants is essential. This will reveal how whole-plant integration, diurnal cycles, and field conditions (e.g., drought, biotic interactions) modulate the proposed syndromes, thereby linking mechanisms to ecology.

    • This study provided a strong correlative framework. To establish causal links, manipulative experiments (e.g., 13C-labeling to trace carbon flux or genetic manipulation of isoprenoid synthases) are needed to test the functional role of specific volatiles within these strategies. Furthermore, the seasonal and phenological dynamics of these coordinated traits remain open questions. Investigating their responses to environmental manipulations (e.g., elevated CO2, warming, drought) would clarify the plasticity and stability of ISO and MTS strategies over time.

      Additionally, while our use of excised branches under controlled conditions enabled precise physiological comparisons, future in-situ measurements on intact plants would help validate whether the observed trait-emission relationships accurately reflect constitutive emission patterns, particularly for storage-type monoterpene emitters.

      Addressing these directions would refine the proposed framework and deepen the integration of plant ecophysiology with atmospheric science, ultimately improving predictions of ecosystem–climate feedbacks.

    • This study provides evidence that leaf structural traits, photosynthetic physiology, and BVOC emissions are intrinsically linked, forming coherent 'structure–function–volatile' syndromes in subtropical woody plants. Specifically, isoprene-dominant (ISO) species exhibited higher photosynthetic rates, greater electron transport capacity, and elevated Jmax/Vcmax ratios, consistent with isoprene synthesis functioning as a photosynthetic overflow mechanism for dissipating excess reductants. Conversely, monoterpene-dominant (MTS) species displayed higher specific leaf weight (SLW) and relied on stored emissions, reflecting a conservative, defense-oriented strategy aligned with the 'slow-return' end of the Leaf Economics Spectrum. Together, these findings demonstrate that BVOC chemotypes are not metabolically arbitrary but represent integrated evolutionary solutions to the universal growth–defense trade-off. Consequently, the proposed 'Acquisitive-Overflow' (ISO) and 'Conservative-Storage' (MTS) syndromes offer a trait-based framework for predicting volatile diversity from readily measurable plant functional traits. Future research extending this framework to hyper-emitters and diverse biomes will clarify its generality. By embedding BVOC emissions within the Leaf Economics Spectrum, this study bridges plant ecophysiology with atmospheric science, providing a physiological basis for next-generation models that forecast biosphere–atmosphere feedbacks under global change.

      • The authors confirm their contributions to the paper as follows: study conception and design: Sun Z, Zhou G; data collection: Mao Y, Yuan Y; analysis and interpretation of results: Sun Z, Mao Y, Yao H; draft manuscript preparation: Sun Z, Mao Y, Yao H, Yuan Y, Yu C, Wang M, Ding F. All authors reviewed the results and approved the final version of the manuscript.

      • The datasets generated during and/or analyzed during the current study are available from the corresponding author upon reasonable request.

      • We extend our sincere gratitude to Professor Chunyang Li for his invaluable guidance and support throughout this research. This research was funded by the Personnel Startup Project of the Scientific Research and Development Foundation of Liaocheng University (Grant No. 318042402), the National Natural Science Foundation of China (Grant No. 32071731), the Science and Technology Commonweal Project Fund of Zhejiang Province (Grant No. 2016C32018), and the Key Research and Development Program of Zhejiang Province (Grant No. 2021C02005).

      • The authors declare that they have no conflict of interest.

      • # Authors contributed equally: Yimiao Mao, Hang Yao

      • Copyright: © 2026 by the author(s). Published by Maximum Academic Press, Fayetteville, GA. This article is an open access article distributed under Creative Commons Attribution License (CC BY 4.0), visit https://creativecommons.org/licenses/by/4.0/.
    Figure (6)  Table (2) References (74)
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    Mao Y, Yao H, Yuan Y, Yu C, Wang M, et al. 2026. Divergence in isoprenoid emissions among subtropical broadleaf trees: linking photosynthesis, leaf economics, and volatile defense for forest management. Forestry Research 6: e024 doi: 10.48130/forres-0026-0023
    Mao Y, Yao H, Yuan Y, Yu C, Wang M, et al. 2026. Divergence in isoprenoid emissions among subtropical broadleaf trees: linking photosynthesis, leaf economics, and volatile defense for forest management. Forestry Research 6: e024 doi: 10.48130/forres-0026-0023

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