JXB Advance Access published online on September 4, 2007
Journal of Experimental Botany, doi:10.1093/jxb/erm177
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© 2007 The Author(s).
This is an Open Access article distributed under the terms of the Creative Commons Attribution Non-Commercial License (http://creativecommons.org/licenses/by-nc/2.0/uk/) which permits unrestricted non-commercial use, distribution, and reproduction in any medium, provided the original work is properly cited.This paper is available online free of all access charges (see http://jxb.oxfordjournals.org/open_access.html for further details)
RESEARCH PAPER |
The influence of temperature on within-canopy acclimation and variation in leaf photosynthesis: spatial acclimation to microclimate gradients among climatically divergent Acer rubrum L. genotypes
1Department of Horticulture and Landscape Architecture, Shepardson Building, Colorado State University, Fort Collins, CO 80523–1173, USA
2Department of Horticulture, Clemson University, Clemson, SC 29634-0319, USA
3Department of Forestry and Natural Resources, Clemson University, Clemson, SC, USA 29634-0317, USA
* To whom correspondence should be addressed. E-mail: bauerle{at}clemson.edu
Received 11 June 2007; Revised 21 June 2007 Accepted 9 July 2007
| Abstract |
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Leaf gas exchange and temperature response were measured to assess temperature acclimation within a tree canopy in climatically contrasting genotypes of Acer rubrum L. Over the course of two 50 d continuous periods, growth temperature was controlled within tree crowns and the steady-state rate of leaf gas exchange was measured. Data were then modelled to calculate the influence of genotype variation and vertical distribution of physiological activity on carbon uptake. The maximal rate of Rubisco carboxylation (Vcmax), the maximum rate of electron transport (Jmax), leaf dark respiration rate (Rd), maximum photosynthesis (Amax), and the CO2 compensation point (
) increased with temperature during both (i) a constant long-term (50 d) daytime temperature or (ii) ambient daytime temperature with short-term temperature control (25–38 °C). In addition, within-crown variation in the temperature response of photosynthesis and Rd was influenced by acclimation to local microclimate temperature gradients. Results indicated that carbon uptake estimates could be overestimated by 22–25% if the vertical distribution of temperature gradients is disregarded. Temperature is a major factor driving photosynthetic acclimation and within-crown gas exchange variation. Thus, this study established the importance of including spatial acclimation to temperature- and provenance-, ecotype-, and/or genotype-specific parameter sets into carbon uptake models. Key words: Global change, photosynthetic capacity, temperature acclimation, temperature response
| Introduction |
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Forest trees modify their canopy temperature and humidity microclimate along a vertical gradient. Zweifel et al. (2002) observed about a 1 °C temperature change and 5% humidity change approximately every 4 m from the upper to lower canopy over 22 m in a Picea abies L. forest. Moreover, Harley et al. (1996) observed that over a 12 m height gradient, large differences in temperature (
12 °C) were present in a 22 m mixed hardwood–conifer woodland representative of the eastern deciduous biome. In fact, it is not uncommon for trees in the maritime Pacific climate to exceed 65 m, which would expose their crowns to substantial vertical microclimate gradients that induce variation in canopy physiological responses (Ryan and Yoder, 1997; Bauerle et al., 1999; Cermak et al., 2007). In order to characterize the physiological adjustments to microclimate gradients correctly, there is a need to decipher the interactive effects of different crown environments while accounting for potential crown section physiological acclimation. Although it is well known that increases in ambient temperature cause enzymatic reaction rates to proceed more quickly, the size of tree crowns makes the manipulation of canopy temperature very difficult. Hence, only a few studies have looked at the variation in leaf physiology in response to temperature gradients within a canopy (Niinemets et al., 1999; Griffin et al., 2002). In general, researchers have hypothesized that foliar photosynthetic characteristics are modified by gradients in canopy light availability (Brooks et al., 1996; Bond et al., 1999; Niinemets et al., 1999, 2004). Unfortunately, this research is grounded mostly in correlative evidence. In fact, previous studies may not fully explain the mechanistic basis for responses in gas exchange variation because they did not control the atmospheric temperature.
Niinemets et al. (1999) were the first to study within-canopy variation in temperature. However, because an increase in height in the forest canopy is often accompanied by an increase in air temperature, irradiance, vapour pressure deficit (VPD), and wind speed (Kira and Yoda, 1989), it is hard to disentangle the concurrent changes in microclimate that contribute to the spatial variation in photosynthesis and respiration throughout a canopy. Due in part to the inability to separate microclimate variables along a canopy height gradient, there is little consensus about the mechanisms responsible for leaf photosynthetic and respiratory acclimation within canopies (Niinemets et al., 1999; Baldocchi et al., 2002; Frak et al., 2002; Kosugi and Matsuo, 2006). In addition, there is a paucity of studies that investigate intraspecific photosynthetic temperature response in climatically divergent forest trees (Medlyn et al., 2002a). Consequently, there is still a need to investigate temperature on a spatially explicit basis and to describe the vertical temperature acclimation response.
Recent studies show that growth temperature affects the temperature dependencies of Rubisco kinetics and activation state (Yamorie et al., 2005, 2006; Hikosaka et al., 2006; Weston et al., 2007). Therefore, the maintenance of a higher rate of Rubisco carboxylation (Vcmax) and/or the maximum rate of electron transport (Jmax) may play a key role in photosynthetic heat acclimation (Hikosaka et al., 2006). Moreover, the temperature response of each factor differs among species (Berry and Björkman, 1980; Ferrar et al., 1989; Hikosaka et al., 1999). For that reason, the aim was to characterize and understand the shift in the temperature dependence of photosynthesis that is a result of acclimation to growth temperature.
Here a crown section warming experiment that separates temperature from crown light interception, VPD, and wind within a crown is reported. Although there have been reports of adaptation in ecotypic and species-level photosynthesis and respiration (Berry and Björkman, 1980; Larigauderie and Körner, 1995), the primary objective was to quantify the spatial acclimation to temperature gradients. In addition to isolating the conditions that pertain to canopy position, the temperature dependence of photosynthetic capacity after leaf expansion was examined in two climatically contrasting genotypes of a common eastern biome continuously flushing species (Acer rubrum L.). In so doing, an attempt was made to address scaling assumptions regarding the variation between a big leaf model as opposed to a spatially explicit layered canopy model. This inquiry is needed to ascertain which model is more suitable to obtain reliable estimates of canopy flux in response to temperature and light (Sharkey et al., 1996).
The purpose of this study, therefore, was to mimic the relative natural crown daytime temperature gradient of tall trees (
13 °C) to (i) separate positional influence versus specific temperature effects; (ii) investigate the effect of short- versus long-term temperature manipulation; (iii) decipher the consequences of differences in temperature coefficients for various photosynthetic parameters on the calculated canopy carbon gain; and (iv) examine the carbon uptake estimate difference between a genotype-specific spatially explicit layered canopy model versus a big leaf model. Because experimental systems for regulating temperature are difficult to use on trees, the influence of temperature on photosynthetic capacity within the foliage of individual trees has never been decoupled from light under outdoor conditions. Thus, the present study asked whether growth temperature alone influences the photosynthetic temperature optimum within a canopy and whether within-species variation from climatically contrasting habitats can influence acclimation to elevated temperatures. The results are expanded on in the context of the net effect of the within-canopy distributed temperature response on total carbon exchange.
| Materials and methods |
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Plant material and study site layout
Measurements were carried out during the 2003 growing season in a 0.58 ha outdoor gravel pad of open terrain at the Clemson University Calhoun Field Laboratory in Clemson, SC, USA (latitude 34°40'8''; longitude 82°50'40''). A full description of the site is given in Bauerle et al. (2002). Two genotypes from thermally contrasting parentage were used for intensive sampling in this study: A. rubrum L. (red maple) cv October Glory (OG), native to Massachusetts (latitude 40°27'18''; longitude 74°29'3''), USA, and red maple cv Summer Red (SR), native to Georgia (latitude 31°27'27''; longitude 83°33'41''), USA. A row–column design was used, which resulted in two genotypes, two treatments (temperature-controlled and the mimic of ambient outdoor conditions), and four replicate trees per treatment and genotype with randomly assigned temperature profiles. Each genotype was processed in canopy bags over two separate 50 d periods. To ensure that the trees never experienced substrate water-limiting conditions, each tree was watered three times daily to container capacity with pressure-compensating micro emitters (ML Irrigation Inc., Laurens, SC, USA) and spaced 1.5 x 1.5 m. Substrate volumetric water content was monitored on a daily basis (Theta Probe type ML2, Delta-T Devices, Cambridge, UK) and root zone volumetric water content was maintained at 0.4–0.5 m3 m–3 in each 114 litre tree container.
Red maple, a continuous flushing species, developed at least one new fully expanded leaf per branch every 7 d during the experiment. Therefore, leaf measurements took place on leaves that developed under treatment conditions. To assess the extent to which long-term (50 continuous days of temperature control with leaf gas exchange measured on continuously developed fully expanded leaves) versus short-term (the same type of gas exchange measurement as long-term but temperature was controlled only for short durations by the leaf level gas exchange cuvette) temperature exposure influences photosynthetic and respiration responses, this study controlled the daytime growth temperature of whole crown sections. The crown sections without growth temperature control (run at ambient conditions) witnessed a mean growth temperature of 25 °C during the 2003 growing season.
Chamber construction and temperature control
Whole crown chambers were placed on four replicate trees per treatment. Crown chambers were subdivided by dividing each crown into three volumetrically equal area layers (Fig. 1). Each individual tree crown chamber, dimensions 1x1x2 m3, was constructed from 5 cm diameter polyvinyl chloride (PVC) tubing and covered with clear 0.025 mm Mylar® (DuPont, Wilmington, DE, USA). The Mylar® photon flux density (PFD) characteristics were checked with a spectroradiometer (model 1800, Li-Cor Inc., Lincoln, NE, USA). Results similar to Corelli and Magnanini (1993), were found where PFD was >90% of outside incident PFD, with mid-day levels exceeding 1800 µmol m–2 s–1, and the spectral composition was unchanged over the 400–900 nm range. To create the self-contained crown sections, horizontal sheets of Mylar® divided each crown layer and were secured to the trunk with foam rubber gaskets. Hence, each layer subchamber was plumbed independently to maintain growth temperature on an individual crown layer basis (Fig. 1). Three Twintemp® 16300/10700 BTU/h cooling and heating air conditioners (model ES16, Friedrich Inc., San Antonio, TX, USA) were plumbed to 12 Mylar® enclosed crown sections (three sections per crown) and together they continuously controlled temperature in each crown section (Fig. 1). Chamber temperatures were sampled at 10 s intervals with fine wire thermocouples (CR21X, Campbell Sci. Inc., Logan, UT, USA) and a control switch triggered the air conditioners to either heat, cool, or run at ambient temperature (fan only) to maintain the temperature within 1 °C of the set point. Crown section temperatures were assigned randomly per subchamber within each crown, where each crown had three different temperatures controlled at 25, 33, or 38 °C (Fig. 1). The airflow produced >3 volumes min–1 per layer and created a slight positive pressure on the Mylar®, which kept it in a wrinkle-free state for maximum light penetration. A preliminary experiment found the amount of air exchange more than adequate to ensure that CO2 levels did not deviate from outside ambient conditions. At night, temperature was returned to ambient in order to prevent variation in temperature acclimation of dark respiration (Turnbull et al., 2002).
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Calculation of leaf-intercepted radiation and optical characteristics
Photosynthetically active radiation (PAR) was estimated for each crown layer with a three-dimensional light absorption model validated on red maple (Bauerle and Bowden, 2004; Bauerle et al., 2004a). Crown spacing and leaf PAR absorption characteristics of the crown were set up to minimize lower crown shading, where PAR variation between the upper and lower crown position was <10%. Absorbed PAR was calculated by summing the crown subvolumes. Red maple leaf reflectance, transmittance, and absorption values were determined using the non-linear correlation equations of Bauerle et al. (2004b) by averaging five SPAD readings per leaf (Minolta SPAD 502 chlorophyll meter, Minolta Camera Co., Ramsey, NJ, USA). Under the outdoor experimental conditions, leaf PAR was light saturating for red maple at all canopy positions when incident radiation was >550 µmol m–2 s–1 (Bauerle et al., 2003).
Gas exchange measurements
From 27 May to 8 September 2003 (Julian days 147–251), leaf net photosynthesis (Anet) versus CO2 response curves (Anet–Ci curves, where Anet is net photosynthetic rate in µmol m–2 s–1 and Ci is the internal CO2 concentration expressed as the mol fraction of CO2) were measured. The measurements were conducted twice weekly on a 2 d time block. Gas exchange was measured using a portable steady-state gas exchange system (CIRAS-I, PP Systems, Amesbury, MA, USA) equipped with a light-, humidity-, and temperature-controlled cuvette [model PLC5 (B); PP Systems]. Measurements were made on the youngest fully expanded leaf at all three crown layers between 09.00 and 14.30 h. The leaves were tagged and, on any given day, measurements were taken in random order to compensate for any effects caused by time of sampling. At each crown layer, Anet–Ci response curves were constructed at saturating PFD (1200 µmol m–2 s–1). Measurements began at a cuvette CO2 concentration of 370 mmol mol–1 and were decreased as follows: 370, 175, 150, 100, and 50 µmol mol –1; after this sequence was completed, the cuvette CO2 was returned to 370 µmol mol –1 and sequentially increased at the following intervals: 600, 800, 1000, and 1200 µmol mol–1 to generate the Anet–Ci curves. Leaf temperatures were controlled at 25, 33, or 38 °C by the leaf level gas exchange cuvette, and VPD was controlled at 1.3±0.4 kPa at each target temperature by adjusting the water vapour inside the cuvette. It is also important to note that although it was possible to control cuvette VPD, crown section VPD co-varies with temperature. To prevent elevated crown section VPD values from influencing canopy gas exchange, VPD was kept below values that influence red maple stomatal conductance responses (<2.5 kPa) (Bauerle et al., 2004c). Also, it should be noted that red maple is not responsive to VPD changes below 2.5 kPa under well-watered conditions (WL Bauerle et al., unpublished results).
A total of 672 Anet–Ci curves were measured (336 for each genotype, 168 per long- or short-term temperature treatment, and 56 at each genotype long-term or short-term temperature treatment of 25, 33, and 38 °C). To estimate biochemical limitations to carbon assimilation from the curves, the methodology of Wullschleger (1993) was followed. Temperature response curves were constructed by changing the Peltier blocks in a manner similar to Weston et al. (2007), with an initial measurement at 25 °C and then stepwise increases in temperature to 42 °C. Specifically, leaf temperature within the cuvette was increased to 27, 30, 33, 36, 38, and finally to 42 °C. Data were fit to thermodynamic models (see below). For each curve, non-linear regression explained >91% of the variation in Anet–Ci data.
Temperature dependence of gas exchange parameters
To derive temperature dependencies of the Michaelis–Menten coefficient for CO2 (Kc: µmol mol–1), for O2 (Ko: µmol mol–1), the CO2 compensation point (
: µmol mol–1), dark respiration (Rd: µmol m–2 s–1), and the Rubisco specificity factor (
), the parameters were fit with the exponential function:
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Ha is the energy of activation. If a parameter decreased at elevated temperature, such as Vcmax, Jmax, and maximum photosynthesis (Amax), Equation (1) was modified to include entropy (
S) and energy of deactivation (
Hd) (Harley and Tenhunen, 1991; Harley et al., 1992):
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The temperature responses of different parameters were estimated using the secant method (NLIN Procedure, SAS Institute, 2004).
The optimal temperature (Topt) was computed from the above parameters by solving the equation as described in Medlyn et al. (2002b):
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S, the entropy term, is related to Topt by the expression:
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Temperature response parameter comparison
The temperature response of Vcmax from Equation (2) was compared with the Rubisco-limited photosynthesis calculation developed by Bernacchi et al. (2001):
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Leaf mass:area ratio, and total nitrogen
After each gas exchange measurement, the leaf was excised and measured for leaf area (LA) (LI-3000 Li-Cor, Inc., Lincoln, NE, USA) and fresh weight. The leaf was then dried (70 °C for 72 h) and weighed. Nitrogen concentration on a dry mass basis (NM) was determined with a LECO model FP528 nitrogen combustion analyser (LECO Corporation, St Joseph, MI, USA). Total leaf nitrogen was expressed per unit mass.
Modelled carbon uptake
Photosynthetic temperature response parameters were used to parameterize a carbon exchange model (MAESTRA). MAESTRA is an updated version of MAESTRO (Wang and Jarvis, 1990a) and is available on-line at www.bio.mq.edu.au/maestra/. The primary purpose of using MAESTRA in this study was to scale up to the crown and describe the effects of temperature acclimation gradients on carbon flux with depth in the canopy. MAESTRA's application in this study is grounded in the work of others where the model has been described in detail, validated, and used to estimate species-specific photosynthetic production; interested readers are referred to Wang and Jarvis (1990a, b), Kruijt et al. (1999), Luo et al. (2001), Medlyn (1998, 2004), and Bauerle et al. (2002, 2004a, 2006) for MAESTRA applications and detailed descriptions.
For this study, the model's three-dimensional spatially explicit nature was critical. MAESTRA simulated the spatial distribution of daily integrated leaf temperature within the crown, and the photosynthetic response of a target crown was dependent on the distribution of microclimate within the crown. To integrate PAR absorption over temporal and spatial distributions of irradiance, each crown layer was treated as unifacial and the assimilating leaf area was defined as one-sided. The positions and dimensions of the trees surrounding the target crown were used to calculate the sunlit and shaded fractions of leaf area after passing through the neighbouring tree canopies, where the canopy is represented by an array of ellipsoidal tree crowns. In the present study, the intercepted and absorbed radiation was calculated for each crown. The model was run in two different configurations. In the spatially explicit layered configuration, the crown of a tree was divided into three layers, resulting in 12 sectors of 30° with each layer forming 36 equal subvolumes. In the big leaf configuration, the spatial explicitness was removed and the properties of the whole canopy were mapped onto a single leaf (Sellers et al., 1996). Other than genotype-specific temperature response parameters listed in Tables 1, 2, and 4, model parameterization followed Bauerle et al. (2002). In a previous study, values of leaf PAR absorption simulated by the model were validated against fibre-optic micro-quantum sensors and line-quantum sensors (Bauerle and Bowden, 2004). The model was found to simulate adequately the spatial and temporal trends of crown microclimate gradients within deciduous red maple trees (Bauerle et al., 2004a).
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Another critical aspect of the model is the ability to parameterize in detail the physiological and genetic response on a genotype by genotype and crown layer basis (WL Bauerle et al., unpublished results). Thus, the sampling structure and measurements allowed each genotype's genetic difference to be described with genotype-specific parameters and control equations to predict the carbon uptake of each genotype. The response of a genotype to temperature was thus represented by spatially distributing the physiological temperature response along an upper, mid, and lower canopy vertical temperature distribution. All calculations were made on a 15 min time scale.
MAESTRA was used to calculate net daily carbon gain (Cdg; g d–1), which is a direct estimate of growth rate:
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Statistical analysis
For each photosynthetic parameter reported in Tables 1 and 2, a two-way analysis of variance (ANOVA; SPSS 14.01, SPSS Inc., Chicago, IL, USA) was performed as a 2x3 factorial with genotype and temperature as independent variables. Error terms were pooled and reported as standard error of the difference of the means. For each photosynthetic parameter reported in Table 3, a two-way ANOVA was performed to compare the long-term versus short-term acclimation responses with genotype and temperature as independent variables.
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| Results |
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General environmental conditions
Under cloud-free conditions, all crown sections received full sun >1800 µmol m–2 s–1 incident irradiance, a level well above the light saturation point of red maple (Bauerle et al., 2003). Under either overcast conditions or full sun, the PFD variation within a crown was <10% along the vertical gradient (minimal within-crown shading similar to open grown crowns).
Crown position versus microclimate temperature gradient within the crown
Independent effects of the canopy layer were not significant and, regardless of the crown position (top, middle, or bottom layer), long-term exposure to different daytime growth temperatures resulted in leaf acclimation to a specific temperature (25, 33, or 38 °C). With respect to long-term temperature, gas exchange parameters Jmax, Amax, and Rd had a significant temperature acclimation in both genotypes, whereas after 50 d of controlled growth temperature Vcmax only appeared to acclimate in the OG genotype (Table 1 versus 2). The significance of the acclimation responses becomes more pronounced as temperatures steadily increase above 25 °C (Table 1 versus 2), where Table 3 compares these acclimation percentage changes at the highest controlled temperature of 38 °C. The manipulation of crown section temperature did not result in a difference among photosynthetic characteristics at identical controlled temperatures among replicates; however, regardless of crown position, temperature had a significant effect on photosynthetic characteristics (Tables 1 and 2 with standard errors). The spatial influence of long- and short-term microclimate temperature gradients was shown to be a vertical gradient temperature factor rather than other microclimate variables that vary with canopy position. Variation in the calculated temperature-dependent parameters describing leaf photosynthetic and respiration responses are described in the short-term versus long-term temperature exposure section below, and values of temperature-dependent parameters of the leaf photosynthetic temperature response are reported in Table 4.
The influence of short-term versus long-term temperature manipulation on photosynthetic parameters
In all but one case, photosynthetic parameters derived from Anet–Ci response curves increased in response to temperature from 25 °C to 38 °C under conditions where the crown section temperature was only controlled during leaf gas exchange measurement (Table 1). Triose phosphate utilization (TPU), on the other hand, was relatively unchanged in response to this temperature alteration. In addition, the two genotypes did not present a significant difference in their response to the short time scale temperature change, nor did they have a significant alteration in their photosynthetic capacity up to 38 °C (Table 1). Furthermore, regardless of canopy position, the thermodynamic temperature response was similar in both genotypes. No differences in nitrogen concentration of leaves used for gas exchange measurements was found among genotypes, canopy position, or growth temperature, where the SR and OG genotype mean NM was 1368±19 µmol g–1 and 1333±17 µmol g–1 dry weight. In addition, leaf mass per LA was not different either where the SR and OG genotype mean was 0.06±0.003 g cm–2 and 0.07±0.004 g cm–2. Values of the temperature optimum for Vcmax, Jmax, and Amax, however, ranged from 1 °C to 5 °C lower for the OG as opposed to the SR genotype. The Vcmax
Ha was slightly higher in the OG genotype, whereas the
Ha values for Jmax and Amax were similar.
In contrast to values in ambient temperature growth conditions, photosynthetic parameters derived from Anet–Ci response curves after long-term exposure to various controlled temperature treatment conditions did change as a function of genotype (Table 2). Within the canopy, growth temperature had a different effect on the two genotypes. Whereas Amax, Vcmax, and
increased in response to temperature, Jmax and Rd not only increased, but acclimated to growth temperature (Table 3). This resulted in an overall decrease in Rd for both genotypes and a down-regulation of Jmax for OG and up-regulation for SR at both 33 °C and 38 °C. Among the two thermally contrasting genotype habitats, the genotype from the warmer environment (SR) up-regulated Jmax by 4% and 16.4%, and down-regulated Rd by 23% and 25% at 33 °C and 38 °C, respectively. In contrast, the genotype from the cooler climate (OG) decreased Jmax by 4.9% and 9.7% and Rd by 11.5% and 9.7% at 33 °C and 38 °C, respectively. In addition, Vcmax and Amax were relatively unchanged in comparison with short-term temperature-controlled leaves in the SR genotype, but were substantially down-regulated by 31.8% and 14.8 % in the OG genotype (Table 3). Another contrast among the genotypes was the Jmax:Vcmax ratio. Both genotypes had a change in the ratio of Jmax to Vcmax in response to growth temperature; however, the ratio shift was in the opposite direction (Tables 2, 3). At a long-term acclimation temperature of 38 °C, the SR genotype up-regulated Jmax, whereas the OG genotype value was lower when compared with short-term temperature-controlled leaves. Moreover, the long-term growth temperature was very significant in relation to the photosynthetic parameter values. Acclimation to long-term growth temperature resulted in a higher optimum temperature for Vcmax, Jmax, and Amax for the SR compared with the OG genotype (Table 4). Furthermore, the sensitivity to changes in temperature was more pronounced in the genotype from the cooler climate. The differences in temperature sensitivity can be seen in the estimated energy of the activation parameter (
Ha). Reactions with higher activation energy such as those observed in the OG genotype are more temperature sensitive compared with the SR genotype (Table 4). Values of kc, ko, and
, on the other hand, were similar to published values (Bernacchi et al., 2001).
Testing the temperature response against generalized temperature functions for predicting leaf level Rubisco- and RuBP-limited photosynthesis
In comparison with recent improvements in temperature response functions for models of Rubisco-limited and RuBP-limited photosynthesis, fairly good agreement was found between the observations of Vcmax at 25 °C and those of the improved Rubisco-limited Bernacchi et al. (2001) model (Table 5). However, at temperatures of 33 °C and 38 °C, the Bernacchi et al. (2001) model underestimated Vcmax by 33–57% in comparison with what was observed in the temperature response of the genotypes in this study. Similarly, regardless of the genotype, the Bernacchi et al. (2003) equations for predicting both temperature-acclimated (long-term) and non-acclimated (short-term) RuBP-limited photosynthesis performed well at 25 °C. However, at temperatures of 33 °C and 38 °C, the Bernacchi et al. (2003) model of short-term temperature-acclimated Jmax underestimated by 36–54% on the OG genotype and performed only slightly better on the SR genotype (36–38% underestimation). The long-term temperature-acclimated Jmax values were either over- or underpredicted, depending on temperature. In the case of the SR genotype, Jmax was overestimated by 14% at 33 °C and underpredicted by 25% at 38 °C. In the OG genotype, Jmax was underestimated by 32% and 28% at 33 °C and 38 °C, respectively.
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Comparison of carbon uptake estimate differences between a genotype-specific spatially explicit layered canopy model versus a big leaf model
First, regardless of model spatial explicitness, a clear difference was observed in the carbon uptake among climatically divergent genotypes of red maple (Figs 2, 3). Next, this inherent climate adaptation resulted in quite different modelled net carbon uptake of long-term (acclimated) temperature-controlled red maple canopies versus short-term (unacclimated) genotypes in response to elevated temperatures above 25 °C (Fig. 2 versus Fig. 3). At temperatures above 25 °C, the net carbon uptake distinctly separated, with the OG genotype curtailing carbon uptake at 38 °C in acclimated temperature conditions. Up to 38 °C, the SR genotype, however, did not appear to limit carbon uptake to the extent of the OG genotype. Figure 3 illustrates that short-term temperature-controlled leaves (unacclimated) responded to temperature increases; however, genotypes were similar in their temperature response. In fact, intraspecific differences within the species were not evident under the short-term temperature-controlled conditions (Fig. 3).
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Table 3 indicates that the difference between the two genotype carbon uptake responses to long-term elevated temperature was primarily attributed to three temperature-dependent physiological factors. The most significant factor was the Vcmax difference at both 33 °C and 38 °C, where the SR genotype Vcmax hardly changed but the OG carboxylation efficiency went down by 11.1% and 31.8% at 33 °C and 38 °C, respectvely. In addition, among the genotypes, elevated temperature had an opposite effect on Jmax. The SR genotype increased Jmax by 16.4% at 38 °C, but the OG electron transport rate declined by 9.7%. The combination of the Vcmax and Jmax changes also resulted in an altered Jmax/Vcmax ratio (Table 3). Lastly, regardless of genotype, Rd declined at elevated temperature; however, the SR genotype had 15.3% less of a Rd decrease than the OG at 38 °C (Table 3).
The differences in the temperature responses of the two modelling approaches (spatially explicit layered canopy model versus a big leaf model) are illustrated in each panel of Figs 2 and 3. If all the leaves in the canopy are assumed to have a constant physiological response as in a big leaf model, the prediction would overestimate the net carbon uptake at temperatures above 25 °C, regardless of whether the leaves were acclimated to canopy microclimate gradients or not (Figs 2, 3). In fact, the variation among the two modelling approaches increased as the temperature increased beyond 25 °C in both long- and short-term temperature-controlled leaves. For genotype OG, there was a 24% short-term and 22% long-term difference between the big leaf versus spatially explicit layered canopy model estimate at 38 °C. For SR, the results were similar, where there was a 24% and 25% difference between the two modelling methods at 38 °C, respectively. Thus, as temperature increased above 25 °C, there was in increase in the divergence among the two carbon uptake modelling approaches (Figs 2, 3).
| Discussion |
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Elevated global temperatures raised numerous concerns regarding ecosystem function and the influence on carbon exchange (IPCC, 2007). Trees comprise the majority of the carbon-sequestering biomass in terrestrial ecosystems; thus their responses to environment and climate change are a key determinant of global net primary production and carbon sequestration (Valentini et al., 2000; Barford et al., 2001; Breshears et al., 2005). Concern about the gradual rise in atmospheric temperature, predicted to range from 1 °C to 7 °C by 2100, has brought about several temperature-related studies that investigate the physiological responses of trees (Roden and Ball, 1996; Teskey and Will, 1999; Medlyn et al., 2002a; Haldimann and Feller, 2004). Although it is widely known that photosynthesis is affected by temperature on a short-term basis, the direct relationship between temperature and global forest productivity requires an understanding of long-term acclimatory photosynthetic responses that help explain variation in forest carbon exchange across climates and within canopies—two spatial temperature entities that are likely to diverge.
Because of the high autocorrelation between light and temperature along a canopy height gradient, it is very difficult to ascertain whether the decrease in photosynthetic response at lower heights is due to light or temperature acclimation. Recently, however, Zhang et al. (2006) found that temperature was the dominant factor controlling seasonal variation in ecosystem apparent quantum yield and maximum photosynthetic rates in a temperate mixed forest. Zhang et al. (2006) also found that ecosystem respiration of a temperate mixed forest is more sensitive to temperature than that of either a subtropical evergreen coniferous plantation or a subtropical evergreen broad-leaved forest. Our findings on one of the most abundant and widely distributed forest tree species in eastern North America (Hutnick and Yawney, 1961) support the hypothesis that temperature gradients within a canopy drive physiological acclimation of leaf photosynthetic capacity. Even though temperature was not controlled in an independent study by Mäkelä et al. (2004), they too found temperature to affect seasonal changes in photosynthetic capacity. Alternatively, Rayment et al. (2002) found a difference between Jmax values at the upper versus lower canopy of Picea mariana (Mill.) B.S.P.; however, that study did not attribute the large seasonal variation in Vcmax and Jmax to temperature (Vcmax and Jmax) or microclimate (Vcmax). Thus, the relative importance of leaf temperature on photosynthetic acclimation within plant canopies has not arrived at a consensus, probably due to the major challenge of controlling tree crown temperature under outdoor conditions.
It is particularly noteworthy that the present experiment specifically manipulated the temperature of whole crown sections while attempting to minimize variation in other microclimate variables. Since there has been an absence of studies that have been conducted across a controlled canopy temperature gradient, it allowed investigation of an unknown—namely if temperature microclimates within a canopy influence photosynthetic parameters due to acclimation. The current analyses of the temperature response of both photosynthetic and respiratory characteristics indicate that crown sections do indeed acclimate to temperature. Furthermore, the results demonstrate that the temperature-dependent variation in the acclimation of photosynthetic parameters can occur along a height (temperature) gradient, implying that the forest canopy has a response gradient that influences local carbon gain from the upper to lower canopy position. As a result, the variation in photosynthesis and respiration responses along temperature gradients within a canopy need to be accounted for in canopy and ecosystem-level flux models—especially in tall trees.
In most plants, the activation energy of Vcmax increases with growth temperature (Hikosaka et al., 2006). In addition, photosynthetic performance at elevated temperature is largely a function of Rubisco kinetics and the Rubisco activation state (Yamori et al., 2006; Weston et al., 2007). A mechanistic response to temperature was observed, where the activation energy of Vcmax and Jmax increased with growth temperature from 25 °C to 38 °C. The response is consistent with the changes in temperature dependence of the photosynthetic rate due to elevated growth temperature (Yamori et al., 2005, 2006; Hikosaka et al., 2006). In fact, the optimum temperature for growth can shift towards a higher temperature (Yamori et al., 2005). That was found to be the case for the SR genotype but not for the OG genotype, where four temperature-dependent physiological factors diverged among genotypes. In response to temperature, the Vcmax was significantly reduced in the OG genotype, whereas the SR genotype tolerated the elevated temperature by not changing its carboxylation efficiency. With respect to Jmax under acclimated elevated temperature, the genotypes diverged in the opposite direction. The divergence could explain some of the difference in carbon exchange at elevated temperature. For instance, Wilson et al. (2001) showed that neglecting seasonal changes in Jmax and Vcmax could lead to overestimation of net ecosystem carbon exchange. The present findings support this observation and strengthen the need to examine Jmax and Vcmax on both a seasonal and growth temperature basis. Thirdly, the Rd values were lower at elevated growth temperature. It has been shown that respiration is a main determinant of carbon balance in forests (Valentini et al., 2000). Consequently, the 11.5% and 15.3% variation in Rd at 33 °C and 38 °C could help explain why the SR genotype was capable of storing more carbon compared with the OG genotype. Together, these factors suggest that temperature acclimation is dependent on the thermal conditions of the native climate.
Extrapolating carbon dioxide and water vapour flux exchange from the leaf to the canopy can take one of two common paths: the one-layered big leaf or the multilayered spatially explicit modelling approach. The big leaf approach maps properties of the whole canopy onto a single leaf (Sellers et al., 1996) and the multilayered type model integrates the fluxes from each layer (Wang and Jarvis, 1990a). Due to the nature of non-linearity parameterization, the big leaf methodology cannot define the arithmetic mean of leaf-level parameters (McNaughton, 1994; Wang et al., 2001). The multilayered models, on the other hand, can use parameters that are measured and validated at the leaf level. The big leaf model prediction was found to overestimate the net carbon uptake at temperatures above 25 °C, regardless of whether the leaves were acclimated to canopy microclimate gradients or not. Comparatively, the multilayered spatially explicit model was capable of integrating the fluxes through the various temperatures of a canopy by compensating for the non-linear photosynthetic response to temperature. The outcome was a 22–25% lower estimate in the multilayered spatially explicit model due to the arithmetic mean of leaf-level temperature response parameters.
The short-term contribution of the present study is the potential improvement of both spatial and genetic parameterization for scaling carbon uptake estimates to canopies of temperate deciduous forests. In addition, the results are noteworthy because long-term temperature acclimation has not been studied in many commonly widespread species that occur across a continental temperature gradient (Bolstad et al., 2003). It was observed that even though photosynthesis parameters can change due to the temperature effect on enzymatic reactions, these parameters can also down-regulate at long-term daytime temperature exposure above 33 °C. Moreover, the results suggest that there is adaptive variation in the acclimation response along the disparate climatic gradient represented by the red maple genotypes and thus one should not generalize across species with wide climatic distributions in carbon flux modelling. Unlike others who did not control temperature within the crown and speculate acclimation to irradiance (Han et al., 2004) or who made measurements on detached shoots (Medlyn et al., 2002a), the present study accounted for long-term temperature acclimation and leaves were measured in situ. If, as is suggested, acclimation of photosynthetic parameters to temperature does not support the assumption that temperature responses are universally similar within a woody plant species, further knowledge of the mechanisms responsible for temperature acclimation would be useful for modelling carbon uptake under a range of microclimate conditions and provenance, ecotype, and/or genotypes.
Due to the fact that all carbon gain models use a temperature response function, it is imperative that inter- and intraspecific acclimatory temperature dependencies be parameterized correctly. Models that only incorporate a single temperature response curve for all leaves in a canopy may cause significant errors in model estimates of carbon exchange. Recently, Bernacchi et al. (2001, 2003) have attempted to re-parameterize temperature responses of Vcmax and Jmax to improve modelling estimates. Their temperature functions were derived from a transformed line of wild-type tobacco (Nicotiana tobaccum L. cv. W38) operating under the assumption that it would predict well across terrestrial C3 systems. The present comparison of predicted versus actual responses indicates that this is not the case, where the influence of temperature acclimation on enzyme activity and the respective influence on photosynthetic parameters differed substantially. Thus, the development of a mechanistic understanding of these responses is still a major challenge to pursue if we hope to quantify accurately the interactions among temperature, physiological genetics, and ecosystem function.
Controlled environment chambers are useful for developing hypotheses; however, the present findings should still be tested in natural ecosystems. Although the experimental protocol was sufficient to allow investigation of the temperature response, the 13 °C growth temperature range would not be common in the size of trees in this study. The results, on the other hand, should be directly applicable to forest crowns
50 m and, in part, relevant to temperature gradients in all forest crowns. The results of this study may also apply to shifts in seasonal climate, as temperature in forest canopies varies not only vertically but also daily, seasonally, and annually (Harley et al., 1996; Singsaas et al., 1999; Zweifel et al., 2002). In addition, the results indicate the importance of explicitly considering the spatial variation in leaf physiology within a canopy and that this spatially explicit description of canopy physiology can produce a substantially different predicted outcome when compared with a big leaf approach. Clearly, the implications of the present findings identify a weakness in current predictions of how changes in climate may affect carbon storage and release in deciduous forests worldwide and should be the subject of further experimentation.
| Acknowledgements |
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The authors are grateful to MF McLeod and A Hauseman for their dedicated help in instrumentation construction, and to G Wiggin for help in obtaining the various field data. We thank Professors J Toler and L Grimes for their experimental statistical advice, EM Poulin for measurement assistance and editorial comments, and Professors RO Teskey and MW van Iersel for helpful comments on previous drafts of this manuscript. This work was partially funded by the Tree Fund, USDA Specialty Crops Program, and the South Carolina Experiment Station project number SC-1700208.
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Baldocchi DD, Wilson KB, Gu L. How the environment, canopy structure and canopy physiological functioning influence carbon, water and energy fluxes of a temperate broad-leaved deciduous forest—an assessment of the biophysical model CANOAK. Tree Physiology (2002) 22:1065–1077.[ISI][Medline]
Barford CC, Wofsy SC, Goulden ML, Munger JW, Pyle EH, Urbanski SP, Hutyra L, Saleska SR, Fitzjarrald D, Moore K. Factors controlling long- and short-term sequestration of atmospheric CO2 in a mid-latitude forest. Science (2001) 294:1688–1691.
Bauerle WL, Bowden JD. A fiber-optic-based system for integrating photosynthetically active radiation in plant canopies. HortScience (2004) 39:1027–1029.
Bauerle WL, Bowden JD, McLeod MF, Toler JE. Modeling intra-crown and intra-canopy interactions in red maple: assessment of light transfer on carbon dioxide and water vapor exchange. Tree Physiology (2004a) 24:589–597.[ISI][Medline]
Bauerle WL, Hinckley TM, Cermak J, Kucera J, Bible K. The canopy water relations of old growth Douglas-fir trees. Trees Structure and Function (1999) 13:211–217.[ISI]
Bauerle WL, Post CJ, McLeod MF, Dudley JB, Toler JE. Measurement and modeling of the transpiration of a temperate red maple container nursery. Agricultural and Forest Meteorology (2002) 114:45–57.[CrossRef][ISI]
Bauerle WL, Timlin DJ, Pachepsky Ya A, Anantharamu S. Adaptation of the biological simulation model MAESTRA for use in a generic user interface. Agronomy Journal (2006) 98:220–228.
Bauerle WL, Weston DJ, Bowden JD, Dudley JB, Toler JE. Leaf absorptance of photosynthetically active radiation in relation to chlorophyll meter estimates among woody plant species. Scientia Horticulturae (2004b) 101:169–178.[CrossRef]
Bauerle WL, Whitlow TH, Setter TL, Bauerle TL, Vermeylen FM. Ecophysiology of Acer rubrum L. seedlings from contrasting hydrologic habitats: growth, gas exchange, tissue water relations, abscisic acid, and carbon isotope discrimination. Tree Physiology (2003) 23:841–850.[ISI][Medline]
Bauerle WL, Whitlow TH, Setter TL, Vermeylen FM. Abscisic acid synthesis in Acer rubrum L. leaves—a vapor pressure deficit mediated response. Journal of the American Society for Horticulture Science (2004c) 129:182–187.
Bernacchi CJ, Pimentel C, Long SP. In vivo temperature response functions of parameters required to model RuBP-limited photosynthesis. Plant, Cell and Environment (2003) 26:1419–1430.[CrossRef]
Bernacchi CJ, Singsass EL, Pimentel C, Portis AR, Long SP. Improved temperature response functions for models of Rubisco-limited photosynthesis. Plant, Cell and Environment (2001) 24:253–259.[CrossRef]
Berry J, Björkman O. Photosynthetic response and adaptation to temperature in higher plants. Annual Review of Plant Physiology (1980) 31:491–543.[ISI]
Bolstad PV, Reich P, Lee T. Rapid temperature acclimation of leaf respiration rates in Quercus alba and Quercus rubra. Tree Physiology (2003) 23:969–976.[ISI][Medline]
Bond BJ, Farnsworth BT, Coulombe RA, Winner WE. Foliage physiology and biochemistry in response to radiation gradients in conifers with varying shade tolerance. Oecologia (1999) 119:183–192.[CrossRef][ISI]
Breshears DD, Cobb NS, Rich PM, et al. Regional vegetation die-off in response to global-change-type drought. Proceedings of the National Academy of Sciences, USA (2005) 102:15144–15148.
Brooks JR, Sprugel DG, Hinckley TM. The effects of light acclimation during and after foliage expansion on photosynthesis of Abies amabilis foliage within the canopy. Oecologia (1996) 107:21–32.[CrossRef][ISI]
Cermak J, Kucera J, Bauerle WL, Phillips N, Hinckley TM. Tree water storage and its diurnal dynamics related to sap flow and changes of stem volume in old-growth Douglas-fir trees. Tree Physiology (2007) 27:181–198.[ISI][Medline]
Corelligrappadelli L, Magnanini E. A whole tree system for gas exchange studies. HortScience (1993) 28:41–45.
Ferrar PJ, Slayter RO, Vranjic JA. Photosynthetic temperature acclimation in Eucalyptus species from diverse habitats and a comparison with Nerium oleander. Australian Journal of Plant Physiology (1989) 16:199–217.[ISI]
Frak E, Roux XL, Millard P, Adam B, Dreyer W, Escuit C, Sinoquet H, Vandame M, Varlet-Grancher C. Spatial distribution of leaf nitrogen and photosynthetic capacity within the foliage of individual trees: disentangling the effects of local light quality, leaf irradiance, and transpiration. Journal of Experimental Botany (2002) 53:2207–2216.
Griffin KL, Turnbull M, Murthy R. Canopy position affects the temperature response of leaf respiration in Populus deltoides. New Phytologist (2002) 154:609–619.[CrossRef][ISI]
Haldimann P, Feller U. Inhibition of photosynthesis by high temperature in oak (Quercus pubescens L.) leaves grown under natural conditions closely correlates with a reversible heat-dependent reduction of the activation state of ribulose-1,5-bisphosphate carboxylase/oxygenase. Plant, Cell and Environment (2004) 27:1169–1183.[CrossRef]
Han Q, Kawasaki T, Katahara S, Mukai Y, Chiba Y. Horizontal and vertical variations in photosynthetic capacity in a Pinus densiflora crown in relation to leaf nitrogen allocation and acclimation to irradiance. Tree Physiology (2003) 23:851–857.[ISI][Medline]
Han Q, Kawasaki T, Nakano T, Chiba T. Spatial and seasonal variability of temperature responses of biochemical photosynthesis parameters and leaf nitrogen content within a Pinus densiflora crown. Tree Physiology (2004) 24:737–744.[ISI][Medline]
Harley P, Guenther A, Zimmerman P. Effects of light, temperature and canopy position on net photosynthesis and isoprene emission from sweetgum (Liquidambar styraciflua) leaves. Tree Physiology (1996) 16:25–32.[ISI][Medline]
Harley PC, Sharkey TD. An improved model of C3 photosynthesis at high CO2: reversed O2 sensitivity explained by lack of glycerate re-entry into the chloroplast. Photosynthesis Research (1991) 27:169–178.[ISI]
Harley PC, Tenhunen JD. Modeling the photosynthetic response of C3 leaves to environmental factors. In: Modeling crop photosynthesis—From biochemistry to canopy—Boote KJ, Loomis RS, eds. (1991) Madison, WI: Crop Science Society of America. 17–39.
Harley PC, Thomas RB, Reynolds JF, Strain BR. Modelling photosynthesis of cotton grown in elevated CO2. Plant, Cell and Environment (1992) 15:271–282.[CrossRef]
Hikosaka K, Ishikawa K, Borjigidai A, Muller O, Onoda Y. Temperature acclimation of photosynthesis: mechanisms involved in the changes in temperature dependence of photosynthetic rate. Journal of Experimental Botany (2006) 57:291–302.
Hikosaka K, Murakami A, Hirose T. Balancing carboxylation and regeneration of ribulose-1,5-bisphosphate in leaf photosynthesis in temperature acclimation of an evergreen tree, Quercus myrsinaefolia. Plant, Cell and Environment (1999) 22:841–849.[CrossRef]
Hutnick RJ, Yawney HW. Silvical characteristics of red maple (Acer rubrum). In: USDA Forest Service Station Paper 142 (1961) Upper Darby, PA: Northeastern Forest Experiment Station.
IPCC. Fourth assessment report of Working Group I (2007) Geneva, Switzerland: United Nations Environmental Program.
Kira T, Yoda K. Vertical stratification in microclimate. In: Ecosystems of the world 14b. Tropical rain forest ecosystems—Leith H, Werger MJA, eds. (1989) Amsterdam, The Netherlands: Elsevier. 55–72.
Kosugi Y, Matsuo N. Seasonal fluctuations and temperature dependence of leaf gas exchange parameters of co-occurring evergreen and deciduous trees in a temperate broad-leaved forest. Tree Physiology (2006) 26:1173–1184.[ISI][Medline]
Kruijt B, Barton CVM, Rey A, Jarvis PG. The sensitivity of stand-scale photosynthesis and transpiration to changes in atmospheric CO2 concentration and climate. Hydrology and Earth System Science (1999) 3:55–69.
Larigauderie A, Korner C. Acclimation of leaf dark respiration to temperature in alpine and lowland plant species. Annals of Botany (1995) 76:245–252.
Luo Y, Medlyn B, Hui D, Ellsworth D, Reynolds J, Katul G. Gross primary productivity in Duke Forest: modeling synthesis of CO2 experiment and eddy-flux data. Ecological Applications (2001) 11:239–252.[ISI]
Mäkelä A, Hari P, Berninger F, Hänninen H, Nikinmaa E. Acclimation of photosynthetic capacity in Scots pine to the annual cycle of temperature. Tree Physiology (2004) 24:369–376.[ISI][Medline]
McNaughton KG. Effective stomatal and boundary resistances of heterogeneous surfaces. Plant, Cell and Environment (1994) 17:1061–1068.[CrossRef]
Medlyn BE. Physiological basis of the light use efficiency model. Tree Physiology (1998) 18:167–176.[ISI][Medline]
Medlyn BE. A MAESTRO retrospective. In: Forests at the land–atmosphere interface—Mencuccini M, Grace J, Moncrieff J, McNaughton KG, eds. (2004) Wallingford, UK: CABI. 105–122.
Medlyn BE, Dreyer E, Ellsworth D, et al. Temperature response of parameters of a biochemically based model of photosynthesis. II. A review of experimental data. Plant, Cell and Environment (2002b) 25:1167–1179.[CrossRef]
Medlyn BE, Loustau D, Delzon S. Temperature response of parameters of a biochemically based model of photosynthesis. I. Seasonal changes in mature maritime pine (Pinus pinaster Ait. Plant, Cell and Environment (2002a) 25:1155–1165.[CrossRef]
Niinemets U, Kull O, Tenhunen JD. Within-canopy variation in the rate of development of photosynthetic capacity is proportional to integrated quantum flux density in temperate deciduous trees. Plant, Cell and Environment (2004) 27:293–313.[CrossRef]
Niinemets U, Oja V, Kull O. Shape of the leaf photosynthetic electron transport versus temperature response curve is not constant along canopy light gradients in temperate deciduous trees. Plant, Cell and Environment (1999) 22:1497–1513.[CrossRef]
Rayment MB, Loustau D, Jarvis PG. Photosynthesis and respiration of black spruce at three organizational scales: shoot, branch and canopy. Tree Physiology (2002) 22:219–229.[ISI][Medline]
Roden JS, Ball MC. The effects of elevated CO2 on growth and photosynthesis of two Eucalyptus species exposed to high temperatures and water deficits. Plant Physiology (1996) 111:909–919.[Abstract]
Ryan RG, Yoder BJ. Hydraulic limits to tree height and tree growth. Bioscience (1997) 47:235–242.[CrossRef][ISI]
Sharkey TD, Singsaas EL, Vanderveer PJ, Geron CD. Field measurements of isoprene emission from trees in response to temperature and light. Tree Physiology (1996) 16:649–654.[ISI][Medline]
Sellers PJ, Randall DA, Collatz GJ, Berry JA, Field CB, Dazlich DA, Zhang C, Collelo GD, Bounoua L. A revised land surface parameterization (SiB2) for atmospheric GCMs. Part I. Model formulation. Journal of Climate (1996) 9:676R


