Conifers, Angiosperm Trees, and Lianas: Growth, Whole-Plant Water and Nitrogen Use Efficiency, and Stable Isotope Composition (d13C and d18O) of Seedlings Grown in a Tropical Environment1[W][OA] Lucas A. Cernusak2*, Klaus Winter, Jorge Aranda, and Benjamin L. Turner Smithsonian Tropical Research Institute, Balboa, Ancon, Republic of Panama Seedlings of several species of gymnosperm trees, angiosperm trees, and angiosperm lianas were grown under tropical field conditions in the Republic of Panama; physiological processes controlling plant C and water fluxes were assessed across this functionally diverse range of species. Relative growth rate, r, was primarily controlled by the ratio of leaf area to plant mass, of which specific leaf area was a key component. Instantaneous photosynthesis, when expressed on a leaf-mass basis, explained 69% of variation in r (P, 0.0001, n5 94). Mean r of angiosperms was significantly higher than that of the gymnosperms; within angiosperms, mean r of lianas was higher than that of trees. Whole-plant nitrogen use efficiency was also significantly higher in angiosperm than in gymnosperm species, and was primarily controlled by the rate of photosynthesis for a given amount of leaf nitrogen. Whole-plant water use efficiency, TEc, varied significantly among species, and was primarily controlled by ci/ca, the ratio of intercellular to ambient CO2 partial pressures during photosynthesis. Instantaneous measurements of ci/ca explained 51% of variation in TEc (P , 0.0001, n 5 94). Whole-plant 13C discrimination also varied significantly as a function of ci/ca (R 2 5 0.57, P , 0.0001, n 5 94), and was, accordingly, a good predictor of TEc. The 18O enrichment of stem dry matter was primarily controlled by the predicted 18O enrichment of evaporative sites within leaves (R2 5 0.61, P , 0.0001, n 5 94), with some residual variation explained by mean transpiration rate. Measurements of carbon and oxygen stable isotope ratios could provide a useful means of parameterizing physiological models of tropical forest trees. Tropical forest ecosystems have been subject to ex- tensive perturbations associated with anthropogenic activity in recent decades, and such perturbations will likely continue into the foreseeable future (Laurance et al., 2004; Wright, 2005). Effective environmental management requires knowledge of how such pertur- bations impact upon cycling of carbon (C) and water between forest trees and the atmosphere, and how these C and water fluxes relate to plant nutrient status. A sound, mechanistic understanding of the physio- logical processes that control photosynthesis and tran- spiration in tropical trees is therefore essential for understanding and managing the human impact upon tropical forests. In this study, we analyzed the phys- iological controls over growth (the relative rate of C accumulation), nitrogen (N) use efficiency (NUE; the rate of C accumulation for a given N content), water use efficiency (the ratio of whole-plant C gain to water loss), and stable isotope composition (d13C and d18O) in seedlings of a diverse suite of species grown side- by-side in a tropical environment. Conifers dominated the world?s forests prior to the Cretaceous radiation in angiosperm diversity. How- ever, conifers are largely absent from the lowland tropical and subtropical forests of today. It has been suggested that one means by which angiosperm tree species are able to out-compete gymnosperm tree species in tropical environments is through faster seedling growth caused by improved hydraulic effi- ciency (Bond, 1989; Brodribb et al., 2005). Angiosperm xylem tissue contains vessels, specialized water- conducting cells that are generally larger in diameter, and therefore more conductive to water, than conifer tracheids (Sperry et al., 2006). Conifer tracheid diame- ters are biomechanically constrained because these cells must perform the dual function of conducting water and providing structural support to woody tissues, whereas vessels need not perform the latter function in angiosperm wood. Lianas are large woody vines that occur predominantly in tropical forests; by attaching themselves to neighboring trees, they have evolved an additional means of freeing their xylem tissues from structural constraints. Thus, angiosperm lianas may achieve further increases in hydraulic efficiency com- pared to angiosperm trees (Gartner et al., 1990). 1 This work was supported by the Smithsonian Tropical Research Institute. L.A.C. was supported by a postdoctoral fellowship from the Smithsonian Institution and a Tupper Research Fellowship from the Smithsonian Tropical Research Institute. 2 Present address: School of Environmental and Life Sciences, Charles Darwin University, Darwin, Northern Territory 0909, Australia. * Corresponding author; e-mail lucas.cernusak@cdu.edu.au. The author responsible for distribution of materials integral to the findings presented in this article in accordancewith the policy described in the Instructions for Authors (www.plantphysiol.org) is: Lucas A. Cernusak (lucas.cernusak@cdu.edu.au). [W] The online version of this article contains Web-only data. [OA] OpenAccess article can be viewed onlinewithout a subscription. www.plantphysiol.org/cgi/doi/10.1104/pp.108.123521 642 Plant Physiology, September 2008, Vol. 148, pp. 642?659, www.plantphysiol.org  2008 American Society of Plant Biologists In this study, we grew seedlings of several species of gymnosperm trees, angiosperm trees, and angiosperm lianas in a tropical environment. We used this func- tionally diverse range of species to quantify the phys- iological controls over their C and water fluxes. We also took advantage of the contrasting physiology of the study species to test the theoretical basis for var- iation in the C and oxygen (O) stable isotope compo- sition of plant dry matter. THEORY Growth Following Masle and Farquhar (1988), and based on earlier treatments (Blackman, 1919; Evans, 1972), we write the following expression to describe factors that influence the relative rate of C accumulation of a plant: r5 1 mc  dmc dt 5 Al?1 2fc? r ?1? where r is relative growth rate (mol C mol21 C s21), mc is plant C mass (mol C), t is time (s), A is leaf pho- tosynthetic rate (mol C m22 s21), l is the light period as a fraction of 24 h, fc is the proportion of C gained in photosynthesis that is subsequently used for respira- tion by leaves at night and by roots and stems during day and night, and r is the ratio of plant C mass to leaf area (mol C m22). Equation 1 provides a useful tool for examining sources of variation in r among plant species and individuals within a species. It is similar to the classical decomposition of r into net assimilation rate (NAR; gm22 s21) and leaf area ratio (LAR; m2 g21), but allows the assimilation term to be expressed as a net photosynthetic rate, such as would be measured using standard gas exchange techniques (Long et al., 1996). Table I provides definitions of all abbreviations and symbols used in this article. NUE Multiplying both sides of Equation 1 by the molar ratio of plant C to N yields an expression for the NUE of C accumulation: NUE5 1 mn  dmc dt 5Anl?1 2fc?nl ?2? where NUE is whole-plant NUE (mol C mol21 N s21), mn is plant N mass (mol N), An is photosynthetic NUE (mol Cmol21 N s21), and nl is the proportion of plant N allocated to leaves. Equation 2 provides a basis for linking An, a trait often quantified in ecophysiological investigations, with NUE, an integrated measure of NUE at the whole-plant level. Transpiration Efficiency and C Isotope Discrimination The ratio of C gain to water loss at the leaf level during photosynthesis can be expressed as the ratio of the diffusive fluxes of CO2 and water vapor into and out of the leaf, respectively (Farquhar and Richards, 1984): A E 5 ca 2 ci 1:6n ?3? where E is transpiration (mol H2O m 22 s21), ca and ci are CO2 partial pressures in ambient air and leaf intercellular air spaces, respectively, v is the leaf-to- air vapor pressure difference, and 1.6 is the ratio of diffusivities of CO2 and H2O in air. The v is defined as ei-ea, where ei and ea are the intercellular and ambient vapor pressures, respectively. The ratio of C gain to water loss can be scaled to the whole-plant level by taking into account respiratory C use and water loss not associated with photosynthesis (Farquhar and Richards, 1984; Hubick and Farquhar, 1989): TEc5 ?1 2fc?ca 1 2 ci ca   1:6n?11fw? ?4? where TEc is the transpiration efficiency of C gain, and fw is unproductive water loss as a proportion of water loss associated with C uptake, the former mainly comprising water loss at night through partially open stomata. Thus, fw can be approximated as En/ Ed, where En is nighttime transpiration and Ed is daytime transpiration. We suggest that the leaf to air vapor pressure difference, v, can be written as the product of the air vapor pressure deficit (D), and a second term, fv, which describes the magnitude of v relative to D, such that v 5 Dfv. This allows Equation 3 to be written as D  TEc5 ?1 2fc?ca 1 2 ci ca   1:6fv?11fw? ?5? Weighting TEc by D facilitates comparison of the transpiration efficiency of plants grown under differ- ent environmental conditions by accounting for vari- ation due to differences in atmospheric vapor pressure deficit (Tanner and Sinclair, 1983; Hubick and Farquhar, 1989). Thus, it accounts for variation in TEc that is purely environmental. TheDTEc has units of Pa mol C mol21 H2O. Photosynthetic discrimination against 13C (D13C) shares a common dependence with TEc on ci/ca. The D13C in C3 plants relates to ci/ca according to the following equation (Farquhar et al., 1982; Farquhar and Richards, 1984; Hubick et al., 1986): D13C5 a 2 d1 ?b 2 a? ci ca ?6? where a is the discrimination against 13C during dif- fusion through stomata (4.4&), b is discrimination against 13C during carboxylation by Rubisco (29&), and d is a composite term that summarizes collectively the discriminations associated with dissolution of CO2, Growth, Water Use, and Stable Isotopes in Tropical Trees Plant Physiol. Vol. 148, 2008 643 Table I. Abbreviations and symbols used in the text A Area-based photosynthesis rate (mmol CO2 m 22 s21) Am Mass-based photosynthesis rate (nmol CO2 g 21 s21) An Photosynthetic NUE (mmol CO2 mol 21 N s21) a Discrimination against 13C during diffusion through stomata b Discrimination against 13C during carboxylation by Rubisco C Molar concentration of water (mol m23) ca Partial pressure of CO2 in ambient air (Pa) ci Partial pressure of CO2 in leaf intercellular air spaces (Pa) D Vapor pressure deficit of ambient air (kPa) Dg Growth-weighted vapor pressure deficit of ambient air (kPa) Di Average daytime vapor pressure deficit of ambient air during week i (kPa) D18 Diffusivity of H2 18O in water (m2 s21) d Discrimination against 13C during C3 photosynthesis not associated with a or b E Transpiration rate (mmol m22 s21) Ed Daytime transpiration rate (mmol m 22 s21) Et Cumulative transpiration over the course of the experiment (mol) En Nighttime transpiration rate (mmol m 22 s21) ea Vapor pressure of ambient air (kPa) ei Vapor pressure in leaf intercellular air spaces (kPa) gs Stomatal conductance (mol m 22 s21) L Scaled effective path length relating to 18O advection and diffusion (m) LAR Leaf area ratio (m2 kg21) LA1 Leaf area at the initiation of the experiment (m 2) LA2 Leaf area at the conclusion of the experiment (m 2) l Light period as a fraction of 24 h lc Mass of C in leaf litter abscised during the experiment (mol C) mc Plant C mass (mol C) mc1 Plant C mass at the initiation of the experiment (mol C) mc2 Plant C mass at the conclusion of the experiment (mol C) mn Plant N mass (mol N) MTR Mean transpiration rate over the course of the experiment (mol m22 d21) NAR Net assimilation rate (g dry matter m22 s21) NUE Whole-plant N use efficiency (mol C mol21 N d21) n1 Leaf N as a proportion of whole-plant N Parea Leaf P per unit area (mmol m 22) pex Proportion of O atoms exchanging with medium water during cellulose synthesis px Proportion of water in developing cells not subject to evaporative 18O enrichment R The 18O/16O ratio of any water or dry matter component of interest Ra The 13C/12C ratio of CO2 in ambient air Rp The 13C/12C ratio of plant C Rs The 18O/16O ratio of irrigation (source) water r Relative growth rate (mol C mol21 C d21) SLA Specific leaf area (m2 kg21) TEc Whole-plant transpiration efficiency of C gain (mmol C mol 21 H2O) v Leaf-to-air vapor pressure difference (kPa) vg Growth-weighted leaf-to-air vapor pressure difference (kPa) vi Average daytime leaf-to-air vapor pressure difference for week i (kPa) wi Predicted dry matter increment for week i (g) D13C Discrimination against 13C D13Cp Discrimination against 13C in dry matter of the whole plant relative to CO2 in air D18Oe The 18O enrichment of evaporative sites within leaves compared to source water D18Oeg Growth-weighted prediction of D 18Oe over the course of the experiment D18Oei Predicted average daytime D 18Oe for week i D18OL The 18O enrichment of average lamina leaf water compared to source water D18Op The 18O enrichment of stem dry matter compared to source water D18Ov The 18O enrichment of atmospheric water vapor compared to source water d13C The 13C/12C ratio relative to the PeeDee Belmnite international standard d13Ca The d 13C of CO2 in ambient air d13Cp The d 13C of plant C d18O The 18O/16O ratio relative to Vienna Standard Mean Ocean Water d18Op The d 18O of stem dry matter d18Os The d 18O of irrigation (source) water (Table continues on following page.) Cernusak et al. 644 Plant Physiol. Vol. 148, 2008 liquid phase diffusion, photorespiration, and dark respiration (Farquhar et al., 1989a). The term d may be excluded from Equation 5, in which case the re- duction in D13C caused by d is often accounted for by taking a lower value for b. The D13C is defined with respect to CO2 in air as D 13C 5 Ra/Rp 2 1, where Ra is13C/12C of CO2 in air and Rp is 13C/12C of plant C. Combining Equations 5 and 6 gives D  TEc5 ca?1 2fc??b 2 d 2D 13C? 1:6fv?11fw??b 2 a? ?7? Equation 7 suggests a negative linear dependence of TEc (or DTEc) on D 13C, although it can be seen that there are many other terms in Equation 7 that have the potential to influence the relationship between the two. O Isotope Enrichment It has been suggested that measurements of the O isotope enrichment of plant organic material (D18Op) can provide complementary information to that in- ferred from D13C in analyses of plant water-use effi- ciency (Farquhar et al., 1989b, 1994; Sternberg et al., 1989; Yakir and Israeli, 1995). Specifically, D18Op could provide information about the ratio of ambient to in- tercellular vapor pressures, ea/ei, and thus about the leaf-to-air vapor pressure difference, ei-ea, during pho- tosynthesis. Note that ei-ea is equal to v in Equation 3. In the steady state, water at the evaporative sites in leaves becomes enriched in 18O relative to water en- tering the plant from the soil, according to the follow- ing relationship (Craig and Gordon, 1965; Dongmann et al., 1974; Farquhar and Lloyd, 1993): D18Oe5 e 1 1 ek1 ?D18Ov 2 ek? ea ei ?8? where D18Oe is the 18O enrichment of evaporative site water relative to source water, e1 is the equilibrium fractionation between liquid water and vapor, ek is the kinetic fractionation that occurs during diffusion of water vapor out of the leaf, and D18Ov is the discrim- ination of ambient vapor with respect to source water. The D18O of any water or dry matter component is defined with respect to source water (water entering the roots from the soil) as D18O 5 R/Rs 2 1, where D18O is the 18O enrichment of the component of inter- est and R and Rs are the 18O/16O ratios of the compo- nent of interest and source water, respectively. The e1 can be calculated as a function of leaf temperature (Bottinga and Craig, 1969), and ek can be calculated by partitioning the resistance to water vapor diffusion between stomata and boundary layer, with the two weighted by appropriate fractionation factors (Farquhar et al., 1989b; Cappa et al., 2003). The D18Ov can be calculated from measurements of the d18O of ambient vapor and source water. If such data are not available, a reasonable approximation is to estimate D18Ov as 2e1, whichmeans that ambient vapor is assumed to be in isotopic equilibrium with soil water. An up- to-date summary of equations necessary for parame- terization of Equation 8 can be found in Cernusak et al. (2007b). Average lamina leaf water 18O enrichment (D18OL) is generally less than that predicted for evaporative site water (Yakir et al., 1989; Flanagan, 1993; Farquhar et al., 2007), and carbohydrates exported from leaves have been observed to carry the signal of D18OL rather than D18Oe (Barbour et al., 2000b; Cernusak et al., 2003, 2005; Gessler et al., 2007). The D18OL has been sug- gested to relate to D18Oe according to the following relationship (Farquhar and Lloyd, 1993; Farquhar and Gan, 2003): D18OL5D 18Oe ?1 2 e2?? ? ?9? where ? is a Pe?clet number, defined as EL/(CD18), where E is transpiration rate (mol m22 s21), L is a scaled effective path length (m), C is the molar con- centration of water (mol m23), and D18 is the diffusiv- ity of H2 18O in water (m2 s21). The C is a constant, and D18 can be calculated from leaf temperature (Cuntz et al., 2007). The constancy of L, or otherwise, is currently under investigation (Barbour and Farquhar, 2004; Barbour, 2007; Kahmen et al., 2008; Ripullone et al., 2008). If L is assumed relatively constant, Equa- tion 9 predicts that D18OL will vary as a function of both D18Oe and E. To test for an influence of E on D 18OL, it is necessary to first account for variation in D18OL caused by D18Oe (Flanagan et al., 1994). To this end, the relative deviation ofD18OL fromD 18Oe (12 D 18OL/D 18Oe) can be examined, in which case Equation 9 can be written as 1 2 D18OL D18Oe 5 1 2 ?1 2 e2?? ? ?10? Table I. (Continued from previous page.) ecp The d 18O difference between plant dry matter and cellulose extracted from it ek Kinetic H2 18O fractionation for diffusion through stomata and leaf boundary layer ewc The 18O enrichment of cellulose compared to the water in which it formed e1 Equilibrium H2 18O fractionation during the phase change from liquid to gas fc Proportion of net photosynthesis subsequently used for respiration fv Scaling factor to convert D to v (5 v/D) fw Unproductive water loss as proportion of that associated with photosynthesis ? Pe?clet number r Plant C mass per unit leaf area (mol C m22) Growth, Water Use, and Stable Isotopes in Tropical Trees Plant Physiol. Vol. 148, 2008 645 Equation 10 predicts that 1 2 D18OL/D 18Oe should increase as E increases. The transfer of the leaf water 18O signal to plant organic material can be described by the following equation (Barbour and Farquhar, 2000): D18Op5D 18OL?1 2 pexpx?1 ewc1 ecp ?11? where D18Op is 18O enrichment of plant dry matter, pex is the proportion of O atoms that exchange with local water during synthesis of cellulose, a primary constit- uent of plant dry matter, px is the proportion of unenriched water at the site of tissue synthesis, ewc is the fractionation between organic oxygen and me- dium water, and ecp is the difference in D 18O between tissue drymatter and the cellulose component. For tree stems, pexpx has been found to be relatively constant at about 0.4 (Roden et al., 2000; Cernusak et al., 2005). The ewc is relatively constant at about 27& (Barbour, 2007), and for stem dry matter, ecp appears to be relatively constant at about 25& (Borella et al., 1999; Barbour et al., 2001; Cernusak et al., 2005). If these assumptions are valid, variation in D18Op should primarily reflect variation in D18OL. Thus, combining Equations 10 and 11 provides a means of testing for an influence of E on D18Op, assuming that D 18Op provides a time-integrated record of D18OL (Barbour et al., 2004): 1 2 D18Op 2 ewc 2 ecp 1 2 pexpx   D18Oe 5 1 2 ?1 2 e2?? ? ?12? RESULTS Growth, Photosynthesis, and Elemental Concentrations Daytime meteorological conditions over the course of the experiment are shown in Table II. Dates of initiation of transpiration measurements and harvest for each species are shown in Table III. Table III also shows the initial and final dry masses, in addition to root/shoot ratios. Variation in relative growth rate, r, among species is shown in Figure 1A; variation in the components of r, A, and 1/r, is shown in Figure 1, B and C, respectively. The r varied significantly among functional groups (P , 0.0001), and among species within functional groups (P , 0.0001). Gymnosperm trees had the lowest mean value of r, whereas angio- sperm lianas had the highest mean value; angiosperm trees had a mean value of r intermediate between that of gymnosperm trees and angiosperm lianas (Fig. 1A). In contrast, there was less variation among species and functional groups in instantaneous photosynthesis rates expressed on a leaf area basis (Fig. 1B), although the species Pinus caribaea and Stigmaphyllon hypargyreum were notable for having relatively high values of A. Variation in r tended to be more closely associated with variation in 1/r than with variation in A. Gym- nosperm trees had the lowest mean value of 1/r, whereas angiosperm trees had an intermediate mean value, and angiosperm lianas had the highest mean value (Fig. 1C). The liana species S. hypargyreum pos- sessed swollen, tuberous roots, which caused it to have a root/shoot ratio much higher than any other species in the study (Table III), and to have a reduced 1/r relative to the other two liana species (Fig. 1C). Variation in instantaneous photosynthesis, when expressed on a leaf mass basis, was a good predictor of variation in r (Fig. 2). The former was measured over several minutes, whereas the latter was measured over several months. Mass-based photosynthesis, Am, is the product of A (mol m22 s21) and specific leaf area (SLA; m2 kg21). The correlation between Am and r was almost entirely driven by variation in SLA, because A on a leaf area basis was not significantly correlated with r (P 5 0.14, n 5 94). The C and N concentrations of leaves, stems, roots, and whole plants for each species are given in Sup- plemental Table S1. For whole-plant C concentration, there was significant variation, both among functional groups (P , 0.0001), and among species within func- tional groups (P , 0.0001), as shown in Figure 3A. Gymnosperm trees had a mean C concentration of 49.6%, significantly higher than angiosperm trees and lianas. Angiosperm trees and lianas did not differ from each other in whole-plant C concentration, and had mean values of 45.4% and 44.9%, respectively. For whole plant N concentration, there was also significant variation among functional groups (P , 0.0001) and among specieswithin functional groups (P, 0.0001), as shown in Figure 3B. Angiosperm lianas had the highest mean whole-plant N concentration at 1.22%, followed by angiosperm trees at 1.01%, then by gymnosperm trees at 0.82%. Accordingly, there was significant variation among functional groups (P , 0.0001) and Table II. Average daytime meteorological conditions at the study site over the course of the experiment Values are monthly means of measurements taken every 15 min between the hours of 7 AM and 5:30 PM local time. We focused on daytime hours to characterize conditions during photosynthetic gas exchange. 2005 2006 June July Aug Sept Oct Nov Dec Jan Feb March April May Air temperature (C) 28.0 26.7 28.6 29.6 30.0 27.7 30.7 28.1 27.9 29.1 28.7 28.2 Relative humidity (%) 81.3 82.9 82.6 83.3 79.3 84.2 75.0 72.5 68.8 68.3 74.1 80.1 Vapor pressure deficit (kPa) 0.73 0.62 0.71 0.70 0.89 0.60 1.12 1.06 1.18 1.31 1.03 0.78 Wind speed (m s21) 0.33 0.26 0.31 0.33 0.45 0.29 0.50 0.61 0.87 0.82 0.75 0.38 Photon flux density (mmol m22 s21) 685 655 649 628 750 602 743 808 859 925 854 685 Cernusak et al. 646 Plant Physiol. Vol. 148, 2008 among species within functional groups (P , 0.0001) in whole-plant C/N mass ratio (Fig. 3C). Gymno- sperm trees had the highest mean whole-plant C/N at 64.7 g g21, followed by angiosperm trees at 49.6 g g21, then by angiosperm lianas at 39.0 g g21. Concentrations of phosphorus (P), calcium (Ca), and potassium (K), and the N/P mass ratio in leaf dry mat- ter for each species are shown in Table IV. There was significant variation among functional groups (P , 0.0001) and among species within functional groups (P, 0.0001) for all elements and for N/P. Angiosperm lianas tended to have higher mean concentrations of P, Ca, and K in their leaf dry matter than angiosperm and gymnosperm trees. The mean leaf N/P was higher in angiosperm trees than in gymnosperm trees or angio- sperm lianas; mean values were 9.3, 4.9, and 4.7 g g21, respectively. When expressed on a leaf area basis, the leaf P concentration was significantly correlated with mean transpiration rate (MTR) across all individuals (R2 5 0.24, P , 0.0001, n 5 94). The equation relating the two was Parea 5 0.096MTR 1 2.75, where Parea is in mmol m22, and MTR is in mol m22 d21. NUE Equation 2 presents a means for analyzing variation among functional groups and species in whole-plant NUE (mol C mol21 N s21). We calculated NUE as the product of r and mc/mn, the whole-plant C to N molar ratio; thus, a relatively high C/N has the effect of increasing NUE. Figure 4A shows variation among species in NUE. There was significant variation among Table III. Experimental time period, initial and final plant dry mass, and root to shoot ratio for each species in the study Values for final dry mass and root to shoot ratio are given as the mean, with the SD in parentheses. An SD is not given for P. guatemalensis because only one plant survived for this species. Full species names are given in Figure 2. NA, Not applicable. Species Family Start Date End Date No. of Plants Initial Dry Mass Final Dry Mass Root to Shoot Ratio g g g g21 Gymnosperm tree species C. lusitanica Cupressaceae May 23, 2005 Dec. 13, 2005 8 5.8 60.2 (19.0) 0.36 (0.06) P. caribaea Pinaceae May 23, 2005 Dec. 13, 2005 8 5.6 64.6 (30.9) 0.27 (0.09) P. guatemalensis Podocarpaceae May 23, 2005 May 11, 2006 1 0.8 107.3 (NA) 0.16 (NA) T. occidentalis Cupressaceae April 26, 2004 Dec. 13, 2005 8 4.7 41.4 (16.5) 0.47 (0.08) Angiosperm tree species C. longifolium Clusiaceae July 11, 2005 March 10, 2006 6 3.1 62.6 (27.0) 0.39 (0.08) C. pratensis Clusiaceae Aug. 22, 2005 May 11, 2006 6 0.2 112.2 (62.3) 0.76 (0.26) H. alchorneoides Euphorbiaceae June 20, 2005 Dec. 13, 2005 6 0.2 36.6 (30.2) 1.10 (0.13) L. seemannii Tiliaceae Aug. 29, 2005 March 10, 2006 7 0.1 39.8 (7.3) 0.61 (0.10) P. pinnatum Fabaceae Nov. 7, 2005 March 10, 2006 2 0.6 53.9 (16.6) 0.58 (0.20) P. pinnatum Fabaceae Nov. 7, 2005 May 11, 2006 3 0.6 21.6 (13.3) 0.36 (0.14) S. macrophylla Meliaceae Nov. 7, 2005 May 11, 2006 7 0.8 24.3 (11.8) 0.34 (0.10) T. rosea Bignoniaceae June 20, 2005 Dec. 13, 2005 6 0.6 64.8 (11.0) 0.92 (0.12) T. grandis Verbenaceae May 17, 2004 May 11, 2006 7 0.1 45.5 (11.3) 0.93 (0.17) Angiosperm liana species G. lupuloides Rhamnaceae Aug. 29, 2005 March 10, 2006 6 0.01 31.5 (15.6) 0.47 (0.20) M. leiostachya Asteraceae Aug. 29, 2005 March 10, 2006 3 0.1 21.2 (4.3) 0.37 (0.27) M. leiostachya Asteraceae Nov. 14, 2005 May 11, 2006 3 0.3 23.2 (4.8) 0.25 (0.06) S. hypargyreum Malphigiaceae Aug. 29, 2005 March 10, 2006 7 0.1 50.3 (20.3) 1.99 (0.21) Figure 1. A to C, Variation among spe- cies in mean relative growth rate (A), net photosynthesis, expressed on a leaf area basis (B), and leaf area per unit plant C mass, 1/r (C). Error bars repre- sent 1 SE. Sample sizes for each species are given in Table III. Growth, Water Use, and Stable Isotopes in Tropical Trees Plant Physiol. Vol. 148, 2008 647 functional groups (P , 0.0001) and among species within functional groups (P , 0.0001). However, un- like results for r, angiosperm trees and lianas did not differ from each other with respect to NUE (P 5 0.84). In contrast, NUE of gymnosperm trees was lower than that of both angiosperm trees (P , 0.0001) and angio- sperm lianas (P , 0.0001). Figure 4, B and C, shows variation among species in the NUE components, An and nl. Variation in NUE among species tended to reflect variation in An, the photosynthetic NUE (Fig. 4B). The An was also higher in angiosperm trees and lianas than in gymnosperm trees (Fig. 4B). This vari- ation in An was offset to a lesser extent by variation in nl, the proportion of plant N allocated to leaves (Fig. 4C). Gymnosperm trees had highest mean nl, at 0.69, followed by angiosperm trees at 0.59, then by angio- sperm lianas at 0.50. Thus, a higher allocation of N to leaves in gymnosperm trees compensated to some extent for their much lower An. However, the An was still the dominant control over NUE (Fig. 5). Transpiration Efficiency Mean values for each species for TEc, the whole- plant transpiration efficiency of C gain, are shown in Table V. Also shown in Table V are the growth- weighted estimates of the daytime vapor pressure deficit, Dg, by species. There was significant variation, both among functional groups (P, 0.0001), and among species within functional groups (P , 0.0001), in both TEc and Dg. However, across the full data set, TEc and Dg were not significantly correlated (P 5 0.11, n 5 94), suggesting that Dg was not a primary control over TEc. Taking the product of Dg and TEc allows analysis of variation in TEc independently of variation in Dg, as articulated in Equation 5. The DgTEc also varied significantly among functional groups (P , 0.0001) and among species within functional groups (P , 0.0001). Angiosperm trees had the highest mean DgTEc at 1.58 Pa mol C mol 21 H2O, followed by an- giosperm lianas at 1.30 Pa mol C mol21 H2O, then by gymnosperm trees at 1.11 Pa mol C mol21 H2O. Among all species, there was a 3.7-fold variation in DgTEc (i.e. the largest species mean was 3.7 times the smallest species mean). Table V summarizes for each species the compo- nents of DgTEc that we quantified: fv, the ratio of leaf- to-air vapor pressure difference to air vapor pressure deficit; fw, the ratio of unproductive to productive water loss; and ci/ca, the ratio of intercellular to ambient CO2 partial pressures during photosynthesis. Although there was a 1.8-fold variation among species in fv, this parameter did not appear to be a primary control over DgTEc: the term 1/fv explained only 13% of variation in DgTEc (R 2 5 0.13, P 5 0.0004, n 5 94); moreover, the slope of the relationship between DgTEc and 1/fv was negative, opposite to that predicted by Equation 5. The parameter fw similarly did not ap- pear to exert a strong control over DgTEc: although DgTEc was positively correlated with 1/(11 fw) (R 25 0.18, P , 0.0001, n 5 92), there was only a 1.1-fold variation in this term among species, suggesting that it could only account for a variation in DgTEc of ap- proximately 10%. In contrast, the ci/ca appeared to be the primary control over DgTEc. Among species, there was a 2.3-fold variation in instantaneous measure- ments of 12 ci/ca, and ci/ca explained 46% of variation in DgTEc. Regression coefficients are given in Table VI. Furthermore, instantaneous measurements of 12 ci/ca explained 64% of variation in the composite term vgTEc(1 1 fw) (R 2 5 0.64, P , 0.0001, n 5 94). Taking this product means that only the variables fc, ca, and ci/ca remain on the right side of Equation 5. Variation in instantaneousmeasurements of ci/ca was largely driven by variation in stomatal conductance, gs, rather than by variation in photosynthesis, A. If gs Figure 2. Mean relative growth rate plotted against instantaneous measurements of photosynthesis expressed on a leaf mass basis. White symbols with internal cross-hairs refer to gymnosperm tree species; completely white symbols refer to angiosperm liana species; black symbols and black symbols with internal cross-hairs refer to angio- sperm tree species. Cernusak et al. 648 Plant Physiol. Vol. 148, 2008 controls variation in ci/ca, then ci/ca should decrease as 1/gs increases. The 1/gs is equivalent to the stomatal resistance. In contrast, if A controls ci/ca, then ci/ca should decrease as A increases. Figure 6A shows that instantaneous ci/ca decreased as a linear function of 1/gs. In contrast, Figure 6B shows that there was a weak tendency for ci/ca to increase as A increased, op- posite to the trend that would be expected if A were controlling ci/ca. We used measurements of leaf temperature, taken with a hand-held infrared thermometer, to calculate values of fv for the species harvested on the second and third harvest dates (Table III). We then compared these instantaneous measurements of fv with our time-integrated estimates for each plant based on leaf energy balance predictions and meteorological data. The time-integrated estimates of fv compared favorably with the instantaneous measurements of fv (R2 5 0.42, P , 0.0001, n 5 55), thus providing some validation of the former. Stable Isotope Composition The C isotope composition of leaves, stems, roots, and whole plants is shown for each species in Table VII. Also shown is the difference in d13C between leaves and the sum of stems plus roots, the heterotro- phic component of the plant. Across all individuals, leaf d13C was more negative than stem d13C (P , 0.0001, n 5 94) and root d13C (P , 0.0001, n 5 94), whereas stem d13C was more negative than root d13C, but by a much smaller amount (P 5 0.0008, n 5 94); mean values for leaf, stem, and root d13C were 229.4, 228.1, and 227.8&, respectively. Table IV. Leaf P, Ca, and K concentrations, and N/P ratios of experimental plants Values are given as the mean for each species, with the SD in parentheses. No SD is given for P. guatemalensis because only one individual of this species survived. Sample sizes for the other species ranged from five to eight individuals, as shown in Table III. NA, Not applicable. Species P Ca K N/P g kg21 g kg21 g kg21 g g21 Gymnosperm tree species C. lusitanica 3.10 (0.76) 8.3 (0.9) 20.9 (2.8) 3.6 (0.8) P. caribaea 1.43 (0.47) 3.6 (1.4) 9.6 (1.6) 7.6 (1.4) P. guatemalensis 2.48 (NA) 8.1 (NA) 16.9 (NA) 5.9 (NA) T. occidentalis 4.24 (0.86) 10.5 (2.2) 16.8 (1.5) 3.4 (0.8) Angiosperm tree species C. longifolium 0.94 (0.23) 7.7 (0.8) 8.4 (1.4) 12.4 (1.5) C. pratensis 1.38 (0.47) 13.6 (1.1) 14.4 (5.2) 9.7 (2.1) H. alchorneoides 2.22 (0.59) 12.5 (3.9) 24.0 (4.3) 6.8 (1.5) L. seemannii 3.59 (0.81) 18.0 (2.1) 14.2 (1.6) 5.0 (1.4) P. pinnatum 1.68 (0.23) 10.2 (2.1) 16.7 (4.3) 18.2 (5.7) S. macrophylla 1.33 (0.35) 13.4 (1.5) 20.3 (3.0) 12.0 (2.8) T. rosea 1.43 (0.04) 14.4 (4.3) 15.1 (4.4) 11.1 (2.2) T. grandis 5.96 (0.42) 8.6 (1.0) 13.3 (2.1) 2.0 (0.2) Angiosperm liana species G. lupuloides 5.33 (1.15) 14.4 (2.1) 24.5 (2.4) 4.4 (0.9) M. leiostachya 2.66 (0.30) 13.2 (1.4) 29.5 (3.5) 6.6 (1.2) S. hypargyreum 6.23 (1.09) 23.4 (3.3) 24.6 (4.0) 3.5 (0.5) Figure 3. A to C, Variation among spe- cies in the C concentration of dry matter on a whole-plant basis (A), the N con- centration of dry matter on a whole- plant basis (B), and the C/N mass ratio of dry matter on a whole-plant basis (C). Error bars represent 1 SE. Sample sizes for each species are given in Table III. Growth, Water Use, and Stable Isotopes in Tropical Trees Plant Physiol. Vol. 148, 2008 649 We converted plant d13C values to 13C discrimina- tion by assuming d13C of atmospheric CO2 to be 28&. Whole-plant D13C, D13Cp, covered a range from 18.8& to 22.9& among species, corresponding to d13Cp values ranging from226.3& to230.2& (Table VII). There was significant variation in D13Cp among functional groups (P 5 0.002) and among species within functional groups (P, 0.0001). TheD13Cp was lower in angiosperm trees than in gymnosperm trees, whereas angiosperm lianas did not differ significantly from angiosperm or gymnosperm trees. Mean values were 21.0&, 21.2&, and 21.5& for angiosperm trees, angiosperm lianas, and gymnosperm trees, respectively. The D13Cp was significantly correlated with instan- taneous measurements of ci/ca (Fig. 7), as predicted by Equation 6. We estimated the term d of Equation 6 by least-squares regression by assuming fixed values for a and b of 4.4& and 29&, respectively. This resulted in an estimate for d of 3.1&; the regression equation explained 57% of variation in D13Cp. Thus, the predic- tive power of this relationship was equivalent to that obtained with a standard linear regression, in which both the slope and intercept are free to vary (Fig. 7). Using the mean estimate of 3.1& for d, and values of 4.4& and 29& for a and b, respectively, we calculated a D13Cp-based estimate of ci/ca for each plant. Mean values of these estimates for each species are given in Table V. There was a 2.4-fold variation among species in the D13Cp-based estimates of 1 2 ci/ca. Variation in D13Cp was significantly correlated with variation in DgTEc (Fig. 8); the former explained 49% of variation in the latter. Regression coefficients and the coefficient of determination for least-squares linear regressions of TEc, DgTEc, and vgTEc against D 13C of leaves, stems, roots, and whole plants are given in Table VI. In general, whole-plant D13C was a better predictor of variation in TEc than D 13C of leaves, stems, or roots individually. Additionally, weighting of TEc by Dg or vg tended to result in modest increases in the proportion of variation explained by the regression models (Table VI). Correlations between D13Cp and 1/gs and A further supported the conclusion that variation in ci/ca was largely driven by variation in gs. The D 13Cp decreased as a linear function of 1/gs (Fig. 6C). In contrast, the D13Cp showed a weak tendency to increase as a func- tion of A (Fig. 6D), opposite to the trend that would be expected if A controlled variation in ci/ca. Variation among species in the O isotope composi- tion of stem dry matter is given in Table VII. We calculated the 18O enrichment above source water of stemdrymatter,D18Op, from themean d 18O of irrigation water of 24.3&. The observed D18Op was significantly correlated with the predicted 18O enrichment of evap- orative site water, D18Oe, weighted by predicted weekly growth increments (Fig. 9). We tested whether the residual variation in D18Op, after accounting for var- iation in D18Oe, was related to transpiration rate by plotting 1 2 [(D18Op 2 ewc 2 ecp)/(1 2 pexpx)]/D 18Oe against the MTR. As shown in Equation 12, this term should increase with an increasing transpiration rate if there is a significant Pe?clet effect. Our analysis detected a significant relationship between the two Figure 4. A to C, Variation among spe- cies in whole-plant NUE (A), photosyn- thetic NUE (B), and nl, the leaf N content as a proportion of whole-plant N content (C). Error bars represent 1 SE. Sample sizes for each species are given in Table III. Figure 5. Whole-plant NUE plotted against photosynthetic NUE. Whole-plant NUE was calculated from mean relative growth rate, measured over several months, whereas photosynthetic NUE was calculated from instantaneous photosynthesis measurements, taken over several minutes. Different symbols refer to different species, as detailed in Figure 2. Cernusak et al. 650 Plant Physiol. Vol. 148, 2008 parameters (R2 5 0.14, P5 0.0002, n5 94), supporting the notion of a significant Pe?clet effect, although there was considerable scatter in the relationship. Using the MTR and En/Ed, we calculated a daytime MTR, then used the nonlinear regression routine in SYSTAT to solve for an average value of L, the scaled effective path length, across the full data set. This analysis estimated a mean value of L for the full data set of 53 mm, with the 95% confidence interval ranging from 43 to 62 mm. DISCUSSION In this article, we present a comprehensive compar- ison of physiological processes in seedlings of conifers, angiosperm trees, and angiosperm lianas under trop- ical field conditions. The comparison yielded novel insights into physiological differences among these functional groups, when grown in a tropical environ- ment. For example, we observed that liana species, on average, had higher 1/r than tree species, and that this trait was associated with faster growth. We also ob- served that gymnosperm trees had significantly lower whole-plant NUE than both angiosperm trees and angiosperm lianas. In addition, the results provided an integrated account of the physiological controls over growth, whole-plant water and NUE, and stable iso- tope composition across the full range of species. Relative growth rate, r, was mainly controlled by variation in 1/r, the amount of assimilative surface area for a given plant biomass (Fig. 1). Of the compo- nents of 1/r, the SLA played a key role, such that the product of SLA and instantaneous photosynthesis, A, was a strong predictor of variation in r (Fig. 2). The whole-plant NUE was mainly controlled by An, the photosynthetic rate for a given amount of leaf N (Fig. 5). An increase in the proportional allocation of N to leaves, nl, in species with low An was observed; how- ever, the increased nl compensated to only a relatively modest extent for low An (Fig. 4). The primary control over the transpiration efficiency of C uptake, TEc, was ci/ca, the ratio of intercellular to ambient CO2 partial pressures during photosynthetic gas exchange (Tables V and VI). The ci/ca was also the primary control over whole-plant 13C discrimination, D13Cp (Fig. 7), such that variation in D13Cp was closely correlated with variation in TEc (Table VI; Fig. 8). The ci/ca, in turn, was largely controlled by stomatal conductance, gs (Fig. 6). The 18O enrichment of stem dry matter, D18Op, was primarily controlled by the predicted 18O enrich- ment of the evaporative sites within leaves, D18Oe, during photosynthetic gas exchange (Fig. 9). Variation in leaf transpiration rate further explained some of the residual variation in D18Op not accounted for by vari- ation in D18Oe. Growth and NUE We observed that the term 1/r was the primary control over variation in r, and that A was a relatively conservative parameter among species (Fig. 1). These Table V. Transpiration efficiency and related parameters for each species Symbol definitions are as follows: transpiration efficiency of C uptake (TEc); growth-weighted daytime vapor pressure deficit (Dg) and leaf-to-air vapor pressure difference (vg); the ratio of nighttime to daytime transpiration (En/Ed); and the ratio of intercellular to ambient CO2 partial pressures (ci/ca). The ci/ca is given as the value measured with a portable photosynthesis system (instantaneous), or as the value estimated from whole-plant 13C discrimination (D13Cp-based). Values are given as the mean for each species, with the SD in parentheses. No SD is given for P. guatemalensis because only one individual of this species survived. Sample sizes for the other species ranged from five to eight individuals, as shown in Table III. NA, Not applicable. Species TEc Dg vg fv (5 vg/Dg) fw (5 En/Ed) Instantaneous ci/ca D13Cp-Based ci/ca mmol C mol21 H2O kPa kPa Gymnosperm tree species C. lusitanica 1.29 (0.20) 0.76 (0.01) 0.90 (0.07) 1.17 (0.08) 0.11 (0.02) 0.78 (0.04) 0.80 (0.02) P. caribaea 1.20 (0.19) 0.76 (0.01) 0.72 (0.05) 0.95 (0.07) 0.04 (0.02) 0.86 (0.03) 0.88 (0.02) P. guatemalensis 3.48 (NA) 1.04 (NA) 1.71 (NA) 1.64 (NA) 0.04 (NA) 0.63 (NA) 0.63 (NA) T. occidentalis 1.85 (0.19) 0.76 (0.01) 0.92 (0.03) 1.21 (0.05) 0.03 (0.03) 0.80 (0.02) 0.78 (0.01) Angiosperm tree species C. longifolium 1.83 (0.24) 1.05 (0.02) 1.53 (0.12) 1.46 (0.10) 0.04 (0.04) 0.76 (0.04) 0.78 (0.05) C. pratensis 2.16 (0.22) 1.02 (0.01) 1.42 (0.06) 1.39 (0.06) 0.01 (0.01) 0.76 (0.03) 0.73 (0.01) H. alchorneoides 1.50 (0.20) 0.83 (0.01) 1.37 (0.04) 1.65 (0.05) 0.08 (0.01) 0.80 (0.02) 0.85 (0.01) L. seemannii 0.98 (0.15) 1.20 (0.00) 1.43 (0.20) 1.19 (0.16) 0.05 (0.01) 0.80 (0.03) 0.81 (0.02) P. pinnatum 2.76 (0.62) 1.12 (0.10) 1.53 (0.28) 1.39 (0.36) 0.02 (0.01) 0.73 (0.09) 0.71 (0.06) S. macrophylla 1.07 (0.22) 1.05 (0.01) 1.21 (0.03) 1.15 (0.03) 0.07 (0.01) 0.86 (0.02) 0.88 (0.02) T. rosea 1.92 (0.24) 0.82 (0.00) 1.37 (0.18) 1.67 (0.21) 0.11 (0.02) 0.75 (0.06) 0.79 (0.03) T. grandis 0.84 (0.07) 0.98 (0.01) 1.20 (0.08) 1.23 (0.09) 0.08 (0.01) 0.88 (0.03) 0.81 (0.03) Angiosperm liana species G. lupuloides 0.96 (0.34) 1.25 (0.01) 1.37 (0.08) 1.10 (0.06) 0.04 (0.01) 0.84 (0.03) 0.80 (0.02) M. leiostachya 0.89 (0.23) 1.11 (0.10) 1.39 (0.20) 1.25 (0.12) 0.07 (0.02) 0.79 (0.05) 0.80 (0.06) S. hypargyreum 1.35 (0.14) 1.21 (0.01) 1.18 (0.06) 0.97 (0.05) 0.03 (0.01) 0.82 (0.03) 0.82 (0.02) Growth, Water Use, and Stable Isotopes in Tropical Trees Plant Physiol. Vol. 148, 2008 651 results agree with those presented previously for 24 herbaceous species (Poorter and Remkes, 1990; Poorter et al., 1990), and for many woody species (Cornelissen et al., 1996; Atkin et al., 1998; Wright and Westoby, 2000). For the herbaceous species, SLA was also a key component of 1/r, such that variation in r was not correlated with variation in A, but was strongly cor- related with variation in Am, the product of A and SLA (Poorter et al., 1990). It should be noted that A was measured near the end of the experiment, and our results thus do not preclude the possibility that vari- ation in A may have modulated r earlier in plant development. Nonetheless, our measurements of Am explained more than two-thirds of total variation in r (Fig. 2). Among the species that we grew, the gymno- sperm trees generally had lowest 1/r and r, whereas angiosperm lianas had highest 1/r and r, with angio- sperm trees intermediate between the two (Fig. 1). This pattern suggests that variation in 1/r could be related to hydraulic efficiency, with the tracheid-bearing gym- nosperm species constrained by a lower hydraulic conductance for a given plant mass, and thereby requiring a greater plant mass to support a given amount of assimilative, and thus evaporative, surface area. On the other hand, the angiosperm liana species, having freed themselves from the constraint of struc- tural self-sufficiency, and possessing hydraulically ef- ficient vessels, might then have required a smaller plant mass to deliver water to a given leaf surface area. Measurements of whole-plant hydraulic conductance per unit plant mass would be necessary to confirm this hypothesis. However, it would be consistent with differences in hydraulic conductivity observed previ- ously between gymnosperm and angiosperm seed- lings (Brodribb et al., 2005). As shown in Equation 1, the term fc, the proportion of net C fixation used for respiration, has potential to influence r. It was previously observed for 24 herba- ceous species that fc ranged from about 0.5 to 0.3, and that r was negatively correlated with fc, as predicted by Equation 1 (Poorter et al., 1990). Although we did not measure fc in our study, we can speculate that the slower-growing species had higher values, because they generally had higher whole-plant C concentra- tions (Fig. 3A), which would correlate with higher tissue construction costs (Vertregt and Penning de Vries, 1987; Poorter, 1994). The r was negatively cor- related with whole-plant C concentration across the full data set (R2 5 0.35, P , 0.0001, n 5 94). The leaf N/P mass ratios that we observed (Table IV) were generally low for tropical vegetation (Reich and Oleksyn, 2004). However, they are consistent with a previous study conducted under similar conditions, but with variable amounts of rice (Oryza sativa) husk mixed into the experimental soil (Cernusak et al., 2007b). At a similar rice husk/soil mixture as used in this study, we previously observed a mean leaf N/P ratio of 5.9 for Ficus insipida (Cernusak et al., 2007b), whereas the overall mean for all species in this study was 7.2. The generally low leaf N/P ratios suggest that plant growth in this study was constrained pri- marily by N availability, rather than by P availability (Koerselman and Meuleman, 1996; Aerts and Chapin, 2000). This is consistent with the addition of rice husks increasing the C/N ratio of the experimental soil, thereby favoring microbial immobilization of soil N, Table VI. The proportion of variation in transpiration efficiency explained by 13C discrimination and instantaneous ci/ca Linear regression equations were fitted with the following parameters alternatively used as dependent variables: transpiration efficiency of C uptake (TEc); the product of TEc and growth-weighted vapor pressure deficit (DgTEc); and the product of TEc and growth-weighted leaf-to-air vapor pressure difference (vgTEc). Independent variables were whole-plant 13C discrimination (D13C); D13C of leaves, stems, or roots individually; and instantaneous ci/ca. For each analysis, n5 94. All regression coefficients were significant at P , 0.0001. Dependent Variable Regression Coefficient Model R2 Intercept Whole-Plant D13C & Leaf D13C & Stem D13C & Root D13C & Instantaneous ci/ca TEc 7.76 20.298 0.45 DgTEc 8.40 20.330 0.49 vgTEc 14.4 20.594 0.53 TEc 7.04 20.253 0.38 DgTEc 8.03 20.300 0.48 vgTEc 12.9 20.501 0.45 TEc 6.87 20.262 0.40 DgTEc 7.42 20.290 0.45 vgTEc 12.8 20.528 0.50 TEc 6.66 20.255 0.36 DgTEc 6.53 20.251 0.32 vgTEc 11.8 20.487 0.40 TEc 7.30 27.27 0.51 DgTEc 7.21 27.20 0.46 vgTEc 13.6 214.6 0.62 Cernusak et al. 652 Plant Physiol. Vol. 148, 2008 and thus reducing N availability to plants. This pro- vided a useful experimental basis for comparing NUE among the species in our study, because N was likely the nutrient most limiting plant growth. We calculated whole-plant NUE as the product of r and mc/mn, the whole-plant molar ratio of C to N. Although the gymnosperm species had higher C/N than the angiosperm species (Fig. 4), they were still at a marked disadvantage with respect to NUE. Such dis- advantage resulted primarily from a lower An (Figs. 4 and 5). This difference between gymnosperm and angiosperm seedlings, whereby the former employed Nmuch less efficiently than the latter for accumulating C, could be decisive in determining competitive out- comes between the two. Although productivity in tropical forests is generally considered P limited, it has also been reported that N availability can constrain tree growth in both montane (Tanner et al., 1998) and lowland (LeBauer and Treseder, 2008) tropical forests. Thus, a higher NUE may contribute to angiosperm dominance in tropical environments. The lowAn in the gymnosperm species compared to the angiosperm species resulted primarily from lower SLA, because A was generally similar between the two groups, and leaf N concentration was lower in gymnosperms than in angiosperms (Supplemental Table S1). Transpiration Efficiency The species included in the study exhibited a large variation in the transpiration efficiency of C uptake, TEc (Table V). This is consistent with previous results showing large variation in TEc among seven tropical tree species (Cernusak et al., 2007a). When the TEc for each individual plant was normalized according to its growth-weighted mean daytime vapor pressure defi- cit, Dg, the variation among species was still apparent, suggesting that Dg was not a primary control over TEc. Additionally, the relative ranking among species in this study was consistent with results for three species that were also measured previously (Cernusak et al., 2007a); in this study Platymiscium pinnatum had the highest DgTEc, Swietenia macrophylla an intermediate value, and Tectona grandis the lowest value (3.05, 1.12, and 0.82 Pa mol C mol21 H2O, respectively). Previ- ously, we observed that TEc for these three species was 3.97, 2.88, and 1.63 mmol C mol21 H2O, respectively (Cernusak et al., 2007a). In this study, we were able to confirm that ci/ca was the primary control over DgTEc. The fv also showed a moderate variation among species, suggesting that it could be an important source of variation in DgTEc (Table V); however, the fv tended to be negatively correlated with ci/ca, due to a mutual dependence of the two parameters on gs. Thus, it appeared that variation in fv mostly served to dampen what would have been the full effect of variation in ci/ca on DgTEc. For example, plants with low gs tended to have low ci/ca (Fig. 6), which would increase DgTEc, as shown in Equation 5. All else being equal, the low gs would also cause leaf temperature to increase, thereby in- creasing fv, which would then cause a counteracting Figure 6. A to D, The top two panels show instanta- neous measurements of ci/ca plotted against stomatal resistance (A) and photosynthesis (B); the bottom two panels show whole-plant 13C discrimination plotted against stomatal resistance (C) and photosynthesis (D). Stomatal resistance is the inverse of stomatal conduc- tance. Different symbols refer to different species, as described for Figure 2. Growth, Water Use, and Stable Isotopes in Tropical Trees Plant Physiol. Vol. 148, 2008 653 decrease in DgTEc. However, it is clear from the large variation in DgTEc and its correlation with ci/ca (Table VI) that variation in fv only dampened, and did not completely cancel, the effect of ci/ca on DgTEc. Of the other terms in Equation 5, we found that fw, the un- productive water loss as a proportion of that associ- ated with photosynthesis, played only a minor role in modulating DgTEc, in agreement with previous results (Cernusak et al., 2007b). Finally we consider variation in 1 2 fc: although this term is an important functional trait, and may play an important role in modulating r, it likely plays a lesser role in controlling DgTEc than ci/ca. For example if fc varied among species from 0.3 to 0.5 (Poorter et al., 1990), the term 1 2 fc would vary from 0.5 to 0.7, whereas we ob- served variation in 12 ci/ca from 0.12 to 0.27 (Table V). Thus, the formerwould be associatedwith a 1.4-fold var- iation in DgTEc, and the latter with a 2.3-fold variation in DgTEc. There was significant variation in DgTEc among the plant functional groups that we studied, such that angiosperm trees had highest DgTEc, on average, and gymnosperm trees lowest, with angiosperm lianas intermediate between the two. Angiosperm trees also had an advantage over gymnosperm trees if water-use efficiency was analyzed as TEc, vgTEc, ci/ca, or D 13Cp. Thus, in addition to having an advantage over gym- nosperm seedlings in NUE, angiosperm seedlings may also have a competitive advantage in terms of water-use efficiency, when grown in tropical environ- ments. However, it should be emphasized that our experiment was carried out under well-watered con- ditions, and thus may not necessarily be indicative of trends when water availability is limiting to plant growth. Of the gymnosperm species that we grew, only one, Podocarpus guatemalensis, occurs naturally in the trop- ical forests of Panama. Although generally associated with highland forests, this species also occurs on low- lying islands off both the Pacific and Atlantic coasts. Unfortunately, only one individual of P. guatemalensis survived in our experiment, and we therefore ex- Table VII. The C and O isotope composition of experimental plants Whole-plant d13C values were calculated by weighting the d13C for each tissue by the fraction of C in that tissue relative to the whole plant. The d13C of stems plus roots was calculated similarly to show the difference between the d13C of leaves and heterotrophic tissues. Values are given as the mean for each species, with the SD in parentheses. No SD is given for P. guatemalensis because only one individual of this species survived. Sample sizes for the other species ranged from five to eight individuals, as shown in Table III. NA, Not applicable. Species Carbon-Isotope Ratio (d13C) & Oxygen-Isotope Ratio (d18O) & Leaves Stems Roots Whole Plant Leaves 2 (Stems 1 Roots) Stems Gymnosperm tree species C. lusitanica 229.7 (0.3) 227.8 (0.4) 226.8 (1.0) 228.5 (0.5) 22.4 (0.5) 20.1 (0.4) P. caribaea 230.7 (0.6) 230.0 (0.6) 229.4 (0.4) 230.2 (0.5) 20.9 (0.2) 20.0 (0.3) P. guatemalensis 225.4 (NA) 223.3 (NA) 223.5 (NA) 224.5 (NA) 22.0 (NA) 24.7 (NA) T. occidentalis 228.9 (0.2) 227.5 (0.3) 227.2 (0.6) 228.0 (0.3) 21.6 (0.5) 20.7 (0.4) Angiosperm tree species C. longifolium 228.4 (1.3) 227.2 (0.8) 228.1 (1.2) 228.0 (1.1) 20.7 (0.5) 23.8 (0.6) C. pratensis 227.1 (0.3) 226.4 (0.4) 226.9 (0.3) 226.9 (0.3) 20.4 (0.1) 23.0 (0.3) H. alchorneoides 231.0 (0.1) 229.8 (0.3) 228.7 (0.4) 229.6 (0.3) 22.0 (0.3) 20.6 (0.3) L. seemannii 229.3 (0.4) 228.1 (0.8) 228.2 (0.4) 228.6 (0.4) 21.1 (0.3) 22.8 (0.2) P. pinnatum 227.3 (1.1) 225.7 (1.6) 225.4 (2.0) 226.3 (1.3) 21.7 (0.8) 24.8 (1.3) S. macrophylla 231.6 (0.4) 229.3 (0.3) 229.1 (0.4) 230.3 (0.4) 22.4 (0.1) 23.9 (0.5) T. rosea 229.6 (0.8) 228.0 (0.6) 227.5 (0.8) 228.1 (0.7) 22.0 (0.5) 23.2 (0.3) T. grandis 229.5 (0.5) 228.0 (0.5) 227.9 (0.6) 228.6 (0.6) 21.5 (0.2) 22.9 (0.3) Angiosperm liana species G. lupuloides 229.2 (0.5) 228.0 (0.5) 228.3 (0.3) 228.4 (0.4) 21.1 (0.5) 24.8 (0.4) M. leiostachya 229.3 (1.3) 228.0 (1.1) 227.0 (1.3) 228.3 (1.3) 21.7 (0.2) 23.8 (1.0) S. hypargyreum 229.5 (0.7) 229.2 (0.4) 228.7 (0.5) 228.9 (0.5) 20.7 (0.3) 22.4 (1.1) Figure 7. Whole-plant 13C discrimination plotted against the ratio of intercellular to ambient CO2 partial pressures determined from instan- taneous gas exchange measurements. Different symbols refer to differ- ent species, as defined in Figure 2. Cernusak et al. 654 Plant Physiol. Vol. 148, 2008 cluded it from all species-level analyses. However, the lone surviving individual was interesting in that it had the highest DgTEc and lowest ci/ca of any plant in the study (Figs. 7 and 8). The ci/ca of 0.63 that we ob- served for this individual of P. guatemalensis is similar to a ci/ca of about 0.60 observed previously for well- watered Podocarpus lawrencii (Brodribb, 1996). Further research is necessary to determine whether high water-use efficiency is a common trait within the genus Podocarpus, and whether this trait contributes to the ability of Podocarpus to persist in otherwise angiosperm- dominated tropical forests. Stable Isotope Composition Whole-plant 13C discrimination, D13Cp, showed a strong correlation with instantaneous measurements of ci/ca (Fig. 7), suggesting that in general D 13Cp was a faithful recorder of ci/ca, as predicted by Equation 6. The mean value for d that we estimated for the full data set was 3.1&, reasonably similar to a value of 4.0&, recently estimated for Ficus insipida (Cernusak et al., 2007b). The D13Cp was also a reasonably good predictor of variation in TEc, DgTEc, and vgTEc (Table VI). We previously observed that the relationship between D13Cp and TEc broke down at the species level, appearing to reflect species-specific offsets in the relationship between the two parameters (Cernusak et al., 2007a). Whereas there was some evidence of similar behavior in this study, as can be seen in Figure 8, the species-level relationship between D13Cp and DgTEc was generally much stronger in this study. For example, in a least-squares linear regression be- tween D13Cp and DgTEc using species means, the for- mer explained 57% of variation in the latter (R25 0.57, P 5 0.002, n 5 14); if P. guatemalensis was included in the regression, the D13Cp explained 77% of variation in DgTEc (R 2 5 0.77, P , 0.0001, n 5 15). The main dif- ference between the earlier study (Cernusak et al., 2007a) and this study was likely the range of variation in D13Cp exhibited by the particular species that com- prised the experiments. In the earlier study, mean values for D13Cp at the species level ranged from only 20.3 to 21.7&, whereas in this study, species means ranged from 18.8& to 22.9&; including the individual of P. guatemalensis would further extend the lower range to 16.9&. Although our results show a generally strong cor- relation between D13Cp and DgTEc, we suggest that it is best to err on the side of caution when interpreting variation among species in the former as indicative of variation among species in the latter. As shown in Equation 7, there are many terms with potential to influence the relationship between D13Cp and DgTEc , not the least of which is variation in d, which could be associated with variation among species in mesophyll conductance to CO2 (Lloyd et al., 1992; Warren and Adams, 2006; Seibt et al., 2008). Moreover, as was previously the case (Cernusak et al., 2007a), we ob- served significant variation among species in the dif- ference between d13C of leaves and that of stems and roots (Table VII). The mechanistic basis for such var- iation among species in the d13C difference between leaves and heterotrophic tissues is not well under- stood (Hobbie and Werner, 2004; Badeck et al., 2005). The 18O enrichment of stem dry matter, D18Op, varied significantly among species, and much of the observed variation inD18Op could be explained by vari- ation in D18Oe, the predicted 18O enrichment of evap- Figure 8. The product of transpiration efficiency of C gain (TEc) and daytime vapor-pressure deficit of ambient air (Dg) plotted against whole-plant 13C discrimination. Different symbols refer to different species, as defined in Figure 2. Daytime air vapor-pressure deficit was weighted according to the predicted weekly growth increment for each individual plant. Figure 9. The 18O enrichment of stem dry matter relative to irrigation water plotted against the predicted 18O enrichment of water at the evaporative sites in leaves. The predicted D18Oe was weighted accord- ing to the predicted weekly growth increment for each individual plant. Different symbols refer to different species, as defined in Figure 2. Growth, Water Use, and Stable Isotopes in Tropical Trees Plant Physiol. Vol. 148, 2008 655 orative sites within leaves (Fig. 9). Because plants were grown over different time periods throughout the year, and due to predicted differences in leaf temperature, there was a reasonable variation among species in predicted D18Oe. Species means for growth-weighted D18Oe ranged from 6.9& to 13.0& (14.6& for P. guatemalensis), and explained 73% of variation in the observed species means for D18Op (R 2 5 0.73, P 5 0.0001, n 5 14), or 75% if P. guatemalensis was included (R2 5 0.75, P , 0.0001, n 5 15). These correlations suggest that the assumptions described in the theory section for the D18Op model are reasonable. Addi- tionally, we observed that the term 12 [(D18Op2 ewc2 ecp)/(1 2 pexpx)]/D 18Oe was significantly related to the daytime MTR across the full data set, providing evi- dence for a Pe?clet effect, as articulated in Equation 12. This result is consistent with an experiment involving three temperate tree species (Barbour et al., 2004). In this study, we estimated a mean scaled effective path length, L, for the full data set of 53 mm, similar to a value of 54 mm estimated previously for Eucalyptus globulus (Cernusak et al., 2005). Analysis of D18Op in stem dry matter likely provides an advantage over analysis of leaf dry matter for data sets such as ours, which comprise diverse sets of species, because ecp for stem dry matter tends to be less variable within and among species than ecp for leaf dry matter (Borella et al., 1999; Barbour et al., 2001; Cernusak et al., 2004, 2005). Given a sound theoretical understanding of sources of variation in d13C and d18O in plant dry matter, it should be possible to use such isotopic data to con- strain physiological models of tropical forest trees. Data from the present experiment support the sug- gestion that measurements of d13C can be used to make time-integrated estimates of ci/ca at the tree or stand scale. The photosynthetic rate, A, can then be pre- dicted from ci, assuming ca is known or can be pre- dicted. Finally, gs can be calculated from A, ci, and ca. An example of this modeling approach was recently provided (Buckley, 2008), along with a discussion of its advantages and disadvantages. In the case of d18O, it should be possible to use this signal to reconstruct the ratio of ambient to intercellular vapor pressures, ea/ei, during photosynthesis (Farquhar et al., 1989b; Sternberg et al., 1989). The strong relationship that we observed between stem dry matter D18Op and the predicted D18Oe (Fig. 9) supports this idea. However, our analysis also confirmed that the relationship be- tween D18Op and D 18Oe was further modified by tran- spiration rate, E, suggesting that it may be necessary to obtain information independently about E to calculate ea/ei from D 18Op. Such information might be obtained from sap flux measurements or eddy covariance data, for example. Assuming ea is known or can be pre- dicted, an estimate of ei based on D 18Op might then be particularly valuable, as it was recently suggested that the leaf-to-air vapor pressure difference, ei-ea, will likely be an important control over productivity in tropical forest trees in the face of changing climate (Lloyd and Farquhar, 2008). CONCLUSION We observed that 1/r was an important control over relative growth rate, r, in a diverse group of seedlings grown under tropical field conditions, including gym- nosperm trees, angiosperm trees, and angiosperm lianas. The gymnosperm trees generally had lower 1/r and r than the angiosperm species, and this may have reflected differences in the hydraulic efficiency of plant biomass among functional groups. Additionally, we observed that An, the photosynthetic NUE, was the primary control over whole-plant NUE, and that the gymnosperm species appeared to be at a significant disadvantage with respect to this trait compared to angiosperm species. Variation in whole-plant water use efficiency among species was primarily controlled by ci/ca, which in turn varied as a function of stomatal conductance. Whole-plant 13C discrimination was also controlled by ci/ca, and thus correlated with whole- plant water use efficiency. The 18O enrichment of stem dry matter of the experimental plants varied primarily as a function of the predicted 18O enrichment of evaporative site water within leaves, and secondarily as a function of the daytime MTR. Results provided quantitative information about the mechanisms con- trolling fluxes of C and water between forest trees and the atmosphere, and the coupling of these processes to plant N status. Moreover, our data set enabled rigor- ous testing of the theoretical basis for variation in 13C and 18O of plant dry matter; measurements of these stable isotope ratios could prove useful for parame- terizing forest ecosystem process models. MATERIALS AND METHODS Study Site and Plant Material The study was carried out at the Santa Cruz Experimental Field Facility, a part of the Smithsonian Tropical Research Institute, located in Gamboa, Republic of Panama (907# N, 7942# W), at an altitude of approximately 28 m above sea level. Average meteorological conditions at the study site during the experiment are shown in Table II. These values were calculated from data collected on site every 15 min by an automated weather station (Winter et al., 2001, 2005). Seedlings of Cupressus lusitanica, Pinus caribaea, and Thuja occidentalis were obtained from a commercial nursery in Chiriqui Province, Republic of Panama. All other species were grown from seed collected in the Panama Canal watershed, or obtained as seedlings from PRORENA, a native species reforestation initiative operated through the Center for Tropical Forest Science at the Smithsonian Tropical Research Institute. Familial associations for each species are shown in Table III. The species C. lusitanica and P. caribaea are conifers, with native distributions extending from Mexico to Nicaragua. T. occidentalis is a conifer native to northeastern North America, and Tectona grandis is a timber species native to south and southeast Asia. All other species included in the study occur naturally in Panama. The initial dry mass at the commencement of transpiration measurements for each species is shown in Table III; these dry masses were estimated by harvesting three to five individuals judged to be similar in size to the seedlings retained for the experiment. Seedlings were transplanted individually into 38-L plastic pots (Rubbermaid Round Brute; Consolidated). Each pot contained 25 kg of dry soil mixture, which comprised 60% by volume dark, air-dried top soil, and 40% by volume air-dried rice (Oryza sativa) husks. The rice husks were added to improve soil structure and drainage. The pot water content was brought to field capacity by the addition of 8 kg of water. The soil surface was covered with 2 kg of gravel to minimize soil evaporation, and the outer walls of each pot were lined with reflective insulation to minimize heating by Cernusak et al. 656 Plant Physiol. Vol. 148, 2008 sunlight. Ametal trellis was added to each pot containing a liana seedling. The pots were situated under a rain shelter with a glass roof, such that there was essentially no interception of rain by the pots in the otherwise open-air conditions. The initiation of measurements varied among species, due to the temporal variation in the availability of seed and seedlings. Harvest dates also varied, depending on the date of initiation of measurements and growth rates; there were three harvests in total. The start and end dates of transpiration measurements for each species are given in Table III. Growth and Transpiration Efficiency Measurements Pots were weighed at a minimum frequency of once per week to the nearest 5 g with a 64-kg capacity balance (Sartorius QS64B; Thomas). After the mass was recorded, water was added to each pot to restore it to its mass at field capacity. As plant water use increased with increasing plant size, the pots were weighed and watered more frequently. We endeavored to maintain pot water content above 5 kg at all times, such that the range of soil water contents experienced by the plants ranged approximately from field capacity to 60% of field capacity. Control pots without plants were deployed among the pots with plants in a ratio of one control pot to each six planted pots. The control pots wereweighed each week to estimate soil evaporation. Cumulative plant water use was calculated as the sum of pot water loss over the course of the experiment minus the average water loss of control pots for the same time period. Shortly before plant harvest, the pots were weighed at dawn and dusk for 2 d to calculate nighttime transpiration separately from daytime transpi- ration. Immediately following plant harvest, total plant leaf area was mea- sured with a leaf area meter (LI-3100; LI-COR). Leaves, stems, and roots were separated at harvest and oven-dried to a constant mass at 70C; theywere then weighed to the nearest 0.02 g. The mean relative growth rate, r, of each plant was calculated as r 5 [ln(mc2)2 ln(mc1)]/t, where ln(mc2) and ln(mc1) are natural logarithms of the C mass at the end and beginning of the experiment, respectively, and t is the duration of the experiment (Blackman, 1919). The MTR over the course of the experiment was calculated as the cumulative water transpired divided by the leaf area duration (Sheshshayee et al., 2005): MTR5 Et/[(LA1 1 LA2)0.5t], where Et is cumulative water transpired, and LA1 and LA2 are the leaf area at the beginning and end of the experiment, respectively. The transpiration efficiency of C gain, TEc, was calculated as TEc5 (mc22mc11 lc)/Et, where lc is the C mass of leaf litter abscised during the experiment. To compare the D experienced by species that were grown over different time periods (Table III), we calculated a growth-weighted D for each individ- ual plant. Dry matter increments were predicted at weekly time steps for each plant using relative growth rates calculated over the full experiment. Thus, the dry matter increment for week 1,w1, was calculated asw15m12m0, wherem0 was initial plant dry mass, and m1 was calculated as m1 5 m0e rt, with t 5 7 d; the r was calculated as described above. The dry matter increment in week 2, w2, was then calculated as w2 5 m2 2 m1, where m2 was calculated as m2 5 m1e rt, with t again set at 7 d, and so on. For each week during the experimental period, we also calculated an average daytime D from the meteorological data collected at 15-min intervals. Growth-weighted D, Dg, was then calculated as Dg 5 + n i51 Diwi + n i51 wi ?13? whereDi is the average daytime D for week i (kPa), and wi is the predicted dry matter increment for week i (g). In addition to calculating a growth-weighted D for each species, we also predicted a growth-weighted v. Average weekly v for each plant was predicted using a leaf energy balance model developed by D.G.G. dePury and G.D. Farquhar (unpublished data), and described by Barbour et al. (2000a). The model was parameterized with weekly average daytime values for air tem- perature, relative humidity, irradiance, and wind speed taken from the data collected by the automated weather station. Stomatal conductance for each plant, measured as described below, was further used to parameterize the model. The model predicted average weekly daytime leaf temperature for each plant. The intercellular water vapor pressure, ei, was then calculated as the saturation vapor pressure at leaf temperature, and this value was used to calculate an average weekly value of v for each plant. The growth-weighted v, vg, was then calculated as in Equation 13, but replacing Di with vi, the average daytime v for week i. In a similar fashion, we predicted a growth-weighted D18Oe for each plant. For each weekly time step, the predicted value of ea/ei was used with Equation 8 to calculate average weekly daytime D18Oe. The D 18Ov was assumed equal to 2e1, calculated from air temperature (Bottinga and Craig, 1969). Growth- weighted D18Oe, D 18Oeg, was then calculated for each plant as in Equation 13, but replacing Di with D 18Oei, the average daytime D 18Oe for week i. Leaf Gas Exchange and Leaf Temperature Measurements Wemeasured leaf gas exchange on three to five leaves per plant in the week preceding plant harvest with a Li-6400 portable photosynthesis system (LI- COR). Leaves were illuminated with an artificial light source (6400-02B LED; LI-COR) at a photon flux density of 1,200 mmol m22 s21. Measurements were made during both the morning and afternoon for each plant, and the mean of the two sets of measurements was taken for each individual. The mean leaf temperature during measurements was 32.7 6 1.5C (mean 6 1 SD), and the mean v was 1.55 6 0.46 kPa (mean 6 1 SD). Several days prior to the harvests that took place on March 11, 2006 and May 10, 2006 (Table III), we made measurements of leaf temperature with a hand-held infrared thermometer (Raytek MT Minitemp; Forestry Suppliers). Measurements were repeated two to three times on three to five leaves per plant under clear-sky conditions near midday. Values for each plant were averaged, and v was calculated from measurements of relative humidity and air temperature, assuming ei was at saturation at the average leaf temperature for each plant. Leaf temperature was not measured for the plants harvested on December 13, 2005 (Table III). Stable Isotope and Elemental Analyses Leaf, stem, and root dry matter were ground to a fine, homogeneous powder for analysis of isotopic and elemental composition. The d13C, total C, and total N concentrations were determined on subsamples of approximately 3 mg, combusted in an elemental analyzer (ECS 4010; Costech Analytical Technologies) coupled to a continuous flow isotope ratio mass spectrometer (Delta XP; Finnigan MAT). The d18O of stem dry matter was determined on subsamples of approximately 1 mg (Delta XP; Finnigan MAT), following pyrolysis in a high-temperature furnace (Thermoquest TC/EA; Finnigan MAT). Analyses were carried out at the Stable Isotope Core Laboratory, Washington State University. The d13C and d18O values were expressed in d notation with respect to the standards of PeeDee Belemnite and Vienna Standard Mean Ocean Water, respectively. The 13C discrimination of plant dry matter (D13Cp) was calculated as D 13Cp 5 (d 13Ca 2 d 13Cp)/(1 1 d 13Cp), where d13Ca is the d 13C of CO2 in air and d 13Cp is that of plant dry matter. We assumed a d13Ca of 28&. The oxygen isotope enrichment of stem dry matter (D18Op) was calculated as D 18Op 5 (d 18Op 2 d 18Os)/(1 1 d 18Os), where d 18Op is d18O of stem dry matter, and d18Os is that of irrigation (source) water. Irrigation water was drawn from two 800-L tanks, sealed to prevent evapo- ration, which were periodically refilled with tap water, to buffer against short-term variation in d18Os. The tank water had a mean d 18O of 24.3 6 0.5& (mean6 1 SD, n5 6); we therefore calculated D18Op assuming a d 18Os of24.3&. Leaf dry matter was further analyzed for P, K, and Ca concentrations by acid digestion and detection on an inductively coupled plasma optical- emission spectrometer (Perkin Elmer). Leaf samples were prepared by digesting approximately 200 mg of sample material under pressure in polytetrafluoroethylene vessels with 2 mL of concentrated nitric acid. Statistical Analyses We analyzed relationships between continuous variables using least- squares linear regression. Variation among species and among functional groups (gymnosperm trees, angiosperm trees, and angiosperm lianas) was assessed with a nested design in the general linear model routine of SYSTAT 11 (SYSTAT Software); the functional group and species nested within the functional group were taken as independent factors. For these analyses, the number of observations was 93, the degrees of freedom for the functional group was 2, the degrees of freedom for species nested within the functional group was 11, and the degrees of freedom error was 79. Pairwise comparisons among species or functional groups were then carried out according to Tukey?s method. Among the study species, there was one, Podocarpus guatemalensis, for which only one individual survived. All other species Growth, Water Use, and Stable Isotopes in Tropical Trees Plant Physiol. Vol. 148, 2008 657 comprised between five and eight individuals, as shown in Table III. Because there was only one individual of P. guatemalensis, we excluded this species from analyses aimed at assessing variation among functional groups and species. However, we included the individual in linear regression analyses of continuous variables. We considered it important to report data for this individual, as it represents the only gymnosperm species in the study native to the tropical forests of Panama. Supplemental Data The following materials are available in the on-line version of this article. Supplemental Table S1. The C and N concentrations of experimental plants. ACKNOWLEDGMENTS We thank Milton Garcia and Aurelio Virgo for technical assistance, and Ben Harlow for carrying out isotopic and elemental analyses. Received May 26, 2008; accepted June 23, 2008; published July 3, 2008. LITERATURE CITED Aerts R, Chapin FS (2000) The mineral nutrition of wild plants revisited: a re-evaluation of processes and patterns. Adv Ecol Res 30: 1?67 Atkin OK, Schortemeyer M, McFarlane N, Evans JR (1998) Variation in the components of relative growth rate in ten Acacia species from contrast- ing environments. Plant Cell Environ 21: 1007?1017 Badeck FW, Tcherkez G, Nogues S, Piel C, Ghashghaie J (2005) Post- photosynthetic fractionation of stable carbon isotopes between plant organs?a widespread phenomenon. Rapid Commun Mass Spectrom 19: 1381?1391 Barbour MM (2007) Stable oxygen isotope composition of plant tissue: a review. Funct Plant Biol 34: 83?94 Barbour MM, Andrews JT, Farquhar GD (2001) Correlations between oxygen isotope ratios of wood constituents of Quercus and Pinus samples from around the world. Aust J Plant Physiol 28: 335?348 Barbour MM, Farquhar GD (2000) Relative humidity- and ABA-induced variation in carbon and oxygen isotope ratios of cotton leaves. Plant Cell Environ 23: 473?485 Barbour MM, Farquhar GD (2004) Do pathways of water movement and leaf anatomical dimensions allow development of gradients in H2 18O between veins and the sites of evaporation within leaves? Plant Cell Environ 27: 107?121 BarbourMM, Fischer RA, Sayre KD, Farquhar GD (2000a) Oxygen isotope ratio of leaf and grain material correlates with stomatal conductance and grain yield in irrigated wheat. Aust J Plant Physiol 27: 625?637 Barbour MM, Roden JS, Farquhar GD, Ehleringer JR (2004) Expressing leaf water and cellulose oxygen isotope ratios as enrichment above source water reveals evidence of a Pe?clet effect. Oecologia 138: 426?435 Barbour MM, Schurr U, Henry BK, Wong SC, Farquhar GD (2000b) Variation in the oxygen isotope ratio of phloem sap sucrose from castor bean. Evidence in support of the Pe?clet effect. Plant Physiol 123: 671?679 Blackman VH (1919) The compound interest law and plant growth. Ann Bot (Lond) 33: 353?360 Bond WJ (1989) The tortoise and the hare: ecology of angiosperm domi- nance and gymnosperm persistence. Biol J Linn Soc 36: 227?249 Borella S, Leuenberger M, Saurer M (1999) Analysis of d18O in tree rings: wood-cellulose comparison and method dependent sensitivity. J Geo- phys Res 104: 19,267?19,273 Bottinga Y, Craig H (1969) Oxygen isotope fractionation between CO2 and water, and the isotopic composition of marine atmospheric CO2. Earth Planet Sci Lett 5: 285?295 Brodribb T (1996) Dynamics of changing intercellular CO2 concentration (ci) during drought and determination of minimum functional ci. Plant Physiol 111: 179?185 Brodribb TJ, Holbrook NM, Hill RS (2005) Seedling growth in conifers and angiosperms: impacts of contrasting xylem structure. Aust J Bot 53: 749?755 Buckley TN (2008) The role of stomatal acclimation in modelling tree adaptation to high CO2. J Exp Bot 59: 1951?1961 Cappa CD, Hendricks MB, DePaulo DJ, Cohen RC (2003) Isotopic frac- tionation of water during evaporation. J Geophys Res 108: 4525 Cernusak LA, Aranda J, Marshall JD, Winter K (2007a) Large variation in whole-plant water-use efficiency among tropical tree species. New Phytol 173: 294?305 Cernusak LA, Farquhar GD, Pate J (2005) Environmental and physiolog- ical controls over oxygen and carbon isotope composition of Tasmanian blue gum, Eucalyptus globulus. Tree Physiol 25: 129?146 Cernusak LA, Pate JS, Farquhar GD (2004) Oxygen and carbon isotope composition of parasitic plants and their hosts in southwestern Aus- tralia. Oecologia 139: 199?213 Cernusak LA, Winter K, Aranda J, Turner BL, Marshall JD (2007b) Transpiration efficiency of a tropical pioneer tree (Ficus insipida) in relation to soil fertility. J Exp Bot 58: 3549?3566 Cernusak LA, Wong SC, Farquhar GD (2003) Oxygen isotope composition of phloem sap in relation to leaf water in Ricinus communis. Funct Plant Biol 30: 1059?1070 Cornelissen JHC, Diez PC, Hunt R (1996) Seedling growth, allocation and leaf attributes in a wide range of woody plant species and types. J Ecol 84: 755?765 Craig H, Gordon LI (1965) Deuterium and oxygen-18 variations in the ocean and the marine atmosphere. In E Tongiorgi, ed, Proceedings of a Conference on Stable Isotopes in Oceanographic Studies and Palaeo- temperatures. Lischi and Figli, Pisa, Italy, pp 9?130 Cuntz M, Oge?e J, Farquhar GD, Peylin P, Cernusak LA (2007) Modelling advection and diffusion of water isotopologues in leaves. Plant Cell Environ 30: 892?909 Dongmann G, Nurnberg HW, Fo?rstel H, Wagener K (1974) On the enrichment of H2 18O in the leaves of transpiring plants. Radiat Environ Biophys 11: 41?52 Evans GC (1972) The quantitative analysis of plant growth. Blackwell Scientific, Oxford Farquhar GD, Cernusak LA, Barnes B (2007) Heavy water fractionation during transpiration. Plant Physiol 143: 11?18 Farquhar GD, Condon AG, Masle J (1994) Use of carbon and oxygen isotope composition and mineral ash content in breeding for improved rice production under favorable, irrigated conditions. In KG Cassman, ed, Breaking the Yield Barrier. International Rice Research Institute, Manila, Philippines, pp 95?101 Farquhar GD, Ehleringer JR, Hubick KT (1989a) Carbon isotope discrim- ination and photosynthesis. Annu Rev Plant Physiol Plant Mol Biol 40: 503?537 Farquhar GD, Gan KS (2003) On the progressive enrichment of the oxy- gen isotopic composition of water along leaves. Plant Cell Environ 26: 801?819 Farquhar GD, Hubick KT, Condon AG, Richards RA (1989b) Carbon isotope fractionation and plant water-use efficiency. In PW Rundel, JR Ehleringer, KA Nagy, eds, Stable Isotopes in Ecological Research, Springer-Verlag, New York, pp 21?46 Farquhar GD, Lloyd J (1993) Carbon and oxygen isotope effects in the exchange of carbon dioxide between terrestrial plants and the atmo- sphere. In JR Ehleringer, AE Hall, GD Farquhar, eds, Stable Isotopes and Plant Carbon-Water Relations. Academic Press, San Diego, pp 47?70 Farquhar GD, O?Leary MH, Berry JA (1982) On the relationship between carbon isotope discrimination and the intercellular carbon dioxide concentration in leaves. Aust J Plant Physiol 9: 121?137 Farquhar GD, Richards RA (1984) Isotopic composition of plant carbon correlates with water-use efficiency in wheat genotypes. Aust J Plant Physiol 11: 539?552 Flanagan LB (1993) Environmental and biological influences on the sta- ble oxygen and hydrogen isotopic composition of leaf water. In JR Ehleringer, AE Hall, GD Farquhar, eds, Stable Isotopes and Plant Carbon-Water Relations. Academic Press, San Diego, pp 71?89 Flanagan LB, Phillips SL, Ehleringer JR, Lloyd J, Farquhar GD (1994) Effect of changes in leaf water oxygen isotopic composition on discrimina- tion against C18O16O during photosynthetic gas exchange. Aust J Plant Physiol 21: 221?234 Gartner BL, Bullock SH, Mooney HA, Brown VB, Whitbeck JL (1990) Water transport properties of vine and tree stems in tropical deciduous forest. Am J Bot 77: 742?749 Gessler A, Peuke AD, Keitel C, Farquhar GD (2007) Oxygen isotope Cernusak et al. 658 Plant Physiol. Vol. 148, 2008 enrichment of organic matter in Ricinus communis during the diel course and as affected by assimilate transport. New Phytol 174: 600?613 Hobbie EA, Werner RA (2004) Intramolecular, compound-specific, and bulk carbon isotope patterns in C3 and C4 plants: a review and synthesis. New Phytol 161: 371?385 Hubick KT, Farquhar GD (1989) Carbon isotope discrimination and the ratio of carbon gained to water lost in barley cultivars. Plant Cell Environ 12: 795?804 Hubick KT, Farquhar GD, Shorter R (1986) Correlation between water-use efficiency and carbon isotope discrimination in diverse peanut (Arachis) germplasm. Aust J Plant Physiol 13: 803?816 Kahmen A, Simonin K, Tu KP, Merchant A, Callister A, Siegwolf R, Dawson TE, Arndt SK (2008) Effects of environmental parameters, leaf physiological properties and leaf water relations on leaf water d18O enrich- ment in different Eucalyptus species. Plant Cell Environ 31: 738?751 Koerselman W, Meuleman AFM (1996) The vegetation N:P ratio: a new tool to detect the nature of nutrient limitation. J Appl Ecol 33: 1441?1450 Laurance WF, Oliveira AA, Laurance SG, Condit R, Nascimento HEM, Sanchez-Thorin AC, Lovejoy TE, Andrade A, D?Angelo S, Ribeiro JE, et al (2004) Pervasive alteration of tree communities in undisturbed Amazonian forests. Nature 428: 171?175 LeBauer DS, Treseder KK (2008) Nitrogen limitation of net primary productivity in terrestrial ecosystems is globally distributed. Ecology 89: 371?379 Lloyd J, Farquhar GD (2008) Effects of rising temperatures and [CO2] on the physiology of tropical forest trees. Philos Trans R Soc Lond B Biol Sci 363: 1811?1817 Lloyd J, Syvertsen JP, Kriedemann PE, Farquhar GD (1992) Low conduc- tances for CO2 diffusion from stomata to the sites of carboxylation in leaves of woody species. Plant Cell Environ 15: 873?899 Long SP, Farage PK, Garcia RL (1996) Measurement of leaf and canopy photosynthetic CO2 exchange in the field. J Exp Bot 47: 1629?1642 Masle J, Farquhar GD (1988) Effects of soil strength on the relation of water-use efficiency and growth to carbon isotope discrimination in wheat seedlings. Plant Physiol 86: 32?38 Poorter H (1994) Construction costs and payback time of biomass: a whole plant perspective. In J Roy, E Garnier, eds, AWhole Plant Perspective on Carbon-Nitrogen Interactions. SPB Academic Publishing, The Hague, The Netherlands, pp 11?127 Poorter H, Remkes C (1990) Leaf-area ratio and net assimilation rate of 24 wild species differing in relative growth rate. Oecologia 83: 553?559 Poorter H, Remkes C, Lambers H (1990) Carbon and nitrogen economy of 24 wild species differing in relative growth rate. Plant Physiol 94: 621?627 Reich PB, Oleksyn J (2004) Global patterns of plant leaf N and P in relation to temperature and latitude. Proc Natl Acad Sci USA 101: 11001?11006 Ripullone F, Matsuo N, Stuart-Williams H, Wong SC, Borghetti M, Tani M, Farquhar GD (2008) Environmental effects on oxygen isotope enrichment of leaf water in cotton leaves. Plant Physiol 146: 729?736 Roden JS, Lin GG, Ehleringer JR (2000) A mechanistic model for inter- pretation of hydrogen and oxygen isotope ratios in tree-ring cellulose. Geochim Cosmochim Acta 64: 21?35 Seibt U, Rajabi A, Griffiths H, Berry JA (2008) Carbon isotopes and water use efficiency: sense and sensitivity. Oecologia 155: 441?454 Sheshshayee MS, Bindumadhava H, Ramesh R, Prasad TG, Lakshminarayana MR, Udayakumar M (2005) Oxygen isotope enrichment (D18O) as a measure of time-averaged transpiration rate. J Exp Bot 56: 3033?3039 Sperry JS, Hacke UG, Pittermann J (2006) Size and function in conifer tracheids and angiosperm vessels. Am J Bot 93: 1490?1500 Sternberg LSL, Mulkey SS, Wright SJ (1989) Oxygen isotope ratio strat- ification in a tropical moist forest. Oecologia 81: 51?56 Tanner CB, Sinclair TR (1983) Efficient water use in crop production: research or re-search. In H Taylor, ed, Limitations to Efficient Water Use in Crop Production. ASA-CSSA-SSSA, Madison, WI, pp 1?28 Tanner EVJ, Vitousek PM, Cuevas E (1998) Experimental investigation of nutrient limitation of forest growth on wet tropical mountains. Ecology 79: 10?22 Vertregt N, Penning de Vries FWT (1987) A rapid method for determin- ing the efficiency of biosynthesis of plant biomass. J Theor Biol 128: 109?119 Warren CR, Adams MA (2006) Internal conductance does not scale with photosynthetic capacity: implications for carbon isotope discrimination and the economics of water and nitrogen use in photosynthesis. Plant Cell Environ 29: 192?201 Winter K, Aranda J, Garcia M, Virgo A, Paton SR (2001) Effect of elevated CO2 and soil fertilization on whole-plant growth and water use in seedlings of a tropical pioneer tree, Ficus insipida Willd. Flora 196: 458?464 Winter K, Aranda J, Holtum JAM (2005) Carbon isotope composition and water-use efficiency in plants with crassulacean acid metabolism. Funct Plant Biol 32: 381?388 Wright IJ, Westoby M (2000) Cross-species relationships between seedling relative growth rate, nitrogen productivity and root vs leaf function in 28 Australian woody species. Funct Ecol 14: 97?107 Wright SJ (2005) Tropical forests in a changing environment. Trends Ecol Evol 20: 553?560 Yakir D, DeNiro MJ, Rundel PW (1989) Isotopic inhomogeneity of leaf water: evidence and implications for the use of isotopic signals trans- duced by plants. Geochim Cosmochim Acta 53: 2769?2773 Yakir D, Israeli Y (1995) Reduced solar irradiance effects on net primary productivity (NPP) and the d13C and d18O values in plantations of Musa sp. Musaceae. Geochim Cosmochim Acta 59: 2149?2151 Growth, Water Use, and Stable Isotopes in Tropical Trees Plant Physiol. Vol. 148, 2008 659