670 BIOTROPICA 32(4a): 670?676 2000 Sources of Variability in Isoprene Emission and Photosynthesis in Two Species of Tropical Wet Forest Trees1 Manuel Lerdau and Heather L. Throop Department of Ecology and Evolution, State University of New York at Stony Brook, Stony Brook, New York 11794-5245 U.S.A. ABSTRACT Isoprene (2-methyl-1,3-butadiene), a volatile organic compound produced by many plants, is the principal source of photochemically active reduced compounds in the troposphere. Emission from tropical forest trees accounts for . 70 percent of the annual global ?ux of isoprene, and under certain environmental conditions, trees may lose a large fraction of their ?xed carbon to isoprene production. It is not known, however, if the production and emission of isoprene serve an adaptive role, or are factors that control isoprene emission from tropical trees well understood. We present results from a study investigating patterns of variability in isoprene emission and photosynthesis in two tropical wet forest tree species, Brosimum utile (H. B. K.) Pitt (Moraceae) and Dussia munda (Leguminosae/Fabaceae). We used leaf-level measurements to investigate the within- and among-individual variability in isoprene emission and photosynthetic rates, and looked at how these rates changed with light intensity. Leaves of both species showed similar responses to increases in light intensity, with photosynthesis appearing closer to saturation than isoprene emission at high light intensities. There was a large difference in both the photosynthetic and isoprene emission patterns of canopy and subcanopy leaves, with canopy leaves consistently showing much greater isoprene ?ux and photosynthetic rates than subcanopy leaves. This difference was smaller, although still discernible, when differences in speci?c leaf weight (SLW) were considered. These results suggest that tropical trees exhibit biochemical as well as structural responses to canopy position, with patterns of vertical variability that resemble those seen in temperate trees. These data have important implications for understanding the possible functional signi?cance of isoprene emission and for creating accurate canopy-level isoprene ?ux models. Key words: Brosimum utile; canopy; Dussia munda; isoprene; Panama; photosynthesis; tropical wet forest; vertical var- iation; volatile organic compounds. THE PRODUCTION AND EMISSION BY PLANTS of volatile organic compounds (VOCs) is one of the most im- portant ways in which plant processes in?uence the structure and functioning of the atmosphere (Ler- dau et al. 1997). Atmospheric photochemistry models have shown that VOC oxidation has major impacts on the residence times and concentrations of tropospheric ozone, carbon monoxide, and methane (Fehsenfeld et al. 1992, Pierce et al. 1998). In addition, studies of plant environmental physiology have demonstrated the major roles of VOCs in such diverse plant functions as herbivore defense, pollinator attraction, and stress tolerance (Lerdau et al. 1997). One of the most important VOCs in terms of both atmospheric impacts and rate of emission relative to photosynthesis is iso- prene, 2-methyl-1,3-butadiene (Fehsenfeld et al. 1992). Global models of VOC emissions have identi?ed tropical wet forests as the single most important source of isoprene, making understand- ing emission controls paramount for biosphere/at- mosphere research (Guenther et al. 1995). 1 Received 3 May 1999; revision accepted 10 November 1999. Isoprene is produced in chloroplasts and emitted through stomata immediately after production. Iso- prene-emitting plants typically expend ca 0.1?2.0 percent of their net photosynthesis on isoprene emission (Monson et al. 1994, Sharkey et al. 1996). Under conditions of water stress, however, plants can emit isoprene at a greater rate than they ?x car- bon through photosynthesis (Tingey et al. 1979, Lerdau & Keller 1997). This carbon cost suggests that there may be a bene?t to isoprene production and emission, and recent papers have suggested a role for isoprene emission in thermal stress tolerance (Sharkey & Singsaas 1995, Singsaas et al. 1997; cf. Logan & Monson 1999). The pattern of variability observed within and among plants can offer insights into the functional importance of isoprene emission and is essential for developing predictive models of emission that can be used in atmospheric chemistry. Previous research on isoprene emission variabil- ity has found a number of environmental factors that govern emission rates on varying timescales. From a given leaf at any one time, light and tem- perature are the two most important controls (Guenther et al. 1993, Sharkey & Loreto 1993). Other studies have demonstrated that isoprene emis- Sources of Variability in Tropical Isoprene Fluxes 671 sion at constant light and temperature depends upon the developmental stage of the leaf measured and its nitrogen concentration (Harley et al. 1994, Litvak et al. 1996). Experiments in controlled environ- ments have shown that the light intensity in which a leaf develops has a strong in?uence on its isoprene emission capacity (Sharkey et al. 1991, Litvak et al. 1996). These studies of controls over variability have led to the concept of `` instantaneous'' emission con- trols (controls such as light and temperature that affect the emission rate from any one leaf at any one time) and `` basal'' emission controls (those factors that explain differences in emission rates from leaves which are in identical light and temperature envi- ronments; Monson et al. 1995). While the instantaneous controls over isoprene emission variability have been investigated for more than 20 years and appear to apply similarly to plants from many different taxa and many different ecosystems, basal variability controls are not well understood, especially in plants from tropical eco- systems (Zimmerman 1979, Keller & Lerdau 1999). Research in other aspects of plant function, such as carbon gain and water use, have demon- strated that one of the most important potential sources of variability is vertical position in the can- opy. Canopy position is often tied to the light en- vironment in which leaves develop, and thus to leaf physical structure and biochemical function (Field 1983). Trees from two temperate tree genera, Liq- uidambar (Hamamelidaceae) and Quercus (Faga- ceae), have been examined and found to show sub- stantial amounts of vertical variability in isoprene emission capacity expressed on a leaf area basis. This variability has been partially, although not ful- ly, explained as resulting from the impacts of can- opy position on speci?c leaf weight (SLW; Harley et al. 1996, 1997; Sharkey et al. 1996). There, however, have not been any examinations of the patterns of vertical variability in isoprene emission from tropical trees. Studies of variability controls in tropical taxa are important to evaluate the gen- erality of patterns seen in temperate taxa, because of the importance of isoprene emission in the trop- ical atmosphere, and to develop predictive models of isoprene emission. Previous research has suggested that isoprene ?uxes from tropical ecosystems may control daily concentrations of the hydroxyl radical, and thus the redox state of the tropical troposphere (Jacob & Wofsy 1988). Earlier studies on isoprene emission from these systems have focused on instantaneous rather than basal controls (Lerdau & Keller 1997, Keller & Lerdau 1999, Lerdau & Throop 1999). This paper presents the ?rst estimates of vertical variability in isoprene emission rates within and among individuals from trees in a tropical ecosys- tem. Based on the patterns of variability observed, we were able to gain insight into the sources of variability and thus into the functional signi?cance of isoprene emission. Such insight is also a ?rst step toward incorporating variability into predictive models of isoprene emission. MATERIALS AND METHODS Research was conducted at the Fort Sherman can- opy crane, which is managed by the Smithsonian Tropical Research Institute for the United Nations Environmental Program. The canopy crane is lo- cated within Fort Sherman near the Atlantic coast of the Republic of Panama in a forest preserve site of ca 120 km2. The average annual rainfall at the site is ca 3500 mm, and all species are evergreen. The exact forest age is not known, but historical estimates suggest that it has not received intensive logging within the last 200 years. The canopy av- erage height is ca 40 m, with the tallest trees . 44 m. The crane is 52 m high and has a radial length of 54 m. This length gives a horizontal area cov- erage of ca 9000 m2. The true area coverage was slightly higher because the crane tower was located at a low point within the circle; i.e., the tower was in a streambed, and hills rose up on either side. The crane has a 1.4-m2 gondola, the position of which is controlled by a crane operator working at the top of the tower. The crane operator maintains contact with the gondola occupants by means of a two-way radio and can position the gondola any- where within the reach of the crane. The gondola is large enough for two people and the analytical equipment (described below). Measurements of photosynthesis and isoprene emission were made following the methods de- scribed by Lerdau and Keller (1997), using a LI- 6400 gas exchange system (LI-COR, Lincoln, Ne- braska) with a temperature and light controlled cu- vette and a Voyager gas chromatograph with a pho- toionization detector (Photovac-PE, Norwalk, Connecticut). The LI-6400 system incorporates thermoelectric heat exchangers mounted on the sides of the cuvette to control temperature, and a variable intensity red LED light source with a peak irradi- ance at 670 nm. Tenneson et al. (1994) have shown that the red light has no effect on isoprene emission relative to white light sources, as long as all mea- surements are made under steady-state conditions. Carbon dioxide and water vapor were measured us- 672 Lerdau and Throop ing the LI-COR open-path infrared gas analyzers. Sample air from the chamber-mounted detectors in the LI-COR could be routed directly to the gas chromatograph. A Te?ony valve was used to direct air?ow either to the gas chromatograph or to the LI-6400 reference and sample analyzers. The LI- 6400 gas exchange system uses a CO2-cartridge de- livery system to maintain constant CO2 concentra- tions in the cuvette. Tests showed that this system contained no contaminants that interfered with iso- prene measurements (data not shown). The air?ow through the LI-6400 cuvette was held constant at 200 mmol/sec. The gas chromato- graph contained a small pump that drew air at 70 mmol/sec through a 1-ml sample loop for ten sec- onds. Sample gas in the loop was valve-injected onto a 0.53-mm internal diameter CP-Sil-5 col- umn 10 m in length. The column was maintained at 408C and hydrocarbon-free air was used as the carrier gas. The detector output was linear across a broad range of isoprene concentrations, from 0 to 600 ppb, with an intercept through zero. The de- tection limit on this system was ca 2 ppb, and the precision and accuracy both were within ten per- cent of the measured value. These conditions al- lowed us to identify phytogenic isoprene emission rates of $4 nmol/m2/sec. Single-point calibrations were performed daily using a gas phase isoprene standard prepared by vaporizing and diluting pure liquid isoprene (obtained from Sigma/Aldrich, St. Louis, Missouri) according to a method recom- mended by Photovac (Anonymous 1990). These standards were compared to commercially available gravimetric standards (Scott-Marrin, Irvine, Cali- fornia) and were always found to be within ten percent. Linearity was determined for both the commercial and static dilution standards by con- ducting serial dilutions. For the daily single-point calibrations, saturated headspace of a vial contain- ing pure isoprene at known temperature (08C) was diluted once in a known volume of air to obtain a gas phase concentration within the range typically seen during emission studies, usually 100 ppb. For two species (Brosimum utile [H. B. K.] Pitt [Moraceae] and Dussia munda [Leguminosae/Faba- ceae]), variations within and among individuals for isoprene emission and photosynthetic rate were mea- sured. Both Brosimum and Dussia are common, widespread genera found throughout South and Meso-America (Gentry 1993). These two species are typical of wet forests, but other members of these genera are found in seasonal dry forests as well (Croat 1978). Characterizations were made on in- dividuals that were growing underneath the boom of the crane. Within each individual, simultaneous photosynthetic and isoprene ?ux measurements were taken on three sun leaves (in full sun at the top of the canopy) and three shade leaves (shade leaves se- lected were those in the darkest possible location easily accessible from the gondola and were at least 3 m below the top of the canopy; LAI data were not collected). Measurements were made on three individuals of B. utile and on two individuals of D. munda. Light response measurements were made on all six leaves used for each individual and were con- ducted at 308C, with light levels varying from 125 to 1760 mmol photons/m2/sec. The CO2 concen- tration in the cuvette was held at 360 ppm and the relative humidity was maintained between 60 and 85 percent. Measurements were collected between 0900 hours and 1500 h. SLW calculations were made on all six measured leaves on both D. munda individuals and on all six measured leaves on two of the three B. utile individuals. SLW was determined for each leaf measured by collecting a known area of leaf (excluding the midrib), drying it at 608C until no weight change was observed, and then weighing the leaf disks on an analytical balance. Both photosynthetic and isoprene emission rates were calculated for each leaf on both an area basis and on a per unit mass basis. The means of these rates for both sun and shade positions on each individual were calculated. For each species at each canopy position, a grand mean was calculated by determining the mean of the within-individual tree means. The change in photosynthesis and iso- prene emission between 1000 mmol photons/m2/ sec (equivalent to half of full sunlight) and 1760 mmol photons/m2/sec (the maximum light inten- sity possible with the light source) was calculated by dividing rates at 1760 mmol photons/m2/sec by rates at 1000 mmol photons/m2/sec and multiply- ing by 100. These data were arcsine-square root transformed and analyzed with a paired t-test. Mean SLWs of sun and shade leaves for each spe- cies were compared using a t-test. RESULTS All individuals of both species showed similar re- sponses in both photosynthesis and isoprene emis- sion to light intensity. The general response was a hyperbolic or rectangular hyperbolic change in iso- prene emission and photosynthesis to a linear in- crease in light intensity (Fig. 1). In general, pho- tosynthesis appeared to be closer to saturation at higher light intensities than isoprene. The mean percent change in photosynthetic rate between Sources of Variability in Tropical Isoprene Fluxes 673 FIGURE 1. Light response curves for isoprene ?ux and photosynthetic rates in (a) Brosimum utile and (b) Dussia munda. Each point represents the rates (x? 6 SE) for all measured leaves of each species. Rates are calcu- lated on a per-area basis. Open symbols represent iso- prene emissions, and closed circles represent photosyn- thesis. FIGURE 2. Light response curves of among-individ- ual and canopy position variability for isoprene ?ux and photosynthetic rates. Each point represents the x? 6 SE for all sun or shade leaves of a given individual. Rates were calculated on a per-area basis. (a) Brosimum utile photosynthesis. (b) Dussia munda photosynthesis. (c) B. utile isoprene ?ux. (d) D. munda isoprene ?ux. Open symbols are sun leaves; closed symbols are shade leaves; different shapes represent different individuals. light intensities of 1000 and 1760 mmol photons/ m2/sec (98.09% for B. utile and 117.67% for D. munda) was less than the mean percent change in isoprene emission (143.64% for B. utile and 130.49% for D. munda). For both species, the change was signi?cantly greater for isoprene than photosynthesis after an arcsine-square root trans- formation (for B. utile, transformed photosynthesis x? 5 5.67, isoprene x? 5 6.86, N 5 12, t 5 5.05, P , 0.01; for D. munda, transformed photosyn- thesis x? 5 6.22, isoprene x? 5 6.56, N 5 12, t 5 3.82, P , 0.01). Although there were notable dif- ferences among individuals in their isoprene emis- sion and photosynthetic rates at any one light in- tensity, the differences between sun- and shade-de- veloped leaves overwhelmed the among-individual variability for both processes (Fig. 2). When the mean rates were plotted together, the differences became even more apparent, with sun leaves having higher ?ux and photosynthetic rates than shade leaves on a per unit area basis (Fig. 3). By 500 mmol photons/m2/sec light, the sun leaves had sig- ni?cantly greater photosynthetic and isoprene emission rates for both species (Fig. 3). Differences were seen between the SLWs (where SLW 5 biomass:leaf area ratio) for sun and shade leaves of each species. For D. munda, sun leaves had a signi?cantly greater SLW than shade leaves (shade leaf SLW x? 5 192 g/m2, sun leaf SLW x? 5 258 g/m2; N 5 6, t 5 2.39, P , 0.05), while there was no signi?cant difference for B. utile (shade leaf SLW x? 5 180 g/m2, sun leaf SLW x? 5 169 g/m2; N 5 6, t 5 0.220, P . 0.05). It is 674 Lerdau and Throop FIGURE 3. Light response curves for sun and shade leaves. Each point represents the x? 6 SE for all sun or shade leaves for each species. Rates were calculated on a per-area basis. (a) Brosimum utile photosynthesis. (b) Dus- sia munda photosynthesis. (c) B. utile isoprene ?ux. (d) D. munda isoprene ?ux. Open symbols are sun leaves; closed symbols are shade leaves. For both species, all shade means differ signi?cantly from sun means at 500 mmol photons/m2/sec for both photosynthesis (for B. utile, t 5 3.56, df 5 10, P , 0.01; for D. munda, t 5 2.20, df 5 10, P , 0.05) and isoprene ?ux (for B. utile, t 5 2.65, df 5 10, P 5 0.01; for D. munda, t 5 5.11, df 5 10, P , 0.001). FIGURE 4. Light response curves for sun and shade leaves. Each point is the x? 6 SE for all sun or shade leaves of each species. Rates were calculated on a mass basis. (a) Brosimum utile photosynthesis. (b) Dussia mun- da photosynthesis. (c) B. utile isoprene ?ux. (d) D. munda isoprene ?ux. Open symbols are sun leaves; closed sym- bols are shade leaves. For both species, shade and sun means do not differ signi?cantly at 500 mmol photons/ m2/sec for both photosynthesis (for B. utile, t 5 1.73, df 5 10, P . 0.05; for D. munda, t 5 0.48, df 5 10, P . 0.1) and isoprene ?ux (for B. utile, t 5 1.68, df 5 10, P . 0.05; for D. munda, t 5 1.26, df 5 10, P . 0.1). possible that, particularly for D. munda, observed differences in physiological rates may have been due to variations in SLW. To test for this possibility, the mass-based overall sun vs shade light response curves were plotted; i.e., Figure 3 was replotted with units in nmol/g/h for isoprene and mmol/g/h for photosynthesis (Fig. 4). The differences be- tween sun and shade leaves, although smaller, were still apparent, indicating that SLW does not com- pletely explain the physiological differences be- tween sun and shade leaves. Sources of Variability in Tropical Isoprene Fluxes 675 DISCUSSION Differences in light environment between the can- opy and subcanopy of trees have long been asso- ciated with differences in leaf development and photosynthetic rates (Field 1983, Hirose & Werger 1987). Leaves that develop in darker subcanopy en- vironments are known to have lower SLW, and in some cases, reduced allocation of resources per unit biomass to carbon ?xation (Bjo?rkman 1981, Hi- rose & Werger 1987, Ellsworth & Reich 1993). Previous research on vertical variations in area- based isoprene emission and photosynthesis for Quercus and Liquidambar has demonstrated that most, although not all, of the variation in physio- logical rates as one moves through the canopy can be explained by changes in SLW (Harley et al. 1996, Sharkey et al. 1996). Of the differences that remain, the effect of canopy position on isoprene emission always has been found to be larger than the effect on photosynthesis. The two tropical taxa measured in this study showed similar patterns in the effects of canopy po- sition on isoprene emission and photosynthesis. The decrease in SLW of subcanopy leaves relative to can- opy leaves in D. munda mirrored a pattern com- monly observed in temperate trees. The high vari- ance of SLW in B. utile and the small sample size of this study may have obscured a similar pattern in that species. The sun/shade differences for all leaves of both species in isoprene emission rate were greater on an area basis than on a mass basis (177% greater in sun leaves at 1000 mmol photons/m2/sec for the area-based measurements and 126% greater on a mass basis). Similar, but smaller, mass- and area- based differences also were seen for photosynthesis (154% greater in sun leaves at 1000 mmol/m2/sec for the area-based measurements and 132% greater on a mass basis). Although generalizations based on so few taxa and only two vertical points are risky, these results suggest that tropical trees show the same patterns of vertical variations in gas ?uxes as tem- perate trees, perhaps to an even greater extent. Recent studies on the controls over gas ?uxes into and out of leaves have emphasized the impor- tance of SLW in determining physiological rates. In this context, SLW appears to serve as a master structural integrator of leaf-level processes and con- trols (Reich et al. 1997). The results presented here on gas exchange in B. utile and D. munda highlight the need to examine biochemical as well as struc- tural adaptations. These trees appear to show ad- justments to light availability that go beyond what can be explained by changes in SLW. It is worth noting that these adjustments were larger for iso- prene production than for photosynthesis and thus support the suggestion that isoprene emission may serve an adaptive role in helping leaves tolerate the greater thermal stress that occurs in the top of the canopy compared to the subcanopy (Sharkey et al. in press). These results, however, do not exclude the possibility that isoprene emission occurs as a nonadaptive consequence of the high light-induced up-regulation of another metabolic pathway such as the carotenoid pathway (Lerdau et al. 1997). These results also have important implications for efforts to model isoprene emission in tropical ecosystems. Emissions from these ecosystems are a major source of reduced photochemically active compounds to the troposphere. Understanding var- iations in basal emissions rates is essential to de- veloping realistic models of canopy-scale emissions (Geron et al. 1997). If the pattern observed for B. utile and D. munda is found in other tropical iso- prene-emitters, then ecosystem-scale ?ux models will need to incorporate a basal emission rate that declines with canopy depth, irrespective of changes in SLW. Clearly, an important next step will be to examine vertical variations in trace gas ?uxes for more taxa of tropical trees. The recent deployment of canopy cranes in several tropical forests now makes this strategy feasible (Lowman 1998). ACKNOWLEDGMENTS This research was supported by a NASA New Investigator Program award to ML. We thank S. J. Wright and I. Verleye for logistical support. We thank S. J. Wright, M. Garcia, and M. Samaniego for assistance in identifying plant taxa and analyzing samples, and E. Andrade and J. Herrera for operating the crane. The Smithsonian Trop- ical Research Institute and the United Nations Environ- mental Program jointly sponsor the Canopy Biology Pro- gram. Special thanks are due to the government of Den- mark for contributing the Ft. Sherman crane. LITERATURE CITED ANONYMOUS. 1990. Photovac technical bulletin no. 21. Photovac Inc., Deer Park, New York. BJO? RKMAN, O. 1981. Responses to different quantum ?ux densities. In O. Lange, P. Nobel, C. Osmond, and H. Ziegler (Eds.). Encyclopedia of plant physiology, vol. 12A, pp. 57?107. Springer-Verlag, Berlin, Germany. 676 Lerdau and Throop CROAT, T. 1978. Flora of Barro Colorado Island. Stanford University Press, Stanford, California. ELLSWORTH, D., AND P. REICH. 1993. Canopy structure and vertical patterns of photosynthesis and related leaf traits in a deciduous forest. Oecologia 96: 169?178. FEHSENFELD, F., C. CALVERT, R. FALL, P. GOLDAN, A. GUENTHER, C. HEWITT, B. LAMB, S. LIU, M. TRAINER, H. WESTBERG, AND P. ZIMMERMAN. 1992. Emission of volatile organic compounds from vegetation and the im- plications for atmospheric chemistry. Global Biogeochem. Cycles 6: 389?430. FIELD, C. 1983. Allocating leaf nitrogen for the maximization of carbon gain: leaf age as a control on the allocation program. Oecologia 56: 341?347. GENTRY, A. 1993. A ?eld guide to woody plants of northwest South America. University of Chicago Press, Chicago, Illinois. GERON, C. D., D. NIE, R. ARNTS, T. SHARKEY, E. SINGSAAS, P. VANDERVEER, A. GUENTHER, J. SICKLES, AND T. KLEIN- DIENST. 1997. Biogenic isoprene emission: model evaluation in a southeastern United States bottomland de- ciduous forest. J. Geophys. Res. 102: 18,889?18,901. GUENTHER, A., N. HEWITT, D. ERICKSON, R. FALL, C. GERON, T. GRAEDEL, P. HARLEY, L. KLINGER, M. LERDAU, W. MCKAY, T. PIERCE, B. SCHOLES, R. STEINBRECHER, R. TALLAMRAJU, J. TAYLOR, AND P. ZIMMERMAN. 1995. A global model of natural volatile organic compound emissions. J. Geophys. Res. 100: 8873?8892. , P. ZIMMERMAN, P. HARLEY, R. MONSON, AND R. FALL. 1993. Isoprene and monoterpene emission rate vari- ability: model evaluation and sensitivity analysis. J. Geophys. Res. 98: 12,609?12,617. HARLEY, P., A. GUENTHER, AND P. ZIMMERMAN. 1996. Effects of light, temperature, and canopy position on net photosynthesis and isoprene emission from sweetgum, Liquidambar styraci?ua, leaves. Tree Physiol. 16: 25?32. , , AND . 1997. Environmental controls over isoprene emission in deciduous oak canopies. Tree Physiol. 17: 705?714. , M. LITVAK, T. SHARKEY, AND R. MONSON. 1994. Isoprene emission from velvet bean leaves. Interactions between nitrogen availability, growth, photon ?ux density and leaf development. Plant Physiol. 105: 279?285. HIROSE, T., AND M. WERGER. 1987. Maximizing daily carbon photosynthesis with respect to the leaf nitrogen allocation pattern in the canopy. Oecologia 72: 520?526. JACOB, D., AND S. WOFSY. 1988. Photochemistry of biogenic emissions over the Amazon forest. J. Geophys. Res. 93: 1477?1486. KELLER, M., AND M. LERDAU. 1999. Isoprene emission from tropical forest canopy leaves. Global Biogeochem. Cycles 13: 19?29. LERDAU, M., A. GUENTHER, AND R. MONSON. 1997. Plant production and emission of volatile organic compounds. BioScience 47: 373?383. , AND M. KELLER. 1997. Controls over isoprene emission from trees in a sub-tropical dry forest. Plant Cell Environ. 20: 569?578. , AND H. L. THROOP. 1999. Isoprene emission and photosynthesis in a tropical wet forest canopy: implications for model development. Ecol. Appl. 9: 1109?1117. LITVAK, M., F. LORETO, P. HARLEY, T. SHARKEY, AND R. MONSON. 1996. The response of isoprene emission rate and photosynthesis rate to photon ?ux and nitrogen supply in aspen and white oak trees. Plant Cell Environ.19: 549?559. LOGAN, B., AND R. MONSON. 1999. Thermotolerance of leaf discs from four isoprene-emitting species is not enhanced by exposure to exogenous isoprene. Plant Physiol. 120: 821?825. LOWMAN, M. 1998. Forest canopies 1998: global perspectives. Selbyana 19: 133?134. MONSON, R., P. HARLEY, M. LITVAK, M. WILDERMUTH, A. GUENTHER, P. ZIMMERMAN, AND R. FALL. 1994. Environ- mental and developmental controls over the seasonal pattern of isoprene emission from aspen leaves. Oecologia 99: 260?270. , M. LERDAU, T. SHARKEY, D. SCHIMEL, AND R. FALL. 1995. Biological aspects of constructing biological hydrocarbon emission inventories. Atmos. Environ. 29: 2989?3002. PIERCE, T., C. GERON, L. BENDER, R. DENNIS, G. TONNESEN, AND A. GUENTHER. 1998. In?uence of increased isoprene emissions on regional ozone modeling. J. Geophys. Res. 103: 25,611?25,629. REICH, P., M. WALTERS, AND D. ELLSWORTH. 1997. From tropics to tundra: global convergence in plant functioning. Proc. Natl. Acad. Sci. 94: 13,730?13,734. SHARKEY, T., AND F. LORETO. 1993. Water stress, temperature, and light effects on the capacity for isoprene emission and photosynthesis of kudzu leaves. Oecologia 95: 328?333. , , AND C. DELWICHE. 1991. High carbon dioxide and sun/shade effects on isoprene emission from oak and aspen tree leaves. Plant Cell Environ. 14: 333?338. , AND E. SINGSAAS. 1995. Why plants emit isoprene. Nature 374: 769. , , M. LERDAU, AND C. GERON. 1999. Weather effects on isoprene emission capacity and applications in emissions algorithms. Ecological Appl. 9: 1132?1137. , , P. J. VANDERVEER, AND C. GERON. 1996. Field measurements of isoprene emission from trees in response to temperature and light. Tree Physiol. 16: 64?654 SINGSAAS, E., M. LERDAU, K. WINTER, AND T. SHARKEY. 1997. Isoprene increases thermotolerance of isoprene-emitting species. Plant Physiol. 115: 1413?1420. TENNESON, D., E. SINGSAAS, AND T. SHARKEY. 1994. Light emitting diodes as a light source for photosynthesis research. Photosynth. Res. 39: 85?92. TINGEY, D., M. MANNING, L. GROTHUS, AND W. BURNS. 1979. The in?uence of light and temperature on isoprene emission from live oak. Plant Physiol. 47: 112?118. ZIMMERMAN, P. 1979. Determination of emission rates of hydrocarbons from indigenous species of vegetation in the Tampa/St. Petersburg, Florida area. EPA 904/9-77-028. EPA, Washington, DC.