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Elevated atmospheric CO2 concentration improves water use efficiency and growth of a widespread Cerrado tree species even under soil water deficit

ABSTRACT

Changes in atmospheric CO2 levels are accompanied by ecological interactions involving other environmental factors, such as drought, which can severely alter the water balance of plants, thereby influencing sap flow, gas exchange, and plant growth. The objective of this study was to evaluate the water use economy, leaf gas exchange, and growth of young plants of the species Lafoensia pacari subjected to high concentrations of atmospheric CO2 ([CO2]) and soil water deficit. Increased vapor pressure deficit was observed from 1200 to 1800 hours. Plants under elevated [CO2] exhibited increased leaf photosynthesis, resulting in improved growth. Specific leaf area was lower in plants under high [CO2], mainly after soil water deficit treatment. Daily irrigated plants growing under ambient [CO2] had higher stem sap flow velocity (cm h-1) and hourly sap flow (kg h-1), mainly during the hottest hours of the day, than plants under high [CO2]. Improved water use by plants growing under high [CO2] may result in increased availability of water in the soil, partially offsetting future drought events and extending the growth period.

Keywords:
biomass allocation; leaf gas exchange; sap flow; specific leaf area; water economy

Introduction

In plant communities with a pronounced dry season, plant water economy is of great importance to ecosystem functionality (Franco 2005Franco AC. 2005. Biodiversidade de forma e função: implicações ecofisiológicas das estratégias de utilização de água e luz em plantas lenhosas do Cerrado. In: Scariot A, Souza-Silva JC, Felfili JM. (eds.) Cerrado: ecologia, biodiversidade e conservação. Brasília, Ministério do Meio Ambiente. p. 179-196.; Oliveira et al. 2005Oliveira RS, Bezerra L, Davidson EA, et al. 2005. Deep root function in soil water dynamics in cerrado savannas of central Brazil. Functional Ecology 19: 574-581; Goldstein et al. 2008Goldstein G, Meinzer FC, Bucci SJ, Scholz FG, Franco AC, Hoffmann WA. 2008. Water economy of Neotropical savanna trees: six paradigms revisited. Tree physiology 28: 395-404. ). The Brazilian Cerrado shows well-defined climatic seasonality, with a dry and cold winter and a hot and wet summer (Klink & Machado 2005Klink CA, Machado RB. 2005. Conservation of the Brazilian Cerrado. Conservation Biology 19: 707-713.). Owing to pronounced seasonal precipitation, woody species show decreased stomatal conductance (gs), leaf transpiration rates (E), and net photosynthesis during the dry season (Moraes & Prado 1998Moraes, JAPV, Prado, CHBA 1998. Photosynthesis and water relations in cerrado vegetation. In: Scarano FR, Franco AC. (eds.) Ecophysiological strategies of xerophytic and amphibious plants in the neotropics. Series Oecologia Brasiliensis. Rio de Janeiro, UFRJ. p. 45-63.; Franco 2002Franco AC. 2002. Ecophysiology of woody plants. In: Oliveira PS, Marquis RJ. (eds.) The Cerrados of Brazil: ecology and natural history of a neotropical savanna. New York, Columbia University Press. p. 178-197.; Bucci et al. 2004Bucci SJ, Goldstein G, Meinzer FC, Scholz FG, Franco AC, Bustamante M. 2004. Functional convergence in hydraulic architecture and water relations of tropical savanna trees: from leaf to whole plant. Tree Physiology 24: 891-899. ; Prado et al. 2004Prado CHBA, Wenhui Z, Cardoza Rojas MH, Souza GM. 2004. Seasonal leaf gas exchange and water potential in a woody cerrado species community. Brazilian Journal of Plant Physiology 16: 7-16. ). Stomatal control of water loss results in low variations in leaf water potential between the dry and rainy seasons (Franco 1998Franco AC. 1998. Seasonal patterns of gas exchange, water relations and growth of it Roupala montana, an evergreen savanna species. Plant Ecology 136: 69-76.). The stomatal control of transpiration in adult woody Cerrado species is more dependent on the vapor pressure deficit (VPD), which is twofold higher in the dry season compared to the rainy season (Bucci et al. 2004Bucci SJ, Goldstein G, Meinzer FC, Scholz FG, Franco AC, Bustamante M. 2004. Functional convergence in hydraulic architecture and water relations of tropical savanna trees: from leaf to whole plant. Tree Physiology 24: 891-899. ; 2008Bucci SJ, Scholz FG, Goldstein G, et al. 2008. Water relations and hydraulic architecture in Cerrado trees: adjustments to seasonal changes in water availability and evaporative demand. Brazilian Journal of Plant Physiology 20: 233-245. ), than on soil water availability (Meinzer et al. 1999Meinzer FC, Goldstein G, Franco AC, et al. 1999. Atmospheric and hydraulic limitations on transpiration in Brazilian cerrado woody species. Functional Ecology 13: 273-282. ; Naves-Barbiero et al. 2000Naves-Barbiero CC, Franco AC, Bucci SJ, Goldstein G. 2000. Fluxo de seiva e condutância estomática de duas espécies lenhosas sempre-verdes no campo sujo e cerradão. Revista Brasileira de Fisiologia Vegetal 12: 119-134.). However, for juvenile woody Cerrado species, soil water deficit plays an important role in leaf transpiration (Costa et al. 2015Costa AC, Rezende-Silva SL, Megguer CA, Moura LMF, Rosa M, Silva AA. 2015. The effect of irradiance and water restriction on photosynthesis in young jatobá-do-cerrado (Hymenaea stigonocarpa) plants. Photosynthetica 53: 118-127. ), since juvenile plants have shallow root systems and compete with herbaceous species for water (Hoffmann et al. 2004aHoffmann WA, Lucatelli VM, Silva FJ, et al. 2004a. Impact of the invasive alien grass Melinis minutiflora at the savanna‐forest ecotone in the Brazilian Cerrado. Diversity and Distributions 10: 99-103.; Rossatto et al. 2012Rossatto DR, Sternberg LSL, Franco AC. 2012. The partitioning of water uptake between growth forms in a neotropical savanna: do herbs exploit a third water source niche? Plant Biology 15: 84-92.). In addition to ontogenetic differences for the control of transpiration, in the Cerrado, root depth varies among species with contrasting leaf habitat (deciduous versus evergreens) and life forms (trees, shrubs, and grass), resulting in distinct patterns of water relations (Rossatto et al. 2012Rossatto DR, Sternberg LSL, Franco AC. 2012. The partitioning of water uptake between growth forms in a neotropical savanna: do herbs exploit a third water source niche? Plant Biology 15: 84-92.).

To our knowledge, no studies have examined the influence of elevated atmospheric CO2 concentration ([CO2]) on stem sap flow in woody species and the consequences of water economy in the plants in Cerrado physiognomies. Shifts in CO2 may result in great changes in crown functionality in plant species (Cramer et al. 2001Cramer W, Bondeau A, Woodward FI, et al. 2001. Global response of terrestrial ecosystem structure and function to CO2 and climate change: results from six dynamic global vegetation models. Global Change Biology 7: 357-373. ). Because plant transpiration is the main regulator of mass and energy exchange between the atmosphere and vegetation (Baldocchi & Meyers 1998Baldocchi D, Meyers T. 1998. On using eco-physiological, micrometeorological and biogeochemical theory to evaluate carbon dioxide, water vapor and trace gas fluxes over vegetation: a perspective. Agricultural and Forest Meteorology 90: 1-25.), understanding the influence of long-term rising [CO2] on water use by woody species is important for the modeling of future atmospheric conditions (Uddling et al. 2008Uddling J, Teclaw RM, Kubiske ME, Pregitzer KS, Ellsworth DS. 2008. Sap flux in pure aspen and mixed aspen-birch forests exposed to elevated concentrations of carbon dioxide and ozone. Tree Physiology 28: 1231-1243.). Sap flow in plants grown under high [CO2] decreases as gs decreases (Wullschleger & Norby 2001Wullschleger SD, Norby RJ. 2001. Sap velocity and canopy transpiration in a sweetgum stand exposed to free‐air CO2 enrichment (FACE). New Phytologist 150: 489-498. ; Gunderson et al. 2002Gunderson CA, Sholtis JD, Wullschleger SD, Tissue DT, Hanson PJ, Norby RJ. 2002. Environmental and stomatal control of photosynthetic enhancement in the canopy of a sweetgum (Liquidambar styraciflua L.) plantation during 3 years of CO2 enrichment. Plant, Cell & Environment 25: 379-393. ; Cech et al. 2003Cech PG, Pepin S, Körner C. 2003. Elevated CO2 reduces sap flux in mature deciduous forest trees. Oecologia 137: 258-268. ). These decreases will result in decreased leaf transpiration and increased water-use efficiency (WUE) by plants in the plant community (Battipaglia et al. 2013Battipaglia G, Saurer M, Cherubini P, et al. 2013. Elevated CO2 increases tree‐level intrinsic water use efficiency: insights from carbon and oxygen isotope analyses in tree rings across three forest FACE sites. New Phytologist 197: 544-554. ). The decreased plant transpiration due to elevated [CO2] could result in a decrease in relative air humidity, even at a regional scale (Leuzinger & Korner 2007Leuzinger S, Körner C. 2007. Water savings in mature deciduous forest trees under elevated CO2. Global Change Biology 13: 2498-2508. ; Keenan et al. 2013Keenan TF, Hollinger DY, Bohrer G, et al. 2013. Increase in forest water-use efficiency as atmospheric carbon dioxide concentrations rise. Nature 499: 324-327. ).

The importance of the influence of rising [CO2] on the plant transpiration is related to whether the vegetation is under anthropogenic pressure, as is observed in the Cerrado (Klink & Machado 2005Klink CA, Machado RB. 2005. Conservation of the Brazilian Cerrado. Conservation Biology 19: 707-713.). Cerrado deforestation contributes not only to the deregulation of the local climate but also to the length of the dry season in Amazonian sites (Costa & Pires 2010Costa MH, Pires GF. 2010. Effects of Amazon and Central Brazil deforestation scenarios on the duration of the dry season in the arc of deforestation. International Journal of Climatology 30: 1970-1979. ). In Cerrado sensu lato, the effects of rising [CO2] are combined with increased soil water deficit, making plants exhibit more efficient carbon gain, even under soil water deficit (Souza et al. 2016Souza JP, Melo NM, Pereira EG, Halfeld AD, Gomes IN, Prado CHB. 2016. Responses of woody Cerrado species to rising atmospheric CO2 concentration and water stress: gains and losses. Functional Plant Biology 43: 1183-1193. ). In addition, high [CO2] could potentially change biomass partitioning towards aerial structures in woody species, which benefits them when competing with herbaceous plants (Melo et al. 2018Melo NMJ, Rosa RSEG, Pereira EG, Souza JP. 2018. Rising [CO2] changes competition relationships between native woody and alien herbaceous Cerrado species. Functional Plant Biology 45: 854-864. ). Thus, the synergism between CO2 and water availability could intensify the responses of woody species under changes in regional climate (Keenan et al. 2013Keenan TF, Hollinger DY, Bohrer G, et al. 2013. Increase in forest water-use efficiency as atmospheric carbon dioxide concentrations rise. Nature 499: 324-327. ).

Lafoensia pacari (Lythraceae) is a widespread tree species in Cerrado areas, occurring in 74 % of 376 areas analyzed by Ratter et al. (2003Ratter JA, Bridgewater S, Ribeiro JF. 2003. Analysis of the floristic composition of the Brazilian cerrado vegetation III: comparison of the woody vegetation of 376 areas. Edinburgh Journal of Botany 60: 57-109.) and in Atlantic forest remnants in São Paulo, Brazil (Kortz et al. 2014Kortz AR, Coelho S, Castello ACD, Corrêa LS, Leite EC, Koch I. 2014. Wood vegetation in Atlantic rain forest remnants in Sorocaba (São Paulo. Brazil). Check List 10: 344-354. ). Besides, L. pacari possesses ethnopharmacological importance, with the leaves being used for wound healing and treating cutaneous mycoses and gastritis (Pereira et al. 2018Pereira LOM, Vilegas W, Tangerina MMP, et al. 2018. Lafoensia pacari A. St.-Hil.: Wound healing activity and mechanism of action of standardized hydroethanolic leaves extract. Journal of Ethnopharmacology 219: 337-350. ). In this study, we aimed to evaluate the growth, stem sap flow, leaf water potential, leaf gas exchange, chlorophyll content, and biomass partitioning in young L. pacari plants grown under ambient or high [CO2]. We also investigated the influence of soil water deficit in plants growing under distinct [CO2]. Owing to the rising [CO2] in the atmosphere, we expected decreased stem sap flow and gs in L. pacari plants. Hence, plants grown under elevated [CO2] were expected to become more efficient in water use, even with soil water deficit. Thus, the increase in [CO2] may benefit L. pacari plants, making them more efficient in saving water and thereby increasing leaf gas exchange and growth.

Materials and methods

Plant materials, soil characteristics, and experimental design

The species utilized in the experiment was Lafoensia pacari A. St.-Hil, which exhibits arboreal characteristics, occurring in Cerrado sensu stricto areas and in forest vegetation in Cerrado sensu lato areas (Santos et al. 2009Santos LW, Coelho MFB, Pirani FR. 2009. Phenology of Lafoensia pacari A. St.-Hil.(Lythraceae) in Barra do Garças, Mato Grosso State, Brazil. Revista Brasileira de Plantas Medicinais 11: 12-17. ). The soil utilized for the growth of L. pacari plants was typical of Cerrado sensu stricto areas in Minas Gerais state, Brazil, and has been described by Souza et al. (2016Souza JP, Melo NM, Pereira EG, Halfeld AD, Gomes IN, Prado CHB. 2016. Responses of woody Cerrado species to rising atmospheric CO2 concentration and water stress: gains and losses. Functional Plant Biology 43: 1183-1193. ).

L. pacari (approximately three months old) seedlings were acquired and transferred to the soil in 10 L plastic pots. The treatments with distinct [CO2] were as follows: two open-top chambers (OTCs) with 40 plants under ambient [CO2] (430 ppm), and two OTCs with 40 plants under high [CO2] (700 ppm). The OTCs used in this experiment were as described by Melo et al. (2018Melo NMJ, Rosa RSEG, Pereira EG, Souza JP. 2018. Rising [CO2] changes competition relationships between native woody and alien herbaceous Cerrado species. Functional Plant Biology 45: 854-864. ). After all plants were 270 days old, with 245 days under an atmosphere enriched with CO2, the plants were divided into four treatments: 20 plants under ambient [CO2], watered daily; 20 plants under ambient [CO2], with cyclical suspension of watering; 20 plants under high [CO2], watered daily; and 20 plants under high [CO2], with cyclical suspension of watering. Soil water deficit was introduced thrice during the experiment by halting irrigation one month before the fourth (360 days old), fifth (450 days old), and sixth (540 days old) morphophysiological surveys. After each survey, all seedlings were watered daily until the next cycle. Air temperature and humidity were measured throughout the experimental period to calculate VPD according to Jones (1992Jones HG. 1992. Plants and microclimate: A quantitative approach to environmental plant physiology. 2nd. edn. Cambridge, Cambridge University Press. ).

Leaf gas exchange and chlorophyll content index

Leaf gas exchange and chlorophyll content index (CCI) values were determined in two leaves in five individuals (n = five individuals per treatment) in each treatment. All leaves used were totally expanded without signs of senescence or herbivory. The measurements were made when plants were 90, 180, 270, 360, 450, and 540 days old and were under high atmospheric [CO2] for 60, 155, 245, 335, 425, and 515 days. The total chlorophyll was determined using clorofiLOG (model CFL 1030; FALKER Porto Alegre, Rio Grande do Sul, Brazil). Leaf gas exchange was measured with an infrared gas analyzer (model LCA-4; Analytical Development Company, Hodesdon, UK), working in open mode (atmospheric air is passed through a chamber containing the leaf, which is dispensed after the second analysis). To saturate leaf photosynthesis (photosynthetic photon flux density = 1500 μmol m-2 s-1), a light source (PLU-002; ADC) attached to a narrow Parkinson Leaf Chamber (PLCN-4) was used. Leaf temperature (25-27 °C) inside the PLCN-4 was maintained using a Peltier system. Leaf gas exchange measurements were made between 0800 and 1100 hours, the optimal period for leaf gas exchange for Cerrado species (Prado & Moraes 1997Prado CHBA, Moraes JAPV. 1997. Photosynthetic capacity and specific leaf mass in twenty woody species of Cerrado vegetation under field conditions. Photosynthetica 33: 103-112.). The following leaf gas exchange parameters were measured: maximum net photosynthesis (P N , μmol m-2 s-1), stomatal conductance (gs, mol m-2 s-1), and leaf transpiration rate (E, mmol m-2 s-1). From the values of P N and E, we obtained WUE = P N /E, μmol mmol-1.

Leaf water potential

The same individuals used to determine leaf gas exchange parameters were used to obtain leaf water potential (Ψleaf) values in the same period and plant age. Two leaves per individual (n = five individuals per treatment) were used for each treatment. All leaves were detached from shoots for immediate determination of Ψleaf using a portable digital pression chamber (SKPM model 1400/80; Skye Instruments Ltd.).

Stem sap flow

Sap flow was determined in the stem base in five individuals for each treatment at the end of the experiment when the plants were 540 days old. Sap flow velocity was determined by multiplying raw heat pulse velocity by correction factors (thermal diffusivity, asymmetry of alignment, and wound coefficient). Sap flow (in kilograms) was calculated by multiplying sap velocity by sap wood area (Burgess 2014Burgess S. 2014. SFM1 Sap flow meter manual. Version 4.0. Armidale, ICT International.). Sap flow was monitored for three days in each plant using a sap flow meter (ICT, model SFM1) by the heat ratio method (Burgess et al. 2000Burgess SS, Adams MA, Bleby TM. 2000. Measurement of sap flow in roots of woody plants: a commentary. Tree Physiology 20: 909-913.). Before the stem sap flow measurements, the active xylem area was determined in five individuals per treatment. Each of the five individuals was cut at the stem base and then submerged in a beaker with 2 % methylene blue. The beaker was covered with plastic to avoid dye evaporation. The plants were maintained for two days with the stem base submerged in the dye solution, and the stem was then cut; the region dyed blue was considered the active xylem area. The outer and inner diameters of the stained area were measured, and the active xylem area was determined according to methods described by Naves-Barbiero et al. (2000Naves-Barbiero CC, Franco AC, Bucci SJ, Goldstein G. 2000. Fluxo de seiva e condutância estomática de duas espécies lenhosas sempre-verdes no campo sujo e cerradão. Revista Brasileira de Fisiologia Vegetal 12: 119-134.).

Leaf area and plant biomass

A group of five individuals for each treatment was used for leaf, stem, and root dry mass and leaf area measurements. Data collection was performed when plants were 90, 180, 270, 360, 450, and 540 days old and were grown in elevated [CO2] for 65, 155, 245, 335, 425, and 515 days. Stem dry mass was determined after all buds and leaves were removed, when the leaf area and mass were measured (the same leaves removed from the stems). The root dry mass measurement was performed together with stem dry mass determination. Leaf area was calculated with Image-Pro software, 5.0 (Media Cybernetics, Inc., Silver Spring, MD, USA). Leaves, stems, and roots were dried out in a stove with air circulation (TECNAL TE -394/3; Piracicaba, São Paulo, Brasil) at 60 °C to a constant weight (Pérez-Harguindeguy et al. 2013Pérez-Harguindeguy N, Díaz S, Garnier E, et al. 2013. New handbook for standardised measurement of plant functional traits worldwide. Australian Journal of Botany 61: 167-234.), and the masses were measured using an analytical balance (Series BL-320H; Shimadzu, Tokyo, Japan). All leaves on the stems were considered independently of size and age. The leaf area per stem was determined by the sum of all leaf areas in the same individual.

Shoot-foliage relationships

From the determination of morphological traits (mass and area of leaves and length and mass of stems and roots), the following biometric indices were calculated: specific leaf area (SLA; cm2 g-1), root/stem ratio (RSR; g g-1), and leaf area ratio (LAR; cm2 g-1).

Vegetative morphometry

The lengths and diameters of stems and numbers of leaves were determined in 10 individuals per species in plants under high and ambient [CO2]. Stem length was measured by using a millimeter ruler, and a caliper was used to determine the diameter at the stem base. Total leaf number was registered weekly, when diameters and lengths of stems were determined. These measurements were initiated after 90 days of beginning the experiment (DBE). Two leaves for each individual (n = 10 individuals per treatment) were marked, and development was observed to determine leaf life span (LLS) from emergence until senescence (more than 90 % yellowing) or abscission. The same leaves previously marked for LLS measurement were utilized to calculate the leaf expansion interval (LEI; days to full expansion) and leaf expansion rate (LER; mature leaf area divided by LEI cm2 days-1).

Statistical analyses

For the first 245 DBE, the experiment had randomized blocks in a 2 × 3 factorial design, with two [CO2] levels (430 and 700 ppm) and three measurement dates. After 245 DBE, the experiment had randomized blocks in a 2 × 2 × 3 factorial design, with two [CO2] levels (430 and 700 ppm), two water levels (with and without soil water deficit), and three measurement dates. The average values and standard errors were calculated for all morphophysiological and phenological traits measured in L. pacari plants. Analysis of variance and post-hoc Tukey’s tests were applied to evaluate differences between treatments. The R program was used to perform all statistical analyses (R Development Core Team 2014R Development Core Team. 2014. A language and environment for statistical computing. Vienna, R Foundation for Statistical Computing. http://www.R-project.org/. 19 Aug. 2016.
http://www.R-project.org/...
). To verify the degree of correlation between VPD and stem sap flow, we used Spearman’s correlation coefficient (Rs) because the entire data set did not demonstrate normal distribution. These correlations were performed using the OriginPro program, version 8.0 (http://www.OriginLab.com/).

Results

Leaf gas exchange, leaf water potential, chlorophyll content, and WUE

PN values were higher in plants grown under elevated [CO2] than under ambient [CO2] during the experimental period, even under soil water deficit, being more evident at 515 DBE (p < 0.05, interactions between CO2 and DBE, and between CO2, water, and DBE; Fig. 1). For the first 245 DBE, plants under ambient [CO2] showed higher gs and E than plants under high [CO2] did (except for E values at 155 DBE, p < 0.05, interactions between DBE and CO2; Fig. 1). Importantly, at 515 DBE, high values of gs were found in plants under elevated [CO2] and soil water deficit (p < 0.05, interactions between CO2, water, and DBE; Fig. 1).

Figure 1
Leaf gas exchange in Lafoensia pacari plants grown under ambient [CO2] (watered daily ○, and cyclical suspension of watering ▽) or high [CO2] (watered daily ●, and cyclical suspension of watering ▼). P N = maximum net photosynthesis (A); gs = stomatal conductance (B); E = leaf transpiration rate (C); WUE = water-use efficiency (D); Ψleaf = leaf water potential (E); Total chl = index of total chlorophyll (F). Symbols represent averages (n = 5), and bars represent ± standard error values. Asterisks indicate differences among CO2, water, or periods of measurement: *, main effect; **, double interaction; ***, triple interaction. DBE, days after beginning the experiment. Dashed line indicates the beginning of water deficit treatment.

Plants under elevated [CO2] showed higher WUE than that of plants under ambient [CO2] from 60 to 245 DBE. However, after 335 DBE, there was an inversion, and plants under ambient [CO2] showed higher WUE than that of plants under elevated [CO2] (except at 425 DBE, p < 0.05, interactions between CO2 and DBE; Fig. 1).

Only after soil water deficit application, plants grown under high [CO2] showed high total chlorophyll content (p < 0.05, simple effect of CO2 or water; Fig. 1). The Ψleaf values were not influenced by [CO2]. After soil water deficit, plants irrigated daily showed less negative values of Ψleaf compared to water-stressed plants (p < 0.05, interactions between DBE and water; Fig. 1).

Stem sap flow and active xylem area

Significantly higher (p < 0.05) values of stem sap flow velocity (cm h-1) and hourly sap flow (kg h-1) were observed between 1000 and 1300 hours (Fig. 2). However, after 1300 hours, there was a decrease in stem sap flow during the hottest period of the day (high VPD values). Plants under ambient [CO2] and daily irrigation showed higher (p < 0.05) hourly sap flow, mainly at noon (double interaction between CO2 and water, p < 0.05; Fig. 2), than plants under elevated [CO2] did (double interaction between CO2 and water, p < 0.05; Fig. 2). Regardless of [CO2], plants irrigated daily showed higher sap flow velocity, mainly in the hottest period of the day (double interaction between water and hour of the day, p < 0.05; Fig. 2).

Figure 2
Vapor pressure deficit (VPD) (A), hourly sap flow (B), and stem sap flow velocity (C) in L. pacari plants grown under ambient [CO2] (watered daily ○, and cyclical suspension of watering ▽) or high [CO2] (watered daily ●, and cyclical suspension of watering ▼). Symbols represent averages (n = 5), and bars represent ± standard error values. Asterisks indicate differences among CO2, water, or hours: *, main effect; **, double interaction.

However, stem sap flow was significantly higher (p < 0.05) in plants under ambient [CO2] and daily irrigation than that of the other treatments (double interaction between CO2 and water, p < 0.05; Fig. 2). Thus, L. pacari plants grown under elevated [CO2] showed improved water use even under soil water deficit.

Correlation (p < 0.05, Tab. 1) was found only between stem sap flow velocity and VPD in L. pacari plants grown under elevated [CO2] and soil water deficit (Tab. 1).

Table 1
Spearman’s correlation coefficient between water vapor pressure deficit (VPD), stem sap flow velocity (SFV), and hourly sap flow (HSF) in plants grown under ambient [CO2] (430 ppm, watered daily and cyclical suspension of watering) or high [CO2] (700 ppm, watered daily and cyclical suspension of watering). Bold values indicate p < 0.05.

L. pacari plants grown under elevated [CO2] showed a larger active xylem area than that of plants under ambient [CO2] (main effect of CO2, p < 0.05; Tab. 2).

Table 2
Active xylem area (cm2) in plants grown under ambient [CO2] (430 ppm, watered daily and cyclical suspension of watering) or high [CO2] (700 ppm, watered daily and cyclical suspension of watering). Asterisks indicate differences between CO2 treatments (p < 0.05).

Leaf area and biomass allocation

There were no differences (p > 0.05) in average and total leaf areas among CO2 treatments until 245 DBE (Fig. 3). After soil water deficit application, plants under elevated [CO2], regardless of water treatment, showed higher leaf area values than those of plants under ambient [CO2] (p < 0.05, interactions between CO2 and DBE and water; Fig. 3).

Figure 3
Morphological traits of L. pacari plants grown under ambient [CO2] (watered daily ○, and cyclical suspension of watering ▽) or high [CO2] (watered daily ●, and cyclical suspension of watering ▼). Total leaf area (A); average leaf area (B); total leaf dry mass (C); stem dry mass (D); root dry mass (E); total dry mass (F). Symbols represent averages (n = 5), and bars represent ± standard error values. Asterisks indicate differences among CO2, water, or hours: *, main effect; **, double interaction. DBE, days after beginning the experiment. Dashed line indicates the beginning of water deficit treatment.

From 245 DBE, leaf, root, stem, and total dry masses were higher (p < 0.05) in plants under elevated [CO2], mainly after soil water deficit application (interactions between CO2 and water; Fig. 3). The total dry mass was significantly higher (p < 0.05) in plants under elevated [CO2] after 155 DBE (interactions between CO2 and DBE), even after soil water deficit application (interactions between CO2 and DBE and water; Fig. 3).

Biometric indices

There were no differences (p > 0.05) in RSRs between plants under elevated and ambient [CO2] (Fig. 4). Moreover, SLA and LAR were higher (p < 0.05) in plants under ambient [CO2] than under elevated [CO2] at 245 DBE (interactions between CO2 and DBE; Fig. 4). However, after soil water deficit application, plants under elevated [CO2] showed higher (p < 0.05) LAR than that of plants under ambient [CO2] (interactions between CO2, DBE, and water; Fig. 4). Plants under ambient [CO2] showed higher (p < 0.05) SLA, mainly after soil water deficit application (simple effect of CO2; Fig. 4).

Figure 4
Biometrical index in L. pacari plants grown under ambient [CO2] (watered daily ○, and cyclical suspension of watering ▽) or high atmospheric [CO2] (watered daily ●, and cyclical suspension of watering ▼). LAR = leaf area ratio (A); SLA = specific leaf area (B); RSR = root/stem ratio (C). Symbols represent averages (n = 5), and bars represent ± standard error values. Asterisks indicate differences among CO2, water, or hours: *, main effect; **, double interaction. DBE, days after beginning the experiment. Dashed line indicates the beginning of water deficit treatment.

Vegetative morphometry

There were no differences (p > 0.05) in LERs and LLSs between plants under elevated and ambient [CO2] (Tab. 3). However, LEI was higher (p < 0.05) in plants under elevated [CO2] than under ambient [CO2].

Table 3
Leaf development in Lafoensia pacari plants grown in ambient (430 ppm) [CO2] or high (700 ppm) [CO2].

Plants under elevated [CO2] showed higher (p < 0.05) stem diameters and lengths from 120 DBE (interactions between CO2 and DBE, Fig. 5). However, plants under elevated [CO2] showed higher (p < 0.05) leaf numbers only after 330 DBE (interactions between CO2 and DBE; Fig. 5).

Figure 5
Vegetative morphometry in L. pacari plants grown under ambient [CO2] (○) or high [CO2] (●). Leaf number (A); stem length (B); stem diameter (C). Symbols represent averages (n = 5), and bars represent ± standard error values. Asterisks indicate differences between CO2 or periods of measurement: *, main effect; **, double interaction. DBE, days after beginning the experiment.

Discussion

In the present study, L. pacari plants showed stomatal control of leaf transpiration, primarily during the hottest hours of the day, even in plants grown under elevated [CO2]. At noon, Cerrado plants show decreased leaf transpiration and stem sap flow (Naves-Barbiero et al. 2000Naves-Barbiero CC, Franco AC, Bucci SJ, Goldstein G. 2000. Fluxo de seiva e condutância estomática de duas espécies lenhosas sempre-verdes no campo sujo e cerradão. Revista Brasileira de Fisiologia Vegetal 12: 119-134.; Franco & Lutgge 2002Franco AC, Lüttge U. 2002. Midday depression in savanna trees: coordinated adjustments in photochemical efficiency, photorespiration, CO2 assimilation and water use efficiency. Oecologia 131: 356-365.), even with elevated solar radiation and atmospheric evaporative demand. In this way, the stomata confer strong control of transpiratory flow throughout the day, and this response is linked to increased vapor pressure deficit (Schulze 1993Schulze ED. 1993. Soil water deficits and atmospheric humidity as environmental signals. In: Smith JAC, Griffiths H. (eds.) Water deficits: plant responses from cell to community. Oxford, Scientific Publisher. p. 129-145.). This was more evident in L. pacari plants grown under elevated [CO2] and soil water deficit (positive correlation between VPD and sap flow velocity). For young Cerrado plants, soil water availability has a great effect over leaf gas exchange (Costa et al. 2015Costa AC, Rezende-Silva SL, Megguer CA, Moura LMF, Rosa M, Silva AA. 2015. The effect of irradiance and water restriction on photosynthesis in young jatobá-do-cerrado (Hymenaea stigonocarpa) plants. Photosynthetica 53: 118-127. ). However, in our study, the interaction between elevated [CO2] and soil water stress appeared to have made L. pacari plants more dependent on VPD for leaf gas exchange.

Plant species grown under elevated [CO2] demonstrate improved WUE (Leakey et al. 2009Leakey AD, Ainsworth EA, Bernacchi CJ, Rogers A, Long SP, Ort DR. 2009. Elevated CO2 effects on plant carbon, nitrogen, and water relations: six important lessons from FACE. Journal of Experimental Botany 60: 2859-2876. ; Keenan et al. 2013Keenan TF, Hollinger DY, Bohrer G, et al. 2013. Increase in forest water-use efficiency as atmospheric carbon dioxide concentrations rise. Nature 499: 324-327. ). Enhanced WUE is crucial because it diminishes water stress and increases the growing season (Sleen et al. 2015Sleen P, Groenendijk P, Vlam M, et al. 2015. No growth stimulation of tropical trees by 150 years of CO2 fertilization but water-use efficiency increased. Nature Geoscience 8: 24-28. ) for plant species. According to Sleen et al. (2015)Sleen P, Groenendijk P, Vlam M, et al. 2015. No growth stimulation of tropical trees by 150 years of CO2 fertilization but water-use efficiency increased. Nature Geoscience 8: 24-28. , increased WUE occurs at a pan-tropical scale, but this high WUE is not accompanied by growth stimulation. Battipaglia et al. (2013Battipaglia G, Saurer M, Cherubini P, et al. 2013. Elevated CO2 increases tree‐level intrinsic water use efficiency: insights from carbon and oxygen isotope analyses in tree rings across three forest FACE sites. New Phytologist 197: 544-554. ) found that five species under high [CO2] distributed in three FACE experiments in Italy and the United States of America showed a 70 % increase in WUE. Several published papers (Cech et al. 2003Cech PG, Pepin S, Körner C. 2003. Elevated CO2 reduces sap flux in mature deciduous forest trees. Oecologia 137: 258-268. ; Wullschleger & Norby 2001Wullschleger SD, Norby RJ. 2001. Sap velocity and canopy transpiration in a sweetgum stand exposed to free‐air CO2 enrichment (FACE). New Phytologist 150: 489-498. ; Leuzinger & Korner 2007Leuzinger S, Körner C. 2007. Water savings in mature deciduous forest trees under elevated CO2. Global Change Biology 13: 2498-2508. ; Sleen et al. 2015Sleen P, Groenendijk P, Vlam M, et al. 2015. No growth stimulation of tropical trees by 150 years of CO2 fertilization but water-use efficiency increased. Nature Geoscience 8: 24-28. ) have reported improvements in WUE for forest species; however, there are few data (Souza et al. 2016Souza JP, Melo NM, Pereira EG, Halfeld AD, Gomes IN, Prado CHB. 2016. Responses of woody Cerrado species to rising atmospheric CO2 concentration and water stress: gains and losses. Functional Plant Biology 43: 1183-1193. ) for savanna species grown under elevated [CO2] and for the consequences of WUE on water economy by plant species.

In our study, L. pacari plants grown under high [CO2] did not show decreased leaf transpiration but did exhibit higher WUE, except for 335 and 515 DBE. In these measurement periods (335 and 515 DBE), plants under elevated [CO2] showed higher gs, resulting in elevated leaf transpiration and thus, lower WUE. However, in plants under elevated [CO2], the increase in WUE was likely caused by increased leaf photosynthesis. The amount of water passing through the xylem in plants grown under high [CO2] was lower than that of plants under ambient [CO2], even producing large active xylem area. The low stem sap flow in L. pacari under elevated [CO2] might have resulted from the greater control of stomatal conductance mainly under soil water stress; however, xylem cavitation might have occurred in individuals under elevated [CO2], because under high [CO2], L. pacari produces a larger active xylem area, being more susceptible to cavitation (Bobich et al. 2010Bobich EG, Barron-Gafford GA, Rascher KG, Murthy R. 2010. Effects of drought and changes in vapour pressure deficit on water relations of Populus deltoides growing in ambient and elevated CO2. Tree Physiology 30: 866-875.).

Thus, L. pacari plants showed fine stomata control, primarily under elevated [CO2], preventing water loss and increasing WUE. Several studies have shown that elevated [CO2] influences water dynamics in the plant body, resulting in water conservation (Wullschleger & Norby 2001Wullschleger SD, Norby RJ. 2001. Sap velocity and canopy transpiration in a sweetgum stand exposed to free‐air CO2 enrichment (FACE). New Phytologist 150: 489-498. ; Cech et al. 2003Cech PG, Pepin S, Körner C. 2003. Elevated CO2 reduces sap flux in mature deciduous forest trees. Oecologia 137: 258-268. ; Leakey et al. 2009Leakey AD, Ainsworth EA, Bernacchi CJ, Rogers A, Long SP, Ort DR. 2009. Elevated CO2 effects on plant carbon, nitrogen, and water relations: six important lessons from FACE. Journal of Experimental Botany 60: 2859-2876. ; Keenan et al. 2013Keenan TF, Hollinger DY, Bohrer G, et al. 2013. Increase in forest water-use efficiency as atmospheric carbon dioxide concentrations rise. Nature 499: 324-327. ). In our study, L. pacari plants grown under elevated [CO2] showed low water use, which could result in high water availability in the soil, partially offsetting drought events and extending the growth period (Sleen et al. 2015Sleen P, Groenendijk P, Vlam M, et al. 2015. No growth stimulation of tropical trees by 150 years of CO2 fertilization but water-use efficiency increased. Nature Geoscience 8: 24-28. ). Furthermore, the high water availability in the soil may result in changes in competitive interactions among plant species (Soliveres et al. 2015Soliveres S, Maestre FT, Ulrich W, et al. 2015. Intransitive competition is widespread in plant communities and maintains their species richness. Ecology Letters 18: 790-798.). In addition, the high biomass allocation to roots linked with low water use in L. pacari plants may result in water saving in the soil profile, which would make the water readily available to young woody and herbaceous plants of the Cerrado. All these modifications could be beneficial to native plants in natural areas. However, with the decrease in the amount of water transpired, air temperature might increase, and ambient humidity and recycling of continental precipitation might decrease (Keenan et al. 2013Keenan TF, Hollinger DY, Bohrer G, et al. 2013. Increase in forest water-use efficiency as atmospheric carbon dioxide concentrations rise. Nature 499: 324-327. ). Another important ecosystem process that would be changed by elevation in [CO2] is decreased precipitation in areas that depend on water transpired in other regions (Keenan et al. 2013Keenan TF, Hollinger DY, Bohrer G, et al. 2013. Increase in forest water-use efficiency as atmospheric carbon dioxide concentrations rise. Nature 499: 324-327. ).

The lower SLA in L. pacari plants grown under elevated [CO2] indicated that these plants allocated more biomass to leaves. At high [CO2], the mesophyll resistance may increase due to increased biomass allocation to leaves (Medlyn et al. 2011Medlyn BE, Duursma RA, Zeppel MJ. 2011. Forest productivity under climate change: a checklist for evaluating model studies. Wiley Interdisciplinary Reviews: Climate Change 2: 332-355. ; Temme et al. 2015Temme AA, Liu JC, Cornwell WK, Cornelissen JH, Aerts R. 2015. Winners always win: growth of a wide range of plant species from low to future high CO2. Ecology and Evolution 5: 4949-4961. ), resulting in more resistance to leaf gas diffusion. Low SLA serves to take up more of the most limiting resource, carbon, required for optimal growth (Bloom et al. 1985Bloom AJ, Chapin III FS, Mooney HA. 1985. Resource limitation in plants-an economic analogy. Annual review of Ecology and Systematics 16: 363-392.). In this way, low SLA in L. pacari plants can reduce water vapor diffusion and contribute to water saving at the leaf level. The leaves of L. pacari also exhibit delayed development (high LEI). Souza et al. (2016Souza JP, Melo NM, Pereira EG, Halfeld AD, Gomes IN, Prado CHB. 2016. Responses of woody Cerrado species to rising atmospheric CO2 concentration and water stress: gains and losses. Functional Plant Biology 43: 1183-1193. ) and Melo et al. (2018Melo NMJ, Rosa RSEG, Pereira EG, Souza JP. 2018. Rising [CO2] changes competition relationships between native woody and alien herbaceous Cerrado species. Functional Plant Biology 45: 854-864. ) found that for three woody Cerrado species, leaf expansion was faster when the species were grown under elevated [CO2] than in plants under ambient [CO2]. However, the woody Cerrado species studied by Souza et al. (2016)Souza JP, Melo NM, Pereira EG, Halfeld AD, Gomes IN, Prado CHB. 2016. Responses of woody Cerrado species to rising atmospheric CO2 concentration and water stress: gains and losses. Functional Plant Biology 43: 1183-1193. showed high SLA under high [CO2]. Thus, L. pacari plants need more time to construct highly complex leaf cohorts under elevated [CO2], showing higher LEIs than plants under ambient [CO2]. These modifications in leaf structure (low SLA) could prevent water loss from leaves, making plants more efficient in water use.

Along with other physiological modifications, the elevation in [CO2] highlighted the influence of CO2 on the growth of Cerrado species. In a previous study, Souza et al. (2016Souza JP, Melo NM, Pereira EG, Halfeld AD, Gomes IN, Prado CHB. 2016. Responses of woody Cerrado species to rising atmospheric CO2 concentration and water stress: gains and losses. Functional Plant Biology 43: 1183-1193. ) showed that woody Cerrado plants changed their normal ontogeny, speeding up aboveground growth, mainly after 1 year of age. After 1 year, L. pacari plants showed intense biomass accumulation, mainly in the aerial parts, and exhibited better physiological performance (leaf photosynthesis and chlorophyll content). Thus, even under soil water deficit, L. pacari, similar to other woody Cerrado species grown under elevated [CO2] (Souza et al. 2016Souza JP, Melo NM, Pereira EG, Halfeld AD, Gomes IN, Prado CHB. 2016. Responses of woody Cerrado species to rising atmospheric CO2 concentration and water stress: gains and losses. Functional Plant Biology 43: 1183-1193. ), would present better aerial growth but not at the expense of root production. This shift in the biomass allocation pattern to aerial parts could make savanna species taller and decrease incoming sunlight to beneath the strata (Bond et al. 2003Bond WJ, Midgley GF, Woodward FI. 2003. The importance of low atmospheric CO2 and fire in promoting the spread of grasslands and savannas. Global Change Biology 9: 973-982. ). Because the cerrado sensu stricto (savanna) area is structured as a two-layered system (Walker & Noy-Meir 1982Walker BH, Noy-Meir I. 1982. Aspects of the stability and resilience of savanna ecosystems. In: Huntley BJ, Walker BH. (eds.) Ecology of tropical savannas. Ecological studies (analysis and synthesis). Berlin/ Heidelberg, Springer. p. 556-590. ; Nardoto et al. 1998Nardoto GB, Souza MP, Franco AC. 1998. Estabelecimento e padrões sazonais de produtividade de Kielmeyera coriacea (Spr) Mart. nos cerrados do Planalto Central: efeitos do estresse hídrico e sombreamento. Revista Brasileira de Botânica 21 doi: 10.1590/S0100-84041998000300011.; Hoffmann et al. 2004bHoffmann WA, Orthen B, Franco AC. 2004b. Constraints to seedlings success of savanna and forest tree across the savanna-forest boundary. Oecologia 140: 252-260.), the incoming light restriction beneath the strata can change competitive relationships among woody and herbaceous species (Melo et al. 2018Melo NMJ, Rosa RSEG, Pereira EG, Souza JP. 2018. Rising [CO2] changes competition relationships between native woody and alien herbaceous Cerrado species. Functional Plant Biology 45: 854-864. ).

This is the first study to demonstrate water saving by a savanna species grown under elevated [CO2]. Although only one woody species was evaluated, our findings demonstrated that CO2 elevation improved the water use, resulting in better growth capacity. Because Cerrado vegetation shows seasonal precipitation, which is important for the establishment and adaptation of Cerrado plants, the likely changes in water dynamics could alter functional processes in Cerrado areas, as well as ecological interactions (such as competition) between woody and herbaceous Cerrado species.

Acknowledgements

We thank FAPEMIG (FORTIS-TCT-10254/2014 and APQ 00281-11) for financial support.

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Publication Dates

  • Publication in this collection
    19 June 2019
  • Date of issue
    Jul-Sep 2019

History

  • Received
    03 Aug 2018
  • Accepted
    11 Mar 2019
Sociedade Botânica do Brasil SCLN 307 - Bloco B - Sala 218 - Ed. Constrol Center Asa Norte CEP: 70746-520 Brasília/DF. - Alta Floresta - MT - Brazil
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