<?xml version="1.0" encoding="ISO-8859-1"?><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance">
<front>
<journal-meta>
<journal-id>2011-2173</journal-id>
<journal-title><![CDATA[Revista Colombiana de Ciencias Hortícolas]]></journal-title>
<abbrev-journal-title><![CDATA[rev.colomb.cienc.hortic.]]></abbrev-journal-title>
<issn>2011-2173</issn>
<publisher>
<publisher-name><![CDATA[Sociedad Colombiana de Ciencias Hotícolas, Universidad Pedagógica y Tecnológica de Colombia]]></publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id>S2011-21732016000100002</article-id>
<article-id pub-id-type="doi">10.17584/rcch.2016v10i1.4456</article-id>
<title-group>
<article-title xml:lang="en"><![CDATA[Spondias tuberosa trees grown in tropical, wet environments are more susceptible to drought than those grown in arid environments]]></article-title>
<article-title xml:lang="es"><![CDATA[Árboles de Spondias tuberosa que crecen en ambientes húmedos de las zonas tropicales son más susceptibles a la sequía que los cultivados en ambientes áridos]]></article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname><![CDATA[CAMARGOS ANTUNES]]></surname>
<given-names><![CDATA[WERNER]]></given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[RÊGO MENDES]]></surname>
<given-names><![CDATA[KEILA]]></given-names>
</name>
<xref ref-type="aff" rid="A02"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[RODRIGUES DE MELO CHAVES]]></surname>
<given-names><![CDATA[AGNALDO]]></given-names>
</name>
<xref ref-type="aff" rid="A03"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[OMETTO]]></surname>
<given-names><![CDATA[JEAN PIERRE]]></given-names>
</name>
<xref ref-type="aff" rid="A04"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[JARMA-OROZCO]]></surname>
<given-names><![CDATA[ALFREDO]]></given-names>
</name>
<xref ref-type="aff" rid="A05"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname><![CDATA[POMPELLI]]></surname>
<given-names><![CDATA[MARCELO FRANCISCO]]></given-names>
</name>
<xref ref-type="aff" rid="A02"/>
</contrib>
</contrib-group>
<aff id="A01">
<institution><![CDATA[,University of Maringá Department of Biology ]]></institution>
<addr-line><![CDATA[Maringá ]]></addr-line>
<country>Brazil</country>
</aff>
<aff id="A02">
<institution><![CDATA[,Federal University of Pernambuco Department of Botany Plant Ecophysiology Laboratory]]></institution>
<addr-line><![CDATA[Recife ]]></addr-line>
<country>Brazil</country>
</aff>
<aff id="A03">
<institution><![CDATA[,Tropical Semiarid Agricultural Research Center  ]]></institution>
<addr-line><![CDATA[Petrolina ]]></addr-line>
<country>Brazil</country>
</aff>
<aff id="A04">
<institution><![CDATA[,Brazilian Institute for Space Research Remote Sensing Division ]]></institution>
<addr-line><![CDATA[São José dos Campos ]]></addr-line>
<country>Brazil</country>
</aff>
<aff id="A05">
<institution><![CDATA[,University of Córdoba Faculty of Agricultural Sciences Agronomy Department]]></institution>
<addr-line><![CDATA[Montería ]]></addr-line>
<country>Colombia</country>
</aff>
<pub-date pub-type="pub">
<day>01</day>
<month>06</month>
<year>2016</year>
</pub-date>
<pub-date pub-type="epub">
<day>01</day>
<month>06</month>
<year>2016</year>
</pub-date>
<volume>10</volume>
<numero>1</numero>
<fpage>9</fpage>
<lpage>27</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http://www.scielo.org.co/scielo.php?script=sci_arttext&amp;pid=S2011-21732016000100002&amp;lng=en&amp;nrm=iso"></self-uri><self-uri xlink:href="http://www.scielo.org.co/scielo.php?script=sci_abstract&amp;pid=S2011-21732016000100002&amp;lng=en&amp;nrm=iso"></self-uri><self-uri xlink:href="http://www.scielo.org.co/scielo.php?script=sci_pdf&amp;pid=S2011-21732016000100002&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p><![CDATA[In this study, we investigated the different responses of Spondias tuberosa (umbu) trees, which grow in two different ecological life zones in northeast Brazil: tropical wet and tropical arid ecosystems. We evaluated the responses of plants grown under humid and dry conditions by measuring the photosynthesis, water status, fluorescence parameters, carbon isotopes and antioxidant system activity. The higher net photosynthesis values were recorded contemporaneously with the lower VPD values. The highest internal-to-ambient CO2 concentration and the absence of typical changes in the fluorescence parameters suggested an onset of a nonstomatal limitation in the photosynthesis. Our results showed that umbu plants can adjust their antioxidant activity during the dry season as a defensive strategy against the deleterious effects of water stress. This evidence is supported by the observed modifications in the pigment concentrations, increased accumulation of hydrogen peroxide and malondialdehyde, high levels of electrolyte leakage, increased antioxidant activity, and decreased carbon isotope discrimination in the umbu trees during the dry season. Supported by multivariate analysis of variance, significantly effect of interaction between categorical “months of collect and location” predicts a strong “dry season effect” on our dataset. Taken together, our data show that umbu trees grown in a wet tropical environment are more susceptible to drought, as compared with their tropical arid counterparts.]]></p></abstract>
<abstract abstract-type="short" xml:lang="es"><p><![CDATA[En este trabajo se investigaron las respuestas de árboles de Spondias tuberosa (umbu), que crecen en dos zonas ecológicas del nordeste de Brasil: húmeda tropical y árida tropical. Se evaluaron las respuestas de las plantas con base en fotosíntesis, estado hídrico, parámetros de fluorescencia, isotopos de carbono y actividad del sistema antioxidante. Los altos valores de las tasas de fotosíntesis fueron correlacionados con bajos valores del DPV; los altos niveles de concentración interna de CO2 y la ausencia de cambios típicos en los parámetros de fluorescencia, sugieren la aparición de una limitación no estomática de la fotosíntesis. Los resultados indicaron que las plantas de umbu pueden ajustar su actividad antioxidante durante la estación seca como una estrategia de defensa ante los efectos perjudiciales de un estrés por sequía. Esta afirmación está soportada por las modificaciones observadas en la concentración de pigmentos, incrementos en la acumulación de peróxido de hidrógeno y malondialdehido, altos niveles de electrolitos libres, incremento de la actividad antioxidante y decrecimientos en la discriminación isotópica del carbono en la localidad árida. El análisis de varianza multivariado mostró efectos significativos para la interacción “mes de colecta y localidad”, lo cual fue fuertemente predecible en la localidad. El análisis integral de los datos demostró que los árboles de umbu que crecieron en un ambiente húmedo tropical, son más susceptibles a la sequía, comparados con su contraparte de ambientes áridos tropicales.]]></p></abstract>
<kwd-group>
<kwd lng="en"><![CDATA[Caatinga]]></kwd>
<kwd lng="en"><![CDATA[carbon isotope composition]]></kwd>
<kwd lng="en"><![CDATA[global climate change]]></kwd>
<kwd lng="en"><![CDATA[nonstomatal limitations]]></kwd>
<kwd lng="en"><![CDATA[Umbuzeiro]]></kwd>
<kwd lng="en"><![CDATA[water stress]]></kwd>
<kwd lng="es"><![CDATA[Caatinga]]></kwd>
<kwd lng="es"><![CDATA[composición isotópica del carbono]]></kwd>
<kwd lng="es"><![CDATA[cambio climático]]></kwd>
<kwd lng="es"><![CDATA[limitaciones no estomáticas]]></kwd>
<kwd lng="es"><![CDATA[umbuzeiro]]></kwd>
<kwd lng="es"><![CDATA[estrés hídrico]]></kwd>
</kwd-group>
</article-meta>
</front><body><![CDATA[  <font face="verdana" size="2"> &nbsp;    <p>Doi: <a href="http://dx.doi.org/10.17584/rcch.2016v10i1.4456" target="_blank">http://dx.doi.org/10.17584/rcch.2016v10i1.4456</a></p> &nbsp;    <center>     <p><b><font size="4">Spondias tuberosa trees grown in tropical, wet environments are more susceptible to drought than   those grown in arid environments </font></b></p> </center> &nbsp;    <center>     <p><b><font size="3">&Aacute;rboles de Spondias tuberosa que crecen en ambientes h&uacute;medos de las   zonas tropicales son m&aacute;s susceptibles a la sequ&iacute;a que los cultivados en   ambientes &aacute;ridos </font></b></p> </center> &nbsp;<b>     <center>       <p>WERNER CAMARGOS ANTUNES<sup>1</sup>, KEILA RÊGO MENDES<sup>2</sup>, AGNALDO RODRIGUES DE MELO CHAVES<sup>3</sup>, JEAN     PIERRE OMETTO<sup>4</sup>, ALFREDO JARMA-OROZCO<sup>5</sup> MARCELO FRANCISCO POMPELLI<sup>2,       6</sup></p> </center> </b>     <p><sup>1</sup> Department of Biology, University of Maring&aacute;, Maring&aacute;, PR (Brazil).    <br> <sup>2</sup> Plant Ecophysiology Laboratory, Federal University of Pernambuco, Department of   Botany, CCB, Recife, PE (Brazil).     ]]></body>
<body><![CDATA[<br><sup>3</sup> Tropical Semiarid Agricultural Research Center, Embrapa Semi&aacute;rido, Petrolina,   PE (Brazil).     <br><sup>4</sup> Brazilian Institute for Space Research, Remote   Sensing Division, S&atilde;o Jos&eacute; dos Campos, SP (Brazil).     <br><sup>5</sup> Faculty of Agricultural   Sciences, Agronomy Department, University of C&oacute;rdoba, Monter&iacute;a (Colombia).     <br><sup>6</sup> Corresponding author. <a href="mailto:mfpompelli@gmail.com">mfpompelli@gmail.com</a></p>     <p>Received   for publication: 13-01-2016 Accepted for publication: 14-05-2016</p> <hr size="1">     <p><b>ABSTRACT</b></p>     <p>In   this study, we investigated the different responses of Spondias tuberosa (umbu) trees,   which grow in two different ecological life zones in northeast Brazil: tropical   wet and tropical arid ecosystems. We evaluated the responses of plants grown   under humid and dry conditions by measuring the photosynthesis, water status,   fluorescence parameters, carbon isotopes and antioxidant system activity. The   higher net photosynthesis values were recorded contemporaneously with the lower   VPD values. The highest internal-to-ambient CO<sub>2</sub> concentration and   the absence of typical changes in the fluorescence parameters suggested an   onset of a nonstomatal limitation in the photosynthesis. Our results showed   that umbu plants can adjust their antioxidant   activity during the dry season as a defensive strategy against the deleterious   effects of water stress. This evidence is supported by the observed   modifications in the pigment concentrations, increased accumulation of hydrogen   peroxide and malondialdehyde, high levels of   electrolyte leakage, increased antioxidant activity, and decreased carbon   isotope discrimination in the umbu trees during the   dry season. Supported by multivariate analysis of variance, significantly   effect of interaction between categorical “months of collect and location”   predicts a strong “dry season effect” on our dataset. Taken together, our data   show that umbu trees grown in a wet tropical   environment are more susceptible to drought, as compared with their tropical   arid counterparts.</p>       <p><b>Additional keywords: </b>Caatinga, carbon isotope composition,   global climate change, nonstomatal limitations, Umbuzeiro,   water stress.</p> <hr size="1">     <p><b>RESUMEN</b></p>     <p>En este trabajo se   investigaron las respuestas de &aacute;rboles de Spondias tuberosa (umbu), que crecen en dos zonas ecol&oacute;gicas   del nordeste de Brasil: h&uacute;meda tropical y &aacute;rida tropical. Se evaluaron las   respuestas de las plantas con base en fotos&iacute;ntesis, estado h&iacute;drico, par&aacute;metros   de fluorescencia, isotopos de carbono y actividad del sistema antioxidante. Los   altos valores de las tasas de fotos&iacute;ntesis fueron correlacionados con bajos   valores del DPV; los altos niveles de concentraci&oacute;n interna de CO<sub>2</sub> y   la ausencia de cambios t&iacute;picos en los par&aacute;metros de fluorescencia, sugieren la   aparici&oacute;n de una limitaci&oacute;n no estom&aacute;tica de la fotos&iacute;ntesis. Los resultados   indicaron que las plantas de umbu pueden ajustar su   actividad antioxidante durante la estaci&oacute;n seca como una estrategia de defensa   ante los efectos perjudiciales de un estr&eacute;s por sequ&iacute;a. Esta afirmaci&oacute;n est&aacute;   soportada por las modificaciones observadas en la concentraci&oacute;n de pigmentos,   incrementos en la acumulaci&oacute;n de per&oacute;xido de hidr&oacute;geno y malondialdehido,   altos niveles de electrolitos libres, incremento de la actividad antioxidante y   decrecimientos en la discriminaci&oacute;n isot&oacute;pica del carbono en la localidad   &aacute;rida. El an&aacute;lisis de varianza multivariado mostr&oacute; efectos significativos para   la interacci&oacute;n “mes de colecta y localidad”, lo cual fue fuertemente predecible   en la localidad. El an&aacute;lisis integral de los datos demostr&oacute; que los &aacute;rboles de umbu que crecieron en un ambiente h&uacute;medo tropical, son m&aacute;s   susceptibles a la sequ&iacute;a, comparados con su contraparte de ambientes &aacute;ridos   tropicales.</p>     ]]></body>
<body><![CDATA[<p><b>Palabras clave adicionales: </b>Caatinga, composici&oacute;n isot&oacute;pica del carbono, cambio clim&aacute;tico,   limitaciones no estom&aacute;ticas, umbuzeiro, estr&eacute;s   h&iacute;drico.</p>   <hr size="1"> &nbsp;    <p><b><font size="3">INTRODUCTION</font></b></p>     <p>Water   stress is an important factor that affects plant growth and yield, especially   in the hot and seasonally wet-dry climates in the semiarid regions of the world   (Ondrasek, 2014).</p>     <p>A   combination of drought and excess light decreases the efficiency of   photosynthesis and may also lead to leaf overheating, especially when the transpirational leaf cooling is reduced due to water   deficits (Rizhsky et al., 2004; Rizhsky et al., 2002; Valladares and Pearcy,   1997).</p>     <p>Tropical plants growing   under water stress exhibit modifications in photosynthetic processes, including disruptions in the   stomatal control of the leaf gas exchange (Arcoverde<i>et al.</i>, 2011; Lawlor and Tezara,   2009; Lima Filho, 2007; Pompelli <i>et al.</i>, 2010a; Santos <i>et al.</i>, 2013), alterations in chlorophyll fluorescence   kinetics (Faraloni<i>et</i> <i>al.</i>, 2011; Maxwell and Johnson, 2000), damage to   photosynthetic membranes (Krieger-Liszkay, 2005),   changes in the carbohydrate status (Chimenti<i>et al.</i>, 2002; Silva <i>et al.</i>, 2010), and others. The water stress-induced limitation of net   photosynthesis (<i>P</i><sub>N</sub>) may cause damage to the plant with exposure to   excess irradiance; if this energy is not safely dissipated, it may cause an overreduction of the reaction centers and increased   production of reactive oxygen species (ROS) in the chloroplasts, leading to   photosystem PSII damage (Smirnoff, 1995). </p>     <p>Knowledge of species physiology <i>in situ </i>under arid/semiarid conditions may   contribute significantly to our understanding of how to optimize productivity   in trees under drought conditions in natural environments. Data regarding species physiology under arid   conditions may also indicate how these species can be used in the regeneration   of important regions undergoing desertification. In this context, we examined <i>Spondias</i> <i>tuberosa</i> Arruda (“umbuzeiro”   or “umbu plant”), which is a small native tree that   grows naturally among Caatinga vegetation throughout   arid, semiarid and wet environments in northeastern Brazil, where it is adapted   to survive under water stress conditions (Lins Neto<i>et al.</i>, 2012). This tree is considered to   be a species with great economic, social and ecological importance to the   arid/semiarid northeast, Brazil (Lins Neto<i>et</i> <i>al.</i>, 2010). At the end of the dry season, the umbuzeiro partially shed their leaves to avoid transpiration, reducing the plant’s growth   rate, leaf initiation and leaf expansion during the drought, until the   beginning of the first rains (Cavalcanti<i>et al. </i>1996). During this period, the   survival of the species is assured by a specialized root system bearing tubers   (or xylopodia), whose function is to store water,   soluble sugars, starch, minerals, and other solutes (Lins Neto<i>et al.</i>, 2010). Old   plants growing in their native fields can have more than 1,000 xylopodia, and their fresh weight can exceed 2,000 kg.   These resources are used during the dry season to maintain normal plant   metabolism (Cavalcanti and Resende,   2006; Lima Filho, 2001; Lima Filho,   2004).</p>     <p>There are few reports describing the physiological   behavior of plants under arid conditions and their interactions with the   environment (Campos et al., 2012; Cattivelli et al.,   2008; Dombroski et al., 2011; Lima Filho, 2004). For example, Lima Filho (2004) observed that the environmental difference between the dry and rainy   seasons is the primary factor that influences the course of gas exchange in umbu trees under semiarid conditions. Nevertheless, Lima Filho (2001) suggested that, under dry conditions, the   diurnal water balance of the S. tuberosa would be   maintained at the expense of water stored in the tubers and by restricted   transpiration. In addition, Lima Filho (2007) also   noted that the gas exchange of umbu plants with fewer   tubers was more strongly affected than the gas exchange of plants with more   tubers under water-stressed soil conditions. These investigators suggested that   the root tubers may act as an important source of water under stress   conditions. However, the aforementioned studies (Lima Filho,   2001; Lima Filho, 2004; Lima Filho,   2007) only describe the gas exchange of umbu trees   under semiarid conditions and the importance of tubers in helping plants avoid   stress.</p>     <p>In this study, we hypothesized that variations in the   seasonal rainfall regime distinctly affect the ecophysiological plant performance in contrasting environments (wet and arid). It may affect the photoprotection and carbon gain and may also limit   growth in S. tuberosa trees, mostly in plants grown   in tropical wet regions, because the root mass fraction of well-watered trees   is often reduced, as compared with that of waterstressed trees reducing the photosynthetic capacity (Poorter et al., 2012). Therefore, the main objective of this study was to evaluate the   effects of the seasonal rainfall regime alterations on the plant physiological   behavior for the gas exchange and photoprotection of   S. tuberosa trees growing under wet and arid conditions in two regions of Bahia State, northeast, Brazil.</p> &nbsp;    <p><b><font size="3">MATERIALS AND METHODS</font></b></p>     <p><i><b>Site description and experimental design</b></i></p>     ]]></body>
<body><![CDATA[<p>This experiment was conducted with 2.0 to 3.0-m tall,   9-year-old <i>Spondias tuberosa</i>Arruda (Anacardiaceae) trees that were grown on   commercial plantations following appropriate cultural practices, except water   supplementation (Ara&uacute;jo, 2007). Two different   commercial plantations located in Cruz das Almas (12º35’ S; 39º15’ W; 126 m a.s.l.) and Andara&iacute; (12º48’ S;   41º19’ W; 395 m a.s.l.) in northeast Brazil were   evaluated. These two cities are at least 300 km away from each other and located   in different ecological life zones, which are tropical wet - Cruz das Almas and   tropical arid - Andara&iacute; (Tanajura <i>et al.</i>, 2010). As presented in <a href="#f1">figure 1</a>,   two seasons were observed during the study period (June 2010 to May 2011): a   dry season (precipitation less than 50 mm) and a rainy season. During the study   period, the accumulated precipitation in Cruz das Almas and Andara&iacute; was 1397±60 mm and 692±48 mm, respectively. Uniform and healthy <i>S. tuberosa </i>trees were   selected from populations at the study sites. On the plantations, the tree   density is 156 plants/ha with a spacing of 8 m x 8 m. Annually, 75 g of a   slow-release fertilizer (containing 15% N, 9% P, 12% K, 1% Mg, 2.3% S, 0.05%   Cu, 0.45% Fe, 0.06% Mn and 0.02% Mo) are applied per   plant. The fertilizer was applied at a 10-cm depth from the soil surface. In   both environments (tropical wet and tropical arid), the <i>S</i>. <i>tuberosa</i> plants   partially shed their leaves at the end of the dry season. The data were   collected from trees grown under field conditions during the humid (July 2010   and April 2011) and dry (September and November 2010) seasons. The air   temperature and rainfall during the experiment period were obtained from an   automatic weather station installed within 5 km of the experiment sites. The soil   water balance and actual evapotranspiration data were obtained from Agritempo (2013). (n=10). These parameters were measured <i>in situ</i> under clear-sky conditions. The   leaf chamber was configured to 1,000 &#956;mol m-2 s-1 saturating light from LED source and ambient   CO<sub>2 </sub>concentration (380 &#956;mol mol–1). The data were   collected at ambient conditions of temperature and relative humidity. To assess   the effect of time on <i>g</i>s and net photosynthesis (<i>P</i><sub>N</sub>), we collected data at five different times (08:00, 10:00, 12:00, 14:00   and 16:00 h; solar time), using the same leaves throughout the day on each   occasion. The chlorophyll fluorescence was measured after 30-min with   dark-adapted leaves and all of the parameters are estimated according to Genty<i>et al. </i>(1989) and Maxwell and Johnson (2000,   2008).</p>     <center>     <p><a name="f1"><a href="img/revistas/rcch/v10n1/v10n1a2f1.gif" target="_blank">Figure 1</a></a></p> </center>     <p><b>Water   potential measurements</b></p>     <p>The leaf-water potential (&#936;<sub>w</sub>) was measured using a Scholander-type   pressure chamber (mod 3005F01; Soil Moisture Equipment Corp, Santa Barbara,   CA). The measurements were taken in one leaf per plant at predawn (n=10).</p>     <p><b>Carbon   isotope composition</b></p>     <p>From each experiment tree (n=5), one expanding leaf   was collected <i>in situ </i>and it was oven-dried for 72 h at   70ºC. The isotope ratio, which was expressed as &#948;<sup>13</sup>C, was calculated as</p>     <p>    <center> <img src="img/revistas/rcch/v10n1/v10n1a2e1.gif"> </center></p>     <p>where Rsample is the <sup>13</sup>C/<sup>12</sup>C   ratio in the sample and Rstandard is the <sup>13</sup>C/<sup>12</sup>C   ratio in the standard (PDB-Pee Dee Belemnite).</p>     ]]></body>
<body><![CDATA[<p><b>Biochemical analysis</b></p>     <p>Leaf discs (1.4 cm in diameter) were collected <i>in situ </i>at 09:00-10:00 a.m. under clear-sky   conditions, rapidly frozen in liquid nitrogen, and stored at -20ºC until   analysis. Antioxidant   enzymes, including superoxide dismutase (SOD; EC 1.15.1.1), catalase (CAT; EC   1.11.1.6) and ascorbate peroxidase (APX; EC 1.11.1.11), were assayed as   described by Pompelli et al. (2010a). The H<sub>2</sub>O<sub>2</sub> was analyzed according to Chen and Kao (1999). The Malondialdehyde (MDA) was determined following Cakmak and Horst   (1991). The electrolyte leakage was assayed according to Campos et al. (2012).</p>     <p>The chlorophyll a+b and   total carotenoids were extracted with 80% (v/v) aqueous acetone and quantified   spectrophotometrically according to Pompelli et al.   (2013). &#946;-carotene, violaxanthin (V), antheraxanthin (A) and zeaxanthin (Z), were assayed by HPLC   as reported by Ramalho et al. (1999).</p>     <p><b>Statistical analysis</b></p>     <p>The data were first analyzed by multivariate analysis   of variance (MANOVA) with “month of collection and location” as categorical factors   and using as dependent variables “photosynthetic” (P<sub>N,</sub> E, g<sub>s</sub>, C<sub>i</sub>:C<sub>a</sub>,   WUE, T<sub>leaf</sub>, VPD), “photochemical” (&#934;<sub>PSII</sub>,   P, D, P<sub>E</sub>) and “enzymatic” (SOD, CAT, APX, H<sub>2</sub>O<sub>2</sub>,   MDA, electrolyte leakage) group in a GLM Bi-factorial MANOVA, for each   variable. Since the interaction effect was highly significant according to the   Wilks test in all of the performed analyses (P&#8804;0.0001), the effective   hypothesis decomposition was done with a one-way ANOVA, and the means were   compared using Duncan’s or Student’s t test. All of the statistical tests were   performed using the statistical software package Statistica version 10.0 (StatSoft, Tulsa, OK). The Lilliefors   test was conducted to assess whether the experiment errors were normally   distributed. As no transformation was needed, all of the statistical analyses   were carried out on untransformed data. The results were considered to be   significant when P&#8804;0.05. Only the 8:00h data (when applicable) were used   for the photosynthetic variable in MANOVA.</p> &nbsp;    <p><b><font size="3">RESULTS</font></b></p>     <p><b>Gas exchange measurements</b></p>     <p>Annual fluctuations in the net photosynthesis (P<sub>N</sub>),   stomata conductance (g<sub>s</sub>) and transpiration   (E) were observed for the two populations. High variations throughout the day   were observed, with a 7-fold difference between the extreme values (<a href="#f2">Fig. 2</a>).   The PN was always greater than 10 &#956;mol CO<sub>2</sub> m-<sup>2</sup> s-<sup>1</sup> during the humid season, peaking at 17.4 &#956;mol CO<sub>2</sub> m-<sup>2</sup> s-<sup>1</sup> for   plants evaluated in April under wetter climate conditions. The P<sub>N</sub> of   the tropical arid plants was consistently lower than the P<sub>N</sub> of the   tropical wet plants. By means of all of the performed MANOVA, a strong   interaction between the categorical variables “month of collect and location”   notably pointed to a generalized “dry season effect” (November) and indicated   that S. tuberosa plants have a differential behavior   in wet and arid environments in this season. Consistent with this, the November   measurements show that reductions in the P<sub>N</sub> were stronger in the   plants grown in the tropical humid environment than they for the tropical arid   counterparts</p>     <p>(<a href="#f2">Fig. 2</a>). From the humid to the dry season, the PN   decreased by 84% and 34% in the tropical wet and tropical arid plants,   respectively (<a href="#f2">figure 2</a>), and the relationship between PN and gs was significantly positive (r = 0.753; P&#8804;0.001).   When only the dry season data were analyzed, the correlations were not   significant (P=0.688), indicating circumstantially that gs could be a key factor in determining carbon uptake in a humid environment, but not in a dry one.</p>     <p>A negative relationship between the photosynthetic   parameters and PAR (r = -0.421, -0.349, and -0.339 for P<sub>N</sub>, E and gs, respectively; P&#8804;0.05) was observed. During both   seasons, the photosynthetic parameters differed significantly between the ecosystems, but these differences became stronger during the dry season (<a href="#f2">figure 2</a>).</p>     ]]></body>
<body><![CDATA[<center>     <p><a name="f2"><a href="img/revistas/rcch/v10n1/v10n1a2f2.gif" target="_blank">Figure 2</a></a></p> </center>     <p>The P<sub>N</sub>, E and g<sub>s</sub> may have decreased because of a high vapor pressure deficit (VPD), as confirmed   by their strong negative correlations (r = -0.809, -0.786, and -0.849 for PN, E   and g<sub>s</sub>, respectively; P&#8804;0.0001).</p>     <p>In the tropical wet plants, the WUE was strongly   reduced during the dry season but sharply recovered at the beginning of the   rainy season (figure 3). A similar pattern was not observed for the WUE of the   tropical arid plants, which remained constant throughout the year (<a href="#f3">figure 3</a>). A   50% increase was verified in the <i>C</i><sub>i</sub>:<i>C</i><sub>a</sub> ratio during the dry season, as compared with the   humid season in both populations (<a href="#f3">Fig. 3</a>) circumstantially indicating a   nonstomatal limitation of photosynthesis in this season. A high <i>C</i><sub>i</sub>:<i>C</i><sub>a</sub> was correlated with lower <i>P</i><sub>N</sub> and <i>E </i>values (<i>r </i>= -0.947 and   -0.877, respectively; <i>P</i>&#8804;0.0001) and a positive   relationship (<i>r </i>= 0.828; <i>P</i>&#8804;0.0001) between the <i>C</i><sub>i</sub>:<i>C</i><sub>a</sub> and &#948;<sup>13</sup>C was verified.</p>     <p>The predawn leaf water potential (&#936;<sub>pd</sub>) was higher than -1.0 MPa during   the entire study period, with the exception of November, when the lower values   were observed in the plants grown in tropical wet. This result provides evidence that the trees experienced moderate to severe water stress (<a href="#f3">figure 3</a>).</p>     <center>     <p><a name="f3"><a href="img/revistas/rcch/v10n1/v10n1a2f3.gif" target="_blank">Figure 3</a></a></p> </center>     <p><b>Chlorophyll fluorescence and   quenching</b></p>     <p>The maximum efficiency of photosystem II (F<sub>v</sub>:F<sub>m</sub> ratio) showed significant   differences (P&#8804;0.05) between the dry and humid seasons (<a href="#t1">table 1</a>). During   the dry season, there was a small reduction in the Fv:Fm ratio at midday (<a href="#t1">table 1</a>), with the lowest value found in the tropical wet   environment at November. The F<sub>v</sub>:F<sub>m</sub> ratio (table 1), &#934;PSII and P, followed similar trends (<a href="#f4">figure 4</a>). All of   these parameters in both ecosystems reached their minimum values during the dry   season and the maximum values during the humid seas P = 0.015), but they were   not correlated with the atmospheric temperature (P = 0.773). This finding   indicates that plants that were exposed to a water shortage were capable of   dissipating part of the excess energy as latent heat to minimize the water lost   by transpiration (r = -0.946; P&#8804;0.0001, between D and transpiration).</p>     <center>    ]]></body>
<body><![CDATA[<p> <a name="f4"><img src="img/revistas/rcch/v10n1/v10n1a2f4.gif"></a></a> </p></center>     <center>     <p><a name="t1"><a href="img/revistas/rcch/v10n1/v10n1a2t1.gif" target="_blank">Table 1</a></a></p> </center>     <p><b>Carbon   isotope composition</b></p>     <p>Consistent with the dry season effect predicted by   MANOVA’s performance, the plants grown in the tropical wet climate showed less   enriched &#948;<sup>13</sup>C values, as compared with the   tropical arid plants throughout the study period (<a href="#f5">figure 5</a>), with exception of   the data collected in November. During the rainy season, the &#948;<sup>13</sup>C ranged from -29.18 to -29.72‰ in the leaves of   tropical wet plants and the value in the tropical arid leaves was approximately   -28‰. During the dry season, the &#948;<sup>13</sup>C composition of the leaves from the tropical wet plants varied   substantially (3.1‰); however, the composition of the leaves from the tropical   dry plants did not vary substantially (0.6‰). The physiological responses to   drought (<a href="#f3">figure 3</a>) reflected the isotopic signature, or &#948;<sup>13</sup>C, of the leaves. A less negative isotopic signature   was observed under the drought conditions (<a href="#f5">figure 5</a>).</p>     <center>     <p><a name="f5"><a href="img/revistas/rcch/v10n1/v10n1a2f5.gif" target="_blank">Figure 5</a></a></p> </center>     <p><b><i>Biochemical   analysis</i></b></p>     <p>The chlorophyll content of the tropical wet plants was   similar to that of the tropical arid plants; however, the minimum chlorophyll   content in both climates was observed at the end of the water deficit period   (November), with the tropical arid plants showing a higher concentration than   their tropical wet counterparts (<a href="#t2">table 2</a>). Independent of the locations, the water shortages led to a reduction in the total chlorophyll (~17%).</p>     <p>The &#946; -carotene, antheraxanthin and zeaxanthin concentrations showed similar fluctuations, with gradual   increases from July to November and a decrease in April in the next year.   Significant correlations between Z and <i>D </i>(<i>r</i> = 0.558; <i>P</i>&#8804;0.0001)   and between VAZ and <i>D</i> (<i>r </i>= 0.557; <i>P</i>&#8804;0.0001) ratios were shown during the year. For   example, the thermal energy dissipation and <i>D </i>were associated with increased levels of de-epoxidated forms of A and Z within the VAZ cycle (<a href="#t2">table 2</a>) in November.</p>     ]]></body>
<body><![CDATA[<p>The SOD, CAT and APX activities were positively   interrelated. Overall, the antioxidant enzymes activities were significantly   increased (35%, 51% and 46%, respectively) in the plants grown during the dry   season, as compared with the plants grown during the humid season (<a href="#f6">figure 6</a>).   The observed elevated H<sub>2</sub>O<sub>2</sub> accumulation may promote   membrane damage and the release of MDA (<i>r </i>= 0.542; <i>P</i>&#8804;0.0001). I n fact, t he M DA level during the   dry season was 40% higher than that observed during the humid season. This   finding reflects the 80% increase in electrolyte leakage during the dry season   in both ecosystems (<a href="#f6">figure 6</a>). Indeed, the MDA level and the level of electrolyte leakage showed a strong and significant correlation (<i>r </i>= 0.701; <i>P</i>&#8804;0.0001).</p>     <center>     <p><a name="f6"><a href="img/revistas/rcch/v10n1/v10n1a2f6.gif" target="_blank">Figure 6</a></a></p> </center>     <center>     <p><a name="t2"><a href="img/revistas/rcch/v10n1/v10n1a2t2.gif" target="_blank">Table 2</a></a></p> </center> &nbsp;    <p><b><font size="3">DISCUSSION</font></b></p>     <p>The current study provides a seasonal profile of the   daily photosynthetic performance of S. tuberosa trees   grown under wet and arid conditions in natural environments. In general, the umbu plants grown in the tropical wet environments showed a   differential behavior mainly at drought when compared to the tropical arid   environment with the same stress. The multivariate and physiological analysis   points to higher susceptibility to drought for the tropical wet plants. In all   of the plants, the diurnal course PN, g<sub>s</sub>,   and E values were maximal during the midmorning and decreased in the afternoon   and those parameters did not respond toan elevated   light stimulus, most likely because Tleaf and VPD   were increased (figure 2). It is possible that these environmental factors may   have somehow affected the stomatal functioning during the day although we   cannot rule out the effect of endogenous factors related to the activity of the   circadian rhythm in modulating stomatal functioning and <i>P</i>N (Mendes and Marenco,   2014). The effect of VPD on <i>P</i>N, <i>g</i><sub>s</sub>, and <i>E </i>showed that   changes in intensity of light can alter the performance of the photosynthetic apparatus   over the course of a day irrespective of the seasonal rainfall regime. In this   study, we showed that, during the period when the water stress was most severe, <i>i.e.</i>, November, the photosynthetic rates   of the tropical arid plants were significantly higher than the rates in the   tropical wet plants, an effect that was strongly shifted at the beginning of   the rainy season, which is the opposite to what should be expected for trees   growing in a wet environment. Some investigators previously reported that S. <i>tuberosa</i> can maintain its &#936;<sub>pd</sub> at a relatively constant level   during the beginning of the dry season (Lima Filho,   2001; Lima Filho, 2004; Lima Filho,   2007; Lins Neto<i>et al.</i>, 2012). A possible explanation for this result is   that the umbu tree reduces its stomatal conductance   in response to drought early in the morning, resulting in a dramatic decline in   plant water loss and assuring significant water storage in the tubers (Lima Filho and   Silva, 1988). However, as the water in the soil decreases, which leads to   reduced water storage in the tubers, both E and gs substantially decrease as a function of &#936;<sub>pd</sub> (Lima Filho, 2004; Silva et al., 2008). S. tuberosa root tubers can serve as water storage vessels,   and a higher root mass fraction, lower leaf masses and lower total leaf areas   are observed in arid environments (Ara&uacute;jo et al.,   2009; Lima Filho, 2004; Poorter et al., 2012), which may help the plants to perform better in droughts. These   factors may play a substantial role in the amount of water supplied via tubers   and the level of water conservation in leaves to maintain a higher PN under an   extreme drought. Despite greater volume of rains in October and November in the   arid environment, all of the analyses were done after the rains in both   locations throughout the year, excluding small variations of monthly   accumulated rainfall as shown in figure 1 A and allowing us to explore   physiological patterns for seasonal fluctuation. Additionally, it is plausible to   speculate that plants growing in areas with a lower water content throughout   the year may have xylem vessels with lower diameters, as this represents an   important mechanism for avoiding cavitation under extreme droughts (Nardini et al., 2014; Silva et al., 2013), while also restricting   water flow when water is plentiful. The annual profile of leaf transpiration   (figure 2E), which was focused on the morning period when the stomata are wide   open, corroborates this proposition.</p>     <p>In the present study, the E was strongly affected by   the VPD associated with a high temperature and high solar radiation, especially   during the dry season (figure 2). The increased VPD led to an increase in   transpiration, leading to evaporative leaf cooling due to latent heat loss if   water was available. This is in agreement with results reported by others (Passos et al., 2009; Santos et al., 2013). If water was not   available, a high irradiance (figure 2A), particularly during drought, may have   been related to the extremely high leaf temperatures (figure 2B).</p>     <p>An increase in C<sub>i</sub> due to stress could occur   in response to low photosynthetic activity (Singh and Reddy, 2011); however,   this is not a universal response. Stomatal closure typically leads to a   decrease in C<sub>i</sub>, thereby leading to a decrease in the C<sub>i</sub>:C<sub>a</sub> ratio. The decreased <sub>Ci</sub> indicates that stomatal limitations are dominant under moderate but not in   severe drought, as observed in tropical wet plants evaluated in November (Fig. 3B).   At this time, the umbu leaves showed high C<sub>i</sub>:C<sub>a</sub> ratios with a low P<sub>N</sub>,   which indicates that there is a limitation of carbon uptake imposed by nonstomatal   factors. The dry season had a detrimental effect on the Rubisco activity or ATP   synthesis; moreover, under progressive droughts, the mesophyll conductance (gm)   may decline (Flexas and Medrano, 2002; Lawlor and Tezara, 2009). This allows us to conclude that the   nonstomatal limitation likely occurred along with the potential limitation of conductance   of the mesophyll, which together must have accounted for the PN decreases   during the driest months (Ni and Pallardy, 1992;   Silva et al., 2010).</p>     <p>When the photochemical quenching was reduced, the   non-photochemical energy quenching (D and P<sub>E</sub>) was increased (figure   4). The deconvolution of fluorescence signals clearly indicates decreases in   the photochemical quenching parameters and damage to PSII. The lower extent to   which PSII uses the energy absorbed by chlorophyll in photochemical reactions   and the increase in non-photochemical signals suggests that trees grown in wet,   tropical environments are damaged by excess light under droughts. The lower F<sub>v</sub>:F<sub>m</sub> (md) values (table 1) and the   larger D and smaller &#934;PSII values (figure 4) observed throughout the year   in trees grown in wet environments and subsequently exposed to drought   conditions (i.e., in November) supports this conclusion.</p>     ]]></body>
<body><![CDATA[<p>The decreased F<sub>v</sub>:F<sub>m</sub> ratio implies a decrease in the capture and conversion rate of excitation   energy by PSII reaction centers and, thus, a reduction in PSII photochemical   efficiency (Ramalho et al. 1999). These results   strongly suggest that PSII disorganization appeared to be highly pronounced in   sensitive plants, as compared with resistant ones (Huseynova,   2012). A decrease in &#934;PSII occurred after the P<sub>N</sub> decrease,   suggesting that nonstomatal limitations, rather than photochemical limitations,   primarily limited PN. Moreover, a reduced CO<sub>2</sub> supply is expected to   negatively affect the Calvin cycle, which in turn would limit PSII efficiency   (Stitt, 1991). These sequential decreases in the P<sub>N</sub> and &#934;<sub>PSII</sub> under droughts have been described in the literature, as a decrease in   photosynthesis intensity is one photoprotection mechanism used by plants to preserve the photochemical apparatus during stress   (Genty et al. 1989). The decrease in the chlorophyll   content in the tropical wet plants in the drought period (table 2), especially   from September to November, suggests that photosystem damage occurred during   this period and would have limited the speed of post-drought recovery. However,   the drought-induced reduction in leaf pigments is considered to be a typical   oxidative stress indicator that might be attributed to pigment photooxidation, chlorophyll degradation and/or chlorophyll   synthesis deficiency (Campos et al., 2012; Pompelli et al., 2010a; Pompelli et al., 2010b).</p>     <p>The decreased P values were not entirely offset by the   increased D during the dry season, leading instead to a higher P<sub>E</sub>.   The increased P<sub>E</sub> suggests that the down-regulation of PSII to   prevent the over-reduction of QA was not sufficient to compensate for the   decreased demand for electrons through NADP<sup>+</sup> consumption (Chaves et   al., 2008; Pompelli et al., 2010b; Ramalho et al., 1999). This outcome may in turn result in   singlet oxygen formation and damage to membrane components, similar to that   which occurs during light stress (Takahashi and Badger, 2011).</p>     <p>As the drought progressed and soil water content   declined, the &#948;<sup>13</sup>C increased and became less negative, with   values lower than -27.2‰, suggesting a carbon limitation induced by water   limitation (Schifman et al., 2012), as reported in   this study (figure 5). The less negative values of &#948;<sup>13</sup>C in the tropical arid plants indicated that   the water status was generally lower, with a consequent increase in the   stomatal closure and some degree of CO<sub>2</sub> restriction in   photosynthesis during the humid months. The opposite situation during the   driest month (November) indicates that the tropical wet plants experienced   greater restriction of CO<sub>2</sub> influx than the tropical arid plants</p>     <p>The high carotenoid-to-Chl ratios during the dry season (table 2), particularly in leaves from the wet   environments, may help the leaves to avoid photooxidative processes because, in addition to their role as secondary light-absorbing   pigments, the carotenoids prevent the photooxidation of the photosynthetic apparatus by reducing the Chl triplet quencher, preventing the formation of singlet oxygen (<sup>1</sup>O<sub>2</sub>),   or by acting directly on <sup>1</sup>O<sub>2</sub> scavengers (Krieger-Liszkay 2005). These mechanisms may help to protect the   plants, but they are not always sufficient to prevent photodamage in dry leaves.</p>     <p>Plants subjected to water stress tend to overproduce   ROS in different tissues (Carvalho, 2008), and   antioxidant enzymes constitute an important line of cellular defense,   detoxifying ROS compounds. However, we showed that the increases in the CAT and   APX activities during the dry season were not enough to dissipate the excess,   reducing the power accumulated in the H<sub>2</sub>O<sub>2</sub> that was   generated from the water-water cycle or in the SOD activity. In November, the   driest month, the H<sub>2</sub>O<sub>2</sub> and MDA levels were as high as   they were in September, despite the increased activity of the enzymes in the antioxidative system. Although there were increases in the   H<sub>2</sub>O<sub>2</sub>, MDA and antioxidant enzymes levels, our results   showed that S. tuberosa plants have the ability to   increase their antioxidant activity during the dry season (figure 6) as a   defense strategy against the deleterious effects, indicating that APX plays a   positive role in the response to water stress. However, this mechanism is not   robust enough to prevent damage. We attribute the improved drought tolerance of   S. tuberosa plants that were grown in the arid   environment to the combination of high leaf &#936;<sub>w</sub>,   higher g<sub>s</sub> and E, and evaporative leaf   cooling that allow for the maintenance of a constant leaf temperature. The likely   outcome is an increased net CO<sub>2</sub> influx and elevated P and &#934;<sub>PSII</sub> with an efficient sink for electrons from photosynthesis, thus preventing ROS production   and reducing cellular oxidative damages. Our data do not indicate that modestly   increased carotenoid pools can serve as an effective antioxidant system.</p> &nbsp;    <p><b><font size="3">Conclusions</font></b></p>     <p><i>P</i><sub>N</sub> and <i>g</i><sub>s</sub> in <i>S. tuberosa</i>trees appear to be highly sensitive   to diurnal variations, and even when the photosynthetic parameters are affected   by environmental factors (<i>e.g., </i>light and VPD), the stomatal   response to a water deficit suggests that stomatal closure is the first line of   defense against desiccation in umbu trees.   Furthermore, the over-excitation of the reaction centers of PSII during the dry   season may increase ROS production in various subcellular organelles, such as   chloroplasts and peroxisomes. Although the physiological profile of <i>S. tuberosa</i> characterizes it as a drought   tolerant species the P<sub>N</sub>, g<sub>s</sub> and   E in the plants of the tropical wet population are likely to be limited by the   water deficit during the dry season, unlike the umbu plants   of the arid population. Such species, when growing under low water conditions,   can acclimate to this abiotic stress and are able to survive subsequent drought   periods with less damage, as compared with plants from tropical wet regions.</p>     <p>Finally, our results suggest that this species has   great potential to acclimate to the altered environment predicted for   arid/semiarid regions as a result of climate changes. However, further studies   are needed to determine the effects of a prolonged dry season on S. tuberosa plants and to develop strategies to mitigate these   effects.</p> &nbsp;    <p><b>Acknowledgements</b></p>     <p>The authors would like to thank the National Council   for Scientific and Technological Development, CNPq (Grants 473202/2008-5) and the Foundation for Science and Technology of   Pernambuco (Grants APQ-0150-2.03/08) for their financial support of this   research.</p> &nbsp;    ]]></body>
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