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ISSN 10214437, Russian Journal of Plant Physiology, 2013, Vol. 60, No. 3, pp. 322–329. © Pleiades Publishing, Ltd., 2013. 322 1 INTRODUCTION Low and high air temperatures are known as most important factors influencing plant performance and distribution. In a changing world with increasing envi ronmental temperatures that can alter distribution of existing invasive species [1], the knowledge of the effects of low and high temperatures on weeds can be used to predict their behavior and as a tool allowing us to identify sensible habitats to invasions. Optimum temperatures for photosynthesis exhib ited by a plant species reflect the environmental tem perature range, to which the species has genetically and physiologically been adapted [2]. When plants are exposed to temperatures above or below their opti mum physiological range, their photosynthetic per formance becomes affected [3]. Thus, extreme tem peratures can inhibit photosynthesis in many different ways, such as decreasing the efficiency of photosystem II (PSII), limiting enzymatic rates of the Calvin cycle, 1 This text was submitted by the authors in English. altering photorespiration, or changing the structure of thylakoids [4, 5]. Extreme temperature effects on photosynthesis can occur in darkness, for example, during cold nights [6], and they are aggravated when plants are exposed to high levels of irradiance [7]. In this context, interspe cific difference in temperature tolerance can be recorded. Lantana camara L. (Verbenaceae) has been classi fied between the most invasive species around the world, in tropical and subtropical regions worldwide between 35 ° N and 35 ° S [8]. It has been described that in the field L. camara grows actively at tempera tures above +15 ° C [9], being susceptible to frosts and low temperatures; so it seldom occurs in places where temperatures frequently fall below +5 ° C [10], where its branches and leaves die and its growth ceases [11]. Nevertheless, no study is available about the specific effects of temperature on L. camara photosynthetic apparatus. The aims of this work were to analyze the effects of low and high temperatures on the photosynthetic per formance of L. camara leaves in darkness to identify the lowest and the highest temperature limits, at which its leaves are able to resist during nighttime and to know if two populations of L. camara coming from Effect of Low and High Temperatures on the Photosynthetic Performance of Lantana camara L. Leaves in Darkness 1 J. CarriónTacuri, A. E. RubioCasal, A. de Cires, M. E. Figueroa, and J. M. Castillo Departamento de Biología Vegetal y Ecología, Universidad de Sevilla, Ap. 1095, 41080 Sevilla, Spain; fax: +34+954615780; email: [email protected] Received May 24, 2012 Abstract —Low and high temperatures are known as most important factors influencing plant performance and distribution. Plants of Lantana camara L. coming from two distinct geographical populations (Iberian Peninsula and Galápagos Islands) were cultivated in a common garden experiment, and their leaves were subjected to thermal treatments (from +20.0 to –7.5 ° C during the winter and from +20.0 to +50.0 ° C during the summer) in a programmable water bath in darkness. Their photosynthetic performance and their recovery capacity after the thermal treatment were evaluated by measuring chlorophyll fluorescence, net photosynthe sis rate, and leaf necrosis. In general, L. camara photosynthetic apparatus showed a wide range of tempera ture tolerance in darkness, showing optimal functioning of its photosystem II just after exposure to tempera tures between –2.5 and +35.0 ° C for the Iberian population and between +10.0 and +25.0 ° C for the Galápa gos population. Just after exposure to low and high temperatures, gradual cold and heatinduced photoinhibition was recorded for both populations. After 24 h, leaves of L. camara demonstrated a great recovery capacity from –2.5 to +42.5 ° C. However, leaves of the treatments from –5.0 ° C down and +47.50 ° C up showed permanent damages to the photosynthetic apparatus and to the leaf tissues. Slight inter population differences were found only at extreme temperatures. Keywords: Lantana camara , Galápagos, Iberian Peninsula, necrosis, net photosynthesis, photoinhibition, recovery capacity, thermal tolerance DOI: 10.1134/S1021443713030047 Abbreviations : F 0 —basal fluorescence; F m —maximum fluores cence; F v / F m —maximum quantum efficiency of PSII photo chemistry; P N —net photosynthesis rate; PSII—photosystem II. RESEARCH PAPERS
RUSSIAN JOURNAL OF PLANT PHYSIOLOGY Vol. 60 No. 3 2013 EFFECT OF LOW AND HIGH TEMPERATURES ON THE PHOTOSYNTHETIC 323 contrasted latitudes show different response to tem perature. With these aims, we evaluated in a common garden experiment the photosynthetic performance and the recovery capacity after high and low tempera ture treatments for L. camara plants coming from the Galápagos Archipelago and from the Southwest of Iberian Peninsula. We hypothesized: (1) the photo synthetic apparatus of L. camara would be sensible to temperature lower than +5 ° C , and (2) L. camara from the Iberian Peninsula would have a higher tolerance to extreme temperatures than the population from the Galápagos Islands since Iberian populations are exposed to more extreme temperatures during sum mer and winter than the Galápagos populations. MATERIALS AND METHODS Plant material. Two wild Lantana camara L. popu lations were studied, one from the center of the L. camara latitudinal geographic distribution at the Galápagos Archipelago (from the Transition Zone (ca. 120 m above sea level) in Santa Cruz Island, 0 ° 42 ′ S; 90 ° 19 ′ W ) and another from the northern extreme of its geographic distribution at Southwest of Iberian Peninsula (Asperillo Sea Cliff, Huelva, 37 ° 06 ′ N; 6 ° 46 ′ W). At both locations, L. camara was originally coming from gardens, arriving in 1938 for first time in the Galápagos [12] and probably during the seventies or eighties after the construction of Parador de Maza g ó n in 1968 on the Asperillo Sea Cliff. Two distinct seasons can be differentiated over the year in the Galápagos Islands: during the warmwet season (January to June) mean daily air temperature is between +25 and +26 ° C and during the cooldry sea son (July to December) temperature is between +18 and +26 ° C [13]. The Southwest of Iberian Peninsula is under Mediterranean climate modified by oceanic influence with wet winters (January mean temperature is of +11 ° C with minimum of ca. 0 ° C ; frost does not occur in most years) and warm and sunny summers (August mean temperature is of +25 ° C ; rarely maxi mum temperatures exceeds +40 ° C ) [14]. Seeds were collected from 10 plants chosen ran domly in each population. 10 plants of each popula tion were cultivated in plastic pots in peat soil at the openair area of the greenhouse facilities of the Uni versity of Seville during 4 months. Controlledtemperature experiment. The youngest fully expanded leaf was used to avoid possible effects related to ontogenetic leaf development since it might affect the temperature sensitivity. Leaves collection ( n = 5 leaves per treatment and population chosen randomly from different individuals) for lowtemper ature experiment was carried out at sunrise on the 21st February 2011 and for high temperature experi ment on the 22nd June 2011, so the plants were accli mated to winter and summer conditions, respectively. Average daily temperature during the month previ ous to collection in winter was + 11.4 ± 0.5 ° C , with a maximum momentary temperature of +24.9 ° C and a minimum of +0.9 ° C , while in summer it was + 26.0 ± 0.6 ° C , with +40.4 ° C (max) and +12.9 ° C (min) (www.meteored.com). After collection leaves were immediately stored in a saturated humidity atmo sphere at +20 ° C during 3 h. Leaves were placed individually in sealed plastic bags and immersed in a programmable water bath (Neslab RTE200, NESLAB Instr., United States) for 30 min in darkness [15]. Ethylene glycol 30% (v/v) was used to avoid ice crystal formation in the water bath. Every leaf was immersed at the same time in the water bath at +20.0 ° C . During the lowtemperature experiment, tempera ture was decreasing gradually from +20.0 to 0 ° C with steps of 5.0 ° C and from 0.0 to –7.5 ° C with steps of 2.5 ° C. The exposure to low temperatures in darkness would correspond with the conditions experienced by leaves during nocturnal chilling episodes, such as those recorded at L. camara northern and southern extremes of its geographical distribution range and at high altitudes all across its geographical distribution. During the hightemperature experiment, tempera ture was increasing gradually from +20.0 to +40.0 ° C with steps of 5.0 ° C and from +40.0 to +50.0 ° C with steps of 2.5 ° C. The exposure to high temperature in darkness would correspond with the conditions expe rienced by L. camara leaves during some summer nights at the Southwest Iberian Peninsula (ca. +30 ° C). After 30 min in each thermal treatment, chlorophyll a fluorescence was recorded in a dark room to not disrupt the darkadapted state of leaves. To assess the recovery capacity of the photosyn thetic apparatus, leaves were kept in saturated humid ity, +20 ° C and exposed to ca. 40 μ mol/(m 2 s) during 24 h [15]; these conditions of lowlight intensity favor the substitution of damaged proteins of the PSII. A period of milder temperatures is required to return to rates of photosynthesis as those prior to the extreme temperature event [6]. After the recovery period, necrosis percentage was measured as the proportion of the total leaf area. Chlorophyll a fluorescence fast dynamic and net photosynthesis rate were also recorded. Chlorophyll fluorescence. Chlorophyll a fluores cence measurements were carried out in darkadapted leaves (at least during 30 min) using a FMS2 portable modulated fluorimeter (Hansatech Instr., United Kingdom) on the adaxial leaves surface. The minimal fluorescence level in the darkadapted state ( F 0 ) was measured by using a modulate pulse (PPFD < 0.05 μ mol/(m 2 s) for 1.8 μ s) too small to induce signifi cant physiological changes in the plant [16]. The data stored were averages taken over a 1.6s period. Maximal fluorescence in this state ( F m ) was measured after apply ing a saturating actinic light pulse of 15000 μ mol/(m 2 s) for 0.7 s [17]. The value of F m was recorded as the highest average of two consecutive points. Values of the variable fluorescence ( F v = F m − F 0 ) and the maximum
324 RUSSIAN JOURNAL OF PLANT PHYSIOLOGY Vol. 60 No. 3 2013 CARRIÓNTACURI et al. quantum efficiency of PSII photochemistry ( F v / F m ) were calculated. Net photosynthesis. Net photosynthesis rate ( P N ) was measured as O 2 evolution using an LD2 Hansatech leaf chamber with a gas phase O 2 electrode at 25 ° C ( n = 3 –5 leaves per treatment and two measurements in each leaf). A buffer of 1 M carbonate/bicarbonate (pH 9.0) was used to provide a CO 2 saturated atmo sphere. Saturating irradiance was provided by an LS2 Hansatech source. Photosynthetic photon flux density (PPFD) was measured using an integrating quantum sensor cell (LiCor, 190 SB). Statistical analysis. All statistical tests were carried out using the SPSS v. 18 (Statistic Inc.). Data were tested for normality with the Kolmogorov–Smirnov test and for homogeneity of variance with the Levene test. Mean physiological data for the same population at different temperatures were compared using one way analysis of variance (ANOVA, F test) followed by Tukey’s Honest Significant Difference (HSD). When normality or homogeneity of variance was not reached, data were analyzed using KruskalWallis non–parametric analysis of variance, followed by the Mann–Whitney U test to compare means between two treatments. Interpopulation differences at the same temperature were compared using Student t test for independent samples. Deviation was calculated as standard error of mean (SE). RESULTS Chlorophyll Fluorescence Just after Thermal Treatments F v / F m for both populations decreased logarithmi cally at low temperatures and sigmoidal at high tem peratures (Figs. 1a, 1b). At low temperatures, F v / F m for the Iberian popula tion was similar from +20.0 to –2.5 ° C (ca. 0.770), decreasing significantly at –5.0 and − 7.5 ° C (ca. 0.680) (KruskalWallis, P < 0.01; MannWhitney U test, P < 0.05). For the Galápagos population, F v / F m was simi lar from +20.0 to +10.0°C (ca. 0.790), decreasing sig nificantly at –2.5, –5 (ca. 0.710), and –7.5°C (0.550) (KruskalWallis, P < 0.01; MannWhitney U test , P < 0.05). These decreases in F v / F m for both populations were due to a logarithmic drop of F m and constant lev els of F 0 . F v / F m was lower for the Galápagos population than for Mazag ó n at − 7.5 ° C ( t test, P < 0.05) (Fig. 1a). At high temperatures, F v / F m for the Iberian popu lation was constant from +20.0 to +35.0 ° C (ca. 0.870), decreasing significantly from +40.0 (0.830) to +50.0 ° C (0.060) (KruskalWallis, P < 0.001; Mann Whitney U test, P < 0.01). F v / F m for the Galápagos population was also ca. 0.870 from +20.0 to +25.0 ° C , decreasing significantly from +30.0 ° C (0.860) onwards and strongly from +42.5 (0.750) to +50.0 ° C (0.060) (KruskalWallis, P < 0.001; MannWhitney U test, P < 0.01). These drops in F v / F m were due to decreasing F m together with increasing F 0 . F v / F m was similar for both populations in every treatment ( t test, P > 0.05) (Fig. 1b). Chlorophyll Fluorescence after the Recovery Period After the recovery period after low temperatures, both populations showed an exponential drop of F v / F m below –2.5 ° C (Fig. 2a,b). Leaves showed a great recovery capacity from +20.0 ° C to –2.5 ° C for both populations, with high and similar F v / F m (ca. 0.770). Recovery capacity was slightly lower after –5.0 ° C (ca. 0.590). After –7.5 ° C, leaves showed the lowest F v / F m (ca. 0.110) (KruskalWallis, P < 0.01; Mann Whitney U test, P < 0.05) coinciding with the lowest F 0 and Fm (MannWhitney U test, P < 0.05). There were no significant differences in F v / F m between pop ulations in any treatment (Fig. 2a). After the recovery period after high temperatures, leaves of both populations showed similar values of F v / F m (ca. 0.860) from +20.0 to +42.5 ° C, decreasing significantly after +45.0 ° C (ca. 0.83), +47.5 ° C (ca. 0.500) and +50.0 ° C (ca. 0.090) (KruskalWallis, P < 0.01; MannWhitney U test, P < 0.05). The unique difference in F v / F m between both populations was recorded after +47.5 ° C, with the Galápagos popula tion showing higher F v / F m than the Iberian Penin sula population ( t test, P < 0.05) (Fig. 2b). At +20.0 ° C, leaves of both populations acclimated to summer conditions showed the lower photoinhibi tion levels (higher F v / F m ) than leaves acclimated to winter just after the thermal treatment ( t test, P < 0.01) and after the recovery period only Galápagos populations maintained that difference ( t test, P < 0.001). These differences were due to similar F m for both seasons and slightly higher F 0 during winter ( t test, P < 0.05) (Figs. 1a, 1b; Figs. 2a, 2b). Net Photosynthesis Rate After the recovery period, P N for the Iberian popu lation subjected to low temperatures decreased loga rithmically, varying between 17.8 ± 2.2 μ mol O 2 /(m 2 s) after +20.0 ° C and 2.9 ± 0.3 μ mol O 2 /(m 2 s) after − 7.5 ° C (ANOVA, F = 4.207, P < 0.01) (Fig. 3a). P N for the Galápagos population subjected to low temper atures decreased also logarithmically, varying between ca. 15 μ mol O 2 /(m 2 s) after +20.0 ° C and +5.0 ° C to 1.6 ± 0.2 μ mol O 2 /(m 2 s) after − 7.5 ° C (ANOVA, F = 16.510, P < 0.001). Leaves of L. camara from the Galápagos population did not recover after –5.0 and − 7.5 ° C , showing lower P N than the other treatments (Tukey’s HSDtest, P < 0.05). Instead, leaves from the Iberian population showed a significant lower P N only after − 7.5 ° C (Fig. 3a). On the other hand, P N for leaves of L. camara from both populations decreased sigmoidal at high temper atures. P N for the Iberian population was similar from +20 to +42.5 ° C (ca. 15 μ mol O 2 /(m 2 s) ) and decreased significantly from 11.4 ± 0.7 μ mol O 2 /(m 2 s) ) to
RUSSIAN JOURNAL OF PLANT PHYSIOLOGY Vol. 60 No. 3 2013 EFFECT OF LOW AND HIGH TEMPERATURES ON THE PHOTOSYNTHETIC 325 +50.0 ° C (3.6 ± 1.2 μ mol O 2 /(m 2 s)) ) (KruskalWallis, P < 0.01; MannWhitney U test, P < 0.05; Fig. 3b). Instead, P N for the Gal á pagos population was constant from +20.0 to +47.5 ° C (ca. 15 μ mol O 2 /(m 2 s) ), showing lower P N after +47.5 ° C (2.0 ± 0.4 μ mol O 2 /(m 2 s)) ) (KruskalWallis, P < 0.05; MannWhitney U test, P < 0.05). P N was higher for the Gal á pagos population than for the Iberian population after +40.0 and +45.0 ° C ( t test, P < 0.05; Fig. 3b). Necrosis Leaves from both populations showed necrosis only at temperatures lower than +5.0 ° C , varying from 6% at 0 ° C to 100% at − 7.5 ° C . The necrosis percentage was significantly higher after − 7.5 ° C than after all treatments except − 5.0 ° C (KruskalWallis, P < 0.05; MannWhitney U test, P < 0.05) (Fig. 3c). Leaves from the Iberian population showed necro sis at +47.5 ° C (23%) and at +50.0 ° C (74%) (Kruskal Wallis, P < 0.01; MannWhitney U test, P < 0.05), while leaves from the Galápagos populations suffered necrosis only at +50.0 ° C (88%) (KruskalWallis, P < 0.01; MannWhitney U test, P < 0.01) (Fig. 3d). DISCUSSION In field studies, L. camara has been described as a species sensitive to low temperatures, its branches and leaves showing thermal stress symptoms at tempera tures lower than +5.0 ° C [10, 11]. Nevertheless, its (а)1.0 0.8 0.6 0.4 0.2 0 F v / F m Abbce bd AB B a e cde * b e BBBB A 1200 1000 800 600 400 200 BC C F m , rel. units (c) BC BC BC bbbbbb b a AB B 400 300 200 100 –10 –5 0 5 10 15 20 Temperature, ° C F 0 , rel. units a aaaa aa a A A AAAAAA (e) (b) D ab c 1.0 0.8 0.6 0.4 0.2 0 F v / F m D AAAA B bb a c e e C C d (d) 1200 1000 800 600 400 200 F m , rel. units a aa A A AA A B BC BC Cee ab bc cd de 400 300 200 100 F 0 , rel. units 20 25 4530 4035 50 * AAAA aaaa AB ab b C CC c c BC c (f) Fig. 1. Maximum quantum efficiency of PSII photochemistry (( F v / F m , (a, b)), maximum fluorescence (( F m , (c, d)), and basal fluorescence (( F 0 , (e, f)) after 30 min of treatment from +20.0 to –7.5 ° C (left panels) and from +20.0 to +50.0 ° C (right panels) for leaves of L. camara from the Galápagos Islands (white symbols; dotted line) and from the Southwest Iberian Peninsula (black symbols; continued line). Different letters denote significant differences between treatments (ANOVA or KruskalWallis, P < 0.05) for the same population (Iberian Peninsula: capital letters; Galápagos: lowercase letters) and asterisks denote differences between populations for the same temperature ( t test, P < 0.05). Data are means ± SE.
326 RUSSIAN JOURNAL OF PLANT PHYSIOLOGY Vol. 60 No. 3 2013 CARRIÓNTACURI et al. photosynthetic apparatus in our experiments demon strated a wide temperature tolerance range in darkness (from –2.5 to +42.5 ° C ). Thus, its tolerance to low temperatures was higher than that of other species, such as pea ( Pisum sativum ) that was not able to recover after +4.0 ° C [18] and the Mediterranean trees Juniperus oxicedrus, J. phoenicea , and Pinus pinea that showed a poor recovery capacity after +10.0 ° C for 30 min [15]. The comparison between our results and field observations point out that L. camara would be especially sensitive to the synergic effects of low tem peratures and high radiation levels, being much less sensitive to low temperatures in darkness. L. camara showed optimal functioning of its PSII with very low photoinhibition levels ( F v / F m between ca 0.750 and ca. 0.870) just after exposure to tempera tures between –2.5 and +35.0 ° C for the Iberian pop ulation and between +10.0 and +25.0 ° C for the Galápagos population. The Iberian population main tained the same optimum temperature interval in 24 h after treatment (with maximum and constant F v / F m and P N ) as just after the temperature exposure. In con trast, the Galápagos population expanded its optimum temperature interval to –5.0 and +42.5 ° C after recov ery, showing P N higher than 10 μ mol O 2 /(m 2 s) between –5.0 ° C and +47.5 ° C. These P N values were in the range of those reported for Iberian L. camara at +23 ° C at openair conditions (10–15 μ mol CO 2 /(m 2 s) [19]. These wide ranges of thermal tolerance occurred when plants were acclimated to summer or winter conditions and were exposed gradually to high or low (а)1.0 0.8 0.6 0.4 0.2 0 F v / F m 1200 1000 800 600 400 200 F m , rel. units (c) 200 –10 –5 0 5 10 15 20 Temperature, ° C F 0 , rel. units (e) (b) 1.0 0.8 0.6 0.4 0.2 0 F v / F m (d) 1200 1000 800 600 400 200 F m , rel. units F 0 , rel. units 20 25 4530 4035 50 (f) 00 150 100 50 0 200 150 100 50 0 A B a bab c C d BC abc bc * cd d * AAAAAA AA AAAA A A A AAAA A A A A BB BBBBB B B B B BBBB * B B aaaaa a a a a a a a a A a a b b b b b b b b b b b b b b bb Bbbbb ab ab ab c C CCC C d abc abc bc Fig. 2. Maximum quantum efficiency of PSII photochemistry (( F v / F m (a, b)), maximum fluorescence (( F m (c, d)), and basal flu orescence (( F 0 (e, f)) after a recovery period of 24 h after the treatment from +20.0 to –7.5 ° C (left panels) and from +20.0 to +50.0 ° C (right panels) for leaves of L. camara from the Galápagos Islands (white symbols; dotted line) and from the Southwest Iberian Peninsula (black symbols; continued line). Different coefficients (Iberian Peninsula: capital letters; Galápagos: lowercase letters) denote significant differences between treatments (ANOVA or KruskalWallis, P < 0.05) and asterisks denote differences between populations for the same temperature ( t test, P < 0.05). Data are means ± SE.
RUSSIAN JOURNAL OF PLANT PHYSIOLOGY Vol. 60 No. 3 2013 EFFECT OF LOW AND HIGH TEMPERATURES ON THE PHOTOSYNTHETIC 327 temperatures, respectively, since acclimation is a key factor in the regulation of the thermal tolerance. Just after exposure to low temperatures, gradual coldinduced photoinhibition was recorded for both populations, reflected in the lower F v / F m as a conse quence of a decrease in F m with similar F 0 [20]. This photoinhibition, higher at belowzero temperatures, revealed deactivation of PSII reaction centers [21] preventing overexcitation of photosynthesis and oxi dative damages [22]. Photoinhibition levels increased and P N decreased gradually at temperatures lower than − 2.5 ° C in 24 h after the low temperature treatment. Low temperatures inhibit the rate of photosynthesis through limiting enzymatic rates of the Calvin cycle [5] and also affecting diffusion processes in the elec tron transport chain [23]. The photoinhibition level in 24 h after the thermal treatment was much higher than just after the thermal treatment: for − 5.0 ° C ca. 0.600 vs. 0.700 and − 7.5 ° C ca. 0.100 vs. 0.600. These low F v / F m after 24 h together with low F m , F 0 , and P N (as low as ca. 2.5 μ mol O 2 /(m 2 s)) reflected permanent damages to the photosynthetic apparatus [21]. In fact, the high necrosis percentages recorded for tempera tures lower than − 2.5 ° C evidenced the disruption of structures and functions of cells and tissues by the freezing effect of large ice masses [24]. On the other hand, abrupt heatinduced photoin hibition was recorded for both populations from +45.0 ° C onwards just after the thermal treatment, reflected in a sudden drop in F v / F m due to decreasing F m and increasing F 0 . Pea plants showed similar responses with F 0 increasing from +42.5 ° C onwards [18]. This has been interpreted as a reflection of reduced energy transport effectiveness from antenna chlorophyll a to the reaction center of PSII [25] and/or directly due to the block of PSII reaction cen ters [15, 26]. Leaves exposed to +45.0 ° C that showed high photoinhibition levels just after the thermal treat ment ( F v / F m ca. 0.500) recovered completely after 24 h ( F v / F m ca. 0.800), showing P N between 12– 15 μ mol O 2 /(m 2 s). High temperatures may affect photosynthesis by altering the excitation energy distri bution by changing the structure of thylakoids, by pro voking excessive membrane fluidity, enhancing oxida tive stress, and by changing the activity of the Calvin cycle and other metabolic processes, such as photores piration [27], or may inhibit the repair of PSII (28). At higher temperatures ( >+47.5 ° C ), low F v / F m values after the recovery period (<0.495), together with P N values as low as ca. 2.5 μ mol O 2 /(m 2 s), denoted per manent damages to the photosynthetic apparatus. Furthermore, necrosis was also recorded at the highest –10 –5 0 5 10 15 20 Temperature, ° C 20 25 4530 4035 50 (а) (c) (b) (d) 20 15 10 5 0 100 80 60 40 20 0 Net photosynthesis, µ mol/(m 2 s) Necrosis, % 20 15 10 5 0 100 80 60 40 20 0 Net photosynthesis, µ mol/(m 2 s) Necrosis, % AB B bc b a c A ABC C D abAB B BBB B B B B bc b bb aa aa a aa a a a cc c B AA A A A A C Fig. 3. Net photosynthesis rate (a, b) and necrosis percentage (c, d) after 24 h of recovery for leaves of L. camara from the Galápa gos Islands (white symbols and dotted line) and from the Iberian Peninsula (black symbols and continued line), which the previ ous day during the winter were subjected to treatments of 30 min from +20.0 to –7.5 ° C (left panels) and during the summer from +20.0 to +50.0 ° C (right panels). Different coefficient (Iberian Peninsula: capital letters; Galápagos: lowercase letters) denote significant differences between treatments (ANOVA or KruskalWallis, P < 0.05) and asterisks denote significant differences between populations for the same temperature ( t test, P < 0.05). Data are means ± SE.
328 RUSSIAN JOURNAL OF PLANT PHYSIOLOGY Vol. 60 No. 3 2013 CARRIÓNTACURI et al. temperatures coming from denaturation of membrane proteins or from melting of membrane lipids, which leads to membrane rupture and the loss of cellular contents [29]. Both populations of Lantana responded similarly to temperature treatments. Slight interpopulation dif ferences were found only at extreme temperatures. F v / F m just after the lowest thermal treatment at − 7.5 ° C was lower for the Galápagos than for the Iberian pop ulation. After 24 h, this difference disappeared but P N still indicated a better photosynthetic functioning for the Iberian than for the Galápagos population. On the other hand, the chlorophyll fluorescence dynamic of both populations was similar just after the exposure to high temperatures, but leaves from the Galápagos population subjected to +47.5 ° C showed higher val ues of F v / F m and P N after 24 h than the Iberian popu lation. During day time, plants in the field are not only exposed to low or high temperatures but suffer fre quently from synergetic effects of temperatures and high radiation intensities [4, 20]. In these field condi tions, excess energy must be dissipated or the chloro plast membranes sustain oxidative damages, which can lead to tissue and/or whole plant death [30], as has been reported in L. camara [11]. We worked in dark conditions, trying to emulate nocturnal chilling epi sodes, such as those recorded at L. camara northern and southern extremes of its geographical distribution range showing that it has a wide temperature toler ance, but this tolerance could be much narrower in field conditions where extreme temperatures coincide with high radiation levels. Thus, further studies are necessary to know the synergetic effects of both low and/or high temperatures with high radiation intensi ties, and the effect of more prolonged episodes of low and high temperatures on L. camara leaves. ACKNOWLEDGMENTS Thanks to Jesús and José of the Greenhouse of the University of Seville for their assistance and Raúl Ser rano for his help in laboratory. This research was supported by Agencia Española de Cooperación Internacional para el Desarrollo (AECID) through a grant to the first author. REFERENCES 1. Hellmann, J.J., Byers, J.E., Bierwagen, B.G., and Dukes, J.S., Five Potential Consequences of Climate Change for Invasive Species , Conserv. Biol., 2008, vol. 22, pp. 534–543. 2. Berry, J. and Björkman, O., Photosynthetic Response and Adaptation to Temperature in Higher Plants, Annu. Rev. Plant Physiol. , 1980, vol. 31, pp. 491–543. 3. Lichtenthaler, H.K., Vegetation Stress: An Introduc tion to the Stress Concept in Plants, J. Plant Physiol. , 1996, vol. 148, pp. 4–14. 4. Adams, W.W., DemmigAdams, B., Verhoeven, A.S., and Barker, D.H., “Photoinhibition” during Winter Stress: Involvement of Sustained Xanthophyll Cycle Dependent Energy Dissipation, Aust. J. Plant Physiol. , 1994, vol. 22, pp. 261–276. 5. Stitt, M. and Hurry, V., A Plant for All Seasons: Alter ations in Photosynthetic Carbon Metabolism during Cold Acclimation in Arabidopsis, Curr. Opin. Plant Biol. , 2002, vol. 5, pp. 199–206. 6. Davidson, N.J., Battaglia, M., and Close, D.C., Pho tosynthetic Responses to Overnight Frost in Eucalyptus nitens and E. globulus, Trees , 2004, vol. 18, pp. 245– 252. 7. Powles, S.B., Photoinhibition of Photosynthesis Induced by Visible Light, Annu. Rev. Plant Physiol. , 1984, vol. 35, pp. 15–44. 8. Day, M.D., Wiley, C.J., Playford, J., and Zalucki, M.P., Lantana Current Management Status and Future Pros pects , Canberra: Australian Centre for International Agricultural Research, 2003. 9. Anon. National Strategy for Lantana Management , Bris bane: Queensland Department of Natural Resources, 2000. 10. Sharma, G.P., Raghubanshi, A.S., and Singh, J.S., Lantana Invasion: An Overview, Weed Biol. Manag., 2005, vol. 5, pp. 157–165. 11. Thakur, M.L., Ahmad, M., and Thakur, R.K., Lantana Weed ( Lantana camara var. aculeata Linn) and Its Pos sible Management through Natural Insect Pests in India, Ind. For. , 1992, vol. 118, pp. 466–488. 12. Tye, A., Invasive Plant Problems and Requirements for Weed Risk Assessment in the Galápagos Islands, Weed Risk Assessment , Groves, R.H., Panetta, F.D., and Vir tue, J.G., Eds., Collingwood: CSIRO Publ., 2001, pp. 153–175. 13. McMullen, C.K., Flowering Plants of the Galapagos , Cornell: Cornell Univ. Press, 1999. 14. Castellanos, E.M., Figueroa, M.E., and Davy, A.J., Nucleation and Facilitation in Saltmarsh Succession: Interactions between Spartina maritima and Arthrocne mum perenne, J. Ecol. , 1994, vol. 82, pp. 239–248. 15. RubioCasal, A.E., LeiraDoce, P., Figueroa, M.E., and Castillo, J.M., Contrasted Tolerance to Low and High Temperatures of Three Tree Taxa CoOccurring on Coastal Dune Forests under Mediterranean Cli mate, J. Arid Environ. , 2010, vol. 74, pp. 429–439. 16. Schreiber, U., Schliwa, W., and Bilger, U., Continuous Recording of Photochemical and Nonphotochemical Chlorophyll Fluorescence Quenching with a New Type of Modulation Fluorimeter, Photosynth. Res. , 1986, vol. 10, pp. 51–62. 17. BolhàrNordenkampf, H.R. and Öquist, G., Chloro phyll Fluorescence as a Tool in Photosynthesis Research, Photosynthesis and Production in a Changing Environment: A Field and Laboratory Manual , Hall, D.O., Scurlock, J.M.O., BolhàrNordenkampf, H.R., Lee goog, R.C., and Long, S.P, Eds., London: Chapman & Hall, 1993, pp. 193–206. 18. Georgieva, K. and Lichtenthaler, H.K., Photosyn thetic Activity and Acclimation Ability of Pea Plants to Low and High Temperature Treatment as Studied by
RUSSIAN JOURNAL OF PLANT PHYSIOLOGY Vol. 60 No. 3 2013 EFFECT OF LOW AND HIGH TEMPERATURES ON THE PHOTOSYNTHETIC 329 Means of Chlorophyll Fluorescence, J. Plant Physiol. , 1999, vol. 155, pp. 416–423. 19. CarriónTacuri, J., RubioCasal, A.E., de Cires, A., Figueroa, M.E., and Castillo, J.M., Lantana camara L.: A Weed with Great LightAcclimation Capacity, Photo synthetica, 2011, vol. 49, pp. 321–329. 20. Close, D.C., Beadle, C.L., Brown, P., and Holz, G.K., ColdInduced Photoinhibition Affects Establishment of Eucalyptus nitens (Deane and Maiden) Maiden and Eucalyptus globulus Labill, Trees, 2000, vol. 15, pp. 32–41. 21. Maxwell, K. and Johnson, G.N., Chlorophyll Fluores cence – A Practical Guide, J. Exp. Bot., 2000, vol. 51, pp. 659–668. 22. Huner, N.P.A., Öquist, G., Hurry, V.M., Krol, M., Falk, S., and Griffith, M., Photosynthesis, Photoinhi bition and Low Temperature Acclimation in Cold Tol erant Plants, Photosynth. Res. , 1993, vol. 37, pp. 19–39. 23. Laisk, A. and Oja, V., Range of Photosynthetic Control of Post Illumination P700 + Reduction Rate in Sun flower Leaves, Photosynth. Res. , 1994, vol. 39, pp. 39–50. 24. Pearce, R.S., Plant Freezing and Damage, Ann. Bot. , 2001, vol. 87, pp. 417–424. 25. Briantais, J., Vernotte, C., Krause, G., and Weis, E., Chlorophyll a Fluorescence of Higher Plants: Chloro plasts and Leaves, Light Emission by Plant and Bacteria , Govindjee, Amesz, J., and Fork, D., Eds., New York: Academic, 1986, pp. 539–583. 26. Wen, X., Gong, H., and Lu, C., Heat Stress Induces an Inhibition of Excitation Energy Transfer from Phyco bilisomes to Photosystem II but Not to Photosystem I in a Cyanobacterium Spirulina platensis, Plant Physiol. Biochem., 2005, vol. 43, pp. 389–395. 27. Yordanov, I., Response of Photosynthetic Apparatus to Temperature Stress and Molecular Mechanisms of Its Adaptation, Photosynthetica , 1992, vol. 26, pp. 517– 531. 28. Allakhverdiev, S.I., Kreslavskii, V.D., Klimov, V.V., Los, D.A., Carpentier, R., and Mohanty, P., Heat Stress: An Overview of Molecular Responses in Photo synthesis, Photosynth. Res. , 2008, vol. 98, pp. 541–550. 29. Ahrens, M.J. and Ingram, D.L., Heat Tolerance of Cit rus Leaves , Hort. Sci. , 1988, vol. 23, pp. 747–748. 30. Foyer, C., Lelandais, M., and Kunert, K.J., Photooxi dative Stress in Plants , Physiol. Plant. , 1994, vol. 92, pp. 696–717. View publication statsView publication stats