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On-line version ISSN 1677-9452
Braz. J. Plant Physiol. vol.21 no.4 Campo dos Goytacazes 2009
Distúrbios fisiológicos promovidos pelo ozônio em cinco cultivares de Phaseolus vulgaris L.
Cláudia C. ClebschI,*; Armando M. Divan JuniorII; Paulo L. OliveiraI; Márcio NicolauIII
IUniversidade Federal do Rio Grande do Sul, Departamento de Pós- Graduação em Ecologia, Av. Bento Gonçalves, 9500, Agronomia, 91501-970 Porto Alegre, Rio Grande do Sul, Brasil
IIUniversidade Federal do Rio Grande do Sul,Centro de Ecologia, Laboratório de Bioindicação Vegetal, Av. Bento Gonçalves, 9500, Agronomia, 91501-970 Porto Alegre, Rio Grande do Sul, Brasil
IIIEmpresa Brasileira de Pesquisa Agropecuária, Centro Nacional de Pesquisa do Trigo, Br 285, km 294, s/n, 99001-970 Passo Fundo, Rio Grande do Sul, Brasil
Bean seedlings of Fepagro 26, Guapo Brilhante, Iraí, Macotaço and US Pinto 111 cultivars were submitted to treatments with or without addition of ozone to the ambient air, in order to evaluate the effects of exposure on photosynthesis, relative electrolyte leakage, foliar abscission and biomass of the seedlings. Exposure to ozone caused significant decreases in the net assimilation of all cultivars except Iraí. It also caused a significant increase in electrolyte leakage from the Pinto cultivar, but only when AOT40 was the highest. It also produced significant anticipation in the time of foliar abscission in the Pinto, Fepagro and Guapo cultivars. The variability observed in the biomass measurements reflected the limitations to perform long-term controlled-environment studies, one of the major challengers yet to be overcome in order to obtain more conclusive data on damages induced on crop species resulting from tropospheric ozone enrichment.
Key words: photosynthesis, relative electrolyte leakage, foliar abscission, biomass.
Plântulas de feijão das cultivares Fepagro 26, Guapo Brilhante, Iraí, Macotaço e US pinto 111 foram submetidas aos tratamentos com e sem adição de ozônio ao ar ambiente, com o objetivo de avaliar os efeitos da exposição sobre a fotossíntese, permeabilidade relativa a eletrólitos, abscisão foliar e biomassa das plântulas. A exposição ao ozônio causou decréscimos significativos na assimilação líquida de todas as cultivares, exceto na Iraí. Causou também um aumento significativo na permeabilidade relativa a eletrólitos da cultivar Pinto, mas apenas quando a AOT40 foi a mais elevada. Além disso, produziu uma antecipação significativa no tempo de abscisão foliar nas cultivares Pinto, Fepagro e Guapo. A variabilidade observada nas medidas de biomassa total, refletiu as limitações para se executar estudos de longo prazo em condições ambientais controladas, um dos principais desafios ainda por ser superado antes que se possa obter dados mais conclusivos sobre os danos em espécies cultivadas resultantes do enriquecimento do ozônio toposférico.
Palavras-chave: fotossíntese, permeabilidade relativa a eletrólitos, abscisão foliar, biomassa.
Ozone (O3) is present in low concentrations throughout the atmosphere and in the stratosphere is beneficial, since its O3 layer prevents potentially damaging ultraviolet light from reaching the Earth's surface. However, when O3 is continuously formed in the troposphere it becomes an air pollutant with harmful effects on a wide variety of plants, including native vegetation and important crops. In the last few decades, anthropic activities have induced significant increases in tropospheric ozone concentrations on a global scale (Bray et al., 2000). The majority of ground level O3 formation occurs when precursors gases such as nitrogen oxides (NOx), carbon monoxide (CO) and several volatile organic compounds, react in the atmosphere in the presence of sunlight. Industrial emissions, motor vehicle exhaust, and chemical solvents are the major anthropogenic sources of these precursors. Ozone, which is part of the group of photochemical oxidants, has a harmful effect on vegetation and animals because of its high oxidative power (Halliwell and Gutteridge, 2007), thus intensifying the formation of reactive oxygen species (ROS) in the cells (Bray et al., 2000).
In human beings, O3 or its derived free radicals are associated with the increased incidence of lung diseases; irritated eyes, nose and throat; nausea; headache and prematurely aged skin (Klumpp et al., 2001). In plants several physiological and biochemical processes associated with carbon assimilation and, thus, with vigor and productivity, are adversely impacted by O3, and some evidences suggest that this pollutant could be more damaging to vegetation than all other air pollutants together (Elagöz and Manning, 2005).
According to Heggestad (1991) and Nali et al. (1998), sensitivity to O3 differs among species and even among cultivars and ecotypes, but the mechanisms involved in this differential susceptibility has not yet been well understood. Moreover, it would be very useful to define the characteristics of the plants that can be used as indicators of their sensitivity potential to O3 exposure, but the key parameter is not yet known (Ribas et al., 2005). The factors that determine plant sensitivity or tolerance have not yet been clarified, but it seems clear that they involve physiological, anatomical, biochemical and environmental aspects (Alonso et al., 2001). Therefore, the ranking of relative resistance to ozone often varies with the criterion used for it determination (Pearson et al., 1996).
Among the few articles that concern sensitivity to O3 for native and naturalized species, most are based, for the short term, on observing the development of visible symptoms, and for the long term, on the effects on growth and reproductive effort (Bungener et al., 1999). However, these parameters are not always easy to interpret, since they are influenced by several other environmental factors or take a long time to evaluate. Furthermore, they must considered evidence of a physiological and/or biochemical response to the pollutant (Scebba et al., 2006) and even so, visible damage does not necessarily indicate sensitivity in terms of growth reduction. Nonetheless, a close relationship has been shown between the appearance of some symptoms and different degrees of susceptibility to the pollutant (Guidi et al., 1998).
Of all physiological processes affected by O3, photosynthesis appears to be particularly sensitive and reductions in this process may occur even before appearance or in the absence of any visible symptoms (Guidi et al., 1997). According to Pell et al. (1994), the photosynthetic process may be affected by the occurrence of damage involving stomatal movements, the collection of light or the biochemical stage of CO2 fixation. The total photosynthetic capacity of the plant may also be reduced by loss of leaves (accelerated senescence, and/or reduced production), and by the increased respiratory rate to perform functions such as repairing cell constituents, or by the increased production of certain compounds (ATP and reductant compounds) needed for detoxification and defense (Mooney and Winner, 1988). On the other hand, the biomass responses are part of the ozone-induced physiological changes, and thus they can be used as a valuable criterion to classify the sensitivity of species/cultivars to this pollutant (Ribas et al., 2005). Finally, relative electrolyte leakage is a precious tool to evaluate the lipid damage that so commonly occurs under oxidative stress conditions.
Based on the above, and taking into account that the current critical levels of O3 to protect agricultural crops, natural vegetation and forest species against adverse effects are based on dose-response relations derived mainly from experiments with open-top chambers (Grünhage et al., 2001), a plant gasification system was built with an ozone -enriched atmosphere. The main objective of this work was to evaluate the effects of ozone exposure on five bean (Phaseolus vulgaris L.) cultivars, four of them developed by FEPAGRO North Coast (located in Rio Grande do Sul, Brazil), and one that is known to be ozone sensitive, US Pinto 111 (Arndt et al., 1987), using for this purpose photosynthetic parameters, relative electrolyte leakage, foliar abscission and total biomass of the seedling.
MATERIALS AND METHODS
The chambers: Based on the model developed by Mandl et al. (1973) and Heagle et al. (1973), and improved by Aidar et al. (2002), two open-top chambers were built, 90 cm in diameter by 106 cm high. In one of them an ozonizer was connected (OZ Engenharia, model GHR150B, Porto Alegre, Brazil), equipped with three O3 production cells, corona effect, with a nominal production of 85 mg.h-1 each.
Cultivation conditions: The bean seeds (Phaseolus vulgaris L.) of the Fepagro 26, Guapo Brilhante, Macotaço, Iraí and US Pinto 111 cultivars were sown in plastic 2-liter bottles, cut at a height of 20 cm, with a perforated base and involved with brown paper. The culture substrate used was prepared with a volume proportion of 2:1:1 of vermiculite (medium), sand (medium and washed), and peat, respectively, which was previously homogenized. In each vase three seeds were placed and before the beginning of exposure the excess seedlings were removed leaving only a single seedling per vase.
Until the time of exposure, the seedlings were kept on a bench at the Center of Ecology of the Federal University of Rio Grande do Sul (UFRGS), in the municipality of Porto Alegre RS, under a sombrite-type mesh (cutting 30% radiation) and in the unpolluted ambient air. The vases were irrigated daily, and one day before the beginning of exposure, each vase received 100 mL of fertilizer solution (4 g L-1 of Vitaplan Nutriverde 13-13-15 + Micronutrients - Nutriplan Products Company, Paraná, Brazil).
Fumigation: Seven fumigation events (experiments) were performed in all, the first four of them during the period from December 2006 to March 2007, and the last three during the period from September to December 2007. In all of them, eight days after sowing (stage V2, according to Elagöz and Manning, 2005), the seedlings were submitted to treatments with and without the addition of ozone to the ambient air inside the two open-top chambers, next to the Center of Ecology at UFRGS, in a fenced-in area of 9 m2 lined with sombrite-type mesh (cutting 30% radiation), in the open air. The period of exposure was always one week, with daily fumigation from 1000 to 1600 h.
During exposure each chamber was irrigated daily with five liters of water, and in each of the 7 experiments performed, 5 seedlings/treatment/cultivar were used, a total of 50 seedlings per experiment, i.e. 25 seedlings per chamber. The distribution of the plants within each chamber was done by drawing lots, but the position of each plant was not changed during the period of exposure. However, it should be emphasized that there was rotation of the chambers, i.e, in each lot of the experiment, the ozonized and non-ozonized chamber were alternated.
Ozone concentration inside the chambers was monitored by the iodometric method (APHA, 1992). Gases were sampled in a fresh washer of the impinger type, containing 75 mL of absorbent solution of KI 2% with the help of a gas sampler (LaMotte, model BD, Chestertown, USA) at a flow of 1.5 L min-1. The sampling point was located in the central position of the chambers in relation to their diameters, and at the height of the unifoliolated primary leaves. The concentrations at each exposure and in each chamber can be viewed in table 1. In order to compare the ozone doses fumigated in each lot of the experiment, the AOT40 (AOT Accumulative Exposure over a Threshold) criterion was adopted, which is simply the hourly accumulative O3 concentration over the 40 ppbv threshold (expressed in ppb h) (Martins and Rodrigues, 2001).
Photosynthetic parameters: The response curves to CO2 (A/Ci curves), performed after the end of the first, fourth and fifth experiments were obtained by using an infrared gas analyzer (CIRAS 2, PPSystems, Hitchin, UK), with a cuvette measuring 4.5 cm2, photosynthetically active radiation of 800 µmol.m-2.s-1, chamber temperature at 25ºC and humidity adjusted to 60% of relative ambient air humidity. The measurements were performed during the period from 0800 to 1700 h, always on the unifoliolated primary leaves, in a room at the Center of Ecology at UFRGS, with controlled temperature between 24-26ºC. In addition, care was taken to measure always in pairs, i.e, exposed and non-exposed seedlings of a same cultivar were measured sequentially.
Based on the data extracted from the A/Ci curves, the following parameters were estimated: instantaneous net assimilation (A); maximum assimilation (Amax); carboxylation efficiency (ce); maximum rate of carboxylation of rubisco (Vcmax); maximum rate of electron transport (Jmax); stomatal limitation (Ls); stomatal conductance (gs); transpiration (E); CO2 ratio of the leaf intercellular air space and ambient CO2 (Ci/Ca); water use efficiency and respiration (WUE).
To obtain instantaneous net assimilation, stomatal conductance, transpiration and Ci/Ca ratio, the first point on the A/Ci curve of each plant (Ca of approximately 350 µmol.m-2.s-1) was used.
The estimation of maximum photosynthetic assimilation and carboxylation efficiency was obtained from the adjustment of curve A/Ci to the equation proposed by Prado and Moraes (1997).
Maximum rate of carboxylation of rubisco, maximum rate of electron transport and respiration were estimated from the A/Ci curves with the help of the Photosynthesis Assistant program, version 1.1.2 (Parsons and Ogston, 1998), which is based on the von Caemmerer and Farquhar equations (1981).
The stomatal limitation was calculated from the response curves to CO2 using the equation developed by Farquhar and Sharkey (1982), modified by T. D. Sharkey.
Finally, the water use efficiency in each plant was calculated from the ratio between net photosynthetic assimilation and the transpiration of the first point on curve A/Ci, where the CO2 concentration is close to ambient.
Relative electrolyte leakage: In order to evaluate the relative electrolyte leakage, measured after the end of the first, fourth and fifth experiment, 10 disks of 6.7 mm in diameter each were used, extracted from the unifoliolated primary leaves, washed and incubated in three times distilled water. After 24 h incubation at ambient temperature, the electrical conductivity of the solution was measured in a conductivity meter (WTW, model LF197). The disks were then frozen in liquid nitrogen and then immersed in three times distilled water for over 24 h, after which the electrical conductivity was measured again. The relative electrolyte leakage (REL) was calculated according to the following equation:
Where: C1 = conductivity measured during the first 24 h,
C2 = conductivity measured during the following 24h.
Foliar abscission: Foliar abscission, evaluated in the third and seventh experiment, was calculated from the average of the number of days after appearing, that the two unifoliolated primary leaves took to fall off.
Dry mass accumulation: The total biomass of each seedling, both in the second and the sixth experiment, was washed in running water, dried in an oven for seven days at 60ºC and weighed on a semi-analytic scale (Sartorius, 2006 MP).
Statistical analysis: The data obtained were analyzed in the Sigmastat SPSS Institute Inc., version 2.03) statistical program, using the t-Test. When the data was not homogeneous as to variances and normality of distribution (required to apply this analysis), the Mann-Whitney non-parametric test was performed. The significance criteria adopted were values of α < 0.05 and α < 0.10 was considered the tendency.
RESULTS AND DISCUSSION
Photosynthetic parameters: The photosynthetic parameters were evaluated in the first, fourth and fifth experiment. In the first, that had an AOT40 of approximately 154 ppb h, exposure to ozone caused a significant reduction in the instantaneous net assimilation of Guapo, Fepagro and Macotaço cultivars (p = 0.005; 0.038 and 0.046, respectively) (Figure 1A). In the fourth experiment, with an AOT40 of about 587 ppb h, the exposure to ozone did not cause significant reductions in the instantaneous net assimilation of any cultivar, although a tendency was found for cultivars Fepagro and Guapo (p = 0.076 and 0.090, respectively) (Figure 1B), and an anticipation of the senescence of primary leaves occurred in treatment with O3, which culminated in foliar abscission, even before the A/Ci curves were measured in four of the five seedlings of the Pinto cultivar and in a seedling of Iraí, Fepagro and Macotaço cultivars. In the fifth experiment with an AOT40 of approximately 304 ppb h, there was a significant reduction in the instantaneous net assimilation of Fepagro and Pinto cultivars and a tendency to reduction in the Iraí cultivar (p = 0.004, 0.006 and 0.084, respectively) (Figure 1C).
The mean instantaneous net assimilation values of all cultivars, both for plants exposed and for the controls, were above those found by Guidi et al. (2000) in their experiment with beans of the Pinto cultivar, which found assimilation values of 5 µmol.m-2.s-1 for the plants in the control treatment and 3.64 µmol.m-2.s-1 for plants exposed to ozone (150 ppb for 2 hours). The exception was experiment 4, which had values that were generally a bit lower, although very similar to those of Guidi et al. (2000).
Knowing that the instantaneous net photosynthesis suffers a strong effect from the environment, the low photosynthesis values found in experiment 4, which was performed in March 2007, may, at least in part, be accounted for by the high temperatures associated with low light intensity. The low light intensity during this lot of the experiment occurred due to less obliqueness of the sunrays, which was worsened by the existence of a building that blocked the light during most of the day, because of the season at the time.
In Fepagro cultivar, instantaneous net assimilation was reduced by exposure to O3 in experiment 1 (154 ppb h of O3) and 5 (304 ppb h of O3), while in experiment 4 (587 ppb h of O3) there was only a tendency to reduction in this parameter. In the first experiment, this reduction was caused by the limitation in the carboxylation process (significant reduction in the maximum rate of carboxylation of rubisco 40.120 ± 7.011 µmol.m-2.s-1 in the control treatment against 25.260 ± 7.385 µmol.m-2.s-1 in the exposed plants and a tendency to reduction in the carboxylation efficiency 0.148 ± 0.064 µmol.m-2.s-1 in the control treatment against 0.080 ± 0.035 µmol.m-2.s-1 in the exposed plants) and by the availability of RuBP (tendency for reduction in the maximum rate of electron transport 70.760 ± 13.737 µmol.m-2.s-1 in control treatment against 52.060 ± 7.385 µmol.m-2.s-1 in the exposed plants). Although the stomatal conductance and transpiration did not present significant differences among treatments, there was a significant reduction in the stomatal limitation (10.546 ± 1.972% in the control treatment against 7.138 ± 2.430% in the exposed plants) and, consequently, in the water use efficiency (6.661 ± 0.928 µmol.mmol-1 in the control treatment against 4.623 ± 1.084 µmol.mmol-1 in the exposed plants), while the Ci/Ca ratio increased significantly (0.170 ± 0.049 in the control treatment against 0.642 ± 0.056 in the exposed plants). On the other hand the maximum assimilation showed a tendency to reduction (12.856 ± 1.547 µmol.m-2.s-1 in the control treatment against 10.252 ± 2.537 µmol.m-2.s-1 in the exposed plants), because of the limitations in the carboxylation process and the availability of RuBP. In the fifth experiment, the significant reduction in instantaneous net assimilation was accompanied by a significant reduction in the stomatal conductance (174.000 ± 15.149 mmol.m-2.s-1 in the control treatment against 78.800 ± 30.277 mmol.m-2.s-1 in the exposed plants), which caused a significant reduction in transpiration (2.790 ± 0.158 mmol.m-2.s-1 in the control treatment against 1.616 ± 0.463 mmol.m-2.s-1 in the exposed plants). However, the stomatal limitation had a tendency to reduction in the exposed plants (14.048 ± 5.141% in the control treatment against 8.894 ± 3.422% in the exposed plants), which indicates that the CO2 entering the leaves was not the limiting factor. Besides this, the Ci/Ca ratio and respiration did not present differences among treatments, which supports the idea that the limitation of the photosynthesis is not at the CO2 influx but in the tendency to reduce the maximum rate of electron transport. In the fourth experiment, although AOT40 was higher, there was only a tendency to reduction in the instantaneous net assimilation of this cultivar, caused by a significant reduction in carboxylation efficiency (0.125 ± 0.068 µmol.m-2.s-1 in control treatment against 0.036 ± 0.020 µmol.m-2.s-1 in the exposed plants). The maximum carboxylation velocity did not present a significant difference or tendency to difference among the treatment in this experiment.
In Guapo cultivar, instantaneous net assimilation was significantly reduced only in experiment 1. In the fourth experiment there was only a tendency to the reduction in assimilation without changes in the other parameters evaluated, and in the fifth, not even the instantaneous net assimilation was changed by exposure to ozone. The reduction of net assimilation in experiment 1 was caused by the limitation in the carboxylation process (significant reduction in the maximum rate of carboxylation of rubisco 67.280 ± 35.688 µmol.m-2.s-1 in the control treatment against 28.580 ± 7.374 µmol.m-2.s-1 in the exposed plants and of carboxylation efficiency 0.340 ± 0.400 µmol.m-2.s-1 in control treatment against 0.090 ± 0.027 µmol.m-2.s-1 in the exposed plants) and by the the availability of RuBP (tendency to reduction in the maximum rate of electron transport 88.100 ± 25.106 µmol.m-2.s-1 in control treatment against 61.960 ± 14.622 µmol.m-2.s-1 in the plants exposed). Although stomatal conductance and transpiration did not present significant differences among the treatments, there was a tendency to reduction in the stomatal limitation (13.847 ± 4.433% in control treatment against 8.845 ± 2.369% in the exposed plants) and a significant reduction in the water use efficiency (8.473 ± 2.138 µmol.mmol-1 in control treatment against 5.617 ± 0.855 µmol.mmol-1 in exposed plants), while the Ci/Ca ratio increased significantly (0.408 ± 0.121 in control treatment against 0.584 ± 0.063 in the exposed plants).
In Iraí cultivar instantaneous net assimilation was not significantly reduced in any of the three experiments performed, and the single parameters that were significantly altered were dark respiration in experiment 4, which increased in the plants exposed to ozone (0.820 ± 0.288 µmol.m-2.s-1 in control treatment against 1.232 ± 0.097 µmol.m-2.s-1 in the plants exposed), and maximum assimilation in experiment 5, which was reduced in the plants exposed (20.205 ± 5.069 µmol.m-2.s-1 in control treatment against 13.931 ± 3.256 µmol.m-2.s-1 in exposed plants).
In Macotaço cultivar the instantaneous net assimilation was significantly reduced only in experiment 1, and this was caused by a tendency to reducing carboxylation efficiency, (0.222 ± 0.078 µmol.m-2.s-1 in control treatment against 0.135 ± 0.035 µmol.m-2.s-1 in plants exposed) without concomitant changes in the maximum carboxylation velocity.
Finally, the Pinto cultivar did not present a significant difference in the instantaneous net assimilation and in any other photosynthetic parameter evaluated in experiment 1, which had the lowest AOT40. With an intermediate AOT40 (experiment 5), the instantaneous net assimilation was significantly reduced and with a higher concentration (experiment 4) there was foliar abscission in 4 of the 5 seedlings (exposed) even before the assimilation was measured, and a significant increase was only found in the relative electrolyte leakage since no statistical analysis could be performed. The reduction of net assimilation in experiment 5 can be attributed to a limitation in the carboxylation process (significant reduction in maximum rate of carboxylation of rubisco 49.560 ± 10.769 µmol.m-2.s-1 in control treatment against 25.900 ± 11.195 µmol.m-2.s-1 in the exposed plants and to the tendency to reduction in carboxylation efficiency 0.127 ± 0.053 µmol.m-2.s-1 in the control treatment against 0.066 ± 0.028 µmol.m-2.s-1 in the exposed plants) and by the availability of RuBP (significant reduction in the maximum rate of electron transport 103.220 ± 23.550 µmol.m-2.s-1 in control treatment against 54.360 ± 17.371 µmol.m-2.s-1 in the exposed plants). Although stomatal conductance has presented a tendency to reduction (187.600 ± 30.851 mmol.m-2.s-1 in control treatment against 131.600 ± 52.219 mmol.m-2.s-1 in the exposed plants), which reflected a tendency to concomitant reduction in transpiration (2.932 ± 0.277 mmol.m-2.s-1 in control treatment against 2.260 ± 0.645 mmol.m-2.s-1 in the exposed plants), there was a significant reduction in the stomatal limitation (14.363 ± 3.688% in control treatment against 7.320 ± 2.686% in exposed plants), and in water use efficiency (3.594 ± 0.393 µmol.mmol-1 in control treatment against 3.643 ± 0.735 µmol.mmol-1 in exposed plants). The significant reduction in the stomatal limitation mentioned above, the tendency to an increase in the Ci/Ca ratio (0.619 ± 0.074 in the control treatment against 0.706 ± 0.060 in the exposed plants) and significant reduction in respiration (1.786 ± 0.422 µmol.m-2.s-1 in control treatment against 1.184 ± 0.401 µmol.m-2.s-1 in exposed plants) indicate that the influx of CO2 into the leaf was not the limiting factor of photosynthesis.
The stomatal limitation reduction in the Fepagro cultivar (experiment 1) and in the Pinto cultivar (experiment 5), and the tendency to reduction of the stomatal limitation in the Fepagro cultivar (experiment 5) and in the Guapo cultivar (experiment 1) is directly related to the limitation in the caboxylation process (amount and activity of rubisco), since it will generate a smaller difference between the net assimilation of Ci350 and Ca350 in the plants exposed. On the other hand, the reduction in the efficiency of water use for these same cultivars and experiments (except the Fepagro cultivar experiment 5, which did not present changes in water use efficiency when exposed to ozone) was the consequence of a significant reduction in the photosynthesis without concomitant reduction in transpiration. In the Pinto cultivar (experiment 5), although there was a tendency to reduction of transpiration, it did not occur in the same proportion as the decrease in assimilation, which justifies the significant reduction in water use efficiency for this cultivar.
The significant increase in the Ci/Ca ratio in Fepagro (experiment 1) and Guapo cultivar (experiment 1) and the tendency to increase this same ratio in Pinto cultivar (experiment 5) are consequences of the significant reduction in the maximum rate of carboxylation of rubisco, and the reduction (Guapo cultivar) or tendency to reduction (Fepagro and Pinto cultivars) of the carboxylation efficiency which, in turn, cause a reduction in CO2 use, making it accumulate in the leaves, and thus allowing to even cause stomatal closing. That is why the significant reduction in stomatal conductance in Fepagro cultivar (experiment 5) and the tendency to reduction in Pinto cultivar (experiment 5) did not cause increased stomatal limitation. As to dark respiration, this cannot be involved in the increased Ci/Ca ratio, since the concentration of CO2 respiration is very small compared to what is assimilated, and also because no significant difference was found between the treatments for this parameter in Fepagro and Guapo cultivars (experiment 1), and in Pinto cultivar (experiment 5) there was a significant reduction in respiration.
The reduction in net assimilation is often the first detectable symptom observed in plants treated with ozone (Reichenauer et al., 1998). Among the parameters most associated with this decrease in the present study are maximum rate of carboxylation of rubisco, which presented significant reduction in Fepagro (experiment 1), Guapo (experiment 1) and Pinto (experiment 5), and carboxylation efficiency which presented a significant reduction in Fepagro cultivar (experiment 4) and Guapo cultivar (experiment 1) and the tendencies to reduction in Fepagro cultivar (experiment 1), Macotaço cultivar (experiment 1) and Pinto cultivar (experiment 5). Both maximum rate of carboxylation of rubisco, and carboxylation efficiency reflect the activity of rubisco in vivo (Rogers and Humphries 2000), and carboxylation reductions were considered the main factors responsible for impairment in photosynthesis by Pell et al. (1994) and Guidi et al. (2001).
Guidi et al. (2000), working with bean plants of Pinto cultivar, also found results that agree with the idea that the primary target of ozone are the enzymes involved in the Calvin cycle and, particularly, rubisco activity. Rubisco inhibition induces less use of NADPH and ATP, and this consequently causes a reduction in the activity of the electron transportation system, and an increased proportion of closed reaction centers of Photosystem II. Closed reaction system, in turn, are in a greater state of reduction in QA (Quinone A), which may increase plant susceptibility to photoinhibition.
In this study, the maximum rate of electron transport, which presented a significant reduction only in Pinto cultivar (experiment 5), but which had a tendency to reduction in Fepagro cultivar (experiment 1 and 5) and in Guapo (experiment 1), also appears to have contributed to the reductions found in net assimilation. Another reason for reduction in electron transportation is mentioned by Calatayud et al. (2003), who say that ozone can alter photochemical reactions of photosynthesis, reducing the electron transportation rate between the two photosystems. In this way, photosynthesis inhibition may be the result of reduced ATP and NADPH availability (Calatayud et al., 2004). Besides, gluthatione, which is acknowledged as the central component of antioxidant defense in most aerobic organisms (Foyer et al., 1997), requires NADPH both for its synthesis and for its reduction. Thus again, the photosynthesis decline observed may be the result of less NADPH available for carbon reduction (Gupta et al., 1991). Calatayud et al. (2002) mention decreased electron transportation as one of the mechanisms responsible for reducing the photosynthesis process in Lactuca sativa L.
On the other hand, stomatal conductance presented a significant reduction only in Fepagro cultivar (experiment 5) and a reduction tendency only in Pinto cultivar (experiment 5), but these reductions were not related to decreased assimilation. Reductions in stomatal conductance caused by exposure to ozone were also found by Guidi et al. (2000) in the Pinto cultivar of P. vulgaris plants. Studies indicate that stomatal conductance may increase or diminish in response to damage caused by ozone, depending on the genotype, ozone concentration and sensitivity of the guard cells (Robinson et al., 1998). According to McAinsh et al. (2002) a rapid decline in stomatal opening, and therefore in stomatal conductance, is commonly observed in the presence of ozone during a short period of exposure, while long duration exposure to ozone slows down stomatal responses.
Noormets et al. (2001) and Zheng et al. (2002) reported that the decreases in rubisco content and activity, rather than the electron transportation and regenerative capacity of ribulose-1,5-bisphosphate(RuBP), are the primary factors responsible for the deleterious effects of ozone in CO2 assimilation. In addition to the effects on rubisco and RuBP regeneration, another factor which may potentially affect the assimilation of CO2 is the decreased stomatal opening (Zheng et al., 2002). However the decreased stomatal opening may be a reflection of maintaining the leaf intercellular concentration of CO2 caused by the inhibition of the carboxylation process. Therefore, according to Farage and Long (1999) the low stomatal conductance may be only partially responsible for the decreased rate of photosynthesis through the limitation of CO2 influx.
Relative electrolyte leakage: Concerning the relative electrolyte leakage, O3-exposure to 154 ppb h (experiment 1 did not produce a change in the relative electrolyte leakage in any cultivar (Figure 2A). When AOT40 was raised to 304 ppb h (experiment 5) there was a tendency to an increase in Pinto cultivar (Figure 2C) and, finally, when exposure became 587 ppb h, there was a significant increase in Pinto cultivar and a tendency to an increase in Macotaço cultivar (Figure 2B). In the plants exposed to ozone, the electrolyte leakage is one of the first symptoms of damage to the membrane and results from oxidation of proteins of the sulphydryl group and lipids from the membrane (Guidi et al., 1999). Changes in membrane functioning affect a large range of cell processes, through loss of metabolytes and loss of compartmentalization, and may lead to increased tissue senescence (Weber et al., 1994).
Foliar Abscission: Foliar abscission was monitored in the third and seventh experiment. In the third, which had an AOT40 of approximately 153 ppb h, ozone exposure anticipated the abscission of the primary leaves of Pinto cultivar on average by 11 days (p = <0.001), and of Fepagro cultivar by 7 days (p = 0.004), besides presenting a tendency to a 5-day anticipation in Guapo cultivar (p = 0.090) (Figure 3A). However, under an AOT40 of about 212 ppb h (seventh experiment) Guapo cultivar was the only one which had a significant anticipation in abscission (an average of 3 days, with p = 0.004), and Fepagro cultivar presented a strong tendency to anticipation of approximately 4 days (p = 0.051) (Figure 3B).
Under physiological conditions, senescence is a highly regulated process, involving chlorophyll degradation, photosynthetic decline, protein degradation and lipid peroxidation, culminating in the remobilization of nutrients and foliar abscission (Ribas et al., 2005). The acceleration of senescence has been widely reported as one of the characteristic processes of exposure to O3 (Ribas et al., 2005; Ranford and Reiling, 2007). It can be anticipated by changes in the functioning of the membrane, which affect a great variety of cell processes by metabolite losses and the compartmentalization caused by lipid peroxidation from the membrane (Weber et al., 1994; Calatayud et al., 2003). However, it is not clear whether the acceleration of senescence is due to the induction of the normal process, i.e., to a type of programmed cell death as part of the hypersensitivity response, or the change in carbon budget, favoring respiration in detriment of net assimilation. Since in this study there were practically no changes in respiration and in the relative electrolyte leakage, and since there were few drops in assimilation, possibly senescence in response to oxidative stress is not related directly to the adverse effect on photosynthesis.
Total biomass of the seedling: The accumulation of total dry mass of the plant was evaluated in the second and sixth experiment. In the second, which had an AOT40 of approximately 209 ppb h, ozone treatment caused a tendency to reduction in this parameter, only in the Iraí (p = 0.056) and Fepagro (p = 0.084) cultivars (Figure 4A). In the sixth experiment, a slight increase of the total biomass of Iraí cultivar seedlings (p = 0.098) was observed at exposure to approximately 147 ppb h (Figure 4B).
Although ozone and its reaction products are known to reduce photosynthesis and change the carbohydrate allocation, causing a reduced accumulation of biomass (Rennenberg et al., 1996), this generally occurs over the longer term, as suggested by Davison and Barnes (1998).
In fact, it is noted that the results were not very stable, and a larger dose of ozone did not always damage the plants. This may be partly explained because the response of the plants to ozone is more strongly correlated with the cumulative influx of ozone through the stomata, than with the ozone concentration in the environment, which will depend on soil humidity, atmospheric vapor pressure deficit, wind velocity and air temperature, which influence the degree of stomatal opening (Fuhrer et al., 1992). Besides, it is known that although it was not measured, there was variation in the light intensity intercepted by the seedlings in every experiment depending on the season, and this was lower, especially in experiment 4, thus rendering less clear the differences between the control and exposed seedlings. It was also observed that on a day with bright sun the response to ozone was more marked than on cloudy days. This is because, besides speeding up the metabolism, high intensity light conditions intensify the production of ROS, which occur naturally during the photosynthetic process. In this sense, Guidi et al. (2000) evaluated the combined effects of high irradiance and ozone on the photosynthesis of primary bean leaves of Pinto cultivar, and concluded that the high light intensity may change the reaction of leaves to ozone treatment by reducing the thylakoidal electron transport rate and quantic productivity.
This study presents an overview of how five different bean cultivars respond to ozone exposure. It was noted that the response of photosynthetic parameters of bean seedlings to ozone exposure showed similar patterns in all cultivars, although they exhibited slightly different sensitivities.
In general, ozone shows a harmful effect on the instantaneous net assimilation sometimes yet affecting maximum assimilation. The reductions in both these parameters showed strong correlation with limitation in the carboxylation process (decrease in maximum rate of carboxylation of rubisco and carboxylation efficiency) and also with the decrease in maximum rate of electron transport. The limitation in the carboxylation process resulted in turn in a lower demand by CO2, which caused often an enhancement of Ci/Ca ratio, with few exceptions in which the Ci/Ca ratio remained unchanged. This buildup of leaf CO2 may lead a decrease in stomatal conductance and even transpiration although in our study both these parameters sometimes remain unchanged despite significantly enhance in Ci/Ca ratio. In addition, the buildup of CO2 leads to a decrease in stomatal limitation. Finally, even that cases in which there are some reduction in transpiration, the water use efficiency usually is reduced in plants exposed to ozone due the decrease in transpiration not be in the same proportion as the reduction in net assimilation.
Regarding the relative electrolyte leakage, relatively high doses of ozone (AOT40) were necessary to induce some increase in membrane ion leakage and even so it was not observed in all cultivars. Notwithstanding, the foliar abscission was anticipated in most cultivars with relatively low doses of ozone.
Despite the obvious harmful effects on the crop cultivation, we cannot make clear predictions of anticipated damages on the Phaseolus vulgaris species resulting from tropospheric ozone enrichment. The limitations to perform long-term controlled-environment studies, as discussed earlier, are one of the greatest challengers yet to be overcome in order to obtain well-replicated and more conclusive experiments to be performed in the field.
Acknowledgments: The authors thank Coordenação de Aperfeiçoamento de Pessoal de Nível Superior and Copesul for their financial help, and also OZ Engenharia for donating the ozonizer, as well as the support from engineers Sepé Tiarajú Fernandes dos Santos from Copesul and Fábio Rahmeier from OZ Engenharia.
Aidar MPM, Martinez CA, Costa AC et al (2002) Effects of atmospheric CO2 enrichment on the establishment of seedlings of jatobá. Biota Neotropica 2: 1-10. [ Links ]
Alonso R, Elvira S, Castillo FJ, Gimeno BS (2001) Interactive effects of ozone and drought stress on pigments and activities of antioxidative enzymes in Pinus halepensis. Plant Cell Environ 4: 905-916. [ Links ]
Arndt U, Nobel W, Schweizer B (1987) Bioindikatoren: Möglichkeiten, Grenzen und neue Erkenntnisse. Ulmer, Stuttgart. [ Links ]
APHA (1992) Standard methods for the examination of water and wastewater. 18thed. (Eds Greenberg, Connors, Jenkins). American Public Health Association, Washington, DC. [ Links ]
Bray EA, Bailey-Serres J, Weretilnyk E (2000) Responses to abiotic stresses. In: Buchanan BB, Gruissen W, Jones RL (eds), Biochemistry & Molecular Biology of Plants, pp. 1158-1203. American Society for Plant Physiology, New York. [ Links ]
Bungener P, Balls GR, Nussbaum S et al (1999) Leaf injury characteristics of grassland species exposed to ozone in relation to soil moisture condition and vapour pressure deficit. New Phytol 142: 271-282. [ Links ]
Calatayud A, Alvarado JW, Barreno E (2002) Similar effects of ozone on four cultivars of lettuce in open top chambers during winter. Photosynth 40 (2): 195-200. [ Links ]
Calatayud A, Iglesias DJ, Talón M, Barreno E (2003) Effects of 2-month ozone exposure in spinach leaves on photosynthesis, antioxidant systems and lipid peroxidation. Plant Physiol Biochem 41: 839-845. [ Links ]
Calatayud A, Iglesias DJ, Talón M, Barreno E (2004) Response of spinach leaves (Spinacia oleracea L.) to ozone measured by gas exchange, chlorophyll a fluorescence, antioxidant systems and lipid peroxidation. Photosynth 42 (1): 23-29. [ Links ]
Davison AW, Barnes JD (1998) Effects of ozone on wild plants. New Phytol 139: 135-151. [ Links ]
Elagöz V, Manning, WJ (2005) Responses of sensitive and tolerant bush beans (Phaseolus vulgaris L.) to ozone in open-top chambers are influenced by phenotypic differences, morphological characteristics and the chamber environment. Environ Pollut 136:371-383. [ Links ]
Farage PK, Long SP (1999) The effects of ozone fumigation during leaf development on photosynthesis of wheat and pea: an in vivo analysis. Photosynth Res 59: 1-7. [ Links ]
Farquhar GD, Sharkey TD (1982) Stomatal conductance and photosynthesis. Annu Rev Plant Physiol 33: 317-345. [ Links ]
Foyer CH, Lopez-Delgado H, Dat JF, Scott IM (1997) Hydrogen peroxide and glutathione associated mechanisms of acclimatory stress tolerance and signalling. Physiol Plant 100: 241-254. [ Links ]
Grünhage L, Krause GHM, Köllner B et al (2001) A new flux-orientated concept to derive critical levels for ozone to protect vegetation. Environ Pollut 111:355-362. [ Links ]
Guidi L, Nali C, Ciompi S, Lorenzini G, Soldatini GF (1997) The use of chlorophyll fluorescence and leaf gas exchange as methods of studying the different responses to ozone of two bean cultivars. J Exp Bot 48: 173-179. [ Links ]
Guidi L, Nali C, Lorenzini G, Soldatini GF (1998) Photosynthetic response to ozone of two poplar clones showing different sensitivity. Chemosfere 36: 657-662. [ Links ]
Guidi L, Bongi G, Ciompi S, Soldatini GF (1999) In Vicia faba leaves photoinhibition from ozone fumigation in light precedes a decrease in quantum yield of functional PS2 centres. J Plant Physiol 154: 167-172. [ Links ]
Guidi L, Tonini M, Soldatini GF (2000) Effects of high light and ozone fumigation on photosynthesis in Phaseolus vulgaris. Plant Physiol Biochem 38: 717-725. [ Links ]
Guidi L, Nali C, Lorenzini G, Soldatini GF (2001) Effect of chronic ozone fumigation on the photosynthetic process of poplar clones showing different sensitivity. Environ Pollut 113: 245-254. [ Links ]
Gupta AS, Alscher RG, Mccune D (1991) Response of photosynthesis and cellular antioxidants to ozone in Populus leaves. Plant Physiol 96: 650-655. [ Links ]
Halliwell B, Gutteridge JMC (2007) Free radicals in biology and medicine. 4thed. Oxford University Press Inc., New York. [ Links ]
Heagle AS, Body DE, Heck WW (1973) An open-top field chamber to assess the impact of air pollution on plants. J Environ Qual 2: 365-368. [ Links ]
Heggestad HE (1991) Origin of Bel-W3, Bel-C and Bel-B tobacco varieties and their use as indicators of ozone. Environ Pollut 74: 264-291. [ Links ]
Klumpp A, Ansel W, Klumpp G, Fomin A (2001) Um novo conceito de monitoramento e comunicação ambiental: a rede européia para avaliação da qualidade do ar usando plantas bioindicadoras (EuroBionet). Rev Bras Bot 24 (4): 511-518. [ Links ]
Mandl RH, Weinstein LH, Mccune DC, Keveny M (1973) A cylindrical, open-top chamber for the exposure of plants to air pollutants in the field. J Environ Qual 2: 371-376. [ Links ]
Martins RA and Rodrigues GS (2001) Efeitos potenciais do ozônio troposférico sobre as plantas cultivadas e o biomonitoramento ambiental. In: de Lima MA, Cabral OMR, Miguez JDG (eds), Mudanças climáticas globais e a agricultura brasileira, pp.143-165. EMBRAPA Meio Ambiente, Jaguariúna, SP. [ Links ]
Mcainsh MR, Evans NH, Montgomery LT, North KA (2002) Calcium signalling in stomatal responses to pollutants. New Phytol 153 (3): 441- 447. [ Links ]
Mooney HA, Winner WE (1988) Carbon gain, allocation and growth as affected by atmospheric pollutants. In: Schulte-Hostede S, Darral NM, Blank LW, Wellburn AR (eds), Air pollution and plant metabolism, pp. 272-287. Elsevier Applied Science, London. [ Links ]
Nali C, Guidi L, Filippi F, Soldatini GF, Lorenzini G (1998) Photosynthesis of two poplar clones contrasting in O3 sensitivity. Trees 12: 196-200. [ Links ]
Noormets A, Sober A, Pell EJ et al (2001) Stomatal and non-stomatal limitation to photosynthesis in two trembling aspen (Populus tremuloides Michx.) clones exposed to elevated CO2 and/or O3. Plant Cell Environ 24: 327-336. [ Links ]
Parsons R, Ogston SA (1998) Photosynthesis Assistant Windows software for analysis of photosynthesis. Vers. 1.1.2. Dundee Scientific, Dundee, Scotland. [ Links ]
Pearson S, Davison AW, Reiling K, Ashenden T , Ollerenshaw JH (1996) The effects of different ozone exposure on three contrasting populations of Plantago major L. New Phytol 132: 493-502. [ Links ]
Pell EJ, Eckart NA, Glick RE (1994) Biochemical and molecular basis for impairment of photosynthesis potential. Photosynth Res 39: 453-462. [ Links ]
Prado CHBA, Moraes JAPV (1997) Photosynthetic capacity and specific leaf mass in twenty woody species of Cerrado vegetation under field conditions. Photosynth 33:103-12. [ Links ]
Ranford J, Reiling K (2007) Ozone induced leaf loss and decreased leaf production of European Holly (Ilex aquifolium L.) over multiple seasons. Environ Pollut 145:355-364. [ Links ]
Reichenauer TG, Goodmann BA, Kostecki P, Soja G (1998) Ozone sensitivity in triticum durum and t. aestivum with respect to leaf injury, photosynthetic activity and free radical content. Physiol Plant 104: 681-686. [ Links ]
Rennenberg H, Herschbach C, Polle A (1996) Consequences of air pollution on shoot-root interactions. J Plant Physiol 148: 296-301. [ Links ]
Ribas A, Peñuelas J, Elvira S, Gimeno BS (2005) Ozone exposure induces the activation of leaf senescence-related process and morphological and growth changes in seedlings of Mediterranean tree species. Environ Pollut 134: 291-300. [ Links ]
Robinson MF, Heat J, Mansfield TA (1998) Disturbances in stomatal behaviour caused by air pollutants. J Exp Bot 49: 461-469. [ Links ]
Rogers A, Humphries SW (2000) A mechanistic evaluation of photosynthetic acclimation at elevated CO2. Glob Chang Biol 6: 1005-1011. [ Links ]
Scebba F, Giuntini D, Castagna A, Soldatini G, Ranieri A (2006) Analysing the impact of ozone on biochemical and physiological variables in plant species belonging to natural ecosystems. Environ Exp Bot 57: 89-97. [ Links ]
Von Caemmerer S, Farquhar GD (1981) Some relationships between the biochemistry of photosynthesis and the gas exchange of leaves. Planta 153: 376-429. [ Links ]
Weber JA, Tingey DT and Andersen CP (1994) Plant response to air pollution. In: Wilkinson RE (ed), Plant-environment interactions, pp. 355-411. Marcel Dekker, New York. [ Links ]
Wullschleger SD (1993) Biochemical limitations to carbon assimilation in C3 plants a retrospective analysis of the A/Ci curves from 109 species. J Exp Bot 44: 907-920. [ Links ]
Zheng Y, Shimizu H, Barnes JD (2002) Limitations to CO2 assimilation in ozone-exposed leaves of Plantago major. New Phytol 155: 67-78. [ Links ]
Received: 17 November 2008; Accepted: 16 March 2010.
Abbreviations: A, Instantaneous net assimilation per unit leaf area; Amax Maximum assimilation; AOT40, Hourly accumulative O3 concentration over the 40 ppbv threshold; ATP, Adenosine triphosphate; Ci/Ca, Ratio of the concentration of CO2 in the leaf intercellular air space and the bulk CO2; CO2, Carbon dioxide; E, Transpiration per unit leaf area; ce, Carboxylation efficiency; ROS, Reactive oxygen species gs, Stomatal conductance to CO2 diffusion; Jmax, Maximum rate of electron transport; Ls, Stomatal limitation; NADPH, Reduced nicotinamide adenine dinucleotide phosphate; O3, Ozone; RuBP, Ribulose-1,5-biphosphate; Vcmax, Maximum rate of carboxylation of rubisco; REL, Relative electrolyte leakage; WUE, Water use efficiency.
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