Services on Demand
- Cited by SciELO
- Access statistics
- Cited by Google
- Similars in SciELO
- Similars in Google
On-line version ISSN 0717-3458
Electron. J. Biotechnol. vol.15 no.4 Valparaíso July 2012
Production of phenolic metabolites by Deschampsia antarctica shoots using UV-B treatments during cultivation in a photobioreactor
Álvaro Sequeida1 · Eduardo Tapia1 · Marcelo Ortega2 · Pablo Zamora3 · Álvaro Castro2 · Christian Montes4 · Gustavo E. Zúñiga5 · Humberto Prieto*4
1Universidad Técnica Federico Santa María-Pontificia Universidad Católica de Valparaíso, Programa Doctorado en Biotecnología, Valparaíso, Chile
*Corresponding author: email@example.com
Financial support: FONDEF, Instituto Chileno Antártico, BIOFRUTALES.
Keywords: Deschampsia antarctica, phenolic compounds, temporary immersion bioreactor, UV-B elicitation.
Deschampsia antarctica (DA), the only species in the Gramineae family endemic to the Antarctic territory, is characterized by a combination of high levels of free endogenous phenylpropanoid compounds under normal in situ and in vitro growth conditions. In this article, we describe the design and use of a specific temporary immersion photobioreactor to produce both increased DA biomass and secondary metabolite accumulation by UV-B elicitation during cultivation. Three min-long immersions in an induction medium applied every 4 hrs at 14ºC ± 1 and 20/4 hrs light/darkness photoperiod increased DA biomass production over previous in vitro reports. Biomass duplication was obtained at day 10.7 of culturing, and maximum total phenolics and antioxidant activity were observed after 14 day of culturing. The addition of UV-B radiation pulses for 0.5 hrs at 6 hrs intervals increased total phenolics and antioxidant activity more than 3- and 1.5- fold, respectively, compared to controls with no UV-B. Significant accumulation of scopoletin, chlorogenic acid, gallic acid and rutin was found in these plantlets. This is the first bioreactor designed to optimize biomass and phenylpropanoid production in DA.
In Antarctica, environmental factors such as low temperatures (0 to 6ºC during the summer and 0 to -6ºC during the winter, Alden and Hermann, 1971), limited water availability (Robinson et al. 2003), high salinity and high levels of UV-B radiation (Alberdi et al. 2002) are limiting conditions for most plants. However, these conditions have not affected D. antarctica (DA), one of the two flowering plants native to the continent. Many studies have documented the deleterious effects of UV-B on plants, including reduced growth and photosynthesis (Germ et al. 2005; Ruhland et al. 2005). UV-B also places oxidative stress on aerobic cells (Yang et al. 2005; Yannarelli et al. 2006), which leads to the generation of several reactive oxygen species (superoxide anion, hydrogen peroxide and hydroxyl radical), each of which targets different macromolecules (Apel and Hirt, 2004).
One of the most interesting aspects of DA is its ability to generate high levels of compounds derived from the phenylpropanoid pathway, i.e. phenolic acids and flavonoids (Ruhland et al. 2005). These compounds in turn generate antioxidant activity and protective action against UV-B through a selective sunscreen protection that affects targets in the mesophyll. UV-B increases the concentration of flavonoids in DA (Day et al. 2001; Van de Staaij et al. 2002; Ruhland et al. 2005) such as orientin, luteonin and isoswertiajaponin 2''-O-beta-arabinopyranoside (Webby and Markham, 1994; Rozema et al. 2002). Flavonoids act as photoreceptors, anti-microbial, feeding deterrents, metal chelators and antioxidants, protecting plants against factors that induce the oxidative stress and damage caused by free radicals (Kliebenstein, 2004; Ververidis et al. 2007).
Experts in the field of metabolic engineering have shown a great deal of interest in the production of antioxidant compounds (Ververidis et al. 2007), and DA is a very attractive natural source of these compounds. However, limited access to Antarctica and the difficulties that this territory presents for the planning of basic or applied research programs stand as obstacles to the plants use in biotechnology.
Adequate culture systems offer important operational plasticity, expanding experimental scopes and offering culturing changes that can be measured in real time. Several reports support the use of temporary immersion bioreactors (TIBs) as high efficiency tools for optimizing the production of plant materials (Escalona et al. 1999; McAlister et al. 2005; Etienne et al. 2006). However, very few researchers describe these systems as tools for optimizing secondary metabolite production (Quiala et al. 2006; Arencibia et al. 2008).
In this study, researchers designed and used a TIB for both DA biomass propagation and UV-B light elicitation in order to allow for in vivo synthesis and the accumulation of phenylpropanoid-derived compounds.
DA plants from Robert Island were prepared, transported to the laboratory, stored and propagated as described by Zamora et al. (2010). In this solid-state (S-St) procedure, shoots are stored and propagated using a micro-propagation medium every 21 day. Plantlets from S-St were used as experimental inoculums for TIB experimentation. Inoculums were leaf and root cuts of 1 and 0.5 cm in length, respectively. Between 10 and 15 explants (1.2 g fresh weight) were used as inoculums.
TIB design and construction
The TIB was made from two Pyrex glass vessels connected by stainless steel joints and pipes; an upper vessel (UPV; Figure 1a) containing shoots in culture with a 1 cm water jacket to keep the culturing temperature constant and a lower vessel (LOV; Figure 1b) containing culture media. The system was designed exclusively for DA propagation at bench scale using MS-Visio Software 2010 (Microsoft). The UPV consisted of a cylindrical section and a truncated cone section. The cylindrical section was defined by:
In which Hi is the maximum height reached by DA shoots kept under the S-St system before a new round of propagation (8 cm in average) and D is the diameter of the section.
The volume added to the upper container by the truncated cone was defined by:
In which R and r are the radius of the upper and lower sections of the cone, respectively. The total volume of UPV was obtained by adding the two volumes.
The LOV consisted of a cylindrical section and a truncated cone section. However, the volume of LOV only included the cylindrical section of the vessel defined using Equation 1 because the truncated section was used as an over-pressure cavity in order to allow the medium to flow towards the UPV.
For UPV, the operative volumetric value was 1 L using the length of the UV-B light lamp (13.4 cm, Type G4T5E, Sankyo Denki Co, Ltd., Tokyo, Japan) as the diameter of the vessel. The height of the bioreactor was 60% overestimated due to the addition of inner luminescence and in order to avoid the immersion of the light lamp in culture medium and provide adequate headspace for gas exchange. Compressed air was pumped by a Vento 1000 compressor (Indura S.A. Inc., Santiago, Chile), allowing pneumatic culture media to transfer from LOV to UPV. Once interrupted, the culture media flushed back. All of this was controlled by a solenoid valve. The pump tubing was silicon Masterflex L/S LS17 and LS 18 (Cole-Palmer, IL, USA), and the air filters were Millipore FG 0.2 mm (Millipore, Billerica, MA, USA).
The temperature in the water jacket in the UPV was maintained at 14ºC with a Thermo-Circulator Labtech circulator (Alexandra Point, Singapore). The shoots were placed in a stainless steel grid (Figure 1c). Culture media were contained in the LOV. The valves allowed for culture media sampling and sucrose consumption monitoring. Immersion duration and frequencies were controlled by a 6-station Orbit® WaterMaster® temporizer (North Salt Lake, Utah, USA) which allowed researchers to open and close a ¾ diameter zero differential pressure solenoid Burket valve (Irvine, California, USA).
Culture establishment and UV-B light induction
Initial conditions for DA shoot culturing were set with a frequency of 6 three-min immersions per day. Micropropagation culture media were based on the method described by Zamora et al. (2010) modified for liquid culture supplemented with 0.2 mg/L kinetin and 0.3 mg/L benzylamino purine, henceforth the immersion medium (IM). All procedures were carried out at 14ºC ± 1 and under a 20/4 (day/night) light regime. For UV-B elicitation experiments, the lamp used emitted 0.34 mW cm-2 UV-B radiation on the stainless steel grid as experimentally determined by a VLX-3W CE radiometer with microprocessor (Vilber Lourmat, France). UV-B treatments were a pulse of 4 hrs per day at 49.6 kJ m-2 imitating peak situations of daily UV-B between noon and 3 pm during Antarcticas springtime (George et al. 2002) (A) or 0.5 hrs UV-B pulses at 6 hrs intervals per day at 6.2 kJ m-2 (B).
DA shoots were picked at 7, 14 and 21 days post-inoculation (dpi) in the UPV. In addition, 5 mL of IM was sampled every 2 days. Plantlets were transferred to filter paper in order to eliminate excess liquid for 45 min at room temperature and weighed. The sucrose content of IM samples was determined using acid hydrolysis methodology (Marques and Farah, 2009). For experiments in which UV-B led to the induction and identification of specific phenolic compounds, cultures were first subjected to a control white light photoperiod (20/4 hrs) in order to obtain 7-day growth biomasses. Additional 7 days of culturing under the specific UV-B treatments was then carried out.
Total phenolics extraction
Phenolics were extracted using a modified methodology based on Lin and Harnly (2007).
Total phenolics content
The total phenolics compound content was determined using a modified Folin-Ciocalteu colorimetric method (Asami et al. 2003).
Free radical scavenging activity of methanolic extracts was measured using the stable purple chromogen 2,2-diphenyl-1-picrylhydrazyl (DPPH) radical (Sigma-Aldrich, St. Louis, MO, USA) in the photometric assay adapted from Grzegorczyk et al. (2007). Free radical scavenging capacity was calculated and expressed using the equation:
% antioxidant activity = [(Absorbance of blank-Absorbance of sample)/Absorbance of blank] * 100
Volumetric productivity (Qx)
DA volumetric productivity was calculated by determining fresh weight in time-course analyses. Samples were picked at days 0, 7, 14 and 21 of cultivation. Three separate culturing batches were started using 1.2 g of cultured shoots.
Phenolics volumetric productivity (Qp)
Phenolics volumetric productivity was calculated as indicated by Asami et al. (2003). All plant material was sampled from the bioreactor at days 0, 7, 14 and 21 dpi. Three separate culturing batches were started using 1.2 g of cultured plantlets.
Analysis of phenolic compounds by LC/MS
A 6490 Triple Quadrupole LC/MS equipped with an ESI source (Agilent Technologies, Palo Alto, CA, USA) was used. All determinations were performed under negative ionization mode with a capillary voltage of 3000 V. Nitrogen was used as the nebulizer gas (35 psig) and drying gas at 10 L/min at a temperature of 300ºC. The PMT, fragmenter and skimmer were set at 850, 100 and 60 V, respectively. A full scan mass spectrum was acquired from m/z 100 to 1300. Data acquisition and processing were carried out using MassHunter MS Optimizer software (Agilent Technologies, Palo Alto, CA, USA). Separation was achieved on a C18 column; 150 x 4.6 mm I.D.; 5 µm particle size (Agilent Technologies, Palo Alto, CA, USA). The mobile phase consisted of water with 0.1% formic acid (a) and acetonitrile with 0.1% formic acid (b) at a flow rate of 0.5 mL/min. The linear elution gradient was from 80% (a) to 60% (a) in 20 min. Each run was followed by a 5 min wash with 100% (b) and an equilibration period of 11 min with 80% (a) /20% (b). The total run time for analysis was 20 min. Ten microliters of the sample were injected and peaks were to be assigned based on the mass of the standard compounds (Sigma).
All data were subjected to variance analyses. Means were separated using an LSD test at 5% significance using Statgraphics Centurion XV (Manugistics Inc., Rockville, MD, U.S.A.). Analysis of the specific growth rate (µ) in Table 1 was carried out using Tukeys test from the same software package. The results are shown as mean ± standard deviation (SD).
Previous micropropagation procedures for DA consisted of 21 days long sub-culturing cycles in IM (Zamora et al. 2010). Neither biomass gain nor active budding is experimentally obtained beyond this period. The use of an ad-hoc TIB (Figure 1a) allowed for the characterization of biomass production during this culturing (Figure 1e). Starting batching conditions in TIB led to a peak in biomass production of 3.0 ± 0.1 g/L after 14 days of cultivation with no significant biomass production beyond this stage. The biomass duplication rate was obtained from these data at around 10 days post inoculation (dpi). A high rate of sucrose consumption up to 5 dpi (Figure 1e) was observed. Although the synthesis of phenolic compounds observed between 7 and 21 dpi showed no statistical differences during that period (not shown), the highest value (5.1 ± 0.1 mg of GAE per mL/g FW) was determined at day 14. Interestingly, a peak of 23% in radical scavenging on DPPH was clearly established at 14 dpi as well (not shown), while antioxidant activity was dramatically reduced at the end of batching (21 dpi, 14.3 ± 0.01%). These data suggested a stationary phase of DA cultivation with maximal biomass production from 14 day of cultivation. The reduction in sucrose consumption rates observed after 5 dpi fits perfectly with the assumption that secondary metabolism is triggered (Collin, 2001), i.e. carbon skeletons and primary metabolites generated during the first part of the time-course (days 1-5) are linked to the implementation of metabolic processes unrelated to biomass duplication and closer to secondary metabolism pathways (days 6-14).
Analysis of induced compounds under simulated UV-B stress conditions was performed by comparing DA batches obtained after control [UV-B (-)] and two [UV-B (+)] situations in which the maritime Antarctic conditions during the plants growing season (i.e. up to 137 kJ m−2, (A)) were compared to a milder radiation presence (6.2 kJ m−2, (B)). The specific growth rate (µ) for the control situation was 0.065 * d-1 (Table 1), which led to a Qx of 0.22 gFW*d-1*L-1 at 14 dpi. The attenuated UV-B treatment (B) markedly reduced the total biomass yield to 0.19 (gFW*d-1*L-1) in the same term despite a similar µ of 0.064 d-1 (Table 1) that duplicated the biomass at 10.8 dpi. The intensive UV-B treatment (A) did not have a marked effect on biomass production prior to 14 dpi, and biomass did not begin to be duplicated until 12.4 dpi (Qx = 0.17 gFW*d-1*L-1). As a complement to these kinetic determinations, Qp of phenolic compounds was defined using TIB culturing in the presence of UV-B. Attenuated treatment led to important increases in Qp value in comparison to the control and extreme UV-B conditions. The content of phenolic compounds and radical scavenging activities in methanolic extracts confirmed that control cultures had increased amounts of total phenolic compounds and DPPH scavenging activity at 14 dpi compared to similar batching at 7 dpi (Table 1). However, (A) had a profoundly detrimental effect on both determinations at both batching times (Table 1). In contrast, the concentration of total phenolics under (B) showed a three-fold increase on average compared to control conditions at both dpi, and antioxidant activity showed a two-fold increase on average compared to the same controls at both dpi.
Table 1 reveals a cultivation step of up to 14 dpi in which biomass production with no visual impact on explants viability due to (B) is observed. An important synthesis of secondary metabolites is translated into higher Qp values than those observed in control situations. The use of this system for production of phenylpropanoid-related bioactive compounds was assayed by continuous 14-day long cultures. Pre-growth batches in which a DA biomass was grown by 7 day of culturing were subjected to treatments (A) and (B) during 7 day of additional batching. Mass spectrometry analyses of plantlets extracted from (B) treatments showed significant accumulation of compounds such as scopoletin and, to a lesser extent, chlorogenic acid, gallic acid and rutin. In contrast, and according to the data gathered by applying (A), extremely low production of the evaluated compounds was recorded in all cases.
The molecules identified through the process outlined above are described as antioxidants. These elements are commonly used in the pharmaceutical industry in sunscreens and in the food industry as food enhancers (Wang and Luo, 2007; Bayoumi et al. 2008; Marques and Farah, 2009). It seems that the increase in these compounds may be a metabolic defensive response that is meant to restore the equilibrium between antioxidants and reactive oxygen species due to the oxidative burst caused by exposure to UV-B radiation (Zhang and Björn, 2009; Zamora et al. 2010). Researchers have already established that chlorogenic acid shows a marked tendency to accumulate in plant tissues that are subjected to UV-B radiation (Demkura et al. 2010), shielding the underlying tissue from harmful UV radiation (Jaakola et al. 2004). Furthermore, it seems that there is a direct link between rutin accumulation and elicitation by UV-B radiation in some plant tissue cultures (Zhang and Björn, 2009), which is consistent with the results obtained in this study. Conversely, no accumulation of these compounds was obtained during (A), which supports the idea that this treatment causes important damage to the explants. To our knowledge, this is the first report describing the use of TIB for elicitation of this type of compound in a tissue culture of DA using UV-B radiation.
In conclusion, a successful automation of in vitro culturing for DA has been achieved using a specific TIB. This system allowed for the proliferation and induction of the generated biomass and synthesis of phenolic compounds under elicitation with UV-B. Note that every parameter defined in this article is merely a first approach to the culture and induction of this species under ex-situ conditions, which were established in order to explore technical opportunities for basic and applied experimentation. Although the immersion schedule (duration and frequency) and the general culturing conditions generated satisfactory results (handling of DA growth and secondary metabolism), they should be optimized in future studies. Certainly, DA culturing in TIB creates opportunities for producing enough biomass to conduct both basic and applied research. The use of this extremophile in the bio-production of interesting biotechnology compounds, such as chlorogenic acid, now seems plausible.
ARENCIBIA, A.; BERNAL, A.; YANG, L.; CORTEGAZA, L.; CARMONA, E.; PÉREZ, A.; HU, C.; LI, Y.; ZAYAS, C. and SANTANA, I. (2008). New role of phenylpropanoid compounds during sugarcane micropropagation in Temporary Immersion Bioreactors (TIBs). Plant Science, vol. 175, no. 4, p. 487-496. [CrossRef] [ Links ]
ASAMI, D.; HONG, Y.; BARRETT, D. and MITCHELL, A. (2003). Comparison of the total phenolic and ascorbic acid content of freeze-dried and air-dried marionberry, strawberry, and corn grown using conventional, organic, and sustainable agricultural practices. Journal of Agricultural and Food Chemistry, vol. 51, no. 5, p. 1237-1241. [CrossRef] [ Links ]
BAYOUMI, S.; ROWAN, M.; BLAGBROUGH, I. and BEECHING, J. (2008). Biosynthesis of scopoletin and scopolin in cassava roots during post-harvest physiological deterioration: The E-Z-isomerisation stage. Phytochemistry, vol. 69, no. 17, p. 2928-2936. [CrossRef] [ Links ]
DAY, T.; RUHLAND, C. and XIONG, F. (2001). Influence of solar ultraviolet-B radiation on Antarctic terrestrial plants: Results from a 4-year field study. Journal of Photochemistry and Photobiology B: Biology, vol. 62, no. 1-2, p. 78-87. [CrossRef] [ Links ]
DEMKURA, P.; ABDALA, G.; BALDWIN, I. and BALLARÉ, C. (2010). Jasmonate-dependent and -independent pathways mediate specific effects of solar ultraviolet B radiation on leaf phenolics and antiherbivore defense. Plant Physiology, vol. 152, no. 2, p. 1084-1095. [CrossRef] [ Links ]
ESCALONA, M.; LORENZO, J.; GONZÁLEZ, B.; DAQUINTA, M.; GONZÁLEZ, J.L.; DESJARDINS, Y. and BORROTO, C. (1999). Pineapple (Ananas comosus L. Merr) micropropagation in temporary immersion systems. Plant Cell Reports, vol. 18, no. 9, p. 743-748. [CrossRef] [ Links ]
GEORGE, A.; PEAT, H. and BUMA, A. (2002). Evaluation of DNA dosimetry to assess ozone-mediated variability of biologically harmful radiation in Antarctica. Photochemistry and Photobiology, vol. 76, no. 3, p. 274-280. [CrossRef] [ Links ]
GERM, M.; KREFT, I. and OSVALD, J. (2005). Influence of UV-B exclusion and selenium treatment on photochemical efficiency of photosystem II, yield and respiratory potential in pumpkins (Cucurbita pepo L.). Plant Physiology and Biochemistry, vol. 43, no. 5, p. 445-448. [CrossRef] [ Links ]
GRZEGORCZYK, I.; MATKOWSKI, A. and WYSOKINSKA, H. (2007). Antioxidant activity of extracts from in vitro cultures of Salvia officinalis L. Food Chemistry, vol. 104, no. 2, p. 536-541. [CrossRef] [ Links ]
JAAKOLA, L.; MÄÄTTÄ-RIIHINEN, K.; KÄRENLAMPI, S. and HOHTOLA, A. (2004). Activation of flavonoid biosynthesis by solar radiation in bilberry (Vaccinium myrtillus L.) leaves. Planta, vol. 218, no. 5, p. 721-728. [CrossRef] [ Links ]
KLIEBENSTEIN, D. (2004). Secondary metabolites and plant/environment interactions: A view through Arabidopsis thaliana tinged glasses. Plant, Cell & Environment, vol. 27, no. 6, p. 675-684. [CrossRef] [ Links ]
LIN, L.Z. and HARNLY, J. (2007). A screening method for the identification of glycosylated flavonoids and other phenolic compounds using a standard analytical approach for all plant materials. Journal of Agricultural and Food Chemistry, vol. 55, no. 4, p. 1084-1096. [CrossRef] [ Links ]
MCALISTER, B.; FINNIE, J.; WATT, M.P. and BLAKEWAY, F. (2005). Use of the temporary immersion bioreactor system (RITA®) for production of commercial Eucalyptus clones in Mondi Forests (SA). Plant Cell, Tissue and Organ Culture, vol. 81, no. 3, p. 347-358. [CrossRef] [ Links ]
QUIALA, E.; BARBÓN, R.; JIMÉNEZ, E.; DE FERIA, M.; CHÁVEZ, M.; CAPOTE, A. and PÉREZ, N. (2006). Biomass production of Cymbopogon citratus (D.C.) stapf., a medicinal plant, in temporary immersion systems. In Vitro Cellular & Developmental Biology - Plant, vol. 42, no. 3, p. 298-300. [CrossRef] [ Links ]
ROBINSON, S.; WASLEY, J. and TOBIN, A. (2003). Living on the edge-plants and global change in continental and maritime Antarctica. Global Change Biology, vol. 9, no. 12, p. 1681-1717. [CrossRef] [ Links ]
ROZEMA, J.; BJÖRN, L.O.; BORNMAN, J.F.; GABERCIK, A.; HÄDER, D.P.; TROT, T.; GERM, M.; KLISCH, M.; GRÖNIGER, A.; SINHA, R.P.; LEBERT, M.; HE, Y.; BUFFONI-HALL, R.; DE BAKKER, N.V.J.; VAN DE STAAIJ, J. and MEIJKAMP, B. (2002). The role of UV-B radiation in aquatic and terrestrial ecosystems-an experimental and functional analysis of the evolution of UV-absorbing compounds. Journal of Photochemistry and Photobiology B: Biology, vol. 66, no. 1, p. 2-12. [CrossRef] [ Links ]
RUHLAND, C.; XIONG, F.; CLARK, W. and DAY, T. (2005). The influence of ultraviolet-B radiation on growth, hydroxycinnamic acids and flavonoids of Deschampsia antarctica during springtime ozone depletion in Antarctica. Photochemistry and Photobiology, vol. 81, no. 5, p. 1086-1093. [CrossRef] [ Links ]
VAN DE STAAIJ, J.; DE BAKKER, N.V.; OOSTHOEK, A.; BROEKMAN, R.; VAN BEEM, A.; STROETENGA, M.; AERTS, R. and ROZEMA, J. (2002). Flavonoid concentrations in three grass species and a sedge grown in the field and under controlled environment conditions in response to enhanced UV-B radiation. Journal of Photochemistry and Photobiology B: Biology, vol. 66, no. 1, p. 21-29. [CrossRef] [ Links ]
VERVERIDIS, F.; TRANTAS, E.; DOUGLAS C.; GUENTER, V.; KRETZSCHMAR G. and PANOPOULOS, N. (2007). Biotechnology of flavonoids and other phenylpropanoid-derived natural products. Part II: Reconstruction of multienzyme pathways in plant and microbes. Biotechnology Journal, vol. 2, no. 10, p. 1235-1249. [CrossRef] [ Links ]
WANG, Z. and LUO, D. (2007). Antioxidant activities of different fractions of polysaccharide purified from Gynostemma pentaphyllum Makino. Carbohydrate Polymers, vol. 68, no. 1, p. 54-58. [CrossRef] [ Links ]
WEBBY, R. and MARKHAM, K. (1994). Isoswertiajaponin 2-O-β-arabinopyranoside and other flavone-C-glycosides from the Antarctic grass Deschampsia antarctica. Phytochemistry, vol. 36, no. 5, p. 1323-1326. [CrossRef] [ Links ]
YANG, Y.; YAO, Y.; XU, G. and LI, C. (2005). Growth and physiological responses to drought and elevated ultraviolet-B in two contrasting populations of Hippophae rhamnoides. Physiologia Plantarum, vol. 124, no. 4, p. 431-440. [CrossRef] [ Links ]
YANNARELLI, G.; GALLEGO, S. and TOMARO, M. (2006). Effect of UV-B radiation on the activity and isoforms of enzymes with peroxidase activity in sunflower cotyledons. Environmental and Experimental Botany, vol. 56, no. 2, p. 174-181. [CrossRef] [ Links ]
ZAMORA, P.; RASMUSSEN, S.; PARDO, A.; PRIETO, H. and ZUÑIGA, G. (2010). Antioxidant responses of in vitro shoots of Deschampsia antarctica to Polyethylene glycol treatment. Antarctic Science, vol. 22, p. 163-169. [CrossRef] [ Links ]
Note: Electronic Journal of Biotechnology is not responsible if on-line references cited on manuscripts are not available any more after the date of publication.