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Revista Brasileira de Farmacognosia

Print version ISSN 0102-695X

Rev. bras. farmacogn. vol.21 no.2 Curitiba Mar./Apr. 2011  Epub Apr 15, 2011

http://dx.doi.org/10.1590/S0102-695X2011005000060 

Effects of heavy metals and light levels on the biosynthesis of carotenoids and fatty acids in the macroalgae Gracilaria tenuistipitata (var. liui Zhang & Xia)

 

 

Ernani PintoI,II; Ana Paula CarvalhoII; Karina Helena Morais CardozoIII; Francisco Xavier MalcataII; Fabyana Maria dos AnjosI; Pio ColepicoloIV

IDepartamento de Análises Clínicas e Toxicológicas, Faculdade de Ciências Farmacêuticas, Universidade de São Paulo, Brazil
IIEscola Superior de Biotecnologia, Universidade Católica Portuguesa, Portugal
IIIFleury Group, Brazil
IVDepartamento de Bioquímica, Instituto de Química, Universidade de São Paulo, Brazil

Correspondence

 

 


ABSTRACT

We present here the effect of heavy metals and of different light intensities on the biosynthesis of fatty acids and pigments in the macroalga Gracilaria tenuistipitata (var. liui Zhang & Xia). In order to verify the fatty acid content, gas chromatography with flame ionization detection (GC-FID) was employed. Pigments (major carotenoids and chlorophyl-a) were monitored by liquid chromatography with diode array detection (HPLC-DAD). Cultures of G. tenuistipitata were exposed to cadmium (Cd2+, 200 ppb) and copper (Cu2+, 200 ppb), as well as to different light conditions (low light: 100 µmol.photons.m-2.s-1, or high light: 1000 µmol.photons.m-2.s-1). Cd2+ and Cu2+ increased the saturated and monounsaturated fatty acid content [14:0, 16:0, 18:0, 18:1 (n-7) and 18:1 (n-9)] and all major pigments (violaxanthin, antheraxanthin, lutein, zeaxanthin, chlorophyll-a and β-carotene). Both heavy metals decreased the levels of polyunsaturated fatty acids (PUFA) [18:2 (n-6), 18:3 (n-6), 18:5 (n-4), 20:4 (n-6), 20:5 (n-3), 22:6 (n-3)]. G. tenuistipitata cultures were exposed to high light intensity for five days and no statistically significant differences were observed in the content of fatty acids. On the other hand, the levels of pigments rose markedly for chlorophyll-a and all of the carotenoids studied.

Keywords: Gracilaria tenuistipitata, carotenoids, xanthophylls, heavy metals, fatty acids, light intensity


 

 

Introduction

Diverse environmental conditions can clearly interfere with the biosynthesis of natural products from algae (Pinto et al., 2003a). Variations in the light intensity, temperature, pH, UV radiation, content of macro- and micronutrients, sea tides and presence of pollutants have been described as natural and anthropogenic disturbances that can influence the physiology, composition and quantity of some marine macroalgal metabolites (Franklin & Forster, 1997; Hader & Figueroa, 1997; Hader et al., 1998; Pinto et al., 2003b; Cardozo et al., 2007; Gressler et al., 2011).

Fatty acids and carotenoids play an important role in the function and integrity of the chloroplast thylakoid membrane of photosynthetic organisms (Frank & Cogdell, 1996; Havaux, 1998; Sigaud-Kutner et al., 2002; Su et al., 2010). In fact, algal fatty acids (saturated, monounsaturated and polyunsaturated - PUFA) and carotenoids (carotenes and xanthophylls) vary their quality and quantity according to the environmental conditions (Barros et al., 2005; Britton, 1995; Cardozo et al., 2002; Collen et al., 2003; Colombo et al., 2006). The genera belonging to the Rhodophyta phylum are generally rich in PUFA (Khotimchenko et al., 2002; Li et al., 2002; Wahbeh, 1997). Rhodophyta species found in low temperature waters are usually richer in PUFA, with a higher n-3/n-6 fatty acid ratio, and possess a higher degree of total unsaturation. It has been reported that the genus Gracilaria contains mainly C 20:4 (n-6) and C 20:5 (n-3) and other saturated and monounsaturated fatty acids (Gressler et al., 2010). Heavy metals can be accumulated by some species of macroalgae and interfere with photosynthesis (Baumann et al., 2009; Gledhill et al., 1997). It was also reported that copper (Cu) and cadmium (Cd) induce oxidative stress in G. tenuistipitata (Collen et al., 2003).

Macroalgae biosynthesize a variety of pigments, including several carotenoids that are usually found in terrestrial plants (i.e., violaxanthin, antheraxanthin, zeaxanthin, lutein and β-carotene) as well as chlorophyll-a (Cardozo et al., 2007). Under culture conditions, light and heavy metals have been shown to induce the biosynthesis of carotenoids in G. tenuistipitata. Carnicas et al. (1999) described an oscillation of pigments in G. tenuistipitata when cultures were grown under two different irradiance levels. After addition of Cu2+ and Cd2+, the content of β-carotene and lutein of this species increased during growth (Collen et al., 2003).

The purpose of the present investigation was to simulate two different environmental situations with cultures of G. tenuistipitata and to monitor the biosynthesis of fatty acids and pigments. The first experiment was carried out to mimic an area polluted with heavy metals (low amounts of Cd2+ and Cu2+ were added to the cultures). The second assay was designed to reproduce a natural condition of variable light intensity (cultures were grown under 100 or 1000 µmol.photons.m-2.s-1). Our findings indicate that both conditions interfere with the biosynthesis of fatty acids and pigments, maintaining G. tenuistipitata homeostasis and coping with oxidative stress.

 

Materials and Methods

Chemicals and reagents

The pigments violaxanthin, antheraxanthin and zeaxanthin were obtained from DHI, Water & Environment©, and lutein, β-carotene and chlorophyll-a from Sigma-Aldrich®. The fatty acid mixture was purchased from Sigma-Aldrich®. Merck (Darmstadt, Germany) supplied HPLC grade methanol and ethyl acetate. All other chemicals were of analytical grade.

Cultures

The marine red macroalga G. tenuistipitata Chang (var. liui Zhang & Xia) was grown at an irradiance of 100 µmol.photons.m-2.s-1 at 20 °C in seawater diluted to 20 ppt with distilled water, bubbled with air, with a light:dark (12 h:12 h) regime before the start of the experiments. The algae were fertilized according to Haglund et al. (1996), a modification of Provasoli et al. (1957), and fertilized the day before the experiment; no nutrients were added during the experiment. The seawater was changed at the start of the experiment. Heavy metals were added as solutions of CdCl2 (Cd2+, 200 ppb) and CuSO4.5H2O (Cu2+, 200 ppb). During the experiments, the conditions were identical except for the light level; two irradiances were used, 100 (control, low light intensity, L-) and 1000 µmol.photons.m-2.s-1 (high light intensity, L+). The initial density of algae in the experiments was 1 g fresh weight (FW) per L. For the control and heavy metals experiments, harvesting was done 6 h after the start of the light period. For the high-light experiments, harvesting was performed 6 and 18 h after the start of the light period (for both control L- and L+). Samples were frozen in liquid nitrogen and kept at -70 °C until analyzed.

Pigment analyses

Chlorophyll-a (Chl-a), β-carotene, violaxanthin, antheraxanthin, lutein and zeaxanthin were extracted following the procedure described by Carnicas et al. (1999) with a few modifications. Briefly, 2 mL of dimethylformamide were added to 200 mg dried algae (lyophilized). After incubation in an ultrasonic bath (10 min), 1 mL of methanol/ethylacetate (MeOH/EtOAc, 1:1) was added and the samples were filtered through 0.22 µm Millipore® membranes. Aliquots of the extracts (100 µL) were injected onto the HPLC. The analysis was performed on a Shimadzu HPLC system consisting of two LC-10AD pumps fitted with an auto-injector (SIL-10ADVP), a photodiode array detector (SPD-M10AVP) set at 445 nm, and a system-controller (SCL-10AVP). Data were stored in Class-VP 5.032 software. A Luna RP-18 column (250 mm x 4.6 mm, particle size 5 µm, Phenomenex®), with a pre-column guard (particle size 5 µm, RP-18 Phenomenex®) was used for pigment separation. The flow rate was 1.0 mL.min-1 and MeOH and EtOAc were HPLC grade (Merck®). The gradient was achieved with 70% MeOH and EtOAc; for the first 6 min, the gradient was 25-27% EtOAc followed by 4 min at 27% EtOAC and then increased to 75% EtOAc over 5 min and maintained constant at 75% EtOAc for 12 min. Pigments were identified by comparing retention times and absorption spectra with authentic standards.

Fatty acid analyses

Fatty acid methyl esters (FAME) were obtained by direct transesterification of lyophilized samples of G. tenuistipitata, as described by Carvalho & Malcata (2005a, b). Acetyl chloride was used as the derivatization agent and heptadecanoic acid as internal standard. FAMEs were analyzed with a gas chromatograph (Hewlett Packard 5890), equipped with a flame ionization detector and a polar, 60-m fused silica Supelcowax10 (Supelco®) capillary column. The oven temperature was programmed to increase from 170 to 220 °C at a rate of 1 oC/min; the injector and detector temperatures were 250 and 270 °C, respectively; helium was used as the carrier gas. Pure standards of the free fatty acids (Sigma®) were used for fatty acid identification, which was based on comparison of the peak retention times of the samples and standards under similar elution conditions. Peak areas were quantified by automatic integration (Hewlett Packard 3395) and calculations were performed according to the AOCS Official Method Ce lb-89 (Firestone, 1994). Fatty acids were named using the code i:j (n-k), where i indicates the total number of carbon atoms, j the number of double bonds, and k the position of the last double bond counted from the terminal methyl group.

Statistical analyses

Data were expressed as average values±SD (standard deviation). The results were tested for significance at the 0.05 level by comparing the average value obtained for the control (three replicates) with those of the experiments performed with varying light intensity (three replicates) or in the presence of heavy metals (three replicates) employing one-way analysis of variance and the Student-Newman-Keuls multiple comparison test.

 

Results and Discussion

The major fatty acids found in G. tenuistipitata [14:0, 16:0, 18:0, 18:1 (n-7), 18:1 (n-9), 18:2 (n-6), 18:3 (n-6), 18:5 (n-4), 20:4 (n-6), 20:5 (n-3), 22:6 (n-3)] were similar to those already reported for other Gracilaria and red algae species (Colombo et al., 2006; Gressler et al., 2010; Khotimchenko et al., 2002; Li et al., 2002; Moore, 2006; Wahbeh, 1997). When cultures were exposed to Cu2+ and Cd2+, the amount of saturated and monounsaturated fatty acids [14:0, 16:0, 18:0, 18:1 (n-7), 18:1 (n-9)] increased (Figure 1A). In contrast, the levels of PUFA [18:2 (n-6), 18:3 (n-6), 18:5 (n-4), 20:4 (n-6), 20:5 (n-3), 22:6 (n-3)] diminished, the decrease being more significant for the treatment with Cd2+ (Figure 1B). No significant variation of the fatty acids was found when cultures were submitted to high light intensity (data not shown).

Heavy metals can change the lipid and fatty acid composition of algae (Rocchetta et al., 2006; Vavilin et al., 1998). The mechanisms involve mostly oxidative stress and the production of reactive oxygen/nitrogen species that lead to oxidation of lipids (Pinto et al., 2003b). As expected and supported by other experiments with cultures of algae (Collen et al., 2003; Okamoto et al., 2001; Rocchetta et al., 2006), PUFA are the fatty acids most affected and their levels are reduced in the presence of heavy metals. In our experiments, Cd2+ proved to be more toxic than Cu2+ and significantly decreased the concentration of PUFA.

The evolution and physiological aspects of thylakoid membranes in plants and algae are not completely elucidated. The profile of fatty acids and carotenoids may change according to the species and the environmental conditions (Benning, 2008; Triantaphylides & Havaux, 2009). Carotenoids play an important role in membrane stability, as well as being natural antioxidants (Britton, 1995; Havaux, 1998; Havaux & Niyogi, 1999; Guaratini et al., 2005). As shown in Figure 2, the quantities of all carotenoids and of chlorophyll-a markedly increased in the presence of Cu2+ and Cd2+. However, no difference was observed between Cu2+ and Cd2+ treatments.

 

 

Xanthophylls have a particular function in photosynthetic organisms. Terrestrial plants and most all macroalgae possess the so-called xanthophyll cycle. Under certain stressful conditions, including high light incidence, plants can dissipate the excess energy in photosynthesis via a cyclic reaction involving two successive de-epoxidations of violaxanthin to zeaxanthin, with antheraxanthin as an intermediate (DemmigAdams & Adams, 1996; Eskling et al., 1997; Havaux & Niyogi, 1999). As mentioned above, low and high light irradiances (L- and L+: 100 and 1000 µmol.photons.m-2.s-1, respectively) had no effect on the biosynthesis of fatty acids in G. tenuistipitata. Nevertheless, the quantity of carotenoids related to the xanthophyll cycle showed a singular pattern, with zeaxanthin, anteroxanthin and violaxanthin increasing significantly under L+ (Figures 3). Our results corroborate the findings of Carnicas et al. (1999), indicating that the xanthophyll cycle may play an important role under conditions of high light exposure.

 

 

The other pigments had comparable profiles; the content of lutein, chlorophyll-a and β-carotene increased under L+ (Figure 4). These results are related to previous experiments performed by our group (Collen et al., 2003), where the concentrations of lutein and β-carotene in cultures of G. tenuistipitata were found to increase under an irradiation intensity of 250 µmol.photons.m-2.s-1. In addition, in the control (L-), no difference was noted when samples were collected after 6 or 18 h (middle of the day phase at 12 h or middle of the dark phase at 24 h, respectively). On the contrary, when compared to the control, L+ experiments presented higher amounts of pigments at both 12 h or 24 h harvest times (Figures 3 and 4).

 

 

Conclusions

Our results point out that heavy metals and different light conditions modify the biosynthesis of fatty acids and pigments, showing that cultures of G. tenuistipitata can modify its physiology under some environmental stressful conditions.

 

Acknowledgements

This work was supported by the Brazilian research funding agencies Conselho Nacional de Desenvolvimento Científico e Tecnológico, Fundação de Amparo a Pesquisa do Estado de São Paulo and Coordenação de Aperfeiçoamento de Pessoal de Nível Superior, Ministério da Saúde, Ministério de Ciência e Tecnologia and CNPq-INCT-Redoxoma.

 

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Correspondence
Ernani Pinto
Departamento de Análises Clínicas e Toxicológicas
Faculdade de Ciências Farmacêuticas, Universidade de São Paulo
Av. Prof. Lineu Prestes 580, Bloco 13B
05508000, São Paulo-SP, Brazil
ernani@usp.br
Tel. +55 11 3091 1505

Received 22 Dec 2010
Accepted 17 Jan 2011

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