Journal of the Chilean Chemical Society
versión On-line ISSN 0717-9707
J. Chil. Chem. Soc. v.54 n.4 Concepción dic. 2009
J. Chil. Chem. Soc., 54, Nº 4 (2009), págs. 401-404.
INCREASE OF TOTAL GLUTATHIONE AS A RESPONSE TO CD INDUCED STRESS IN A CHILEAN ENDEMIC BRYOPHYTES (THUIDIUM SP.)
GENNY LEINENWEBER1*, SUSANA STEGEN1 AND PAULA DIAZ-PALMA1
1Departamento de Química, Facultad de Ciencias, Universidad Católica Del Norte, Avenida Angamos 0619* Antofagasta, Chile. e-mail: email@example.com
Bryophytes collected from the IV Region of Chile, were treated with CdCl2 to stimulate the synthesis of phytochelants. After cadmium treatment, total peptides were extracted from the plants and were analyzed using HPLC to search for the presence of phytochelatin molecules.
Chromatography results showed the absence of phytochelatin-like molecules in bryophytes. However, glutathione and a molecule suspected to be γ-glutamil-cistein were detected. The latter compound is knowed to be involved in the metabolic pathway of the gluthatione and phytochelatin synthesis.
The results indicated the absence of detectable phytochelatins in bryophytes containing heavy metal as contaminants. The increase in glutathione during the experimental period may have been due to a response to oxidative stress. Thus this work suggests an important role of the glutathione in the detoxifcation mechanisms of bryophytes.
Key words: Bryophytes, glutathione, chromatography, oxidative stress.
Contamination is currently one of the most studied phenomena. Elevated concentrations of heavy metals, of natural or anthropogenic origin, are one of the most diffcult contaminants to study 1. However there are organisms, like a large variety of plants, which are resistant to high levels of heavy metals
2,3. Research in these organisms resistant to heavy metals have found the presence of compounds synthesized at intra-cellular level, which are capable of immobilizing these elements. Because of their ability to store metals, these organisms have been considered as an alternative to be used as bio-monitors or biological extractors at contaminated sites 4, 5, 6, 7.
The phytochelatins and the glutathione compose a class of compounds generated by plants in response to heavy metals. These phylochelatins are a family of peptides that have been identifed in plants and some microorganisms. Phytochelatins have a primary structure of (γ-glutamil- cysteine)n glycine, with n=2-11 8, 9, 10. They are synthesized from glutathione, which is a tripeptide formed by glutamic acid, cysteine and glycine (γ-glutamil-cisteinil-glycine). Glutathione also plays an important role in the response of plants to environmental stress, oxidative stress and that produced by xenobiotic compounds such as heavy metals 4, 6, 11. Phytochelatins have been described in different types of organisms such as plants, nematodes, algae and yeasts 3,12. Some studies have demonstrated that bryophytes (mosses) do not form phylochelatins, but only their precursor glutathione 5, 11.
Considering that bryophytes have been described as organisms which are particularly reactive to contaminants and thus may have an important role as bio-indicators of environmental contamination 5, 13, 14, 15, 16, 17, this contribution examined the presence of phytochelants in endemic Chilean mosses challenged with a heavy metal, cadmium, by means of high-pressure liquid chromatography (HPLC).
Collection and maintenance of mosses
Mosses were collected from the area of Alcohuas in the IV Region of Chile (Figure 1), at the northern limit of mosses geographic distribution in Chile. The collection site is located on the eastern shore of the Alcohuas River, an affuent of the Elqui River, the main river in the area. A large amount of spray is generated at the site, which keeps it humid and permits the development of numerous trees and shrubs. The luminosity is restricted, which makes it appropiated for the growth of mosses of only one genus, Thuidium sp.
Mosses were collected in October, 2005. Approximately, 7 cm2 of plants and soil were extracted from 10 different points scattered in the site. Samples were stored in hermetically sealed bags to preserve the humidity during the return to Antofagasta.
Treatment of mosses with cadmium
To induce the formation of phytochelants in moss plants, these were watered once daily with 100 µmoles/L of Cd (II), for a period of 12 days. Previous studies with different species of mosses demonstrated that this concentration of Cadmium increased the GSH pool signifcantly 11, 12. Plants were sprayed, since mosses absorb water through the cuticle.
Three samples of moss plants of 300 mg, were taken at day 0 (before watering with Cd), 4, 7 and 12 of exposition to the Cd solution according to the experimental design suggest by Bruns and col. 11. Moss plants were cut and washed four times with supra-pure water (distilled and deionized), after removal of dry stems and soil. Plants were allowed to dry on paper towels at room temperature.
Extraction of non-proteic thioles
Non-proteic thioles were extracted using the protocol of Sneller and col. 18, homogenizing 40 mg of dry plant material in 2 ml of a cold solution of DTPA (Fluka) 6.3 mM and 0.1% (v/v) TFA (Fluka). Mosses were ground in a porcelain mortar free of metals. The homogenized slurry was centrifuged at 10,000 g. The supernatant was fltered with a 0.22 µm nylon flter. Samples were stored refrigerated until use.
Derivatization of sample with monobromobiane
The buffer solution was 450 µl of 200 mM HEPPS pH 8.2 containing DTPA 6.3 mM. DPTA was added to minimized GSH oxidation, reducing the potencial ability of Cd (II) to catalyze this reaction 19. Then 10 µl of a solution of 25 mM monobromobimane dissolved in acetonitrile was added. To this mixture 250 µl of sample was added, mixed and stored in the dark for 30 min at 45º C. The reaction was stopped by adding 300 µl of a 1M solution of metasulfonic acid (MSA) (Fluka). Samples were stored at 4ºC until analysis by HPLC. Samples were derivatized and detected with a fuorescence detector 19.
A Kromasil Analytic Column of 60 Å, 4.6 mm diameter and 25 mm length was used. Before injection, the column was equilibrated with methanol (Merck) and HPLC grade water (Merck) at 12% (v/v) and 88% (v/v), respectively, both containing 0.1% trifuoracetic acid (TFA, Merck) at a fow of 0.5 ml/min. All solutions used were previously fltered with a GV membrane flter (Durapore) EM PDVF, 0.22 µm pore size, 47 mm diameter.
A volume of derivatized sample was injected and the column was run in a slightly concave gradient of 12-25% (v/v) of methanol for 15 min, followed by a linear gradient of 25-35% (v/v) of methanol from 15 to 29 min. Finally, a linear gradient of 35-50% (v/v) of methanol was applied from 29 to 50 min. The wavelength used for excitation was 380 nm and the emission wavelength was monitored at 470 nm 18.
The compound N-acetyl-L-cysteine (Merck) was used to verify the derivatization process. Glutathione (Merck), a tripeptide composed of glutamic acid, cysteine and glycine was used as a standard for retention times.
Determination of Cd in mosses
Mosses without Cd and samples watered with Cd for 4, 7 and 12 days were washed with abundant deionized water (18MΩ) and dried at room temperature on absorbent towels. About 0,300 g (± 0,100 mg) of powdered and homogenized sample was treated with 5 ml of concentrated HNO3 (65% suprapure), 4 ml of H2O s.p. (18MΩ) and 1 ml of H2O2 (35%). To avoid cross-contamination, digestion vessels were previously cleaned in a bath of 10% (v/v) nitric solution for 48 h.
Solutions were analyzed by fame atomic absorption spectrometry (AAS) (Perkin Elmer Model AANALYST 700) using an EDL lamp (discharge lamp without electrode). The detection limit (LOD= 0.010 µg/ml) was calculated as the concentration corresponding to signals equal to three-times the standard deviation of 10 replicates of a blank solution. The standards of Cd used were of 0.5, 1 and 2 µg/ml. A preparation with 1.5 µg/ml was used to test the calibration curve (quality control of the method). The accuracy (bias) and precision (%RSD) of the methods were tested with certifed reference materials: Spinach NBS 1570 (2,84±0,07 mg/kg) and Sea Lettuce BCR 279 (0,274±0,035 mg/kg). The results obtained for Cd (2,93±0,12 and 0,263±0,12 mg/kg respectively) are in excellent agreement with the certifed values, supported by the traceability test of t Student. One sample of reference materials and blanks were included in each analytical batch and three parallel measurements were made in all cases.
The analytical precision and accuracy determined by quality assurance and quality control procedures using certifed reference materials, a duplicate, blanks and internal standards, was better than ±10%.
RESULTS AND DISCUSSION
The mosses watered with Cd showed a color change from light green (fgure 2A) to yellowish-brown (Figure 2B). This phenomenon is so well documented like response to different causes: the phenolic compounds oxidation21; the alteration of chlorophyll; and the inhibition of chlorophyll synthesis 2, 23, 24. An important effect on chlorophyll is the substitution of the Mg (II) by Cd (II) in its structure, which transforms the molecula into a feophytine, and the organism acquires a characteristic yellow-brown color 22.
All biochemical events mentioned above should be associated to a response of plants to the environmental stress provoked by Cd 22.
The chromatogram of the derivatization test showed the peaks corresponding to N-acetyl-L-cysteine at 37.21 min. join to the peaks of the derivatizing agent monobromobimane at 28.96 and 38.43 min (Figure 3A). These results demonstrated that the SH(s) groups of N-acetyl-L-cysteine reacted with the monobromobimane, which validates its use with the moss samples since this compound unites with the SH(s) peptide residues extracted from them. Figure 3B shows the chromatogram with the glutathione standard, which showed a peak at 30.5 min.
Figure 4 B, C and D shows the chromatograms of the samples of mosses treated with Cd. The spectrum of the moss without Cd (Figure 4A) showed the peaks of monobromobimane, as well as a very small peak at 30.50 min, the retention time of glutathione. The presence of this peak indicated that glutathione is a constitutive compound of the mosses analyzed. This means that it is always produced by the plant even in the absence of Cd, since it has different functions in the cell; as an antioxidant compound, maintining the intracellular redox state and detoxifying xenobiotics and heavy metals by chelation 25.
The chromatograms of mosses exposed to Cd for 4 to 12 days showed the same peaks corresponding to the retention time of glutathione (Figure 4 B, C and D). The progressive increase in the area under the curve of these peaks indicates that these plants increased their total cadmium content with more time of exposure to Cd (Table 1). Also, the peaks of the derivatizing agent were detected in these three chromatograms (Figure 4 B to D). As show in the Table 2, the GSH content increased under Cd (II) stress.
This result suggests that there was a stimulation of the synthesis of glutathione as a chelating agent of Cd, which would trigger an antioxidant response to the stress provoked by the presence of this heavy metal in the tissues of the mosses. Glutathione has been described as a transitory chelating agent in bryophytes, since this compound is capable of transporting Cd to the vacuole of the cells, where it is stored and immobilized as Cd3(PO4)2 5, 11.
The appearance of a peak with a retention time of 31 minutes in the chromatogram of the samples with 7 days of Cd exposure (Figure 4 C), after the peak of GSH at 30 minutes, suggests the presence of another thiolic compound, which might be a precursor of GSH, for example γ-EC (γ-glutamil cisteine). This compound has been described as a precursor of glutathione. Sneller and col.18 and Rijstenbil and col.19 reported the presence of a peak next to that of glutathione, which was identifed as γ-glutamil cisteine using a standard of this compound.
Determination of Cd in bryophytes.
The concentration of Cd, measured in dry plant material, increased from 13.6 µg/gr (d.w) at day 0 of the experiment to 35.6 µg/gr (d.w.) at day 4 and 40.3 µg/gr (d.w) at day 7. However, at day 12 the Cd concentration decreased to 31.3 µg/gr (d.w.).
On other hand, since cadmium is not an essential element for plants 26, the increase of Cd (II) during the course of the experiment (Table 3) must be associated with the bio-accumulation of this element. This agrees with other reports in the literature 5, 11, 12, 13, 15, 16, 27 which have documented the capacity of mosses to sequester heavy metals when they are in high concentration in the environment. The decrease of Cd (II) concentration observed on day 12 of the experiment is counter to the expected bio-accumulation, which suggests a possible effect of loss of effciency or saturation of the enzymatic bio-accumulation machinery 28. As with any enzyme kinetics, the bio-accumulation of heavy metals has a saturation point 28.
These results suggest a good correlation between accumulation of glutathione and the Cd content in plants; which could indicate the chelation process was carried out by this peptide.
The results obtained here indicate the absence of the phytochelatin type of chelating agents in bryophytes submitted to Cd (II) stress. This agrees with other reports which have studied bryophytes in similar experimental conditions 5, 11. Preliminary results from our laboratory using PCR analysis indicated that the phytochelatin synthase gene, should be absent in plants of Thuidium sp. (unpublished data). Therefore, not expression of the phytochelatin synthesis should be expected in this kind of plants.
Based upon the results obtained here, the oligopeptide glutathione appears to have a fundamental role in the bio-accumulation of cadmium in bryophytes. This seems to be the most relevant mechanism in the response of these plants to the stress caused by cadmium.
The exposure of mosses to cadmium for a period of 12 days induced the synthesis of glutathione, which showed a steady increase during the experimental period. Also, we observed the appearance of an unidentifed compound that presumably corresponded to γ-EC.
We did not detect the appearance of phytocheatins in response to stress by cadmium. This result corroborates previous studies in indicating that in case of bryophytes, only glutathione and their precursors, cysteine and γ-EC, are involved in the process of chelation of heavy metals.
The analysis conducted by Atomic Absorption, shows the availability of these plants to bioacumulate cadmium. We detect a saturation point in this process through the cessation of Cd accumulation towards the end of the experimental period.
Through the confrmation of the ability of some endemic mosses (Thuidium sp.), to bioacumulate heavy metals through a chelation process, this work contributes to the realization of the use of bryophytes as biomonitors in environmental contamination.
The authors are grateful to Dr. Victor Kesternich, for his critical reading of the manuscript. Other acknowledgments, to Dr. Javier Palacios for his technical support in this work.
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(Received: March, 10, 2009 - Accepted: September 28, 2009).