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Seasonal variation of the major secondary metabolites present in the extract of Eremanthus mattogrossensis Less (Asteraceae: Vernonieae) leaves

Abstract

The species Eremanthus mattogrossensis, known as "veludo do cerrado" (cerrado velvet), is native to the Brazilian Cerrado. Because the amount of metabolites present in plants may be influenced by biological and environmental factors, here we conducted an HPLC-DAD-MS/MS investigation of the metabolite concentrations found in the MeOH/H2O extract of the leaves of this species. The main compounds were identified and quantified, and the metabolites were grouped by chemical class (caffeoylquinic acids, flavonoids, and sesquiterpene lactone). Statistical analysis indicated a straight correlation between the quantity of metabolites and seasonality, suggesting that environmental properties elicit important metabolic responses.

Eremanthus mattogrossensis; HPLC-DAD-MS/MS methodology; seasonal variation


ARTIGO

Seasonal variation of the major secondary metabolites present in the extract of Eremanthus mattogrossensis Less (Asteraceae: Vernonieae) leaves# # Artigo em homenagem ao Prof. Otto R. Gottlieb (31/8/1920-19/6/2011)

Dayana Rubio GouveaI; Leonardo Gobbo-NetoI; Humberto T. SakamotoI; Norberto Peporine LopesI; João Luís Callegari LopesI,* * e-mail: joaoluis@usp.br ; Fernando MeloniII; Juliano Geraldo AmaralIII

IDepartamento de Física e Química, Faculdade de Ciências Farmacêuticas de Ribeirão Preto, Universidade de São Paulo, Av. do Café, s/n, 14040-903 Ribeirão Preto - SP, Brasil

IIDepartamento de Biologia, Faculdade de Ciências e Letras de Ribeirão Preto, Universidade de São Paulo, Av. Bandeirantes, 3900, 14040-901 Ribeirão Preto - SP, Brasil

IIIInstituto Multidisciplinar em Saúde, Universidade Federal da Bahia, Rua Rio de Contas, 58, Quadra 17, Lote 58, 45029-094 Vitória da Conquista - BA, Brasil

ABSTRACT

The species Eremanthus mattogrossensis, known as "veludo do cerrado" (cerrado velvet), is native to the Brazilian Cerrado. Because the amount of metabolites present in plants may be influenced by biological and environmental factors, here we conducted an HPLC-DAD-MS/MS investigation of the metabolite concentrations found in the MeOH/H2O extract of the leaves of this species. The main compounds were identified and quantified, and the metabolites were grouped by chemical class (caffeoylquinic acids, flavonoids, and sesquiterpene lactone). Statistical analysis indicated a straight correlation between the quantity of metabolites and seasonality, suggesting that environmental properties elicit important metabolic responses.

Keywords:Eremanthus mattogrossensis; HPLC-DAD-MS/MS methodology; seasonal variation.

INTRODUCTION

Despite the existence of genetic control, gene expression, and genotypes, the total content and relative proportions of secondary metabolites in plants may vary over time and space (seasonal and daily variation as well as intraplant, interplant, and interspecies distinctions), so that they occur at different levels.1-3 The amount of metabolites present in a given plant may be influenced by biological and environmental factors4 as well as biochemical, physiological, ecological, and evolutionary processes.3,5 Seasonality, circadian rhythm, plant development, phenology, temperature, altitude, water availability, UV radiation, nutrients, pollution, mechanical stimuli, and attacks by herbivores or pathogens are considered to be the factors that most affect the occurrence of plant metabolites.4,6

Most of the studies about the factors influencing secondary metabolite concentration are restricted to a few commercially important species native mainly to temperate regions. These species have long been manipulated by men, and the cultivated specimens have stood selective pressure due to choice of samples with the characteristics desired by humans. Because these plants may have lost their original behavior, their wild behavior cannot be inferred from the currently cultivated specimens.1,7

Specific in situ and in locus studies are mandatory for better understanding of the chemical behavior and more thorough appreciation of the variation in metabolite concentrations of wild plants in tropical ecosystems. This information is necessary for both evolutionary and chemotaxonomic studies and shall assist expansion of the current knowledge about the ecological interactions taking place between a certain plant and its surroundings.8

Cerrado is the second largest Brazilian biome. It stands out due to its wide variety of animals and plant species, which in turn is associated with a large array of environments. The 22 species of the genus Eremanthus Less (Asteraceae: Vernonieae) are restricted to this biome. The species Eremanthus mattogrossensis Less. is widely distributed in the western area of the Central Brazilian Plateau and exists at elevations ranging from 500 to 1,000 m in the Cerrado. This plant is particularly common in Mato Grosso and is popularly known as "veludo do cerrado" (cerrado velvet) and "casca freta" (cleft bark). Phytochemical analysis of the genus Eremanthus has revealed the presence of flavonoids, polyacetylenes, triterpenes, and sesquiterpenes, and sesquiterpene lactones have been very often reported as secondary metabolites in this plant.9 In this work, we aimed to identify and quantify the major compounds found in E. mattogrossensis and to evaluate the seasonal variation in their concentrations.

EXPERIMENTAL

General experimental procedures

Chemicals

HPLC grade methanol (MeOH), acetonitrile (MeCN), and acetic acid were obtained from J.T. Baker. De-ionized water 18 mW (Milli-Q, Millipore) was employed in all the experiments.

Equipment

HPLC analysis was conducted on a Shimadzu HPLC-DAD, LC-6AD pump coupled to a Diode Array Detector (SPD-M10Avp, Shimadzu), and to an auto injector (SIL-10AF, Shimadzu), all controlled by the software CLASS-VP 6.14. A LC-RP-18 column (5 mm, 4.6/250 mm; Sigma-Aldrich) connected with a guard-column (4.6/10.0 mm) composed of equivalent material was utilized.

Plant material

E. mattogrossensis branches were collected in the municipality of Delfinópolis, state of Minas Gerais, Brazil (S 20º20'55.0', W 046º47'63.8''; 864 m altitude) and identified by Prof. Dr. J. Semir of the Botany Department of the Biology Institute of the University of Campinas (UNICAMP), state of São Paulo, Brazil. A voucher specimen was deposited under the code NPL 288 in the Herbarium of this same institution.

As soon as possible, the plant material was dried under forced ventilation at 40 ºC, for 48 h, and stored in a dry place, away from light and insect attack.

Ten specimens were collected from the same population on the same day and at the same time. Three specimens were collected on different days, at one-month intervals, for 21 months (Jun/2000-Feb/2002), at 12:00 pm (± 30 min), for the seasonal studies.

Sample preparation for chromatographic analysis

The leaves of each E. mattogrossensis branch were ground in an analytical mill. The powdered leaves (30 mg) were weighed in a glass vial, to which 3 mL of a MeOH/H2O (9:1) solution containing the internal standard coumarin (30 µg mL-1) were added. This mixture was subjected to extraction in ultrasonic bath for 10 min. The resulting extract (500 mL) was transferred to a centrifuge tube (1.5 mL), to which 500 mL hexane were added. The tube was vortex-stirred and centrifuged at 1200 g for 10 min. A 300 mL aliquot was removed from the hydro-alcoholic phase and filtered on a 0.45-mm cellulose acetate membrane. The filtrate (20 mL) was submitted to HPLC analysis.

Analytical HPLC method

The following mobile phase gradient was employed for HPLC-DAD analysis, at a flow rate of 1.6 mL min-1: solvent A = aqueous acetic acid, 2% (v/v); solvent B = MeCN, 98%-acetic acid, 2% (v/v); elution profile = 0-35 min, 10-18% B (linear gradient), 35-40 min, 18-23% B (linear gradient), 40-50 min, 23-28% B (linear gradient), 50-60 min, 28-40% B (linear gradient), 60-65 min, 40-100% B (linear gradient), 65-70 min (column washing), 100% B (isocratic), 70-75 min, 100-10% B (linear gradient), 75-80 min (column equilibration), 10% B (isocratic); the UV-DAD detector was set to record spectra between 210 and 600 nm, and UV chromatograms were recorded at 270 and 325 nm.

HPLC-DAD-MS and -MS/MS analyses

HPLC-DAD-MS and -MS/MS analyses were performed by using the same column and elution gradient described for the analytical HPLC method. The parameters and apparatus used in the mass spectrometry analysis were the same as those described in a previous study published by our research group.10

Method validation

The analytical methodology was validated in accordance with current Brazilian and international legislations,11 using the same parameters employed for the previously described methodology,10 except for the fact that at least one substance of each class of secondary metabolite identified in the E. mattogrossensis leaf extracts was utilized. On the basis of availability, 4 compounds were chosen for construction of the analytical curves and method validation, namely di-C-glucosylflavone vicenin-2 (6,8-di-C-β-glucopyranosylapigenin), chlorogenic acid (5-O-E-caffeoylquinic acid), 3,4-di-O-E-caffeoylquinic acid, and the sesquiterpene lactone goyazensolide. Peak areas were calculated at 325 nm for flavonoids and caffeoylquinic acids, and at 270 nm for the sesquiterpene lactone goyazensolide.

The internal standard (I.S.) method was utilized for construction of analytical curves for the standards of these compounds at concentrations of 0.2, 0.5, 1.0, 2.0, 5.0, 10.0, 20.0, 50.0, 100.0, 200.0, 500.0, and 1000.0 µg mL-1, in triplicate. The overall recovery level of the method was determined by spiking 50.0, 100.0, and 150.0 µg of each standard substance into a matrix consisting of dried and powdered E. mattogrossensis leaves (30.0 mg) that had been previously exhaustively extracted (5 times) by the same extraction method described above and then dried.

Statistical analysis

Exploratory multivariate techniques were employed for assessment of the seasonality effect on the quantified metabolites. The climate variables maximum temperature, minimum temperature, and rainfall were selected for identification of the natural seasonal groups. Cluster analysis performed by the hierarchical method adopting Euclidian distance as similarity measure and Ward method for linkage groups was utilized. In the next step, the non-hierarchical method K-means was used for detection of variables within the groups. The groups identified by the hierarchical method and K-means were tested by Hotelling's T2 test,12 to confirm the differences between groups.

To evaluate the variation of metabolite concentrations, the metabolites were grouped by chemical class (caffeoylquinic acids, flavonoids, and sesquiterpene lactone), and the metabolites concentration values were added up according to the respective chemical class. The values resulting from each metabolite class were categorized into 4 concentration levels (a, b, c, d), which contained a similar number of samples (each category had around 25% of the total number of samples). The samples were grouped according to the month/season, in accordance to the cluster analysis data. Multivariate correspondence analysis (CA) was applied for better understanding of the effect of seasonal variation on the amount of each class of chemical compound. The relationship amount variation/chemical classes/seasons was examined by correlation with the dimensional axis calculated by CA.13 The software Statistica 7.0 was employed for all the data analysis.

RESULTS AND DISCUSSION

Chromatographic peak identification

The chromatographic signals identification was conducted as previously published by our research group.10 To this end, the chemosystematics information about the genus was compared to the UV spectra and the data generated by mass spectrometry. Peak identity was confirmed by co-injection of standard compounds previously isolated by our group, when possible. In the case of chlorogenic acid derivatives, they have characteristic fragmentation profiles in ESI previously described in the literature.14 In this case, only the data from MS/MS, accurate mass, UV spectrum and elution order in reverse phase chromatography allow the correct identification of compounds.

The accurate mass obtained for all peaks were in agreement with the exact masses calculated for the deprotonated molecule relative to each compound (Table 1). Only the identified signals are described below. Figure 1 illustrates an example chromatogram and the peaks numbering, including the non-identified flavonoids (flavonoids NI: peaks 3, 5, 8 e 10). It is important to note that for this species have been reported two sesquiterpene lactones15 and only one was identified at the present work (Figure 2).



3-O-E-caffeoylquinic acid

The first isomer identified by mass spectrometry in the negative ionization mode was the ion m/z 353, which was attributed to the deprotonated molecule characteristic of mono-caffeoylquinic isomers. Fragmentation of this ion generated the ion m/z 191 as the base peak and the ion m/z 179 as the secondary ion in the MS2 spectra. These data allowed us to assign this substance (signal number 1) as 3-O-E-caffeoylquinic acid.

5-O-E-caffeoylquinic acid

The chromatographic signal number 2 displayed the ion m/z 353 (deprotonated molecule) and a fragment ion m/z 191 in the mass spectrum (negative ionization mode). Its UV spectrum was typical of caffeoylquinic acid (UV max: ~ 299 and 325 nm). Taken together, these data suggested quinic acid esterified with a single unit of caffeic acid. Comparison of the retention time of this substance with a standard confirmed this signal as 5-O-E-caffeoylquinic acid.

3,4-di-O-E-caffeoylquinic acid

Signal number 6 also exhibited the characteristic UV spectrum of caffeoylquinic acid described above. The base peak in the mass spectrum recorded in the negative ionization mode was the ion m/z 515, which indicated the presence of a positional isomer of di-caffeoylquinic acid. The peak obtained in the positive ionization mode was the ion m/z 499, consistent with a dehydrated di-caffeoylquinic acid [M+H - H2O]+. However, [M+H]+ 517 and [M+Na]+ 539 were also detected. Again, key data on the identification of caffeoylquinic acids by HPLC-DAD-MS/MS,14 the presence of the ions m/z 191, 179 and 173 in the mass spectrum obtained from the fragmentation of the deprotonated molecule m/z 515, and comparison of the retention time with that of a standard allowed identification of this peak as 3,4-di-O-E-caffeoylquinic acid.

3,5-di-O-E-caffeoylquinic acid

The signal designated number 7 also presented the characteristics of di-caffeoylquinic acid. However, considering the presence of the ions m/z 191 and m/z 179 in the mass spectrum obtained from fragmentation of the ion m/z 515 in the negative ionization mode, and taking the order of elution into account, this signal was identified as 3,5-di-O-E-caffeoylquinic acid.

4,5-di-O-E-caffeoylquinic acid

For identification of this compound (signal designated number 9) the absence of the ion m/z 191 and the presence of the ions m/z 179 and m/z 173 in the mass spectrum obtained from fragmentation of the ion m/z 515 in the negative ionization mode were considered, together with comparison of the retention time with a standard.

Vicenin-2

The chromatographic signal labeled number 4 displayed UV spectrum with maximum absorption around 270 and 330 nm. The compound also produced fragmentation ions typical of di-C-glucosylflavones, such as those generated from water loss and sugar fragmentation. Fragmentation of the ion 595 [M+H]+ was verified in the positive ionization mode, as evidenced by the peaks at 577 [M+H - 18]+, relative to water loss, and 457 [M+H - 120]+, corresponding to loss of sugar parts. Comparison of the retention time of this signal with a standard enabled its identification as vicenin-2.

Goyazensolide

Identification of signal number 11 was accomplished by comparison with the retention time (co-elution) of a previously isolated authentic standard. The accurate mass obtained for this peak was in agreement with the exact masses calculated for the deprotonated molecule of this compound, and the product ion spectrum exhibited the same previously described fragmentation patterns and diagnostic ions.16

Method validation

Analytical method validation ensured reliability and credibility of the results for the purposes of this study and covered the concentration range required for chemical variability analysis. The validated method presented suitable limits of detection and quantitation, as well as satisfactory precision and recovery. All the results are listed in Tables 2 , 3 and 4 .

Sensitivity, accuracy, and precision data obtained via validation of the analytical method by HPLC-DAD are summarized in Tables 3 and 4 .

Statistical analysis

Figure 3 reveals that the caffeoylquinic acids are more intense as compared to the concentration of all the chemical compounds belonging to other classes, in all the studied periods. The lowest flavonoids and caffeoylquinic acids concentrations were verified in March (0.51 µg mL-1 and close to 4.78 µg mL-1, respectively). Sesquiterpene lactone was also present in low quantity in this period. The highest mean caffeoylquinic acids concentration values were detected in December (20.05 µg mL-1) and February (22.66 µg mL-1). As for flavonoids, the major mean values occurred in November (5.7 µg mL-1) and December (6.63 µg mL-1). Concerning sesquiterpene lactone, the largest mean values were found in October (6.49 µg mL-1) and December (5.91 µg mL-1), whereas the lowest mean value was registered in July (3.62 µg mL-1).


Within the caffeoylquinic acids and flavonoids classes, there was no marked variation in metabolite proportions, and the respective metabolites presented equivalent means and standard error (Table 5). The compound 3,5-di-O-E-caffeoylquinic acid was the most abundant among the caffeoylquinic acids, comprising approximately 57.8% of the total, while 3-O-E-caffeoylquinic acid was present in the lowest proportion (4.5%). The other caffeoylquinic acid isomers represented between 10.3 and 14.7% of the total amount of caffeoylquinic acids. In the case of flavonoids, the non-identified metabolites numbered 3 and 5 were the most representative (NI 3 27.5%, NI 5, 28.5%; NI 8 21.97%). Only one sesquiterpene lactone (goyazensolide) was detected, so it constituted 100% of this chemical class.

Hierarchical cluster analysis carried out for the rainfall and temperature variables (Figure 4) showed three readily distinguishable groups, in accordance with the Euclidian distances; the non-hierarchical method K-means confirmed the month distribution suggested by the hierarchical method (Figure 5). According to both methods, the first group was constituted by the hot and rainy months (November, December, January, and February), whereas the second group consisted of cold and dry months (May, June, July, and August). The third group comprised transition months (March, April, September, and October), so the characteristics were intermediate. The Hotelling's T2 test was performed, so as to compare samples by environmental variable values. This test indicated that there were statistically significant differences among all the values (Figure 5).



Correspondence analysis (CA) was accomplished by grouping samples in accordance with the environmental periods indicated by cluster analyses. In other words, the samples data were organized by following the identified seasons (rainy, dry, and transition).

Based on the CA results, first dimension held back 93.48% of data inertia. Because the first dimension (D-1) retained the most important information about samples ordination, it was used alone to understand plant metabolite concentration variation throughout the different seasons. The dry season (G2) and the rainy season (G1) were plotted in opposite sides of D-1, evidencing strong and inverse correlation between them (Table 6). The plots representing the transition months (G3) were placed in average positions of D-1, indicating weak correlation with this axis. Hence, the CA results revealed that the core seasons; i.e., the dry and rainy seasons, presented opposite metabolite concentration patterns, whilst the transition months exhibited intermediate conditions.

Interpretation of each metabolite coordinate on D-1 (CA) showed that the caffeoylquinic acids group underwent the widest concentration variation along the season cycle, followed by sesquiterpene lactone (Table 6). Indeed, the plant contained lower amounts of all the chemical compounds in the dry season (G2), as compared to the other seasons (G1 and G3). Although all the metabolites classes existed in higher concentrations during the or close to the rainy season, there was strong correlation between the higher concentrations and the rainy season for the caffeoylquinic acids and flavonoids groups, whereas the sesquiterpene lactone quantity reached its peak at a different timing.

It is known that temperature could control the flavonoids biosynthesis.18 For Arnica montana for example, temperature is the key factor on the alterations of the phenolic compounds in higher altitudes.19 Another example is the case of Brassica oleracea, that high levels of UV radiation led to increase the concentration of flavonoids, however the changes induced by UV did not alter the capacity to attract herbivore insects.20

In the present work, we could not explain exactly the factors that are responsible for the correlation between the caffeoylquinic acids and flavonoids higher concentrations and the rainy season. However it is known that several factors may alter the secondary metabolism of plants.1 Some of them are temperature, UV radiation and rainfall. So, we can only suggest that in the rainy season, temperature and UV radiation are more intense and consequently can cause an increase in the concentration of phenolic compounds which have recognized UV protective action.

CONCLUSIONS

A new HPLC-DAD-MS/MS method was developed and validated allowing the analysis of the major metabolites found in the methanol/water extract of the leaves of Eremanthus mattogrossensis. Ten specimens were analyzed from the same population on the same day and at the same time and no statistical difference on metabolite production were found. Three of these specimens were analyzed on different days, at one-month intervals, for 21 months and was verified a high correlation between the amount of E. mattogrossensis metabolites and seasonality, indicating that environmental properties promote important metabolic responses. Was found a strong correlation between the higher concentrations of caffeoylquinic acids and flavonoids and the rainy season that can be explained by the fact that in the rainy season, temperature and UV radiation are more intense and consequently can cause an increase in the concentration of phenolic compounds.

ACKNOWLEDGMENTS

This work was supported by FAPESP, CAPES, and CNPq. The authors acknowledge Prof. Dr. J. Semir (Department of Morphology and Plant Systematics, Biology Institute, State University of Campinas, State of São Paulo, Brazil) for plant identification. The authors would also like to thank IBAMA (Instituto Brasileiro do Meio Ambiente e dos Recursos Naturais Renováveis) for license nº 029/2006 and CNPq (Conselho Nacional de Desenvolvimento Científico e Tecnológico) for authorizing access to a component of genetic heritage (nº 010143/2011-4).

REFERENCES

1. Gobbo-Neto, L.; Lopes, N. P.; Quim. Nova 2007,30,374.

2. Wallaart, T. E.; Pras, N.; Beekman, A. C.; Quax, W. J.; Planta Med. 2000,66,57; Grace, S.; Logan, B.; Adams, W.; PlantCell Environ. 1998,21,513; Lopes, N. P.; Kato, M. J.; de Aguiar Andrade, E. H.; Soares Maia, J. G.; Yoshida, M.; Phytochemistry 1997,46,689; Bowers, M. D.; Collinge, S. K.; Gamble, S. E.; Schmitt, J.; Oecologia 1992,91,201.

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5. Lindroth, R. L.; Hsia, M. T. S.; Scriber, J. M.; Biochem. Syst. Ecol. 1987,15,681.

6. Holopainen, J. K.; Gershenzon, J.; Trends Plant Sci. 2010,15,176; Morales, L. O.; Tegelberg, R.; Brosche, M.; Keinanen, M.; Lindfors, A.; Aphalo, P. J.; Tree Physiology 2010,30,923; Albert, A.; Sareedenchai, V.; Heller, W.; Seidlitz, H. K.; Zidorn, C.; Oecologia 2009,160,1; Betz, G. A.; Gerstner, E.; Stich, S.; Winkler, B.; Welzl, G.; Kremmer, E.; Langebartels, C.; Heller, W.; Sandermann, H.; Ernst, D.; Trees-Structure and Function 2009,23,539; Chen, F.; Liu, C.-J.; Tschaplinski, T. J.; Zhao, N.; Crit. Rev. in Plant Sciences 2009,28,375; Bidart-Bouzat, M. G.; Imeh-Nathaniel, A.; J. Integrative Plant Biology 2008,50,1339; Opitz, S.; Kunert, G.; Gershenzon, J.; J. Chem. Ecol. 2008,34,508; Baraza, E.; Zamora, R.; Hódar, J.; Gómez, J.; Handbook of functional plant ecology, 2nd ed., Marcel Dekker: New York, 2007; Spencer, K. C.; Chemical mediation of coevolution, Academic Press: San Diego, 1988.

7. Gouvea, D. R.; Gobbo-Neto, L.; Lopes, N. P. In Plant Bioactives and Drug Discovery; Cechinel-Filho, V., ed.; John Wiley & Sons: New York, 2012, chap. 12.

8. Poorter, L. In Biotic interactions in the tropics; Burslem, D.; Pinard, M.; Hartley, S., eds.; Cambridge University Press: Cambridge, 2005; Vogel, S.; Life's devices; Princeton University Press: New Jersey, 1988.

9. Vichnewski, W.; Takahashi, A. M.; Tucciturco Nasi, A. M.; Rodrigues, D. C.; Goncalves, G.; Dias, D. A.; Lopes, J. N. C.; Goedken, V. L.; Gutiérrez, A. B.; Herz, W.; Phytochemistry 1989,28,1441; Le Quesne, P. W.; Levery, S. B.; Menachery, M. D.; Brennan, T. F.; Raffauf, R. F.; J. Chem. Soc., Perkin Trans. 1978,12,1572.

10. Gobbo-Neto, L.; Lopes, N. P.; J. Agric. Food Chem. 2008,56,1193.

11. Agência Nacional de Vigilância Sanitária (ANVISA); Guia para Validação de Métodos Analíticos e Bioanáliticos, RE nº 899, 29/5/2003; ICH - International Conference on Harmonisation of Technical Requirements for Registration of Pharmaceuticals for Human Use; ICH Harmonised Tripartite Guideline. Validation of analytical procedures: text and methodology Q2(R1), 2005.

12. Manly, B. J. F.; Métodos Estatísticos Multivariados, 3ª ed., Bookman: Porto Alegre, 2008; Johnson, R. A.; Wichern, D. W.; Applied multivariate statistical analysis, 5th ed., Prentice Hall: New Jersey, 2002.

13. Hair Junior, J. F.; Anderson, R. E.; Tatham, R. L.; Black, W. C.; Análise multivariada de dados, 5ª ed., Bookman: Porto Alegre, 2005.

14. Clifford, M. N.; Kirkpatrick, J.; Kuhnert, N.; Roozendaal, H.; Salgado, P. R.; J. Agric.Food Chem. 2008,106,379; Clifford, M. N.; Knight, S.; Surucu, B.; Kuhnert, N.; J. Agric.Food Chem. 2006,54,1957; Clifford, M. N.; Knight, S.; Kuhnert, N.; J. Agric.Food Chem. 2005,53,3821; Clifford, M. N.; Johnston, K. L.; Knight, S.; Kuhnert, N.; J. Agric.Food Chem. 2003,51,2900; Clifford, M. N.; J. Sci. Food Agric. 2000,80,1033.

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16. Crotti, A. E. M.; Bronze-Uhle, E. S.; Nascimento, P. G. B. D.; Donate, P. M.; Galembeck, S. E.; Vessecchi, R.; Lopes, N. P.; J. Mass Spectrom. 2009,44,1733.

17. http://tempoagora.uol.com.br/previsaodotempo.html/brasil/observados, acessada em Fevereiro 2010.

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Recebido em 7/5/12; aceito em 18/9/12; publicado na web em 26/10/12

  • 1. Gobbo-Neto, L.; Lopes, N. P.; Quim. Nova 2007,30,374.
  • 2. Wallaart, T. E.; Pras, N.; Beekman, A. C.; Quax, W. J.; Planta Med. 2000,66,57;
  • Grace, S.; Logan, B.; Adams, W.; PlantCell Environ. 1998,21,513;
  • Lopes, N. P.; Kato, M. J.; de Aguiar Andrade, E. H.; Soares Maia, J. G.; Yoshida, M.; Phytochemistry 1997,46,689;
  • Bowers, M. D.; Collinge, S. K.; Gamble, S. E.; Schmitt, J.; Oecologia 1992,91,201.
  • 3. Darrow, K.; Bowers, M. D.; Biochem. Syst. Ecol. 1997,25,1;
  • Bowers, M. D.; Stamp, N. E.; Ecology 1993,74,1778.
  • 4. Harborne, J. B.; Introduction to ecological biochemistry; Academic Press; New York, 1993.
  • 5. Lindroth, R. L.; Hsia, M. T. S.; Scriber, J. M.; Biochem. Syst. Ecol. 1987,15,681.
  • 6. Holopainen, J. K.; Gershenzon, J.; Trends Plant Sci. 2010,15,176;
  • Morales, L. O.; Tegelberg, R.; Brosche, M.; Keinanen, M.; Lindfors, A.; Aphalo, P. J.; Tree Physiology 2010,30,923;
  • Albert, A.; Sareedenchai, V.; Heller, W.; Seidlitz, H. K.; Zidorn, C.; Oecologia 2009,160,1;
  • Betz, G. A.; Gerstner, E.; Stich, S.; Winkler, B.; Welzl, G.; Kremmer, E.; Langebartels, C.; Heller, W.; Sandermann, H.; Ernst, D.; Trees-Structure and Function 2009,23,539;
  • Chen, F.; Liu, C.-J.; Tschaplinski, T. J.; Zhao, N.; Crit. Rev. in Plant Sciences 2009,28,375;
  • Bidart-Bouzat, M. G.; Imeh-Nathaniel, A.; J. Integrative Plant Biology 2008,50,1339;
  • Opitz, S.; Kunert, G.; Gershenzon, J.; J. Chem. Ecol. 2008,34,508;
  • Baraza, E.; Zamora, R.; Hódar, J.; Gómez, J.; Handbook of functional plant ecology, 2nd ed., Marcel Dekker: New York, 2007;
  • Spencer, K. C.; Chemical mediation of coevolution, Academic Press: San Diego, 1988.
  • 7. Gouvea, D. R.; Gobbo-Neto, L.; Lopes, N. P. In Plant Bioactives and Drug Discovery; Cechinel-Filho, V., ed.; John Wiley & Sons: New York, 2012, chap. 12.
  • 8. Poorter, L. In Biotic interactions in the tropics; Burslem, D.; Pinard, M.; Hartley, S., eds.; Cambridge University Press: Cambridge, 2005;
  • Vogel, S.; Life's devices; Princeton University Press: New Jersey, 1988.
  • 9. Vichnewski, W.; Takahashi, A. M.; Tucciturco Nasi, A. M.; Rodrigues, D. C.; Goncalves, G.; Dias, D. A.; Lopes, J. N. C.; Goedken, V. L.; Gutiérrez, A. B.; Herz, W.; Phytochemistry 1989,28,1441;
  • 10. Gobbo-Neto, L.; Lopes, N. P.; J. Agric. Food Chem. 2008,56,1193.
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    » link
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  • #
    Artigo em homenagem ao Prof. Otto R. Gottlieb (31/8/1920-19/6/2011)
  • *
    e-mail:
  • Publication Dates

    • Publication in this collection
      30 Nov 2012
    • Date of issue
      2012

    History

    • Received
      07 May 2012
    • Accepted
      18 Sept 2012
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