Print version ISSN 1984-8250
Braz. J. Pharm. Sci. vol.47 no.3 São Paulo July/Sept. 2011
Kristiane de Cássia MariottiI; Fabiano BarretoII; Gabriela Cristina SchmittI; Ivomar ZancanaroI; Eliane DallegraveIII; Rodrigo Bustos SingerIV; Mirna Bainy LealV; Renata Pereira LimbergerI, *
ILaboratory of Analysis and Toxicological Research, Department of Analysis, Faculty of Pharmacy, Federal University of Rio Grande do Sul Toxicology Laboratory,
IINational Agricultural Laboratory of Rio Grande do Sul, LANAGRO/RS
IIIToxicology Information Center of Rio Grande do Sul, State Foundation of Production and Research in Health
IVDepartment of Botany, Federal University of Rio Grande do Sul
VLaboratory of Pharmacology and Toxicology of Natural Products, Department of Pharmacology, Institute of Basic Health Sciences, Federal University of Rio Grande do Sul
Gunnera (Gunneraceae) forms a complex association with the cyanobacterium Nostoc puctiforme L. Gunnera-Nostoc symbiosis is the only one reported involving a flowering plant, and results in the formation of the neurotoxic amino acid β-N-methylamino-L-alanine (BMAA). The species Gunnera manicata L., for which phytochemical, pharmacological and toxicological studies are lacking, is found in Southern Brazil. Therefore, acute toxicity and the presence of neurotoxic amino acid were investigated in aqueous extracts of G. manicata. The acute toxicity test was conducted by administering aqueous root extract of G. manicata at a concentration of 2000 mg/kg in a single dose orally to Wistar rats. Lethality was monitored daily for 14 days after treatment. The relative mass of organs was analyzed by one-way ANOVA and macroscopic changes were investigated. The analysis of BMAA, a procedure performed by GC/MS, involved a preliminary derivatization step. The ESI-MS/MS analysis was done by direct infusion. The present study demonstrated absence of neurotoxin in the samples of G. manicata analyzed and absence of acute toxicity in aqueous root extracts. These data confirm that extracts from the roots of G. manicata have a high margin of drug safety.
Uniterms: Gunnera manicata L./toxicity. β-N-methylamino-L-alanine/identification. Neurotoxins/identification. Acute toxicity.
Gunnera (Gunneraceae) forma uma complexa associação com a cianobactéria Nostoc puctiforme L. A simbiose Gunnera-Nostoc é a única relatada envolvendo uma angiosperma e, em decorrência desta, ocorre a formação da neurotoxina β-N-metilamino-L-alanina (BMAA). No sul do Brasil, encontra-se a espécie G. manicata L., da qual não constam, na literatura científica, estudos fitoquímicos, farmacológicos e toxicológicos. Assim, o presente estudo avaliou a toxicidade aguda e a presença da neurotoxina BMAA em extratos aquosos de G. manicata. O ensaio de toxicidade aguda foi realizado com extrato aquoso das raízes de G. manicata na concentração de 2000 mg/kg, administrado em dose única via oral em ratos Wistar. Letalidade foi observada diariamente durante 14 dias pós-tratamento. Após a eutanásia, a massa relativa dos órgãos foi analisada por ANOVA de uma via e investigou-se a presença de alterações macroscópicas. A análise do BMAA por CG/EM envolveu uma etapa preliminar de derivatização, já a análise por ESI-EM/EM foi realizada por infusão direta. O presente estudo demonstrou a ausência da neurotoxina nas amostras de G. manicata analisadas bem como a ausência de toxicidade aguda no extrato aquoso das raízes. Esses dados demonstram alta margem de segurança dos extratos testados.
Unitermos: Gunnera manicata L./toxicidade. β-N-metilamino-L-alanina/identificação. Neurotoxina/identificação. Toxicidade aguda.
Gunnera (Gunneraceae) comprises more than forty species occurring mainly in the Southern Hemisphere (Wanntorp, 2003). Some cyanobacteria are involved in symbioses with hosts such as fungi (lichens), bryophytes, cycads, mosses, ferns (Azolla) and Gunnera. The most common cyanobacteria found in symbioses with plants belong to the filamentous heterocystous genus Nostoc (Nilsson, Bergman, Rasmussen, 2000). Gunnera-Nostoc symbiosis is unique in being the only angiosperm genus involved in symbiotic associations with the nitrogen-fixing cyanobacterium Nostoc puctiforme L.. This symbiosis is possibly a relic of an earlier partnership which evolved during a period when there was a limited supply of inorganic forms of nitrogen (Osborne et al.,1992).
Motile filaments of cyanobacteria, known as hormogonia, colonize Gunnera plants through cells in the plant's specialized stem glands. In an in vitro experiment, optimized conditions were determined for establishing Nostoc-Gunnera symbiosis by inoculating mature glands with hormogonia from Nostoc punctiforme. Gunnera manicata L. plants were grown in nitrogen-replete medium and nitrogen status was found to be the main determinant of gland development. In contrast to uninoculated plants, G. manicata plants colonized by N. punctiforme were able to continue growing in N-limited medium (Chiu et al., 2005).
Beta-N-methylamino-L-alanine (BMAA), a non protein amino acid, was found to be produced by cyanobacterial root symbionts of the genus Nostoc (Cox et al., 2005). The naturally occurring, non-essential amino acid BMAA has recently been found in high concentrations in brain tissue of patients with tauopathies such as the Amyotrophic Lateral Sclerosis-Parkinsonism-Dementia Complex (ALS/PDC) in the South Pacific island of Guam and in a small number of North American Caucasian patients with sporadic Alzheimer's disease. BMAA is produced by cyanobacteria present in all conceivable aquatic and/or terrestrial ecosystems and may be accumulated in living tissues in free and protein bound forms through the process of biomagnification (Papapetropoulos, 2006). Once ingested, BMAA can be bound by proteins within the body, resulting in a slow release of free BMAA over years as contaminated proteins are metabolized. The demonstration, by enzymatic cleavage, that BMAA is incorporated within the actual amino acid sequence of the protein would lend weight to this hypothesis. BMAA was discovered in the brain tissues of nine Canadian Alzheimer's patients (Cox et al. 2005) and in neurotoxic foods, including cycad flour, flying foxes and other feral or wild animals that are important components of the traditional Chamorro diet (Banack, Murch, Cox, 2006). In addition, it was also found in cyanobacterial-plant symbiosis such as Gunnera kauaienisis (Cox et al., 2005). Nilsson and coworkers (2000) found 45 cyanobacteria isolated from 11 different Gunnera species originating from different geographical areas. The most common cyanobacteria found in symbioses with plants belong to the filamentous heterocystous genus Nostoc (Nilsson, Bergman, Rasmussen, 2000).
The G. manicata species, on which there is scant scientific data from phytochemical, pharmacological or toxicological studies, is found in Southern Brazil, mainly in coastal regions. Considering that G. manicata plants were able to be colonized by N. punctiforme and that the formation of the BMAA neurotoxin can result from this symbiosis, the present study investigated the presence of BMAA and acute toxicity in aqueous extracts of the genus G. manicata, native to Southern Brazil.
MATERIALS AND METHODS
Chemicals and reagents
BMAA (CAS 15920-93-1) was purchased from Sigma Chemical Co. (St. Louis, USA). Water was purified using a Milli-Q system (Millipore, Bedford, USA). Pyridine and acetonitrile (HPLC grade) were obtained from Merck (Darmstadt, Germany), ethanol from Proquimios (Rio de Janeiro, RJ, Brazil), dichloromethane from Cromato (Diadema, SP, Brazil) and ethyl-chloroformate from Sigma Chemical Co. (St. Louis, USA).
Roots of G. manicata were obtained from the Aparados da Serra region, Southern Brazil, and identified by Rodrigo B. Singer. A voucher specimen (R.B. Singer s. n., Serra da Rocinha, January 15th, 2009) has been deposited at the ICN herbarium - Departamento de Botânica - UFRGS in Porto Alegre, Brazil.
Preparation of extracts
The aqueous extract was made from the dried roots or leaves extracted in a water bath at 50 °C for 3 hours. The extract obtained was collected, filtered and then concentrated to dryness under reduced pressure. The resulting residue was subsequently dissolved in water for analysis.
Twelve male and twelve female Wistar rats weighing 191.16 ± 12.92 g and 222.5 ± 22.05 g, respectively and obtained from the State Foundation of Production and Research in Health (FEPPS) were used. The animals were housed in 47x34x18 cm polyethylene cages (6 animals per cage) under standard conditions of temperature (22 ± 2 ºC), controlled humidity and 12 h-light/dark cycle. All animals were fasted overnight but were provided with water ad libitum. Experimental procedures were performed during the light phase of the cycle. The experiments were performed after approval of the protocol by the FEPPS Research Ethics Committee (number CEP/FEPPS-04/2008) and were carried out in accordance with current guidelines for the care of laboratory animals (Olfert, Cross, McWilliam, 1998).
The experiments were conducted by dividing the rodents into groups of six rats each, all of which were treated orally (by gavage) with water (control) or 2000 mg/kg of G. manicata aqueous root extract. The 2000 mg/kg dose was chosen based on previous experiments by our research group, showing signs of low or non-toxicity. All treatments were administered at a constant volume of 10 mL/kg. The animals were observed after dosing for 1 min and at 5, 15, 30 min and 1, 2, 3, 4, 5, 6 h for the presence of respiratory, digestive and neurological alterations. The specific signs monitored were alterations in locomotor activity, stimulus reaction, piloerection, salivation, gasping, ptosis, tearing, tremors, writhing, and convulsions. The number of deaths and weight were noted every 24 h for 14 days. After the 14th day, surviving rats were euthanized, necropsied and analyzed for macroscopic alterations in heart, liver, kidneys, adrenals, lungs, brain and spleen. The weight of the organs was determined and expressed as relative weight (organ mass/ body weight x 100). In acute toxicological studies, 6 animals per group were used, and only at the high dose, in order to minimize the biological variability and to minimize the number of animals used in the study, considering the ethical aspects (Brasil, 2004; Cazarin, Corrêa, Zambrone, 2004).
Derivatization and extraction procedures
Standard of BMAA derivatives were prepared by treating of 250 µL of BMAA solution (10 ng/mL) with a mixture of 100 µL ethanol and 80 µL pyridine (65:25:10 by volume). A 15 µL aliquot of ethyl-chloroformate was added and the mixture was shaken vigorously for about 30 s until the evolution of CO2 gas was complete. The derivatives were extracted with 100 µL of dichloromethane, with vigorous shaking. The mixture solution was centrifuged at 3500 rpm for 10 min. The extraction was performed twice. The organic layer was dried under N2 gas and reconstituted by adding 100 µL of dichloromethane. A 1 µL aliquot of extract was injected into the GC injection port running in a solvent vent mode (Guo et al., 2007). The same treatment was received for aqueous extracts of roots and leaves which were analyzed by gas chromatography-mass spectrometry (GC-MS). Both were analyzed with or without spiking standard BMAA.
Another extraction procedure was tested to investigate the presence of BMAA in roots and leaves. Acid hydrolysis was accomplished using 6 M HCl as the extraction medium, and by incubating for 17h at 110 ºC to release any protein-bound BMAA. Excess HCl was evaporated and the residue dissolved in water (600 µL). After centrifugation the extracts were passed through syringe filters. Ultrafiltration was used when necessary before injecting aliquots directly into the tandem mass spectrometry (ESI-MS/MS). These samples were also derivatized and analyzed by the GC-MS system. All of these samples were analyzed with or without spiking standard BMAA.
Determination of BMAA by GC-MS
The samples were analyzed by GC/MS using a quadrupole MS system (Shimadzu CLASS17A-QP5000) operating at 70 eV. GC analysis was performed using a fused silica capillary column (30 cm x 0.25 x /0.25 mm, coated with DB-5). Injector and detector temperatures were set at 270 °C; the oven temperature was kept at 60 °C for 3 min and then ramped to 280 °C at a rate of 20 °C/min. The final temperature of 280 °C was reached in 5 min. Helium was employed as the carrier gas (1 m:/min). This methodology was adapted from Guo and co-workers (2007). Under these conditions, the retention time of the BMAA derivative was 12.45 min, as depicted by the chromatogram in Figure 1.
Determination of BMAA by ESI-MS/MS - Mass spectrometric condition
The analysis was done by direct infusion into a Sciex API 5000 triple stage quadrupole mass spectrometer (Applied Biosystems, Foster City, CA, USA). The solvent used in the infusion syringe was a mixed of 0.1% formic acid and acetonitrile (50:50 v/v). The flow rate of the syringe was 10 µL min"1. The ions were monitored full scan in positive mode, where nitrogen was used for both nebulizer and collision gas. The fragmentation profile was obtained from selection of a pattern ion and monitored in MS2 mode. Fragments were observed by tuning MS1 for m/z 119 and then scanning MS2 for product ions. The optimal collision energy was 10 eV. For reliable identification, five specific product ions (m/z 102, 88, 76, 73 and 44), all derived from a precursor ion of m/z 119 and originating from different parts of the molecule, were detected (Rosén, Hellenäs, 2008).
All the results were expressed as mean ± SEM (standard error of mean). Statistical analysis for body weight gain was evaluated by repeated measures analysis of variance (ANOVA) and relative organ weight was analysed by one-way ANOVA using SPSS 10.0 software. The significance level was set at p < 0.05.
Rats administered G. manicata roots extract developed no clinical signs of toxicity either immediately or during the post-treatment period with 2000 mg/kg. In the same observation period, no deaths occurred. Similarly, no macroscopic changes in organs and no statistically significant changes were observed in the assessment of the relative mass of organs of necropsied animals.
The analytical investigation of the aqueous root and leaf extracts, as well as extracts made by acid hydrolysis, showed no chromatographic profile or mass spectrum characteristic of the standard of ethyl chloroformate derivatization of BMAA. Similarly, on ESI-MS/MS analysis in both extraction procedures, no neurotoxin was observed. After several analyses of different samples, neurotoxin was considered absent in G. manicata.
G. manicata is a popular ornamental plant native to Southern Brazil. Despite its ornamental use, no toxicity studies were found in scientific literature. After an extensive review we observed that this species can be infected by Nostoc puctiforme L. (Chiu et al., 2005) and as a result of this symbiosis the beta-N-methylamino-L-alanine (BMAA) can be produced. This is a non protein amino acid recently associated with Amyotrophic Lateral Sclerosis-Parkinsonism-Dementia Complex (ALS/PDC) in the South Pacific Island of Guam. Therefore, the aim of this study was to elucidate acute toxicity and investigate the presence of BMAA. The present investigation shows that the aqueous extract of the roots of G. manicata is non-toxic by the oral route in rats, at least up to maximum doses of 2000 mg/kg body weight.
For the chemical analysis by GC/MS, chloroformates derivatizing with simpler alkyls were used, with ethyl known for years as one of the favorable reagents for treating amino groups in gas chromatography. They have been revealed randomly as exceptionally rapid esterification agents (Husek, 1998). The chemical pretreatment of the sample was aimed at removing the active hydrogen atoms from all, or at least most, of the reactive groups. It is desirable that it be carried out as quickly as possible with a minimum number of reagents and reaction steps. Since BMAA is a non-protein aminoacid, ethyl chloroformate was chosen for derivation procedures for GC/MS analysis.
To eliminate any doubt regarding the presence or absence of BMAA, it was confirmed by ESI-MS/MS analysis, focusing on the absence of this non-protein amino acid in the samples investigated.
It should also be stressed that Nostoc symbiosis is widespread amongst Gunnera species (Wanntorp, Wanntorp, 2003). Nostoc aggregates are clearly visible in transversal sections of the G. manicata stem, as greenish dots or areas (R.B. Singer, pers. obs). Even the tiny G. herteri (a small, annual species which is apparently the sister-group of all remaining Gunnera spp.) (Rutishauer, Wanntrop, Pfeifer, 2004) displays the anatomic stem channels that allow the Nostoc "infection". The absence of toxic compounds in G. manicata strongly suggests that the presence of symbiotic Nostoc colonies does not per se enable the secretion of the aforementioned toxic compounds. This situation suggests that other factors (e.g. ecological factors, phylogenetic biases etc.) may be involved. Sampling G. manicata stems in different regions may help to elucidate whether the presence/absence of toxic compounds is ecologically biased or not. On the other hand, a dense sampling within the Gunnera species may allow elucidation of whether or not the presence of toxic compounds is phylogenetically biased (e.g. toxic compounds are found or lacking in groups of phylogenetically-related species).
In conclusion, the present study demonstrated the absence of the neurotoxin BMAA in samples of G. manicata native to Southern Brazil. The absence of acute toxicity in aqueous root extracts of G. manicata under the conditions used in the experiment suggests that G. manicata may be safer for pharmacological use because samples without BMAA do not induce neurological or systemic injuries. These results demonstrate that the extracts of the roots of G. manicata have a high margin of drug safety. Further phytochemical and biological studies are underway in order to prospect bioactive compounds or plant extracts.
The authors would like to acknowledge Dr. Ernani Pinto for providing us with BMAA, synthesized by his research group for our preliminary analysis and also to extend our thanks to FEPPS for donation of the animals. This work was supported by CNPq.
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Received for publication on 10th February 2010
Accepted for publication on 11th April 2011
* Correspondence: R. P. Limberger. Laboratório de Análises e Pesquisas Toxicológicas, Departamento de Análises, Faculdade de Farmácia, Universidade Federal do Rio Grande do Sul. Av. Ipiranga, 2752 - 90610-000 - Porto Alegre - RS, Brazil. E-mail address: email@example.com