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Brazilian Journal of Microbiology

Print version ISSN 1517-8382On-line version ISSN 1678-4405

Braz. J. Microbiol. vol.33 no.1 São Paulo Jan. 2002

http://dx.doi.org/10.1590/S1517-83822002000100013 

UPTAKE OF FREE AND COMPLEXED SILVER IONS BY DIFFERENT STRAINS OF RHODOTORULA MUCILAGINOSA

 

Newton C.M. Gomes1; Carlos A. Rosa2; Patrícia F. Pimentel3; Leda C.S. Mendonça-Hagler1*

1Departamento de Microbiologia Geral, Instituto de Microbiologia, Universidade Federal do Rio de Janeiro, Rio de Janeiro, RJ, Brasil. 2Departamento de Microbiologia, Instituto de Ciências Biológicas, Universidade Federal de Minas Gerais, Belo Horizonte, MG, Brasil. 3Fundação Centro Tecnológico de Minas Gerais, Belo Horizonte, MG, Brasil

Submitted: April 30, 2001; Returned to authors for corrections: August 20, 2001; Approved: February 25, 2002

 

 


ABSTRACT

Five strains of Rhodotorula mucilaginosa were tested for the ability to accumulate free and complexed silver ions by metabolism-dependent and -independent processes. The ability to take up Ag+ was observed in both live and dead biomass, whereas silver dicyanide [Ag (CN)2-] uptake was strictly glucose dependent. In contrast to Ag (CN)2-, glucose addition inhibited by 16 to 25% the Ag+ uptake rate of living UFMG - Y02, Y27, and Y35 cells, while strains CBS 316 and UFMG-Y01 showed an improved uptake rate of about 115% and 13%, respectively. The Langmuir sorption model was used to evaluate the silver sorption capability of the R. mucilaginosa strains. The calculated qmax value suggested that R. mucilaginosa strains UFMG-Y27 had the highest loading capacity. The type strain CBS 316 had the lowest qmax but showed the highest affinity for silver ions. The results provided by the Fourier Transform Infra Red analysis (FTIR) suggest that C=O groups represent the main reactive site for silver uptake by the strain UFMG-Y27.

Key words: Bioaccumulation, biosorption, Rhodotorula mucilaginosa, silver


 

 

INTRODUCTION

Many metals and metalloids can be accumulated by yeasts and some of them are essential for structural and/or catalytic functions, whereas others are of no known metabolic importance (14). In general, microorganisms accumulate metals by biosorption or bioaccumulation processes. The first one involves metal adsorption around the cell envelope and is a metabolism-independent process. Bioaccumulation is strictly dependent on cell metabolism and involves active translocation of metals into the cell.

Biosorption phenomena occur as a result of metal ion interactions with functional groups in organic polymers on the cell surface (28). It is believed that phosphate, carboxyl, amine and amide groups found in carbohydrates, lipids, proteins, and other biopolymers of the microbial cell envelope represent the main sites for metal adsorption (9,24,26). The charge distribution and geometry of these binding sites may vary with the composition of the cell envelope of each microorganism, resulting in markedly different metal-binding affinities.

Bioaccumulation is a much slower process of metal uptake than biosorption and may be inhibited by the absence of nutrients such as glucose, nitrogen, and phosphate, by low temperatures and by the action of metabolic inhibitors (11,12,21). The process of metal accumulation and detoxification by living microorganisms includes metal sequestering by low molecular weight metabolic products (e.g. oxalic and citric acids), complexation and chelation of metals by sulfide and siderophores, enzymatically mediated metal deposition (e.g. phosphatase), influx of metals trough the cell membrane, metal binding by low molecular weight proteins (metallothioneins), and metal compartmentalization in vacuoles (13,23,24).

Silver plating is extensively used by various industries for production of durable and decorative products. The metal is normally plated from alkaline cyanide solutions (4) that usually generate silver dicyanide [Ag (CN)2-] as a contaminant in the wastewater. Silver dicyanide may be accompanied by other silver species and is a chemically stable and extremely toxic metal complex of high mobility in the environment. Recently we have studied 56 yeast strains isolated during the cyanidation process for gold extraction. Rhodotorula mucilaginosa (Syn. Rhodotorula rubra) strain UFMG-Y27 was able to survive at concentrations of Ag (CN)2- up to 40 mg l-1, and had the highest ability to take up this compound compared to all other yeasts tested (15). By the light of interesting results obtained in our previous work we have attempted to study four R. mucilaginosa strains previously isolated (15) and the type strain (CBS 316). They were characterized taxonomically and investigated for their ability to remove free (Ag+) and complexed [Ag (CN)2-] silver ions from dilute aqueous solutions by metabolism-dependent and -independent processes.

 

MATERIALS AND METHODS

Yeast source and identification

Samples (25 ml) were inoculated into flasks containing 25 ml of two-fold concentrated yeast nitrogen base (YNB - Difco) supplemented with 1% glucose and 0.01% chloramphenicol or into 25 ml of two- fold concentrated modified YGP broth medium containing final concentrations of 0.5% yeast extract, 1% peptone, 2% glucose and 0.01% chloramphenicol. The flasks were incubated at room temperature (25 ± 3ºC) with shaking (250 rev/min) for 3-10 days. Pure cultures were obtained by streaking the yeast growth on YM agar (0.3% yeast extract, 0.3% malt extract, 0.5% peptone, 1% glucose, and 2% agar). The yeasts were identified according to Barnett et al. (3) and Kurtzman and Fell (20).

Yeast biomass preparation for experiments on metabolism-dependent and independent silver uptake

R. mucilaginosa strains were inoculated into Erlenmeyer flasks containing Yeast Carbon Base (YCB - Difco) supplemented with 0.1% (NH4)2SO4. Cells from the late exponential growth phase (48 h) were harvested by centrifugation at 1,200 x g for 10 min and washed three times with distilled deionized water. The fresh cell pellets (1 mg ml-1 dry weight) were immediately used for the metabolism-dependent experiments and the remaining ones were dried at 60ºC to a constant weight for the metabolism-independent experiments. Due to the high ability of chloride ions to form insoluble complexes with silver (AgCl), all experiments were done in chloride-free medium to prevent precipitation of Ag+ as silver chloride.

Metabolism-dependent silver uptake

Living cells were added to 250 ml Erlenmeyers flasks containing 25 ml of 10 mM morpholineethanesulfonic acid (MES) buffer, previously adjusted to pH 6.5 with 1 M NaOH or HNO3 and 2% glucose (2). The final biomass concentration was 1 mg (dry weight) ml-1. Cell suspensions were previously equilibrated in MES buffer with glucose at 25ºC, with shaking (250 rev/min) for 1 h before the addition of 20 mg l-1 of silver as Ag (CN)-2 or Ag+ using their respective salts KAg (CN)2 and Ag NO3. After 12 hours of incubation the solution was centrifuged at 1,200 x g for 10 min and the supernatants were retained for metal analysis. Silver uptake values were determined from the difference between the final silver concentrations in the control flasks without yeast cells and in the test flasks. MES buffer was used because of its low metal-binding property (2,16).

Metabolism-independent silver uptake

Dried yeast biomass was added to 25 ml of 10 mM MES buffer, pH 6.5, to a final concentration of 1 mg (dry weight) ml-1 in 250 ml Erlenmeyer flasks (2). Free and complexed silver ions, Ag+ and Ag (CN)2-, respectively, were added to the suspensions to the desired final concentrations (1 to 65 mg l-1). The flasks were incubated for 3 h and after this period the biomass was centrifuged at 1,200 x g for 10 min and the supernatant was retained for silver analysis. The amount of metal removed was determined by the difference in metal content between flasks containing no biomass (control) and flasks containing biomass (test). Before each metabolism-independent experiment the dehydrated yeast biomass was rehydrated by pre-incubation in 10 mM MES buffer (8 hours), pH 6.5, with magnetic stirring.

Isotherm model

The extent of experimental silver uptake by yeast biomass was expressed according to the following equation:

Metal uptake q = (Ci - Cf) . V/M

Where Ci and Cf are the initial and equilibrium (final) metal ion concentrations (mg/L), respectively, V is the volume of sample solution (L), and M is the dry weight of the biomass added (g). In general, metabolism-independent metal uptake is directly related to metal sorption by the cell surface. The sorption data were fitted to the Langmuir adsorption isotherm model:

q = (b . Cf . qmax)/(1 + b . Cf)

Where qmax is the maximum sorbate (metal) uptake and b is the Langmuir constant related to adsorption energy and it is an indication of the "apparent affinity" of the biosorbent toward the metal (28).

Metal analysis

Metal analysis was performed using an atomic absorption spectrophotometer with an air-acetylene flame (Varian model AA-475) by reference to appropriate standard metal solutions according to APHA (1).

Fourier- transform infrared (FTIR) analysis

A FTIR spectrometer was used for the determination of the functional groups which may be involved in the silver biosorption process (10). Infrared spectra of silver-loaded and -unloaded yeast biomasses were recorded on a Perkin Elmer FTIR spectrometer (Model PARAGON 1000 PC). Disks of 100-mg KBr containing 1% of finely ground powder (<20 mm) of each sample were prepared less than 24 hours before recording.

 

RESULTS AND DISCUSSION

Although all R. mucilaginosa strains studied in this work had generally similar physiological profiles and were identified as members of that species, their carbon assimilation patterns presented discernible differences. The strains differed in their assimilation of trehalose, maltose, melezitose, L-arabinose, D-glucitol, ribitol, and manitol (Table 1). As with the taxonomic physiological tests, the silver uptake studies also showed a wide variation in metal uptake ability among all strains studied.

 

 

Nonliving (dried biomass) R. mucilaginosa strains UFMG-Y01, 02, 27, 35 and the type strain (CBS 316), were tested for the ability to accumulate free (Ag+) and complexed [Ag (CN)2-] silver ions. In all cases silver as Ag (CN)2- was refractory to the process of metabolism-independent metal uptake (biosorption, data not shown), whereas free silver ions were readily sequestered by the inactive biomass. The failure to take up silver as Ag (CN)2- may be attributed to the strength of the metal-anion complex or to repulsion of the negatively charged microbial cell surface for anionic metal complexes such as Ag (CN)2-.

For comparative purpose, silver (Ag+) sorption data were quantitatively evaluated by adsorption isotherms and using the Langmuir model. Fitting the experimental adsorption data with the model was important in order to determine maximum metal uptake and to establish the affinity of the reactive sites on the cell surface for silver. The calculated qmax (maximum metal accumulated) and b values (affinity) suggested that R. mucilaginosa strain UFMG-Y27 had the highest loading capacity, but not the highest affinity for silver (Table 2). The type strain CBS 316 had the lowest qmax but showed the highest affinity for silver ions, as evidenced by the Langmuir parameter b (6.85). This high affinity to silver is of fundamental importance for removal of very dilute silver cations from wastewaters (17). The low qmax and the high b value for silver shown by this strain would be explained by a relatively low number of sites for silver interaction on the cell surface, but with a very high reactivity of these binding sites for silver cations.

 

 

The infrared (IR) spectra of silver -loaded and -unloaded yeast biomass from the yeast strains were compared for the determination of functional groups which may be involved in the silver biosorption process (8,10). With exception of UFMG ¾ Y27, the IR spectra of the silver-loaded of R. mucilaginosa strains did not show significant differences in comparison a typical silver-unloaded biomass. The R. mucilaginosa (UFMG ¾ Y27) strain clearly displayed shifts of the stretching band located at 1650 cm-1 (Fig. 1). The stretching band at 1650 corresponds to amide I band — a CO stretching mode conjugated to NH deformation mode (18). The shifts of this band may correspond to the complexing of the carbonyl group by dative coordination to metals.

 

 

Fig. 2 represents the maximum uptake of free and cyanide-complexed silver ions in the presence and absence of glucose. The maximum silver uptakes by dead yeasts are shown for comparison. The addition of glucose was important to evaluate the effect of an energy source during the process of silver uptake by a living yeast biomass. Both silver species (Ag+ and Ag (CN)2-) were taken up by the living yeasts in presence of glucose (Fig. 2). Curiously, strain CBS 316 had the maximum uptake of Ag (CN)2- in presence of glucose. However, Ag (CN)2- uptake by the living yeast strains was not detectable in the absence of glucose (data not shown), clearly showing that glucose is of fundamental importance for Ag (CN)2- uptake.

 

 

The glucose dependence of Ag(CN)2- uptake is a strong indication that the uptake of this compound is an energy-dependent process. All strains had a higher ability to accumulate free silver ions when metabolically active. Since living cells can present all types of non-metabolic interactions with metals as well as interactions that require active metabolism, we may assume that yeasts may accumulate more metals when they are metabolically active than when they are inactive. Glucose addition also had influence on free silver ions (Ag+) uptake by the yeasts. Strains UFMG-Y02, Y27, and Y35 showed a reduction in uptake rate of about 19%, 25% and 16%, respectively, when glucose was added, whereas strains CBS 316 and UFMG-Y01 showed an increased uptake rate about 115.1% and 12.7%, respectively. Several investigators explain the increase in metal uptake caused by glucose as the result of an improvement of the mechanisms of membrane transport (e.g., an increased synthesis of transport proteins) (2,5). Although strains UFMG-Y01 and CBS 316 exhibited such an improvement, the decrease in Ag+ uptake observed for the other three strains in the presence of glucose is not in agreement with the transport model. Therefore, we can assume that, in some cases, the addition of glucose to the metal solution can be prejudicial for the evaluation of microorganisms potentially important for metal removal.

In general, glucose causes microorganisms to pump out H+ ions and transport them into the cell via a symport mechanism. These H+ ions are frequently bound to anionic sites on the cell wall, resulting in competition between protons and metal cations for anionic sites on the microbial cell (6,27). In agreement with the results shown previously for Ag (CN)2- uptake, it is reasonable to assume that this phenomenum could be useful to increase adsorption of anionic charged metal complexes to the cell surface.

Since the potential of R. mucilaginosa and other species of this genus has been evaluated for removal of heavy metals from solutions (7,19,22,25), it is important to stress that R. mucilaginosa strains can show many phenotypic differences. In this work we observed that R. mucilaginosa strains have physiological differences and they also show considerable variation in metal removal capacity.

Due the complexity of the industrial wastewater environment, silver can be found under different chemical forms. Therefore, the evaluation of microorganisms able to uptake silver in its complex forms is of fundamental importance to develop feasible bioprocesses to remove or recover silver from industrial waste waters. Both live and dead cells of R. mucilaginosa strains were able to take up Ag+, whereas silver dicyanide [Ag(CN)2-] uptake was a strictly energy- dependent process. The strain UFMG ¾ Y27 can resist to high concentrations of Ag(CN)2- (15), and since metal cyanide complex uptake seems to be mostly an energy- dependent process, this characteristic is of fundamental importance for silver dicyanide removal by it from industrial effluents.

 

ACKNOWLEDGMENTS

We acknowledge funding by the Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq), the Fundação de Amparo e Pesquisa do Estado de Minas Gerais (FAPEMIG) and PADCT (grant 430/95). We thank Dr. Allen N. Hagler for providing the Rhodotorula mucilaginosa type strain.

 

 

RESUMO

Acúmulo de íons de prata livres e complexados por diferentes linhagens de Rhodotorula mucilaginosa

Quatro linhagens de Rhodotorula mucilaginosa e uma linhagem padrão dessa mesma espécie foram investigadas quanto a habilidade de acumular íons de prata livres (Ag+) e complexados [Ag (CN)2-], através de processos dependentes e independentes do metabolismo. A habilidade de acumular Ag+ foi observada em ambas as células, vivas e mortas. Contudo, o acúmulo de Ag (CN)2- foi um processo estritamente dependente de energia. Durante os estudos que avaliaram a dependência de uma fonte energética para o acumulo de íons de prata livres (Ag+) foi observado que a adição de glicose resultou na diminuição do acúmulo de Ag+ por três linhagens (UFMG ¾ Y02, 27 and 35). Ao passo que as linhagens CBS 316 e UFMG ¾ Y01 apresentaram aumento do acúmulo desse metal. A analise dos resultados de biossorção através do modelo de Langmuir, sugerem que a linhagem UFMG ¾ Y27 possui a maior capacidade de acúmulo de prata (carga). Enquanto que a linhagem padrão CBS 316 apresentou a menor capacidade de carga e a maior afinidade por ions de prata. Analises de infra vermelho da biomassa fúngica, com e sem prata, mostraram que os grupamentos C=O foram os principais sítios de ligação desse metal pela linhagem UFMG ¾ Y27.

Palavras-chave: bioacumulação, biossorção, Rhodotorula mucilaginosa, prata

 

 

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* Corresponding author. Mailing address: Departamento de Microbiologia Geral, Instituto de Microbiologia Prof. Paulo de Góes, Bloco I, CCS, Universidade Federal do Rio de Janeiro, Ilha do Fundão. 21941-590, Rio de Janeiro, RJ, Brasil.

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