Identification of free Amino Acids in Brewer s Yeast after Heavy Metals Biosorption

Similar documents
Removal of Copper and Lead Ions from Aqueous Solution Using Brewer Yeast as Biosorbent

Biosorption of aqueous chromium VI by living mycelium of phanerochaete chrysosporium

Proteins: Characteristics and Properties of Amino Acids

Removal of Heavy Metals Fe 3+, Cu 2+, Zn 2+, Pb 2+, Cr 3+ and Cd 2+ from Aqueous Solutions by Using Eichhornia Crassipes

Screening of Algae Material as a Filter for Heavy Metals in Drinking Water

A Plausible Model Correlates Prebiotic Peptide Synthesis with. Primordial Genetic Code

CHEMISTRY ATAR COURSE DATA BOOKLET

Comparision of Langmuir and Freundlich Equilibriums in Cr, Cu and Ni Adsorption by Sargassum

BIOSORPTION OF HEAVY METALS BY PSEUDOMONAS BACTERIA

Potentiometric Titration of an Amino Acid. Introduction

Exam I Answer Key: Summer 2006, Semester C

Interference of Aluminum in Heavy Metal Biosorption by a Seaweed Biosorbent

EFFECT OF DIFFERENT CONDITIONS ON Cu(II) AND Cr(VI) BIOSORPTION BY DRIED WASTE TEA FUNGAL BIOMASS. Radojka N. Razmovski and Marina B.

Studies Leading to the Development of a Highly Selective. Colorimetric and Fluorescent Chemosensor for Lysine

Kinetic studies on the effect of Pb(II), Ni(II) and Cd(II) ions on biosorption of Cr(III) ion from aqueous solutions by Luffa cylindrica fibre

A rapid and highly selective colorimetric method for direct detection of tryptophan in proteins via DMSO acceleration

Adsorption of Cd(II) ions by synthesize chitosan from fish shells

Utilization of Diatoms to Collect Metallic Ions

Removal of Cadmium from Wastewater using low cost Natural Adsorbents

Content : Properties of amino acids.. Separation and Analysis of Amino Acids

Removal and Recovery of Uranium using Microorganisms Isolated from North American Uranium Deposits

Developing a Low Cost Activated Carbon from Agricultural Waste for the Removal of Heavy Metal from Contaminated Water

Removal of Heavy Metals from Aqueous Solution Using Rhizopus delemar Mycelia in Free and Polyurethane-Bound Form

Amino Acids and Peptides

Removal of Heavy Metals (Fe 3+, Cu 2+, Zn 2+, Pb 2+, Cr 3+ and Cd 2+ ) from Aqueous Solutions by Using Hebba Clay and Activated Carbon

The effect of preparation of biogenic sorbent on zinc sorption

Chemistry Chapter 22

REMOVAL OF HEAVY METALS USING COMBINATION OF ADSORBENTS - A CASE STUDY USING INDUSTRIAL WASTE WATER

CHEM J-9 June 2014

Supporting Information

Pauh, Penang, Malaysia. Keywords: Binary metal, immobilized, Saccharomyces cerevisiae, response surface methodology

Sorption of Cr(III) from aqueous solutions by spent brewery grain

Removal efficiency on magnetite (Fe 3 O 4 ) of some multicomponent systems present in synthetic aqueous solutions

Exam III. Please read through each question carefully, and make sure you provide all of the requested information.

EXPERIMENTAL PROCEDURE

BIOSORPTION OF Cu(II) BY LIVE AND DEAD CELLS OF Yarrowia lipolytica

Using Higher Calculus to Study Biologically Important Molecules Julie C. Mitchell

Uptake and Recovery of Lead by Agarose Gel Polymers

International Journal of Fundamental & Applied Sciences

Dual Use of a Chemical Auxiliary: Molecularly Imprinted Polymers for the Selective Recovery of Products from Biocatalytic Reaction Mixtures

Removal of Hexavalent and Total Chromium from Aqueous Solution by Avocado Shell

Environment Protection Engineering REMOVAL OF HEAVY METAL IONS: COPPER, ZINC AND CHROMIUM FROM WATER ON CHITOSAN BEADS

International Journal of Pharma and Bio Sciences REMOVAL OF ZINC FROM AQUEOUS SOLUTION USING COFFEE INDUSTRY WASTE ABSTRACT

Determination of the Amino Acid Sequence of an Unknown Dipeptide

Removal of Some Toxic Heavy Metals by means of Adsorption onto Biosorbent Composite (Coconut Shell Charcoal - Calcium Alginate) Beads

Separation of Large and Small Peptides by Supercritical Fluid Chromatography and Detection by Mass Spectrometry

Solutions In each case, the chirality center has the R configuration

Properties of amino acids in proteins

Collision Cross Section: Ideal elastic hard sphere collision:

Copper biosorption in a column of pretreated Aspergillus niger biomass

Viewing and Analyzing Proteins, Ligands and their Complexes 2

Katarzyna Zielińska, Alexandre G. Chostenko, Stanisław Truszkowski

BENG 183 Trey Ideker. Protein Sequencing

Chromatography 1 of 26 Boardworks Ltd 2016

BIOSORPTION OF ZINC AND MANGANESE BY MICROCOCCUS VARIANS AND STAPHYLOCOCCUS AUREUS ISOLATED FROM SOIL

Protein structure. Protein structure. Amino acid residue. Cell communication channel. Bioinformatics Methods

Assessment of Interference in Biosorption of a Heavy Metal

Content : Properties of amino acids.. Separation and Analysis of Amino Acids

Amino Acid Features of P1B-ATPase Heavy Metal Transporters Enabling Small Numbers of Organisms to Cope with Heavy Metal Pollution

A Fluorescence Turn-On Sensor for the Detection of Palladium Ions that Operates Through In-Situ Generation of Palladium Nanoparticles

INTRODUCTION. Amino acids occurring in nature have the general structure shown below:

Amino acids: Optimization in underivatized formula and fragment patterns in LC/ESI-MS analysis. Yoshinori Takano (JAMSTEC)

INTERNATIONAL JOURNAL OF ENVIRONMENTAL SCIENCES Volume 6, No 5, Copyright by the authors - Licensee IPA- Under Creative Commons license 3.

Supporting Information. Selective detection of trace amount of Cu 2+ using semiconductor nanoparticles in photoelectrochemical analysis

A. Two of the common amino acids are analyzed. Amino acid X and amino acid Y both have an isoionic point in the range of

EXAM 1 Fall 2009 BCHS3304, SECTION # 21734, GENERAL BIOCHEMISTRY I Dr. Glen B Legge

Uranium biosorption by Spatoglossum asperum J. Agardh:

Translation. A ribosome, mrna, and trna.

Biosorption of binary mixtures of heavy metals by green macro alga, Caulerpa lentillifera

Influence of operating conditions on the removal of Cu, Zn, Cd and Pb ions from wastewater by adsorption

IMMOBILIZATION OF Cu(II) IONS FROM AQUEOUS SYSTEMS INTO ECO-FRIENDLY, LOW-COST BIOMATERIAL

1. Amino Acids and Peptides Structures and Properties

Heavy Metal Removal by the Waste Biomass of Penicillium chrysogenum

Near UV-Visible Electronic Absorption Originating from Charged

Application of a Pulp Mill Waste for Wastewater Treatment. H. Yu, G.H. Covey and A.J. O Connor

Adsorption study on pomegranate peel: Removal of Ni 2+ and Co 2+ from aqueous solution

Removal Of Copper From Waste Water Using Low Cost Adsorbent

Lecture 15: Realities of Genome Assembly Protein Sequencing

Application of Bacteria to Remove Americium from Radioactive Liquid Waste *Corresponding author

Phytoremediation of Cu(II) by Calotropis Procera Roots

Supporting Information. Adsorption of Cu(II), Zn(II), and Pb(II) from aqueous single. and binary metal solutions by regenerated cellulose and

Biosorption of Ni(ii) and Pb(ii) by Phanerochaete chrysosporium from a binary metal system - Kinetics

12/6/12. Dr. Sanjeeva Srivastava IIT Bombay. Primary Structure. Secondary Structure. Tertiary Structure. Quaternary Structure.

Electronic Supplementary Information (ESI)

AMMONIA ADSORPTION FROM AQUEOUS SOLUTION USING NATURAL ZEOLITES. Faculty of Science, Ubon Ratchathani University, Ubon Ratchathani 31490, Thailand

Draft Method proposal: determination of glucoheptonic acid (HGA) in fertilizers.

Electronic Supplementary Information

Lecture'18:'April'2,'2013

A ratiometric fluorescent probe for specific detection of cysteine over. homocysteine and glutathione based on the drastic distinction in the

7.05 Spring 2004 February 27, Recitation #2

Int.J.Curr.Res.Aca.Rev.2016; 4(6): Biosorption of Lead (II), Nickel (II) Iron (II) and Zinc (II) on Flyash from Dilute Aqueous Solution

THE UNIVERSITY OF MANITOBA. PAPER NO: _1_ LOCATION: 173 Robert Schultz Theatre PAGE NO: 1 of 5 DEPARTMENT & COURSE NO: CHEM / MBIO 2770 TIME: 1 HOUR

REMOVAL OF CU 2+ IONS BY IMMOBILIZED A. LENTULUS FUNGAL STRAIN FROM INDUSTRIAL WASTEWATER

Modelling and Kinetics of Cd(II) Biosorption onto Inactive Instant Dry Baker s Yeast

Molecular Selective Binding of Basic Amino Acids by a Water-soluble Pillar[5]arene

Biokinetic Study on Chromium Removal from Textile Wastewater Using Azadirachta Indica as a Low Cost Adsorbent

Principles of Biochemistry

Supporting Information

Removal of Direct Red Dye Using Neem Leaf Litter

Removal of copper (II), iron (III) and lead (II) ions from Mono-component Simulated Waste Effluent by Adsorption on Coconut Husk

Transcription:

Identification of free Amino Acids in Brewer s Yeast after Heavy Metals Biosorption Andreea Stănilă 1, Zorita Diaconeasa 1, Floricuta Ranga 1, Florinela Fetea 1 1 Faculty of Food Science and Technology, University of Agricultural Sciences and Veterinary Medicine, 400372, 3-5 Manastur St., Cluj-Napoca, Romania, e-mail: andreea.stanila@usamvcluj.ro Abstract. Yeasts of genera Saccharomyces are efficient biosorbents for heavy metal ions. The aim of this study was to identify if the free amino acids present in brewer yeast are involved in metal biosorption due to their capacity to coordinate metal ions. As biosorbent was used non-living brewer s yeast type Saccharomices cerevisae at 0.5% yeast dose. Copper, lead and zinc solution of 1mg/L concentrations were prepared using their salts. The experiments were conducted at ph=6, which is the most appropriate for amino acids extraction. The amino acids were identified by HPLC-DAD/-ESI-MS chromatography. The experiments were conducted by mixing metals solution with yeast and shaken at a constant speed of 120 rpm at 20 0 C for 120 minute. The samples were centrifuged at 2500 rpm for 15 minute and the pellet were analysed for amino acids identification. The amino acids extraction from pellets was performed using HCl 0,05M/deionized water (v/v) 1/1. The HPLC analysis was performed on a Agilent 1200 system equipped with a binary pump delivery system LC-20 AT, a degasser DGU-20 A3, diode array SPD-M20 A, UV VIS detector (DAD). Amino acids were identified using an EEZ:Faast Kit for free amino acids, The amino acids identified by HPLC method were glycine, glutamic acid, leucine, isoleucine, ornithine, lysine, histidine, homophenylalanine, tyrosine, glutamine in control brewer yeast (before biosorption) and their profile differs according with the metal ions types. According with the peaks area there are differences in the presence of the amino acids due to the possible coordination with copper, lead and zinc ions. Keywords: Brewer yeast, amino acids, biosorption, heavy metals 1 Introduction Biosorption can be defined as the selective sequestering of metal soluble species that result in the immobilization of the metals by microbial cells. Biosorption is a process with some unique characteristics. It can effectively sequester dissolved metals from very dilute complex solutions with high efficiency. This makes biosorption an ideal candidate for the treatment of high volume low concentration complex waste-waters (Gadd, 1993; Wang, 2006). The selective sequestering of metal soluble species that result in the immobilization of the metals by microbial 455

cells is defined as biosorption. It refers to physicochemical mechanisms of inactive (i.e. non-metabolic) metal uptake by microbial biomass (Volesky 2001). Metal sequestering by different parts of the cell can occur via various processes: complexation, chelation, coordination, ion exchange, precipitation, reduction (Wang 2009, Alluri, 2007). Immobilization may be the result of more than one mechanism, for example, metal complexation may be followed by metal reduction or metal precipitation. These biopolymers, constituents of the cell wall and the other parts of the cell possess functional groups that have a significant potential for metal binding (Dakiky, 2002). Metal uptake by non-living cells is mainly a passive biosorption and consists in an adsorption of metal ions to the cells surface by interactions between metal and functional groups displayed on the surface of the cells (Paknikar, 2003). Brewer's yeast is made from a one-celled fungus called Saccharomyces cerevisiae and is used to make beer. It also can be grown to make nutritional supplements. The yeast biomass has been successfully used as biosorbent for removal of Ag, Au, Cd, Co, Cr, Cu, Ni, Pb, U, Th and Zn from aqueous solution. Yeasts of genera Saccharomyces, Candida, Pichia are efficient biosorbents for heavy metal ions. A number of literatures have proved that S. cerevisiae can remove toxic metals, recover precious metals and clean radionuclides from aqueous solutions to various extents (Podgorskii, 2004; Tálos, 2009) 2 Materials and Methods Saccharomices cerevisae biomass was supplied as a lyophilized by-product from industrial ethanol production. Prior use as a biosorbent, the biomass was pretreated in order to remove fine particles and to displace any metals already bound to the sorption sites. The waste biomass as washed with deionized water by stirring followed by centrifugation at 3000 rpm for 20 minutes. The supernatant was discarded and the pellet was reslurried in deionized water. The procedure was repeated for three times until the supernatant was clear. Metals solution were prepared using the mixture of their salts CuSO 4 5H 2 O, PbNO 3 2H 2 O, ZnSO 4 of analytical reagent grade. The concentrations of metals ions established were 1 mg/l for Cu 2+, Zn 2+, Pb 2+ and were obtained by dissolving the appropriate salts in deionized water. Experimental procedure: Metal ion binding experiments were performed by incubation of 25 mg biomass (dry weight) with 50 ml mixture of metals ions-containing solution in 125-ml Erlenmeyer flask on an orbital rotary shaker at 120 rpm for 120 minutes. The experiment was conducted at ph=6 and was established by adjusting it with HCl 0.1M or NaOH 0.1M solutions. In order to identify the free amino acids from biomass by HPLC chromatography the samples were centrifuged at 2500 rpm for 15 minutes, the supernatant was discarded and the pellets were analysed. The free amino acids were extracted from the pellets using two types of solutions: HCl 0,05M/deionized water (v/v) 1/1. HPLC analysis was performed on a Agilent 1200 system equipped with a binary pump delivery system LC-20 AT (Prominence), 456

a degasser DGU-20 A3 (Prominence), diode array SPD-M20 A, UV VIS detector (DAD). Amino acids (100 µl) from control brewer s yeast and samples provided after biosorption of metal ions were identified using an EZ:Faast Kit for free amino acids, provided by Phenomenex (USA). The results are presented in the next table and figures. 3 Results and Discussions The absorption mechanisms of metals are different and depend on cellular metabolism. In non-living brewer yeast this mechanism is one of physical-chemical interaction between metal ions and some functional groups, especially amino and carboxyl. The aim of this study was to establish the amino acids from brewer yeast involvement in metal ions biosorption, as it is known that amino and carboxyl groups could be responsible for complexation depending on ph intervals and metal:ligand ratio. In the HPLC chromatograms these involvement could be observed by changing the absorption intensities between amino acids from brewer yeast control and brewer yeast charged with metal ions by biosorption. The standard solutions of amino acids used for analysis were selected according with the literature data regarding the presence of these compounds in brewer yeast (Podgorskii, 2004). The main amino acids identified by HPLC method were glycine (Gly), asparagine (ASN), glutamic acid (GLU), leucine (LEU), isoleucine (ILE), ornithine (ORN), lysine (LYS), histidine (HYS), homophenylalanine (HPHE), tyrosine (TYR), glutamine GLN), alanine (ALA), valine (VAL), triptophan (TRP), phenylalanine (PHE), α-aminobutyric acid (ABA). The separation and identification of amino acids were performed on brewer yeast uncharged with metal ions (control) and brewer yeast charged with metal ions after their biosorption at different ph values. The results are presented in the next table and figures. The profiles of chromatograms are different between control brewer yeast and samples charged with metal ions due to the absorption of copper, zinc and lead after incubation. It is supposed that amino acids from brewer yeast has the capacity to coordinate these metal ions and the complexes resulted have different retention times and peaks area than free amino acids as it can be seen in the Table 1. From the data above it can be presumed that amino acids are involved in metal coordination due to their capacity of metal binding through carboxyl and amino groups. Another explanation regarding the changes in amino acids profiles and content is that that it could be affected by autolysis and fermentation conditions like time, temperature, ph, moisture content (Cabuk, 2005). 457

Nr crt 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 Table 1. Amino acids identified in brewer yeast uncharged (control) and charged with metal ions. control m/z control area GLN/275 10704200 ASN/243 GLY/204 ALA/218 ORN/347 PRO/244 HIS/370 VAL/246 GLU/318 1,11E+08 2,93E+08 4,8E+08 6,34E+08 8,99E+08 3,2E+08 1,29E+08 6,34E+08 TRP/333 76783688 LEU/260 PHE/294 3,63E+08 2,4E+08 ILE/260 68063784 ABA/232 23497502 HPHE/189 TYR/396 2,83E+08 7,83E+08 Cu biosorption (area) Pb biosorptio n (area) Zn biosorptio n (area) - - - - 17414728 24690218 34229200 62596676 86537960 59079340 76963752 2,02E+08 18151634 4,06E+08 2,96E+08 2,16E+08 25244664 5,98E+08 7473274 55393300 79203976 - - - 31089642-59059104 - 23041980 25558244 16612316 38825024 87357976-47576664 - 6770684 8980013 25713988 - - - 26532408 94582776 2,33E+08 37071216 1,21E+08 2,67E+08 The metal binding capacity differs from an amino acids to other: GLN, Val and AAA which are present in uncharged brewer yeast sample disappear in the chromatograms of charged brewer s yeast with all metal ions; ASN and TRP have good affinity for copper ions, GLU for lead ions, and PHE for copper and zinc ions. The others amino acids present different affinity for metal ions according with their molecular structure and the capacity to coordinate copper, lead and zinc. According to covalent index Pb(II) ion is classified as a class b ion, while Cu(II) and Zn(II) are classified as borderline ion, so the behavior of coordination is not full the same and the binding capacity is different (Iqbal, 2004; Niebeer, 1973). 458

Fig. 1. HPLC chromatogram of amino acids extracted from control brewer s yeast (A), amino acids extracted from brewer s yeast charged with copper ions (B), with lead ions (C), with zinc ions (D). 4 Conclusions This study represents a first step in elucidation of the absorption mechanism of metal ions from aqueous solution by brewer yeast. Thus, the preliminary results lead to the conclusion that free amino acids, above other constituents from yeast, could be involved in metal biosorption. This process is strongly dependent on experimental 459

conditions, especially on ph level, as it is known that each metal ions have characteristic ph limits for coordination with different organic ligands. This study reveal the presence of 16 free amino acids in brewer s yeast and significant differences in their profile and content after biosorption of copper, lead and zinc, which could be explained by the coordination of these ions by carboxyl and amine groups of the ligands. Acknowledgments. This work was supported by Romanian Ministry of Education and Scientific Research UEFISCDI - PN-II-PT-PCCA-2013-4-0743 References 1. Alluri, HK., Ronda, SR., Setalluri, VS. (2007). Biosorption: an ecofriendly alternative for heavy metal removal. African Journal of Biotechnology 6(25):2924-2931. 2. Cabuk, A., Akar, T., Tunali, S., Tabak, O., 2005. Biosorption characteristics of Bacillus sp. ATS-2 immobilized in silica gel for removal of Pb(II). J.Hazard Mater 136:317-323. 3. Dakiky, M., Khamis, M., Manassra, A., Mereb, M. (2002). Selective adsorption of chromium (VI) in industrial wastewater using low-cost abundantly available adsorbents. Adv. Environ. Res. 6: 533-540. 4. Gadd, GM. (1993). Interactions of fungi with toxic metals. Phytologist 124:25 60 5. Iqbal, M., Edyvean, R.G.J., 2004. Biosorption of lead, copper and zinc ions on loofs sponge immobilized biomass of Phanerochaete chrysosporium. Miner.Eng. 17:217-223. 6. Paknikar, KM., Pethkar, AV., Puranik, PR. (2003). Bioremediation of metalliferous Wastes and products using Inactivated Microbial Biomass. Indian J. Biotechnol. 2: 426-443. 7. Podgorskii, VS., Kasatkina, TP., Lozovaia, OG. (2004). Yeasts-biosorbents of heavy metals. Mikrobiol. Z 66:91-103. 8. Tálos, K., Páger, C., Tonk, S., Majdik, C., Kocsis, B., Kilár, F., Pernyeszi, T. (2009). Cadmium biosorption on native Saccharomyces cerevisiae cells in aqueous suspension. Acta Universitatis Sapientiae, Agriculture and Environment, 1: 20-30. 9. Volesky, B. (2001). Detoxification of metal-bearing effluents: biosorption for the next century. Hydrometallurgy 59:203 16. 10. Wang, JL., Chen, C. (2006). Biosorption of heavy metals by Saccharomyces cerevisiae: a review. Biotechnol Advances 24:427 51. 11. Wang, JL., Chen, C. (2009). Biosorbents for heavy metal removal and their future. Biotechnology Advances 27:195-226. 460

12. Niebeer E., McBryde W.A., 1973. Free energy relationships in coordinate chemistry (III): a comprehensive index to complex stability. Can.J.Chem.51:2512-2524. 461