PROTEIN a CHROMATOGRAPHY – the PROCESS ECONOMICS DRIVER in Mab MANUFACTURING
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Protocols and Tips in Protein Purification
Department of Molecular Biology & Biotechnology Protocols and tips in protein purification or How to purify protein in one day Second edition 2018 2 Contents I. Introduction 7 II. General sequence of protein purification procedures 9 Preparation of equipment and reagents 9 Preparation and use of stock solutions 10 Chromatography system 11 Preparation of chromatographic columns 13 Preparation of crude extract (cell free extract or soluble proteins fraction) 17 Pre chromatographic steps 18 Chromatographic steps 18 Sequence of operations during IEC and HIC 18 Ion exchange chromatography (IEC) 19 Hydrophobic interaction chromatography (HIC) 21 Gel filtration (SEC) 22 Affinity chromatography 24 Purification of His-tagged proteins 25 Purification of GST-tagged proteins 26 Purification of MBP-tagged proteins 26 Low affinity chromatography 26 III. “Common sense” strategy in protein purification 27 General principles and tips in “common sense” strategy 27 Algorithm for development of purification protocol for soluble over expressed protein 29 Brief scheme of purification of soluble protein 36 Timing for refined purification protocol of soluble over -expressed protein 37 DNA-binding proteins 38 IV. Protocols 41 1. Preparation of the stock solutions 41 2. Quick and effective cell disruption and preparation of the cell free extract 42 3. Protamin sulphate (PS) treatment 43 4. Analytical ammonium sulphate cut (AM cut) 43 5. Preparative ammonium sulphate cut 43 6. Precipitation of proteins by ammonium sulphate 44 7. Recovery of protein from the ammonium sulphate precipitate 44 8. Analysis of solubility of expression 45 9. Analysis of expression for low expressed His tagged protein 46 10. Bio-Rad protein assay Sveta’s easy protocol 47 11. -
Coagulation-Flocculation As a Submerged Biological Filter Pre-Treatment with Landfill Leachate
Coagulation-flocculation as a submerged biological filter pre-treatment with landfill leachate A. Gálvez Perez1,2, A. Ramos1,2,3, B. Moreno1,2,3 & M. Zamorano Toro1,2 1Department of Civil Engineering, Granada University, Spain 2MITA Research Group 3Institute of Water Research Abstract Landfill leachate may cause environmental problems if it is not properly managed and treated. An appropriate treatment process of landfill leachate often involves a combination of physical, chemical and biological methods to obtain satisfactory results. In this study, coagulation-flocculation was proposed as a pre- treatment stage of partially stabilized landfill leachate prior to submerged biological filters. Several coagulants (ferric, aluminium or organic) and flocculants (cationic, anionic or non-ionic) were assayed in jar-test experiments in order to determine optimum conditions for the removal of COD and total solids. Among the cationic flocculants, that of highest molecular weight and cationicity (CV/850) showed highest removal efficiencies (15% COD and 8% TS). Organic and aluminium coagulants showed better results than ferric coagulants. Coagulant removal efficiencies were between 9% and 17% for COD and between 10% and 15% for TS. Doses of 1 ml/l of coagulant were preferred. Some combinations of coagulant and flocculant enhanced the process. The best combinations obtained were FeCl3+A30.L, Ferriclar+A20.L, SAL8.2+A30.L and PAX-18+A30.L, which presented COD removal efficiencies between 24% and 37% with doses between 10 and 18 ml/l. Keywords: landfill leachate, coagulation-flocculation, submerged biological filter pre-treatment. Waste Management and the Environment II, V. Popov, H. Itoh, C.A. Brebbia & S. -
Integrated Leaching and Separation of Metals Using Mixtures of Organic Acids and Ionic Liquids
molecules Article Integrated Leaching and Separation of Metals Using Mixtures of Organic Acids and Ionic Liquids Silvia J. R. Vargas, Helena Passos , Nicolas Schaeffer * and João A. P. Coutinho CICECO-Aveiro Institute of Materials, Department of Chemistry, University of Aveiro, 3810-193 Aveiro, Portugal; [email protected] (S.J.R.V.); [email protected] (H.P.); [email protected] (J.A.P.C.) * Correspondence: nicolas.schaeff[email protected] Academic Editors: Magdalena Regel-Rosocka and Isabelle Billard Received: 4 November 2020; Accepted: 25 November 2020; Published: 27 November 2020 Abstract: In this work, the aqueous phase diagram for the mixture of the hydrophilic tributyltetradecyl phosphonium ([P44414]Cl) ionic liquid with acetic acid (CH3COOH) is determined, and the temperature dependency of the biphasic region established. Molecular dynamic simulations of the [P44414]Cl + CH3COOH + H2O system indicate that the occurrence of a closed “type 0” biphasic regime is due to a “washing-out” phenomenon upon addition of water, resulting in solvophobic segregation of the [P44414]Cl. The solubility of various metal oxides in the anhydrous [P44414]Cl + CH3COOH system was determined, with the system presenting a good selectivity for CoO. Integration of the separation step was demonstrated through the addition of water, yielding a biphasic regime. Finally, the [P44414]Cl + CH3COOH system was applied to the treatment of real waste, NiMH battery black mass, being shown that it allows an efficient separation of Co(II) from Ni(II), Fe(III) and the lanthanides in a single leaching and separation step. Keywords: critical metals; process intensification; metal leaching; solvent extraction; solvometallurgy 1. Introduction Solvometallurgy, the extraction of metals from primary and secondary sources using solutions containing less than 50 vol. -
A Basic Chloride Method for Extracting Aluminum from Clay
(k Bureau of Mines Report of investigations/l984 A Basic Chloride Method for Extracting Aluminum From Clay By P. R. Bremner, L. J. Nicks, and D. J, Bauer UNITED STATES DEPARTMENT OF THE INTERIOR Report of Investigations 8866 A Basic Chloride Method for Extracting Aluminum From Clay By P. R. Bremner, L. J. Nicks, and D. J. Bauer UNITED STATES DEPARTMERIT OF THE INTERIOR William P. Clark, Secretary BUREAU OF MINES Robert C. Worton, Director Library of Congress Cataloging in Publication Data: Bremner, P, R. (Paul R,) A basic chloride method for extracting aluminum from clay. (Bureau of Mines report of investigations ; 8866) Bibliography: p. 8. Supt. of Docs. no.: I 28.23:8866. 1. Alumit~urn-Metallurgy. 2. Leaching. 3. Chlorides. 4, Kao- linite, I. Nicks, 1;. J. (Larry J.), 11. Bauer, D. J. (Donald J,). 111. Title. IV. Series: Report of investigations (United States. Bureau of TN23.U43 [TN776] 622s [669'.722] 84-600004 CONTENTS .Page Abstract ....................................................................... 1 Introduction ................................................................... 2 Materials. equipment. and procedures .......O.O...........,............... 3 Results and discussion........................................................b 3 Effects of calcination time and temperature .................................. 3 Single-stage leaching and crystallization... ................................. 4 Countercurrent leaching and crystallization.................................. 5 Purification and solubility studies ........................*................ -
Lecture 08: Leaching and Extraction
Mass transfer Lecture 08: Leaching and extraction Jamin Koo 2019. 10. 10 1 Learning objectives • Understand when leaching would be a more preferred, effective separation method. • Analyze cascades leaching using the material balance equation and associated graphs. • Determine when liquid extraction will be preferred versus distillation. 2 Today’s outline • Leaching Introduction Leaching equipment, dispersed solid leaching Cascades leaching, equilibrium analysis Variable underflow Ex. 23.1 • Liquid extraction Introduction Terminology and types 3 23.1 Introduction to Leaching • Definition: method of removing one constituent from a solid or liquid by means of a liquid solvent • Examples In chemical process In daily life 4 23.1 Mass transport • Generally there are five rate steps in the leaching process. (1) The solvent is transferred from the bulk solution to the surface of the solid. (fast) (2) The solvent penetrates or diffuses into the solid. (slow) (3) The solute dissolves from the solid into the solvent. (slow) (4) The solute diffuses through the mixture to the surface of the solid. (5) The solute is transferred to the bulk solution. 5 23.1 Leaching equipment • Generally, two types are used with respect to whether or not the mixture (often solid) is permeable. When working with permeable mass, percolation through stationary solid beds may be used. What will impact percolation? What will impact leaching? 6 23.1 Leaching equipment • Generally, two types are used with respect to whether or not the mixture (often solid) is permeable. When working with impermeable mass, solids are dispersed into the solvent and are later separated from it. e.g., moving-bed leaching 7 23.1 Dispersed-solid leaching • Solid is dispersed in the solvent by mechanical agitation in a tank or flow mixer. -
Manufacturing of Agarose-Based Chromatographic Media with Controlled Pore and Particle Size
MANUFACTURING OF AGAROSE-BASED CHROMATOGRAPHIC MEDIA WITH CONTROLLED PORE AND PARTICLE SIZE by Nicolas Ioannidis A thesis submitted to The University of Birmingham for the degree of DOCTOR OF PHILOSOPHY School of Chemical Engineering College of Engineering and Physical Sciences The University of Birmingham 2009 University of Birmingham Research Archive e-theses repository This unpublished thesis/dissertation is copyright of the author and/or third parties. The intellectual property rights of the author or third parties in respect of this work are as defined by The Copyright Designs and Patents Act 1988 or as modified by any successor legislation. Any use made of information contained in this thesis/dissertation must be in accordance with that legislation and must be properly acknowledged. Further distribution or reproduction in any format is prohibited without the permission of the copyright holder. ABSTRACT Chromatography remains the most commonly employed method for achieving high resolution separation of large-sized biomolecules, such as plasmid DNA, typically around 150-250 nm in diameter. Currently, fractionation of such entities is performed using stationary phases designed for protein purification, typically employing pore sizes of about 40 nm. This results into a severe underexploitation of the porous structure of the adsorbent as adsorption of plasmid DNA occurs almost exclusively on the outer surface of the adsorbent. In this study, the effect of two processing parameters, the ionic strength of agarose solution and quenching temperature, on the structure of the resulting particles was investigated. Three characterization methods, Atomic Force and cryo-Scanning Electron microscopy, as well as mechanical testing of single particles where used to quantify the effect of these parameters on the pore size/size distribution and mechanical properties of the adsorbent. -
EXPRESSION, PURIFICATION and CRYSTALLIZATION TRIALS of SMALL RUBBER PARTICLE PROTEIN (SRPP) from Hevea Brasiliensis
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Repository@USM EXPRESSION, PURIFICATION AND CRYSTALLIZATION TRIALS OF SMALL RUBBER PARTICLE PROTEIN (SRPP) FROM Hevea brasiliensis SARANPAL SINGH A/L SATINDER SINGH UNIVERSITI SAINS MALAYSIA EXPRESSION, PURIFICATION AND CRYSTALLIZATION TRIALS OF SMALL RUBBER PARTICLE PROTEIN (SRPP) FROM Hevea brasiliensis by SARANPAL SINGH A/L SATINDER SINGH Thesis submitted in fulfillment of requirements for the degree of Master of Science February ACKNOWLEDGEMENT I owe my highest gratitude to Professor Dr. K. Sudesh Kumar and Dr. Teh Aik Hong for being my true mentors and for always being available when needed. My gratitude goes to them for their thoughtful insights, motivation, patience, professional rigour, and intellectual contributions. I could not have imagined having better advisors and mentors during the pursuit of my master’s degree. Their meticulous reading and critical comments on my drafts gave me the kind of feedback that always revitalized, encouraged, and propelled me forward with enthusiasm. It is an honor to have work with them. I am indebted and grateful for the encouragement and inspiration shared by my lab mates and post-docs at CCB: Chiam Nyet Cheng, Chung Corrine, Jess Loh Swee Cheng, Sam Ka Kei, Yue Keong Choon, Tengku Yasmin, Sim Pei Fang, Dr. Go Furusawa, Dr. Sheri-Ann Tan, Dr. Suganthi Appalasamy, Dr. Lau Nyok Sean, Dr.Farrukh Jamil, Dr. Abhilash Usharraj, and Dr. Gincy Paily Thottahil. I also appreciate the help of the administrative department of CCB for being helpful: Ms. Tengku Zalina Tengku Ahmad, Cik Nurul Farhana Che Hassan, and Ms. -
WO 2015/094804 Al 25 June 2015 (25.06.2015) P O P C T
(12) INTERNATIONAL APPLICATION PUBLISHED UNDER THE PATENT COOPERATION TREATY (PCT) (19) World Intellectual Property Organization International Bureau (10) International Publication Number (43) International Publication Date WO 2015/094804 Al 25 June 2015 (25.06.2015) P O P C T (51) International Patent Classification: (74) Agent: HEMENWAY, Carl; The Dow Chemical Com C13B 50/00 (201 1.01) BOW 61/14 (2006.01) pany, Intellectual Property, P.O. Box 1967, Midland, BOW 61/02 (2006.01) Michigan 48641-1967 (US). (21) International Application Number: (81) Designated States (unless otherwise indicated, for every PCT/US20 14/069248 kind of national protection available): AE, AG, AL, AM, AO, AT, AU, AZ, BA, BB, BG, BH, BN, BR, BW, BY, (22) International Filing Date: BZ, CA, CH, CL, CN, CO, CR, CU, CZ, DE, DK, DM, ' December 2014 (09.12.2014) DO, DZ, EC, EE, EG, ES, FI, GB, GD, GE, GH, GM, GT, (25) Filing Language: English HN, HR, HU, ID, IL, IN, IR, IS, JP, KE, KG, KN, KP, KR, KZ, LA, LC, LK, LR, LS, LU, LY, MA, MD, ME, MG, (26) Publication Language: English MK, MN, MW, MX, MY, MZ, NA, NG, NI, NO, NZ, OM, (30) Priority Data: PA, PE, PG, PH, PL, PT, QA, RO, RS, RU, RW, SA, SC, 61/917,508 18 December 201 3 (18. 12.2013) US SD, SE, SG, SK, SL, SM, ST, SV, SY, TH, TJ, TM, TN, TR, TT, TZ, UA, UG, US, UZ, VC, VN, ZA, ZM, ZW. (71) Applicants: DOW GLOBAL TECHNOLOGIES LLC [US/US]; 2040 Dow Center, Midland, Michigan 48674 (84) Designated States (unless otherwise indicated, for every (US). -
Flocculating Cations
Effect of Reclaimed Water on Desert Soil Dr. Jim Walworth Department of Soil, Water and Environmental Science University of Arizona Reclaimed Water • Let’s separate impacts of reclaimed water on soil from effects on people or on growing plants – Pathogens may impact people – Plants can be directly affected by salts, nutrients, specific ion toxicities, and indirectly by soil physical properties – Soil physical properties can be affected by salt and sodium • In this presentation, we’re only going to consider impacts on soil physical properties, not on plant growth or people Soil clay particles can be unattached to one another (dispersed) or clumped together (flocculated). Dispersed Particles Flocculated Particles Flocculation is important because water moves mostly in large pores between aggregates. Also, plant roots grow mainly between aggregates. When empty, these large pores supply oxygen to roots and soil microbes. In all but the sandiest soils, dispersed clays plug soil pores and impede water infiltration and soil drainage. Why do soils flocculate? Why do soils disperse? To answer these questions, we need to understand something about the nature of soil clay particles. Most clay particles have a negative electrical charge. Like charges repel, so clay particles repel one another. Negatively charged Negatively charged clay particle clay particle Cations (positively charged molecules) can make clay particles stick together (flocculate). Some cations are very good flocculators, others are not so effective. ++ Negatively charged Negatively -
Differences Between Homogeneous Spermidine Synthases Isolated
J. Biochem. 96, 1273-1281 (1984) Differences between Homogeneous Spermidine Synthases Isolated from Rat and Pig Liver1 Banri YAMANOHA,* Keijiro SAMEJIMA,*,z Terumi NAKAJIMA,** and Tadashi YASUHARA** *Tokyo Biochemical Research Institute , Takada, Toshima-ku, Tokyo 171, and **Institute for Medical and Dental Engineering, Tokyo Medical and Dental University, Kandasurugadai, Chiyoda-ku, Tokyo 101 Received for publication, May 25, 1984 Spermidine synthase was purified to homogeneity from rat and pig liver by a method modified from a previously reported one using DEAE-Sepharose, S-adenosyl(5•Œ)- 3-thiopropylamine-Sepharose affinity chromatography, Sephacryl S-300 gel filtration and polyacrylamide gel electrophoresis. No apparent difference between the two enzymes was observed in specific activity, molecular weight (74,000), or subunit composition (two subunits). However, significant differences were observed in their pI values, which were 5.16 for the pig enzyme and 5.34 for the rat enzyme, and their peptide maps. Amino acid compositions of the two enzymes were closely related, but differed significantly in some amino acids. In addition, the rat enzyme was more sensitive to inhibition by S-adenosyl-1,8-diamino-3-thiooctane than the pig enzyme. Spermidine synthase [EC 2.5.1.16] catalyzes the On the other hand, a recent report (4) has shown transfer of the propylamine moiety from S-adeno that there were significant differences among sper syl(5•Œ)-3-methylthiopropylamine (decarboxy Ado midine synthases from different bacterial species Met) to putrescine to form spermidine. The en and rat ventral prostate in their responses to two zyme has been purified to homogeneity from potent spermidine synthase inhibitors, S-adenosyl- Escherichia coli (1), rat prostate (2), and bovine 1,8-diamino-3-thiooctane (AdoDATO) (5, 6) and brain (3); each has shown very similar properties dicyclohexylamine (7). -
Leaching and Solvent Extraction Purification of Zinc from Mehdiabad
www.nature.com/scientificreports OPEN Leaching and solvent extraction purifcation of zinc from Mehdiabad complex oxide ore Faraz Soltani1, Hossna Darabi2, Reza Aram3 & Mahdi Ghadiri4,5* An integrated hydrometallurgical process was used for the zinc leaching and purifcation from a zinc ore containing 9.75 wt% zinc. The zinc minerals in the ore were hemimorphite, willemite, and calcophanite. Main gangue minerals were quartz, goethite, hematite, and calcite. Central composite design (CCD) method was used to design leaching experiments and the optimum conditions were found as follows: 30% of solid fraction, 22.05% sulphuric acid concentration, and the leaching temperature of 45 °C. The PLS containing 35.07 g/L zinc, 3.16 g/L iron, and 4.58 g/L manganese impurities was produced. A special purifcation process including Fe precipitation and Zn solvent extraction was implemented. The results showed that after precipitation of iron, Zn extraction of 88.5% was obtained with the 2 stages extraction system composed of 30 vol% D2EHPA as extractant. The overall Zn recovery from the ore was 71.44%. Therefore, an appropriate solution containing 16.6 g/L Zn, 0.05 g/L Fe, and 0.11 g/L Mn was prepared for the electro-winning unit without using the roasting and calcination steps (conventional method), which result in environmental pollution. Te importance of zinc oxide ores processing such as carbonate and silicates minerals have increased because of the depletion of zinc sulphide ores and the restriction on sulphur emissions during their processing 1–6. Te zinc oxide ores usually contain several diferent minerals including zincite (ZnO), smithsonite (ZnCO 3), hydrozincite 2 (2ZnCO3·3Zn(OH)), hemimorphite (Zn 4Si2O7(OH)2·H2O), and willemite (Zn 2SiO4) . -
Leaching of Chalcopyrite Under Bacteria–Mineral Contact/Noncontact Leaching Model
minerals Article Leaching of Chalcopyrite under Bacteria–Mineral Contact/Noncontact Leaching Model Pengcheng Ma 1,2, Hongying Yang 2,*, Zuochun Luan 1, Qifei Sun 1, Auwalu Ali 2 and Linlin Tong 2 1 Technology Center, Shandong Zhaojin Group Co., Ltd., No.108 Shengtai Road, Zhaoyuan 265400, China; [email protected] (P.M.); [email protected] (Z.L.); [email protected] (Q.S.) 2 School of Metallurgy, Northeastern University, 3-11 Wenhua Road, Shenyang 110819, China; [email protected] (A.A.); [email protected] (L.T.) * Correspondence: [email protected] Abstract: Bacteria–mineral contact and noncontact leaching models coexist in the bioleaching process. In the present paper, dialysis bags were used to study the bioleaching process by separating the bacteria from the mineral, and the reasons for chalcopyrite surface passivation were discussed. The results show that the copper leaching efficiency of the bacteria–mineral contact model was higher than that of the bacteria–mineral noncontact model. Scanning electron microscopy (SEM), X-ray diffraction (XRD), and Fourier-transform infrared (FTIR) were used to discover that the leaching process led to the formation of a sulfur film to inhibit the diffusion of reactive ions. In addition, the deposited jarosite on chalcopyrite surface was crystallized by the hydrolysis of the excess Fe3+ ions. The depositions passivated the chalcopyrite leaching process. The crystallized jarosite in the bacteria EPS layer belonged to bacteria–mineral contact leaching system, while that in the sulfur films belonged to the bacteria–mineral noncontact system. Citation: Ma, P.; Yang, H.; Luan, Z.; Keywords: chalcopyrite; bacteria leaching; passivation; jarosite Sun, Q.; Ali, A.; Tong, L.