Reducing Protein a Leaching During Protein a Affinity Chromatography

Total Page:16

File Type:pdf, Size:1020Kb

Reducing Protein a Leaching During Protein a Affinity Chromatography (19) TZZ¥Z¥_T (11) EP 3 095 793 A1 (12) EUROPEAN PATENT APPLICATION (43) Date of publication: (51) Int Cl.: 23.11.2016 Bulletin 2016/47 C07K 16/06 (2006.01) (21) Application number: 16164203.8 (22) Date of filing: 24.06.2004 (84) Designated Contracting States: • McDONALD, Paul J. AT BE BG CH CY CZ DE DK EE ES FI FR GB GR San Francisco, CA 94133 (US) HU IE IT LI LU MC NL PL PT RO SE SI SK TR • O’LEARY, Rhona M. Designated Extension States: San Francisco, CA 94127 (US) AL HR LT LV MK (74) Representative: Kiddle, Simon John et al (30) Priority: 28.07.2003 US 490500 P Mewburn Ellis LLP City Tower (62) Document number(s) of the earlier application(s) in 40 Basinghall Street accordance with Art. 76 EPC: London EC2V 5DE (GB) 04777121.7 / 1 648 940 Remarks: (71) Applicant: GENENTECH, INC. •This application was filed on 07-04-2016 as a South San Francisco, CA 94080-4990 (US) divisional application to the application mentioned under INID code 62. (72) Inventors: •Claims filed after the date of filing of the application • FAHRNER, Robert L. / after the date of receipt of the divisional application San Mateo, CA 94403 (US) (Rule 68(4) EPC). • LAVERDIERE, Amy San Francisco, CA 94107 (US) (54) REDUCING PROTEIN A LEACHING DURING PROTEIN A AFFINITY CHROMATOGRAPHY (57) A method for reducing leaching of protein A during protein A affinity chromatography is described which involves reducing temperature of pH of, or by adding one or more protease inhibitors to, a composition that is subject to protein A affinity chromatography. EP 3 095 793 A1 Printed by Jouve, 75001 PARIS (FR) EP 3 095 793 A1 Description [0001] This is a non-provisional application claiming priority under 35 USC §19 to provisional aplication number 60/490, 500 filed July 28, 2003, the entire disclosure of which is hereby incorporated by reference. 5 BACKGROUND OF THE INTENTION Field of the Invention 10 [0002] The present invention concerns protein purification. In particular, the invention concerns a method for reducing leaching of protein A during protein A affinity chromatography by reducing temperature or pH of, or by adding one or more protease inhibitors to, a composition that is subjected to protein A affinity chromatography. Description of Related Art 15 [0003] The large-scale, economic purification of proteins is increasingly an important problem for the biotechnology industry. Generally, proteins are produced by cell culture, using either mammalian or bacterial cell lines engineered to produce the protein of interest by insertion of a recombinant plasmid containing the gene for that protein. Since the cell lines used are living organisms, they must be fed with a complex growth medium, containing sugars, amino acids, and 20 growth factors, usually supplied from preparations of animal serum. Separation of the desired protein from the mixture of compounds fed to the cells and from the by-products of the cells themselves to a purity sufficient for use as a human therapeutic poses a formidable challenge. [0004] Procedures for purification of proteins from cell debris initially depend on the site of expression of the protein. Some proteins can be caused to be secreted directly from the cell into the surrounding growth media; others are made 25 intracellularly. For the latter proteins, the first step of a purification process involves lysis of the cell, which can be don e by a variety of methods, including mechanical shear, osmotic shock, or enzymatic treatments. Such disruption releases the entire contents of the cell into the homogenate, and in addition produces subcellular fragments that are difficult to remove due to their small size. These are generally removed by differential centrifugation or by filtration. The same problem arises, although on a smaller scale, with directly secreted proteins due to the natural death of cells and release 30 of intracellular host cell proteins in the course of the protein production run. [0005] Once a clarified solution containing the protein of interest has been obtained, its separation from the other proteins produced by the cell is usually attempted using a combination of different chromatography techniques. These techniques separate mixtures of proteins on the basis of their charge, degree of hydrophobicity, or size. Several different chromatography resins are available for each of these techniques, allowing accurate tailoring of the purification scheme 35 to the particular protein involved. The essence of each of these separation methods is that proteins can be caused either to move at different rates down a long column, achieving a physical separation that increases as they pass further down the column, or to adhere selectively to the separation medium, being then differentially eluted by different solvents. In some cases, the desired protein is separated from impurities when the impurities specifically adhere to the column, and the protein of interest does not, that is, the protein of interest is present in the "flow-thraugh." 40 [0006] Affinity chromatography, which exploits a specific interaction between the protein to be purified and an immo- bilized capture agent, may also be an option for some proteins. Protein A is a useful adsorbent for affinity chromatography of proteins, such as antibodies, which contain an Fc region. Protein A is a 41 kD cell wall protein from Staphylococcus aureas which binds with a high affinity (about 10 -8M to human IgG) to the Fc region of antibodies. [0007] US Patent Nos. 6,127,526 and 6,333,398 (Blank, G.) describe an intermediate wash step during protein A 45 affinity chromatography using hydrophobic electrolytes, e.g., tetramethylammonium chloride (TMAC) and tetraethylam- monium chloride (TEAC), to remove the impurities, but not the immobilized protein A or the protein of interest, bound to the protein A column. SUMMARY OF THE INVENTION 50 [0008] The present invention concerns a method of purifying a protein which comprises a C H2/CH3 region, comprising reducing the temperature of a composition comprising the protein and one or more impurities subjected to protein A affinity chromatography in the range from about 3°C to about 20°C, wherein protein A leaching is reduced. [0009] Preferably the protein is an antibody, e.g. one which binds an antigen selected from the group consisting of 55 HER2, vascular endothelial growth factor (VEGF), IgE, CD20, CD40, CD11a, tissue factor (TF), prostate stem cell antigen (PSCA), interleukin-8 (IL-8), epidermal growth factor receptor (EGFR), HER3, HER4, α4β7 or α5β3. In another embod- iment, the protein is an immunoadhesin, such as a TNF receptor immunoadhesin. [0010] The invention also concerns a method of purifying a protein which comprises a CH2/CH3 region by protein A 2 EP 3 095 793 A1 affinity chromatography comprising: (a) subjecting the protein to protein A affinity chromatography and measuring leached protein A in a composition comprising the protein which is recovered from the protein A affinity chromatography; 5 (b) if protein A leaching is detected in step (a), reducing the temperature of a composition comprising the protein and one or more impurities subjected to protein A affinity chromatography in the range from about 3°C to about 20°C, such that protein A leaching is reduced. [0011] The invention further provides a method for reducing leaching of protein A during protein A affinity chromatog- 10 raphy comprising reducing protease activity in a composition subjected to protein A affinity chromatography, wherein the composition comprises a protein which comprises a CH2/CH3 region and one or more proteases. Brief description of the Drawings 15 [0012] Figure 1 depicts protein A leaching as a function of temperature for various antibody products on PROSEP A™. Leached protein A is shown in ng/mg (ng protein A per mg antibody). Temperature on the x-axis refers to the temperature of the water bath. The column was equilibrated and washed with 25 mM Tris, 25mM NaCl, 5mM EDTA, 20 pH 7.1, washed with 25 mM Tris, 25 mM NaCl, 0.5 M TMAC, 5 mM EDTA pH 5.0 or 7.1, eluted with either 25 mM citrate pH 2.8, or 0.1 M acetic acid pH 2.9, regenerated with 0.1 M phosphoric acid, and stored in 0.2 M sodium acetate, 2 % benzyl alcohol pH 5.0. Trastuzumab was run on a bed height of 20 cm, loaded to 20 g Trastuzumab/ L resin, washed with TMAC pH 5.0, eluted with 25 mM citrate pH 2.8, and pooled from 0.1 AU to 2 CV’s. Humanized 2C4 was run on a 20 cm bed height column, loaded to 15 g humanized 2C4 per liter resin, washed with TMAC pH 25 7.1, eluted with 25 mM citrate pH 2.8, and pooled from 0.1 AU to 2 CV’s pool volume. Humanized VEGF antibody was run on 14cm bed height, loaded to 20 g humanized VEGF antibody per liter of resin, washed with TMAC pH 5.0, eluted with 0.1 M acetic acid pH 2.9, and pooled from 0.2 AU to 2 CV’s pool volume. Humanized CD11 a antibody was run on a 14 cm bed height, loaded to 20 g humanized CD11 a antibody per liter of resin, washed with TMAC pH 7.1, eluted with 0.1M acetic acid pH2.9, and pooled from 0.2 AU to 2CV’s. 30 Figure 2 depicts a comparison of temperature dependent protein A leaching from PROSEP A™ and PROSEP vA™ with Trastuzumab, humanized 2C4, and humanized CD11a antibody. Leached protein A is shown in ng/mg (ng protein A per mg antibody). Temperature on the x-axis refers to the temperature of the water bath.
Recommended publications
  • 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.
    [Show full text]
  • PROTEIN a CHROMATOGRAPHY – the PROCESS ECONOMICS DRIVER in Mab MANUFACTURING
    PROCESS Application Note PROTEIN A CHROMATOGRAPHY – THE PROCESS ECONOMICS DRIVER IN mAb MANUFACTURING THE OPTIMIZATION OF THE PROTEIN A CAPTURE STEP IN DOWNSTREAM PROCESSING PLATFORMS CAN CONSIDER- ABLY IMPROVE PROCESS EFFICIENCY AND ECONOMICS OF INDUSTRIAL ANTIBODY MANUFACTURING. PARAMETERS LIKE RESIN REUSE AND ITS CAPACITY CONTRIBUTE CONSIDERABLY TO THE PRODUCTION COSTS. THE USE OF A HIGH CAPACITY PROTEIN A RESIN CAN IMPROVE THE PROCESS EFFICIENCY AND ECONOMICS. THIS PAPER PRESENTS THE KEY FEATURES OF A NEW CAUSTIC STABLE PROTEIN A RESIN PROVIDING EXTREMELY HIGH IgG BINDING CAPACITIES. Biopharmaceuticals represent an ever growing important Protein A affinity resins are dominating the Cost of Goods part of the pharmaceutical industry. The market for recom- (COGs) of mAb manufacturing. Bioreactors at the 10.000 L binant proteins exceeded $ 100 billion in 2011 with a scale operating at a titer of about 1g/L typically generate contribution of 45% sales by monoclonal antibodies (mAbs) costs of $ 4-5 million (2). Therefore the Protein A capturing (1). The introduction of the first mAb biosimilars in Europe step is the key driver to improve process economics. Besides raised the competitive pressure in an increasingly crowded the capacity of the resin, life time and cycle numbers market place. The industry faces challenges, such as patent significantly contribute to the production costs in mAb expirations accompanied by approvals of corresponding manufacturing. biosimilars, failures in clinical trials/rejections or the refusal of health insurers to pay for new drugs. Today, the IgG binding capacities of most Protein A resins are in the range of 30-50 g/L, offering significant advantages These challenges force the industry to minimize risk and time- for the processing of high-titer feedstreams when compared to-market and to proceed more cautiously.
    [Show full text]
  • 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.
    [Show full text]
  • 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 ........................*................
    [Show full text]
  • 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.
    [Show full text]
  • 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
    [Show full text]
  • 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) .
    [Show full text]
  • 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.
    [Show full text]
  • Review of Extraction Techniques
    International Journal of Advanced Research in Chemical Science (IJARCS) Volume 6, Issue 3, 2019, PP 6-21 ISSN No. (Online) 2349-0403 DOI: http://dx.doi.org/10.20431/2349-0403.0603002 www.arcjournals.org Review of Extraction Techniques Extraction Methods: Microwave, Ultrasonic, Pressurized Fluid, Soxhlet Extraction, Etc Komal Patel1, Namrata Panchal2, Dr. Pradnya Ingle3* 3Associate Professor Department of Chemical Engineering, Shivajirao S. Jondhale College of Engineering, Dombivli (East), 421201, University of Mumbai, India. *Corresponding Author: Dr. Pradnya Ingle, Associate Professor Department of Chemical Engineering, Shivajirao S. Jondhale College of Engineering, Dombivli (East), 421201, University of Mumbai, India. Abstract: In recent years, variety of Extraction techniques has been introduced for the recovery of organic compounds. Extraction Methods are widely used in various Industries for Separation of components and has wide range of applications. Details of basic theories applicable to types of Extraction such as - Liquid- Liquid Extraction, Solid Phase Extraction, Solid Liquid Extraction and Supercritical Extraction, etc. including the choice of solvent, procedure, respective advantages disadvantages and their applications are explained. Finally, the specific extraction techniques such as Microwave Extraction, Ultrasonic Extraction, Pressurized Fluid Extraction and Soxhlet Extraction along with their applications are also explained. Keywords: Extraction, Liquid-Liquid Extraction, Solid Phase Extraction, Solid Liquid Extraction,
    [Show full text]
  • Leaching in Soil Columns
    OECD/OCDE 312 Adopted : 13 April 2004 OECD GUIDELINES FOR THE TESTING OF CHEMICALS Leaching in Soil Columns INTRODUCTION 1. Man-made chemicals may reach soil directly via deliberate application (e.g. agrochemicals) or via indirect routes (e.g. via waste water → sewage sludge → soil or air → wet/dry deposition). For risk assessment of these chemicals, it is important to estimate their potential for transformation in soil and for movement (leaching) into deeper soil layers and eventually into groundwater. 2. Several methods are available to measure the leaching potential of chemicals in soil under controlled laboratory conditions, i.e. soil thin-layer chromatography, soil thick-layer chromatography, soil column chromatography, and adsorption - desorption measurements (1)(2). For non-ionised chemicals, the n-octanol-water partition coefficient (Pow) allows an early estimation of their adsorption and leaching potential (3)(4)(5). 3. The method described in this Test Guideline is based on soil column chromatography in disturbed soil (see Annex 1 for definition). Two types of experiments are performed to determine (i) the leaching potential of the test substance, and (ii) the leaching potential of transformation products (study with aged residues) in soils under controlled laboratory conditions1. The method is based on existing guidelines (6)(7)(8)(9)(10)(11). 4. An OECD Workshop on soil/sediment selection, held at Belgirate, Italy in 1995 (12) agreed on the number and type of soils for use in this test. It also made recommendations with regard to collection, handling and storage of soil samples for leaching experiments. PRINCIPLE OF THE TEST 5. Columns made of suitably inert material (e.g.
    [Show full text]
  • A White Paper Describing Produced Water from Production of Crude Oil
    AAA WWWhhhiiittteee PPPaaapppeeerrr DDDeeessscccrrriiibbbiiinnnggg PPPrrroooddduuuccceeeddd WWWaaattteeerrr fffrrrooommm PPPrrroooddduuuccctttiiiooonnn ooofff CCCrrruuudddeee OOOiiilll,,, NNNaaatttuuurrraaalll GGGaaasss,,, aaannnddd CCCoooaaalll BBBeeeddd MMMeeettthhhaaannneee Prepared for: U.S. Department of Energy National Energy Technology Laboratory Under Contract W-31-109-Eng-38 Prepared by: Argonne National Laboratory John A. Veil Markus G. Puder Deborah Elcock Robert J. Redweik, Jr. January 2004 Produce Water White Paper i TABLE OF CONTENT Executive Summary............................................................................................................ v 1 Introduction............................................................................................................. 1 1.1 What Is Produced Water? ................................................................................... 1 1.2 Purpose................................................................................................................ 1 1.3 Layout of White Paper........................................................................................ 2 1.4 Acknowledgments .............................................................................................. 2 2 Produced Water Characteristics.............................................................................. 3 2.1 Major Components of Produced Water .............................................................. 3 2.1.1 Produced Water from Oil Production ............................................................
    [Show full text]
  • Leaching Pattern of Phosphate Glass Fertilizers with Different Compositions Under Soxhlet Distillation Conditions
    Cerâmica 66 (2020) 250-255 http://dx.doi.org/10.1590/0366-69132020663792874 250 Leaching pattern of phosphate glass fertilizers with different compositions under Soxhlet distillation conditions (Lixiviação de fertilizantes de vidros de fosfato com diferentes composições em condições de destilação com Soxhlet) B. Mandal1, G. Hazra2*, G. K. Ghosh3, T. Das1 1University of Burdwan, Department of Chemistry, Burdwan-713104, W.B., India 2Kalna College, Department of Chemistry, Kalna-713409, W.B., India 3Visva-Bharati University, Department of Soil Science & Agricultural Chemistry, Sriniketan-731236, W.B., India Abstract Glass fertilizers in the phosphate systems were melted at 900-950 °C with a soaking period of 1 h. Leaching study of these glasses with a maximum time period of 300 h was conducted under Soxhlet distillation condition with distilled water. Weight loss and the leach rates of the glass fertilizer samples were calculated from BET surface area measurements. They were in the range of 6.3x10-3 to 2.3x10-3 g.m-2.h-1 at 90 °C. The effect of different modifier ions like Na+, Fe3+, Mg2+, Ca2+, and K+ in the basic phosphate networks on melting and time of melting has been found to be evident. The pH determination ranging from 4.80 up to 7.50 of the leachate solution at ambient temperature under varying time intervals showed interesting and regular variations. The leaching study of such glasses under Soxhlet condition showed Ca2+, Mg2+, and K+ to be good candidates as modifier towards faster leaching. The findings have been corroborated in terms of ionic size, ionic radius, and hence the ionic potential of the modifier ions incorporated into the glass structure.
    [Show full text]