The Leaching and Passivation of Chalcopyrite in Acid

Total Page:16

File Type:pdf, Size:1020Kb

The Leaching and Passivation of Chalcopyrite in Acid THE LEACHING AND PASSIVATION OF CHALCOPYRITE IN ACID SULFATE MEDIA by RALPH PETER HACKL B.Sc.(Hons.), The University of British Columbia, 1977 M.Sc, The University of British Columbia, 1983 A THESIS SUBMITTED IN PARTIAL FULFILLMENT OF THE REQUIREMENTS FOR THE DEGREE OF DOCTOR OF PHILOSOPHY in THE FACULTY OF GRADUATE STUDIES Department of Metals and Materials Engineering We accept this thesis as conforming to the required standard THE UNIVERSITY OF BRITISH COLUMBIA November 1995 © Ralph Peter Hackl, 1995 In presenting this thesis in partial fulfillment of the requirements for an advanced degree at the University of British Columbia, I agree that the library shall make it freely available for reference and study. I further agree that permission for extensive copying of this thesis for scholarly purposes may be granted by the head of my department or by his or her representatives. It is understood that copying or publication of this thesis for financial gain shall not be allowed without my written permission. Department of Metals and Materials Engineering The University of British Columbia Vancouver, B.C., Canada Date: HoVe^bvr 20, 199$ ABSTRACT Sulfate-based leaching processes for chalcopyrite (CuFeSa) are attractive because of their inherent simplicity. Unfortunately, high copper extractions are not attainable in a reasonable residence time unless the leaching temperature exceeds 200°C (oxygen pressure leaching) or chalcopyrite is "activated" by a pretreatment method prior to leaching. In the present work, the oxygen pressure leaching behaviour of chalcopyrite in the temperature range 110-220°C was studied to shed new light on the reasons for the slow leaching. At temperatures where molten elemental sulfur is stable (120-180°C), the reaction was found to be prematurely stifled by liquid sulfur formed during leaching. The liquid sulfur wetted and agglomerated the unreacted mineral particles, effectively stopping the leach at 40-70% copper extraction. The feasibility of using surfactants to disperse the sulfur and enhance the copper extraction in the temperature range 125-155°C was investigated. Most of the surfactants tested decomposed too rapidly to be of benefit. The best results were obtained with orthophenylenediamine (OPD) when it was added continuously at a low temperature (125°C) and a high dosage (50 kg/t). Under these conditions the surfactant was successful in dispersing liquid sulfur and it effected a modest increase in copper extraction over that obtained at 110°C, but only after prolonged retention times (6 hours). It was found that chalcopyrite leached slowly even if molten sulfur was prevented from wetting the mineral surfaces. This led to the conclusion that the reaction rate is ultimately controlled by a passivating mechanism unrelated to elemental sulfur formation. Oxidized chalcopyrite mineral surfaces were examined by Auger electron spectroscopy and X-ray photoelectron spectroscopy to identify the presence of any passivating layers that may form during leaching. The results indicated that an iron-deficient, copper-rich sulfide layer forms on the surface of chalcopyrite as a result of solid state changes that occur in the mineral during leaching. This layer is thought to be a copper polysulfide, CuSn, where n > 2. The layer is quite thin (-10-100 nm) and hence is not detectable by conventional electron microscopy. The copper polysulfide is believed to passivate the chalcopyrite. The addition of silver ions at a temperature below the sulfur melting point (110°C) was found to catalyze the leach, resulting in the copper extraction increasing from 53% to 96% after -111- 3 hours leaching. Silver alone was ineffective at 125°C and 155°C because the leach was stifled by liquid sulfur. However, when silver was used in conjunction with OPD at 125°C the copper extraction was again enhanced significantly, to 91%. The OPD prevented the sulfur from wetting the mineral surfaces, allowing the catalytic effect of the silver ions to be maintained. A simple mathematical model was formulated to explain the leaching and passivation of chalcopyrite at low temperature (110°C). The reaction kinetics can be explained in terms of a mixed diffusion/chemical reaction model where the reaction rate is initially dependent on the rate at which copper and iron diffuse through the thickening passive layer. The passive layer also leaches, but at a slower rate than the chalcopyrite. Eventually, the passive layer reaches a steady state thickness and the kinetics are then controlled by the rate at which the passivating layer decomposes. The linear rate constant k\ for the decomposition of the passive layer was calculated to be 5.0x10"3 um/min. The low value of k\ explains why inordinately long residence times are required to obtain a high copper extraction from chalcopyrite at 110°C. -iv- TABLE OF CONTENTS ABSTRACT ii TABLE OF CONTENTS iv List of Tables viii List of Figures x List of Symbols xiv ACKNOWLEDGEMENTS xvii CHAPTER 1 - INTRODUCTION 1 CHAPTER 2 - LITERATURE REVIEW 4 2.1 Elemental Sulfur 4 2.1.1 Properties of Elemental Sulfur Allotropes 4 2.1.2 Aqueous Oxidation of Elemental Sulfur in Acid Sulfate Media 6 2.2 Properties of Chalcopyrite 10 2.2.1 Crystal Structure 10 2.2.2 Thermodynamic Considerations 11 2.3 Leaching of Chalcopyrite in Sulfate Media 14 2.3.1 Ferric Sulfate Leaching 14 2.3.2 Oxygen Pressure Leaching 16 2.3.3 Bioleaching 19 2.4 Passivation of Chalcopyrite 22 2.4.1 Electrochemical Studies 22 2.4.2 Surface Studies 26 2.5 Activation of Chalcopyrite 29 2.5.1 Thermal Activation 29 2.5.2 Mechanical Activation 31 2.5.3 Chemical Activation with Silver Ions 32 2.6 Use of Sulfur Dispersing Surfactants in Leaching 34 2.6.1 Overview of Surfactant Properties in Mineral-Aqueous Media 34 2.6.2 Surfactants in Oxygen Pressure Leaching of Zinc Concentrates 38 2.6.3 Surfactants in Oxygen Pressure Leaching of Nickeliferous Pyrrhotite Concentrates 40 2.6.4 Surfactants in Pressure Oxidation of Refractory Gold Ores and Concentrates 42 2.7 Conclusions and Focus of the Present Study 44 CHAPTER 3 - BASIC PRINCIPLES OF AUGER ELECTRON SPECTROSCOPY AND X-RAY PHOTOELECTRON SPECTROSCOPY 46 3.1 Introduction 46 3.2 Notation used in AES and XPS 47 3.3 Auger Electron Spectroscopy 47 3.3.1 The Auger Process 47 3.3.2 Properties of Auger Electrons 49 -V- 3.3.3 Generation and Interpretation of Auger Spectra 50 3.3.4 Strengths and Limitations of AES 51 3.4 X-ray Photoelectron Spectroscopy 52 3.4.1 The XPS Process 52 3.4.2 Properties of Photoelectrons 53 3.4.3 Generation and Interpretation of XPS Spectra 53 3.4.3.1 Core Level Emission Peaks 54 3.4.3.2 X-ray-Excited Auger Emission Peaks 55 3.4.3.3 Secondary Peaks 56 3.4.3.4 Quantification 57 3.4.4 Strengths and Limitations of XPS 57 3.5 Sputter Depth Profiling 57 CHAPTER 4 - EXPERIMENTAL PROCEDURES 59 4.1 Interfacial Experiments 59 4.1.1 Reagents 59 4.1.2 Surfactants 59 4.1.3 Chalcopyrite Mineral 61 4.1.4 Apparatus 61 4.1.5 Formation of Pendant Drops 63 4.1.6 Formation of Sessile Drops 64 4.1.7 Determination of the Aqueous Solution Density at Elevated Temperature 65 4.1.8 Determination of Interfacial Tensions and Contact Angles 66 4.1.8.1 Interfacial Tensions by the Method of the Selected Plane 66 4.1.8.2 Manual Measurement of Contact Angles 67 4.1.8.3 Axisymmetric Drop Shape Analysis 68 4.1.9 Determination of Work of Adhesion Values 69 4.2 Oxygen Pressure Leaching Experiments 69 4.2.1 Reagents 69 4.2.2 Mineral Samples 70 4.2.2.1 Gibraltar Copper Concentrate 70 4.2.2.2 Messina Chalcopyrite 70 4.2.2.3 Covellite 71 4.2.3 Particle Size Analyses of the Mineral Samples 72 4.2.3.1 Sieve Analyses 72 4.2.3.2 Particle Size Analysis with the Elzone Particle Size Counter 73 4.2.3.3 Particle Size Analysis with the Horiba Photosedimentation Instrument.. 73 4.2.4 Surfactants , 74 4.2.5 Pressure Leaching Apparatus and Procedures 74 4.2.6 Analytical Methods 77 4.2.7 Calculation of Metal Extractions and Sulfide Oxidation Extents 78 4.3 Analysis of Chalcopyrite Surfaces 79 4.3.1 Sample Preparation 79 4.3.2 Auger Electron Spectroscopy Procedures 80 4.3.3 X-ray Photoelectron Spectroscopy Procedures 80 CHAPTER 5 - RESULTS AND DISCUSSION 82 5.1 Interfacial Experiments 82 -vi- 5.1.1 Effect of Surfactants on the Sulfur-Solution Interfacial Tension 82 5.1.2 Effect of Surfactants on the Sulfur-Chalcopyrite Contact Angle....'. 83 5.1.3 Effect of Surfactants on the Work of Adhesion 86 5.1.4 Discussion 87 5.1.4.1 Surfactants and Sulfur-Solution Interfacial Tensions 87 5.1.4.2 Surfactants and Sulfur-Chalcopyrite Contact Angles 88 5.1.4.3 Possible Surfactant-Chalcopyrite and Surfactant-Sulfur Bonding Interactions 90 5.2 Pressure Leach Experiments 91 5.2.1 Effect of Temperature on Chalcopyrite Reaction Kinetics and Sulfur Yield .... 91 5.2.2 Effect of Liquid Sulfur on Chalcopyrite Oxidation 96 5.2.3 Preliminary Evaluation of Surfactants in Pressure Leaching Tests 103 5.2.4 Effect of Continuous Surfactant Addition at High Pulp Density 105 5.2.5 Effect of Batch and Continuous Surfactant Additions at Low Pulp Density... 106 5.2.6 Effect of Surfactants In Silver Catalyzed Oxygen Pressure Leaching 108 5.2.6.1 Effect of Silver in the Absence of Surfactants 110 5.2.6.2 Effect of Silver in the Presence of Surfactants 113 5.2.7 Discussion 115 5.3 Surface Characterization Experiments 117 5.3.1 Auger Electron Spectroscopy Results 117 5.3.1.1 Spectral Features 117 5.3.1.2 Surface Composition Results 119 5.3.1.3 Sputter Depth Profiling Results 120 5.3.2 X-ray Photoelectron Spectroscopy Results 123 5.3.2.1 GeneralFeatures of Broad-Scan Spectra 123 5.3.2.2
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]