Mercury Extraction with LIX26 and LIX84 Ionic Exchangers in n-Heptane Project Objective: The goal of the project is to study the capacity of two commercially.

Slides:



Advertisements
Similar presentations
Calibration Techniques
Advertisements

Using C1V1=C2V2.
Removal of Cu(II) ions from aqueous solution effluent using Melamine-Formaldehyde-DTPA resin in a fixed-bed up-flow column By Ahmad Baraka Supervisors.
Adsorption of Dissolved Metals from the Berkeley Pit using Thiol-SAMMS By: Amaury Betancourt, DOE Fellow, Florida International University, Dr. Dawn Wellman,
InfraCal TOG/TPH Analyzer, Model CVH Extraction Procedure.
Stoichiometry: Quantitative Information about chemical reactions.
A STUDY OF THE RATE OF METABOLISM OF CAFFEINE IN URINE PRESENTED BY KATIE COLEMAN AND COLLEEN WALSH.
Concentration of Solutions. Concentrations of Solutions (Section 2.5) Concentration = quantity of solute quantity of solution A solution is dilute if.
Logical In-Vial Dilution with Ultrafiltration for Anion Analysis IC Application Work AW US Presented by Carlos Bazán 1.
Printed by Determination of an Unknown Substance by Titration Larry Sepulveda  Objective: To determine the identity and industrial.
Dilutions. Solve problems involving the dilution of solutions. Include: dilution of stock solutions, mixing common solutions with different volumes and.
Pumpkin Purification Removal of Toxic Metals from an Aqueous Solution Using Curcurbita Agricultural Waste Products Lauren Hodge Dallastown Area High School.
minor address change.
Organic Matter Turnover Root Exudate s Fall or harvest Table 1. Soil characteristics of Burrehøjvej field soil. Sorption of Dissolved Organic C and P to.
Separation Science All separations go against the 2 nd Law of Thermodynamics: entropy increases during any natural process.
Printed by Determination of an Unknown Substance by Titration Larry Sepulveda  Objective: To determine the identity of an unknown.
Copper Ion Analysis Cory Sennett November 15, 2006 CH EN 4903.
<701> DISINTEGRATION
Dilutions. Preparing Dilutions Concentrated solutions that are diluted before use to a specified concentration and volume are frequently used in the laboratory.
InfraCal Ethanol Blend Analyzer Ethanol in Gasoline Sample Analysis for Low Levels
Angelo Harb Mia Simon Austin Moreman Michael Garfagnoli HOW DOES CARBON- BASED ASH AFFECT THE P H OF THE WATER IN THE VAN NORDEN MEADOW?
Section 15.2 Describing Solution Composition 1. To understand mass percent and how to calculate it 2. To understand and use molarity 3. To learn to calculate.
InfraCal Ethanol Blend Analyzer Ethanol in Gasoline Calibration for Low Levels
Solutions used in medical laboratory. O Solution is a homogeneous mixture of two or more substances. O Solute is the dissolved substance, whereas solvent.
Solutions & Solubility Solution Preparation by dilution.
Dilutions.
Potential Changes to Sections and 307.9: Standards Applicability and Attainment Gregg Easley TCEQ Water Quality Standards Team September 6, 2007.
1 Chapter 2 Steps in a chemical analysis Plan of analysis Before doing any quantitative analysis, the following questions should be answered: 1-
MAT 1235 Calculus II Section 9.3 Separable Equations II Version 2
Absorption Spectroscopy CHEM 251 Week of November 1 st, 2010 Alexis Patanarut.
Determination of the Solubility Product K sp of Ca(OH) 2 Experiment 13.
Abstract Quantitative Comparative Analysis of Proteins in three types of Beans: Green Beans, Lima Beans, and Soy Beans By, Ashley Rowles Bean: Correction.
Instrumental Analysis Polarography and Voltammetry
Poster Templates Ionic exchange between Riva Self Cure ® GIC and demineralized dentine Ionic exchange between Riva Self Cure ® GIC.
Titrations. The process of adding measured volumes of an acid or base of known concentrations to an acid or base of unknown concentration until neutralization.
Kinetics of Cadmium ions Adsorption on Tree Fern from Aqueous Solutions Chung-Chi Wang* and Yuh-Shan Ho # School of Public Health, Taipei Medical University.
Elizabeth Keily, Daniel Boehling, Arif M. Sikder, S
Solutions used in medical laboratory
Ionic Equilibria III: The Solubility Product Principle
One-Stage Quantitative
Chemistry 16.2.
Ionic Equilibria: Part II Buffers and Titration Curves
Novel Material for the Removal of PCBs and Mercury from Water
Unit A: Chemistry Topic: Calculating Concentrations
Adsorption capacity study of activated bone carbon to remove yellow dye tartrazine from aqueous solution I. M. Reck, R. M. Paixão, R. Bergamasco, M. F.
Jonas Plauska, Lina Ragelienė, Lina Kubilė
How does the volume of snow compare to the volume of liquid from the melted snow ?  
Preparation of Solutions
Concentration of Solutions
The Solubility Product Constant, Ksp
Extraction and isomerization rates of α-acids for bittering beer
Titration Stations.
Experiment 7 Preparation and Properties of Buffers
Click a hyperlink or folder tab to view the corresponding slides.
Isotherm Study of Metal Ion Adsorption onto Tree Fern
Solubility Product Constant (Ksp)
Section 10.1 Separable Equations II
Gel Filtration Chromatography.
Chapter 15: Applications of Aqueous Equilibria
Coagulation Factor Assays
Answers the question, “How to ‘unmix’?”
Dilutions.
Fang-Ching Lee#, Wen-Ta Chiu and Yuh-Shan Ho*
Two-Stage Batch Adsorber Design Using Pseudo-Second-Order Kinetic Model for the Adsorption of Basic Blue 69 Dye onto Peat I-Hsin Lin1#, Ming-Huang Wang1,
Ionic Equilibria: Part II Buffers and Titration Curves
Concentration & Dilution
Volume 84, Issue 1, Pages (January 2003)
Concentration = # of moles volume (L) V = 1000 mL V = 1000 mL
Levofloxacin structural formula
Presentation transcript:

Mercury Extraction with LIX26 and LIX84 Ionic Exchangers in n-Heptane Project Objective: The goal of the project is to study the capacity of two commercially available ionic exchangers (LIX26, LIX84) to remove Hg (II) from surface water, by performing a series of batch experiments that will enable the determination of the maximum binding capacity of each surfactant, the efficiency of the ionic exchangers at a given concentration of Hg and the fixed percentage (by volume) of the surfactant. Likewise, the change in total organic carbon (TOC) in the aqueous layer due to the use of surfactants, as well as the time dependence of the surfactants’ efficiency, are of interest. Background The streams of the EFPC watershed must comply with TN State’s criteria for recreational use of surface waters, which requires a mercury concentration lower than 51 parts per trillion (ppt). Ten years (7/1/1997 to 10/29/2007) of mercury concentration data collected at Station 17 (EFK 23.4 according to DOE’s classification, see Figure 1a) shows average discharge rates of 14 cfs and average mercury concentrations of 500 ppt with peaks up to 17,300 ppt, which considerably exceeds the requirement of < 51 ppt (Figure 1b). Therefore, 90% reduction of mercury is required to comply with the state law. Sergiu Fiodorov (DOE Fellow) - Florida International University Dr. Georgio Tachiev, ARC-FIU Mentor and Project Manager Figure 1. Section of EFPC watershed. a) Location of Y-12 upstream of station 17, b) Mercury concentrations measured at Sta-17 (in parts per trillion). Conclusion The batch experiments showed that, as expected, the capacity of the ionic exchangers remains unchanged after 5 minutes, which confirms previous studies that found the equilibrium to be reached after approximately 2 minutes. The concentration of TOC increases in the aqueous solution with increasing volume of the surfactant for LIX84, but remains unchanged for LIX26. The % of mercury extracted ranged from 72% for LIX26 up to 98.5% for LIX84. Acknowledgments Dr. Georgio Tachiev Dr. Yelena Katsenovich Dr. Yong Cai Dr. Leonel Lagos Procedure A series of standard Hg (II) solutions are prepared in 50 mL plastic vials with a concentration of Hg (II) ranging from 1 ppm to 3 ppm. To each vial, 3 mL of 86.2% n-heptane is added, containing (1%, 2% and 5%) of the ionic exchanger in a 1:10 ratio with respect to the aqueous layer. The pH of the samples is adjusted to 7 by adding the appropriate amount of 0.1 M KOH. The vials are mixed in a laboratory shaker for 15 min, after which the two layers are separated in a separatory funnel. Measurements The aqueous layer is analyzed for Hg (II) concentration at South MercoLAB according to the ACP method. The concentration of the total organic carbon (TOC) is analyzed with a Shimadzu TOC-V CSH/CSN Total Organic Carbon analyzer. The analysis began with a standard calibration run of six standards with known concentration of TOC, as well as using 2 blanks for every 5 samples to ensure quality control of the analysis. Results Materials and Methods Ionic exchangers: LIX 26 LIX ppm (±1%) Hg (II) stock solution N-Heptane 0.1 M KOH solution Table 1. Mercury extraction data Figure 2. Mercury extraction with Lix26 Figure 3. Mercury extraction with LIX84 Figure 4. TOC dependence on % of the surfactant Figure 5. Mercury removal depending on time of mixing