14C Content and Specification of SIERs from BWR

Slides:



Advertisements
Similar presentations
ENVE 201 Environmental Engineering Chemistry 1
Advertisements

Reaction Energy and Reaction Kinetics
Gases Follow-up.
Class evaluations.
Important/significant foundation soil physical properties Color Texture Structure Consistence Coarse fragments Reaction.
HPLC Analysis of Ionic Compounds Nicholas H. Snow Seton Hall University.
Biodegradation of organic pollutants in a composting environment in Mauritius Vijayalaxmi Jumnoodoo PhD Candidate Department of Chemical and Environmental.
Analytical Chemistry Acid-Base. Arrhenius Theory: H+ and OH- This theory states that an acid is any substance that ionizes (partially or completely) in.
L.B. Begrambekov Plasma Physics Department, Moscow Engineering and Physics Institute, Moscow, Russia Peculiarities, Sources and Driving Forces of.
Catalytic wet air oxidation The Budapest University of Technology and Economics Department of Chemical and Environmental Process Engineering Arezoo Mohammad.
Soil Acidity and pH Causes, remediation, and measurement.
Determination of Dominant Trace Metal Sequestration Processes in Two Vertical Flow Bioreactors Using Modified Tessier Extractions J.A. LaBar and R.W. Nairn.
Created with MindGenius Business 2005® Ion Exchange Chromatography Ion Exchange Chromatography Principles Small K means low affinity – so low RT K is often.
Validation of Analytical Method
problem solved Preservation of Samples for RETS, REMP and RW Bob Litman Radiochemistry Laboratory Basics Presented in coordination with GEL.
IV. Water Chemistry A. pH, hardness, and other ionic compounds and gases affecting water quality.
Gas, Cloudwater, and Rain Hydrogen Peroxide and Methylhydroperoxide Measurements in RICO Brian G. Heikes, Center for Atmospheric Chemical Studies, Graduate.
CO 2 Capture from Flue Gas using Amino Acid Salt Solutions Benedicte Mai Lerche Kaj Thomsen & Erling H. Stenby.
NDA PhD Bursary Spent Fuel Theme Carwyn Jones, Nuclear Technologies (representing NDA) 25 th August 2015.
Temperature Measured with a thermometer Units are ◦C
This project has received funding from the European Union’s Seventh Framework Programme for research, technological development and demonstration under.
Stephanie Freeman January 10 th, 2007 Rochelle Group University of Texas at Austin – Dept. of Chemical Engineering.
PART -III Analytical Methods for Metal Speciation in Water and Solids
Cement waste matrix evaluation and modelling of the long-term stability of cementitious waste matrices.
Caroline De Bodt, Quentin d’Hoop, Jérôme Harlay and Lei Chou
KINETICS OF SURFACE-BOUND BENZO[A]PYRENE AND OZONE ON ORGANIC AND INORGANIC AEROSOLS N.-O. A. Kwamena, J. A. Thornton, J. P. D. Abbatt Department of Chemistry,
1 Trends in soil solution chemistry in temperate forests under on-going recovery from acidification and climate change in Flanders, Belgium Arne Verstraeten.
This project has received funding from the Euratom research and training programme under grant agreement No Improving the geological.
Impact of declining atmospheric deposition on forest soil solution chemistry in Flanders, Belgium Arne Verstraeten 15 th Meeting of the ICP Forests Expert.
3.6: ACIDS AND BASES … Equilibrium Constants…K a and K b.
Title: Lesson 10: Salt Hydrolysis
A method for measuring phosphorus nutrient limitation using the oxygen isotopic composition of phosphates Joseph Murray Arizona State University Acknowledgements:
PH of Salts When acids are neutralized by bases, water and a salt is formed. The salt solution can be acidic, basic, or neutral depending on the acid.
1 Laboratory Activity Three. Title: “Acids, Bases, Buffers, Titrations” Word / Phrase Association:  H + ions, OH - ions.  pH, pOH.  Strong vs. weak.
Introduction The pyrolysis products of natural polymers often exhibit very similar neural losses during collision induced dissociation (CID) Some ions.
Multi-Analyte LC-MS/MS Methods – Best Practice.
Soil Chemistry.
Chem. 1B – 9/15 Lecture.
PROCESS OF HYDROTHERMAL CONVERSION OF CARBON DIOXIDE INTO FORMIC ACID WITH ZINC Daniel Román González, Alexander Navarrete, Antonio Nieto, Ángel Martín,
Comparative simulative studies using PHREEQC-Interactive and Visual MINTEQ model for understanding metal-NOM complexation occurring in cooling and raw.
EXPERIMENTAL TECHNIQUES Steady-state techniques In radiolytic investigations the conversion (i.e., the ratio of transformed and starting molecules) is.
Acid Base Equilibrium.
Steve Swanton CAST Symposium, Lyon, 17 January 2018
Höchsterstrasse 73, A-6850 Dornbirn, Tel ,
CArbon-14 Source Term CAST
CArbon-14 Source Term CAST
Evolution of Ionic Exchange Resins
CArbon-14 Source Term CAST
CArbon-14 Source Term CAST
Buffers A buffer is a mixture of chemicals that make a solution resist a change of pH pH remains relatively constant when adding an acid or base A buffer.
CArbon-14 Source Term CAST
Name: André Rübel Organisation: GRS Date:
Introduction If nontoxic organic pollutants get discharged into a river, lake or stream, they should be pretty harmless, right?
CArbon-14 Source Term CAST
For more information, please visit the CAST website at:
Olli Nummi, Fortum, Finland
CArbon-14 Source Term CEA/EDF contribution to WP4 Ion-Exchange Resins CAST final symposium Lyon 16th - 18th January 2018 Name: J. Comte(1), S. Legand(1),
CArbon-14 Source Term CAST
Carbon cycle theme The Earth’s carbon cycle has a stabilizing mechanism against sudden addition of CO2 to the atmosphere About 50% of carbon emission is.
Petr Večerník ÚJV Řež, a. s. 16th – 18th January 2018 CAST Symposium
Selective removal of oxygen from biomass-derived compounds
CArbon-14 Source Term CAST
CArbon-14 Source Term CAST
M. Wojnicki 1. , M. Luty-Błocho1, K. Kołczyk1, and P
Ocean Acidification Topics Acids Bases pH Scale Ocean Acidification.
Key Messages on Soils and Nutrient Cycling effects
Name: Klas Källström Organisation: SKB Date:
Gas measurements performed using a Gasmet DX-4000 FTIR
Public outreach for the EC Carbon-14 Source Term project
Presentation transcript:

14C Content and Specification of SIERs from BWR EC CAST (CArbon-14 Source Term) Project 14C Content and Specification of SIERs from BWR C. Rizzato, A. Bukaemskiy, N. Shcherbina Forschungszentrum Jülich GmbH The project has received funding from the European Union’s Seventh Framework Programme for research, technological development and demonstration under grant agreement no. 604779, the CAST project.

Contents Introduction and sample selection (T.4.1) 14C in SIERs (T.4.2): Analytical approach Total 14C content and speciation Morphological features of SIERs 14C released from SIERs (T.4.3): During leaching During storage Effects of 𝛾-radiation and theoretical approach: Model 𝛾-irradiation experiments with IERs Benchmarking of experimental and model results Conclusions A. Bukaemskiy, N. Shcherbina, C. Rizzato – Final CaST Symposium – 16-18/01/2018 Corrado Rizzato – CAST WP4 Meeting – Pitești (RO)

Introduction and sample selection [Wolff. 2012] Sample selection criteria: Samples of SIERs from two different NPP were collected (FZJA, FZJB); 𝛾-activity limitation; Different storage times (FZJB). A. Bukaemskiy, N. Shcherbina, C. Rizzato – Final CaST Symposium – 16-18/01/2018 Corrado Rizzato – CAST WP4 Meeting – Pitești (RO)

Analytical approach: 14C content and speciation in SIERs (Task 4.2) Sequential stripping of exchangeable and non-exchangeable 14C-fractions with quantification by LSC and HPLC. The remaining fraction associated with particulate matter is investigated by SEM. 14C retained on SIERs Exchangeable Non-exchangeable Combustion Acidification Wet Oxidation Inorganic HCO3-, CO32- Organic HCOO-,CH3OO- Organic CxHyOz Particulate matter LSC (quantification) SEM HPLC (speciation and quantification) A. Bukaemskiy, N. Shcherbina, C. Rizzato – Final CaST Symposium – 16-18/01/2018

Total 14C: combustion vs. sequential stripping (Task 4.2) Sample: FZJA Method for total 14C: Combustion with oxidation of released species Method for inorg./org. 14C: Acidification and wet oxidation Total 14C: 1770 ± 286 Bq/g Inorganic 14C: 1900 ± 256 Bq/g Organic 14C: 6.3 ± 0.4 Bq/g Good reproducibility of results on total 14C and speciation Inorganic and organic fractions of 14C were 99.6 % and 0.4 % respectively The difference could be explained by the presence of a small fraction of particulate matter or by sample inhomogeneity A. Bukaemskiy, N. Shcherbina, C. Rizzato – Final CaST Symposium – 16-18/01/2018 Corrado Rizzato – CAST WP4 Meeting – Pitești (RO)

14C inventory and speciation in SIERs (Task 4.2) Inorganic 14C fractions ranges from 99.6 % to 98.9% Organic 14C fraction ranges from 0.4 to 1.1% No particular trend in 14C speciation depending on SIERs age and origin A. Bukaemskiy, N. Shcherbina, C. Rizzato – Final CaST Symposium – 16-18/01/2018 Corrado Rizzato – CAST WP4 Meeting – Pitești (RO)

14C inventory and speciation in SIERs (Task 4.2) Sample FZJA: HPLC results Injection peak Formic acid Acetic acid Ghost peak Formic acid detected in small amounts (∼µg/gresin) (after regeneration) Acetic acid – below detection limit A. Bukaemskiy, N. Shcherbina, C. Rizzato – Final CaST Symposium – 16-18/01/2018 Corrado Rizzato – CAST WP4 Meeting – Pitești (RO)

Morphological study (Task 4.2) FZJB Carbon Co Co Fe Agglomerates containing Fe and Co were observed with SEM/EDX A. Bukaemskiy, N. Shcherbina, C. Rizzato – Final CaST Symposium – 16-18/01/2018

Morphological study (Task 4.2) FZJB EDX-signal Agglomerates containing only Fe were observed with SEM/EDX A. Bukaemskiy, N. Shcherbina, C. Rizzato – Final CaST Symposium – 16-18/01/2018

14C release from SIERs (Task 4.3) Main factors influencing 14C release: Acid-base equilibrium in the solution Effect of service/storage temperatures and/or strong oxidants (thermal/chemical degradation) Radiolysis: most -emitters in cation exchange fraction Bacterial growth: conversion of inorganic 14C into organic or produce anions that will displace 14C from the resins A. Bukaemskiy, N. Shcherbina, C. Rizzato – Final CaST Symposium – 16-18/01/2018

14C release: leaching in high pH solutions On-line release of volatile 14C from SIERs in cementitious env. pH evolution Release of 14C in the gas phase is a result of a transient conditions: (local) pH decrease due to the release of H+ from the cation-exchange resins On certain SIERs/XOH ratio CO2 may be released A. Bukaemskiy, N. Shcherbina, C. Rizzato – Final CaST Symposium – 16-18/01/2018 Corrado Rizzato – CAST WP4 Meeting – Pitești (RO)

14C release: storage (Task 4.3) Release of 14C at RT Release of 14C at RT and 50°C At T = 20ºC FR, % = 0.77 ± 0.02 At T = 50ºC FR, % = 1.5 ± 0.5 Release of 14C: fast kinetics, influenced by equilibrium with atmospheric CO2 Enhanced release at elevated temperature: degradation of QA-groups Self-irradiation effects on BWR SIERs was not observed on the laboratory time-scale A. Bukaemskiy, N. Shcherbina, C. Rizzato – Final CaST Symposium – 16-18/01/2018 Corrado Rizzato – CAST WP4 Meeting – Pitești (RO)

Model γ-irradiation of IERs (Task 4.3) Residual exchange capacity Irradiated model IERs Residual exchange capacity 0.1, 0.5, 1 MGy NH3 HCOOH CO32- TMA H2 C2H6 C3H6O C3H8 Released species in solution & gas phase g, air De-amination and de-methylation are the preferred degradation mechanisms De-amination causes decrease in salt-splitting capacity, de-methylation – increase of non-salt-splitting capacity; Decreasing of salt-splitting capacity may promote a release of 14C as 14CO2 A. Bukaemskiy, N. Shcherbina, C. Rizzato – Final CaST Symposium – 16-18/01/2018

Benchmarking of experimental and model experiments 𝛾-irradiated IERs Theoretical modeling (in progress) SIERs Common findings: H2, CO2, formic and acetic acids, TMA Some unidentified organic species C2H6 C3H6O C3H8 Main degradation mechanism - de-amination, which provides for the loss of exchange capacity and release of 14CO2 fraction Theoretical modelling (MD) is in progress to identify other accompanying processes A. Bukaemskiy, N. Shcherbina, C. Rizzato – Final CaST Symposium – 16-18/01/2018 Corrado Rizzato – CAST WP4 Meeting – Pitești (RO)

Conclusions 14C is present in BWR SIERs mainly in inorganic form (98.9 - 99.7%); organic fraction ranges from 0.4 to 1.1%; agglomerates of particulate matter were identified; One of identified organic species is formic acid (exchangeable fraction); Release of volatile 14C occurs during storage, increased at high temperatures; when SIERs are in contact with an alkaline solution, transient pH conditions result in the release of volatile 14C; Ageing and radiolytic effects on BWR SIERs were not observed on the laboratory time-scales; Model experiments of 𝛾-radiation on IERs demonstrated a release of H2, CO2, formic acid and QA-fragments, which is in agreement with the results for SIERs; the main degradation mechanism was proposed to be de-amination, which may provide for the loss of exchange capacity and release of 14CO2; The results were obtained for unconditioned SIERs. The behaviour of e.g. cemented SIERs or other waste forms is likely to be different in repository-relevant conditions. A. Bukaemskiy, N. Shcherbina, C. Rizzato – Final CaST Symposium – 16-18/01/2018

Thanks For Your Attention