Forschungszentrum Karlsruhe

Reduced activation ferritic-martensitic steels (e.g. EUROFER) are considered for application in future fusion technology as structural material, which is in contact with the breeding material Pb-17Li. Various corrosion experiments have been made in the past, however, evaluation of these tests, which were mostly conducted up to moderate temperatures of up to 480°C, was performed with respect to determine corrosion rates and mechanisms e.g. dissolution of some elements out of the steels and comparison of the results with earlier tested RAFM-steels of type F82H-mod. OPTIFER, and MANET. In the mean time the envisaged operation limits e.g. in temperature increased to roughly 550°C and flow regimes may change. Thus extrapolations of the RAFM-steel corrosion behavior determined in the past to the new working conditions may be problematic due to large uncertainties or reliability and, additionally, only low knowledge on transport of dissolved components in the Pb-17Li flow is present. In contrast to earlier investigations, these changes in requirements need the going over from (only) mechanism based corrosion tests to model supported tests. Furthermore, the whole loop has to be considered in the evaluation of the corrosion tests together with other occurring phenomena and mechanisms as transport effects and precipitations. Therefore, under this task the development of modeling tools for describing Pb-17Li corrosion (dissolution, material transport and precipitations) was started. The modular structured tools are based on physical, chemical and thermo-hydraulic parameters and, in the first stage, the development was focused on the dissolution of EUROFER and validation with older test results obtained at 480°C in our PICOLO loop earlier. In the second stage the new 550°C test results – obtained in the part corrosion testing of this task were used for validation at a second temperature level and transport phenomena were considered. This report consists of the two subtasks a) corrosion testing and b) modeling with the main achievements given for each part in the next paragraphs. A) Corrosion testing at 550°C The corrosion testing of bare cylindrical EUROFER samples was performed in the upgraded PICOLO loop for testing at the new blanket relevant temperature of 550°C in flowing Pb-17Li with a flow rate of about 0.22 m/s – the same flow value and configuration as used in earlier 480°C tests. The post exposure analyses of the samples from the 550°C champagne showed that the corrosion mechanisms are the same as detected at the lower exposure temperature of 480°C namely homogeneous corrosion attack and dissolution of steel components. In the test series durations up to 5,000 h were examined and a corrosion rate was evaluated of about 500 μm/a. This value is more than 5 times the rate observed in 480°C tests and represents a dramatically increase in corrosion rate by a slight increase of only 70 K in testing temperature. Under these conditions 1 m2 TBM surface would generate about. 4 kg Fe dissolved in Pb-17Li per year. The operation of PICOLO loop showed clearly the dangerous situation of loop blockages by precipitations formed in the cooler sections after short times (approx. 3,000 h) due to the high amount of dissolved and transported corrosion products. Looking in more detail the first test results obtained at 550°C with a short time base of 5,000 h will not have yet the high reliability for 4 extrapolation up to several 10,000 h known from the 480°C tests as required for TBM design. However a new test series was launched to increase reliability and also statistics with exposure times up to 10,000 h. A global valuation of the evaluated corrosion rates at 550°C in comparison with 480°C values and data coming from other laboratories using the empirical Sannier correlation showed that the new 550°C data are well positioned in the complex temperature and flow rate depending corrosion attack picture. These corrosion figures illustrate that corrosion of bare RAFM steels at high temperatures – also at reduced flow rates in real TBM’s may be a serious and challenging task in handling of blanket systems beside tritium permeation and may require corrosion protection measures by coatings. B) Development of modeling tools and their validation The developed modeling tools are based on physical and electrochemical parameters to describe the occurring mechanisms and phenomena in a nonisothermally operated loop. The developed and validated tools will simulate in the basic model configuration dissolution (corrosion attack), transportation of corrosion products and precipitation effects in dependence of the thermo hydraulic parameters (e.g. flow velocity, temperature profile) of the test loop PICOLO. The validation process showed that the selection of ‘good’ physical properties e.g. diffusion coefficients will have a critical impact on the results modeled. The validation of the two different test temperatures indicated that probably values evaluated by Feuerstein will be most reliable ones. Under these boundary conditions the developed tools reproduced the measured corrosion rates (90 μm/a at 480°C and 500 μm/a at 550°C) rather well with about 80 μm/a and 520 μm/a, respectively. The parameterization of the whole loop showed the sections where dissolution or precipitation takes place in dependence of the local temperatures. The modeling of precipitation needs more experimental input to decide whether needle like particles are formed or if precipitates grow on the surfaces. Additionally, validation with varied flow rates should be performed in future to have a tool for reliable prediction of effects in TBM’s working far away of tested loop configuration.

[1]  T. Arnold,et al.  Sorption of uranium(VI) onto phyllite , 1998 .

[2]  F. Morel,et al.  Oligoelectrolyte Model for Cation Binding by Humic Substances , 1992 .

[3]  G. Bernhard,et al.  Uranium(VI) sorption onto phyllite and selected minerals in the presence of humic acid , 2000 .

[4]  P. Silberzan,et al.  Silanation of silica surfaces. A new method of constructing pure or mixed monolayers , 1991 .

[5]  M. H. Back,et al.  Kinetic studies of metal speciation using chelex cation exchange resin: application to cadmium, copper, and lead speciation in river water and snow. , 1994, Environmental science & technology.

[6]  R. Jervis,et al.  The volatilization of iodine species over dilute iodide solutions , 1993 .

[7]  G. Bernhard,et al.  Uranyl(VI) carbonate complex formation: Validation of the Ca2UO2(CO3)3(aq.) species , 2001 .

[8]  T. Olson,et al.  Aqueous Chlorination Kinetics and Mechanism of Substituted Dihydroxybenzenes , 1996 .

[9]  A. Townshend Standard potentials in aqueous solutions , 1987 .

[10]  J. Higgo,et al.  The mobility and stability of iodine-humic and iodine-fulvic complexes through sand , 1993 .

[11]  R. Ramette,et al.  Thermodynamics of Iodine Solubility and Triiodide Ion Formation in Water and in Deuterium Oxide , 1965 .

[12]  R. Wershaw A new model for humic materials and their interactions with hydrophobic organic chemicals in soil-water or sediment-water systems , 1986 .

[13]  J. Rook Formation of Haloforms during Chlorination of natural Waters , 1974 .

[14]  T. Arnold,et al.  Sorption behavior of U(VI) on phyllite: experiments and modeling. , 2001, Journal of contaminant hydrology.

[15]  D. Kinniburgh,et al.  Generic NICA-Donnan model parameters for proton binding by humic substances. , 2001, Environmental science & technology.

[16]  B. Porsch Epoxy- and diol-modified silica: Optimization of surface bonding reaction , 1993 .

[17]  A. Möslang,et al.  Thermal and mechanical behaviour of the reduced-activation-ferritic-martensitic steel EUROFER , 2002 .

[18]  G. Szabó,et al.  Evaluation of silica-humate and alumina-humate HPLC stationary phases for estimation of the adsorption coefficient, Koc, of soil for some aromatics , 1992 .

[19]  G. Whitesides,et al.  Self-assembled organic monolayers: model systems for studying adsorption of proteins at surfaces , 1991, Science.

[20]  M. McGovern,et al.  Role of Solvent on the Silanization of Glass with Octadecyltrichlorosilane , 1994 .

[21]  G. Choppin Humics and Radionuclide Migration , 1988 .

[22]  Nancy Y. Ip,et al.  Surface Characterization of a Silicon-Chip-Based DNA Microarray , 2001 .

[23]  G. Charlot,et al.  Analyse quantitative minérale , 1955 .

[24]  P. A. Smith,et al.  Iodine dispersion and effects on groundwater chemistry following a release to a peat bog, Manitoba, Canada , 1989 .

[25]  J. I. Kim,et al.  Complexatíon of Trivalent Actinide Ions (Am3+, Cm3+) with Humic Acid: The Effect of Ionic Strength , 1996 .

[26]  A. Fadeev,et al.  Activated silica supports for preparation of Chromatographic sorbents. A comparative study of silicas containing attached epoxy, tosyloxy and halogen groups , 1996 .

[27]  J. J. Morgan,et al.  Aquatic Chemistry: Chemical Equilibria and Rates in Natural Waters , 1970 .

[28]  D. Julthongpiput,et al.  Sticky Molecular Surfaces: Epoxysilane Self-Assembled Monolayers , 1999 .

[29]  V. Moulin,et al.  Fate of actinides in the presence of humic substances under conditions relevant to nuclear waste disposal , 1995 .

[30]  F. Jones,et al.  ToF‐SIMS and XPS studies of the interaction of silanes and matrix resins with glass surfaces , 1993 .

[31]  Melissa A. Denecke,et al.  Combined AFM and STXM in situ study of the influence of Eu(III) on the agglomeration of humic acid , 2002 .

[32]  Lifeng Chi,et al.  Growth of Self-Assembled n-Alkyltrichlorosilane Films on Si(100) Investigated by Atomic Force Microscopy , 1995 .

[33]  R. Marchelli,et al.  Quantitative removal of uranyl ions from aqueous solutions using micellar-enhanced ultrafiltration , 1992 .

[34]  J. Scamehorn Surfactant - Based Separation Processes , 1989 .

[35]  Michael A. Freitas,et al.  The application of electrospray ionization mass spectrometry (ESI MS) to the structural characterization of natural organic matter , 2002 .

[36]  R. Jay Direct Titration of Epoxy Compounds and Aziridines. , 1964 .

[37]  Nicole Jaffrezic-Renault,et al.  Influence of the Deposition Process on the Structure of Grafted Alkylsilane Layers , 1997 .

[38]  Jürgen Konys,et al.  Corrosion behavior of EUROFER steel in flowing eutectic Pb–17Li alloy , 2004 .

[39]  P. Faure,et al.  Natural and Laboratory Oxidation of Low-Organic-Carbon-Content Sediments: Comparison of Chemical Changes in Hydrocarbons , 2000 .

[40]  P. Toulhoat,et al.  Applications of NAA, PIXE and XPS for the quantification and characterization of the humic substances/iodine association , 2000 .

[41]  R. Dahlgren,et al.  Interaction kinetics of I2(aq) with substituted phenols and humic substances. , 2000 .

[42]  R. Nyquist,et al.  Interpreting Infrared, Raman, and Nuclear Magnetic Resonance Spectra , 2001 .

[43]  J. Watts,et al.  The interaction of a commercial dry film adhesive with aluminium and organosilane treated aluminium surfaces: a study by XPS and ToF-SIMS , 2002 .

[44]  P. Wong,et al.  A characterization of the β-glycidoxypropyltrimethoxysilane and aluminium interface by SIMS and XPS , 1997 .

[45]  L. Nony,et al.  Structural Characterization of Self-Assembled Monolayers of Organosilanes Chemically Bonded onto Silica Wafers by Dynamical Force Microscopy , 2001, physics/0510094.

[46]  A. J. Freeman,et al.  Handbook on the Physics and Chemistry of the Actinides , 1985 .

[47]  Otto Exner,et al.  The Hammett Equation—the Present Position , 1972 .

[48]  J. Lyklema Fundamentals of Colloid and Interface Science. Vol. V : Soft Colloids , 2005 .

[49]  H. Sims,et al.  Some effects of pH on inorganic iodine volatility in containment , 1996 .

[50]  C. Gerber,et al.  Immobilization of Antibodies on a Photoactive Self-Assembled Monolayer on Gold , 1996 .

[51]  P. Bertrand,et al.  ToF-SIMS study of organosilane self-assembly on aluminum surfaces , 2001 .

[52]  J. Quinton,et al.  Conformational dynamics of γ-APS on the iron oxide surface: an adsorption kinetic study using XPS and ToF-SIMS , 2000 .

[53]  D. Keller,et al.  Scanning force microscopy under aqueous solutions. , 1997, Current opinion in structural biology.

[54]  R. F. Clayton,et al.  Investigations of the uptake of transuranic radionuclides by humic and fulvic acids chemically immobilized on silica gel and their competitive release by complexing agents , 1998 .

[55]  F. Livens,et al.  Aggregation of humic substances by metal ions measured by ultracentrifugation , 2001 .

[56]  U. von Gunten,et al.  Determination of Iodide and Iodate by Ion Chromatography with Postcolumn Reaction and UV/Visible Detection. , 1999, Analytical chemistry.

[57]  J. McCarthy,et al.  Adsorption and desorption of natural organic matter on iron oxide: mechanisms and models. , 1994, Environmental science & technology.

[58]  U. Gunten,et al.  Formation of Iodo-Trihalomethanes during Disinfection and Oxidation of Iodide-Containing Waters , 2000 .

[59]  V. Moulin,et al.  Investigation of humic acid samples from different sources by photon correlation spectroscopy , 1991 .

[60]  H. Gallard,et al.  Chlorination of phenols: kinetics and formation of chloroform. , 2002, Environmental science & technology.

[61]  S. E. Pepper,et al.  Chapter 5 The effects of humic substances on radioactivity in the environment , 2002 .

[62]  H. Duschner,et al.  Characterization of humic and fulvic acids from Gorleben groundwater , 1990 .

[63]  A. Minnaard,et al.  Chemical immobilisation of humic acid on silica , 1998 .

[64]  P. Burba,et al.  Analytical fractionation of aquatic humic substances and their metal species by means of multistage ultrafiltration , 1996, Analytical and bioanalytical chemistry.

[65]  K. Heumann,et al.  Transformation of Iodide in Natural and Wastewater Systems by Fixation on Humic Substances , 2000 .

[66]  V. Moulin,et al.  Direct characterization of iodine covalently bound to fulvic acids by electrospray mass spectrometry. , 2001, Rapid communications in mass spectrometry : RCM.

[67]  L. Carlsen,et al.  Enzymatically Controlled Iodination Reactions in the Terrestrial Environment , 1991 .

[68]  R. Konings,et al.  The release of fission products from degraded UO2 fuel: Thermochemical aspects , 1993 .

[69]  F. Rondelez,et al.  Silanization of Solid Substrates: A Step Toward Reproducibility , 1994 .

[70]  F. Glombitza,et al.  Biotechnology based opportunities for environmental protection in the uranium mining industry , 1992 .

[71]  V. Brendler,et al.  Speciation of Uranium in Seepage Waters of a Mine Tailing Pile Studied by Time-Resolved Laser-Induced Fluorescence Spectroscopy (TRLFS) , 1996 .

[72]  G. Buckau,et al.  Characterization of a humic gel synthesized from an activated epoxy silica gel , 2002 .

[73]  G. Geipel,et al.  Determination of inorganic species in seepage water of uranium-mining rockpiles and in related media , 1994 .

[74]  D. Lemordant,et al.  Dual Use of Micellar-Enhanced Ultrafiltration and Time-Resolved Laser-Induced Spectrofluorimetry for the Study of Uranyl Exchange at the Surface of Alkylsulfate Micelles , 1994 .

[75]  B. Jensen Migration phenomena of radionuclides into the geosphere : a critical review of available information , 1982 .

[76]  D. Lemordant,et al.  Extraction and Release of Metal Ions by Micellar-Enhanced Ultrafiltration: Influence of Complexation and pH , 1996 .

[77]  J. I. Kim,et al.  Americium(III)-Humate Interaction in Natural Groundwater: Influence of Purification on Complexation Properties , 1997 .

[78]  T. Flament,et al.  CORROSION OF MARTENSITIC STEELS IN FLOWING Pb17Li , 1991 .

[79]  George M. Whitesides,et al.  Structure and reactivity of alkylsiloxane monolayers formed by reaction of alkyltrichlorosilanes on silicon substrates , 1989 .

[80]  P. C. Hiemenz,et al.  Principles of colloid and surface chemistry , 1977 .

[81]  P. Toulhoat,et al.  Molecular structure of fulvic acids by electrospray with quadrupole time-of-flight mass spectrometry. , 2001, Rapid communications in mass spectrometry : RCM.

[82]  M. Morrison [85a] Iodination of tyrosine: Isolation of lactoperoxidase (bovine) , 1970 .

[83]  J. Watts,et al.  Evidence of specific interaction between γ‐glycidoxypropyltrimethoxysilane and oxidized aluminium using high‐mass resolution ToF‐SIMS† , 2000 .

[84]  Jae-Il Kim,et al.  In situ AFM study of sorbed humic acid colloids at different pH , 1999 .

[85]  Y. Bichsel Hypoiodous acid: kinetics of the buffer-catalyzed disproportionation , 2000 .

[86]  E. LeBoeuf,et al.  Spectroscopic characterization of the structural and functional properties of natural organic matter fractions. , 2002, Chemosphere.

[87]  J. I. Kim,et al.  Numerical modeling of humic colloid borne americium (III) migration in column experiments using the transport/speciation code K1D and the KICAM model. , 2001, Journal of contaminant hydrology.

[88]  S. Shaw,et al.  The international collaborative programme on organosilane coupling agents: an introduction☆ , 1998 .

[89]  K. Papadopoulos,et al.  AFM on humic acid adsorption on mica , 2000 .

[90]  C. Tondre,et al.  An Attempt to Theoretically Predict Third-Phase Formation in the Dimethyldibutyltetradecylmalonamide (DMDBTDMA)/Dodecane/Water/Nitric Acid Extraction System , 1999 .

[91]  H. Gallard,et al.  Chlorination of natural organic matter: kinetics of chlorination and of THM formation. , 2002, Water research.

[92]  J. Watts,et al.  The Interaction of γ-Glycidoxypropyltrimethoxysilane with Oxidised Aluminium Substrates: The Effect of Drying Temperature , 2000 .

[93]  P. Warwick,et al.  Modelling the effect of humic substances on the transport of europium through porous media : a comparison of equilibrium and equilibrium/kinetic models , 2000 .

[94]  F. Livens,et al.  A physicochemical model of metal–humate interactions , 2000 .

[95]  K. Franke,et al.  Mobilization and Retardation of Uranium DOC Species at Three Mine Piles in Schlema/Alberoda, Saxony, Germany , 2000, Isotopes in environmental and health studies.

[96]  J. Marinsky,et al.  Ultrafiltration as a technique for studying metal—humate interactions: studies with iron and copper , 1990 .

[97]  V. Moulin,et al.  Retention behaviour of humic substances onto mineral surfaces and consequences upon thorium (IV) mobility: case of iron oxides , 2002 .

[98]  Mengqi Zeng,et al.  Liquid Metals , 1951, Nature.

[99]  H. Seidel,et al.  Einfluss des Schwefelgehaltes von Sedimenten auf die Mobilisierung von Schwermetallen durch bakterielle Laugung , 1995 .

[100]  A. Bauer,et al.  Experimental investigation of the interaction of clays with high-pH solutions: A case study from the Callovo-Oxfordian formation, Meuse-Haute Marne underground laboratory (France) , 2002 .