Origin and mobility of fulvic acids in the Gorleben aquifer system: implications from isotopic data and carbon/sulfur XANES

Abstract The Gorleben aquifer system, overlaying a Permian salt dome, has been under investigation for more than two decades for the potential to host a nuclear waste repository. Groundwater in the system shows a range of compositions, especially with respect to salt content and dissolved organic carbon (DOC) concentration. An uncertainty for safety analysis is the mobility of metal-complexing dissolved organic acids. Hence, isotopic data and carbon/sulfur K-edge X-ray absorption near edge structure (XANES) spectroscopy have been used in order to determine the mobility of fulvic acids (FAs). Isotopic data (13C, 14C, 3H) show that FAs from the recharge zone are mobile over the entire depth, including into the salt dome influenced brines.14C and δ 34S (up to 34‰) analysis shows furthermore that enhanced DOC (mainly humic and fulvic acids) concentrations originate from microbiologically mediated turnover of lignite intercalations in sandy Miocene sediments (“in situ generation”). XANES revealed that these in situ generated FAs have a high Carom/Caliph ratio (∼2.8), a decreased carboxyl/carbonyl content (less hydrophilic), a red shift in the Carom = Carom peak at 285.2eV, indicating heteroatom substitution and aromatic ring distortion, and feature a high reduced S content (∼69%). Shallow recharge groundwater and deep brine derived FAs exhibit a similar Carom/Caliph ratio (1.1–1.4), indicating invariance in the backbone structure against higher residence times and variation in geochemical conditions. XANES data also suggest that only heteroatom-substituted, destabilized aromatic ring structures of the FAs are stable in the brines and revealed 43% reduced S in recharge FAs and high (61%) reduced S with higher sulfate content in the channel brine FAs. Sulfur redox speciation therefore reflects geochemical conditions/reactions and shows a high stability of reduced sulfur species in more aerobic channel brine environments. The application of carbon and sulfur XANES shows that key structural information can be obtained from small sample amounts. The high mobility of FAs over a range of groundwater conditions and residence times verifies the potential for dissolved humic substances to enhance radionuclide transport.

[1]  P. Fritz,et al.  Origin and mobility of humic colloids in the Gorleben aquifer system , 2000 .

[2]  P. Bloom,et al.  X-ray absorption spectroscopic evidence for the complexation of HG(II) by reduced sulfur in soil humic substances , 1999 .

[3]  N. Hertkorn,et al.  Functional group analysis of natural organic colloids and clay association kinetics using C(1s) spectromicroscopy , 2003 .

[4]  Jae-Il Kim Actinide Colloids in Natural Aquifer Systems , 1994 .

[5]  S. Manahan Interactions of Hazardous-Waste Chemicals with Humic Substances , 1988 .

[6]  G. Cody,et al.  Inner-Shell Spectroscopy and Imaging of a Subbituminous Coal: In-Situ Analysis of Organic and Inorganic Microstructure Using C(1s)-, Ca(2p)-, and Cl(2s)-NEXAFS , 1995 .

[7]  M. L. Thompson,et al.  Sulfur in Biosolids-Derived Fulvic Acid: Characterization by XANES Spectroscopy and Selective Dissolution Approaches , 2000 .

[8]  J. Miao,et al.  X1A: Second-generation undulator beamlines serving soft x-ray spectromicroscopy experiments at the NSLS , 1996 .

[9]  J. Palacios,et al.  Characterization of humic acid from leonardite coal: an integrated study of PY-GC-MS, XPS and XANES techniques , 2002 .

[10]  Harald Ade,et al.  Trends in the Carbonyl Core (C 1S, O 1S) → π*C=O Transition in the Near-Edge X-ray Absorption Fine Structure Spectra of Organic Molecules , 2002 .

[11]  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 .

[12]  P. Warman,et al.  Characterization of ester sulphate in a gypsum-amended podzol using an immobilized sulphatase reactor , 1994, Biology and Fertility of Soils.

[13]  J. Palacios,et al.  A study of sulfur functionalities in fossil fuels using destructive- (ASTM and Py-GC/MS) and non-destructive- (SEM-EDX, XANES and XPS) techniques , 2002 .

[14]  D. Canfield Biogeochemistry of Sulfur Isotopes , 2001 .

[15]  R. Artinger,et al.  A kinetic study of Am(III)/humic colloid interactions. , 2002, Environmental science & technology.

[16]  P. Fritz,et al.  14C dating of Gorleben groundwater , 2000 .

[17]  J Kirz,et al.  Chemical contrast in X-ray microscopy and spatially resolved XANES spectroscopy of organic specimens. , 1992, Science.

[18]  A. Hitchcock,et al.  Carbon K-shell excitation spectra of linear and branched alkanes , 1987 .

[19]  A. Bauer,et al.  Colloid-borne americium migration in Gorleben groundwater: significance of iron secondary phase transformation. , 2003, Environmental science & technology.

[20]  Chris Jacobsen,et al.  Process optimization for production of sub-20 nm soft x-ray zone plates , 1997 .

[21]  J. McCarthy,et al.  Subsurface transport of contaminants , 1989 .

[22]  A. Autry,et al.  Sulfonate S: A major form of forest soil organic sulfur , 1990, Biology and Fertility of Soils.

[23]  P. Fritz,et al.  Characterization of groundwater humic substances : influence of sedimentary organic carbon , 2000 .

[24]  Bruce D. Honeyman,et al.  Geochemistry: Colloidal culprits in contamination , 1999, Nature.

[25]  Chris Jacobsen,et al.  Micro-XANES: Chemical contrast in the scanning transmission X-ray microscope , 1994 .

[26]  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 .

[27]  Eberhard E. Fetz,et al.  Liquid Crystal Alignment on Carbonaceous Surfaces with Orientational Order , 2001 .

[28]  A. Hitchcock,et al.  Inner-shell spectroscopy of benzaldehyde, terephthalaldehyde, ethylbenzoate, terephthaloyl chloride and phosgene: models for core excitation of poly(ethylene terephthalate) , 1992 .

[29]  Scott Fendorf,et al.  Speciation of sulfur in humic and fulvic acids using X-ray absorption near-edge structure (XANES) spectroscopy , 1997 .

[30]  Harald Ade,et al.  CALIBRATED NEXAFS SPECTRA OF SOME COMMON POLYMERS , 2003 .

[31]  A. Hitchcock BIBLIOGRAPHY OF ATOMIC AND MOLECULAR INNER-SHELL EXCITATION STUDIES , 1982 .

[32]  M. T. Browne,et al.  Diffraction-limited imaging in a scanning transmission x-ray microscope , 1991, Optical Society of America Annual Meeting.

[33]  P. Fritz,et al.  Groundwater in-situ generation of aquatic humic and fulvic acids and the mineralization of sedimentary organic carbon , 2000 .

[34]  David J. Clifford,et al.  The organic geochemistry of coal: from plant materials to coal , 1997 .

[35]  G. Cody,et al.  The application of soft X-ray microscopy to the in-situ analysis of sporinite in coal , 1996 .

[36]  J. Boon,et al.  Quantitative analysis of sulfonic acid groups in macromolecular lignosulfonic acids and aquatic humic substances by temperature-resolved pyrolysis-mass spectrometry , 1993 .

[37]  P. Fritz,et al.  Development of climatic and vegetation conditions and the geochemical and isotopic composition in the Franconian Albvorland aquifer system , 2000 .

[38]  Roger C. Prince,et al.  Photooxidation of crude oils , 1998 .

[39]  Z. Berner,et al.  S- and O-isotopic character of dissolved sulphate in the cover rock aquifers of a Zechstein salt dome , 2002 .

[40]  Chen,et al.  High-resolution K-shell photoabsorption measurements of simple molecules. , 1991, Physical review. A, Atomic, molecular, and optical physics.

[41]  A. Hitchcock,et al.  Inner-shell spectroscopy of p-benzoquinone, hydroquinone, and phenol: Distinguishing quinoid and benzenoid structures , 1992 .

[42]  D. Hesterberg,et al.  Stability of Reduced Organic Sulfur in Humic Acid as Affected by Aeration and pH , 2001 .

[43]  G. Buckau,et al.  The Migration Behaviour of Transuranium Elements in Gorleben Aquifer Systems: Colloid Generation and Retention Process , 1988 .

[44]  S. Purushothaman,et al.  Liquid Crystal Alignment on Carbonaceous Surfaces with Orientational Order , 2001, Science.

[45]  H. Ågren,et al.  A theoretical study of the near-edge x-ray absorption spectra of some larger amino acids , 1998 .

[46]  B. Manowitz,et al.  Interactions of thiols with sedimentary particulate phase: studies of 3-mercaptopropionate in salt marsh sediments from Shelter Island, New York , 1997 .

[47]  D. Canfield,et al.  Sulfur isotope fractionation during bacterial reduction and disproportionation of thiosulfate and sulfite , 1998 .

[48]  Chris Jacobsen,et al.  Carbon edge XANES spectroscopy of amino acids and peptides , 1997 .

[49]  M. Mastalerz,et al.  A geochemical study of macerals from a Miocene lignite and an Eocene bituminous coal, Indonesia , 1996 .

[50]  C. E. Brion,et al.  Inner-shell excitation of formaldehyde, acetaldehyde and acetone studied by electron impact , 1980 .

[51]  Jacobsen,et al.  Soft X‐ray spectroscopy from image sequences with sub‐100 nm spatial resolution , 2000, Journal of microscopy.