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  • 1
    Online Resource
    Online Resource
    New York :Cambridge University Press,
    Keywords: Water chemistry. ; Electronic books.
    Description / Table of Contents: This is the first comprehensive text on the theory and practice of aquatic organic matter fluorescence analysis, written by the experts who pioneered the research area. The book will be of interest to those establishing field, laboratory, or industrial applications of fluorescence, including advanced students and researchers.
    Type of Medium: Online Resource
    Pages: 1 online resource (408 pages)
    Edition: 1st ed.
    ISBN: 9781139905831
    Series Statement: Cambridge Environmental Chemistry Series
    DDC: 572/.435809162
    Language: English
    Note: Cover -- Half-title -- Series information -- Title page -- Copyright information -- Table of contents -- List of contributors -- About the Editors -- Preface -- Part I Introduction -- 1 The Principles of Fluorescence -- 1.1 Luminescence -- 1.2 The Relevance of Quantum Mechanics and Electronic Theory -- 1.2.1 Wave-Particle Duality and Quantization of Energy and Matter -- 1.2.1.1 Subatomic Particles -- 1.2.1.2 Quantized Matter and Energy -- 1.2.1.3 Copenhagen Interpretation -- 1.2.2 Chemical Bonding and Molecular Orbitals -- 1.2.2.1 Sigma Bonds (s Bonds) -- 1.2.2.2 Pi Bonds (p Bonds) -- 1.2.2.3 Antibonding Orbitals -- 1.2.2.4 Nonbonded Electrons -- 1.3 Understanding the Fluorescence Process -- 1.3.1 Electronic Transitions -- 1.3.1.1 Spin Multiplicity -- 1.3.1.2 Absorption -- 1.3.1.3 Franck-Condon Principle -- 1.3.2 Nonradiative Decay -- 1.3.2.1 Vibrational Relaxation -- 1.3.2.2 Internal Conversion and Intersystem Crossing -- 1.3.3 Radiative Decay -- 1.3.4 Fluorescence -- 1.3.4.1 Stokes Shift -- 1.3.4.2 Fluorescence Decay Kinetics -- 1.3.4.3 Fluorescence Efficiency (Quantum Yield) -- 1.3.4.4 Fluorescence Quenching -- 1.3.4.5 Influence of Molecular Structure on Fluorescence -- 1.3.4.6 The Effect of pH -- 1.3.4.7 Effects of Solvents on Fluorescence Emission -- 1.3.4.8 The Heavy Atom Effect -- 1.3.4.9 Fluorescence Spectra -- 1.3.4.10 Scattering of Radiation -- 1.3.4.11 Normalization of Fluorescence Intensities -- References -- 2 Fluorescence and Dissolved Organic Matter: A Chemist's Perspective -- 2.1 Introduction -- 2.2 Theory -- 2.2.1 Absorption -- 2.2.2 Fluorescence -- 2.3 DOM Fluorescence -- 2.4 Fluorophores of Interest -- 2.4.1 Amino Acids and Proteins -- 2.4.2 Simple Phenols -- 2.4.3 Indoles -- 2.4.4 Phenylpropanes -- 2.4.5 Oxygen Ring Compounds -- 2.4.6 Lignin -- 2.4.7 Quinones -- 2.4.8 Alkaloids -- 2.5 Factors Influencing DOM Fluorescence. , 2.5.1 Quenching -- 2.5.2 pH Effects -- 2.5.3 Interactions with Metals -- 2.5.4 Charge Transfer Interactions -- 2.6 Conclusions -- Acknowledgments -- References -- 3 Aquatic Organic Matter Fluorescence -- 3.1 Introduction -- 3.1.1 Peak Nomenclature -- 3.1.2 Humic-like EEM Components -- 3.1.3 Other EEM Components -- 3.1.4 Reconciling PARAFAC Model EEM Components -- 3.2 Fluorescence in Seawater -- 3.2.1 Introduction -- 3.2.2 CDOM in Coastal Ocean and Estuaries -- 3.2.3 CDOM in Open Ocean Waters -- 3.3 Fluorescence in Freshwater -- 3.3.1 Temporal Variation in DOM Source and Dynamics -- 3.3.2 Anthropogenic and Land Use Impacts on DOM -- 3.3.3 Transformations and Reactivity -- 3.3.4 Rainwater DOM Fluorescence -- 3.3.5 Dissolved Organic Carbon vs. Fluorescence Relationships -- 3.4 Fluorescence in Groundwater -- 3.4.1 Introduction -- 3.4.2 Groundwater NOM Fluorescence Characteristics -- 3.4.3 Groundwater Anthropogenic Organic Matter Characteristics -- 3.5 Fluorescence of Wastewater and Drinking Water -- 3.5.1 Wastewater Fluorescence -- 3.5.2 Drinking Water Fluorescence -- References -- Part II Instrumentation and Sampling -- 4 Sampling Design for Organic Matter Fluorescence Analysis -- 4.1 Introduction -- 4.2 Sample Collection -- 4.2.1 Contamination Sources -- 4.2.2 Blanks and Replicate Samples -- 4.2.3 Equipment Cleaning -- 4.2.4 Water Samplers -- 4.3 Sample Preservation -- 4.3.1 Filtration Techniques -- 4.3.2 Effects of Filtration on Fluorescence -- 4.4 Storage -- 4.4.1 General Comments -- 4.4.2 Refrigeration and Freezing -- 4.4.3 Poisoning - Acidification -- 4.5 Summary and Future Needs -- Acknowledgments -- References -- 5 Optical Spectroscopy Instrumentation Design, Quality Assurance, and Control: Bench-Top Fluorimetry -- 5.1 Introduction -- 5.2 Methods of Optical Spectroscopy -- 5.2.1 Absorption Spectroscopy -- 5.2.2 Optical Emission Spectroscopy. , 5.2.3 Scattering -- 5.2.4 Photoluminescence (Fluorescence and Phosphorescence) -- 5.3 The Fluorescence Spectrometer -- 5.3.1 The Ideal Fluorescence Spectrometer System -- 5.3.2 Basic Spectrofluorimeter Design -- 5.4 Measuring Fluorescence -- 5.4.1 Defining the Sensing Volume and Inner Filter Effects -- 5.4.2 Continuum Light Sources -- 5.4.3 Monochromators and Filters -- 5.4.4 Polarization Effects -- 5.4.5 Detectors -- 5.4.6 Measurement Systems: Data Acquisition Electronics and Software -- 5.4.7 Data Collection, Display, and Analysis Software -- 5.4.8 Instrument Performance Validation -- 5.4.9 Linearity, Signal to Noise, and Dynamic Range -- 5.4.10 Speed and Sensitivity -- 5.4.11 Wavelength Accuracy -- 5.4.12 Bandpass Selection -- 5.4.13 Stray Light -- 5.4.14 Cuvettes, Cleaning and Handling -- 5.4.15 Solvents and Contaminants -- 5.4.16 Background Signals: Rayleigh and Raman Scattering -- 5.4.17 Spectral Irradiance of the Excitation Channel -- 5.4.18 Correcting Excitation Signal Channels -- 5.4.19 Correcting Emission Signal Channels -- 5.4.20 Quantum Yield -- 5.4.21 Measuring Quantum Yields: The Three-Measurement Technique -- 5.4.22 Fluorescence Units - What Are They? -- References -- 6 Experimental Design and Quality Assurance: In Situ Fluorescence Instrumentation -- 6.1 Introduction -- 6.2 Historical Perspective of In Situ Sensors -- 6.2.1 Chlorophyll Field Sensors: Precursors to In Situ DOM Fluorometers -- 6.2.2 Evolution of DOM Field Sensors -- 6.3 Instrument Design Types -- 6.3.1 Sensor Configurations -- 6.3.2 Light Sources and Detectors -- 6.3.3 Optical Filters -- 6.3.4 Optical Configurations -- 6.3.5 Data Output -- 6.4 Calibration and Correction Procedures -- 6.4.1 Temperature Correction -- 6.4.2 Blank Subtraction -- 6.4.3 Standards and Intensity Calibration -- 6.4.4 Correction for Inner Filter Effects -- 6.4.5 Dynamic Range. , 6.5 Environmental Considerations -- 6.5.1 Factors of Concern -- 6.5.1.1 Particles -- 6.5.1.2 Bubbles -- 6.5.1.3 Dynamic Range -- 6.5.1.4 Temperature Effects -- 6.5.1.5 Biofouling -- 6.5.1.6 Understanding NOM Sources Within Environments -- 6.5.2 Sensor Choices for Specific Environments -- 6.5.2.1 Optically Dilute Systems -- 6.5.2.2 Optically Thick Systems -- 6.5.2.3 Turbid Systems -- 6.5.2.4 Energetically Flashy Environments -- 6.6 Revolutionizing NOM Studies via High-Resolution Fluorescence Measurements -- 6.6.1 Deployment Platforms -- 6.6.1.1 Spatial Resolution -- 6.6.1.2 Temporal Resolution -- 6.6.2 Importance of Scale -- 6.6.2.1 Neponset River Estuary in Boston Harbor- Small Temporal and Spatial Scales -- 6.6.2.2 Hudson River Estuary - Large Spatial and Small Temporal Scales -- 6.6.2.3 Mississippi Bight Region - Large Spatial and Temporal Scales -- 6.7 Remotely Sensed NOM Measurements -- 6.7.1 Fluorescent CDOM and Validation of Remote Sensing Products -- 6.7.2 Active Remote Sensors -- 6.7.3 Fluorescence of CDOM and Passive Sensors -- 6.7.4 Remote Sensing Summary -- 6.8 Summary -- Acknowledgments -- References -- Part III Environmental Effects -- 7 Physicochemical Effects on Dissolved Organic Matter Fluorescence in Natural Waters -- 7.1 Introduction -- 7.2 The Quenching of DOM Fluorescence -- 7.3 Effects of Molecular Weight and Fluorophore Size -- 7.4 Effect of Temperature -- 7.5 Effect of pH -- 7.6 Effect of Metals -- 7.7 Effect of Salinity (Ionic Strength) -- 7.8 Effect of Particles -- 7.9 Effect of Sunlight -- 7.10 Summary and Future Directions -- Acknowledgments -- References -- 8 Biological Origins and Fate of Fluorescent Dissolved Organic Matter in Aquatic Environments -- 8.1 Introduction -- 8.2. Sources -- 8.2.1 Allochthonous versus autochthonous -- 8.2.2 Terrestrial Organic Matter -- 8.2.3 Aquatic Organic Matter. , 8.3 Microbial Degradation of Fluorescent Dissolved Organic Matter -- 8.3.1 Bioavailability of FDOM -- 8.3.1.1 Amino Acid-like Fluorescence -- 8.3.1.2 Humic-like Fluorescence -- 8.3.2 Interactions between Photochemical and Microbial Degradation -- 8.4 Future Research -- Acknowledgments -- References -- Part IV Interpretation and Classification -- 9 Fluorescence Indices and Their Interpretation -- 9.1 Introduction -- 9.2 Overview of Common Fluorescence Indices -- 9.2.1 A "Humification Index" to Track Chemical Properties Developed by Kalbitz and Colleagues (HIX< -- sub> -- SYN< -- /sub> -- ) -- 9.2.2 Zsolnay's Humification Index to Identify Soil Organic Matter Properties (HIX< -- sub> -- EM< -- /sub> -- ) -- 9.2.3 Freshness Index to Identify Microbial Material in Marine DOM (the "ß/a" and "BIX" Index) -- 9.2.4 Fluorescence Index to identify Precursor Material in Freshwater DOM (FI) -- 9.2.5 The "Peak T/Peak C Ratio" to Identify Sewage Impact on Rivers -- 9.2.6 Redox Index as an Indicator of the Oxidation State of Quinone-Like Moieties -- 9.3 Applications of Fluorescence Indices -- 9.3.1 Using Fluorescence Indices to Identify Environmental Controls on Soil Organic Matter -- 9.3.2 The Development of a Fluorescence Index to Measure Organic Matter Humification Preserved in Cave Stalagmites -- 9.3.3 Understanding Controls on DOM Source and Quality in Surface Waters -- 9.3.4 Understanding DOM Changes in Estuaries -- 9.4 Spectroscopic Challenges toward Using the Indices -- 9.4.1 Instrument-Specific Effects and Proper EEM Correction -- 9.4.2 Concentration Issues and the Inner-Filter Effect -- 9.4.3 pH Effect on Fluorescence -- 9.5 Conclusions -- Acknowledgments -- References -- 10 Chemometric Analysis of Organic Matter Fluorescence -- 10.1 Introduction -- 10.2 Multivariate and Multiway Data Sets -- 10.3 Preprocessing of Data Matrices and Arrays. , 10.4 Exploratory Data Analysis.
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  • 2
    Online Resource
    Online Resource
    Newark :John Wiley & Sons, Incorporated,
    Keywords: Paleoclimatology. ; Electronic books.
    Type of Medium: Online Resource
    Pages: 1 online resource (464 pages)
    Edition: 1st ed.
    ISBN: 9781444361063
    Series Statement: Blackwell Quaternary Geoscience Series ; v.2
    DDC: 551.44/7
    Language: English
    Note: Intro -- Speleothem Science -- Contents -- Preface -- Acknowledgements -- I: Scientific and geologica lcontext -- CHAPTER 1: Introduction to speleothems and systems -- 1.1 What is all the fuss about? -- 1.1.1 What types of speleothem areuseful for generating climate archives? -- 1.1.2 Where do speleothems occur? -- 1.1.3 How do they form? -- 1.1.4 How do we date them? -- 1.1.5 What are the proxies for past environments and climates? -- 1.1.6 How do speleothems compare with other archives? -- 1.1.7 What next for speleothem science? -- 1.2 How is this book organized? -- 1.3 Concepts and approaches of system science -- Box 1.1 Box models and feedback -- 1.4 The speleothem factory within the karst system -- 1.4.1 Long-term change -- 1.4.2 Annual-scale behaviour -- 1.4.3 Decadal- to multi-millennial-scale changes -- CHAPTER 2: Carbonate and karst cave geology -- 2.1 Carbonates in the Earth system over geological time -- 2.2 Lithologies of carbonate hostrocks -- 2.2.1 Carbonate facies -- 2.2.2 The architecture of carbonate host rocks: sequence stratigraphy -- 2.2.3 Impure and geologically complex host rocks -- 2.2.4 Carbonate porosity -- 2.3 Carbonate diagenesis and eogenetic karst -- 2.3.1 Early diagenesis in marine waters and brines -- 2.3.2 Vadose diagenetic processes -- 2.3.3 Meteoric phreatic diagenesis -- 2.3.4 Eogenetic karst development -- 2.3.5 Burial diagenesis -- 2.4 Speleogenesis in mesogenetic and telogenetic karst (with contributions from John Gunn and David J Lowe) -- 2.4.1 Chronologies of cavedevelopment -- 2.4.2 Geometry of cave passages and systems -- 2.4.3 Localization of caves: the inception horizon hypothesis -- 2.4.4 Mesogenetic caves -- 2.4.5 Modelling the development of conduits and networks -- 2.5 Cave infilling -- 2.5.1 Mechanisms of cave infill and their relative power -- 2.5.2 Dating the infills. , 2.5.3 Physical sedimentology -- 2.5.4 Archaeological issues -- 2.5.5 The long-term prognosis -- 2.6 Conclusion -- CHAPTER 3: Surface environments: climate, soil and vegetation -- 3.1 The modern climate system -- 3.1.1 The global energy budget -- 3.1.2 Global patterns of temperature, rainfall and evapotranspiration -- 3.1.3 The general circulation of the atmosphere -- 3.1.4 Ocean circulation and land-ocean interactions -- Box 3.1 Climate indices -- Box 3.2 Back trajectory analysis -- 3.2 Water isotopes in the atmosphere -- 3.2.1 Variation in stable isotopes owing to evaporation and Rayleigh condensation -- 3.2.2 Other factors responsible for variations in isotopic composition -- 3.2.3 Isotopic variations in space within the annual cycle -- 3.2.4 Inter-annual isotopic variations -- 3.3 Soils of karst regions -- 3.3.1 Processes of soil formation -- 3.3.2 Soil development through time -- 3.3.3 Concluding views on karst soils -- 3.4 Vegetation of karst regions -- 3.5 Synthesis: inputsto the incubator -- II: Transfer processes in karst -- CHAPTER 4: The speleothem incubator -- 4.1 Introduction to speleophysiology -- 4.2 Physical parameters and f luid behaviour -- 4.2.1 Measurement of parameters -- 4.2.2 Static parameters in air -- 4.2.3 Dynamic f luid behaviour: laminar versus turbulent f low -- 4.2.4 Dynamic f luid behaviour: advective versus diffusive transport -- 4.3 Water movement -- 4.4 Air circulation -- 4.4.1 Physical causes -- Cave breathing -- Wind-induced f low -- Chimney circulation -- Convection -- Water-induced f low -- 4.4.2 Radon studies as indicators of rates of air-exchange -- 4.4.3 Carbon dioxide and its variability -- 4.4.4 Generalizing seasonality and its implications for speleothems -- 4.5 Heat f lux (authored by David Domínguez-Villar) -- 4.5.1 Sources and mechanisms of heat transfer into caves -- Geothermal heat f lux. , Surface heat f lux -- Heat transferred by the atmosphere -- Heat transferred from water -- Heat transferred from the rock -- 4.5.2 Thermal equilibrium in caves -- 4.6 Synthesis: cave climatologies -- CHAPTER 5: Inorganic water chemistry -- 5.1 Sampling protocols for water chemistry -- Box 5.1 Aqueous chemistry definitions -- 5.2 The carbonate system -- 5.3 Weathering, trace elements and isotopes -- 5.3.1 Overview of element sourcesand sinks -- 5.3.2 Calcite dissolution as an exemplar of weathering processes -- 5.3.3 Mineral weathering -- 5.3.4 Isotope studies -- 5.3.5 Colloidally bound elements -- Box 5.2 Ion behaviour and complexation -- 5.4 Carbon isotopes -- Box 5.3 Stable isotopes and their fractionation -- 5.5 Evolution of cave water chemistry: modelling sources and environmental signals -- 5.5.1 Forward modelling -- 5.5.2 Backward modelling -- CHAPTER 6: Biogeochemistry of karstic environments -- 6.1 Introduction -- 6.2 Organic macromolecules -- 6.2.1 Fluorescent organic matter -- Box 6.1 Organic macromolecules in speleothems -- 6.2.2 Lipid and lignin macromolecules -- Box 6.2 Colloids and gels: interactions between organic matter and inorganic stalagmite proxies (lead author Adam Hartland) -- 6.2.3 Ribosomal DNA -- 6.3 Pollen and spores -- 6.3.1 Pollen -- 6.3.2 Spores -- 6.4 Cave faunal remains -- 6.5 Synthesis and research gaps -- Box 6.3 Vegetation and soil cycling of inorganic proxies: evidence from sulphur isotopes -- III: Speleothem properties -- CHAPTER 7: The architecture of speleothems -- 7.1 Introduction -- 7.2 Theoretical models of stalagmite growth and of stalagmite and stalactite shapes -- 7.2.1 Theories of speleothem growth rate -- 7.2.2 Models of stalagmite shapes -- 7.2.3 Models of stalactite shapes -- 7.3 Geometrical classificationof speleothems -- 7.3.1 Soda-straw stalactites -- 7.3.2 Non-'soda-straw' stalactites. , 7.3.3 'Minimum-diameter' stalagmites -- 7.3.4 Non-'minimum-diameter' stalagmites -- 7.3.5 Flowstones -- 7.3.6 Other speleothem forms -- Box 7.1 Speleoseismicity in the Mechara karst, southeastern Ethiopia (authored by Asfawossen Asrat) -- 7.4 Mineralogy and petrology -- 7.4.1 Mineralogy: aragonite versus calcite -- 7.4.2 Crystal fabrics -- Nucleation -- Crystal morphology -- Impingement growth -- Stalagmite fabrics -- 7.4.3 Laminae -- 7.4.4 Growth phases and hiatuses -- 7.5 Synthesis -- CHAPTER 8: Geochemistry of speleothems -- 8.1 Analysis and the sources of uncertainty -- 8.1.1 What's the research question? -- 8.1.2 Analytical specificity -- 8.1.3 The geometry of the growth surface and spatial precision -- 8.1.4 Analytical precision and accuracy -- 8.2 The growth interface -- 8.2.1 Nanostructure of the growth surface -- 8.2.2 Organic molecules -- 8.2.3 Biological activity at the growth interface -- 8.3 Trace element partitioning -- 8.3.1 Thermodynamic and mixed empirical-thermodynamic approaches -- 8.3.2 Limitations of the partition coefficient concept -- 8.4 Oxygen and carbon isotope fractionation -- 8.4.1 Fluid inclusions -- 8.4.2 Can an equilibrium composition be defined? -- 8.4.3 Kinetic effects during CaCO3 precipitation -- pH and growth rate effects -- The Hendy test -- Modelling fractionation along speleothem surfaces -- 8.4.4 Clumped isotope geothermometry (Δ47 value) -- 8.5 Evolution of dripwater and speleothem chemistry along water f lowlines -- 8.6 Process models of variability over time -- 8.6.1 Stadial- to glacial-length episodes -- 8.6.2 Sub-millennial variation -- 8.6.3 Annual cycles -- CHAPTER 9: Dating of speleothems -- 9.1 Introduction -- 9.2 Dating techniques -- 9.2.1 Interval dating -- 9.2.2 14C -- 9.2.3 U-Th -- 9.2.4 U-Pb -- 9.2.5 Other techniques -- 9.3 Age-distance models -- 9.4 Conclusions -- IV: Palaeoenvironments. , CHAPTER 10: The instrumental era: calibration and validation of proxy-environment relationships -- 10.1 Available instrumental and derived series -- 10.1.1 Directly measured data -- 10.1.2 Interpolated data products -- 10.1.3 Reanalysis data -- 10.1.4 Climate indices -- 10.2 Methodologies -- 10.2.1 Overview of methodologies used in other f ields -- Linear-regression-based techniques -- Compositing records -- Forward modelling -- Pseudoproxies -- 10.2.2 Appropriate methodologies for speleothem calibration -- Linear-regression-based approaches -- Compositing -- Forward modelling -- Pseudoproxies -- 10.3 Case studies of calibrated speleothem proxies -- 10.3.1 Annual lamina thickness -- 10.3.2 δ18O -- 10.3.3 Other proxies -- 10.4 Questions raised and future directions -- CHAPTER 11: The Holocene epoch: testing the climate and environmental proxies -- 11.1 A brief overview of the Holocene -- 11.1.1 The Early Holocene -- 11.1.2 The Mid-Holocene -- 11.1.3 Late Holocene -- 11.2 The past millennium -- 11.2.1 Instrumentally calibrated speleothem climate reconstructions -- 11.2.2 Multi-proxy reconstructions and model-proxy comparisons -- 11.3 Holocene environmental changes: speleothem responses -- 11.3.1 The period of remnant ice sheets in the Early Holocene -- The last Mediterranean sapropel -- The '8.2 ka event' -- 11.3.2 Orbital forcing over the Mid- to Late Holocene -- 11.3.3 Evidence for multi-decadal and multi-centennial climate variability -- Box 11.1 Times-series analysis of speleothems -- 11.3.4 Speleothem evidence of Holocene soil and vegetation change -- 11.4 Questions raised and future directions -- CHAPTER 12: The Pleistocene and beyond -- 12.1 Pleistocene proxy records (ice-age climate f luctuations defined and drawn) -- 12.1.1 Subaqueous speleothem records: Devils Hole, USA -- 12.1.2 Composite speleothem records: Soreq Cave, Israel. , 12.1.3 Palaeoclimate hotspots: the Asian monsoon and the nature of glacial terminations.
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  • 3
    Electronic Resource
    Electronic Resource
    Oxford, UK : Blackwell Publishing Ltd
    Ground water 39 (2001), S. 0 
    ISSN: 1745-6584
    Source: Blackwell Publishing Journal Backfiles 1879-2005
    Topics: Energy, Environment Protection, Nuclear Power Engineering , Geosciences
    Notes: The fluorescence properties of dissolved organic matter (DOM) in ground water in the Permian limestone of northeast England is determined from six monitoring boreholes, a private water supply well and from a natural resurgence in a flooded collapse doline in the environs of Darlington, County Durham, northeast England. Measurements of both protein and “fulvic-like” fluorescence was undertaken from January to December 1999. The wavelengths of fulvic-like fluorescence excitation and emission and of protein fluorescence emission were all determined to be sensitive fingerprints of organic matter fluxes through the ground water, with water within the till and within both gypsum and limestone strata deep inside the Magnesian Limestone being differentiated by these parameters. Previous research has suggested that proteins in waters are “young” in age, hence our seasonal variations suggest that we are sampling recently formed DOM. The rapid response of all deep borehole samples suggests relatively rapid ground water flow, probably through karstic cave systems developed in the gypsum and solution widened features in the dolomitic limestone. Our results suggest that use of both protein and fulvic-like fluorescence wavelength variations provides a DOM signature that can be used as a natural tracer.
    Type of Medium: Electronic Resource
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  • 4
    Electronic Resource
    Electronic Resource
    [s.l.] : Nature Publishing Group
    Nature 364 (1993), S. 518-520 
    ISSN: 1476-4687
    Source: Nature Archives 1869 - 2009
    Topics: Biology , Chemistry and Pharmacology , Medicine , Natural Sciences in General , Physics
    Notes: [Auszug] Forty-three speleothem samples were collected from karst areas in the United Kingdom. After cutting along the axis of growth, 2-mm-thick polished sections were prepared. These were observed under a standard Zeiss microscope fitted with an IV Fl epi-fluorescence condenser containing a 50 W ...
    Type of Medium: Electronic Resource
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  • 5
    Publication Date: 2019-07-15
    Description: The oxygen isotope composition of speleothems is a widely used proxy for past climate change. Robust use of this proxy depends on understanding the relationship between precipitation and cave drip water δ18O. Here, we present the first global analysis, based on data from 163 drip sites, from 39 caves on five continents, showing that drip water δ18O is most similar to the amount-weighted precipitation δ18O where mean annual temperature (MAT) is 〈 10 °C. By contrast, for seasonal climates with MAT 〉 10 °C and 〈 16 °C, drip water δ18O records the recharge-weighted δ18O. This implies that the δ18O of speleothems (formed in near isotopic equilibrium) are most likely to directly reflect meteoric precipitation in cool climates only. In warmer and drier environments, speleothems will have a seasonal bias toward the precipitation δ18O of recharge periods and, in some cases, the extent of evaporative fractionation of stored karst water.
    Repository Name: EPIC Alfred Wegener Institut
    Type: Article , isiRev
    Format: application/pdf
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  • 6
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    Unknown
    PANGAEA
    In:  Supplement to: McDonough, Liza K; Santos, Isaac R; Andersen, Martin; O'Carroll, Denis; Rutlidge, Helen; Meredith, Karina; Oudone, Phetdala; Baker, Andy (2018): Changes in global groundwater organic carbon driven by climate change and urbanization. EarthArXiv Preprints, 11 pp, https://doi.org/10.31223/osf.io/vmaku
    Publication Date: 2023-03-14
    Description: This data set is predominantly sourced from the National Water Quality Monitoring Council (https://www.waterqualitydata.us/portal) and contains water quality data for the United States as well as climate and other ancillary data. This data was used to develop a model to explain groundwater dissolved organic carbon concentrations in the manuscript "Changes in global groundwater organic carbon driven by climate change and urbanization". Units for variables are included in the file "Units for Variables". --- National Water Quality Monitoring Council water chemistry data (https://www.waterqualitydata.us/portal) was obtained from: Chapelle, F. H., Bradley, P. M., Journey, C. A., & McMahon, P. B. (2013). Assessing the Relative Bioavailability of DOC in Regional Groundwater Systems. Ground water 51(3), doi:10.1111/j.1745-6584.2012.00987.x. --- Water table depth data obtained from: Fan, Y., Li, H., & Miguez-Macho, G. (2013). Global patterns of groundwater table depth. Science, 339, 940–943, doi:10.1126/science.1229881. --- Climatic data obtained from www.worldclim.org: Hijmans, R. J., Cameron, S. E., Parra, J. L., Jones, P. G., & Jarvis, A. (2005). Very high resolution interpolated climate surfaces for global land areas. International Journal of Climatology, 25, 1965-1978, doi:10.1002/joc.1276. --- Land use data obtained from: Channan, S., Collins, K., & Emanuel, W. R. (2014). Global mosaics of the standard MODIS land cover type data. University of Maryland and the Pacific Northwest National Laboratory, College Park, Maryland, USA. Retrieved from University of Maryland and the Pacific Northwest National Laboratory. - Friedl, M. A., Sulla-Menasche, D., Tan, B., Schneider, A., Ramankutty, N., Sibley, A., & Huang, X. (n.d.). MODIS Collection 5 global land cover: Algorithm refinements and characterization of new datasets, 2001-2012. Collection 5.1 IGBP Land Cover. Boston University, Boston, MA, USA.
    Keywords: Age, comment; Alabama; Area/locality; Arkansas; Arsenic; Calcium; California; Carbon, organic, dissolved; Chloride; Colorado; Conductivity, electrical; Connecticut; Continent; Country; Delaware; Depth, groundwater table; Depth, well; ELEVATION; Event label; Florida; Fluoride; Georgia; Idaho; Illinois; Indiana; Iowa; Iron; Kansas; Land use; LATITUDE; Lithology/composition/facies; LONGITUDE; Louisiana; Magnesium; Manganese; Maryland; Massachusetts; Michigan; Minnesota; Mississippi; Missouri; MULT; Multiple investigations; Nebraska; Nevada; New Hampshire; New Jersey; New Mexico; New York; North Carolina; North Dakota; Number; Ohio; Oklahoma; Oxygen, dissolved; Pennsylvania; pH; Potassium; Precipitation, annual mean; Precipitation, mean; Precipitation of the driest month; Precipitation of the wettest month; Ratio; Sample ID; Silica, dissolved; Sodium; South Carolina; South Dakota; Sulfate; Temperature, annual range; Temperature, coldest month, minimum; Temperature, mean; Temperature, range daily; Temperature, warmest month, maximum; Temperature, water; Temperature, water, annual mean; Tennessee; Texas; United States; US-AL; US-AR; US-CA; US-CO; US-CT; US-DE; US-FL; US-GA; US-IA; US-ID; US-IL; US-IN; US-KS; US-LA; US-MA; US-MD; US-MI; US-MN; US-MO; US-MS; US-NC; US-ND; US-NE; US-NH; US-NJ; US-NM; US-NV; US-NY; US-OH; US-OK; US-PA; US-SC; US-SD; US-TN; US-TX; US-UT; US-VA; US-VT; US-WA; US-WI; US-WV; US-WY; Utah; Vermont; Virginia; Washington; West Virginia; Wisconsin; Wyoming
    Type: Dataset
    Format: text/tab-separated-values, 232522 data points
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  • 7
    Publication Date: 2024-02-03
    Description: Stalagmites GL-S1, GL-S2, GL-S3 and GL-S4 were collected under scientific license issued by Western Australia's Department of Biodiversity, Conservation and Attractions from Golgotha Cave (34.1°S, 115.1°E) in southwest Western Australia, with collection dates of 2005, 2005, 2008 and 2012, respectively. Cave location is rounded to nearest tenth of a degree as exact locations not disclosed for cave conservation purposes. Speleothems were collected for paleoclimate and paleohydrology studies. Golgotha Cave is located in Eucalyptus forest with dense understorey in the Leeuwin-Naturaliste National Park. The hostrock is Quaternary aeolinite and the soil thickness is variable with measurements ranging from 0.3-3 m deep. The cave entrance is 70 m above sea level. Stalagmites GL-S1 and GL-S4 are located approximately 60 m from the entrance where the limestone thickness overhead is 30 m while GL-S2 and GL-S3 are located approximately 90 m from the entrance where the limestone thickness overhead is 40 m. Mean annual site temperature is 15.6 ±0.5°C and mean annual rainfall is 1101±157 mm (1911-2018 period; Australian Bureau of Meteorology AWRA-L dataset http://www.bom.gov.au/water/landscape. Inside the cave, temperature ranges from 14.5-14.8°C, windspeed is low (≤0.03 m s-1) and relative humidity ranges from 98-100% (Treble et al 2019). Each speleothem was sectioned along the growth axis and milled using a Taig micromill to produce homogenised powders representing increments of 0.1 to 0.2 mm, depending on the speleothem growth rate. Powders were weighed to 180–220 μg and analysed for O and C isotopic values (δ18O and δ13C) using a Finnigan MAT-251 isotope ratio mass spectrometer coupled to a Kiel I carbonate device, or a Thermo MAT-253 isotope ratio mass spectrometer coupled to a Kiel IV carbonate device (using 110–130 μg samples), at the Research School of Earth Sciences, ANU. Analyses were calibrated using NBS-19 standard (δ18Ov-PDB = -2.20 ‰ and δ13Cv-PDB = 1.95 ‰). A further linear correction for δ18O measurements was carried out using the NBS-18 standard (δ18Ov-PDB = -23.0 ‰). The original delta values for NBS-19 and NBS-18 are used to maintain consistency of results through time in the RSES Stable Isotope Facility. Analytical precision for the analyses reported here (NBS-19) are ±0.04 ‰ for δ18O and ±0.02 ‰ for δ13C (N=236) for the MAT-251; and ±0.05 ‰ for δ18O and ±0.01 ‰ (N=27) for the MAT-253 instrument (±1σ standard deviation). Speleothem chronologies were determined by combining information from the date of collection, bomb pulse chronology, laminae counting of annual Sr concentration and U-series disequilibrium (see Supplementary Table 8 in Treble et al., 2022). For GL-S1, the age-depth model for 17th percentile was used in Treble et al., (2022) and the 50th percentile used for other stalagmites.
    Keywords: Golgotha Cave; Last millennium; speleothem; stalagmite; Western Australia
    Type: Dataset
    Format: application/zip, 10 datasets
    Location Call Number Limitation Availability
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  • 8
    Publication Date: 2024-02-03
    Description: Stalagmite GL-S1 chronology in ka CE based on U/Th ages, bomb pulse 14C data and year of collection (2005). Treble et al. (2022) used 17th percentile age-depth model.
    Keywords: Age; Determined according to Treble et al. (2021); DISTANCE; Golgotha_Cave; Golgotha Cave; Last millennium; speleothem; stalagmite; Western Australia
    Type: Dataset
    Format: text/tab-separated-values, 260 data points
    Location Call Number Limitation Availability
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  • 9
    Publication Date: 2024-02-03
    Description: GolgothaCave_GLS1_stalagmite_O&C_isotopes: median depth, d18O and d13C values in VPDB. Chronology is that used for Treble et al (2022).
    Keywords: Age; Determined according to Treble et al. (2021); DISTANCE; Golgotha_Cave; Golgotha Cave; Last millennium; Mass spectrometer Finnigan MAT 251; Sample ID; speleothem; stalagmite; Western Australia; δ13C; δ18O
    Type: Dataset
    Format: text/tab-separated-values, 532 data points
    Location Call Number Limitation Availability
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  • 10
    Publication Date: 2024-02-03
    Description: Dripwater was collected every 4-6 weeks from Golgotha Cave (34.1°S, 115.1°E) in southwest Western Australia from 2005 until 2019, although beginning in 2008 for site 2E and in 2013 for site 1IV. Cave location is rounded to nearest tenth of a degree as exact locations not disclosed for cave conservation purposes. Dripwaters were collected for paleoclimate and paleohydrology studies. Data from August 2005 until March 2012 were previously published in Treble et al. (2013) and the longer dataset in Treble et al (2021). Please cite Treble et al. (2013, 2021) when using these data. Dripwaters were collected at 4-6 week intervals from bulk 1 L high-density polyethylene collection vessels, fitted with funnels, that were emptied following collection of water for analyses. Drip rates were manually timed during each collection visit. The drip sites pair with stalagmites collected from these locations as follows: site 1A (GL-S1), site 1IV (GL-S4), site 2B (GL-S2), site 2E (GL-S3). Stable water isotopes (δ18O and δ2H) collected between August 2005 and April 2011 were determined by: 1. offline equilibration technique at the Research School of Earth Sciences, Australian National University; 2. using an LGR-24 d cavity ringdown mass spectrometer at the University of New South Wales for samples from May 2011-March 2012; and 3. using Picarro L2120-I Water Analyser at ANSTO from 2012 onwards. Analytical error all techniques was 0.1 ‰ (1 s.d.; calculated from within-run internal references materials). See citations in Treble et al. (2013) for details of methods. Golgotha Cave is located in Eucalyptus forest with dense understorey in the Leeuwin-Naturaliste National Park. The hostrock is Quaternary aeolinite and the soil thickness is variable with measurements ranging from 0.3 – 3 m deep. The cave entrance is 70 m above sea level. Dripwater sites 1A, 1IV are located approximately 60 m from the entrance where the limestone thickness overhead is 30 m while dripwater sites 2B and 2E are located approximately 90 m from the entrance where the limestone thickness overhead is 40 m. Mean annual site temperature is 15.6 ±0.5°C and mean annual rainfall is 1101±157 mm (1911-2018 period; Australian Bureau of Meteorology AWRA-L dataset http://www.bom.gov.au/water/landscape. Inside the cave, temperature ranges from 14.5-14.8°C, windspeed is low (≤0.03 m s-1) and relative humidity ranges from 98-100% (Treble et al 2019). Rainfall water isotope measurements from Calgardup Cave, located 5 km from Golgotha Cave and complimentary to this dataset, are available from the IAEA Water Isotope System for data analysis, visualization and Electronic Retrieval, https://nucleus.iaea.org/wiser/ using station code 9564101.
    Keywords: cave monitoring; dripwater; water isotopes; Western Australia
    Type: Dataset
    Format: application/zip, 3 datasets
    Location Call Number Limitation Availability
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