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  • 1
    Call number: AWI G4-95-0109
    Type of Medium: Monograph available for loan
    Pages: xxvi, 293 S. , graph. Darst.
    Note: Contents: Extended Summary. - 1 Introduction. - 2 Susceptibility of Soils to Preferential Flow of Water: A Field Study. - 2.1 Introduction. - 2.2 Materials and Methods. - 2.2.1 Soils. - 2.2.2 Dye Tracer. - 2.2.3 Experimental Design. - 2.2.4 Sprinkling Apparatus. - 2.2.5 Flood Irrigation. - 2.2.6 Analysis of Data. - 2.3 Results and Discussion. - 2.3.1 Infiltration Patterns. - 2.3.2 Maximum Depth of Dye Penetration. - 2.3.3 Effect of Initial Water Content. - 2.3.4 Sprinkling versus Flood Irrigation. - 2.4 Conclusion. - 3 Transport of Herbicides: Experimental Results. - 3.1 Introduction. - 3.2 Materials and Methods. - 3.2.1 Experimental Site. - 3.2.2 Experimental Setup. - 3.2.3 Tracer Experiment. - 3.2.4 Chemical Analysis. - 3.3 Results. - 3.3.1 Water Content and Water Potential. - 3.3.2 Anions and Herbicides. - 3.4 Discussion. - 3.5 Conclusions. - 4 Transport of Herbicides: Modeling of Flow in Sandy Soil. - 4.1 Introduction. - 4.2 Theory. - 4.2.1 Assumptions. - 4.2.2 Model. - 4.2.3 Application. - 4.3 Estimation of Parameters. - 4.4 Results and Discussion. - 4.5 Conclusions. - 5 Transport of Herbicides: Modeling of Flow in Loamy Soil. - 5.1 Introduction. - 5.2 Theory. - 5.2.1 Local Interaction Models. - 5.2.2 Linking Local Interaction Models to DLA. - 5.3 Illustrations. - 5.4 Application to the Tracer Field Experiment. - 5.5 Discussion and Conclusions. - 6 Cooperative Research at University of California, Riverside. - 6.1 Introduction. - 6.2 Linear Transport Models for Adsorbing Solutes. - 6.3 Transport of Bromide, Simazine, and MS-2 Coliphage in a Lysimeter containing undisturbed, unsaturated Soil. - 6.4 Description of Simazine Transport with rate-limited, two-step linear and nonlinear Adsorption. - 6.5 Conclusions. - 7 Conclusions and Recommendations. - 7.1 Conclusions. - 7.2 Recommendations. - APPENDICES. - A Extraction and Analysis of Anions (Chloride and Bromide) from Soil Samples. - A.1 Preface. - A.1.1 General Information. - A.1.2 Guidelines. - A.1.3 Purpose. - A.2 Materials and Methods. - A.2.1 Chemicals. - A.2.2 Extraction of Soil Samples. - A.2.3 Analysis of Anions by HPLC. - B Extraction and Analysis of Triazines (Atrazine and Terbuthylazine) from Soil Samples. - B .1 Preface. - B.1.1 General Information. - B.1.2 Guidelines. - B.1.3 Purpose. - B.2 Materials and Methods. - B.2.1 Chemicals. - B.2.2 Materials. - B.2.3 Extraction of Soil Samples. - B.2.4 Analysis of Pesticides by GC. - B.3 Results. - C Extraction of Triasulfuron from Soil Samples. - C.1 Preface. - C.1.1 General Information. - C.1.2 Guidelines. - C.1.3 Purpose. - C.2 Materials and Methods. - C.2.1 Chemicals. - C.2.2 Materials. - C.2.3 Extraction of Soil Samples. - C.2.4 Analysis of Triasulfuron by Chemoluminescence-immunoassay. - C.2.5 Calculation of concentrations. - C.3 Results. - D Influence of Brilliant Blue FCF on the Adsorption Behavior of Atrazine and Triasulfuron. - D.1 Preface. - D.1.1 General Information. - D.1.2 Guidelines. - D.1.3 Purpose. - D.2 Materials and Methods. - D.2.1 Chemicals. - D.2.2 Apparatus. - D.2.3 Adsorption Experiments. - D.3 Results and Discussion. - E Sprinklingapparatur zur Simulation ungesättigten Stofftransportes in Feldböden. - F Begriffliche Ver(w)irrung: Pflanzenschutzmittel oder Pestizide ; Eine semantische Betrachtung. - G Bromide in the Natural Environment: Occurrence and Toxicity. - H Brilliant Blue FCF as a Dye Tracer for Solute Transport Studies - a Toxicological Overview. - I Tracer Characteristics of Brilliant Blue FCF. - J Glossary of Symbols. - Bibliography.
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  • 2
    Call number: AWI G3-23-94987
    In: Dissertation / Eidgenössische Technische Hochschule Zürich, Nr. 11574
    Type of Medium: Series available for loan
    Pages: XIII, 137 Seiten , Illustrationen
    Series Statement: Dissertation / Eidgenössische Technische Hochschule Zürich No. 11574
    Language: English
    Note: Contents Kurzfassung Summary 1 Introduction 1.1 Water Regime of Mountain Forests in Winter 1.2 Thermodynamics of Frozen Soils 1.3 Water Flow Pathways in Frozen Soils 1.4 Water Infiltration into and Runoff from Frozen Soils 1.5 Objectives and Outline of this Study 2 Field Measurements of Water Transport in Frozen Soils 2.1 Abstract 2.2 Introduction 2.3 Materials and Methods 2.3.1 Test Site 2.3.2 Instrumentation 2.3.3 Soil Physical Properties 2.4 Results and Discussion 2.4.1 Entire Observation Period 2.4.2 Particular Snowmelt Events 2.4.3 Water Balance of Particular Snowmelt Events 2.5 Summary and Conclusions 3 Water and Solute Dynamics in Freezing Soil Columns 3.1 Abstract 3.2 Introduction 3.3 Materials and Methods 3.3.1 Experimental Setup 3.3.2 Determination of the Liquid Water Content 3.3.3 Determination of the Solute Concentration 3.3.4 Model Approach for the Freezing Characteristic Curve 3.4 Results and Discussion 3.4.l Calibration Results 3.4.2 The Freezing and Thawing Cycle 3.4.3 Freezing Characteristic Curves 3.5 Conclusions 4 Modelling Runoff Dynamics in Sloped Frozen Soils 4.1 Abstract 4.2 Introduction 4.3 Model Description 4.4 Model Application 4.5 Results and Discussion 4.5.1 Sensitivity Analysis 4.5.2 Model Calibration 4.5.3 Model Validation 4.5.4 Influence of Temporal Resolution on Model Output 4.5.5 Climate Change Scenarios 4.6 Summary and Conclusions 5 Concluding Remarks Appendices A Additional Field Measurements B Additional Cold-laboratory Measurements C Model Parameter File List of Symbols List of Figures List of Tables Bibliography Curriculum Vitae
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  • 3
    Call number: AWI G4-22-95044
    Type of Medium: Monograph available for loan
    Pages: 145 Seiten , Illustrationen , 23 cm
    ISBN: 3728125768 (kart.)
    Series Statement: Schlußbericht NFP 31
    Language: German
    Note: Inhaltsverzeichnis Zusammenfassung Résumé Summary 1 Einführung 1.1 Hydrologie des Gebirgswaldes im Winter 1.2 Arbeitshypothesen 1.3 Methodischer Ansatz 2 Standorte und Methoden 2.1 Standortwahl 2.2 Untersuchungsstandorte und deren Instrumentierung 2.2.1 Testfläche Davos 2.2.2 Testfläche Alptal 2.3 Verarbeitung der Bilder zur Schneeinterzeption 2.4 Modellierung des Wasser- und Wärmehaushaltes 2.4.1 Modellbeschrieb 2.4.2 Modellanwendung und Klimaszenarien 3 Ergebnisse der Feldmessungen 3.1 Winterverläufe in Davos und im Alptal 3.1.1 Davos 1993/94 3.1.2 Davos 1992/93 3.1.3 Alptal 1993/94 3.1.4 Standort vergleich des Interzeptionsverhaltens 3.1.5 Standortvergleich des Abflussverhaltens 3.2 Einzelereignisse im Alptal und in Davos 3.2.1 Testfläche Alptal 3.2.2 Testfläche Davos 3.3 Wassertransport in der Waldschneedecke 3.4 Zusammenfassung der Feldbeobachtungen 4 Ergebnisse der Modellsimulationen 4.1 Modellkalibrierung 4.1.1 Baumfläche Davos - Winter 1992/93 95 4.1.2 Baumfläche Alptal - Winter 1993/94 und Sommer 1994 4.2 Modelltest 4.2.1 Baurnfläche Davos - Winter 1993/94 4.2.2 Lichtungsfläche Davos - Winter 1993/94 4.3 Simulationen mit heutigen und veränderten Klimabedingungen 4.3.1 Vergleich des gemessenen und stochastisch simulierten Wetters 4.3.2 Auswirkungen einer Klimaänderung in Davos 4.3.3 Auswirkungen einer Klimaänderung im Alptal 4.4 Zusammenfassung der Modellergebnisse 5 Schlussbemerkungen Abbildungsverzeichnis Tabellenverzeichnis Literaturverzeichnis , Zusammenfassung in französischer und englischer Sprache
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  • 4
    Call number: AWI G4-23-95001
    Type of Medium: Monograph available for loan
    Pages: ii, 62 Seiten , Illustrationen
    Language: English
    Note: Contents Summary Introduction Material and Methods 2.1 Experimental Approach and Concept 2.2 Cold Chamber Experiments 2.2.1 Packed Sand Columns 2.2.2 Undisturbed Soil Monolith 2.3 Tracer Extraction and Determination of Tracer Concentrations 2.4 Digital Image Analysis 2.4.1 Photographic Recording 2.4.2 Image Analysis 2.4.3 Statistical Regression Analysis 2.5 Fluorescence Imaging 2.6 Low-Temperature SEM and X-Ray Analysis 2.7 Numerical Simulation 2.7.1 Model Description 2.7.2 Model Application 3 Results From Cold Chamber Experiments 3.1 Packed Sand Columns (Experiment I-III) 3.1.1 Infiltration Behaviour (Experiment I-III) 3.1.2 Dye Tracer Distribution (Experiment III) 3.1.3 Mass Recovery of Dye Tracers (Experiment III) 3.1.4 Vertical Distribution of Dye Tracers Determined From Large Sections (Experiment III) 3.2 Undisturbed Soil Monolith (Experiment IV) 3.2.1 Infiltration Behaviour 3.2.2 Dye Tracer Distributions 3.2.3 Mass Recovery of all Tracers Determined From Large Sections 3.2.4 Vertical Distribution of all Tracers Determined From Large Sections 4 Results From Low-Temperature SEM and X-Ray Analysis 4.1 Dry Sand and Loam 4.2 Wet Sand 4.3 Wet Loam 5 Modelling Results 5.1 Thermal Regime 5.2 Water Content Profile Before the Irrigation 5.3 Infiltration Behaviour 5.4 Water Content Profile After the Irrigation 5.5 Solute Transport 5.6 Energy Exchange at the Surface 6 Conclusions 6.1 Conclusions About the Methods 6.2 Conclusions About the Water Infiltration in Frozen Soil List of Figures List of Tables Bibliography
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  • 5
    Electronic Resource
    Electronic Resource
    Springer
    Water, air & soil pollution 68 (1993), S. 275-289 
    ISSN: 1573-2932
    Source: Springer Online Journal Archives 1860-2000
    Topics: Energy, Environment Protection, Nuclear Power Engineering
    Notes: Abstract In many studies on solute transport soil column experiments arc used to obtain the transport characteristics for Convection-Dispersion-Models. Early breakthrough of the solute pulse has been attributed to a non-equilibrium in phase exchange. It is a standard procedure to determine several model parameter values from such breakthrough curves (BTC). This investigation is focused on the physical significance of simultaneously fitted parameter values used in the convection and diffusion-controlled mass transfer model (mobile — immobile phase concept). Saturated column experiments were conducted with solid phases consisting of porous and solid glass beads. One set of model parameter values was obtained from the breakthrough curves by simultaneous optimization and a second set was determined by independent measurements of individual parameter values. Both sets of parameter values described the BTCs equally well but deviated substantially from each other. These discrepancies were analysed in terms of local parameter sensitivities.
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  • 6
    Electronic Resource
    Electronic Resource
    Springer
    Water, air & soil pollution 68 (1993), S. 291-305 
    ISSN: 1573-2932
    Source: Springer Online Journal Archives 1860-2000
    Topics: Energy, Environment Protection, Nuclear Power Engineering
    Notes: Abstract Transport of volatile hydrocarbons in soils is largely controlled by interactions of vapours with the liquid and solid phase. Sorption on solids of gaseous or dissolved compounds may be important. Since the contact time between a chemical and a specific sorption site can be rather short, kinetic or mass-transfer resistance effects may be relevant. An existing mathematical model describing advection and diffusion in the gas phase and diffusional transport from the gaseous phase into an intra-aggregate water phase is modified to include linear kinetic sorption on gas-solid and water-solid interfaces. The model accounts for kinetic mass transfer between all three phases in a soil. The solution of the Laplace-transformed equations is inverted numerically. We performed transient column experiments with 1,1,2-Trichloroethane, Trichloroethylene, and Tetrachloroethylene using air-dry solid and water-saturated porous glass beads. The breakthrough curves were calculated based on independently estimated parameters. The model calculations agree well with experimental data. The different transport behaviour of the three compounds in our system primarily depends on Henry's constants.
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  • 7
    Electronic Resource
    Electronic Resource
    Springer
    Environmental modeling and assessment 1 (1996), S. 151-158 
    ISSN: 1573-2967
    Keywords: Data worth model ; risk analysis ; parameter uncertainty ; spatial variability ; Bayesian statistics ; geostatistics
    Source: Springer Online Journal Archives 1860-2000
    Topics: Energy, Environment Protection, Nuclear Power Engineering
    Notes: Abstract A data worth model is presented for the analysis of alternative sampling schemes in a special project where decisions have to be made under uncertainty. This model is part of a comprehensive risk analysis algorthm with the acronym BUDA. The statistical framework in BUDA is Bayesian in nature and incorporates both parameter uncertainty and natural variability. In BUDA a project iterates among the analyst, the decision maker, and the field work. As part of the analysis, a data worth model calculates the value of a data campaign before the actual field work, thereby allowing the identification of an optimum data collection scheme. A goal function which depicts the objectives of a project is used to discriminate among different alternatives. A Latin hypercube sampling scheme is used to propagate parameter uncertainties to the goal function. In our example the uncertain parameters are the parameters which describe the geostatistical properties of saturated hydraulic conductivity in a Molasse environment. Our results indicated that failing to account for parameter uncertainty produces unrealistically optimistic results, while ignoring the spatial structure can lead to an inefficient use of the existing data.
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  • 8
    Electronic Resource
    Electronic Resource
    Springer
    Water, air & soil pollution 68 (1993), S. ix 
    ISSN: 1573-2932
    Source: Springer Online Journal Archives 1860-2000
    Topics: Energy, Environment Protection, Nuclear Power Engineering
    Type of Medium: Electronic Resource
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  • 9
    Publication Date: 2002-01-01
    Print ISSN: 0361-5995
    Electronic ISSN: 1435-0661
    Topics: Geosciences , Agriculture, Forestry, Horticulture, Fishery, Domestic Science, Nutrition
    Published by Wiley
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  • 10
    Publication Date: 2002-01-01
    Print ISSN: 0361-5995
    Electronic ISSN: 1435-0661
    Topics: Geosciences , Agriculture, Forestry, Horticulture, Fishery, Domestic Science, Nutrition
    Published by Wiley
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