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  • 1
    Online Resource
    Online Resource
    Newark :John Wiley & Sons, Incorporated,
    Keywords: Soils-Environmental aspects. ; Electronic books.
    Type of Medium: Online Resource
    Pages: 1 online resource (352 pages)
    Edition: 1st ed.
    ISBN: 9781119480471
    Series Statement: Wiley Series Sponsored by IUPAC in Biophysico-Chemical Processes in Environmental Systems Series
    Language: English
    Note: Cover -- Title Page -- Copyright Page -- Contents -- Series Preface -- Preface -- List of Contributors -- Chapter 1 Introduction: Working Across Scales to Project Soil Biogeochemical Responses to Climate -- 1.1. Context -- 1.2. Soil Responses to Environmental Conditions at Diverse Scales: Organic Matter Transformations and Feedbacks to Climate -- 1.2.1. Organic Matter at the Microscale -- 1.2.2. Organic Matter at the Mesocosm Scale -- 1.2.3. Organic Matter at the Plot and Decadal Scale -- 1.2.4. Organic Matter at Ecosystem to Landscape Scales Across Years to Decades -- 1.3. Recent Empirical Investigations of Soil Responses to Environmental Conditions at Diverse Scales: Mineral Weathering -- 1.3.1. Mineral Weathering at the Column or Mesocosm Scale -- 1.3.2. Mineral Weathering at the Ecosystem to Landscape Scale Across Diverse Temporal Scales -- 1.4. Cross-Scale Discrepancies: Two Examples of Nonlinearities That Challenge Predictive Abilities -- 1.5. Models as a Means of Integrating Across Disciplines and Scales -- 1.6. Conclusions -- Acknowledgments -- References -- SECTION 1 Molecular-scale Processes and Critical Reactions -- Chapter 2 The Science and Semantics of "Soil Organic Matter Stabilization" -- 2.1. The Cycling of Organic Matter in Soil -- 2.2. What Is "Stability?" -- 2.2.1. The Paradigm of Chemical Stability (I): Humification and Humic Substances -- 2.2.2. The Paradigm of Chemical Stability (II): Litter Quality -- 2.2.3. The Paradigm of Chemical Stability (III): Molecular Complexity and Activation Energies -- 2.2.4. The Paradigm of Chemical Stability (IV): Plastics and Black Carbon -- 2.3. The Paradigm of Sorptive Protection/Interactions -- 2.4. The Paradigm of Accessibility: Aggregation -- 2.5. The Paradigm of Accessibility: How Location Matters -- 2.6. Microbial Metabolic Performance as a Factor in Soil Carbon Cycling. , 2.7. Habitat Properties as Logistical Constraints -- 2.8. Habitat Properties and Reactant Supply -- 2.8.1. Habitat Properties Determine the Thermodynamics of Decomposition -- 2.8.2. Decomposition and Decomposer Needs: Microbial Carbon Use Efficiency -- 2.8.3. Decomposition and Decomposer Needs: Resource Stoichiometry -- 2.8.4. Plants as an Interested Party in Soil Organic Matter Decomposition -- 2.9. Conclusions -- References -- Chapter 3 Interconnecting Soil Organic Matter with Nitrogen and Phosphorus Cycling -- 3.1. Soil Organic Matter: The Key Player for Controlling Nutrient Cycling -- 3.2. Nitrogen -- 3.2.1. Introduction -- 3.2.2. Biological N Fixation -- 3.2.3. Organic N Stabilization and Depolymerization -- 3.2.4. Microbial Utilization of N in Soils -- 3.2.5. Microbial N Oxidation and Reduction -- 3.2.6. Plant N Uptake as a Function of Resource Availability -- 3.3. Phosphorus -- 3.3.1. Introduction -- 3.3.2. Abiotic Processes -- 3.3.3. Organic P Dynamics and P Recycling -- 3.3.4. Microbial P in Soil -- 3.3.5. Plant and Microbial Strategies for P Uptake -- 3.3.6. Plant P Uptake as Related to Internal Plant Nutritional Status and Soil P Availability -- 3.4. Conclusions -- References -- Chapter 4 Plant-Derived Macromolecules in the Soil -- 4.1. Introduction -- 4.2. Plant Macromolecules as Inputs into the Soil -- 4.2.1. Cellulose and Hemicellulose -- 4.2.2. Lignin -- 4.2.3. Proteins -- 4.2.4. Tannins and Other Polyphenols -- 4.2.5. Cutin, Suberin, and Free Extractable Lipids -- 4.2.6. Other Molecules -- 4.3. Fraction-Specific Molecular Analyses -- 4.3.1. Biomarkers -- 4.3.2. Compound-specific Isotope Analysis (CSIA) -- 4.3.3. Other Complementary Methods -- 4.4. Fate of Plant-Derived Compounds in the Soil -- 4.4.1. Microbial Degradation -- 4.4.2. Abiotic Degradation -- 4.4.3. Movement in the Soil Through Leaching Processes. , 4.4.4. Preservation Mechanisms -- 4.4.5. Turnover of Plant-Derived Molecules -- 4.5. Root- Versus Shoot-Derived Carbon in the Soil -- 4.6. Conclusions -- References -- Chapter 5 Microbe-Biomolecule-Mineral Interfacial Reactions -- 5.1. Introduction -- 5.2. Microbial Colonization of Rock -- 5.2.1. Initial Colonizers of Fresh Mineral Substrate -- 5.3. Mechanisms of Cell Adhesion to Mineral Surfaces -- 5.3.1. Bacterial Surface Geochemistry -- 5.3.2. Bacterial Adhesion at Mineral Surfaces -- 5.4. Mineral Surface Reactions of Extracellular Biomolecules -- 5.4.1. Composition of Extracellular Polymeric Substances (EPS) -- 5.4.2. Adsorption and Fractionation of EPS at Mineral Surfaces -- 5.5. Heteroaggregate Formation -- 5.6. Conclusions and Future Outlook -- References -- SECTION 2 Ecosystem-scale Studies of Ecological Hotspots -- Chapter 6 Greenhouse Gas Emissions in Wetland Rice Systems: Biogeochemical Processes and Management -- 6.1. Introduction -- 6.2. Carbon Biogeochemistry -- 6.2.1. Anaerobic C Pathways -- 6.2.3. Dissolved Organic C -- 6.2.4. CH4 Production, Consumption, and Emission -- 6.2.5. Mitigation Strategies -- 6.3. N Cycles -- 6.3.1. Biogeochemical Pathways -- 6.3.2. N2O Production, Consumption, and Emission -- 6.4. Future Directions -- References -- Chapter 7 The Changing Biogeochemical Cycles of Tundra -- 7.1. Introduction -- 7.2. The Changing Tundra Carbon Cycle -- 7.2.1. Soil Carbon Accumulation -- 7.2.2. Carbon Balance -- 7.2.3. Carbon Inputs -- 7.2.4. Carbon Outputs: CO2 -- 7.2.5. Carbon Outputs: Methane -- 7.3. Changing Tundra Nutrient Cycles -- 7.3.1. Nutrient Limitation -- 7.3.2. Nutrient Stocks -- 7.3.3. The Changing Nitrogen Cycle -- 7.3.4. The Changing Phosphorus Cycle -- 7.3.5. Nutrient Leaching -- 7.3.6. Effects of Fire on Nutrient Cycles -- 7.4. Future Projections -- 7.5. Future Research Directions -- References. , Chapter 8 Linking Sources, Transformation, and Loss of Phosphorus in the Soil-Water Continuum in a Coastal Environment -- 8.1. Phosphorus: An Essential Nutrient Turned into a Contaminant -- 8.2. Transformation of Phosphorus in Soils -- 8.2.1. Transformation of P Pools in Soils Impacted by Agricultural P Loading -- 8.2.2. Formation of Residual and Recalcitrant P Pools in Soils -- 8.3. Surface and Subsurface Flow of Phosphorus from Agricultural Soils to Open Water -- 8.4. Transport of Phosphorus in the Main Channel and Export to Open Waters -- 8.5. Source Tracking of P Released from Soils and Upland Watershed -- 8.6. Implication and Future Research Directions -- Acknowledgments -- References -- Chapter 9 Deep Soil Carbon -- 9.1. Introduction -- 9.2. How Much Carbon Is Stored in the Subsoil? -- 9.3. How Does Carbon Accumulate at Depth? -- 9.4. Factors Contributing to Deep Soil Carbon Persistence -- 9.4.1. Climate -- 9.4.2. Parent Material and Time -- 9.4.3. Relief and Soil Redistribution -- 9.4.4. Biota -- 9.5. Vulnerability of Deep Soil Carbon -- 9.5.1. Land Management -- 9.5.2. Climate Change -- 9.5.3. Disturbance of Buried Soils -- 9.6. Improving Predictions of Deep Soil Carbon -- 9.7. Conclusions -- Acknowledgments -- References -- SECTION 3 Modeling Biogeochemical Cycles and Improvement of Ecosystem Resilience -- Chapter 10 Soil Carbon Dynamics and Responses to Environmental Changes -- 10.1. Introduction -- 10.2. Soil C Inventory -- 10.2.1. Top and Deep Soil C Inventory -- 10.2.2. Global Soil C Stock -- 10.2.3. Permafrost - A Huge Soil C Pool -- 10.2.4. Soil C Inventory Methods -- 10.3. Soil C Dynamics -- 10.3.1. Soil C Input Processes -- 10.3.2. Soil C Output Processes -- 10.3.3. Depth-dependent Soil C Balance -- 10.4. Climate Warming and Soil Carbon -- 10.4.1. Temperature Sensitivity of Different Soil Organic C Pools. , 10.4.2. Thermal Acclimation of Soil Organic C Decomposition -- 10.4.3. Soil Organic C Fraction, Composition, and Stability -- 10.5. Precipitation Change and Soil Carbon -- 10.5.1. Precipitation Amounts -- 10.5.2. Seasonal Rainfall Redistribution -- 10.5.3. Extremes and Precipitation Variability -- 10.5.4. Multifactor and Long-term Experiments -- 10.6. Nitrogen Deposition and Soil Carbon -- 10.6.1. Effects of N Deposition on Quantity and Quality of Plant C Input to Soil -- 10.6.2. Effects Caused by Community Composition Changes -- 10.6.3. Effects of N Deposition on Soil Microbial Activity -- 10.6.4. Effects of N Deposition on Soil Physicochemical Properties -- 10.7. Uncertainties in Modeling Soil C Dynamics -- 10.7.1. Model Structures -- 10.7.2. Poor Representation of Microbial Control on Soil C Cycles -- 10.7.3. Poor Representation of Vertical Soil C Cycles in ESMs -- 10.7.4. Underestimated Soil C Turnover Time in ESMs -- 10.8. Outlook: Neglected Facts and Future Research Directions -- 10.8.1. Neglected Facts About Permafrost Processes -- 10.8.2. Neglected Facts About Human Interferences -- 10.8.3. Neglected Facts About Phosphorus Processes -- 10.9. Conclusions -- References -- Chapter 11 Next-generation Soil Biogeochemistry Model Representations: A Proposed Community Open-source Model Farm (BeTR-S) -- 11.1. Introduction -- 11.2. Proposed SOM Model Structure -- 11.2.1. Litter Input and Polymeric OM Hydrolysis (P1) -- 11.2.2. Microbial Physiology, Microbial Population Dynamics, and Macronutrient Controls (P2) -- 11.2.3. Trophic Interactions and Competition (P3) -- 11.2.4. Mineral-Organic Interactions (P4) -- 11.2.5. Soil Chemistry: Cation Exchange Capacity, pH, Redox, and Salinity (P5) -- 11.2.6. Rhizosphere-Bulk Soil Interactions (P6) -- 11.2.7. Soil Structure, Aggregation, Transport (P7). , 11.3. Mathematical Integration and Solution in the BeTR-S Model Farm.
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  • 2
    Online Resource
    Online Resource
    Newark :John Wiley & Sons, Incorporated,
    Keywords: Environmental chemistry. ; Electronic books.
    Type of Medium: Online Resource
    Pages: 1 online resource (341 pages)
    Edition: 1st ed.
    ISBN: 9780470511190
    Series Statement: Series on Analytical and Physical Chemistry of Environmental Systems Series ; v.11
    DDC: 577.14
    Language: English
    Note: Intro -- Biophysical Chemistry of Fractal Structures and Processes in Environmental Systems -- Contents -- About the Editors -- List of Contributors -- Series Preface -- Preface -- 1 Introduction to the Study of Environmental Fractals -- 2 Introduction to Fractal Geometry, Fragmentation Processes and Multifractal Measures: Theory and Operational Aspects of their Application to Natural Systems -- 3 Methods and Techniques for Fractal Analysis of Environmental Systems -- 4 Fractal Structures and Mechanisms in Coagulation/Flocculation Processes in Environmental Systems: Theoretical Aspects -- 5 Fractal Mechanisms in Coagulation/Flocculation Processes in Environmental Systems -- 6 Fractal Approach to Adsorption/Desorption Processes on Environmental Surfaces -- 7 Applications of Fractals in the Study of Humic Materials -- 8 Fractal Geometry and Microorganisms in the Environment -- 9 Fractal Geometry of Aerosol Particles -- Index.
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  • 3
    Online Resource
    Online Resource
    Newark :John Wiley & Sons, Incorporated,
    Keywords: Bioorganic chemistry. ; Electronic books.
    Type of Medium: Online Resource
    Pages: 1 online resource (905 pages)
    Edition: 1st ed.
    ISBN: 9780470494943
    Series Statement: Wiley Series Sponsored by IUPAC in Biophysico-Chemical Processes in Environmental Systems Series ; v.2
    DDC: 577/.14
    Language: English
    Note: Intro -- BIOPHYSICO-CHEMICAL PROCESSES INVOLVING NATURAL NONLIVING ORGANIC MATTER IN ENVIRONMENTAL SYSTEMS -- CONTENTS -- Series Preface -- Preface -- About the Editors -- List of Contributors -- 1 Evolution of Concepts of Environmental Natural Nonliving Organic Matter -- 2 Formation Mechanisms of Humic Substances in the Environment -- 3 Organo-Clay Complexes in Soils and Sediments -- 4 The Effect of Organic Matter Amendment on Native Soil Humic Substances -- 5 Carbon Sequestration in Soil -- 6 Storage and Turnover of Organic Matter in Soil -- 7 Black Carbon and Thermally Altered (Pyrogenic) Organic Matter: Chemical Characteristics and the Role in the Environment -- 8 Biological Activities of Humic Substances -- 9 Role of Humic Substances in the Rhizosphere -- 10 Dissolved Organic Matter (DOM) in Natural Environments -- 11 Marine Organic Matter -- 12 Natural Organic Matter in Atmospheric Particles -- 13 Separation Technology as a Powerful Tool for Unfolding Molecular Complexity of Natural Organic Matter and Humic Substances -- 14 Analytical Pyrolysis and Soft-Ionization Mass Spectrometry -- 15 Nuclear Magnetic Resonance Analysis of Natural Organic Matter -- 16 EPR, FTIR, Raman, UV-Visible Absorption, and Fluorescence Spectroscopies in Studies of NOM -- 17 Synchrotron-Based Near-Edge X-Ray Spectroscopy of NOM in Soils and Sediments -- 18 Thermal Analysis for Advanced Characterization of Natural Nonliving Organic Materials -- Index.
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  • 4
    Online Resource
    Online Resource
    Newark :John Wiley & Sons, Incorporated,
    Keywords: Nanoparticles--Toxicology. ; Nanoparticles--Environmental aspects. ; Electronic books.
    Type of Medium: Online Resource
    Pages: 1 online resource (509 pages)
    Edition: 1st ed.
    ISBN: 9781119275831
    Series Statement: Wiley Series Sponsored by IUPAC in Biophysico-Chemical Processes in Environmental Systems Series
    Language: English
    Note: Intro -- Engineered Nanoparticles and the Environment -- Contents -- Series Preface -- Preface -- List of Contributors -- PART I Synthesis, Environmental Application, Detection, and Characterization of Engineered Nanoparticles -- 1 Challenges Facing the Environmental Nanotechnology Research Enterprise -- 1.1 Introduction -- 1.1.1 Environmental Applications of Engineered Nanoparticles -- 1.1.2 Environmental Implications of Engineered Nanoparticles -- 1.2 Current Challenges in Environmental Nanotechnology -- 1.2.1 Physicochemical Transformations of Nanomaterials -- 1.2.2 Nanometrology in Environmental Systems -- 1.2.3 Nanotoxicology: Experimental Approaches and Modeling -- 1.2.4 Exposure Modeling for Risk Assessment -- 1.3 Conclusions -- References -- 2 Engineered Nanoparticles for Water Treatment Application -- 2.1 Introduction: an Emerging Water Problem -- 2.1.1 Global Water Scarcity -- 2.1.2 Global Water Contamination -- 2.2 Water Purification Processes Using Nanoparticles -- 2.2.1 Nano-Sized Adsorbents -- 2.2.2 Adsorption of Water Pollutants Using Nanoparticles -- 2.3 Conclusions and Future Perspectives -- References -- 3 Mass Spectrometric Methods for Investigating the Influence of Surface Chemistry on the Fate of Core-Shell Nanoparticles in Biological and Environmental Samples -- 3.1 Introduction -- 3.2 Core-Shell Nanoparticles -- 3.2.1 Nanoparticle Definitions -- 3.2.2 Gold Nanoparticle Synthesis -- 3.2.3 Nanoparticle Surface Chemistry Design -- 3.3 Effect of Surface Chemistry on Nanoparticle Uptake -- 3.3.1 Nanoparticle Uptake into Cells -- 3.3.2 Nanoparticle Uptake and Distributions in Fish -- 3.3.3 Nanoparticle Uptake and Distributions in Plants -- 3.4 Laser DesorptionIonization Mass Spectrometry for Tracking Nanoparticles in Complex Mixtures -- 3.4.1 Mass Spectrometry -- 3.4.2 LDI-MS of Nanoparticles. , 3.4.3 Scope of the LDI-MS Method for Detecting Other Core-Shell Nanoparticles -- 3.4.4 Multiplexed Analysis of Nanoparticles by LDI-MS -- 3.4.5 Monitoring Nanoparticle Monolayer Stability in Biological Samples -- 3.5 Summary and Conclusions -- References -- 4 Separation and Analysis of Nanoparticles (NP) in Aqueous Environmental Samples -- 4.1 Introduction -- 4.2 Major Challenges -- 4.2.1 Low Concentration of Engineered NP -- 4.2.2 Similarity between Engineered, Natural, and Incidential NP -- 4.2.3 Associations of Engineered NP with (Nanoscale) Colloids -- 4.3 Different Approaches to Quantify Engineered NP in Environmental Matrices -- 4.3.1 Combination of "Generic" Analytical Techniques Applied after Enrichment and Separation of Engineered NP -- 4.3.2 Combination of "Specific" Analytical Techniques Applied to Bulk Samples -- 4.4 Initial Sample Preparation for Engineered NP -- 4.4.1 Sedimentation Combined with Stepwise Centrifugation -- 4.4.2 Cross-Flow/Tangential-Flow Filtration -- 4.4.3 Split Flow Thin Cell Fractionation -- 4.5 Sophisticated Sample Preparation for Engineered NP -- 4.5.1 Field-Flow Fractionation -- 4.5.2 Density-Gradient and Analytical Ultracentrifugation -- 4.5.3 Ionic Liquids, Cloud Point Extraction, and Ionic Exchange Resin -- 4.5.4 Chromatographic Methods -- 4.5.5 Electrokinetic Methods -- 4.6 Engineered NP in Different Environmental Compartments (Water, Sludge, Soils, Sediment) -- 4.6.1 Detecting Spiked Engineered NP in Environmental Matrices -- 4.6.2 Detecting "Real" Engineered NP in Environmental Matrices -- 4.7 Future Trends and Demands -- 4.8 List of Abbreviations -- References -- 5 Nanocatalysts for Groundwater Remediation -- 5.1 Organohalides and Nitrates: Common Grounwater Contaminants -- 5.1.1 Introduction to Groundwater -- 5.1.2 Introduction to Organohalides and Nitrate. , 5.2 Conventional Physicochemical Remediation Methods -- 5.2.1 Pump-and-Treat Ex Situ Methods -- 5.2.2 In Situ Methods -- 5.2.3 Biological Remediation -- 5.3 Nanocatalyzed Degradation of Aqueous Compounds -- 5.3.1 Reductive Nanocatalysts for Aqueous Organohalide and Nitrate Remediation -- 5.3.2 Oxidative Photocatalysts for Aqueous Organohalide Remediation -- 5.4 Future Work and Conclusions -- 5.4.1 Emerging Contaminants to Consider -- 5.4.2 New Catalysts to Meet Emerging Challenges -- References -- PART II Environmental Release, Processes, and Modeling of Engineered Nanoparticles -- 6 Properties, Sources, Pathways, and Fate of Nanoparticles in the Environment -- 6.1 Introduction -- 6.2 Nanoparticle Classification -- 6.2.1 Definitions -- 6.2.2 Natural Nanoparticles -- 6.2.3 Engineered Nanoparticles -- 6.3 Sources of Engineered Nanoparticles in the Environment -- 6.4 Behavior and Fate of Engineered Nanoparticles -- 6.4.1 Fate in Water -- 6.4.2 Fate in Soil -- 6.5 Conclusions -- References -- 7 Environmental Exposure Modeling Methods for Engineered Nanomaterials -- 7.1 Introduction -- 7.1.1 Focus of Chapter -- 7.2 Current Decision Support Guidance and Software: Place of Nanomaterials -- 7.2.1 Case Study 1: European Chemical Agency Guidance and the European Union System for the Evaluation of Substances -- 7.2.2 Case Study 2: Specific Advice on Fulfilling Information Requirements for Nanomaterials under REACH (RIP-oN 2) -- 7.2.3 Case Study 3: Forum for the Co-ordination of Pesticide Fate Models and Their Use Models -- 7.2.4 Regulatory Models: Conclusions -- 7.3 Representation of Nano-Specific Data for Modeling Purposes -- 7.3.1 Initial Material Characteristics -- 7.3.2 Environmental Fate and Behavior -- 7.3.3 Material Characterization at Key Exposure Points -- 7.3.4 Data Handling -- 7.3.5 Variability -- 7.3.6 Uncertainty -- 7.3.7 Unknowns/Data Gaps. , 7.3.8 Categorization -- 7.4 Modeling Techniques: Describing The Fate and Flow of Nanomaterials -- 7.4.1 Material Flow Analysis -- 7.4.2 Chemical Fate Modeling -- 7.4.3 Modeling Techniques: Conclusions -- 7.5 Future Data Requirements for The Exposure Modeling of Nanomaterials -- 7.5.1 Summary and Conclusions -- References -- 8 Aggregation Kinetics and Fractal Dimensions of Nanomaterials in Environmental Systems -- 8.1 Introduction -- 8.2 Theoretical Framework -- 8.2.1 Collisions Between Uncharged Particles -- 8.2.2 Incorporating Surface Charge in Collision -- 8.2.3 van Der Waals Forces and Attachment -- 8.2.4 DLVO Theory Capturing Charged Particle Aggregation -- 8.2.5 Attachment Efficiency -- 8.2.6 Non-DLVO Interactions -- 8.2.7 Fractal Dimension -- 8.3 Common Experimental Techniques -- 8.3.1 Coulter Counters -- 8.3.2 Scattering Techniques -- 8.4 State of Nanoparticle Aggregation Studies -- 8.4.1 Role of Background Chemistry (Ionic Strength, pH, NOM, Exposure Media) -- 8.4.2 Role of Physical Attributes and Preparation Methods -- 8.4.3 Role of Environmental Transformations -- 8.5 Recent Advances in Aggregation Studies -- 8.5.1 Advances in Theoretical Framework and Molecular Modeling -- 8.5.2 Dynamics of Fractal Dimension -- 8.5.3 Heteroaggregation -- 8.6 Future Challenges and Research Directions -- 8.6.1 Challenges in Aggregation Modeling -- 8.6.2 Challenges from Material Attributes (Shape and Morphology) -- 8.6.3 Nanohybrids and Nanocomposites -- 8.6.4 Soft-Coating Interaction with Bio- and Geomacromolecules -- 8.6.5 Complex Matrices -- 8.6.6 Future Research Directions -- Acknowledgments -- Appendix: Symbols -- References -- 9 Adsorption of Organic Compounds by Engineered Nanoparticles -- 9.1 Introduction -- 9.2 Sorption Characteristics of OCs on Different Types of ENPs -- 9.2.1 Sorption of OCs on Carbon-Based ENPs. , 9.2.2 Sorption of OCs on Other ENPs -- 9.3 The Methods Applied to Study the Adsorption Mechanisms of OCs by ENPs -- 9.3.1 pH-Dependent Sorption Analysis -- 9.3.2 Sorption Experiments in Organic Solvent -- 9.3.3 Model Chemicals and/or ENPs with Certain Structural Features -- 9.4 OC-ENP Interactions in Environment-Relevant Conditions -- 9.4.1 Effect of pH -- 9.4.2 Effect of Ionic Strength -- 9.4.3 Effect of Dissolved Organic Matter -- 9.4.4 Effect of ENPs Aggregation Status -- 9.4.5 Effect of Competing OCs -- 9.5 The Risks of OC-ENP Interaction -- 9.5.1 The Risks of OCs as Affected by ENPs -- 9.5.2 The Risks of ENPs as Affected by OCs -- 9.6 Summary and Future Perspectives -- Acknowledgments -- References -- 10 Sorption of Heavy Metals by Engineered Nanomaterials -- 10.1 Introduction -- 10.2 Sorption Mechanisms of Heavy Metals by ENMs -- 10.3 Sorption Kinetics of Heavy Metals by ENMs -- 10.3.1 Lagergren Pseudo First-Order Model -- 10.3.2 Lagergren Pseudo Second-Order Model -- 10.3.3 Elovich Equation -- 10.3.4 Intra-particle Diffusion Model -- 10.4 Sorption Thermodynamics of Heavy Metals by ENMs -- 10.4.1 Thermodynamic Sorption Parameters of Heavy Metals by ENMs -- 10.4.2 Thermodynamic Sorption Models -- 10.5 Factors Influencing Heavy Metal Sorption by ENMs -- 10.5.1 Influence of ENM Properties -- 10.5.2 Influence of Heavy Metal Properties -- 10.5.3 Influence of Solution Properties -- 10.6 Summary and Perspective -- References -- 11 Emission, Transformation, and Fate of Nanoparticles in the Atmosphere -- 11.1 Introduction -- 11.2 Summary of Previous Review Articles -- 11.3 Physicochemical Characteristics of Atmospheric Nanoparticles -- 11.3.1 Nucleation Mode -- 11.3.2 Aitken Mode -- 11.3.3 Accumulation Mode -- 11.3.4 Coarse Mode -- 11.4 Emissions of Airborne Nanoparticles in Atmospheric Environment -- 11.4.1 Emissions of Naturally Produced Nanoparticles. , 11.4.2 Emissions of Incidentally Produced Nanoparticles.
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  • 5
    facet.materialart.
    Unknown
    PANGAEA
    In:  Supplement to: Perrino, Enrico Vito; Brunetti, Gennaro; Rovira, Soler Pedro; Senesi, Nicola; Farrag, Karam (2012): Plant communities in multi-metal contaminated soils: a case study in the National Park of Alta Murgia (Apulia Region - Southern Italy). Flora, 16(9), 871-888, https://doi.org/10.1080/15226514.2013.798626
    Publication Date: 2023-01-13
    Description: A phytosociological study was conducted in the National Park of Alta Murgia in the Apulia region (Southern Italy) to determine the adverse effects of metal contamination of soils on the distribution of plant communities. The phytosociological analyses have shown a remarkable biodiversity of vegetation on non-contaminated soils, while biodiversity appeared strongly reduced on metal-contaminated soils. The area is naturally covered by a wide steppic grassland dominated by Stipa austroitalica Martinovsky subsp. austroitalica. Brassicaceae such as Sinapis arvensis L. are the dominating species on moderated contaminated soils, whereas spiny species of Asteraceae such as Silybum marianum (L.) Gaertn. and Carduus pycnocephalus L. subsp. pycnocephalus are the dominating vegetation on heavily metal-contaminated soils. The presence of these spontaneous species on contaminated soils suggest their potential for restoration of degraded lands by phytostabilization strategy.
    Keywords: Altamura; Altamura, Apulia, Italy; Cadmium; Cadmium, standard deviation; Chromium; Chromium, standard deviation; Code; Copper; Copper, standard deviation; DATE/TIME; Event label; Geological sample; GEOS; Gravina_in_Puglia; Gravina in Puglia, Apulia, Italy; LATITUDE; Lead; Lead, standard deviation; LONGITUDE; Nickel; Nickel, standard deviation; Number; Sample code/label; UTM Easting, Universal Transverse Mercator; UTM Northing, Universal Transverse Mercator; UTM Zone, Universal Transverse Mercator; Vegetation type; Zinc; Zinc, standard deviation
    Type: Dataset
    Format: text/tab-separated-values, 474 data points
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  • 6
    ISSN: 1573-2932
    Source: Springer Online Journal Archives 1860-2000
    Topics: Energy, Environment Protection, Nuclear Power Engineering
    Notes: Abstract Copper, Fe, and Mn were used as probes to investigate residual metal reactivity for humic acid (HA) samples extracted from a loam soil, either non-amended or amended with anaerobically digested sewage sludge for 4, 5, 6, or 7 yr at 90 t ha−1. yr−1. Irrespective of their origin, the HA complexes significant amounts of metal, in forms stable against intense water-leaching, in the order Fe 〉 Cl 〉 Mn. Sludge-amended soil HA adsorbed and retained Fe in amounts greater than HA extracted fron non-amended soil. Metal adsorption occurred mainly by cation-exchange replacement of metals previousl: bound to HA. Water-stable Fe3+-HA complexes prepared in the laboratory were partially stable agains H+ and metal ion exchange reactions, whereas Cu2+ and Mn2+ in laboratory-prepared, water-stabl HA complexes were desorbed almost completely by these two reactions. Electron spin resonance spectra indicated that the laboratory-prepared metal-HA complexes had a chemical composition and molecula structure similar to that of indigenous metal-HA complexes, which were stable against all leachin, and cation-exchange treatments. Although the HA samples showed a maximal metal binding (i.e. saturation) as metal loading of the sludge-amended soil increased, they still exhibited a high residua binding capacity for the three metals used as probes.
    Type of Medium: Electronic Resource
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  • 7
    Electronic Resource
    Electronic Resource
    Springer
    Water, air & soil pollution 35 (1987), S. 147-155 
    ISSN: 1573-2932
    Source: Springer Online Journal Archives 1860-2000
    Topics: Energy, Environment Protection, Nuclear Power Engineering
    Notes: Abstract Electron spin resonance (ESR) spectrometry was used to study Cu(II) complexes with anionic surfactant compounds of the types that have been detected in sewage sludge or in the fulvic acid fraction of anaerobically-digested sewage sludge and found to resist biodegradation in the soil environment. The ESR spectra of frozen (77 °K), aqueous solutions of linear alkyl benzene sulfonates and fatty alcohol sulfate esters at Cu-ligand molar ratios ranging from 0.1 to 1 exhibited anisotropic patterns indicative of a d x 2−y 2 groundstate of Cu(II) bound into innersphere complexes with the ligands arranged in square planar coordination. Sulfonate-type surfactants, both in the acid and salt forms, appeared to complex Cu(II) more efficiently than ester sulfate-type surfactants. Conventional physical parameters calculated from the ESR spectra were consistent with fully oxygenated, 4 O-ligand binding sites for the Cu(II) ions and indicated the formation of similar unidentate or bidentate complexes between Cu(II) and the surfactants at any Cu/ligand molar ratio investigated. The spectral lineshapes and related parameters of the Cu(II)-anionic surfactant complexes, however, were not very similar to those observed previously for Cu(II)-sewage sludge FA complexes. It was concluded that anionic surfactants involved in Cu(II) complexation by sewage sludge or sewage sludge fulvic acid do not behave as isolated, independent ligands, but instead may participate as co-ligands with other O-containing functional groups and/or as moities incorporated into the fulvic acid structure.
    Type of Medium: Electronic Resource
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