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  • 1
    Online Resource
    Online Resource
    New York, NY :Springer,
    Keywords: Negotiation in business. ; Electronic books.
    Type of Medium: Online Resource
    Pages: 1 online resource (229 pages)
    Edition: 1st ed.
    ISBN: 9781461327578
    Series Statement: Environment, Development and Public Policy: Environmental Policy and Planning Series
    Language: English
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  • 2
    Online Resource
    Online Resource
    Ithaca :Cornell University Press,
    Keywords: Air--Pollution--Environmental aspects--New York (State). ; Electronic books.
    Description / Table of Contents: A comprehensive synthesis of past, current, and potential future conditions regarding atmospheric sulfur, nitrogen oxides, ammonium, and mercury deposition; surface water chemistry; soil chemistry; forests; and aquatic biota in New York.
    Type of Medium: Online Resource
    Pages: 1 online resource (346 pages)
    Edition: 1st ed.
    ISBN: 9781501700811
    DDC: 551.57/7109747
    Language: English
    Note: Air Pollutant Deposition and Its Effects on Natural Resources in New York State -- Contents -- List of Figures -- List of Plates -- List of Tables -- Preface -- Acknowledgments -- List of Acronyms and Abbreviations -- Chapter 1. Background and Purpose -- 1.1. Atmospheric Deposition in New York -- 1.2. Air Quality Management -- 1.2.1. Clean Air Act -- 1.2.2. Regional Haze Rule -- 1.2.3. Federal Water Pollution Control Act -- 1.2.4. Other Legislation -- 1.3. Ecosystem Functions and Services -- 1.4. Goals and Objectives -- Chapter 2. Resource Sensitivity to Atmospheric Deposition -- 2.1. Geology -- 2.2. Soils -- 2.3. Forest Vegetation -- 2.4. Hydrology and Hydrodynamics -- 2.5. Wetlands -- 2.6. Surface Water -- 2.6.1. Streams and Lakes -- 2.6.1.1. Acid-Base Chemistry -- 2.6.1.2. Nutrients -- 2.6.2. Estuaries and Near-Coastal Marine Waters -- Chapter 3. Principal Stressors -- 3.1. Sulfur, Nitrogen, and Mercury Emissions and Deposition -- 3.1.1. Sulfur Emissions and Deposition -- 3.1.1.1. Sulfur Emissions into the Atmosphere -- 3.1.1.2. Sulfur Deposition -- 3.1.2. Nitrogen Oxide and Ammonia Emissions and Deposition -- 3.1.2.1. Nitrogen Emissions into the Atmosphere -- 3.1.2.2. Nitrogen Deposition and Other Watershed N Sources -- 3.1.3. Mercury Emissions and Deposition -- 3.1.3.1. Mercury Emissions into the Atmosphere -- 3.1.3.2. Mercury Deposition -- 3.2. Watershed Disturbance -- 3.2.1. Timber Harvest and Fire -- 3.2.2. Land Use Change -- 3.2.3. Invasive Species -- 3.2.4. Other Disturbances -- 3.2.5. Multiple Stress Response -- 3.3. Mercury Bioaccumulation and Biomagnification -- 3.4. Climate Change -- 3.4.1. Influence of Soil Freezing on N Cycling -- 3.4.2. Extreme Events -- Chapter 4. Chemical Effects of Atmospheric Deposition -- 4.1. Sulfur -- 4.1.1. Upland Sulfur Cycling Processes -- 4.1.2. Wetland Sulfur Cycling Processes. , 4.1.3. Surface Water Sulfur Cycling Processes -- 4.2. Nitrogen -- 4.2.1. Upland Nitrogen Cycling Processes -- 4.2.2. Wetland Nitrogen Cycling Processes -- 4.2.3. Fresh Surface Water Nitrogen Cycling Processes -- 4.2.4. Coastal Nitrogen Cycling Processes -- 4.2.5. Nitrogen Saturation -- 4.3. Dissolved Organic Carbon -- 4.3.1. Upland Processes -- 4.3.2. Wetland Processes -- 4.3.3. Surface Water Processes -- 4.4. Base Cations and Aluminum -- 4.4.1. Upland Processes -- 4.4.2. Wetland and Surface Water Processes -- 4.5. Acid-Base Interactions -- 4.5.1. Soil-Water Interactions -- 4.5.2. Upland Processes -- 4.5.3. Base Cation Depletion -- 4.5.4. Wetland and Surface Water Processes -- 4.5.4.1. Chronic Acidification Processes -- 4.5.4.2. Episodic Acidification Processes -- 4.6. Nutrient Interactions -- 4.6.1. Terrestrial Effects -- 4.6.2. Wetland Effects -- 4.6.3. Surface Water Effects -- 4.6.3.1. High Elevation Lakes -- 4.6.3.2. Great Lakes -- 4.6.3.3. Coastal Waters -- 4.7. Mercury Interactions -- 4.7.1. Upland Processes -- 4.7.2. Wetland Processes -- 4.7.3. Surface Water Processes -- Chapter 5. Biotic Effects of Atmospheric Deposition -- 5.1. Terrestrial Resource Response to Acidification, Eutrophication and Mercury Input -- 5.1.1. Red Spruce Response to Acidification -- 5.1.2. Sugar Maple Response to Acidification -- 5.1.3. Vegetation Response to Nitrogen Supply -- 5.1.4. Avian Response to Acidification -- 5.1.5. Mercury Methylation -- 5.1.6. Effects of Mercury on Humans -- 5.2. Effects on the Biology of Freshwater Ecosystems -- 5.2.1. Phytoplankton -- 5.2.2. Zooplankton -- 5.2.3. Benthic Macroinvertebrates -- 5.2.4. Fish -- 5.2.4.1. Effects of Acidification on Fish -- 5.2.4.2. Effects of Mercury on Fish -- 5.2.4.3. Effects of Environmental Factors on Mercury Bioaccumulation in Fish -- 5.2.5. Fish-Eating Birds and Mammals -- 5.2.5.1. Fish-Eating Birds. , 5.2.5.2. Fish-Eating Mammals -- 5.2.6. Other Life Forms -- 5.2.7. Community Metrics -- 5.2.7.1. Taxonomic Richness -- 5.2.7.2. Indices of Biotic Integrity -- 5.3. Effects on Coastal Aquatic Biota -- 5.3.1. Phytoplankton in Coastal Waters -- 5.3.2. Submerged Aquatic Vegetation -- 5.3.3. Shellfish and Fish -- Chapter 6. Historical Patterns of Effects -- 6.1. Paleoecological Studies -- 6.2. Watershed Model Hindcast Studies -- 6.3. Recent Trends in Monitoring Data -- 6.3.1. Wet and Dry Deposition -- 6.3.2. Soils -- 6.3.3. Surface Waters -- 6.3.3.1. Chemistry -- 6.3.3.2. Biology -- Chapter 7. Extrapolation of Site-Specific Data to the Broader Region -- 7.1. Methods of Regionalization -- 7.2. Regionalization of Survey Data -- 7.3. Regionalization of Long-Term Monitoring Data -- Chapter 8. Projected Future Responses of Sensitive Resources to Reductions in Acidic Atmospheric Deposition -- 8.1. Modeling Approaches -- 8.1.1. MAGIC -- 8.1.2. PnET-BGC -- 8.1.3. SPARROW -- 8.1.4. WATERSN -- 8.1.5. ASSETS -- 8.2. Projections Based on Existing and Future Emissions Controls -- Chapter 9. Critical Load -- 9.1. Approaches -- 9.2. Critical- and Target-Load Calculations -- 9.3. Utility to Policy Makers -- 9.4. Linkages to Biological Response -- Chapter 10. Climate Linkages -- 10.1. Temperature -- 10.2. Water Quantity and Quality -- Chapter 11. Linkages with Ecosystem Services -- 11.1. Forest and Freshwater Aquatic Resources -- 11.2. Coastal Resources -- Chapter 12. Active Intervention -- Chapter 13. Summary and Important Data Gaps and Recommendations -- Glossary -- References Cited -- About the Author -- Plates are at the end of the book.
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  • 3
    Online Resource
    Online Resource
    Milton :Taylor & Francis Group,
    Keywords: Air--Pollution--United States. ; Electronic books.
    Description / Table of Contents: A variety of air pollutants are emitted into the atmosphere from human-caused and natural emissions sources throughout the United States and elsewhere. These contaminants impact sensitive natural resources in wilderness, including the national parks. The system of national parks in the United States is among our greatest assets. This book provides a compilation and synthesis of current scientific understanding regarding the causes and effects of these pollutants within national park lands. It describes pollutant emissions, deposition, and exposures; it identifies the critical (tipping point) loads of pollutant deposition at which adverse impacts are manifested.
    Type of Medium: Online Resource
    Pages: 1 online resource (683 pages)
    Edition: 1st ed.
    ISBN: 9781498765183
    DDC: 363.739210973
    Language: English
    Note: Cover -- Half Title -- Title Page -- Copyright Page -- Dedication -- Table of Contents -- List of Figures -- List of Tables -- Preface -- Acronyms and Abbreviations -- Acknowledgments -- Author -- Section I: Background -- 1: Introduction -- References -- 2: Pollutant Exposure -- 2.1 Emissions -- 2.2 Deposition -- 2.2.1 Wet Deposition -- 2.2.2 Dry Deposition -- 2.2.3 Total Wet Plus Dry Deposition -- 2.2.4 Occult Deposition -- 2.3 Ozone Production and Dispersion -- 2.4 Mechanism of Exposure to Metals and Persistent Organic Pollutants -- 2.4.1 Mercury -- 2.4.2 Persistent Organic Pollutants -- References -- 3: Impacts -- 3.1 Acidification -- 3.1.1 Terrestrial Effects -- 3.1.1.1 Aluminum Mobilization -- 3.1.1.2 Depletion of Base Cations from Soil -- 3.1.2 Aquatic Effects -- 3.1.3 Spatial Patterns in Acidification Risk -- 3.2 Nutrient Nitrogen Enrichment -- 3.2.1 Terrestrial Effects -- 3.2.2 Aquatic Effects -- 3.2.3 Nitrogen Saturation -- 3.3 Critical Load and Exceedance -- 3.4 Ozone Exposure and Effects -- 3.4.1 Effects of Ozone on Plants -- 3.4.2 Standards and Cumulative Exposure Indices -- 3.4.3 Mode of Action -- 3.4.4 Field Observations -- 3.4.5 Environmental Interactions -- 3.4.6 Spatial Patterns in Ozone Effects -- 3.5 Visibility Impairment -- 3.5.1 Sources of Visibility Degradation -- 3.5.2 Visibility Metrics -- 3.5.3 Visibility Monitoring -- 3.5.3.1 Particle Monitoring -- 3.5.3.2 Optical Monitoring -- 3.5.3.3 View Monitoring -- 3.5.3.4 Regional Haze Rule -- 3.5.3.5 Spatial Patterns in Visibility Impairment -- 3.6 Effects of Exposure to Airborne Toxics -- 3.6.1 Toxic Substances of Concern for This Book -- 3.6.2 Biomagnification -- 3.6.3 Effects of Atmospherically Deposited Toxic Substances -- 3.6.3.1 Effects on Fish -- 3.6.3.2 Effects on Humans -- 3.6.3.3 Effects on Piscivorous Wildlife -- 3.6.4 Spatial Patterns in Exposure to Toxic Substances. , 3.6.4.1 Mercury -- 3.6.4.2 Semivolatile Organic Compounds -- References -- Section II: Case Studies -- 4: Great Smoky Mountains National Park and the Appalachian Highlands Network -- 4.1 Introduction -- 4.2 Atmospheric Emissions and Deposition -- 4.3 Acidification -- 4.3.1 Acidification of Terrestrial Ecosystems -- 4.3.2 Acidification of Aquatic Ecosystems -- 4.3.2.1 Episodic Acidification -- 4.3.2.2 Effects on Aquatic Biota -- 4.4 Nutrient Enrichment -- 4.5 Ozone Injury to Vegetation -- 4.5.1 Ozone Formation -- 4.5.2 Ozone-Sensitive Plants -- 4.5.3 Ozone Exposure Indices and Levels -- 4.5.3.1 Field Surveys of Foliar Injury -- 4.5.3.2 Model Responses -- 4.6 Visibility Degradation -- 4.6.1 Natural Background and Ambient Visibility Conditions -- 4.6.2 Composition of Haze -- 4.6.3 Trends in Visibility -- 4.7 Summary -- References -- 5: Shenandoah National Park and the Mid-Atlantic Network -- 5.1 Background -- 5.2 Atmospheric Emissions and Deposition -- 5.3 Acidification -- 5.3.1 Acidification of Terrestrial Ecosystems -- 5.3.2 Acidification of Aquatic Ecosystems -- 5.3.2.1 Episodic Acidification -- 5.3.2.2 Effects on Aquatic Biota -- 5.4 Nutrient Nitrogen Enrichment -- 5.5 Ozone Injury to Vegetation -- 5.5.1 Ozone Exposure Indices and Levels -- 5.5.2 Ozone Formation -- 5.5.3 Ozone Exposure Effects -- 5.6 Visibility Degradation -- 5.6.1 Natural Background and Ambient Visibility Conditions -- 5.6.2 Composition of Haze -- 5.6.3 Trends in Visibility -- 5.6.4 Development of State Implementation Plans -- 5.7 Summary -- References -- 6: Acadia National Park and the Northeast Temperate Network -- 6.1 Background -- 6.2 Atmospheric Emissions and Deposition -- 6.3 Acidification -- 6.3.1 Acidification of Terrestrial Ecosystems -- 6.3.2 Acidification of Aquatic Ecosystems -- 6.3.2.1 Status -- 6.3.2.2 Past Trends -- 6.3.2.3 Critical Loads for Acidification. , 6.3.2.4 Temporal Variability in Water Chemistry -- 6.4 Nutrient Nitrogen Enrichment -- 6.5 Ozone Injury to Vegetation -- 6.6 Visibility Degradation -- 6.6.1 Natural Background and Ambient Visibility Conditions -- 6.6.2 Composition of Haze -- 6.6.3 Trends in Visibility -- 6.6.4 Development of State Implementation Plans -- 6.7 Toxic Airborne Contaminants -- 6.8 Summary -- References -- 7: South Florida/Caribbean Network -- 7.1 Background -- 7.2 Atmospheric Emissions and Deposition -- 7.3 Acidification -- 7.4 Nutrient Nitrogen Enrichment -- 7.5 Ozone Injury to Vegetation -- 7.6 Visibility Degradation -- 7.6.1 Natural Background and Ambient Visibility Conditions -- 7.6.2 Composition of Haze -- 7.6.3 Trends in Visibility -- 7.6.4 Development of State Implementation Plans -- 7.7 Toxic Airborne Contaminants -- 7.8 Summary -- References -- 8: Great Lakes Network -- 8.1 Background -- 8.2 Atmospheric Emissions and Deposition -- 8.3 Acidification -- 8.3.1 Acidification of Terrestrial Ecosystems -- 8.3.2 Acidification of Aquatic Ecosystems -- 8.3.2.1 Status -- 8.3.2.2 Trends -- 8.4 Nutrient Enrichment -- 8.4.1 Terrestrial Ecosystems -- 8.4.2 Transitional Ecosystems -- 8.4.3 Great Lakes Ecosystems -- 8.5 Ozone Injury to Vegetation -- 8.6 Visibility Degradation -- 8.6.1 Natural Background and Ambient Visibility Conditions -- 8.6.2 Composition of Haze -- 8.6.3 Development of State Implementation Plans -- 8.7 Toxic Airborne Contaminants -- 8.7.1 Hg in Fish -- 8.7.2 Piscivorous Wildlife -- 8.7.3 Persistent Organic Pollutants -- 8.8 Summary -- References -- 9: Mammoth Cave National Park and the Cumberland Piedmont Network -- 9.1 Background -- 9.2 Atmospheric Emissions and Deposition -- 9.3 Acidification -- 9.3.1 Acidification of Terrestrial Ecosystems -- 9.3.2 Acidification of Aquatic Ecosystems -- 9.4 Nutrient Nitrogen Enrichment -- 9.5 Ozone Injury to Vegetation. , 9.5.1 Ozone Exposure Indices and Concentrations -- 9.5.2 Ozone Formation -- 9.6 Visibility Degradation -- 9.6.1 Natural Background and Ambient Visibility Conditions -- 9.6.2 Trends in Visibility -- 9.6.3 Development of State Implementation Plans -- 9.7 Toxic Airborne Contaminants -- 9.8 Summary -- References -- 10: Northern Colorado Plateau Network -- 10.1 Background -- 10.2 Atmospheric Emissions and Deposition -- 10.3 Acidification -- 10.4 Nutrient Nitrogen Enrichment -- 10.5 Ozone Injury to Vegetation -- 10.6 Visibility Impairment -- 10.6.1 Natural Background and Ambient Visibility Conditions -- 10.6.2 Composition of Haze and Sources of Visibility Impairment -- 10.6.3 Development of State Implementation Plans -- 10.7 Toxic Airborne Contaminants -- 10.8 Summary -- References -- 11: The Grand Canyon and the Southern Colorado Plateau Network -- 11.1 Background -- 11.2 Atmospheric Emissions and Deposition -- 11.3 Acidification -- 11.3.1 Effects on Natural Ecosystems -- 11.3.2 Effects on Historic Structures -- 11.4 Nutrient Nitrogen Enrichment -- 11.5 Ozone Injury to Vegetation -- 11.6 Visibility Impairment -- 11.6.1 Natural Background and Ambient Visibility Conditions -- 11.6.2 Composition of Haze -- 11.6.3 Sources of Visibility Impairment in the Southern Colorado Plateau Network -- 11.6.4 Visibility Research at GRCA -- 11.6.5 Trends in Visibility -- 11.7 Toxic Airborne Contaminants -- 11.8 Summary -- References -- 12: Coast and Cascades Network -- 12.1 Background -- 12.2 Atmospheric Emissions and Deposition -- 12.2.1 Emissions -- 12.2.2 Deposition -- 12.3 Acidification -- 12.3.1 Acidification Risk Analysis Results -- 12.3.2 Chronic Surface Acid-Base Chemistry -- 12.3.3 Temporal Variability in Water Chemistry -- 12.4 Nutrient Nitrogen Enrichment -- 12.4.1 Terrestrial Effects of Nutrient Enrichment -- 12.4.2 Aquatic Effects of Nutrient Enrichment. , 12.5 Ozone Injury to Vegetation -- 12.6 Visibility Degradation -- 12.6.1 Natural Background Visibility and Monitored Visibility Conditions -- 12.6.2 Composition of Haze -- 12.6.3 Trends in Visibility -- 12.6.4 State of Washington Regional Haze State Implementation Plan -- 12.7 Toxic Airborne Contaminants -- 12.8 Summary -- References -- 13: Klamath Network -- 13.1 Background -- 13.2 Atmospheric Emissions and Deposition -- 13.3 Acidification -- 13.3.1 Acidification of Terrestrial Ecosystems -- 13.3.2 Acidification of Aquatic Ecosystems -- 13.3.2.1 Episodic Acidification -- 13.3.2.2 Effects on Aquatic Biota -- 13.4 Nutrient Nitrogen Enrichment -- 13.4.1 Aquatic Ecosystem Nutrient Enrichment -- 13.4.2 Terrestrial Ecosystem Nutrient Enrichment -- 13.5 Ozone Injury to Vegetation -- 13.5.1 Ozone Exposure Indices and Levels -- 13.5.2 Ozone Formation -- 13.5.3 Ozone Exposure Effects -- 13.5.3.1 Field Survey Results -- 13.5.3.2 Model Responses -- 13.6 Visibility Degradation -- 13.6.1 Natural Background Visibility and Monitored Visibility Conditions -- 13.6.2 Composition of Haze -- 13.6.3 Trends in Visibility -- 13.6.4 Development of State Implementation Plans -- 13.7 Toxic Airborne Contaminants -- 13.8 Summary -- References -- 14: Hawaii -- 14.1 Background -- 14.2 Atmospheric Emissions and Deposition -- 14.3 Acidification -- 14.4 Nutrient Nitrogen Enrichment -- 14.5 Sulfur Dioxide Injury to Vegetation -- 14.6 Visibility Degradation -- 14.6.1 Natural Background Visibility and Monitored Visibility Conditions -- 14.6.2 Composition of Haze -- 14.6.3 Trends in Visibility -- 14.6.4 Development of State Implementation Plans -- 14.7 Summary -- References -- 15: Mojave Desert -- 15.1 Background -- 15.2 Atmospheric Emissions and Deposition -- 15.3 Acidification -- 15.4 Nutrient Nitrogen Enrichment -- 15.4.1 Risk Ranking -- 15.4.2 Field Studies. , 15.4.3 Modeling Studies.
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  • 4
    Online Resource
    Online Resource
    La Vergne :Royal Society of Chemistry, The,
    Keywords: Nanochemie. ; Electronic books.
    Description / Table of Contents: This book describes the most up-to-date research in the area of nanoparticles that show anti-microbial activity.
    Type of Medium: Online Resource
    Pages: 1 online resource (255 pages)
    Edition: 1st ed.
    ISBN: 9781849735261
    Series Statement: Issn Series
    DDC: 572/.33
    Language: English
    Note: Nanoparticles in Anti-Microbial Materials -- Contents -- Preface -- Chapter 1 Nanoparticles: What Are They? -- 1.1 Introduction -- 1.2 Nano, the Beginning to the Present -- 1.3 Defining the Nanodimension -- 1.4 Physical Chemistry of Nanoparticles -- 1.4.1 Structure -- 1.4.2 Electrical Properties -- 1.4.3 Catalytic Properties -- 1.4.4 Mechanical Properties -- 1.4.5 Surface Plasmon Resonance -- 1.4.6 Anti-microbial Properties -- 1.5 Preparation Methods -- 1.5.1 Nucleation and Growth -- 1.5.2 Synthetic Routes -- 1.6 Applications of Nanoparticles -- 1.6.1 Chemical Sensors -- 1.6.2 Malaria Detection -- 1.6.3 Fluorescent Colloids in Biotechnology -- 1.6.4 Anti-microbial Agents -- 1.6.5 Emerging Approaches -- 1.7 Toxicity and Nanomaterials -- 1.7.1 Size Specific Behavior of Nanoparticles -- 1.7.2 Quantum Dot Toxicity -- 1.7.3 Concepts of Toxicology of Nanomaterials -- 1.7.4 Nanoparticle entry and Target -- 1.7.5 Risk Assessments -- 1.8 Conclusions -- References -- Chapter 2 Microbial Impacts on Surfaces -- 2.1 Introduction -- 2.2 Mechanisms of Adhesion -- 2.2.1 DLVO Theory -- 2.2.2 Thermodynamic Theory -- 2.2.3 Extended DLVO Theory -- 2.3 Further Influential Factors for Microbial Impact -- 2.3.1 Environmental Impacts -- 2.3.2 Flow Adhesion Characterisation -- 2.3.3 Material Surface Impacts -- 2.3.4 Microbial Response to the Nano-surface -- 2.3.5 Specific Influences -- 2.4 Bacterial Responses to a Surface -- 2.5 Bacterial Characteristics -- 2.5.1 Hydrophobicity -- 2.5.2 Surface Charge -- 2.5.3 Shape -- 2.5.4 Attached Matrix of Cells -- 2.5.5 Formation of Biofilms -- 2.5.6 Novel Approaches to Combat Microbial Impact -- 2.6 Conclusions -- References -- Chapter 3 Applications of Nanoparticles -- 3.1 Introduction -- 3.2 Silver Through the Ages -- 3.2.1 Renewed Interest in Silver -- 3.2.2 Anti-microbial Silver: How It Works. , 3.2.3 Molecular Understanding and Modes of Action -- 3.2.4 Silver in Coatings and Polymers -- 3.3 Silver in Materials -- 3.3.1 Medical Devices Containing Silver -- 3.3.2 Release Materials Containing Silver -- 3.3.3 Silver Wound Dressings -- 3.3.4 Textiles Containing Silver -- 3.3.5 Water Treatment and Silver -- 3.3.6 Applications and Emerging Trends -- 3.4 Novel and Emerging Nanomaterials for Anti-microbial Applications -- 3.4.1 Food Packaging -- 3.4.2 Health Effects -- 3.4.3 Gold Nanoparticles -- 3.4.4 Metal Oxides -- 3.4.5 Applications in Disease -- 3.4.6 Biosensing -- 3.5 Conclusions -- References -- Chapter 4 Characterisation of Materials Using Quantitative Approaches -- 4.1 Introduction -- 4.2 Characterisation Techniques -- 4.2.1 X-ray Absorption Spectroscopies: Theory and Application -- 4.2.2 Nuclear Magnetic Resonance (NMR) Analysis -- 4.2.3 Fourier Transform Infrared (FTIR) Analysis -- 4.2.4 Raman Spectroscopy -- 4.2.6 UV-Visible Spectroscopy -- 4.2.7 Thermogravimetric Analysis -- 4.2.8 Differential scanning calorimetry -- 4.2.9 Mass Spectrometry -- 4.2.10 Electron Energy Loss Spectroscopy (EELS) -- 4.2.11 Photoelectron Spectroscopy -- 4.2.12 Spectral Comparisons -- 4.2.13 Atomic Absorption and Inductively Coupled Plasma -- 4.2.14 Dynamic Light Scattering -- 4.2.15 Mössbauer Spectroscopy -- 4.3 Conclusions -- References -- Chapter 5 Visualisation of Nano-anti-microbial Materials -- 5.1 Introduction -- 5.2 Approaches to Visualisation of Anti-microbial Nanomaterials -- 5.3 Scanning Probe Microscopy (SPM) and Nanomaterial Characterisation -- 5.4 AFM and Nanomaterial Characterisation -- 5.5 Practical Advantages of AFM for Characterisation of Anti-microbial Materials -- 5.6 Electron Microscopy Techniques -- 5.7 Scanning Electron Microscopy and Nano-anti-microbial Characterisation -- 5.7.1 Sample Preparation for SEM. , 5.7.2 Novel Variants of SEM for Nano-anti-microbial Analysis -- 5.7.3 Field Emission SEM for Material Characterisation -- 5.8 Transmission Electron Microscopy (TEM) -- 5.8.1 High Resolution TEM (HRTEM), STEM and HAADF STEM -- 5.9 EM Tomography and 3D Reconstruction -- 5.9.1 Sample Preparation for TEM and STEM techniques -- 5.10 Confocal Microscopy and Optical Sectioning -- 5.11 Emerging and Future Techniques for Material Visualisation -- 5.12 Conclusions -- References -- Chapter 6 Biological Methods for Characterisation of Nano-anti-microbial Materials -- 6.1 Introduction -- 6.2 Biological Assessment of Anti-microbial Materials -- 6.2.1 Principle Methods of Anti-microbial Activity Assessment -- 6.2.2 Minimum Inhibitory and Bactericidal Concentration Bioassays for Assessment of Anti-microbial Activity -- 6.2.3 Relevance of MIC Determination for Nano-anti-microbial Materials -- 6.2.4 Plate Counts and Anti-microbial Activity -- 6.2.5 Time-Kill Assays -- 6.2.6 Automated Microplate Methods for Assessment of Anti-microbial Activity -- 6.2.7 Disk Diffusion-Based Assays for Determination of in vitro Anti-microbial Activity -- 6.2.8 Assessing Anti-microbial Activity Using Flow Cytometry -- 6.2.9 Fluorescence Detection and Flow Cytometry -- 6.3 Fluorescence Microscopy Methods for Biological Characterization of Nano-anti-microbial Materials -- 6.3.1 Basic Principles of Fluorescence Microscopy -- 6.3.2 Excitation Sources in Fluorescence Microscopy -- 6.3.3 Applications of Fluorescence Microscopy to Nano-anti-microbial Materials -- 6.3.4 Choice of Fluorophores for Assessment of Nano-anti-microbials -- 6.3.5 Differential Membrane Permeability Staining -- 6.3.6 Multiphoton Fluorescence Microscopy and Anti-microbial Materials -- 6.3.7 Assessing the Cytotoxicity of Nano-Anti-microbials towards Eukaryotic Cell Lines -- 6.4 Conclusions -- References. , Chapter 7 Molecular Biological Techniques -- 7.1 Introduction -- 7.2 What is Molecular Biology? -- 7.3 What is DNA? -- 7.4 What is RNA? -- 7.5 Molecular Biological Techniques -- 7.5.1 Polymerase Chain Reaction (PCR) -- 7.5.2 Reverse Transcriptase PCR (RT-PCR) -- 7.5.3 Real Time Polymerase Chain Reaction -- 7.5.4 Hybridisation -- 7.5.5 In situ Hybridisation -- 7.5.6 Fluorescence in situ Hybridisation -- 7.5.7 FISH Probes -- 7.5.8 SAGE (Serial Analysis of Gene Expression) -- 7.5.9 Microarrays and Gene Chips -- 7.5.10 Advances Using Lab-on-a-Chip or Microfluidic Devices -- 7.5.11 Bioinformatics -- 7.6 Quorum Sensing -- 7.7 Phylogenetic Stains -- 7.8 Conclusions -- References -- Chapter 8 Conclusions -- Subject Index.
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  • 5
    Publication Date: 2017-05-10
    Description: Increases in anthropogenic emissions of sulfur (S) and nitrogen (N) have resulted in increases in the associated atmospheric deposition of acidic compounds. In sensitive watersheds, this deposition has initiated a cascade of negative environmental effects on aquatic ecosystems, resulting in a degradation or loss of valuable ecosystem goods and services. Here, we report the activities of an expert workgroup to synthesize information on acidic deposition-induced aquatic acidification from the published literature and to link critical load exceedances with ecosystem services and beneficiaries, using the Stressor–Ecological Production function–Final Ecosystem Services (STEPS) Framework and the Final Ecosystem Goods and Services Classification System (FEGS-CS). Experts identified and documented the sensitive aquatic ecosystem ecological endpoints valued by humans, and the environmental pathways through which these endpoints may experience degradation in response to acidification. Beneficiary groups were then identified for each sensitive ecological endpoint to clarify relationships between humans and the effects of aquatic acidification, and to lay the foundation for future research and analysis to value these FEGS.
    Electronic ISSN: 2150-8925
    Topics: Energy, Environment Protection, Nuclear Power Engineering
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  • 6
    Publication Date: 2012-11-14
    Description: Land management and natural resource public policy decision-making in the United States can benefit from two resource damage/recovery concepts: ecosystem service (ES) and critical load (CL). The purpose of this paper is to suggest an integrated approach to the application of ES and CL principles for public land management and natural resource policy decision-making. One well known example that is appropriate for ES and CL evaluation is examined here: the acidification of soil and drainage water by atmospheric deposition of acidifying sulfur and nitrogen compounds. A conceptual framework illustrates how the ES and CL approaches can be combined in a way that enhances the strengths of each. This framework will aid in the process of translating ES and CL principles into land management and natural resource policy decision-making by documenting the impacts of pollution on environmental goods and services that benefit humans.
    Electronic ISSN: 2073-4441
    Topics: Energy, Environment Protection, Nuclear Power Engineering
    Published by MDPI Publishing
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  • 7
    Publication Date: 2015-07-12
    Description: Background: The blue crab, Callinectes sapidus, is economically and ecologically important in western Atlantic and Gulf of Mexico coastal estuaries. In 2010 blue crabs in the northern Gulf of Mexico were exposed to crude oil and chemical dispersants from the Deepwater Horizon oil spill. To characterize the blue crab transcriptome and identify genes that could be regulated in response to oil exposure we sequenced transcriptomes from hepatopancreas and gill tissues of juvenile blue crabs after exposing them to a water-accommodated fraction of surrogate Macondo crude oil in the laboratory and compared them to transcriptomes from an unexposed control group. Results: Illumina sequencing provided 42.5 million paired-end sequencing reads for the control group and 44.9 million paired-end reads for the treatment group. From these, 73,473 transcripts and 52,663 genes were assembled. Comparison of control and treatment transcriptomes revealed about 100 genes from each tissue type that were differentially expressed. However, a much larger number of transcripts, approximately 2000 from each tissue type, were differentially expressed. Several examples of alternatively spliced transcripts were verified by qPCR, some of which showed significantly different expression patterns. The combined transcriptome from all tissues and individuals was annotated to assign putative gene products to both major gene ontology categories as well as specific roles in responses to cold and heat, metabolism of xenobiotic compounds, defence, hypoxia, osmoregulation and ecdysis. Among the annotations for upregulated and alternatively-spliced genes were candidates for the metabolism of oil-derived compounds. Conclusions: Previously, few genomic resources were available for blue crabs or related brachyuran crabs. The transcriptome sequences reported here represent a major new resource for research on the biology of blue crabs. These sequences can be used for studies of differential gene expression or as a source of genetic markers. Genes identified and annotated in this study include candidates for responses of the blue crab to xenobiotic compounds, which could serve as biomarkers for oil exposure. Changes in gene expression also suggest other physiological changes that may occur as the result of exposure to oil.
    Electronic ISSN: 1471-2164
    Topics: Biology
    Published by BioMed Central
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  • 8
    Publication Date: 2017-12-28
    Description: Objective—Pulmonary artery smooth muscle cells (PASMCs) from neprilysin (NEP) null mice exhibit a synthetic phenotype and increased activation of Rho GTPases compared with their wild-type counterparts. Although Rho GTPases are known to promote a contractile SMC phenotype, we hypothesize that their sustained activity decreases SM-protein expression in these cells.Approach and Results—PASMCs isolated from wild-type and NEP−/− mice were used to assess levels of SM-proteins (SM-actin, SM-myosin, SM22, and calponin) by Western blotting, and were lower in NEP−/− PASMCs compared with wild-type. Rac and Rho (ras homology family member) levels and activity were higher in NEP−/− PASMCs, and ShRNA to Rac and Rho restored SM-protein, and attenuated the enhanced migration and proliferation of NEP−/− PASMCs. SM-gene repressors, p-Elk-1, and Klf4 (Kruppel lung factor 4), were higher in NEP−/− PASMCs and decreased by shRNA to Rac and Rho. Costimulation of wild-type PASMCs with PDGF (platelet-derived growth factor) and the NEP substrate, ET-1 (endothelin-1), increased Rac and Rho activity, and decreased SM-protein levels mimicking the NEP knock-out phenotype. Activation of Rac and Rho and downstream effectors was observed in lung tissue from NEP−/− mice and humans with chronic obstructive pulmonary disease.Conclusions—Sustained Rho activation in NEP−/− PASMCs is associated with a decrease in SM-protein levels and increased migration and proliferation. Inactivation of RhoGDI (Rho guanine dissociation inhibitor) and RhoGAP (Rho GTPase activating protein) by phosphorylation may contribute to prolonged activation of Rho in NEP−/− PASMCs. Rho GTPases may thus have a role in integration of signals between vasopeptides and growth factor receptors and could influence pathways that suppress SM-proteins to promote a synthetic phenotype.
    Keywords: Vascular Disease
    Print ISSN: 1079-5642
    Electronic ISSN: 1524-4636
    Topics: Medicine
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  • 9
    Electronic Resource
    Electronic Resource
    Oxford, UK : Blackwell Publishing Ltd
    Journal of cardiac surgery 10 (1995), S. 0 
    ISSN: 1540-8191
    Source: Blackwell Publishing Journal Backfiles 1879-2005
    Topics: Medicine
    Notes: Cardiac and cerebral events during coronary artery bypass graft (CABG) surgery remain a major cause of morbidity and mortality. Efforts made to reduce these events will have a significant impact on CABG results. The objective of this study was to examine our results in 394 patients undergoing primary CABG using the single clamp technique that probably has better myocardial and cerebral protective properties than the conventional technique of partial aortic occlusion. Age range was 35 to 88, mean of 66 years, and 168 (43%) were ≥ 70 years of age; 121 (31%) were females, 118 (30%) were diabetic, 339 (82%) were in New York Heart Association Functional Class III or IV, 77 (20%) had a preoperative intra-aortic balloon pump, 213 (54%) were nonelective, 293 (75%) had three vessel disease, and 55 (14%) had critical left main coronary artery stenosis. Antegrade crystalloid cardioplegia was used in the majority of patients, and the distal and proximal anastomoses were sequentially constructed during a single period of total aortic occlusion. The mean number of grafts was 3.5, and 339 (86%) had ≥ 3 grafts; at least one internal mammary artery was used in 346 (88%), a sequential vein or mammary artery in 181 (46%), and 55 (14%) had at least one coronary endarterectomy. The mean cross-clamp time, bypass time, and time to wean off bypass were 63, 83, and 20 minutes, respectively. The overall operative mortality was 11 of 394 (2.8%), a myocardial infarction/low-cardiac output state occurred in 19 (4.8%), and a stroke in 3 (0.8%). The total number of these events or adverse outcomes related directly to the clamping technique was 33 events in 23 patients (8.4%). The low rate of cardiac and cerebral complications associated with the single clamp technique in spite of an increased ischemia time is consistent with our previous results.
    Type of Medium: Electronic Resource
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  • 10
    Electronic Resource
    Electronic Resource
    s.l. : American Chemical Society
    Environmental science & technology 27 (1993), S. 1482-1486 
    ISSN: 1520-5851
    Source: ACS Legacy Archives
    Topics: Chemistry and Pharmacology , Energy, Environment Protection, Nuclear Power Engineering
    Type of Medium: Electronic Resource
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