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Cấu trúc
Series Preface
Contents
Introduction Setting of the Scene, Definitions, and Guide to Volume
References
Part I: Chemical Distribution in Soil and Sediment
Importance of Soil Properties and Processes on Bioavailability of Organic Compounds
1 Introduction
2 General Considerations
2.1 Types of Sorbates
2.2 Sorption Fundamentals
3 Properties of Soil Particles Important for Bioavailability
3.1 Solid and Dissolved Organic Matter
3.2 Pyrogenic Carbonaceous Materials
3.3 Mineral Phases
3.4 Anthropogenic Substances
3.5 Other Soil Features Affecting Bioavailability
4 Sorption and Bioavailability: Thermodynamic Controls
4.1 Chemical Speciation
4.2 Partition Models and Structure-Activity Relationships
4.3 Competitive Effects
5 Sorption and Bioavailability: Non-equilibrium
5.1 General Considerations
5.2 High Desorption Resistance and Its Effects on Bioavailability
5.3 Receptor-Facilitated Bioavailability
5.3.1 Receptor Behavior
5.3.2 The Surface Depletion Effect
5.3.3 Alteration of Soil Matrix or Interfacial Chemistry
5.3.4 Release of Biosurfactants
5.3.5 Direct Mining
6 Conclusions and Future Directions
Sorption of Polar and Ionogenic Organic Chemicals
1 Sorption of Polar (Nonionic) Chemicals
1.1 Classical Linear Free Energy Relationships
1.2 Using a Systematic Polyparameter Approach to Account for all Nonionic Sorptive Interactions
2 Sorption of Ionogenic Chemicals
2.1 Relevance of Ionogenic Chemicals for Risk Assessment
2.2 Chemical Speciation for Ionogenic Chemicals
2.3 Sorbent Speciation Driving Surface Potentials
2.4 Relevant Solvent Parameters for Ionogenic Chemicals
2.5 Relevant Chemical Parameters for Ionogenic Chemicals
2.6 Relevant Sorbent Phases in Soils for Organic Cations
2.7 Sorption of Amphoteric IOCs
Environmental Fate Assessment of Chemicals and the Formation of Biogenic Non-extractable Residues (bioNER)
1 Fate of Chemicals in the Environment: Controlling Factors and Relevance for Risk Assessment
2 Environmental Fate and NER Risk Assessment in Regulatory Testing of Organic Chemicals
3 Microbial Degradation of Organic Chemicals
4 Microbial Biomarkers for bioNER Analytics
5 BioNER Explained Part of `Black Box´ NER in Several Fate Assessments
6 Direct and Indirect Assimilation of Carbon from Chemicals as Two Routes for bioNER Formation
7 Growth and Starvation Metabolism as Two Routes for bioNER Formation
8 Recent ECHA Suggestions for Differentiation Between the Three Types of NER
9 Concluding Remarks and Future Perspectives
Annex
Impact of Sorption to Dissolved Organic Matter on the Bioavailability of Organic Chemicals
2 Sorption of Organic Chemicals to DOM
3 Impact of Sorption to DOM on the Bioavailability of Organic Chemicals
3.1 Bioaccumulation
3.2 Biodegradation
4 Concluding Remarks
Part II: Bioavailability and Bioaccumulation
Measuring and Modelling the Plant Uptake and Accumulation of Synthetic Organic Chemicals: With a Focus on Pesticides and Root ...
2 Plant Uptake of Xenobiotic Compounds
2.1 Transfer from Soil Solution to the Root Including Bioavailable and Residual Fractions
2.2 Plant Uptake via the Root Pathway
3 Measurement of Plant Uptake
3.1 Root Concentration Factor (RCF)
3.2 Translocation Factor (TF)
3.3 Transpiration Stream Concentration Factor (TSCF)
3.4 Plant Uptake Factor (PUF)
3.5 Laboratory Methods of Measuring Plant Uptake
3.5.1 Intact Plant
3.5.2 De-topped Plant
3.5.3 Future Method Development
4 Physical-Chemical Relationships Used in the Modelling of Plant Uptake
4.1 Octanol-Water Partition Coefficient (log KOW) and TSCF
5 Modelling Plant Uptake for Environmental Fate Predictions
5.1 Plant Uptake Within Current Environmental Fate Models
6 Conclusion
Bioaccumulation and Toxicity of Organic Chemicals in Terrestrial Invertebrates
1 Exposure Routes and Organismal Traits
2 Bioaccumulation and Toxicity
3 Models
4 Organic Chemicals and Interactions with Biota
4.1 Plant Protection Products
4.1.1 Herbicides
Bioaccumulation of Herbicides
Effect of Herbicides at Sub-Organism Level
Effect of Herbicides at Individual and Population Levels
4.1.2 Insecticides
Bioaccumulation of Insecticides
Effect of Insecticides at Sub-Organism Level
Effects of Insecticides at Individual and Population Levels
4.1.3 Fungicides
Bioaccumulation of Fungicides
Effect of Fungicides at Sub-Organism Level
Effects of Fungicides at Individual and Population Levels
4.1.4 Molluscicides
Effect of Molluscicides at Individual and Population Levels
4.2 Pharmaceuticals: Veterinary and Human
4.2.1 Bioaccumulation of Pharmaceuticals
4.2.2 Effects of Pharmaceuticals at Sub-Organism Level
4.2.3 Effects of Pharmaceuticals at Individual and Population Levels
4.3 Polycyclic Aromatic Compounds
4.3.1 Bioaccumulation of Polycyclic Aromatic Compounds
4.3.2 Effect of Polycyclic Aromatic Compounds at Sub-Organism Level
4.3.3 Effect of Polycyclic Aromatic Compounds at Individual and Population Levels
4.4 Polychlorinated Biphenyls
4.4.1 Bioaccumulation of Polychlorinated Biphenyls
4.4.2 Effect of Polychlorinated Biphenyls at Sub-Organism Level
4.4.3 Effect of Polychlorinated Biphenyls at Individual and Population Levels
4.5 Flame Retardants
4.5.1 Bioaccumulation of Flame Retardants
4.5.2 Effects of Flame Retardants at Sub-Organism Level
4.5.3 Effects of Flame Retardants at Individual and Population Levels
4.6 Personal Care Products
4.6.1 Bioaccumulation of Personal Care Products
4.6.2 Effect of Personal Care Products at the Sub-Organism Level
4.6.3 Effect of Personal Care Products at Individual and Population Levels
4.7 Mixtures
5 Bioaccumulation in Edible Terrestrial Invertebrates: Link to Human Exposure
6 Final Remarks
Assessment of the Oral Bioavailability of Organic Contaminants in Humans
2 Concepts of In Vivo Bioavailability
2.1 Concepts of Absolute Bioavailability and Relative Bioavailability
2.2 Bioavailability Process and Limitations
2.2.1 Passive Diffusion
2.2.2 Carrier-Mediated Transport
2.3 Rate Limiting Steps in the Gastrointestinal Bioavailability
2.3.1 Dissolution Rate
2.3.2 Perfusion Rate
2.3.3 Diffusion/Permeability Rate
2.3.4 Gastric Emptying Rate
2.4 Computational Modelling and Pharmacoinformatic Approaches to the Prediction of Oral Bioavailability
3 Measurement of Relative Bioavailability (In Vivo Studies)
3.1 Animal Model Selection
3.2 Body Weight
3.3 Exposure Period
3.4 Exposure Mode
3.5 Biomarkers
3.6 Exposure Dose
4 Sample Collection, Treatment and Analysis for Organic Contaminants
5 Validation of In Vitro Studies Using In Vivo Studies
5.1 Correlations Between In Vivo and In Vitro Methods (IVIVC)
6 Challenges and Expectations of Bioavailability Studies
6.1 Improvement of Available In Vitro Models and Statistical Prediction Models
6.2 Prediction of Soil Properties to Compound Bioavailability
6.3 Contaminant Forms and States of Speciation Relate to their Bioavailability
7 Conclusions
Part III: Impact of Sorption Processes on Toxicity, Persistence and Remediation
Carbon Amendments and Remediation of Contaminated Sediments
2 Sediment Remediation
2.1 Need for Remediation
2.2 Traditional Methods
2.2.1 Monitored Natural Recovery
2.2.2 Dredging
2.2.3 Capping
3 Sediment Remediation with Carbon Amendments
3.1 Activated Carbon as a Sorbent
3.2 Applicability
3.3 Remediation Efficiency
3.4 Secondary Ecological Effects
4 Concluding Remarks and Future Prospects
Why Biodegradable Chemicals Persist in the Environment? A Look at Bioavailability
2 Persistence Versus Biodegradability
3 Bioavailability Processes
4 The Microbial Component of Bioavailability: Solubilization and Cell Positioning
5 The Geochemical Component of Bioavailability: Organic Matter and Black Carbon
6 Bioavailability of Biodegradable Chemicals Present as Non-extractable Residues
7 Persistence and Chemical Management
8 Bioavailability in the OECD Test Series
9 Non-standardized Approaches for Assessing Biodegradation
10 Concluding Remarks
Bioavailability as a Microbial System Property: Lessons Learned from Biodegradation in the Mycosphere
1 Bioavailability and Contaminant Degrading Microbial Systems
1.1 Introduction
1.2 Bioavailability as a Driver of Biodegradation
1.3 Microbial System Properties as Drivers of Bioavailability
2 Traits of Mycelial Fungi Relevant for Contaminant Biodegradation
2.1 Fungi Are Ubiquitous and Also Present in Contaminated Habitats
2.2 Fungi Have a Broad Catabolic Potential and Decouple Contaminant Transformation from Biomass Formation
2.3 Fungi Adapt Well to Habitat Heterogeneity and Create Suitable Niches for Contaminant Biodegradation
3 Linking Mycosphere Traits and Processes to Bottlenecks of Contaminant Bioavailability
3.1 Bottleneck 1: Availability to Degraders
3.2 Bottleneck 2: Activity and Abundance of Degraders
3.3 Bottleneck 3: Functional Stability and Diversity of Degraders
4 Lessons Learned: Contaminant Bioavailability Stretches over Various Organizational Levels and Requires Deep Understanding of...
Part IV: Methods for Measuring Bioavailability
Bioavailability and Bioaccessibility of Hydrophobic Organic Contaminants in Soil and Associated Desorption-Based Measurements
2 Conceptual Fate of HOCs in Soils
2.1 Temporal Fractionation of HOCs in Soil
2.1.1 Sorption
2.1.2 Desorption
Desorption Kinetics
3 Contaminant Bioavailability and Bioaccessibility
3.1 Measurement of HOC Bioaccessibility
3.1.1 Exhaustive Measurement of HOC Bioaccessibility
3.1.2 Non-exhaustive Measurement of HOC Bioaccessibility
Mild Solvent Extractions
Aqueous and Aqueous-Based Non-exhaustive Extractions
Extraction with Cyclodextrins
Solid-Phase Extractions
3.1.3 In Vitro Extractions to Simulate Oral Ingestion and Gastrointestinal Digestion Soil-Borne HOCs
4 Desorption-Resistant or Residual HOC Fractions and Associated Potential Risks
5 Considerations for the Development of a Simple Intelligent Desorption Extraction Scheme for the Measurement of HOCs´ Bioacce...
6 Conclusion and Suggestions for Further Research
Appendix
Passive Sampling for Determination of the Dissolved Concentrations and Chemical Activities of Organic Contaminants in Soil and...
1 Fate of Organic Contaminants in Soils and Sediments
2 The Role of Dissolved Organic Contaminants in Soil and Sediment Pore Water
3 Measuring Dissolved Concentrations of Organic Contaminants in Pore Water
4 Passive Sampling for Measuring Dissolved Concentrations of Organic Contaminants
5 Non-depletion Passive Sampling
6 Equilibrium Passive Sampling in Soils and Sediments
7 Confirming the Equilibrium in Equilibrium Passive Sampling
8 Non-equilibrium Passive Sampling in Soils and Sediments
9 Passive Sampling in Soil Slurries Versus Dry Soil
10 Outlook for Passive Sampling in Soils and Sediments
Microbial, Plant, and Invertebrate Test Methods in Regulatory Soil Ecotoxicology
2 Overview on Soil Ecotoxicological Test Methods
2.1 Soil Properties
2.2 Biological Test Methods
2.2.1 Soil Microorganisms
2.2.2 Soil Invertebrates
2.2.3 Plants
2.3 Bioavailability in Prospective and Retrospective Risk Assessment
2.3.1 General Considerations
2.3.2 Case Study
2.3.3 Prospective Risk Assessment
2.3.4 Applications of Bioavailability in Retrospective Risk Assessment
3 Concluding Remarks and Future Prospects
Part V: Bioavailability in Chemical Risk Assessment
Implementation of Bioavailability in Prospective and Retrospective Risk Assessment of Chemicals in Soils and Sediments
2 Consideration of Bioavailability in Prospective Risk Assessment
2.1 General
2.2 Derivation of Risk Limits/Quality Standards
3 Inclusion of Bioavailability in Retrospective Risk Assessment
3.1 General
3.2 Tiered Approaches to Human and Ecological Risk Assessment
3.3 Site-Specific Risk Assessment: The Triad Approach
4 Implementation of Bioavailability in Risk Assessment
4.1 Why Implementation of Bioavailability?
4.2 Experimental Methods Available for Implementation of Bioavailability in (Tiered) Risk Assessment
4.2.1 Organic Contaminants
4.2.2 Heavy Metals
4.3 Reference Framework as the Basis for Implementation of Bioavailability
4.3.1 Relating Actually Bioavailable Concentrations to the Toxicity of Aquatic Biota
4.3.2 Relating Potentially Bioavailable Concentrations to the Toxicity of Soil Biota
5 Perspective
Concluding Remarks and Research Needs
1 Is Bioavailability Science Ready for Use in Regulation of Organic Chemicals?
2 How Should Bioavailability of Organic Chemicals Be Measured?
3 How Should Bioavailability Be Implemented into Regulation of Organic Chemicals?
4 Research Needs in Bioavailability
5 Conclusions
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