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  • 1
    Keywords: Pollutants. ; Electronic books.
    Description / Table of Contents: Reviews of Environmental Contamination and Toxicology provides succinct, critical reviews of timely advances, philosophy and significant accomplishments in xenobiotics as well as those in need of study. The text also explores the toxicological implications involved.
    Type of Medium: Online Resource
    Pages: 1 online resource (231 pages)
    Edition: 1st ed.
    ISBN: 9781441968807
    Series Statement: Reviews of Environmental Contamination and Toxicology Series ; v.208
    DDC: 363.73
    Language: English
    Note: Intro -- Special Foreword -- Foreword -- Preface -- Contents -- Contributors -- Atmospheric Perfluorinated Acid Precursors: Chemistry, Occurrence, and Impacts -- 1 Introduction -- 2 Mechanisms of Atmospheric Formation of Perfluorinated Acids -- 2.1 Perfluorocarboxylic Acids -- 2.1.1 Mechanisms for Atmospheric Formation of Perfluoroacyl Halides -- 2.1.2 Mechanisms for Direct Atmospheric Formation of PFCAs -- 2.2 Perfluorosulfonic Acids (PFSAs) -- 3 Chemistry of Perfluorinated Acid (PFA) Precursors -- 3.1 Volatile Anesthetics -- 3.1.1 CF3 (CF2) x CHClBr -- 3.1.2 CF3 (CF2) x CHClOCHF 2 -- 3.2 Hydrochlorofluorocarbons (HCFCs) -- 3.2.1 CF3 (CF2) x CHFCl -- 3.2.2 CF3 (CF2) x CHCl 2 -- 3.3 Hydrofluorocarbons (HFCs, Non-telomer Based) -- 3.3.1 Saturated Hydrofluorocarbons (HFCs) -- 3.3.2 Hydrofluoroolefins (HFOs) -- 3.4 Fluorotelomer and Related Compounds -- 3.4.1 Perfluorinated Aldehyde (PFAL) Hydrates -- 3.4.2 Perfluorinated Aldehydes (PFALs) -- 3.4.3 Fluorotelomer Aldehydes (FTALs) -- 3.4.4 Odd Fluorotelomer Alcohols (oFTOHs) -- 3.4.5 Even Fluorotelomer Alcohols (FTOHs) -- 3.4.6 Fluorotelomer Olefins (FTOs) -- 3.4.7 Fluorotelomer Iodides (FTIs) -- 3.4.8 Fluorotelomer Acrylate (FTAc) -- 3.5 Perfluoroalkanesulfonamides -- 3.5.1 N -Alkyl-perfluoroalkanesulfonamides (NAFSA) -- 3.5.2 N -Alkyl-perfluoroalkanesulfamidoethanols (NAFSE) -- 4 Atmospheric Sources and Levels -- 4.1 Volatile Fluorinated Anesthetics -- 4.2 Hydrochlorofluorocarbons (HCFCs) -- 4.2.1 Potential Sources to the Atmosphere -- 4.2.2 Atmospheric Concentrations -- 4.3 Hydrofluorocarbons (HFCs, Non-telomer Based) -- 4.3.1 Saturated Hydrofluorocarbons (HFCs) -- 4.3.2 Hydrofluoroolefins (HFOs) -- 4.4 Fluorotelomer Compounds -- 4.4.1 Potential Sources to the Atmosphere -- 4.4.2 Atmospheric Concentrations -- 4.5 Perfluorosulfonamides -- 4.5.1 Potential Sources to the Atmosphere. , 4.5.2 Atmospheric Concentrations -- 5 Impact of Precursors on Environmental Perfluorinated Acid (PFA) Levels -- 5.1 Trifluoroacetic Acid (TFA) -- 5.2 Perfluorooctanesulfonic Acid (PFOS), Perfluorooctanoic Acid (PFOA) and Perfluorononanoic Acid (PFNA) -- 5.3 Long-Chained Perfluorocarboxylic Acids (PFCAs) -- 6 Summary -- References -- Isomer Profiling of Perfluorinated Substances as a Tool for Source Tracking: A Review of Early Findings and Future Applications -- 1 Introduction -- 2 Isomer Nomenclature -- 3 Historical and Current Manufacturing Sources of Perfluoroalkyl Isomers -- 4 Isomer-Specific Analytical Methodologies -- 4.1 Current Analytical Separation Methods -- 4.2 Analytical Quantification Bias -- 4.3 Strategies for Isomer Separation by LC--MS/MS -- 5 Influence of PhysicalChemical Properties on Environmental Fractionation of Perfluoroalkyl Isomers -- 6 Characterization of Perfluoroalkyl Isomer Profiles in the Environment -- 6.1 PFOA Isomer Profiles -- 6.2 Perfluoroalkyl Sulfonate and Sulfonamide Isomer Profiles -- 6.3 Perfluorocarboxylate Isomer Profiles Other than PFOA -- 7 Differences in Toxicity and Bioaccumulation of PFA Isomers -- 8 Summary -- References -- Biodegradation of Fluorinated Alkyl Substances -- 1 Introduction -- 2 The Persistence of Perfluorinated Surfactants -- 3 Understanding the Complex Biodegradation of Fluorotelomer-based Chemicals -- 4 Biodegradation of N-Alkyl Perfluorooctane Sulfonamide Derivatives -- 5 The Role of Fluorinated Polymers -- 6 On the Way to Mineralization Biodegradation of Organic Molecules that Have Low Fluorine Content -- 7 Summary -- References -- Perfluorinated Substances in Human Food and Other Sources of Human Exposure -- 1 Introduction -- 2 PFCs in Edible Fish and Seafood -- 3 Contamination of Food -- 3.1 Indirect Contamination of PFCs in Food Items. , 3.2 Direct Contamination of PFCs in Commercial Food Items -- 4 PFCs in Drinking Water -- 5 Safety Limits and Tolerable Daily Intakes -- 6 Perfluorinated Compounds in House Dust and Air -- 7 Correlation Between PFCs -- 8 Outlook -- 9 Summary -- References -- Index.
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  • 2
    ISSN: 1573-2932
    Keywords: atmospheric fate ; atmospheric transport ; deposition ; emission ; long-range transport ; pesticides ; registration ; remote area ; risk assessment ; transformation
    Source: Springer Online Journal Archives 1860-2000
    Topics: Energy, Environment Protection, Nuclear Power Engineering
    Notes: Abstract The Health Council of the Netherlands organised an international workshop on the fate of pesticides in the atmosphere and possible approaches for their regulatory environmental risk assessment. Approximately forty experts discussed what is currently known about the atmospheric fate of pesticides and major gaps in our understanding were identified. They favoured a tiered approach for assessing the environmental risks of atmospheric dispersion of these chemicals. In the first tier a pesticide's potential for emission during application, as well as its volatilisation potential should be assessed. Estimates of the former should be based on the application method and the formulation, estimates of the latter on a compound's solubility in water, saturated vapour pressure and octanol/water partition coefficient. Where a pesticide's potential for becoming airborne exceeds critical values, it should be subjected to a more rigorous second tier evaluation which considers its toxicity to organisms in non-target areas. This evaluation can be achieved by calculating and comparing a predicted environmental concentration (PEC) and a predicted no-effect concentration (PNEC). By applying an extra uncertainty factor the PNEC can be provisionally derived from standard toxicity data that is already required for the registration of pesticides. Depending on the distance between the source and the reception area, the PEC can be estimated for remote areas using simple dispersion, trajectory type models and for nearby areas using common dispersion models and standard scenarios of pesticide use. A pesticide's atmospheric transport potential is based on factors such as its reaction rate with OH radicals. It should be used to discriminate between those compounds for which only the risks to nearby ecosystems have to be assessed, and those for which the risks to remote ecosystems also have to be determined. The participants were of the opinion that this approach is, in principle, scientifically feasible, although the remaining uncertainties are substantial. Further field and laboratory research is necessary to gain more reliable estimates of the physico-chemical properties of pesticides, to validate and improve environmental fate models and to validate the applicability of standard toxicity data. This will increase both the accuracy of and our confidence in the outcome of the risk assessment.
    Type of Medium: Electronic Resource
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  • 3
    ISSN: 1573-2932
    Keywords: atmospheric lifetimes ; pesticides ; reaction rates ; transformation products
    Source: Springer Online Journal Archives 1860-2000
    Topics: Energy, Environment Protection, Nuclear Power Engineering
    Notes: Abstract The current knowledge about transformation rates and products of pesticides in the atmosphere is reviewed. Reactive species and their concentrations in the atmosphere are presented. Reactions of pesticides with these species (including photolysis) in the gas and the particulate phase are evaluated from available experimental data. The potential of estimation methods is discussed. Experimental techniques for laboratory and outdoor measurements are reviewed. Finally, an estimation is made of uncertainties in atmospheric lifetimes due to chemical or physical reactions. It is concluded that the most important transformation of pesticides in the atmosphere is due to reaction with OH radicals. Very few experimental data for pesticides are available though. The levels of uncertainty in OH radical concentrations are acceptable, however, for a proper estimation of atmospheric removal rates due to reactions with OH radicals of those pesticides for which experimental transformation rates (of homologues) are available.
    Type of Medium: Electronic Resource
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  • 4
    Publication Date: 2023-02-17
    Description: We investigated the ability of accelerated solvent extraction (ASE) to extract selected lipid biomarkers (C19–C34 n-alkanes, n-alcohols and n-fatty acids as well as dehydroabietic acid and β-sitosterol) from a sandy soil profile under Corsican pine. Two organic layers (moss and F1) as well as two mineral soil horizons (EA and C1) were sampled and extracted with DCM/MeOH (93:7 v/v) by ASE at 75 °C and a pressure of 6.9 × 106 Pa or 17 × 106 Pa. Soxhlet extractions were used as the established reference method. After clean-up and derivatization with BSTFA, the extracts were analyzed on GC/MS. Using Soxhlet as a reference, we found ASE to extract all compounds adequately. The n-alkanes, especially, were found to be extracted very efficiently from all horizons studied. Only the n-fatty acids and β-sitosterol from the organic layers seemed to be extracted at a slightly lower efficiency by ASE. In all but two instances the relative abundance of extracted lipids within a component class was the same regardless of the extraction method used. Using a higher pressure in the ASE extractions significantly increased the extraction efficiency for all component classes in the moss layer, except β-sitosterol. The effect was most pronounced for the n-alkanes. In the EA horizon, a higher pressure slightly reduced the extraction efficiency for dehydroabietic acid. The observed differences between ASE and Soxhlet extractions as well as the pressure effect can be explained by a decrease in polarity of the extractant due to the elevated pressure and temperature applied during ASE extractions as compared to Soxhlet extractions. This would mainly increase the extraction efficiency of the least polar biomarkers: the n-alkanes as was observed. In addition, a better penetration of still partially water-filled micro pores under elevated pressure and temperature may have played a role.
    Type: Article , PeerReviewed
    Format: text
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