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  • 1
    Keywords: Sewage-Purification-Technological innovations. ; Electronic books.
    Type of Medium: Online Resource
    Pages: 1 online resource (724 pages)
    Edition: 1st ed.
    ISBN: 9780323900119
    Language: English
    Note: Front cover -- Half title -- Full title -- Copyright -- Contents -- Contributors -- 1 - Nanoadsorbents for scavenging emerging contaminants from wastewater -- 1.1 Introduction -- 1.2 Emerging contaminants -- 1.3 Occurrence of emerging contaminants in aquatic systems -- 1.4 Exposure pathways of emerging contaminants in the environment -- 1.5 Treatment technologies for removal of ECs -- 1.6 Conventional treatment methods -- 1.7 Emerging methods -- 1.7.1 Biological treatment method -- 1.7.2 Advanced oxidation process -- 1.8 Nanoadsorbents -- 1.9 Classification of nanoadsorbents -- 1.10 Methods for preparation of nanoadsorbents -- 1.11 Properties of nanoadsorbents -- 1.12 Mechanisms of nanoadsorption -- 1.13 The π-π interaction -- 1.14 Electrostatic interaction -- 1.15 Hydrophobic interaction -- 1.16 Hydrogen bonding -- 1.17 Factors affecting adsorption process -- 1.17.1 pH -- 1.17.2 Ionic strength -- 1.17.3 Dissolved organic matter -- 1.18 Conclusions -- References -- 2 - Treatment aspect of an emerging pollutant from Pharmaceutical industries using advanced oxidation process: past, curre ... -- 2.1 Introduction -- 2.2 Treatment technologies -- 2.2.1 Recovery process -- 2.2.2 Phase changing technologies -- 2.2.2.1 Adsorption -- 2.2.2.2 Membrane technology -- 2.2.3 Biological process -- 2.3 Advanced oxidation process -- 2.3.1 Nonphotochemical methods -- 2.3.1.1 Ozonation -- 2.3.1.2 Ozone and hydrogen peroxide (Peroxone) -- 2.3.2 Catalytic ozonation -- 2.3.3 Fenton system -- 2.3.3.1 Sulfate-based AOPs -- 2.3.4 Photochemical methods -- 2.3.4.1 O 3  + UV Method -- 2.3.4.2 H 2 O 2 +UV light Method -- 2.3.4.3 H 2 O 2 +UV+ O 3 Method -- 2.3.4.4 Photolysis -- 2.3.4.5 UV/persulfate -- 2.3.4.6 Photo-Fenton Method -- 2.3.4.7 Photocatalysis -- 2.3.4.8 Other AOPs -- 2.4 Future prospects -- References. , 3 - Membrane bioreactor (MBR) as an advanced wastewater treatment technology for removal of synthetic microplastics -- 3.1 Introduction -- 3.2 Microplastic generation and pollution -- 3.3 Effect of Synthetic microplastic pollution -- 3.4 Technical implementation of membrane bioreactor (MBR) for elimination micro plastic pollutants -- References -- 4 - Strategies to cope with the emerging waste water contaminants through adsorption regimes -- 4.1 Introduction -- 4.2 Uptake of pollutants from water via adsorption -- 4.3 Adsorbents and there use in purification of waters -- 4.4 Various emerging pollutants and their effects -- 4.4.1 Heavy metals -- 4.4.2 Dyes -- 4.4.3 Pharmaceuticals -- 4.4.4 Fluoride -- 4.4.5 Arsenic -- 4.4.6 Other emerging pollutants -- 4.5 Adsorption strategies for removal of emerging pollutants from waste waters -- 4.6 Adsorption of pollutants using hydrothermal carbonization: an environment safe procedure using carbon adsorbents -- 4.7 Use of hydrothermal carbonization (HTC) in adsorption -- 4.7.1 Dye adsorption -- 4.7.2 Pesticide(s) adsorption -- 4.7.3 Antibiotics/drugs adsorption -- 4.7.4 Endocrine disrupting chemicals (EDC) -- 4.8 Metals and metal ions adsorption by HTCs -- 4.9 Adsorption of metal(s) from mixture of metals -- 4.10 Adsorption of heavy metals using HTCs -- 4.11 Use of cost-effective adsorbent for adsorption of heavy metals -- 4.12 Uptake of metals using low-cost adsorbent materials -- 4.13 Use of agricultural residues as adsorbents -- 4.14 Uses of industrial wastes as adsorbents -- 4.14.1 Marine materials -- 4.14.2 Clay and zeolite -- 4.15 Adsorption/biosorption of antibiotics from waste water -- 4.16 Elimination of heavy metals via adsorption/biosorption -- 4.17 Heavy metals uptake using activated sludge and sludge-derived materials. , 4.18 Uptake of endocrine disrupting chemicals (EDC) -- 4.19 Future prospects -- 4.20 Conclusion -- References -- 5 - Performances of membrane bioreactor technology for treating domestic wastewater operated at different sludge retention ... -- 5.1 Introduction -- 5.1.1 Fundamentals of membrane bioreactors -- 5.1.2 Development of MBR studies -- 5.1.3 Membrane fouling in MBR systems -- 5.1.4 Performances of MBRs at high biomass retention -- 5.1.5 Task and purpose of the study -- 5.2 Materials and methods -- 5.2.1 Experimental setup -- 5.2.2 Sludge retention time -- 5.2.3 Analysis methods -- 5.3 Results and discussion -- 5.3.1 Effect of SRTs on sludge concentration in the system -- 5.3.2 Effects of SRT on sludge bioactivity -- 5.3.3 Effect of SRT on SVI and viscosity -- 5.3.4 Effects of SRT on COD removal in the system -- 5.4 Influence of SRT on sludge particle size distribution -- 5.5 Conclusions -- Acknowledgements -- Abbreviations -- References -- 6 - Advances in nanotechnologies of waste water treatment: strategies and emerging opportunities -- 6.1 Introduction -- 6.2 Metallic nanoparticles -- 6.3 Nanoadsorbents -- 6.4 Nanobiosorbents -- 6.5 Nanomembranes -- 6.6 Nanocatalysts -- 6.6.1 Photocatalyst based advance oxidation process -- 6.7 Conclusions -- Acknowledgements -- References -- 7 - Water and Wastewater Treatment through Ozone-based technologies -- 7.1 Introduction -- 7.2 Global water scenario -- 7.3 Strategies for solving the water shortage issues -- 7.4 Why ozone-based technologies used for water and wastewater treatment? -- 7.4.1 Advanced Oxidation Process (AOP) -- 7.4.2 Benefits of ozone (O 3 ) based treatment -- 7.5 Worldwide status, history, and background of O 3 based technology for drinking water and wastewater treatment -- 7.6 Use of ozone-based technology for disinfection. , 7.6.1 Mechanisms of Inactivation by Ozone -- 7.7 Treatment of municipal and industrial wastewater through Ozone-based technology -- 7.8 Removal of physical pollutants (odor and taste) through Ozone-based technologies -- 7.9 Removal of various chemical pollutants (COD, BOD and coloring agents) from wastewater through Ozone-based technologies -- 7.10 Factors affecting the Ozonation process -- 7.11 Conclusion and Future prospects -- References -- 8 - Constructed wetland: a promising technology for the treatment of hazardous textile dyes and effluent -- 8.1 Introduction -- 8.2 Classification of dyes -- 8.3 Impact of dye toxicity on environment -- 8.4 Impact of dye toxicity on living beings -- 8.5 Dye remediation strategies -- 8.5.1 Physical methods -- 8.5.2 Chemical methods -- 8.5.3 Biological methods -- 8.6 Constructed wetlands: a step towards technology transfer -- 8.7 Classification of constructed wetlands -- 8.8 Recent developments in textile wastewater treatments using constructed wetlands -- 8.9 Conclusion and future prospective -- References -- 9 - Biogenic nanomaterials: Synthesis, characteristics, and recent trends in combating hazardous pollutants (An arising sc ... -- 9.1 Introduction -- 9.2 History of nanotechnology and conventional synthetic routes of nanomaterials -- 9.3 Nanobiotechnology: An arising scientific horizon -- 9.3.1 Biologically fabricated NPs for the removal of hazardous water pollutants -- 9.3.1.1 Biologically fabricated NPs using bacteria and actinomycetes -- 9.3.1.2 Biologically fabricated NPs using fungi -- 9.3.1.3 Biologically fabricated NPs using yeast -- 9.3.1.4 Biologically fabricated NPs using algae -- 9.3.1.5 Biologically fabricated NPs using plant extracts -- 9.3.1.6 Biologically fabricated NPs using agro-industrial waste extracts. , 9.3.2 Possible mechanisms involved in biomimetic synthesis of NPs -- 9.3.2.1 Role of enzymes and proteins -- 9.3.2.2 Role of exopolysaccharides -- 9.4 Advantages, limitations, drawbacks, and future perspectives of nanobiotechnology -- 9.5 Conclusions -- References -- 10 - Removal of emerging contaminants from pharmaceutical wastewater through application of bionanotechnology -- 10.1 Introduction -- 10.2 Overview of contaminants in pharmaceutical wastewater -- 10.3 Applications of nanomaterials for the removal of pharmaceutical contaminants -- 10.3.1 Nanofiltration -- 10.3.2 Advanced oxidation process -- 10.3.3 Nanosorbents (nanotubes and zeolites) -- 10.4 Concluding remarks -- References -- 11 - Recent advances in pesticides removal using agroindustry based biochar -- 11.1 Introduction -- 11.2 What is biochar? -- 11.3 Characteristics of biochar -- 11.3.1 Porosity and surface area -- 11.3.2 pH -- 11.3.3 Functional groups at the surface -- 11.3.4 Carbon content and aromatic structures -- 11.3.5 Mineral composition -- 11.4 Modified biochar -- 11.5 Hazards of pesticides to environment and health -- 11.6 Recent development in pesticides sorption on biochar -- 11.6.1 Herbicides sorption -- 11.6.2 Insecticides sorption -- 11.6.3 Fungicides sorption -- 11.6.4 Nematicides sorption -- 11.7 Conclusion and future perspective -- References -- 12 - Bioremediation - the natural solution -- 12.1 Introduction -- 12.2 Characteristics of municipal wastewater -- 12.2.1 Organic impurities -- 12.2.2 Solids -- 12.2.3 Nutrients -- 12.2.3.1 Phosphorus -- 12.2.3.2 Nitrogen -- 12.2.3.3 Nitrogen present in municipal wastewater treatment plants (WWTPS) -- 12.2.4 Effects of phosphorus and nitrogen on environment -- 12.2.5 Pathogens -- 12.3 Wastewater treatment -- 12.3.1 Physical treatment -- 12.3.2 Chemical treatment. , 12.3.3 Thermal treatment.
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  • 2
    ISSN: 1572-9729
    Keywords: carrier ; LiP ; manganese (IV) oxide ; MnP ; Phanerochaete chrysosporium ; veratryl alcohol
    Source: Springer Online Journal Archives 1860-2000
    Topics: Biology , Energy, Environment Protection, Nuclear Power Engineering , Agriculture, Forestry, Horticulture, Fishery, Domestic Science, Nutrition
    Notes: Abstract An inert carrier (nylon sponge), a non-inert carrier (barley straw) and the addition of veratryl alcohol or manganese (IV) oxide to the cultures were used to study the production of ligninolytic enzymes by Phanerochaete chrysosporium BKM-F-1767 (ATCC 24725) during semi solid state fermentation conditions. By supplementing the medium with these compounds we could stimulate the ligninolytic system of this fungus. The different carriers employed and the effect of adding veratryl alcohol or manganese (IV) oxide to the cultures were compared in order to determine the best system to produce high activities of ligninolytic enzymes. Lignin peroxidase (LiP) activities higher than 500 U/L and manganese-dependent peroxidase (MnP) activities about 1100 U/L were achieved.
    Type of Medium: Electronic Resource
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