Big Chemical Encyclopedia

Chemical substances, components, reactions, process design ...

Articles Figures Tables About

The degraders

It is also worth mentioning that a fungus often grown commercially and sold as a delicacy, the lignin-degrading white rot fungus (Phanerochaete chry-sosporium), is an exceptionally efficient degrader of recalcitrant contaminations [Pg.172]


The amount of oxygen used in the degradation process is called the biochemical oxygen demand (BOD). A standard test has been devised to measure BOD in which the oxygen utilized by microorganisms in contact with the wastewater over a 5-day period at 20°C is measured. [Pg.308]

The presence of thiophene and its derivatives in crude oils was detected in 1899, but until 1953, the date at which the methyl-thiophenes were identified in kerosene from Agha Jari, Iran crude oil, it was believed that they came from the degradation of sulfides during refining operations. Finally, their presence was no longer doubted after the identification of benzothiophenes and their derivatives (Table 8.9), and lately of naphthenobenzothiophenes in heavy cuts. [Pg.324]

Although direct coupling of a camera to a scintillator can give acceptable results one of its major drawback is the degradation of the quantum noise mainly related to the low transmission of the optics. The following schematics summarizes the particles flux (photons and electrons) across the different stages of the detector ... [Pg.595]

Once a reaction has been performed, we have to establish whether the reaction took the desired course, and whether we obtained the desired structure. For our knowledge of chemical reactions is stiU too cursory there are so many factors influencing the course of a chemical reaction that we are not always able to predict which products will be obtained, whether we also shall obtain side reactions, or whether the reaction will take a completely different course than expected. Thus we have to establish the structure of the reaction product (Figure 1-4). A similar problem arises when the degradation of a xenobiotic in the environment, or in a living organism, has to be established. [Pg.3]

It was further shown that such equations could be extended to a wide variety of amides and related compounds and even allowed the prediction of the degradation products of agrochemicals of the benzoylphenylurea type [13]... [Pg.183]

Figure 10.3-8. The two reaction types necessary for modeling the degradation ofs-triazines in soil. Figure 10.3-8. The two reaction types necessary for modeling the degradation ofs-triazines in soil.
Tutorial Modeling the Degradation oFs-Triazine Herbicides in Soil [16]... [Pg.553]

It has already been mentioned that the degradation of s-triazine herbicides such as atrazinc in soil can be described by two reaction types only, hydrolysis and reductive dealkylation (see Figure 10.3-8). Application oF these two reaction types to a specific s-triazinc compound such as atrazinc provides the reaction network shown in Figure 10,3-12. This can also be vcriFicd by running this example on h ttp //www2,chemie,uni-erlangen.de/semces/eros/,... [Pg.553]

The major problem in such conversions is the degradation of the branched carbon side-chain on C-17 which is present in all abundant steroids and lacking in all steroid hormones. The most important starting material used in industry today is diosgenin from the Mexican dioscorea plant. It is degraded by the method of Marker to 16-dehydropregnenolone in 45% total yield. This compound is a key substance in the production of several hormones with anabolic, catabolic, and sexual effects. [Pg.283]

Hydroxybenzophenones represent the largest and most versatile class of ulbaviolet stabilizers that are used to protect materials from the degradative effects of ulbaviolet radiation. They function by absorbing ultraviolet radiation and by quenching elecbonically excited states. [Pg.1011]

Others would include the addition of materials aimed at increa sing the bioavailabiUty of the contaminant to the degrading organisms. The most studied compounds are surfactants, but cations have been reported to increase the bioavailabiUty of some organic compounds, and sorbents and clays are also considered. The dispersion of spilled oil on water by the appHcation of dispersants is perhaps the major commercial use of this idea. [Pg.24]

Examination of oven-aged samples has demonstrated that substantial degradation is limited to the outer surface (34), ie, the oxidation process is diffusion limited. Consistent with this conclusion is the observation that oxidation rates are dependent on sample thickness (32). Impact property measurements by high speed puncture tests have shown that the critical thickness of the degraded layer at which surface fracture changes from ductile to brittle is about 0.2 mm. Removal of the degraded layer restores ductiHty (34). Effects of embrittled surface thickness on impact have been studied using ABS coated with styrene—acrylonitrile copolymer (35). [Pg.203]

In the removal of contaminating ions such as (PO or Fe " a precipitate such as Ca2(P0 2 Fe(OH)2, after oxidizing ferrous ion to ferric, is formed and the soHd is removed. The addition of surfactants is usually not essential (nor desirable) since most waters contain natural surfactants that would render the soflds sufficiently hydrophobic for flotation to occur. Such surfactants derive from the degradation of organic matter, and humic substances abundantly available in nature (30). [Pg.52]

Chemical Properties. Vacuum thermal degradation of PTFE results in monomer formation. The degradation is a first-order reaction (82). Mass spectroscopic analysis shows that degradation begins at ca 440°C, peaks at 540°C, and continues until 590°C (83). [Pg.352]

Radiation Effects. The primary effect of radiation is the degradation of large molecules to small molecules. Molecular weight reduction can be... [Pg.359]

PMMA-impregnated sol—gel-derived siUca gels have also been examined (54). Long-wave uv illumination was employed in addition to benzoyl peroxide for PMMA polymerization. This method prohibited the degradation of the siUca xerogel from moisture adsorption and desorption. Overall the material behaved more like bulk PMMA than bulk siUca, with the exception of hardness. [Pg.330]

Fypass Flow Effects. There are several bypass flows, particularly on the sheUside of a heat exchanger, and these include a bypass flow between the tube bundle and the shell, bypass flow between the baffle plate and the shell, and bypass flow between the shell and the bundle outer shroud. Some high temperature nuclear heat exchangers have shrouds inside the shell to protect the shell from thermal transient effects. The effect of bypass flow is the degradation of the exchanger thermal performance. Therefore additional heat-transfer surface area must be provided to compensate for this performance degradation. [Pg.489]

Ucon HTF-500. Union Carbide Corp. manufactures Ucon HTE-500, a polyalkylene glycol suitable for Hquid-phase heat transfer. The fluid exhibits good thermal stabHity in the recommended temperature range and is inhibited against oxidation. The products of decomposition are soluble and viscosity increases as decomposition proceeds. The vapor pressure of the fluid is negligible and it is not feasible to recover the used fluid by distiHation. Also, because the degradation products are soluble in the fluid, it is not possible to remove them by filtration any spent fluid usuaHy must be burned as fuel or discarded. The fluid is soluble in water. [Pg.504]

Degradation of a herbicide by abiotic means may be divided into chemical and photochemical pathways. Herbicides are subject to a wide array of chemical hydrolysis reactions with sorption often playing a key role in the process. Chloro-j -triazines are readily degraded by hydrolysis (256). The degradation of many other herbicide classes has been reviewed (257,258). [Pg.48]


See other pages where The degraders is mentioned: [Pg.308]    [Pg.314]    [Pg.292]    [Pg.524]    [Pg.540]    [Pg.550]    [Pg.553]    [Pg.917]    [Pg.102]    [Pg.1135]    [Pg.25]    [Pg.29]    [Pg.31]    [Pg.31]    [Pg.34]    [Pg.35]    [Pg.35]    [Pg.39]    [Pg.39]    [Pg.240]    [Pg.436]    [Pg.140]    [Pg.555]    [Pg.418]    [Pg.427]    [Pg.432]    [Pg.19]    [Pg.254]    [Pg.330]    [Pg.48]    [Pg.52]   


SEARCH



A-1 The degradation products from ozonized solanesol

Abiotic degradation in the air compartment (atmosphere)

Abiotic degradation in the water phase

Ageing time (days) to reach the same degradation level versus sample thickness (mm)

Alternative Pathways for the Degradation of Benzoates and Related Compounds

Application to the Degradation of Specific Contaminants

Bacterial Degradation via Indole. The Tryptophanase Reaction

C Degradation and Elimination of the Organic Component

Chain Shortening The Ruff Degradation

Chemical and Electrochemical Processes that Accompany the Degradation of HTSC Materials

Combining the effects of polymer retention and degradation

Considering the Degradation of Controls over Time

Data Analysis of DSC Heat Effects for the Most Representative (Bio)-degradable Polymers

Degradation in the Environment

Degradation in the Proteasome

Degradation in the presence of oxygen

Degradation of Antibiotics in the Environment

Degradation of Estrogens and Other Reproductive Hormones in the Environment

Degradation of PPCPs in the Environment

Degradation of Plastics in the Environment

Degradation of tritium in the unsaturated zone

Degradation under the influence of light

Deoxyglycosuloses (3-Deoxyglycosones) and the Degradation of Carbohydrates

Deulofeu, The Acylated Nitriles of Aldonic Acids and Their Degradation

Deulofeu, Venancio, The Acylated Nitriles of Aldonic Acids and Their Degradation

ESR as a Tool for the Study of Polymer Degradation

Enzyme Processes the Evolution from Degradation to Synthesis. Biocatalysis in Aqueous and Non-conventional Media

Experimental principles in the investigation of polymer degradation kinetics

Factors Accelerating the Oxidative Degradation of Composites

Factors Controlling the Rate of Photochemical Degradation

Glycosuloses, 3-deoxy-, and the degradation of carbohydrates

Greenwood, C. T., The Thermal Degradation of Starch

Kinetic Degradation and Reaction Mechanisms in the Solid State of Natural Fibers

Kinetics of Polymer Degradation in the Solid State

On the Basis of Degradability

On the Basis of Degradation

Oxidation of Sulfur Atoms the MacDonald-Fischer Degradation

Peptide Sequencing The Edman Degradation

Physical, chemical and biological processes involved in the degradation of pesticides

Polymers of the degrading type

Process for the Alkaline Oxidative Degradation of Reducing Sugars

Processes for the Thermal Degradation of Plastic Wastes

Proteins The Edman degradation

Rearrangement with degradation of the carbon skeleton

Sequencing of Peptides The Edman Degradation

Significance in the Degradation of Carbohydrates

Structural Feature of Uronate—Sugar Conjugates, and the General Pathways for Degradation

Techniques for the Measurement of Enzyme Degradation

The Anaerobic Degradation of Benzoate

The Chemical Reactions of DNA Damage and Degradation

The Chemistry of Sequential Degradation

The Degradation of Long-Chain Molecules

The Edman Degradation and Automated Sequencing of Peptides

The Edman degradation

The Enzymic Degradation of Starch and Glycogen

The Genetics of Degradative Elements

The Hofmann Degradation

The Mechanism of Poly(styrene) Degradation

The Ozone Layer Its Photochemical Formation and Degradation Processes

The Polymer Degradation Process

The Primary Redox-Reactions Degradation of Organic Matter

The Stratospheric Ozone Layer Its Photochemical Formation and Degradation

The Strecker Degradation

The Zincins Collagen Fiber Processing and Degradation

The chemistry of degradation

The degradation environment

The degradation equation

The degradation of litter at sea

The future for degradable plastics

The role of degradable polymers in agricultural systems

The science and engineering of polymer composite degradation

Thermal Analysis in the Study of Polymer (Bio) -degradation

Thermal Degradation Mechanism of the Cured Epo-S Network

Tutorial Modeling the Degradation of s-Triazine Herbicides in Soil

Weak organic bases or acids that degrade the pH gradients across membranes

© 2024 chempedia.info