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Environment Extraction

Several groups have demonstrated the use of trNOESY experiments to determine the structure of peptides bound to their receptor. For example, Kisselev et al. determined the 3D solution structure of the transductin a-subunit bound to light-activated rhodopsin (51). They found that the peptide IKENLKDCGLF formed an a-helix terminated by an open reverse turn (Fig. 11), while in contrast the conformation of the peptide remained disordered when in contact with nonactivated rhodopsin. Their findings led to the development of derivatives of the peptide that maintained the binding conformation and had improved affinity (73). Importantly, in their studies they used rhodopsin in a membrane environment (extracted from bovine rods), emphasizing the capabilities of the method for the study of integral membrane receptor directed inhibitors in their natural environment. [Pg.103]

Amine Environment Extraction Detection Limit or Recovery s R.S.D. (%) Reference... [Pg.381]

Cadmium ranks close to lead and mercury as a metal of current toxicological concern. Cadmium is used in electroplating and galvanization, and in plastics, paint pigments (cadmium yellow), and nickel-cadmium batteries. Because <5% of the metal is recycled, environmental pollution is an important consideration. Coal and other fossil fuels contain cadmium, and their combustion releases the element into the environment. Extraction and processing of zinc and lead also lead to environmental contamination with cadmium. Workers in smelters and other metal-processing plants may be exposed to high concentrations of cadmium in the air however, for most of the population, food is the major source of cadmium. [Pg.1139]

Traditionally, chiral separations have been considered among the most difficult of all separations. Conventional separation techniques, such as distillation, Hquid—Hquid extraction, or even some forms of chromatography, are usually based on differences in analyte solubiUties or vapor pressures. However, in an achiral environment, enantiomers or optical isomers have identical physical and chemical properties. The general approach, then, is to create a "chiral environment" to achieve the desired chiral separation and requires chiral analyte—chiral selector interactions with more specificity than is obtainable with conventional techniques. [Pg.60]

Lubricating Oil Extraction. Aromatics are removed from lubricating oils to improve viscosity and chemical stabihty (see Lubrication and lubricants). The solvents used are furfural, phenol, and Hquid sulfur dioxide. The latter two solvents are undesirable owing to concerns over toxicity and the environment and most newer plants are adopting furfural processes (see Furan derivatives). A useful comparison of the various processes is available (219). [Pg.78]

Dissolved Minerals. The most significant source of minerals for sustainable recovery may be ocean waters which contain nearly all the known elements in some degree of solution. Production of dissolved minerals from seawater is limited to fresh water, magnesium, magnesium compounds (qv), salt, bromine, and heavy water, ie, deuterium oxide. Considerable development of techniques for recovery of copper, gold, and uranium by solution or bacterial methods has been carried out in several countries for appHcation onshore. These methods are expected to be fully transferable to the marine environment (5). The potential for extraction of dissolved materials from naturally enriched sources, such as hydrothermal vents, may be high. [Pg.288]

Responsible Care is the incentive sponsored by the Chemical Manufacturers Association (CMA). Any CMA company must embrace the philosophy of continuous improvements of health, safety, and environmental efforts accompanied by an open communication to the pubHc about products and their production. Thus the total impact of any product on the environment, from the extraction of raw materials, their beneftciation, transportation, production of final product, and disposal of the product at the end of its useful life, must be taken into consideration. [Pg.17]

Emissions During Exterior End Use. When flexible PVC is used in exterior appHcations plasticizer loss may occur due to a number of processes which include evaporation, microbial attack, hydrolysis, degradation, exudation, and extraction. It is not possible, due to this wide variety of contribution processes, to assess theoretically the rate of plasticizer loss by exposure outdoors. It is necessary, therefore, to carry out actual measurements over extended periods in real life situations. Litde suitable data have been pubHshed with the exception of some studies on roofing sheet (47). The data from roofing sheet has been used to estimate the plasticizer losses from all outdoor appHcations. This estimate may weU be too high because of the extrapolation involved. Much of this extracted plasticizer does not end up in the environment because considerable degradation takes place during the extraction process. [Pg.132]

Emissions During Disposal and Incineration. The increasing use of modem incinerators to dispose of domestic waste results in complete combustion of plasticizers to carbon dioxide and water. The preponderance of plasticizer going into landfiUs is as plasticized PVC. Once a landfiU has been capped anaerobic conditions prevail and it is biologically relatively inactive. Under these conditions the main route by which organic components are removed from the landfiU contents is by ingress of water, extraction, and subsequent loss of water from the site to the environment. [Pg.132]

A number of techniques have been developed for the trace analysis of siUcones in environmental samples. In these analyses, care must be taken to avoid contamination of the samples because of the ubiquitous presence of siUcones, particularly in a laboratory environment. Depending on the method of detection, interference from inorganic siUcate can also be problematic, hence nonsiUca-based vessels are often used in these deterrninations. SiUcones have been extracted from environmental samples with solvents such as hexane, diethyl ether, methyl isobutylketone, ethyl acetate, and tetrahydrofuran (THF)... [Pg.59]

Removing an analyte from a matrix using supercritical fluid extraction (SEE) requires knowledge about the solubiUty of the solute, the rate of transfer of the solute from the soHd to the solvent phase, and interaction of the solvent phase with the matrix (36). These factors collectively control the effectiveness of the SEE process, if not of the extraction process in general. The range of samples for which SEE has been appHed continues to broaden. Apphcations have been in the environment, food, and polymers (37). [Pg.242]

Direction of Extraction. The "normal" PT process involves the transfer of a reactive agent from a soHd or aqueous environment into a nonpolar organic solvent. But the exact opposite can be executed extraction from an organic phase into an aqueous phase, for example, for changing selectivities. This "inverse PTC" is done relatively rarely. [Pg.186]

Oil and Petrochemicals. There are a variety of uses for defoamers in oil recovery. They are used in some of the materials used in oil extraction, such as in drilling muds and cement lining, and also directly with the cmde oil itself. In its natural state cmde oil contains dissolved gases held by high reservoir pressure. When this Hve cmde oil is extracted and passed into the low pressure environment of a gas-oil separator, the dissolved gases are... [Pg.466]

Nuclear-physical methods ai e the basic ones in controlling environmental pollution which results from nucleai -power complexes and power plants work. Oil and gas production leads to the extraction of radio nuclides of natural origin in considerable amounts, which later spread from oil-slimes and water wastes in the neighborhoods of oil and gas producing entei prises. Similaidy, toxic and radioactive elements can pollute environment in case of mineral deposits extraction. [Pg.77]

The behavior of elements (toxicity, bioavailability, and distribution) in the environment depends strongly on their chemical forms and type of binding and cannot be reliably predicted on the basis of the total concentration. In order to assess the mobility and reactivity of heavy metal (HM) species in solid samples (soils and sediments), batch sequential extraction procedures are used. HM are fractionated into operationally defined forms under the action of selective leaching reagents. [Pg.459]


See other pages where Environment Extraction is mentioned: [Pg.804]    [Pg.103]    [Pg.263]    [Pg.117]    [Pg.514]    [Pg.36]    [Pg.804]    [Pg.103]    [Pg.263]    [Pg.117]    [Pg.514]    [Pg.36]    [Pg.64]    [Pg.45]    [Pg.176]    [Pg.93]    [Pg.474]    [Pg.202]    [Pg.132]    [Pg.132]    [Pg.177]    [Pg.226]    [Pg.234]    [Pg.475]    [Pg.303]    [Pg.564]    [Pg.494]    [Pg.367]    [Pg.14]    [Pg.478]    [Pg.520]    [Pg.50]    [Pg.241]    [Pg.353]    [Pg.11]    [Pg.194]    [Pg.1825]    [Pg.65]    [Pg.75]    [Pg.116]    [Pg.153]    [Pg.243]   
See also in sourсe #XX -- [ Pg.221 ]




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