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Contaminant levels

In the 1970 s, heavy fuel came mainly from atmospheric distillation residue. Nowadays a very large proportion of this product is vacuum distilled and the distillate obtained is fed to conversion units such as catalytic cracking, visbreaking and cokers. These produce lighter products —gas and gasoline— but also very heavy components, that are viscous and have high contaminant levels, that are subsequently incorporated in the fuels. [Pg.241]

Plutonium (Pu) is an artificial element of atomic number 94 that has its main radioactive isotopes at 2 °Pu and Pu. The major sources of this element arise from the manufacture and detonation of nuclear weapons and from nuclear reactors. The fallout from detonations and discharges of nuclear waste are the major sources of plutonium contamination of the environment, where it is trapped in soils and plant or animal life. Since the contamination levels are generally very low, a sensitive technique is needed to estimate its concentration. However, not only the total amount can be estimated. Measurement of the isotope ratio provides information about its likely... [Pg.369]

Special safety constraints apply to equipment selection, design, and operation in nuclear reprocessing (269). Equipment should be reHable and capable of remote control and operation for long periods with minimal maintenance. Pulsed columns and remotely operated mixer—settlers are commonly used (270). The control of criticaHty and extensive monitoring of contamination levels must be included in the process design. [Pg.80]

Fig. 14. Effects of iron (—), nickel (-), and copper (...) contaminant levels on the saltwater corrosion performance of magnesium AZ91 alloy containing... Fig. 14. Effects of iron (—), nickel (-), and copper (...) contaminant levels on the saltwater corrosion performance of magnesium AZ91 alloy containing...
In the United States, the Compressed Gas Association Hsts nine grades of nitrogen, differentiated by oxygen content, dew point, total hydrocarbon content, and other contaminant levels (25). These grades, more often specified in government than commercial contracts, are shown in Table 3. [Pg.78]

LLDPE by itself does not present any health-related hazard on account of its chemical inertness and low toxicity. Consequently, film, containers, and container Hds made from LLDPE are used on a large scale in food and dmg packaging. Some LLDPE grades produced with unsupported metallocene catalysts have an especially high purity due to high catalyst productivity and a low contamination level of resins with catalyst residue. FDA approved the use of film manufactured from these resins for food contact and for various medical appHcations (80). However, if LLDPE articles contain fillers, processing aids, or colorants, thek health factors must then be judged separately. [Pg.404]

Minimum contained oxygen and maximum contaminant levels where specified for the several grades of oxygen. Contaminants given in volumes per million (vpm). Low purity oxygen (93%) has not been included. [Pg.479]

Basic oxides of metals such as Co, Mn, Fe, and Cu catalyze the decomposition of chlorate by lowering the decomposition temperature. Consequendy, less fuel is needed and the reaction continues at a lower temperature. Cobalt metal, which forms the basic oxide in situ, lowers the decomposition of pure sodium chlorate from 478 to 280°C while serving as fuel (6,7). Composition of a cobalt-fueled system, compared with an iron-fueled system, is 90 wt % NaClO, 4 wt % Co, and 6 wt % glass fiber vs 86% NaClO, 4% Fe, 6% glass fiber, and 4% BaO. Initiation of the former is at 270°C, compared to 370°C for the iron-fueled candle. Cobalt hydroxide produces a more pronounced lowering of the decomposition temperature than the metal alone, although the water produced by decomposition of the hydroxide to form the oxide is thought to increase chlorine contaminate levels. Alkaline earths and transition-metal ferrates also have catalytic activity and improve chlorine retention (8). [Pg.485]

Table 2. Summary of Typical Vehicle Used Oil Contaminant Levels ... Table 2. Summary of Typical Vehicle Used Oil Contaminant Levels ...
The U.S. Environmental Protection Agency, under the Safe Drinking Water Act, set the secondary contaminant level for silver ia drinking water at 0.1 mg/L (20). Secondary contaminants are not considered to be hazardous to health and thus the limits are not federally enforceable. [Pg.85]

The goal of filtration in the modem municipal treatment plant is a maximum of 0.1 ntu (nephelometric turbidity unit), which ensures a sparkling, clear water (8). Freedom from disease organisms is associated with freedom from turbidity, and complete freedom from taste and odor requites no less than such clarity. The National Interim Primary Drinking Water Regulations (NIPDWR) requite that the maximum contaminant level for turbidity at the point of entry into the distribution system be 1.0 ntu unless it can be shown that levels up to 5 ntu do not interfere with disinfection, interfere with the maintenance of a chlorine residual in the distribution system, nor interfere with bacteriological analyses. [Pg.276]

Color can be removed effectively and economically with either alum or ferric sulfate at pH values of 5—6 and 3—4, respectively. The reaction is stoichiometric and is a specific reaction of the coagulant with the color to form an insoluble compound (17). The dosage required may be as high as 100—150 mg/L (380—570 mg/gal). Raw-water colors may be as high as 450—500 units on the APHA color scale. The secondary MCL (maximum contaminant level) for color in the finished water is 15 units, although most municipal treatment plants produce water that seldom exceeds 5 units. [Pg.278]

Drinking water suppHed to carbonated soft drink manufacturing faciUties from private or municipal sources must comply with all regulatory requirements. Treated water must meet all U.S. Environmental Protection Agency primary maximum contaminant levels and may also be subject to additional state requirements. Treated water is routinely analyzed for taste, odor, appearance, chlorine, alkalinity, iron, pH, total dissolved soHds, hardness, and microbiological contamination. [Pg.15]

The procedure of simultaneous extracting-spectrophotometric determination of nitrophenols in wastewater is proposed on the example of the analysis of mixtures of mono-, di-, and trinitrophenols. The procedure consists of extraction concentrating in an acid medium, and sequential back-extractions under various pH. Such procedures give possibility for isolation o-, m-, p-nitrophenols, a-, P-, y-dinitrophenols and trinitrophenol in separate groups. Simultaneous determination is carried out by summary light-absorption of nitrophenol-ions. The error of determination concentrations on maximum contaminant level in natural waters doesn t exceed 10%. The peculiarities of application of the sequential extractions under fixed pH were studied on the example of mixture of simplest phenols (phenol, o-, m-, />-cresols). The procedure of their determination is based on the extraction to carbon tetrachloride, subsequent back-extraction and spectrophotometric measurement of interaction products with diazo-p-nitroaniline. [Pg.126]

Tap water has been analyzed by the method proposed. Total content of chlorine and chloramines in water makes up. 0.12 0.02 mg/L which is less than maximum contaminant level. Standai d deviation does not exceed 0.15. [Pg.241]

Actually, the successful use of cationic surfactants (cSurf), as flotation reagents, frothers, metal corrosion inhibitors, pharmaceutical products, cosmetic materials, stimulates considerable increase in their production and as a result increases their content in natural water. As cationic surfactants are toxic pollutants in natural water and their maximum contaminant level (MCL) of natural water is 0.15-4.0 mg/dm, it is necessary to use methods for which provide rapid and reliable determination with sensitivity equal to at least 0.1 of MCL. Practically most sensitive methods of cationic surfactant determination include the preconcentration by extraction or sorption. Analytical methods without using organic solvents are more preferable due to their ecological safety. [Pg.316]

Control of metalloid content in natural objects, foodstuff and pharmaceuticals is an important task for modern analytical chemistry. Determination of elements such as Arsenic is necessary for evaluation of object toxicity, since their content in environment may exceed MCL (maximum contaminant level), posing hazard to human health. Elements such as Selenium in definite doses are healthy, but in greater quantities they produce toxic effect. [Pg.397]

The gas temperature of the Ar plasma in the range of 600 100 K effects temperatures of water or LN2 cooled samples of 350 30 or 200 30 K, respectively. In addition, C, N, and O species are desorbed from the chamber walls and introduced samples, effecting a plasma contamination level in the 0.01-0.1% range. [Pg.126]

Quantifying the effect of surface roughness or morphology is difficult, however. Surface preparations that provide different degrees of surface roughness also usually produce surfaces that have different oxide thicknesses and mechanical properties, different compositions, or different contaminant levels. The problem of separation of these variables was circumvented in a recent study [52] by using a modified microtome as a micro milling machine to produce repeatable, well-characterized micron-sized patterns on clad 2024-T3 aluminum adherends. Fig. 2 shows the sawtooth profile created by this process. [Pg.446]

Fig. 2. Peel strength of NBR rubber as a function of HD2 grease contamination level on grit-blasted steel using the. solvent-borne Chcmlock 205/23.3 primer/adhesive and the aqueotis Chemlock 805/855. Adapted from Ref. 12. ... Fig. 2. Peel strength of NBR rubber as a function of HD2 grease contamination level on grit-blasted steel using the. solvent-borne Chcmlock 205/23.3 primer/adhesive and the aqueotis Chemlock 805/855. Adapted from Ref. 12. ...
Fig. 35. OSEE response and peel strength of NBR rubber on steel for HD2 grease (data from Ref. [162]) and silicone release agent contamination (data from R.L. Cause, unpublished work and Ref. [10]). The HD2 grease is slightly photoemitting so the OSEE signal does not decrease to zero at high contamination levels. Fig. 35. OSEE response and peel strength of NBR rubber on steel for HD2 grease (data from Ref. [162]) and silicone release agent contamination (data from R.L. Cause, unpublished work and Ref. [10]). The HD2 grease is slightly photoemitting so the OSEE signal does not decrease to zero at high contamination levels.

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See also in sourсe #XX -- [ Pg.210 ]




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