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Containment levels

Most natural gas is substantially free of sulfur compounds the terms. sweet and. sour are used to denote the absence or presence of HgS. Some wells, however, dehver gas containing levels of hydrogen sulfide and other sulfur compounds (e.g., thio enes, mercaptans, and organic sulfides) that must be removed before transfer to commercial pipehnes. Pipehne-company contracts typically specify maximum allowable Emits of impurities HgS and tot sulfur compounds seldom exceed 0.023 and 0.46 g/m (1.0 and 20.0 gr/100 std fF),... [Pg.2366]

Origin of Ions in Nonhydrocarbon Flames. Of flames which do not contain hydrocarbons, only cyanogen/oxygen flames have so far been found to contain levels of natural ionization comparable with those... [Pg.311]

Sensitivity of bivalves to the saxitoxins appears to be more general than has been recognized. Shellfish that contain levels of the saxitoxins that make them dangerous for human consumption can seldom be distinguished visibly from those that are safe. Nevertheless, detailed study has shown (64 R. Mann and S. Hall, unpublished results) that Alexandrium cells have significant effects on bivalve responses, presumably due to the contained saxitoxins. [Pg.42]

There is much concern for the safety of personnel handling articles contaminated with pathogenic viruses such as hepatitis B virus (HB V) and human immunodeficiency vims (HIV) which causes acquired immune deficiency syndrome (AIDS). Some agents have been recommended for disinfection of HBV and HIV depending on the circumstances and level of contamination these are hsted in Table 10.4. Disinfectants must be able to treat rapidly and reliably accidental spills of blood, body fluids or secretions from HIV infected patients. Such spills may contain levels of HIV as high as lO" infectious units/ml. Recent evidence Irom the Medical Devices Agency evaluation of disinfectants against HIV indicated that few chemicals could destroy the vims in a... [Pg.206]

Examples of these improvements are the packaging of dimethylamine products in plastic-lined containers and the elimination of sodium nitrite in the final product. This change in packaging and formulating makes it hi ly probable that N-dimethylnitrosamine will not form during storage of the product. Another example of the improvement of products is that Treflan products today contain less than 1 ppm of N-dipropylnitrosamine (T.) whereas some of the older products contained levels as high as 115-150 ppm several years ago (i, ). [Pg.387]

Many reagent grade solvents contain levels of impurities that make them unsuitable for long term use in hplc. Sometimes the impurities are added deliberately as antioxidants, stabilisers, or for denaturing. Wherever possible, hplc grade solvents should be used to prepare mobile phases, or alternatively the solvents should be adequately purified before use. [Pg.191]

In a worst-case scenario, the run-off from agricultural land may contain levels of fertilizers or animal waste that might seriously contaminate the water supply. [Pg.240]

The irrigation systems were constructed in this valley in 1930-1960s. It was found afterward that irrigation drainage water from parts of the San Joaquin Valley contains levels of selenium and other trace elements that have been implicated in bird deformations in the Kesterson Reservoir. Depending on location and season, the drainage water contains 100-1400 pg/L Se, predominantly as selenate (SeO 2, Se-IV), the most soluble form, whereas the California State Water Resources Control Board has recommended an interim maximum mean monthly selenium concentration of 2-5 pg/L in receiving waters and wetlands. [Pg.261]

Once an assessment on a particular impurity has been made all process-related compounds will be examined to confirm that the impurity of interest is indeed an unknown. An easy way of doing this is to compare the retention times of known process-related compounds to that in question. If this analysis confirms that the compound is an unknown, the next step would be to obtain an LC-MS on the compound. Mass spectrometry provides structural information which aids in determining structure. In some cases, mass spectrometry will be enough to identify the compound. In other cases, more complicated methods like LC-NMR are needed or the impurity will need to be isolated in order to obtain additional information. Compounds that are not purified often contain high levels of by-products and can be used for this purpose. Alternatively, mother liquors from crystallizations also contain levels of by-products. Other ways of obtaining larger quantities of impurities include flash chromatography which is typically used for normal phase separations or preparative HPLC which is more common for reversed phase methods. Once a suitable quantity of the compound in question has been obtained a full characterization can be carried out to identify it. [Pg.289]

In the edible parts of crabs, lobsters, prawns, and shrimps, the content of BaP is either not detectable or does not exceed a few ng per g. However, lobsters taken from a commercial storage facility made of creosoted timber have been found to contain levels of BaP up to 280 and 2300 ng per g in the tail meat and in the digestive gland, respectively (Dunn and Fee, 1979). In the meat of fish from unpolluted seas, BaP is generally below the detectable level (Rainio et al., 1986). [Pg.305]

To deal with this problem the EPA invested in the development and validation of a pharmacokinetic model that is capable of relating intake of lead to blood level. The model also allows the risk assessor to develop blood level estimates that integrate all sources of exposure. Using this model, it becomes possible to determine whether a specific source, such as our suspect water supply, is leading to exposures in excess of the target for all sources combined (this assumes that other sources do not contain levels of lead greater than normal, background... [Pg.254]

Pesticide residues were analyzed in 183 milk samples from 165 Finnish women. Heptachlor was found in 12% of the samples heptachlor epoxide was found in 6.6%. Five percent of the samples contained levels of heptachlor epoxide in excess of 0.0005 mg/kg body weight, an acceptable daily intake (Mussalo-Rauhamaa et al. 1988). Fifteen milk and fat specimens from residents of Grand Forks, British Columbia, and 16 milk and 17 fat specimens from residents of Prince George, British Columbia, were analyzed for pesticide residues. Heptachlor epoxide was found in one milk sample and nine fat samples in the Grand Forks group (>0.004 ppm) and in no milk samples and two fat samples in the Prince George group (>0.004 ppm) (Larsen et al. 1971). The residue was not detectable at levels lower than 0.004 ppm because of limitations of the analytical methods and faulty techniques. It is possible that the potential exposure of the residents to heptachlor may also have occurred via food contaminated with heptachlor. [Pg.62]

Wilson and McGregor [2S] concluded that it is appropriate to use robotics for grinding materials for geological samples. Studies deahng with cross contamination revealed that even samples containing levels of Ph, Zn or Cr above 1% did not pose a problem, provided that 2S g of sand is used to clean the system prior to the next sample analysis. [Pg.176]

Another way to trap sings is to place shallow containers filled with beer in the soil with the top of the container level with the soil snrface. Sings will be attracted to the beer and drown. A solntion of 1 pound of sugar and 1 teaspoon of yeast in a gallon of water fermented two or more days works well. This makes nse of both the trap and the bait concept. [Pg.12]

The interaction parameters z, z, and Ji are defined in the usual way, and t) = /S"//8, where /3" is the resonance integral between nearest neighbors in the adsorbed layer. If rj = 1, the eigenvalue condition. Equation (19), is the same as for the one-dimensional model. The only change is that the discrete localized states (CP and 91) of the one-dimensional model now appear as bands of surface states (CP or 91 bands) associated with the adsorbed layer and the crystal surface. At most, two such bands may be formed, and each band contains levels. This is the number of atoms in the adsorbed layer. Depending on the values of the interaction parameters z and z, these bands may or may not overlap the normal band of crystal states. All this was to be expected, and Fig. 2 gives the occurrence of (P and 91 surface bands when = 1. It is when tj 7 1 (and this will be the usual situation) that a new feature arises. In this case, the second term in the second bracket in Equation (19) does not vanish, and the eigenvalue condition is not the same as in the one-dimensional model. In fact we have z - - 2(1 — jj )(cos 02 - - cos 03) in place of z, and this varies between z - - 4(1 — ij ) and z — 4(1 — tj ). We can still use Fig. 2 if we remember that z varies between these two limits. Then if, for example, this variation... [Pg.11]

One of the four plants presently treats and reuses 75% of its waste stream as vent scrubber washwater. A second plant incinerates formulating/packaging process waste and discharges incinerator blowdown that contains levels of pesticides measured as not detected. [Pg.541]

Hexachlorobutadiene adsorbs to sediments in contaminated water. Sediments from the Niagara River were found to contain 2.9-11 ig/kg (Oliver and Charlton 1984). Sediments from the Great Lakes were reported to contains levels of hexachlorobutadiene typically ranging from 0.08 to 120 i g/kg (Fox et al. 1983 Oliver and Bourbonniere 1985 Oliver and Charlton 1984). Data regarding the levels of hexachlorobutadiene in soils were not located. Hexachlorobutadiene was not detectable in any of 196 sediment samples reported on the STORE database (Staples et al. 1985). The median detection limit was <500 ppb. [Pg.82]

Studies of the inhalation toxicity of cresols have not been adequately detailed. The exposures involved mixtures of vapors and aerosols that were not characterized sufficiently to estimate exposure levels reliably. Furthermore, methods for evaluating the toxicological end points were not adequately described. Therefore, no LSE table or figure containing levels of significant exposure was constructed for this route. Nevertheless, certain general conclusions can be drawn from the reports regarding the toxic potential of inhaled cresols. These are discussed below. [Pg.14]

Contains levels of nickel which vary widely in content. Commercial products include Invar and Permalloy. These alloys are used in certain high-level technology applications such as transoceanic cabling and other applications whereby machining tolerances are exact, such as clocks and variable condensers. [Pg.228]

A humorous example illustrates our inconsistent approach to exposure. The Detroit News analyzed the soil under a development proposed by Mayor Coleman Young and reported that it contained certain chemicals that exceeded EPA recommended levels. The mayor retaliated by having a copy of the newspaper analyzed and revealed that it contained levels of aluminum, copper, zinc, and manganese that exceeded EPA limits for solid waste and soil (Associated Press 1992). [Pg.78]

In tissues of sheep treated orally with a single dose of 5 mg/kg bw, residue levels of closantel were 0.06-0.09 ppm in fat and muscle and up to 0.47 ppm in kidney and liver at 56 day withdrawal at 84 days, residues could not be detected in fat and muscle, whereas liver and kidney contained levels as low as... [Pg.137]

Plants are known to produce toxicants and antinutrilional factors, such as protease inhibitors, hemolytic agents, and alkaloids, which often protect the plant against pests and disease. Many of these toxicants are present in today s crops ai levels that do not cause acute toxicity or do not affect humans or animals when the food is properly prepared. New plant varieties should not contain levels of such toxicants that are above the range that exists in today s crops. [Pg.709]

The Neutralization Module accepts the ton container contents from the TCC module and destroys the agent batchwise through hydrolysis with water followed by caustic addition. The Neutralization Module consists of three units, each located inside a Containment Level A toxic cubicle. There are two HD Reactors and one TCC Effluent Tank in each of the three neutralization units. In each neutralization unit, drained agent held in the Agent Holding Tank is processed in batch neutralization reactions. The rinse and spray water from the TCC Module and spent decontamination solution are stored in the TCC Effluent Tank and process in separate batch reactions. In the neutralization reaction HD reacts with water to yield the principal hydrolysis products of thiodiglycol and hydrochloric acid. After the hydrolysis is complete and sample analysis results confirm the destruction of HD, 18 percent sodium hydroxide is added to the reactor to raise pH in order to increase the hydrolysate biodegradability. The hydrolysate is then pumped to the Hydrolysate Tank in the VOC Treatment Module. [Pg.47]

Safe Drinking Water Act. (1974, 1986, 1996). Specifically applied to water supplied for humans consumption, this act requires the EPA to set maximum levels for contaminants in water delivered to users of public water systems. Two criteria are established for a particular contaminant the maximum containment level goal (MCGL) and the maximum contaminant level (MCL). The former, the MCLG, is the level at which no... [Pg.412]

Cadmium is present at low concentrations in most foods, with those that are consumed in larger quantities making the largest contribution to the population dietary exposure. Although the concentrations of cadmium in food in the UK are generally low, some foods of minor dietary importance such as shellfish or kidney often contain levels in excess of 0.5 mg/kg. Plant-based foods rarely contain more than 0.2 mg/kg on a fresh weight basis, although some root crops such as carrots and parsnip, and some leafy crops, such as spinach and lettuce, tend to contain more cadmium than other plant foods. This is also true of cereals, which indicates that plants tend to take up cadmium from the soil, unlike lead. [Pg.153]


See other pages where Containment levels is mentioned: [Pg.418]    [Pg.278]    [Pg.1040]    [Pg.51]    [Pg.411]    [Pg.49]    [Pg.217]    [Pg.356]    [Pg.27]    [Pg.149]    [Pg.16]    [Pg.360]    [Pg.6]    [Pg.662]    [Pg.411]    [Pg.39]    [Pg.345]    [Pg.298]    [Pg.256]    [Pg.258]    [Pg.96]    [Pg.153]   
See also in sourсe #XX -- [ Pg.424 ]

See also in sourсe #XX -- [ Pg.73 , Pg.216 ]




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Containment biosafety levels

Drinking water maximum containment levels

Maximum containment level

Maximum containment level goal

Secondary maximum containment levels

Shallow Level Complexes Containing Hydrogen

Trace Anions in Samples Containing High Levels of Chloride or Sulfate

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