Contamination, atmospheric

Obtaining meaningful Ar isotope analyses on basalts is analytically challenging, because contamination by atmospheric components is notorious. Potential sources of this contamination include seawater, altered wall rock, or air itself. Basalt glasses may show complicated variations within an individual glassy rim, with lower in both the 

The atmospheric contaminant in MORBs appears to be significantly less in 

It is commonly assumed that all Ar present in a MORE or OIB sample could be derived from air contamination. This is a reasonable assumption provided that the 

Ar/ Ar is 3000, as seems likely for mantle source regions. This assumption allows a 

Burnard et al. 2002). Sarda et al. (1999b) suggested that such a process should produce erratic results rather than a systematic trend. Whether the regional variation in Ar isotopes along ocean ridges carries information about variations in the upper mantle is still debated. Chlorine contents in suites of MORE glasses studied for Ar isotopes could potentially resolve this debate (e.g., Michael and Cornell 1998). 

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There are some theoretical complications discussed in Refs. 91 and 92. Experimental complications include adsorption of solvent or of film on the electrode [93,94] the effect may be used to detect atmospheric contaminants. The atmosphere around the electrode may be flushed with dry nitrogen to avoid condensation problems [87]. 

A brief review of the figures of merit (1) for thermal imaging (4) and gas detection is given to show the various trades-off required to image the thermal environment and detect atmospheric contamination. 

Chemical Gas Detection. Spectral identification of gases in industrial processing and atmospheric contamination is becoming an important tool for process control and monitoring of air quaUty. The present optical method uses the ftir (Fourier transform infrared) interference spectrometer having high resolution (<1 cm ) capabiUty and excellent sensitivity (few ppb) with the use of cooled MCT (mercury—cadmium—teUuride) (2) detectors. 

The salts rapidly hydroly2e to form NF and O2, and react with glass at temperatures above 85°C to form NF and SiF (21). The NF" 4 salts are stable in dry atmospheres to 200°C, but rapidly decompose above 300°C to yield NF, F2, and the corresponding Lewis acid. Therefore, these salts are solid sources of NF and F2, free of atmospheric contaminants and HF. 

E. H. Vemot and C. C. Haun,M< / Toxicology and Proposed Emergemy Exposure Eimits of Nitrogen Trifluoride, AMRL-TR-69-130-Paper No. 13 (AD 710062), Contract E33615-70-V-1046, Syste-Med Corp., Dayton, Ohio, Dec. 1969. Reprinted from the Proceedings of the 5th Annual Conference on Atmospheric Contamination in ConhnedSpaces, Sept. 16—18, 1969, AMRL-TR-69-130 (AD 709994), Dayton, Ohio, Dec. 1969, pp. 165—171. 

Titanium whites resist various atmospheric contaminants such as sulfur dioxide, carbon dioxide, and hydrogen sulfide. Under normal conditions they are not readily reduced, oxidi2ed, or attacked by weak inorganic and organic acids. Titanium dioxide dissolves slightly in bases, hydrofluoric acid, and hot sulfuric acid. Owing to its chemical inertness, titanium dioxide is a nontoxic, environmentally preferred white pigment. 

The amine ends also react with atmospheric contaminants, such as SO2 and oxides of nitrogen and ozone, under ambient storage conditions (50). This phenomenon is referred to as aging and results in reduced acid dye affinity. 

Golorfastness to Atmospheric Contaminants. The test colorfastness to nitrogen oxides, ISO 105-G01 is to assess the fastness of the color to nitrogen oxides that may be present ia hot air that has been passed over heated filaments or from the burning of gas, coal, etc. Specimens are exposed to nitrogen oxides ia a closed container along with standards until the standards have changed to a predetermined extent. 

It is essential to dry passivated surfaces promptly to protect them from moisture and atmospheric contamination. The drying may be carried out by blowing compressed air, which is easier and more economical, or by placing in the same oven as for the paint. Special care need be taken with hidden surfaces, such as in corners, bends and crevices, to ensure that there is no trapped moisture. 

If areas identified as likely to receive significant atmospheric contaminant concentrations include areas supporting edible biota, the biouptake of contaminants must be considered as a possible environmental fate pathway. Direct biouptake from the atmosphere is a potential fate mechanism for lipophilic contaminants. Biouptake from soil or water following transfer of contaminants to these media must also be considered as part of the screening assessments of these media. 

Rider and Amott were able to produce notable improvements in bond durability in comparison with simple abrasion pre-treatments. In some cases, the pretreatment improved joint durability to the level observed with the phosphoric acid anodizing process. The development of aluminum platelet structure in the outer film region combined with the hydrolytic stability of adhesive bonds made to the epoxy silane appear to be critical in developing the bond durability observed. XPS was particularly useful in determining the composition of fracture surfaces after failure as a function of boiling-water treatment time. A key feature of the treatment is that the adherend surface prepared in the boiling water be treated by the silane solution directly afterwards. Given the adherend is still wet before immersion in silane solution, the potential for atmospheric contamination is avoided. Rider and Amott have previously shown that such exposure is detrimental to bond durability. 

There are literally many thousands of chemical compounds that are potential air pollutants. It would be impossible to present all the pertinent data and information needed to evaluate each and every air pollution scenario. There are, however, a wealth of information and data bases that are available on the worldwide Web, along with a number of standard hard copy references to obtain information on the chemical and physical properties, and health risks of potential atmospheric contaminants. 

Selected chemical and physical properties, and data of common and potential atmospheric contaminants,... 

Table 1 is a compilation of chemical and physical properties data for selected atmospheric contaminants. This information is useful for evaluating pollution problems. The following are abbreviations used in the table. 

Chromium is the most effective alloying element for promoting resistance to oxidation. Table 3.10 gives temperatures at which steels can be used in air without excessive oxidation. In atmospheres contaminated with sulfur, lower maximum temperatures are necessary. 

Industrial environments expose individuals to a plethora of airborne chemical compounds in the form of vapors, aerosols, or biphasic mixtures of both. These atmospheric contaminants primarily interface with two body surfaces the respiratory tract and the skin. Between these two routes of systemic exposure to airborne chemicals (inhalation and transdermal absorption) the respiratory tract has the larger surface area and a much greater percentage of this surface exposed to the ambient environment. Or dinary work clothing generally restricts skin exposures to the arms, neck, and head, and special protective clothing ensembles further limit or totally eliminate skin exposures, but breathing exposes much of the airway to contaminants. 

Atmospheres contaminated with acid or halogen gases reduce these values. 

Chemical condensation This occurs when soluble corrosion products or atmospheric contaminants are present on the metal surface. When the humidity exceeds that in equilibrium with a saturated solution of the soluble species, a solution, initially saturated, is formed until equilibrium is established with the ambient humidity. The contaminants have already been detailed and of the corrosion products, obviously sulphates, chlorides and carbonates are most important in this context. However, in some cases there is a lack of reliable data on the vapour pressure exerted by saturated solutions of likely corrosion products. The useful data was summarised in Table 2.7. 

Tests by Clark for the Corrosion Sub-committee of the American Welding Society were carried out at severe marine and industrial sites. After four years, the greatest protection to steel was given by sprayed aluminium coatings combined with aluminium vinyl paint in the following environments id) sea air, ib) sea-water immersion, (c) alternate sea-water immersion and exposure to air (tidal conditions) and id) industrial atmospheres contaminated with sulphur compounds. 

The relatively impure crude Ca obtained from both thermal reduction and electrolytic sources (97-98%) is distilled to give a 99% pure product. Volatile impurities such as the alkali metals are removed in a predistillation mode at 800°C subsequent distillation of the bulk metal at 825-850°C under vacuum removes most of the involatile impurities, such as Al, Cl, Fe and Si. The N content is often not reduced because of atmospheric contamination after distillation. Unfortunately, these commercial methods have no effect on Mg, which is the major impurity (up to 1 wt%). Typical analytical data for Ca samples prepared by electrolysis, thermal reduction (using Al) and distillation are collated in Table 1. 

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