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Such probes are somewhat fragile and cannot measure bubbles smaller than about 1 mm in diameter Light transmittance methods for interfacial area have been widely employed in gas liquid systems Sridhar and Potter (1978) describe one of the more successful versions The techniques are described in more detail in the liquid liquid section Chemical methods can be used to measure interfacial area, as described above (Section 4-75; Robinson and Wilke, 1974) Sampling methods are not suitable since it is impossible to withdraw a sample isokinetically Generally, the results from chemical and physical methods do not agree Chemical methods tend to have a bias toward the smaller bubbles of the distribution, whereas these may be missed by physical methods The method of dynamic gas disengagement (Sriram and Mann, 1977; Patel et al.

, 1989) to obtain an estimate of bubble size distribution is worthy of mention since it is convenient to use, sometimes even in real systems, especially for lower gas fractions The impeller is stopped and the trend in the level measured against time This trend indicates the bubble size distribution if terminal rise velocities are known and if coalescence is negligible..

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wildlife) Salmon egg mortality was high (~67%) for several years The tally of oil-induced wildlife casualties included 250,000 seabirds, 2800 sea otters, 260 bald eagles, 30 harbor seals, and 13 orca whales The US Fish and Wildlife Service estimated recovery times of 20 70 years for some wildlife populations Large animals (eg, Sitka black-tailed deer, brown bear) largely escaped injury Cleanup efforts The initial human, corporate, and governmental response to the spill was largely one of confusion Organized, coordinated oil recovery efforts were delayed Opportunities during the rst 3 days of calm weather were missed It was determined that responsibility for cleanup was Exxon s Cleanup crews were uncertain how to tackle a spill of that magnitude Technologies were unproven Booms (used to corral the oil) and skimmers (used to remove oil from the ocean surface) were applied, but the windstorm on day 3 interfered.

Up to this point, the Slider component examples have not had any authoring time artwork. That is, just an empty movie clip instance shows up on the stage at authoring time, and it s not until runtime that you can see the component. However, once live preview is enabled there will be an authoring time preview. That means it will be possible to set the dimensions of the component using the Property inspector or the Free Transform tool.

Chemical dispersants (that diminish the chance of coating the beaches but increase the toxicity of oil) were used to some degree Due to the windstorm, large masses of oil washed onto coastlines and the oil was redistributed by tides Attempts were made to clean oily shorelines with hot water at high pressure; subsequent evaluations of this approach were that it did more harm (to biota) than good Bioremediation Intrinsic bioremediation (also termed natural attenuation) is the evolutionarily proven suite of processes that occur due to innate forces of nature (physical, chemical, and biological processes) Many populations of microorganisms native to ocean water possess enzymatic capabilities that allow them to utilize petroleum as a carbon and energy source These naturally occurring marine microorganisms digest and grow on hydrocarbons Thus, microorganisms were the key players in destroying the oil released by the Exxon Valdez tanker.

FIGURE 17-4: A A button saved with transparency and Matte: None. The edge is not anti-aliased and shows signs of jaggedness. B Same button saved as a GIF with transparency and default matte color and then placed in an HTML page. Against a lighter background, it works fine. C However, placed on a darker background, the white fringing is clearly visible. D Same button saved with a matte color that matches the background color of the HTML page. The button blends perfectly into the background.

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