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Chlorine release

Chlorine Institute. Members of the Chlorine Institute are required to reaffirm their commitment to the Institute s safety pledge, including prevention of chlorine releases. The safety pledge also includes aimual safety audits, aimual emission and ha2ard evaluations of chlorine operations, periodic emergency-response test drills, and coordination with local officials for protection of the community (32) (see Alkali AND CHLORINE PRODUCTS). [Pg.93]

Chlorine monitors should be strategically located within the plant to detect chlorine releases or leaks on a continuous basis. Monitoring data should be analyzed and reviewed at regular intervals and compared with the operating standards so that any necessary corrective actions can be taken. [Pg.61]

Figure 1.4.3-1 from WASH-1400 compares the risk of 100 nuclear plants with other man-caused risks. This is a CCDF that gives the frequency per year that accidents will L-xcccd a value on the abscissa. For example, for 100 fatalities, the frequency that 100 nuclear power plants could do this is lE-4, air crashes to persons on the ground lE-2, chlorine releases 1. IE-2, dam failures 7E-2, explosions SF-2, fires 1. IE-1, air crashes (total) 5E-1, and total man-caused 9E-1,... [Pg.10]

Chlorine released to environment -potential personnel exposure and injuiy ... [Pg.96]

Interactions refers to any jobs, tasks, or operations carried out by people who could directly or indirectly cause the hazard to be released. Direct interactions with the plant might involve breaking open pipework, opening reactors, etc. Indirect interactions would include remote activation of valves from a control room, or the performance of maintenance on critical plant items. Errors that might occur during these interactions could allow the harm potential to be released. This could occur directly (for example, a worker could be overcome by a chlorine release if an incorrect valve line-up was made) or indirectly (for example, if a pump bearing in a critical cooling circuit was not lubricated, as in the example in Chapter 1). The procedure as described above... [Pg.209]

Primary and secondary amines and amides are first chlorinated at nitrogen by the chlorine released by the gradually decomposing calcium hypochlorite. Excess chlorine gas is then selectively reduced in the TLC layer by gaseous formaldehyde. The reactive chloramines produced in the chromatogram zones then oxidize iodide to iodine, which reacts with the starch to yield an intense blue iodine-starch inclusion complex. [Pg.45]

Chlorine-releasing preparations, e.g. hypochlorite lOOOOppm av. Cb, at least 30min at room temperature Spillage of HIV contaminated blood and body fluid Use fresh solution Deteriorates on storage and may be adversely affected by organic matter... [Pg.206]

Bronopol, wo-thiazolones, chlorine, chlorine-releasing agents, hypochlorites and iodine will oxidize or react with thiol groups. [Pg.259]

So we see the biggest disadvantage by using chlorine (and chlorine releasing products) and hypochlorites, is the minor efficiency at higher pH level and in presence of polluting nitrogenous products, and the fact is it is poisonous. [Pg.132]

Hydrothermal stability (HTS). The stability of the chlorinated resins was determined by a test procedure described in the experimental. The resin according to the standard test is treated with water in a sealed flask at 200 °C for 24 hours to determine the loss in acid functionality and additionally, the level of chlorine released into the aqueous phase. [Pg.342]

Chlorine flow to environment Internal relief valve sticks open Both internal pressure valves fail open and relief valve opens Operation Potential low chlorine flow to Tower Water Basin -see above Chlorine released to environment - potential personnel injury due to exposure Distinctive odor Pressure check valve located outdoors -unlikely to accumulate significant concentration III Action Item Consider venting relief valve above ground level... [Pg.70]

An appropriate emergency procedure would be to alert residents to stay indoors with the windows closed and ventilation off until the cloud passes. An effort by the plant to reduce the quantity of chlorine released is also indicated. [Pg.210]

A network of chlorine detectors is positioned at points close to potential leak sources (such as close to the chlorine vaporiser, compressor flanges and drum, cylinder and tanker filling connections) as well as along the perimeter of the site. Many chlorine detectors are interconnected with automatic plant responses and initiation of chlorine scrubbing where a chlorine release occurs within a contained building. [Pg.151]

To enable a practical building scrubber design, bunds will be insulated to minimise the rate of evaporation from a major liquid chlorine release (i.e. at least to a rate that can be treated by the scrubber). The bunds will slope to a sump to collect small liquid spills, minimising the surface area of the spill and hence minimising the chlorine evaporation rate. [Pg.152]

Rainwater leaked into a room where hundreds of large cardboard drums of solid swimming pool chemicals were stored. The resulting explosion and fire set off a sprinkler system, soaking the remaining drums and spreading the fire. Explosions, fire, and chlorine releases lasted three days. Over 25,000 people were evacuated and 275 people went to the hospital with skin burns and respiratory problems. [Pg.18]

Realistic Dispersion Modeling of Chlorine Release Incident. A1 Waller... [Pg.431]

Figure 5.5 Ozonation of bezafibrate in water at pH 6 and 25°C. The represents bezafibrate concentration, O represents the concentration of chlorine released from that degradation, whereas A represents the concentration of total organic carbon (TOC) removed during the ozonation process. (Adapted from Dantas et al., 2007.)... Figure 5.5 Ozonation of bezafibrate in water at pH 6 and 25°C. The represents bezafibrate concentration, O represents the concentration of chlorine released from that degradation, whereas A represents the concentration of total organic carbon (TOC) removed during the ozonation process. (Adapted from Dantas et al., 2007.)...
Alternative chlorine-releasing compounds include chlorine dioxide and chloramine T. These agents retain chlorine longer and have a prolonged bactericidal action. [Pg.1096]

Chlorinated isocyanurates are also available in tablet (puck) form, either as fast or slow chlorine release. Powdered oxidizers are usually restricted to calcium or lithium hypochlorite, some isocyanurates, and also some hydantoin (BCDMH, etc.) products. [Pg.182]

The Chlorine Institute developed and released Pamphlet 86, Recommendations to Chlor-Alkali Manufacturing Facilities for the Prevention of Chlorine Releases, [16] in October 1990. This 15-page pamphlet acknowledges the ORC report Recommendations for Process Hazards Management of Substances with Catastrophic Potential was one of the primary documents used to develop it. [Pg.280]

Only a small percentage of the chlorine released by photolysis of CFCs is present in the active forms as Cl or CIO, however. Most of it is bound up in reservoir compounds such as hydrogen chloride and chlorine nitrate, formed respectively by hydrogen abstraction (equation 10) from methane and addition (equation 11) to nitrogen dioxide. Slow transport of these reservoir species across the tropopause, followed by dissolution in tropospheric water and subsequent rain-out, provide sink processes for stratospheric chlorine. [Pg.1562]

Gudiksen, R et al., Emergency Response Planning for Potential Accidental Liquid Chlorine Releases, U.S. Department of Energy, Washington, DC, 1986. [Pg.176]

Description The liquid phase reaction of ethylene and chlorine releases approximately 220 kJ/mol of produced EDC. [Pg.58]


See other pages where Chlorine release is mentioned: [Pg.482]    [Pg.83]    [Pg.83]    [Pg.86]    [Pg.38]    [Pg.135]    [Pg.876]    [Pg.51]    [Pg.51]    [Pg.78]    [Pg.152]    [Pg.33]    [Pg.730]    [Pg.293]    [Pg.185]    [Pg.163]    [Pg.310]    [Pg.129]    [Pg.185]    [Pg.59]   
See also in sourсe #XX -- [ Pg.129 , Pg.194 , Pg.204 ]




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