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<br />276 <br /> <br />September, 1970 <br /> <br />IR3 <br /> <br />Type of driving <br /> <br />Idle Deceleration Cruise Acceleration <br /> <br />Percent volume CO <br />Parts per million <br />Muffler temperature, 0 F <br /> <br />5.2 <br />52,000 <br />500 <br /> <br />5.2 <br />52,000 <br />500 <br /> <br />0.8 <br />8,000 <br />700 <br /> <br />4.2 <br />42,000 <br />900 <br /> <br />Depending upon the operating mode, dilution factors varying from 20 to 100 are <br />required to reduce the concentration of CO, as emitted from the exhaust pipe, <br />to levels acceptable for periods up to an hour. <br />The operating mode under which an individual is most likely to encounter <br />high concentrations is, of course, idle. Under idle conditions in an ambient <br />air temperature of 7(1' F, the concentration of CO in the exhaust gases at a <br />point where the temperature is 15(1' F is slightly above 12,000 ppm. In an <br />ambient air temperature of 00 F, the concentration at 15(1' F is over 22,000 <br />ppm. As noted earlier, concentrations of 4,000 ppm or higher are fatal in less <br />than an hour. <br />Lead halides are present in automobile exhaust. It is used in gasoline in the <br />form of tetraethyl or tetramethyl lead. The amount per gal of gasoline varies <br />from 2 g to 4 g, depending on the brand and location where it is sold. Using an <br />average value of 3 g of lead per gal of gasoline and considering a speed of 30 <br />mph at a consumption rate of 1 gal per 15 miles, 6 g of lead, primarily chlo- <br />rides and bromides (4) are released to the atmosphere per hr. Variation of <br />cruising speed or gasoline consumption rate will alter this value in direct <br />proportion. <br />The toxic hazard of lead is severe if inhaled, especially if it is in soluble <br />form and the particle size is between 0.3/-l-2.0/-l. With these characteristics <br />it is retained and readily absorbed by the lungs (11). Much of the lead re- <br />leased to the atmosphere as part of automobile exhaust is in this form. It has <br />been estimated that the principal source of atmospheric lead as an air pollu- <br />tant in urban areas is from the combustion of leaded gasoline (7). About 60 % <br />of the atmospheric lead in the Los Angeles area has been shown to be less than <br />0,45/-l and 90 % is less than 1.6/-l (9). Because of the cumulative factor of lead <br />absorption, the potential hazard of lead poisoning is high, its effects well known <br />(5). <br /> <br />COMPARISON SUMMARY <br /> <br />A direct comparison of a silver-iodide generator and an automobile, both <br />operating in an ambient air temperature of 7(1' F, with their effluents diluted <br />to 1500 F, is as follows: <br /> <br />Silver Iodide Generator Effluent. <br />1. Iodine vapor; concentration 0.47 mg per m3 of air. This is less than <br />one-half the ACGIH threshold level: no hazard. <br />2. Carbon monoxide; concentration 150 ppm. This concentration canbe ac- <br />cepted for at least 1 hr without effect: no hazard. <br />3. Silver iodide and complexes. Absorption is unlikely due to the relative <br />insolubility. If absorbed, no constitutional symptoms will result: no hazard. <br /> <br />., <br />I <br />