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Inhalation Toxicology
International Forum for Respiratory Research
Volume 21, 2009 - Issue 1
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Research Article

Comparison of Environmental Tobacco Smoke (ETS) Concentrations Generated by an Electrically Heated Cigarette Smoking System and a Conventional Cigarette

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Pages 62-77 | Received 28 Feb 2008, Accepted 15 May 2008, Published online: 01 Jan 2009

Figures & data

TABLE 1 Environmentally-controlled room setting and smoking conditionsa

FIG. 1 Layout of the environmentally controlled room, seating for occupants, and location of online and offline sampling equipment.

FIG. 1  Layout of the environmentally controlled room, seating for occupants, and location of online and offline sampling equipment.

TABLE 2 Indoor air constituents measured onlinea

TABLE 3 Indoor air constituents measured offlinea

TABLE 4 Mean concentrations of indoor air constituents (“office” with “high” IAQ conditions)

TABLE 5 Mean concentrations of indoor air constituents (“office” with “medium” IAQ conditions)

TABLE 6 Mean concentrations of indoor air constituents (“office” with “low” IAQ conditions)

TABLE 7 Mean concentrations of indoor air constituents (“hospitality” with “low” IAQ conditions)

FIG. 2 Percent difference between smoking CC (Simulation 5) and smoking CC (Simulation 1) in the concentration of indoor air constituents in the “office” with a “high” IAQ condition.

FIG. 2  Percent difference between smoking CC (Simulation 5) and smoking CC (Simulation 1) in the concentration of indoor air constituents in the “office” with a “high” IAQ condition.

FIG. 3 Percent difference between smoking CC (Simulation 8) and smoking CC (Simulation 4) in the concentration of indoor air constituents in the “hospitality” environment with a “low” IAQ condition.

FIG. 3  Percent difference between smoking CC (Simulation 8) and smoking CC (Simulation 4) in the concentration of indoor air constituents in the “hospitality” environment with a “low” IAQ condition.

FIG. 4 Ratio of indoor air constituent concentrations (background corrected) of particulate phase markers CC/EHCSS for all simulations. For the “office” with “high” IAQ conditions the background was greater than in the EHCSS smoking session (simulation 1); therefore, a ratio could not be calculated.

FIG. 4  Ratio of indoor air constituent concentrations (background corrected) of particulate phase markers CC/EHCSS for all simulations. For the “office” with “high” IAQ conditions the background was greater than in the EHCSS smoking session (simulation 1); therefore, a ratio could not be calculated.

FIG. 5 Cumulative distribution of indoor air nicotine concentrations in European restaurants. The curve to the right (•) is derived from literature (Schorp & Leyden, Citation2002). The curve to the left (▴) is the hypothetical nicotine distribution curve if smoking of CC was replaced by smoking of an EHCSS.

FIG. 5  Cumulative distribution of indoor air nicotine concentrations in European restaurants. The curve to the right (•) is derived from literature (Schorp & Leyden, Citation2002). The curve to the left (▴) is the hypothetical nicotine distribution curve if smoking of CC was replaced by smoking of an EHCSS.

FIG. 6 Cumulative distribution of indoor air particulate-phase ETS-RSP in restaurants in France, Japan, Korea, the United Kingdom, the United States, and Switzerland. The curve to the right (•) is derived from literature (Bohanon et al., Citation2003). The curve to the left (▴) is the hypothetical ETS-RSP curve if smoking of CC was replaced by smoking of an EHCSS.

FIG. 6  Cumulative distribution of indoor air particulate-phase ETS-RSP in restaurants in France, Japan, Korea, the United Kingdom, the United States, and Switzerland. The curve to the right (•) is derived from literature (Bohanon et al., Citation2003). The curve to the left (▴) is the hypothetical ETS-RSP curve if smoking of CC was replaced by smoking of an EHCSS.