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Environmental Tobacco Smoke: Measuring Exposures and Assessing Health Effects (1986)
Commission on Life Sciences (CLS)

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. "7 Exposure-Dose Relationship for Environmental Tobacco Smoke." Environmental Tobacco Smoke: Measuring Exposures and Assessing Health Effects. Washington, DC: The National Academies Press, 1986.

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Environmental Tobacco Smoke: Measuring Exposures and Assessing Health Effects

different when the filters were removed. Particulate concentrations per milliliter ranged from 0.3×109 to 3.3×109, depending on whether the cigarettes were rated ultralow, low, or medium in tax content.

Hinds (1978) compared the particulate size distribution in cigarette smoke using an aerosol centrifuge and a cascade impactor. Although these devices are based on different physical principles, the MMAD values were comparable to those measured by McCusker et al. (1983), ranging from 0.37 to 0.52 µm. Variations depend primarily on the dilution of the smoke. Keith and Derrick (1960) used a specially modified centrifuge, termed a conifuge, to analyze cigarette smoke and reported MMAD and concentration values similar to Hinds (1978) and McCusker et al. (1983). Particulate analysis by a light-scattering photometer yielded a MMAD of 0.29 µm and particulate concentrations of 3×1010/ml.

Time and concentration can modify tobacco smoke. Cigarette smoke aerosols contain volatile components, and evaporation gradually reduces particle diameters. It is also true that when the particle concentrations are extremely high, like those encountered in mainstream smoke, the aerosol can agglomerate rapidly because nearby particles collide with each other and coalesce. If smoke is cooled (reducing the vapor pressure of volatile components) and diluted in room air (reducing the probability of particle collisions), the size of the particles will become more stable. Particle size may also change within the human respiratory tract. After air containing smoke is drawn into the mouth and upper respiratory tract, it becomes humidified. Smoke particles can grow in size because of their affinity for water, termed hygroscopicity (Hiller, 1982a).

BREATHING PATTERN

Particle size is a critical factor in determining the collection efficiency, but breathing pattern is also important For example, large slow tidal volumes will favor alveolar deposition, while high inspiratory flows will promote deposition at bifurcations in the airways. Breath-holding is also important. The greater the elapsed time before the next expiration, the higher the fraction of inspired particles deposited, since there is more time for particles to sediment or diffuse. Individual anatomic differences may influence the amount and distribution of deposited particles. The cross section of airways will influence the linear velocity of the inspired air.

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122
Front Matter (R1-R8)
Contents (R9-R14)
Executive Summary (1-12)
1 Introduction (13-22)
Part I: Physicochemical and Toxicological Studies of Environmental Tobacco Smoke (23-24)
2 The Physicochemical Nature of Sidestream Smoke and Environmental Tobacco Smoke (25-53)
3 In Vivo and In Vitro Assays to Assess the Health Effects of Environmental Tobacco Smoke (54-62)
Part II: Assessing Exosures to Environmental Tobacco Smoke (63-64)
4 Introduction (65-68)
5 Assessubg /Exposures to Environmental Tobacco Smoke in the External Environment (69-100)
6 Assessing Exposures to Enviromental Tobacco Smoke Using Questionnaires (101-119)
7 Exposure-Dose Relationship for Environmental Tobacco Smoke (120-132)
8 Assessing Exposures to Environmental Tobacco Smoke Using Biological Markers (133-160)
Part III: Health Effects Possibly Associated with Exposure to Environmental Tobacco Smoke by Nonsmokers (161-162)
9 Introduction (163-165)
10 Sensory Reactions To and Irritation Effects of Environmental Tobacco Smoke (166-181)
11 Effects of Exposure to Environmental Tobacco Smoke on Lung Function and Respiratory Symptoms (182-222)
12 Exposure to Environmental Tobacco Smoke and Lung Cancer (223-249)
13 Cancers Other than Lung Cancer (250-256)
14 Cardiovascular System (257-268)
15 Other Health Considerations in Children (269-276)
Appendixes (277-278)
Appendix A: Guidelines for Public and Occupational Chemical Exposures to Materials that are Also Found in Environmental Tobacco Smoke (279-283)
Appendix B: Method of Combining Data From Studies of Environmental Tobacco Smoke Exposure and Lung Cancer (284-288)
Appendix C: Adjusments to Epidemiologic Estimates of Excess Lung Cancer in Persons Exposed to Environmental Tobacco Smoke (289-293)
Appendix D: Risk Assessment- Exposure to Environmental Tobacco Smoke and Lung Cancer (294-338)