Lorillard
Fields
- Document File
- 89272449/89272877/Ciar - Board of Directors Minutes of
- Meeting
- 89272835/89272876/Ciar Board Meeting 931202
- Alias
- 89272869/89272871
- Type
- REPT, OTHER REPORT
- BIBL, BIBLIOGRAPHY
- Area
- SPEARS,ALEXANDER/OFFICE
- Litigation
- Stmn/Produced
- Site
- G65
- Master ID
- 89272836/2875
- 89272836 Bod Minutes for 931202 & 931203
- 89272837-2838 Center for Indoor Air Research Minutes of Meeting of the Bo Ard of Directors 931202 & 931203 Ciar Offices
- 89272839 Board of Directors Meeting 931202 & 931203
- 89272840-2855 Interim Report No. 1 Determination of Human Exposure to Env Ironmental Tobacco Smoke Initial Summary of City No. 1 Data
- 89272856
- 89272857
- 89272858-2859 Ciar Application - 'development of Inhalant Allergy and Ast Hma in Children'
- 89272860 940000 Ala / Ata International Conference 940000 Abstract F Orm Eosinophil Cationic Protein in Nasopharyngeal Secretion S From Wheezing Children
- 89272861 Bruce Ames
- 89272861A-2864 Can Organically Grown Tomatoes Give You Cancer? They Are Ab Out As Likely to As the Pesticides That the Epa So Righteou Sly Bans. Ban All Plants - They Pollute
- 89272865 Telecopy
- 89272867
- 89272867A-2868 Inhalation of Sidestream Smoke Accelerates Development of A Rteriosclerotic Plaques (Penn & Snyder, Circulation 88, 182 0 - 5)
Related Documents:
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A recent study' in Circulation contains technical errors and omissions in the inhalation
exposure methodology which prevent a useful analysis of the morphometry data
presented.
The authors state that "moderate levels were chosen so that exporure conditions would be
more relevant to those encountered in indoor environments by passive smokers." No
reference was given to target concentrations, or how these targets would relate to field
measurements. Instead, the reader finds that the mean values obtained in four identical
chambers (no reason is given as why four separate units were needed) for total suspended
particulates (TSP) were between 7.5 and 8.5 milligramsJm3. A recent review of TSP
concentrations in 951 smoking homes and 905 non-smoking homes2 indicated an average
of 0.049 milligrams/m3 for the former and 0.022 milligrams/m3 for the latter, for an overall
difference (which may be due to smoking) between the two of 0. 327 milligrams/m3- This
is more than 300 times less than the "moderate" concentrations used by Penn & Snyder.
Clearly, the statement made in the Discussion ("comparable to the dose that can be
expected under heavy smoking conditions at home") brings a new insight as to what
constitutes "heavy" smoking for these authors, especially as their cockerels were exposed
to this massive concentration continuously for 6 hours per day. The calculations made by
Penn & Snyder in the Discussion contain a number of assumptions and produce results
that are starkly at variance with actual field measurements.2 Hclcomb showed similarly
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small differences in TSP concentrations between smoking and non-smoking restaurants,
offices and transportation.2
In our laboratory3 we have shown no histopathological effects in the vascular systems of
rats exposed to aged and diluted sidestream smoke at the p-ossly exaggerated TSP
concentration of 10 mg/m3, 6 hours per day for 13 weeks (370 times the mean difference
noted above between smoking and non-smoking homes).
Cigarette mainstream smoke, sidestream smoke and environmental tobacco smoke (ETS)
are not synonymous.4 The aging process, a major factor in thc: formation of ETS from
sidestream smoke and exhaled mainstream smoke,5 is not pre:;ent in Penn & Snyder's
design. Exposure to fresh sidestream smoke, as generated by Penn & Snyder, is totally
inappropriate. It is then unclear as to how much of the aerosol presented to the cockerels
was actually inhaled or ingested by them: whole-body exposures are known to produce
large body burdens by the latter route when compared to the fornner.6
No reasons are given for the extensive modification of the smoke generator7 to remove
design features that were incorporated to produce standard Fuffs and smoke with a
constant composition. Together these unreferenced modificadons from our original
design7 would produce an extremely variable aerosol over the fi hours of exposure (no
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data presented); the non-standard methods preclude verification of the results by other
researchers.
References
1. Penn A, Snyder, CA. Inhalation of sidestream cigarette smoke accelerates
development of arteriosclerotic plaques. Circulation 1993; 88:1820-1825.
2. Holcomb, LC. Indoor air quality and environmental tobacco smoke: concentration
and exposure. Env. Intl 1993; 19:9-40.
3. Coggins, CRE, Ayres, PH, Mosberg, AT, Sagartz, JW, Haye:;, AW. Sub-chronic
inhalation study in rats, using aged and diluted sidestream smoke from a reference
cigarette. Inha1. Toxicol. 1993; 5: 77-96.
4. Rodgman, A. Environmental tobacco smoke. Regul. Toxico,'. Pharmacol. 1992; 16:
223-244.
5. Guerin, MR, Jenkins, RA, Tomkins, BA. 1992. The chemistry of environmental
tobacco smoke: composition and measurement. Lewis Publishers, Michigan.
6. Langard, S, Nordhagen, AL. Small animal inhalation chambers and the significance of
dust ingestion from the contaminated coat when exposing rat> to zinc chromate. Acta
Pharmacol. Toxicol. 1980; 46:43-46.
7. Ayres, PH, Mosberg, AT, Coggins, CRE. Modernization of nose-only smoking
machines for use in animal inhalation studies. J. Am. Coll. Toxicol. 1990; 9:441-446.
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