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PUBLIC HEALTH BRIEFS

cause of the incident, container structure and failure, and deaths and injuries   appear in more than one source, they are checked for consistency; otherwise,
resulting from the cargo. DOT attempts to validate death and injury data.         data are not validated.
Specifically excluded from reporting requirements are releases of small
quantities of certain consumer commodities, and releases from motor carrier
firms doing solely intrastate business and from certain water transporters.
Automobiles striking storage tanks and certain transportation-related spills at
fixed facilities are also excluded.                                                                             REFERENCES
     The Acute Hazardous Events (AHE) data base was begun in 1985 and uses        1. SAS Institute Inc: SAS User's Guide: Basics. Version 5 Ed. Cary, NC: SAS
the NRC as its main source of data. However, data are also included from             Institute Inc, 1985.
selected state governments, the Environmental Protection Agency (EPA)             2. US Congress, Office of Technology Assessment: Transportation of haz-
Region 7, some newspapers and wire services, and other sources. Information          ardous materials. Washington, DC: Govt Printing Office, 1986; 66-86.
collected includes cause of event, activity taking place during the event, and    3. Shaw GN, Windham GC, Leonard A, Neutra RN: Characteristics of
type of property damaged. Attempts are made to eliminate deaths and injuries         hazardous material spills from reporting systems in California. Am J Public
not caused by hazardous materials. Because emphasis was placed upon events           Health 1986; 76:540-543.
involving chemicals covered by Superfund legislation and air releases from        4. Industrial Economics, Inc; Management Technology and Data Systems,
fixed sites, many events which appear in the NRC data base are excluded. AHE         Inc; PEI Associates, Inc; ICF, Inc: Acute hazardous events data base.
is maintained and augmented by EPA and its contractors, primarily Industrial         Springfield, VA: National Technical Information Service, 1985; EPA
Economics, Incorporated, and has been updated through 1986.4 If events               Contract No. 68-02-4055.



                  Formaldehyde Exposures from Tobacco Smoke: A Review
                                                                     THAD GODISH, PHD

                                                                                  cigarette, with an average of 12.1 ,ug/cigarette for 16 different
     Abstract: Reports of formaldehyde levels in mainstream, side-                brands.4
stream, and environmental tobacco smoke from nine studies are                           Room or large chamber formaldehyde levels associated
reviewed. Considerable disparity exists between formaldehyde pro-                 with environmental tobacco smoke'9 indicate that formal-
duction rates determined from mainstream-sidestream studies and                   dehyde concentrations in such rooms are high. For example,
those reporting levels in environmental tobacco smoke. Tobacco                    in the studies of Howlett, et al,8 one cigarette smoked in an
smoke does not appear to increase vapor-phase formaldehyde levels                 environmental chamber caused the formaldehyde level to
significantly in indoor environments, but formaldehyde exposure in                increase to 0.21 ppm within a half hour. Formaldehyde
mainstream smoke may pose a risk of upper respiratory system                      production rates calculated from ETS concentrations (Table
cancer and increase the risk of cancer in smokers. (Am J Public                   1) are substantially higher (one to two orders of magnitude)
Health 1989; 79: 1044-1045.)                                                      than those reported for MS, SS, and MS-SS combined.
                                                                                        The considerable disparity in formaldehyde production
                                                                                  rates determined from MS-SS and ETS studies suggests
Introduction                                                                      differences due to methodologies employed in sampling and
     Formaldehyde is a major oxidation by-product of com-                         analysis. In the mainstream-sidestream smoke studies re-
bustion processes including tobacco smoking. It is produced                       ported by the Surgeon General2'3 and by Hoffman,4 gas and
in both the mainstream (MS), and sidestream smoke (SS), and                       particulate phase materials were separated by high-efficiency
has been reported in substantial levels in environmental                          filtration. In studies by Weber, et al,6 no attempt was made
tobacco smoke (ETS).                                                              to remove particulate phase materials. Sundin' employed
     Formaldehyde levels in mainstream, sidestream, and en-                       particulate phase filtration of unknown efficiency. Attempts
vironmental tobacco smoke reported by a number of investi-                        to remove particulate phase materials in ETS samples were
gators are summarized in Table 1. Reported studies vary in                        not reported by Howlett, et al,8 and Klus, et al.9
testing methodologies and expression of concentrations. Con-                            In mainstream-sidestream smoke studies,4 smoke sam-
centration units are those originally reported and those calcu-                   ples were analyzed by the 2,4 dinitrophenylhydrazene-HPLC
lated and standardized by the author from original data, assum-                   method which is specific for free formaldehyde. The chromat-
ing a smoking rate of 35 ml/puff and 10 puffs/cigarette.                          ropic acid method'0 on the other hand was used in the studies
     As seen in Table 1, formaldehyde concentrations in                           ofWeber, et al,6 and Sundin'; it is likely to have been employed
mainstream smoke" ranged from about 10 pug/cigarette to                           in the two other environmental tobacco smoke studies as well
over 100 ,ug/cigarette. Differences in concentrations reflect                     because it is the dominant method used to determine formal-
differences in tobacco type and brand. Higher average                             dehyde concentrations in air. In the chromatropic acid method,
concentrations reported by the Surgeon General in 19863                           formaldehyde forms a stable addition product on sample col-
reflect those of regular non-filter cigarettes.                                   lection in sodium bisulfite solution. On analysis, the addition
     Sidestream vapor-phase formaldehyde concentrations also                      product is destroyed yielding free formaldehyde. Any solution
varied somewhat. Ayer and Yeager5 reported 15-48 ppm. Ho-                         which contains free formaldehyde, a formaldehyde addition
ffman's observations ranged from nondetectable to 34.2 jig/                       product, or organic compounds which produce formaldehyde
                                                                                  on sulfuric acid destruction will test positive for formaldehyde.
                                                                                        On analysis with the chromatropic acid method, the
    Address reprint requests to Thad Godish, PhD, Indoor Air Quality              particulate phase of tobacco smoke has been shown to
Research Laboratory, Ball State University, Muncie, IN 47306. This paper,         contain appreciable quantities of formaldehyde.' This form-
submitted to the Journal September 6, 1988, was revised and accepted for          aldehyde may be present as free formaldehyde dissolved in
publication December 29, 1988.
                                                                                  liquid water or it may be produced by the destruction of
© 1989 American Journal of Public Health 0090-0036/89$1.50                        formaldehyde addition products and possibly other organic

1044                                                                                                                   AJPH August 1989, Vol. 79, No. 8
PUBLIC HEALTH BRIEFS

                   TABLE 1-Formaldehyde Concentrations In Mainstream, Skdetream, and Environmental Tobacco Smoke

                                                                                                             Environmental            Cited
                                    Mainstream                                     Sidestream               Tobacco Smoke           Reference

                    ,ug/puff        ppm/puff              P#g/Cig.            Fg/cig.        ppm/cig.            4g/cig.*
                      1.7              40                   17                                                                           1
                      1-9            23-210               10-90                                                                          2
                      7-10          166-234               70-100                                                                         3
                    0.9-11.9         22-279              9.2-118.9          N.D.-34.9                                                    4
                     (7.4)            (177)               (74.2)              (12.1)
                                                                                               15-48                                     5
                                                                                                                  1629                   6
                                                                                                                   731                   7
                                                                                                                   740                   8
                                                                                                                   441                   9
                      'Calculated from data derived from large chamber studies.

compounds in the solid or liquid phase. Because it is                                   In addition, the US Environmental Protection Agency
incorporated into their molecular structure, addition prod-                             (USEPA) has concluded that sufficient evidence exists to
ucts are unlikely to yield significant quantities of free form-                         implicate formaldehyde as a human carcinogen.'8 USEPA
aldehyde under normal circumstances. Formaldehyde dis-                                  risk assessments predict that individuals with average expo-
solved in water can vaporize from the particulate phase, can                            sures of 0.16-0.19 ppm 16 hours/day for 10+ years in a mobile
remain in solution and react with other particulate phase                               home have upperbound risks of 1.5-3.40 x 1i-O. Mainstream
compounds, or can remain in solution as free formaldehyde                               tobacco smoke exposures would be expected to confer their
and then react with body tissues on inhalation. The potential                           own formaldehyde cancer risk and to increase the risk of
for particulate phase tobacco smoke to produce and release                              upper respiratory system cancer associated with exposures
free formaldehyde is unknown, and the health consequences                               to formaldehyde-contaminated indoor air.
of particulate phase materials are also unknown.
     Effect of Tobacco Smoking on Indoor Formaldehyde
Levels-Because of uncertainties associated with formalde-                                                             REFERENCES
hyde in the particulate phase oftobacco smoke samples and the                            1. Kensler CJ, Battista SP: Components of cigarette smoke with ciliary-
                                                                                            depressant activity. N Engl J Med 1963; 269:1161-1166.
lack of specificity of the chromatropic acid method for free                             2. USDHEW: Smoking and Health: A Report of the Surgeon General. Pub.
formaldehyde, reported ETS studies are of limited usefulness in                             No. (PHS) 79-50069. Washington, DC: Govt Printing Office, 1979.
assessing the effect of tobacco smoking on vapor-phase form-                             3. USDHHS: The Health Consequences of Involuntary Smoking: A Report
aldehyde levels in indoor air. Formaldehyde concentrations in                               of the Surgeon General. Pub. No. (CDC) 87-8398. Washington, DC: Govt
                                                                                            Printing Office, 1986.
indoor air can, however, be calculated from production rates                             4. Hoffman D: Formaldehyde in cigarette main- and sidestream smoke.
reported by the Surgeon General2 3 and by Hoffman.4 The                                     Valhalla, NY: Naylor Dana Institute for Disease Prevention, American
following "worst case" conditions are assumed: 1) 20                                        Health Foundation, 1983.
cigarettes/30 minutes smoking rate; 2) production rates of 120                           5. Ayer HD, Yeager DW: Irritants in cigarette smoke plumes. Am J Public
                                                                                            Health 1982; 72:1183-1285.
and 34 ,ug/cigarette for MS and SS; 3) MS formaldehyde not                               6. Weber A, Jermini C, Grandjean E: Irritating effects on man of air pollution
retained by smoker; 4) zero air exchange rate in a 30 m3                                    due to cigarette smoke. Am J Public Health 1976; 66:672-676.
environmental chamber; and 5) no sinks or other sources                                  7. Sundin B, Haneto P: Formaldehyde emission from particle board and other
present. Under these assumptions, 3080 ,ug formaldehyde                                     building materials: A study from the Scandinavian countries. Maloney T (ed):
                                                                                            Proc Twehth Annual Particle Board Symposium-WSU, 1978; 251-273.
would be produced resulting in a concentration of0.085 ppm. In                           8. Howlett CT, Newton LR, Stevens KR: Formaldehyde: A case study. Proc
a 194 m3 space (typical of a single-wide mobile home) the                                   Fourth Int Conf Indoor Air Quality and Climate 1987; 2:676-681.
concentration would be considerably lower (0.012 ppm). Even                              9. Klus H, Begutter H, Ball M, Intorp M: Environmental tobacco smoke in
under these extreme circumstances, the effect of cigarette                                  real life situations. Proc Fourth Int Conf Indoor Air Quality and Climate
                                                                                            1987; 137-141.
smoking on formaldehyde levels in indoor spaces would be                                10. NIOSH: Manual of Analytical Methods, 3rd Ed. Method 3500. DHHS
negligible. This is consistent with the residential measurements                            Pub. No. 84-100. Cincinnati: NIOSH, 1984.
of Dally, et al, " and Ritchie and Lehnen.'2                                            11. Dally KA, Hanrahan LP, Woodbury MA, Kanarek MS: Formaldehyde
                                                                                            exposure in nonoccupational environments. Arch Environ Health 1981;
     Exposures to Smokers-Formaldehyde levels in main-                                      36:277-284.
stream smoke appear to be high. When dilution inspiration is                            12. Ritchie I, Lehnen R: An analysis of formaldehyde concentrations in mobile
taken into consideration, formaldehyde exposures on a per                                   and conventional homes. J Environ Health 1985; 47:300-305.
puff basis appear to be in the range of 1.5-19.5 ppm/puff. The                          13. Broder I, Corey P, Cole P, Mintz S, Pa ML, Nethercott J: Health status
                                                                                            of residents in homes insulated with urea-formaldehyde foam. In: Pro-
cumulative daily exposure duration for a single pack/day                                    ceedings APCA Specialty Conference-Indoor Air Quality in Cold Cli-
consumption would be approximately 6 minutes and 40                                         mates: Hazards and Abatement Measures, 1986; 155-156.
seconds; the cumulative daily dose, 188-2382 pug (depending                             14. Olson JH, Dossing M: Formaldehyde induced symptoms in day care
on brand smoked). Exposures at the upper end of the range                                   centers. Ind Hyg Assoc J 1982; 43:366-370.
                                                                                        15. Ritchie IM, Lehnen RG: Formaldehyde-related health complaints ofresidents
for a one pack/day consumption would be approximately                                       in mobile and conventional homes. Am J Public Health 1987; 77:323-328.
equivalent to an exposure of 0.25 ppm 22 hours/day in a                                 16. Hendrick DJ, Rando RJ, Lane DJ, Morris MJ: Formaldehyde asthma:
mobile home environment.                                                                    challenge exposure levels and fate after five years. JOM 1982; 24:893-897.
     Health Risks-Recent epidemiological studies indicate                               17. Nordman H, Keskinen H, Tuppurainen M: Formaldehyde asthma-rare
                                                                                            or overlooked. J Allergy Clin Immunol 1985; 75:91-99.
that formaldehyde exposures associated with residential                                 18. Office of Pesticides and Toxic Substances, USEPA: Assessment of health
environments are great enough to cause a variety of acute                                   risks to garment workers and certain home residents from exposure to
symptoms.13'5 Formaldehyde may also cause asthma.'6"17                                      formaldehyde. Washington, DC: USEPA, 1987.

AJPH August 1989, Vol. 79, No. 8                                                                                                                                  1045

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1044

  • 1. PUBLIC HEALTH BRIEFS cause of the incident, container structure and failure, and deaths and injuries appear in more than one source, they are checked for consistency; otherwise, resulting from the cargo. DOT attempts to validate death and injury data. data are not validated. Specifically excluded from reporting requirements are releases of small quantities of certain consumer commodities, and releases from motor carrier firms doing solely intrastate business and from certain water transporters. Automobiles striking storage tanks and certain transportation-related spills at fixed facilities are also excluded. REFERENCES The Acute Hazardous Events (AHE) data base was begun in 1985 and uses 1. SAS Institute Inc: SAS User's Guide: Basics. Version 5 Ed. Cary, NC: SAS the NRC as its main source of data. However, data are also included from Institute Inc, 1985. selected state governments, the Environmental Protection Agency (EPA) 2. US Congress, Office of Technology Assessment: Transportation of haz- Region 7, some newspapers and wire services, and other sources. Information ardous materials. Washington, DC: Govt Printing Office, 1986; 66-86. collected includes cause of event, activity taking place during the event, and 3. Shaw GN, Windham GC, Leonard A, Neutra RN: Characteristics of type of property damaged. Attempts are made to eliminate deaths and injuries hazardous material spills from reporting systems in California. Am J Public not caused by hazardous materials. Because emphasis was placed upon events Health 1986; 76:540-543. involving chemicals covered by Superfund legislation and air releases from 4. Industrial Economics, Inc; Management Technology and Data Systems, fixed sites, many events which appear in the NRC data base are excluded. AHE Inc; PEI Associates, Inc; ICF, Inc: Acute hazardous events data base. is maintained and augmented by EPA and its contractors, primarily Industrial Springfield, VA: National Technical Information Service, 1985; EPA Economics, Incorporated, and has been updated through 1986.4 If events Contract No. 68-02-4055. Formaldehyde Exposures from Tobacco Smoke: A Review THAD GODISH, PHD cigarette, with an average of 12.1 ,ug/cigarette for 16 different Abstract: Reports of formaldehyde levels in mainstream, side- brands.4 stream, and environmental tobacco smoke from nine studies are Room or large chamber formaldehyde levels associated reviewed. Considerable disparity exists between formaldehyde pro- with environmental tobacco smoke'9 indicate that formal- duction rates determined from mainstream-sidestream studies and dehyde concentrations in such rooms are high. For example, those reporting levels in environmental tobacco smoke. Tobacco in the studies of Howlett, et al,8 one cigarette smoked in an smoke does not appear to increase vapor-phase formaldehyde levels environmental chamber caused the formaldehyde level to significantly in indoor environments, but formaldehyde exposure in increase to 0.21 ppm within a half hour. Formaldehyde mainstream smoke may pose a risk of upper respiratory system production rates calculated from ETS concentrations (Table cancer and increase the risk of cancer in smokers. (Am J Public 1) are substantially higher (one to two orders of magnitude) Health 1989; 79: 1044-1045.) than those reported for MS, SS, and MS-SS combined. The considerable disparity in formaldehyde production rates determined from MS-SS and ETS studies suggests Introduction differences due to methodologies employed in sampling and Formaldehyde is a major oxidation by-product of com- analysis. In the mainstream-sidestream smoke studies re- bustion processes including tobacco smoking. It is produced ported by the Surgeon General2'3 and by Hoffman,4 gas and in both the mainstream (MS), and sidestream smoke (SS), and particulate phase materials were separated by high-efficiency has been reported in substantial levels in environmental filtration. In studies by Weber, et al,6 no attempt was made tobacco smoke (ETS). to remove particulate phase materials. Sundin' employed Formaldehyde levels in mainstream, sidestream, and en- particulate phase filtration of unknown efficiency. Attempts vironmental tobacco smoke reported by a number of investi- to remove particulate phase materials in ETS samples were gators are summarized in Table 1. Reported studies vary in not reported by Howlett, et al,8 and Klus, et al.9 testing methodologies and expression of concentrations. Con- In mainstream-sidestream smoke studies,4 smoke sam- centration units are those originally reported and those calcu- ples were analyzed by the 2,4 dinitrophenylhydrazene-HPLC lated and standardized by the author from original data, assum- method which is specific for free formaldehyde. The chromat- ing a smoking rate of 35 ml/puff and 10 puffs/cigarette. ropic acid method'0 on the other hand was used in the studies As seen in Table 1, formaldehyde concentrations in ofWeber, et al,6 and Sundin'; it is likely to have been employed mainstream smoke" ranged from about 10 pug/cigarette to in the two other environmental tobacco smoke studies as well over 100 ,ug/cigarette. Differences in concentrations reflect because it is the dominant method used to determine formal- differences in tobacco type and brand. Higher average dehyde concentrations in air. In the chromatropic acid method, concentrations reported by the Surgeon General in 19863 formaldehyde forms a stable addition product on sample col- reflect those of regular non-filter cigarettes. lection in sodium bisulfite solution. On analysis, the addition Sidestream vapor-phase formaldehyde concentrations also product is destroyed yielding free formaldehyde. Any solution varied somewhat. Ayer and Yeager5 reported 15-48 ppm. Ho- which contains free formaldehyde, a formaldehyde addition ffman's observations ranged from nondetectable to 34.2 jig/ product, or organic compounds which produce formaldehyde on sulfuric acid destruction will test positive for formaldehyde. On analysis with the chromatropic acid method, the Address reprint requests to Thad Godish, PhD, Indoor Air Quality particulate phase of tobacco smoke has been shown to Research Laboratory, Ball State University, Muncie, IN 47306. This paper, contain appreciable quantities of formaldehyde.' This form- submitted to the Journal September 6, 1988, was revised and accepted for aldehyde may be present as free formaldehyde dissolved in publication December 29, 1988. liquid water or it may be produced by the destruction of © 1989 American Journal of Public Health 0090-0036/89$1.50 formaldehyde addition products and possibly other organic 1044 AJPH August 1989, Vol. 79, No. 8
  • 2. PUBLIC HEALTH BRIEFS TABLE 1-Formaldehyde Concentrations In Mainstream, Skdetream, and Environmental Tobacco Smoke Environmental Cited Mainstream Sidestream Tobacco Smoke Reference ,ug/puff ppm/puff P#g/Cig. Fg/cig. ppm/cig. 4g/cig.* 1.7 40 17 1 1-9 23-210 10-90 2 7-10 166-234 70-100 3 0.9-11.9 22-279 9.2-118.9 N.D.-34.9 4 (7.4) (177) (74.2) (12.1) 15-48 5 1629 6 731 7 740 8 441 9 'Calculated from data derived from large chamber studies. compounds in the solid or liquid phase. Because it is In addition, the US Environmental Protection Agency incorporated into their molecular structure, addition prod- (USEPA) has concluded that sufficient evidence exists to ucts are unlikely to yield significant quantities of free form- implicate formaldehyde as a human carcinogen.'8 USEPA aldehyde under normal circumstances. Formaldehyde dis- risk assessments predict that individuals with average expo- solved in water can vaporize from the particulate phase, can sures of 0.16-0.19 ppm 16 hours/day for 10+ years in a mobile remain in solution and react with other particulate phase home have upperbound risks of 1.5-3.40 x 1i-O. Mainstream compounds, or can remain in solution as free formaldehyde tobacco smoke exposures would be expected to confer their and then react with body tissues on inhalation. The potential own formaldehyde cancer risk and to increase the risk of for particulate phase tobacco smoke to produce and release upper respiratory system cancer associated with exposures free formaldehyde is unknown, and the health consequences to formaldehyde-contaminated indoor air. of particulate phase materials are also unknown. Effect of Tobacco Smoking on Indoor Formaldehyde Levels-Because of uncertainties associated with formalde- REFERENCES hyde in the particulate phase oftobacco smoke samples and the 1. Kensler CJ, Battista SP: Components of cigarette smoke with ciliary- depressant activity. N Engl J Med 1963; 269:1161-1166. lack of specificity of the chromatropic acid method for free 2. USDHEW: Smoking and Health: A Report of the Surgeon General. Pub. formaldehyde, reported ETS studies are of limited usefulness in No. (PHS) 79-50069. Washington, DC: Govt Printing Office, 1979. assessing the effect of tobacco smoking on vapor-phase form- 3. USDHHS: The Health Consequences of Involuntary Smoking: A Report aldehyde levels in indoor air. Formaldehyde concentrations in of the Surgeon General. Pub. No. (CDC) 87-8398. Washington, DC: Govt Printing Office, 1986. indoor air can, however, be calculated from production rates 4. Hoffman D: Formaldehyde in cigarette main- and sidestream smoke. reported by the Surgeon General2 3 and by Hoffman.4 The Valhalla, NY: Naylor Dana Institute for Disease Prevention, American following "worst case" conditions are assumed: 1) 20 Health Foundation, 1983. cigarettes/30 minutes smoking rate; 2) production rates of 120 5. Ayer HD, Yeager DW: Irritants in cigarette smoke plumes. Am J Public Health 1982; 72:1183-1285. and 34 ,ug/cigarette for MS and SS; 3) MS formaldehyde not 6. Weber A, Jermini C, Grandjean E: Irritating effects on man of air pollution retained by smoker; 4) zero air exchange rate in a 30 m3 due to cigarette smoke. Am J Public Health 1976; 66:672-676. environmental chamber; and 5) no sinks or other sources 7. Sundin B, Haneto P: Formaldehyde emission from particle board and other present. Under these assumptions, 3080 ,ug formaldehyde building materials: A study from the Scandinavian countries. Maloney T (ed): Proc Twehth Annual Particle Board Symposium-WSU, 1978; 251-273. would be produced resulting in a concentration of0.085 ppm. In 8. Howlett CT, Newton LR, Stevens KR: Formaldehyde: A case study. Proc a 194 m3 space (typical of a single-wide mobile home) the Fourth Int Conf Indoor Air Quality and Climate 1987; 2:676-681. concentration would be considerably lower (0.012 ppm). Even 9. Klus H, Begutter H, Ball M, Intorp M: Environmental tobacco smoke in under these extreme circumstances, the effect of cigarette real life situations. Proc Fourth Int Conf Indoor Air Quality and Climate 1987; 137-141. smoking on formaldehyde levels in indoor spaces would be 10. NIOSH: Manual of Analytical Methods, 3rd Ed. Method 3500. DHHS negligible. This is consistent with the residential measurements Pub. No. 84-100. Cincinnati: NIOSH, 1984. of Dally, et al, " and Ritchie and Lehnen.'2 11. Dally KA, Hanrahan LP, Woodbury MA, Kanarek MS: Formaldehyde exposure in nonoccupational environments. Arch Environ Health 1981; Exposures to Smokers-Formaldehyde levels in main- 36:277-284. stream smoke appear to be high. When dilution inspiration is 12. Ritchie I, Lehnen R: An analysis of formaldehyde concentrations in mobile taken into consideration, formaldehyde exposures on a per and conventional homes. J Environ Health 1985; 47:300-305. puff basis appear to be in the range of 1.5-19.5 ppm/puff. The 13. Broder I, Corey P, Cole P, Mintz S, Pa ML, Nethercott J: Health status of residents in homes insulated with urea-formaldehyde foam. In: Pro- cumulative daily exposure duration for a single pack/day ceedings APCA Specialty Conference-Indoor Air Quality in Cold Cli- consumption would be approximately 6 minutes and 40 mates: Hazards and Abatement Measures, 1986; 155-156. seconds; the cumulative daily dose, 188-2382 pug (depending 14. Olson JH, Dossing M: Formaldehyde induced symptoms in day care on brand smoked). Exposures at the upper end of the range centers. Ind Hyg Assoc J 1982; 43:366-370. 15. Ritchie IM, Lehnen RG: Formaldehyde-related health complaints ofresidents for a one pack/day consumption would be approximately in mobile and conventional homes. Am J Public Health 1987; 77:323-328. equivalent to an exposure of 0.25 ppm 22 hours/day in a 16. Hendrick DJ, Rando RJ, Lane DJ, Morris MJ: Formaldehyde asthma: mobile home environment. challenge exposure levels and fate after five years. JOM 1982; 24:893-897. Health Risks-Recent epidemiological studies indicate 17. Nordman H, Keskinen H, Tuppurainen M: Formaldehyde asthma-rare or overlooked. J Allergy Clin Immunol 1985; 75:91-99. that formaldehyde exposures associated with residential 18. Office of Pesticides and Toxic Substances, USEPA: Assessment of health environments are great enough to cause a variety of acute risks to garment workers and certain home residents from exposure to symptoms.13'5 Formaldehyde may also cause asthma.'6"17 formaldehyde. Washington, DC: USEPA, 1987. 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