S.J.G. ......... . . .. .... .... Environmental Tobacco Smoke Effects on the NO'n-Smoker Report from a Workshop Edit,d by 302058626 BATCo document for Province of British Columbia 19 April 1999 J;; Z 302058627 Contents PRFFACE 5 1. INTRODUCTION . . . . . . . . . . . . . . . . . . . 7 Rogner Rylander 2. REVIEW OF STLIDIES ON ENVIRONMENTAL TOBACCO SMOKE 10 Ragnar Rylander .3. WORKSHOP WCUIAENTS . . . . . . . . . . . . . . . 21 3.1 Introduction . . . ... . . . . . . . . . . . . . . . 21 3.2 Characteristics of tobacco sidestream smoke and factors influencing its concentration and distribution in occupied spa~ez . . . . . . . 21 Aforton Curn 3.3 Reduction of tobacco moke, contaminants in interior spaces by means of filtration . . . . . . . . . . . . . . . . . . . . 37 Preilon E. McNall 3, 3.4 Tobacco smoke inhalation . . . .. . . . . . . . . . . . 44 Da~id Muir 3.5 Epidemiol*cal Investigations on eav'Ironmental tobacco unoke 47 Runc Cederibi and John Colley 3.6 Tobacco smoke allezrgy - does it exist? .50 Geoffrey raytor 3.7 effwAl-df kA- m1ccrittiiL-1.'~;f carbon monoxide in wa -56 Rickard D. Stirwart 3.8 Effects 91 tobacco smoke 01D biological 3YStCZM Kaye 11. Kilbufw 4. WORKSHOP RESULTS . . . . . . .. 79 4.1 Perspectives on environmental tobazco smoke effects . . . . . . . 79 Ragairr Rylander 4.2 Workshop suinzaary-and recommendations . 88 Mort.n:Com, Kayr Kiltrurn Ond R#gnar Ryleader 13 ATCo document for Province of BritiSh Colurnbia 19 April 1999 Pre face The workshop on Eavironotental, Tobacco ROME CtbW,6F, Ph. D. Smoke Effeas " die XLma-Sutoker took Karolinska Institute place on Bermuda, March 27-29, 1974. Department of En%-ir*nmental Health 14' The Workshop ias organizc4 by Ragnar ' 10401 Storkholm 60 - Sweden ether Rylander, Geneva Universitv tog with Morton Com, Pittsburib University PETER CoLE, Af. D. grid Kaye If. K;!btrm, University Of The Royal Hospital of SL Rartholotnew souri. Miss Vicky NicolopGulou acted as Department of Anaesthesia Head Secretary- West Stnithfic4d if! Ile Workshop was supported by Gene- London EC IA 7111B , England va . University through a grant from "Pabriques de Tabac Riunim-, Ncucha- tel, Switzerland- J*Hrq R. T. CoLLY-Y, M. D, Editorial assiqance was pro%ided by London School of Hy0ene and, bilichad A It Russell Tro~lcal 'Adedicine . . . -Delutut t 6"Ietrwid StX6""* -.1fid -Miss Ariane Cam Epidemiology . Keppel Sta-et. (Cower streets Ile participants in the Wwksitop am Lotulad WC I E 711T - E*ghnA lis", Wow. Yvzs AtARm, Pit. D. CoR-4, PiL D.' Uninisity of Pittsburgh UniveTsity of. Pittsburgh Graduatt School of Public. Heilth Graduate School of Public Heqlth munivanii,15,961 -,V4A Pit"h, Y* Pittsburg, Penn Lvania 15261,- USA D03UNGO M. AViAt1q, M. 1). TbRE DAURAMN, M. D. i4 Univmify of Pennsylvania uppola univcnity School-of Nledic;m Gi Institute of-Hygiene Departownt of Pharnuicalogy pox 17007 Philade.lPhin, PenprAv4nia. 19174 U SAI 10462 StocUolm 17 -Sweden - rr4 302058628 BATCO document for Province of BritiSh Columbia 19 April 1999 LAIM FRISERG, I%'l. D. DAVW C. F. Mum, Pli. D., MRCT Karolinska Institute Institnte of Ocetipational Medicine Depamnfw of Environmental Health Roxburgh Place 10401 Stockholm 60 - Sweden Edinburgh F148 9 SU - Scotland HANS-PETER HARKF, Ph.D. MICHAft A. H. RuSSELL, M. D. F(wichungsinst it kit der 'Mt; Maud.%ILY 110~pitat Cigarettenindustrie e.v. 101 Derintark Hill 2 Harriburg 54 London SE5 8AF - England Cazellenkarrip 38 - W. Germany R_,%oNAit RYLANDER, M. D. CustTis HAms, M. D. Institut de Midecine Sociale National Cancer Institute et Pr6ventive Building 37, Room 3C03 20, Quai Ernest Ansermet Bethesda, Maryl.and 20014-- 1J9A 1203 Geieva - Switmiand Present wWress: JAWS C. HAWORTH, M.D. Department of Environmental Hygiene f. The University of -Manitoba University of Gothenburg rp Department of Pediatrics 40033 Gothertbutg 33 - Sweden Children's Hospital 91 685 hannatyne Avenue HLLULr SCHIEVELBEIN, V.D. 11MV Winnipeg Deutsches Hernentrum Miinch n NL-ini~a R3E_OWl - Canada 8 Mijnchen 2 Lothstrassc I I - W. Germany 4. KAvz H. KILIMMN, M. D. is University of Missouri TnEcmok- D. STwtmric, Ph.D. School of Medicine Simon Fraser University Diwision of Pulmonary and Pownputing Science,- Program i~ Environmental Medicine Burnlib; 2, ft. Columbia - Canada - Columbia4 Mis~ri 65201 - USA ART RjcttAwD,D,STz%v M.D,., _ _ The Medical Colleg#_- of Wisconsin, ~N" Q.Au~r Lz~F r, M.D. Departmedi'of G%i~~nrnentat Vla&i" National Heart and')Lung' Institute '8700 Wi!t~rwlsconin 4venkle Ni!tional Institutes of 11cahli, Milwaukee, Wisconsin 53226 - USA BOwMa-Maqland 92W14 - USA GtcwrRw TAYIft, M. 1). PusTow F. MuNAm -la,. Pb, W Uninrsity,of Manch.e9ter 507, Eabt Michigan Stmet Stopford Building Milwauker,- - USA Manch"er M 13 9PT - Englanj 302058629 BATCO document for Province of BritiSh Columbia 19 April 1999 iene ine Introductioii RAoNAR RYLANDER Ile relation bet-een human health and Unfortunately the ideal situation con- agent- in the environment has always ceming information about the effects of been of great interest to mankind. Against agents does not prevail in most cases. In factual information or suspicions that these iiinfances decis'imis concerjung the spottifit Agents m-.vr cause disease in inan, control of agents have to be inade against reactions develop in the society among a background of incomplete data and lack gmups of experts, P01itiLiiuis, "th ad- of information in important areas. Under ministratars and private individuals. These such circumstances the proper eviduittibn reactions 6fic'n have cruotional under- of available data becomes even more im- tones, cspeciA-V in CaSft WhCft iiifonna- purtant. tion on the effects of the agent in question For the evaluation the. exposure agent is incomplete. itself has to be defined -for diff~-rLlfit con- Any agent in the environment suspect- ditions. Ile various ponible effects. on hu- ed of causing harmful'effects must be mans due to exposure must be, reviewed thoroughly studied. The Ideal procedure- and criteria for ex .p.osure limits have to be is to define the agent in physical, ehein- established (Hatch 1973). The criteria last ical or biological ternis~ then to delineate aspect is used in the context established by' P its various effmts ~'And finally to establi4sh WHO for studies of environmetual agen'~k 7 be evaluated for each of the relevant pf- Quality criteria are sets of teso-selected fects and ~Dr. the aferent groups in the to establish a quatititative relationshili be-. tibd in-whom differences k mt-' PUPWA tween'ak ~.~rnt a~icf A' 'Subject. Quality tion pattems niny be expected. criteria need to be established in respect Ile dose-mpomse relationships should w4c effects of the,agent ou'roap's health ' be as accurate as passible .and b.14i on in its broadest sense. Selection of,-tests to .the late st scientific Lnowlvdge. 71w data elucidate the, dose-effect - patiem is im" On CMM Are Of iftipOrtance 10 pt-lblic P0VtAnt..3hUC,AV%UIt5 11136 *410rbPriefte-or - - he"aft autbo; 6_as-.& basij& ta_&-umioo 'Yr;jri"_P1-,f1_-,t,_ liliust; Ac- the accessity for tbe establishment of con- tion-agairist the agent. trol policies. Guider am the limits recotuirwrided, in 302058630 BATCO document for Province of British Columbia 19 April 1999 the fo= of numerical values or "zones", at or below which an undesirable effect does not appear. Standeyrdi ire adrnini~trntive dcci~tons which are taken by a local, 10lional or inteniational authority, t3king into- (7011- sideration nut only thr bt.i cvi- dence available, but also econontic, social, political.and other relevant facters. It is obvious that quality criteria. guidcs and standards must be brought up to date whenever substantial advances in know- ledge occur In recent years there has been much interest and. concern regarding the possible health effects of enviromnentak tobacco smoke. Comprehensive reviews on the available infamiation have be= presented (Schie- velbein 1973) and on two occasions, the health c1fects of environmental tobacco smoke have bem- analyzed by a group of experts. In "The Health Gonwqf4enc of Smok- Wg - a Report Of the Surgeon General 1972 (U.S. MIEW 1972)" - the fella- ing conclusions were presented: I - An atmosphere pontaminak-d with to- acr.O ke can: contri ute S- 1, coMfort of.rnaLny individwils. 2 -The level of carbon monom-ile auaitied in experiments u~ng rootL15 IrIM4 Willi tobacco smoke has. been shown to equA4 and at times to ~mceed~ the legal lintits for maxituum Mr. pollu tion permitted f6r'ambicnt air quiility in scverl&Woc~ and gw_k.abo exc Wd WL M4 Value for a nonn4 work period pres. ently in effc~t for the Vitiled -States -as a whole. The presence of suchlevels indicates thAt' tive. effect of exposure to carlion nionoxi& may on occasion, depending upon the length of expo- sure, be sufficient to lie harinful t(i the health of an exposed person. This would be part icularly significant for people who are already suffering from chmnir bronrlinlitiltbritiarv disease aiul coronary heart di-eftse. 3 Other components of tobacco stnokc. such as particulate inatter and the oxides of nitrogen, have been shown in various concentrations to adversely affect animal pulmonary and cardiac structure and function. The extcnt-.of the contribution.4 of thew substances I- illness 6 liumans exposed to the concentrations present in all atmo- 6 phere contaminawd %ith tobacco smoke it--not presently. known. In a subwquent report (Fietchet- (et al. 1973) an expert group under the auspices of the Royal 'College -of Ph)sicians of London analysed the problem and in their summary presented the"following conclu- %ion- -11here is no evidence that other peo- pie's smoke is dangemus to hvalthy it. call V. extrenvel j irritating and cause Jistresing syjMp- ionU, especially in allergic persons or in dxase 'almoy~afkcted hy heiirt or lung disease- The smoke frmu PTU and cigars is at least as irritating as that froin cigarettes. 1.n*er-trow4ed, ffl- %Tntilatrd, rooms Or in enclosed Paoes such -as cars,,, smoking- can lead it, a carb6ti-mmoxidr, level of 50 lipm or ov 'I. norc w itcl is ~i e T.V.11 F~11_ mitt~d in induitr/." The comiusi-MIS from the abcn-v report-~ have litter been cliallenged bywher scien- awl Iwo I to lk in It Wet ell n,,. l0 e, "I 4 re soli %i in -bj L't 302058631 BATCO document for Province of British Columbia 19 April 1999 expo- to tile This nt for, Z from r,e and imoke, d the show ,-Crs* ardiac ent of cances .0- the ;bac rt al, of their. nclu- ,Athy AQ, "Ls or rt or that or t pet- -ort5 -ien- tists and by public health repiewittativvs rlf~i'air nf elviel-i^lr~ftiril -Hirr. if and the di,cusiou tonceming the possible tile responsibility of the rapporteurs of health effects of envimninental tobacco cacti session tc, compile relctant niaterid smoke have i-ontinued. and present it to tile workMicip. Fr.-,.-r, It was flicrefort, ihought to he desirahir- niher working dr,curnents and discussiors to PeTform ;al vxtcu~ive evaluation of the that took place. tile final manuscripts for problems associaterl with tobacco -.tmoke thr proceedings werr. prepared. All Pay- in the ciwironnici.. aiid aii Lituii"tiuiial ii~tipauts iii tht~ workshop agreed on tile Workshop was organized. "Workshop conclusions and recommen- Twenty-one scientits representing the dations". fields of ventilation. cellular toxicology, caricinogenesis, inhalation toxicology, phar- REFERENCES macology, respirato-y physiology, psychO- Fletcher, C. M.. Donovan, J. W.. Li%vihcr, P. logy, sociology and epidemiology attended J., Waller, R. E. and Ball. K. P. (1973) the 2 ~12 day meeting. Pipe and Cigar Stnoking: The Report of an Ile purMse ot -the Wotkshop was to Expert Ozoup appointed by Actienii ft Snwi. ' review the availabk- information on the ing and Health. Practiti ame 210(1259,; ubject, to we wherr sufficient knowledge 645-652. H. 'Lch, T. If. (1973) Crite-ria for IF-rdati!, existed and whete more irtformation was Exposure Lirniu, Arch. Eau. H-1th 27: needed. The participants werc asked to 231-235. make rmommenclat ions for future work &-hievelbein, H. f 1973) On the Effects of To- with A vicw io determining witethrr and bAirco StrinkinS on the Itimbidity of Non- in which ciTcurustarim environmental to- unoker% (in Gerrn;in). 1"t~nia 14: 236- t 243. bacco smoke might constitute a public U~&DJIX_W. 41972) The -H-fth Come- health problem. quences of Sinaking - A report to the Sur- The presentations and discus-~ions of the meon General, PuWk Health. S-ice, Jan- Workshop covered scnieral aspe"s of tile uafy 1972- subject,ranging from -m-ritila6m to aerosol World Health Or"nization (1972) Environ- ' niontal Health Criteria , Repo" by a WHO diaracteriuics,.pcil toxicity and the proper Sc;-Afic frop (EP 73.21. 302058632 BATCo document for Province of BritiSh Columbia 19 April 1999 2. Review of Studies oii Environmental Tobacco Smoke R %G.VAK R1 LANDER PC 2.1 INTRODUCTION tobacco smoke compounds in various en sot, YI For the purpose of the work-shop a rrview vironmenu. ney estimmed the amount of studies on esivironmental tobacco smoke of airborne particles in railway caniag" d was pmpared with special emphasis on with the aid of a Cottifuge and Lound sm, the close-responsc aspms arki the MI-AnCe that the level was alx-t 4 times higher cr4. in smoke, coml,artmerin that L nO - mok- of the data for exposure to environmental h n s tobacco * smoke under real lifc conditions. ing compartments. Similar proparti6ns =0- The studies were divided into the follow- wem foudd ift mmuraut, ing categories: Determinations were also made of con- densation nucici which include all small Meastim-ment of to1mcco smoke cozuti- particles not detected with the COILifUge. ruents in environmental air. In d.Li.. -we, the difference betcen - Mewturement of tobacco smoke cnti- snoke-free atmospheres and environments Auents in environmental air and in man with a high coucentration of smoke was including studies on exposure effecm - Studies on "posure effects without ix-fold. Of particular intere,st in this iatt st 4dy was the ssimvltaneous measurement measus-ents of .tobacco smoke consti- of 44letent fob." smoke components m 1--t5. rooms .ttqF,,3 UrgL _zuMN- 4 Tipt&f,~ in the revit~ tht! cqnceftlrs~,~~n of d~ ~~ bcca anakrd. At CO-le-15 Of 80 51 afeftnt stilwances has been given in ppm the nicotiu, ejuicentration was 5.2 Aar units as reported by tlw authors wit h oth- ~ingln$. Howev the juethod ai-zinalysii' M cr. units calculated to lacilitatir compari- 'in th~ study Wlk* Dot Very aCCUratP_ tw sorts in brackets. Ile concentration of bew-pyrene in smoky aftrompheres was 3tudied by Galus- 2.2 --MEASUREMENT OF-TOBACCO kinova (1964). In the urban anbimt air ruI X ravimts varied betwmh 0.' SMOKE CONSTITUENTS 1, concent 28 - and EM'IRONMENTAL AIR If. Harm3wi and Efferibergq'. fJ95;U ~t- --Z L-1. , ;Calx~ntraWtt of 2.a~ 14.4 pgf nrt-w ;,.t:A*LLm the vxwentrAtion of WO ms -m mprwd. The aut4or oc;n,. 302058633 BATCo doCumentfor Province of BritiSh Colurnbia 19 April `1999 Hous en- amount ages rd' 71 .m-srnok- ~~portictns of con- '~onifuge. 6 etween oke was in this ~in I I _j garettes g. ;t ~f so It 5-2 anal" in ient air 'S and g busi. 14.4 pgt. clude.41 that thv variations depended on (CO) in thf- air of the room were mca- the general aini,ivm ai, and ii, -~urrd -it Hif(~",vn timr-The levels reached and t1w number of 6qtrettes sninked in after the vmnking of 30 cigarent's ,,crt-: the. room itself. Tin- benpyrene von- 0.51 Ing niC0ti11V'jT13, 0.46 mg acrolein,ml. tent of cigarette niaimtream smoke lies 64 ppin CO and (3.5 nig acctyldchyL;t~ ii-0. between 0.3 and 4.4 pv _100 cigitrett- and I ec concentration under real To achieve th is about twice as witch in sidc~trvam life conditions would me- that 30 smok- smoke. If the concentration fonud in the ers had to assemble in a room with about -en dne to sinoking only it %vould air had be lb rn~' ( 12 x 12 f-ti ..rbce. When -5 therefore have required the constant cigarettes were smokc~ Within 13 minutes, smoking of IM rigarettex per 10-40 mii- the amounts during equal collecting peri- utes depending on the ventilation. ods were: 0.06 mg nicotineltins, 0.07 mg A number of experiments has been acrolcin/ins, 11.5 pprn CO and 1.3 mg pMormed where environmental tobacco acetaldehyde. smoke has been -studied under controlled Hoegg (1972) studied the concentra- conditions. Several of these studies were tion of various constituents. of tobaccr, desigt%ed to study the I W-f-life of tobacco smoke i6i a scaled chamber under con- t sinokc under various conditions. The con- trolled conditions. He found that the GO centrations were increa" to verv high concentration was directly proportional to k-vels. to facilitate the sampling procedure the number of cigarettes sn-4ked in the- or to reduce the influence of transient chamber. The sidestream-mainstreaM ratio variations. which would occur vvith low for GO was found to he 4.7. For partic- levels of the different compounds. Such ulate matter, on the other hand, the ratio cDneentrationswould not be present under was 0.7. After unctking 24 ciprettes simul- realistic oponditions. taxtemsly in.thc 25 m4t test chamber the Marke (1970) reported on experiments concentration of GO was 69.8 ppm. nis- wha involved both- experimental- and would correspond to about 20 smokers in more real i~tic exposure conditions- In the a roolu 'with abuu't 10 m* (9 x 12 feet) Imter which is of more intcrvA in this surface. Based on eVerimental data, nouticction, one peto w sawked I I Cc~aret- Hoegg proposed a general foirmula. to_pm- tei:dutitrg 5-houris-la a 30 P13 L1.7 I or dict the CO concenfration in a sealed 9 X 12 feet) large raium. Measurements roo7 as a tuntfitiin_of the, -ao cli(a- shovwd that during smoking the concen-, rettes smoked. itation of nicotine.mached 0.0".0q in Bridge and-Corn-f1972) perforrned ex- nr3,J meter from-the smokefs bead de- penments in a 91.2 t~-,-c6mber w1here ft . ... . . pending upon vcntiLition. The CO level ciVarette smoking inachine generated -the was below IQ ppin. In another experiment smoke. CO was trionitored continuously. (Harke et al. 1972) an unventifated raorn as an index, of the degree of pollution. (38.2 0) was filled with. smoke hi a- '!Ivey also pctfonned -expetiniteritv, ill inach4te srnoking. 5, 10,15 or 30 eigamml Mo .re lAulral muiua.'At,two partics with within about 13. ruinutes. onuvntta~akm~ aldehydes '(expressed of nic,,tine acr-lein crnirtitions over .1.5 hour$ were foukid to , , r con- a rt"4dt:hy&) and carbon nwonxide be 7 and, 9L pprn when about,60 ciga"es 302058634 BATCO document for Province of BritiSh ColUmbia 19 April 1999 4 12 a-nd 15 vigm, v,re smoked. It wa, ralcti- latrd that abotti t; r,~p. 12 r~, of this animin( liid lwt-n creatcd I)% flie ti-st Im-r- sons Th'. "emp. 'onceitira- tion of stz~pvtidcd patticulate matter was calculated t,~ he 2800 to 1301) 1&gin' at the first party and 2100 to 3200 tag ill at th'! -nd 11!,-ir -z-ahs dpinoti%iiated that in equation, pr,)po,.;cd by Tnrk, which took into acct it ventilation rate. mixing factor, rwni %c4unic and pollutant genvration rme. rmild ~,r mM to accurate- ly predict the equilibrittin concentration of pollutant in an occupied space. lit thew WMLII~d st,ttings CO from cigarette and cigar ~niaking did not exceed the U.S. Federal Ambient Air Quality Stan- clards, whereas the predicted levels of suspe-dcd particuLate ma"er did exceed the maxiintim- It raust however be borne in mitid that the valuls which Bridge and-ACorn rueasured refer to hourly aver- ages whereas the Arn6icnt Air Quality Standard refers to average& over 24 hours. Data front the above studies show that I the arniount 4 tobacm smokc generated in a specific indoor environment and the average concentration can be calculated. Uss inforluation is availaWe on exposure levels noriti4lly presmt`iu different set- tinp stich as meeting roonis. restaumni-s and home-tnivironments. 2.8 MEASI.JiMMENT'OV. SMOKE'CONSTITUIENTS IN ENVIRUNMENTAL AIR AND IN MAN INCLUDIN'll, STUDIES. ON EXPOSURE EFFECTS ~.3.1 Gearral effeet jludie.% ;i~ml stuLhes have been perfor!Wd dic arnoull t of environmental to- Kirco was inea,ni-ed i,, ah zind thr effect on persons pi,--nt in th,- journ was also studied. A cla--sic. study was i-c- rxsrf4 Oil cussed irit section 3.2. J.hans,,on and Rnge 1965) studied thc ii-iiiating properties of cigarette 4~moke in roorn air under diffcreiit tenipciaturet, and humidities. Test persons %verr. placed in a chaniber into which sinuke %A,; fed fiont inachine smoked cigarettes. The ir- ritation was found to be largest in wayrn dry air. A slight increase in the relative hunddity decreased the subjective irrita- tion. A change in subjective perception from !!acceptable" to "unpleasant" was reported at about 4.7 mWnj3 parl"Lue matter for non-smokers and 9 nigims for smokem Eye irritatto 'n was noted it about 9 mg/in" and in this respect smokers and non-sutokers differed little. The authors cvneluded that a venti6tion rate of 12 mi~!hourjlcigarctte srooked was r"puired- h to avoid eye irritation and 50 m3, our/ cigarette smoked to avoid unplcw~ant odors for nou-smokers. Several - other studies involve "peri- ments where the concentration of en- %irortmental- tobacco snuoke, has been in, creased up.to very high levels in order to produce the desired effect. In tht. earlier reported exprrinwm -by. Harke (1970) studieswe~ ad _ _ . _ . .. 4).. rua-d.t: .. itnokm an d nob-smakeis. I I sii4erz and 7 tion-smokcri, were exposed,for 2 hours in a 170 ni" room (about 64 m3 or 24 X 24 feet). After' smoking' ;05 cigam"es without roani ventilation jequivalent to- a "ly consumption of 57 cigarettes lprr-' son), a CO lci.,ul of 30 ppin was recorded he=llb level irt'non-nnokers in- and t cxe&Kd from 0-9 to 2.1 When 107 th I"I "04 R E-' die 'I'I run end i Salo" colj~ 94 A! A161 it:. tk i. sun" I P 302058635 BATCo document for Province of BritiSh Columbia 19 April 1999 mtal to- ait and 1 w room %1*a~ Yc- is d;1- studied T smoie icratul,cs placed was " -IbJW :n warm relative e i-:ta- M. at" was rticulatc g/0 for at about liers and authors ,e of 12 required rall'hour/ ~pleasant experi- ,iof M& order to rrient by 717 on ke. 2 hourx ,or 24 V, alesit to rr"aded -kers in- ticn 107 13 cigarettes ivere smoked With room ven- tilation. th, CO Icvcl wab al>out 5 and the COHI) Ie%-el of non-smokers increased fruin 1.1 tt, I.G. The utine cxcrctiun of nicotitie ua-, about 100 times Inwer among non-smokem than synokvr, Harke and Bleichert 0972) aho re- ported on other physiological measure- ments on persons exposed iii the %ame room. 150 cigarettes were smoked in smoking machines during 30 minutes. Even under these extreme exposure con- ditions no effect was found on skin tem- perature, blood pressure or pulse rate in the exposed nom-3mokcrs. The experiments (Harke et al. 1972) further showed thal the concentration- of all smoke constituents analysed fell at the 'eftd. of smoking, the nxwt rApid being nicotine. )Vhen over 100 cigarettes were smoked during 2 hours ia a 170 m! wom, nicotine concentrations remained fairly cofistant over the collecting periods .30- 94 and 60-124 min. 11tem was almost arL equilibrititu betweca the amount of niewitic intioduced by fresh smoke and the amount lost by sedimentation and other processes, on to4veg sm;4!~ i _.PJFansPQA en aimraft wab undertak by the,.Frderal Aviaoon Administration and the Natiolial ;n3titutc for Qccilpational Saiqly and licalth JI 9711. Thu, purptKe of the study was to dete"nine the levvis, of eertain tobacco smoke corn*pounds in aircraft and to evaluate passengers7 subjective zintctions to tobacco smoke. CO, polycyclic amma- )q*dMrarbom Mid D"V Nyrrt' nWi- stired anu a questionnairr. WAS rUtUPIMCE1 by pn~ssengrrs on 18 -military and 8 domci-- tic fliglits. Illie munpling sites on the aircraft were ing zone of the seatcd passenger. hut ont- side tlit! turbulence '(au--cd by the over- seat ventilation system. The relative hu- taidity aboard the Aircraft, Was less illail 20 11c in all tests. In 72 samples from full)' loaded military ffigbis, 32 contained con- centrations of CO which were 2 ppm or less. Only one was 5 pprn. In the 14 do- mestir flight qrgmrnts, no valite tPachrd 5 ppm. Aldehydes and other volatile hydro- carbons could not be detected. Total par- ticulate matter, which includes tobacco smoke as well as ordinary dust ranged up to 0. 12 rnWnis. The- questionitaixe watt. completed by 3.296 passengers (3043 military and 253 on domestic flights) who were about equally divided betWeen smokers and non- smokem About 20 %, of the smokers and 60 % of the non-smQkcrs reported that they were annoyed by smoking in aircraft. Persons widi a. history of- respiratory diseases were ffiore annoyed both in the smtJdng and non-smoking group. Anderson and Dalhawn (1973) reported a audy in which tobacc 'o smoke cqmpo- nents were mmsured in a 80 ms room with iWit 6 air changt".1ficktor (icom surf6ce sormpondiag w_alapo4matc~i. ~O m~. ,Qr 18 x H 'feetl. 7 swokeis Smoked .37- 6 garcties,.9 small cigaysund 4 pipes over &6 120 utiuut test pvriQi;4 This would approximately corre,%pond to an hourly average consumption of 3.6 cigoerson which Js w#11 above dte.'valu~ of 1.3 re- ported by Bridg~. and ~V orn, (1972). 7-he nw,= c~o level in- the "M during the 120 minuics, -was 4.5 J)prn.'._-Ne,_ incren .it, won-, found in the Lutib val4c4s or the a no"a-mmokers present. The maxiinum amount of partictilat" was 13 rng/in~ -W'ith a uwan of 3.0 mKhn3 ana the max- lorated as near w p(Mible tothe hre.1th- ininiu-nicotine levO 0,.38 mg!T*. Most of 302058636 BATCo document for Province of British Columbia 19 April 1999 W-7 MONOW-0 7 14 thr test 'uhject% -pei ietired f-%-r irritation. fi-, l'-pultud hradad". and one had that Olt, nicotine do.,e ri-i%-ed by the iton-smokcr% ditritig the experiiiient wa~ equivnIent if) ab-t 1112 ig h-- 2.3.2 Siudis ii. CO A number of studies has focused on single compont-nts of environmental to- bacccp smAr. W~ihl (19991 trinchine smoked 15 cigaT% in a 6-5.6 m" sciled room (surface 25 m' or 13 x 15 feet) and measured the CO conce-ntration. fie calculated that 20 cigars had to be smoked to increw the concentration of CO to 156 ppm In order to investigate all accidental death dLw to CO poistning in- a garnge. Srch (1967) created an experiinqntal situa- ticth where 2 smokers and 2 non-SHICilkCAs were studied in a closed.car in a garage. 10 z4arctics were smoked d uring 60 ini n- utes. The CO tevel increased to about 60 ppm after 9-0 minutes and up to 80 after 60 minutes. The COHb in the non-smok- m incmAsed Froin 2-r/,c to 5 9~. Another experiment where tobacco ke %~-as studied inside vehicle, was Performed b~-' Harke ct al, C1974). A Ftimpean car wa pkil:W itt a wind usa. nel and the wmi1ation_-Wind -Iocities and unoke gcv~icration'wt:te varied. When 9 cWmTtrs - were 3uuA-W one afte die, odicr withoqt ventila6ou or i,vutside wind mov-ezvvent~ the dO concentration itt- creased to nvarly 110 ppm. 116 value agrees with those reported by Sith for .1 similir expezimevital kondition. When -vei%itatit-in -as present in the ca i_ if 1~ QP were 10 -ZU ppru. In.n follo%vin& stucty (Harke Ond Peters 1974) UO measurent(ni* were jA-rform'd in cars %vilen dri%-ing through traffic. 1 ~thcvv 2 of 4 pas-qt-tij~(- smoked 2 tiga- rettes each without car %.entilati- the mean CO ctincentmuoir iiirre.-d in 21.4 ppin. It deere-ed to h, ambient 2-3 minutes after rc,,ation id sitioking. Abqov-Pti,,,l ,f CO as al- ~tlvd.ed by Russel.l.ct al. (1973a. 21 lulmom wl~n! 78 minutes seated in a 43 nil un%,entilatcd nitokc-filled room ( 13 x 12 x 8 feet) BCfOl-C the %'~JUIAC- enteted the r-ni 30 cigarettes were left to hurn in asht'ays. During the experiment the 9 smokers smoked 32 cigarette- avid two r-igars and a further 18 cigarette -cre k-ft to burn on the ashtrays. The exposure was un~ plearafft to the test subjects. Ilic expostaiv conditions correspond to an approximative hourly mmumption of 9 cigawtim The average CO concentration. in the room was 10 ppin. The atran COlib level in the 12 non-smokem increwd fforh 1.6 to 2.6 %. The authors concluded that under the mtrrme -experimenw circunnunces,' the amount of CO ab-orbed by non- smokers ~vas about the same as if they had acti~eiy w1oked and inhaled I ciga. 'i 4 th,_ rette dur at period. represcot an exp6surc to etivitruturneniA tobacco sirnoke. whiEh will iw~ wrr,%,F real3ife can- ditions..'They thus represent one extreme of the dose-response relationship. The value 4A the t6tilft it that WrAn Ix- dem- onstrated that even urt&r these c6ndi-, tionst the COHb I.cycl Idue to cp~.Mn- mentail tobacco-swoke exposure-will onk, be vt~ moderately iuctcawd and retruain 106tv the maximum kmel of-4'% sugges- wA In a study &-signed to ml)rosent mom natural conditions the CO -level- -as th'.. 4' 6111: ce"', 1 i1.': LI 'M C.. W; Nul b. zz If PIV pr~ 302058637 BATCO document for Province of BritiSh Columbia 19 April 1999 1."Td tialfic. 2 ciga- Lion the I m I-A air Im-cl spent 78 8 feet). he room asht 111114 gars and tol-Irn wa ext, imimative -tes. The v rown l"'el in 1.6 to ~at under ~AsWkces, non- it they I ciga- tat an sullah ,e cW, 3. The -.tdi- ill only remaili 15 studied a~. all indicatol r,11 iobacco rnvirminit-ntal tobacco swoke I lortling pollution ill intercity T,Li7,:s (Sviff 19-141. rt al., 114iJ). Till! itll%l1tlll( ..ILIILI;d by 'File exlx6niental co-dttions Nvere de- thwe iton-smokers work ing in a laboratory -igned to ?06evr "wom-, cac- and "more area -is about 5 r," of that excroed by realistic worst case" situations and toe,.,[- F-moket, No information is given col - uate wlicilit:r the accepted occupatirnA cerninL, th, arno-i of t,A)Aeco MnOk~ ill I th"iold exposure ma.-ollitim w3l ex- the air. ceedvd. X!-T,rethents - perfornwd in Similar studies were performed by Catio a stationarN- bus with air circtilation and et al. (1970). Subjects %vere studied for fresh air introduction provided by a 3 days in a 66 ins large isolation cham- blower sytern. The rioa air ~cntil.,ticn ber. 157 cignrettm wetr-striollM through- system operating during normal. dri%ing out cacti day restilting in Ili ambient air conditiom was not funedoning. The %Tn- concentration of 32 jig nicotine/Ins and tilation was I air-change, every 4 minutes. a maximal CO value of-40 ppm. Non- Fa,. the "worst c-a--L" --ittl-ation a f.Uy_ smok Ts excreted between 25 and 63 jtg kaded bus was simulated, with all pas- nicotincl,,24 hours, the corresponding fig- sengers smoking, each smoking 50 %, of uers for the !tmokers-be-ing 1135-1.6 ing. the time. For the "mom realistic ,,,orst An ambient air nicotine concentration of case!I condition only khr-- rear 20 % of the 15-35 ttg~Mll re'.1ilted. in Ftn urinary excre- space was Provided- for srooken snJing tion of 22-70 jig~24 hours. - -who smoked 50 % oi the tirne. Ili the The resuft fronri the nicotine air enti- "worst case" situation the CO-h-vel at the (sentration in this study is different from driver's wat was 33 ppm and that in out- that of Anderson and Dalhamn ( 1973). side ambient air 7 ppm- This smoke level In (hat study the air concewmtion of caused subjective disconjort and irritation nicotine -%4ias reported-to be 0.377 mg/tris to 4 out of the 6. expo-M persons in the at CO co6centration of about - 5 ppm. bus. 11te "reallmic wom case" gave a CO The prr_vnt study with . a hi gher CO level of 18 ppui compared to the outside value (40 ppm) only -mcorded l_'-33 tig! Arribient air level of 13 ppin. No Wbjec- ni~. This value does neither agree with I live irritation was reported w-this co~,' that prescytted by Hurke et al. <1972). The latter results are contradictory to 0-51 mg-m$ at a CO concentrat; ofk of 64 those~reportcd by Andcrswi vW I)a1hamn ppm- (0713) Vh* fourid sabjr~ irriwibn st T1te..*t1Adb!&_ ow nicotinc ck-crefirin on a mean 00 level of 4.5 ppnL This Jiscie- non-smokers. exposed to environmental paucy can be eaplaituxi if part of the CO tobacco smoke have dexrlonstrated a de. prmw in the hus:was in m0ty due to tmuble LxFretion which is much lower exhaust furnes penemating -into the sta- than arnong stnakers. 'The. experimental' bus fr6m the varmunding air. tionav dala. uvTL obtainkd in &verim ctits with a . I rglativcly 1 igh e-\ ure and no'data afr- 2.3.3 Studici on nicotire available frolu more a 1sUc._rxp(Uurr t more In a study of inethodb of anMysiL -nicotine condidawL. A YaA wa~ miew-ured in non-iinwker.4 expowd to 302058638 BATCo document for Province of British Columbia 19 April 1999 16 2.4 STUDILS ON EXPO!~URE the isunibc-i- tol thilil-n it, tht- difforf-i;- EMT(, j S 1% 1 1 11OUT subgroups is very e4nall. certain trrnds MEASURXIMNJ OF TOBACCO could k, d,i.,,)-tratrd. An in-r-se Wa, SMOKE CONSTIFUENTS fow'd in ccrtai-ii re!'Ptiaturv sNImpinins. an)OFIK t-hil4ren frorn hoin-, where to- h- _j 2.4.1 Rripiratary sywpfims bacco was pre~,nt. The incid(mcc was re- Several studics deal %,ith the incidence lated to the amount of tobacco smoked. of tipper respiraton, Stwplonjs And -r- (MiH.,cii fluli. ;wIll" wilvir orljv Pipes -n, suir to environniental i(Amcco swoke. One or cigars were smakrd showrd no increase nu,~ such study was reponed by Cameron et al. in symptoms, of -i (1-969). 727 familics were intcrxie~-ed 'I he relation between environmental Sp. by telephone and (piestiourd abutit s%nip- tof)a(co smoke and pulmonary disease was at", toms of acute ilitiess and smoking habits. also studied by Colley- (1974). Thesc, re- ojx,1 In children aged 16 or less the pm-alence sults air discussed in wetion 3.5. of respiratory illnen was found to be in- Harlap nnd Da%ics (1974) published creased in those from homes wherc- the a ftTott relating the hosp 'ital admission parents smoked - 5.9 f~ conip.-irrd skith rate of infants to mternal smoking. They sm"'. 3.1 % in those where tobacco smoke was studied the hospital rx-cords of 10.762 in- not.repor(ed to he prestrit- Thr numbers fants in a Jerusalem population 1965-,69. IRUI -W: were however very symil - the 13tter The smoking hzid)its of -the mothers. wete clin;f givup containing only 9 persons. 1%hen evaluatind in a personal interview - 9.2 % testit the material was reduced to contain only of the modiers were smokers and 7.4 % At: children aged 9 or less or 5 or less. no had given tip smoking earlier. A signif- eye. statistically sigiiificant diffetrntes ,-ere icautly highcr admLsisiort, rate was found ickind bettmen tobarco sukoke lu.id smoke- for bronchitis and pneumonia among Son! free enviromments.- children whose mothers sm,okcA. A dose. Shy -et al. 41970) repdrtcd on the inei- response rel.atiodiJiip %a:,as present foS the of $y dcnce of-acute respiratory illness during number of cigaTtws smoke& No sigmit~ Cowl, one winter in 871 familit, living in arras ifant incre-4.se was found for thq, incidence ' with difft-rr~n! levels of 11;r.pog~lioft. -nic respirstafy tract infection. In a ~f PPM jIluca. raw-Aocirw diad- fp".j to aw" authors toond 'that ~e 1j!gjicr'in.the pofiuted area, but -no -1he increwd' a0missiou rate Ltir hmnehitis Forrqlatioll could ~be fowd between the , or pneurnorna Was not present dtiri-go!~ n's. 'we ah d -their, "0; cwl~rV (61 5 n-krriffiti-of life, tw--r after the fir st thc~ A. smoking habits. ti~rthday. -Nenuan-Taylor at;d Dickinson J1972) The differen6e in admission rate for Whir evaluated the (rcclurucy of.mp0Wry_in-. bronchitis and i7neximonia. 'for chil6ren tobac- yvq~r old untrants i the fections it) f k~ 9 5 with smpkirtg and uon-smokiag mothers till County Priuiary..-Schook iu St. 'Albarts was smaner ;Iutn thatdue Act SUCW clhss ~ntbncl. M h .1 _ re expkmintr the presence- of, a questiciiinai A' 4nifican~ly. incrt-ased '"41n6sioll fre- upper resl .)irAi.my infectiong as wc1l.-as the' queucy due tn jujurws was alsu, itoted'6' smoking habifs of ghc fAmily. Uthough the iirst born infant of fatWlirs where the ents 302058639 BATCO document for Province of British Columbia 19 April 1999 the d4f- ertain ir-d, r) Olfrt- I- J-7 11' .I[Co li-k, d. onI% P.J.- -d no Inc I( F nv.VI.M?1nf,? ry di . was 'I ese re- M, 4) published "I adaiii.n mking. They ,f 10.- 71512 in- ion 1965-.69. hers wert: icur - 9.2 7c s and 7.4 A signif- was fcu.d arwrig A ed. A dosc- t f0t the No signif- Y,~_ fun(T-It h at brolich during the fcr th,-' fiist rate for ug rn4thcrs social clss infants). izion, fVC- noted for 0 law smoked. 'nw clinical rvinpi.rn,- Reicl,, li.6.g ho,,-- ve,y ).- lit this wdy I). ac- typical aflei-gi, On VX1.- T~ -,ult -I, given of the iniuLit'. h-hif. nf --I agent, mch it, LoW nd Ldit or other jticinhc-r~ of the house- drugs, th-c- patients d-tlop,-d n.-al, or- h.ld. cular and broncluil ,ft,r C.pa- sure to -,akc,. Mi", th, ~ourcc 2.4.2 11)-p-ensirivity of tobarro expo%urt- i%-a, reinovt!d, the Tht: rulation betwt-,rt exixsure w crivirou- patients re~-,rtvd disapl.-amn- nf the -mental tob-co -oke and the prcsc!ncc symptorns witlwii 15-V -rinuici.. Sciitch of allvrgic ructlom h~ been i--tigated. test, for tobcco gave weak skin reactions, Sp- (1968) t;ttjdird two s~uuplcs of %-hercas intraderrmal testing gave responscs atopic iiou-sujokers, all of %vhr)m devel- in all Ntir-nts tc~ted. Passive Iransf" oWd symptouis wlit:ii -posed to tobacco from 4 patients chosen at randorn gave stroke. ne first &nuple consisted of pati- positive rivac6ous. Foll-ing de-vitisa- cuts with allergic di~easc%s, such as nasal tion the impro-ment livas reported as allergy, a-sthnia and alk-rgic headache. 'Pie "excellent" in 10 -F-cs and, "falie' in the second sample waa5 dmawrs from profc~ remaining G. simml univenity staff. la addition to Blue (1970) reported wic caw of asth- qucstio"aire dita; the allcrgic group had ma due to cigarette tobacco allergy. Thr clinical examinations including scratch patient was a heavy stuoker who suffered testing- with tobacco extract. from 1"tient asthma attacks, which were About 70 % of each sarrqJl~! reported worse during the winter monthIL After eye irritation on exposure to tobacco giving up smoking the asthjuatic smokc% Nam) syttiptoms, hcadachc, cough, tom-, disappeared. sore throat and nausea were triore corn- Another allergic case -u reported by mon in the allergic group. The frequency Cohnia and De Gara. (1965) who de- 44 symptoms in this group was 15-46 %, scribed a-case of dcrutatitis due to to- compared with 8 -36 % for the rim-al- bacco smoke- A vesiculpbullous dcrinatiti, lergic group. 21 of thr 191 alk-rgic patients de-loped on the hands- of the patient g- a positive reaction to the scratch when cigarette or pipe tobacco was test with tobacco. extract, but none of smoked. This disapi~_" following ccs~ t,no showed an especially'.1vire (he-- rati go of ssridkirsp,~ reac-OWLIQ lffiaki~. ..Kincc no J;iLicnt; irom, Hypersensitivity to tobacco, sapoke was the aergic group gave a history of non- also studiLd by Savci (1970L in 8 non- respratory. allergic syrriptorus. swh~ as smqk=.:"4io had str6ng aftergic b"- itchiM or sLu eru4Aioh afterexpostire to triTnediatc up- ground and who reported i tobatwo smoke, the author concluded that per respiritory discoinfort after being ex- the r~~potiw to coluicco smoke was prob- posed to cigarette snvAe. He (ound tbat ably-not allergic- lie suRginted that part an in the addition of cigam~re,sntoke to , of the ropilisc rnight be.attributabk to. , 'vitro culture of the subjects' lymphocytia. an inctcawd.6carwr*tio-oif vitf-- Zimman (I 97OL:itudied 11; ~vlpic prV w-d tttyin, -idute as comixired to a control tmts in wboru exlx~urr to tobacco smoke cul ure. In 92 contircil 1ruients witIlIout -4 a 302058640 BATOD document for Province of British Columbia 19 April 1999 4- V- I *41 .k 514 kinpli,x-,te latim, the .rmawd thy- not The Iif- upt;4, 6Y ru-n- -old pwb.bly b, tirih.t,d t,, cxpos..-C. d": ,C11 3n tO Thip stuttv. - oil the po-1 '.- allergenic the exl.,cs urr.. FK- action ,f to~ ..- snluk, I- Brit a c.- Th~ finding, are ont-di,tory to thos,! fusing 1?.ttt,- -1-he fact L-, thew i- ieporIL-d by llat-Le and B16illit!tt i19721 that toh?,- extract is who wem not able-to rL~curd uly L!ffcctF Iv ahergenic ls~ sonkt,timcs i~,:n taken to on blood pres-re --r Ttl%c rate under ex- yr-.'n thi, -6;orco mist)ke i. also alJcr- posure conditions whirh were even 1nom M genic. No -~-inientit vvidi.-.ce has bmit extreme. tio presented to ~-ipport this h%i~-thesis. Cameron (1972) also studied children's me rractiorts to enrimnmental tobacco stitokc. cc 2.4.3 Oth, ..-i,ai A sample of 1710 children aged 7-15 . Other effecu; of environmrntal tobacco were asked whe-ther they liked tobacco smok-42 cxpoLum. have bma investigated. smoke, whether they developed symptoms fro L-qu-,-te et aJ. 1 ,1970) --d the acute on exposure to it and what their attitude rel effects of cigarette.smolse on children. 40 was to smoking by their t=ents and to is children %%ib a mean age of ~kft rars were --smnking in gewt-ral- AmotiK the childiva exposed to s-zky and s-Le-frec atmo- aged 7-12 yem, 76 % reported that they iib spheres ,iikai. Lmironnientn!z-hambernwa- disliked environmental tobacco smoke a ba suring 12 x 7 x 7 feet (ca. 9 m3) without "little bit" to "a whole lot". 21 (74o m- Sy3 %Tntilation. S children wt, 5tudird at a portcd indifference and 3 % said that 11. time. Whik in tht~chandwr the children thicy enjoyed it., In the 1.3-15 year age STi watched rno~:z films the harmful group, 58 rA d6liked it and 7 fA said they cv effects at smoking. After 35 minutes dur- enjoyed iL 47 % of the children reported m ing which tizne 6 ciga'n-tu- wcxc stuolrd eye irritation, I I c1b naud iftitmion, 12 % . dc by two smolers Aso presen; in the cham- headache and 37 9b cough. Thaw trou- W -t tt~e aM b1cod ber, n-wasure-zents, of hear ble, nausea and other symptoms were m- IJa Pressum werr taken. parted by 5-101A. Reported vymptorri% sh The non-moking emironment pro- ' were about twice as frequent among chil- in d -ne increase ill the Lcrt rate and M ul Whru ait"I'l, any ns ntal ntrtk-,, it nt evant it, cco ternati; 1 vedL m idenre ental rtaken orkJxl red.. op g. dreb who disliked tObRCI-ID wa sr-to!ic +A-4 -Wadkkg~s-. - Xhe fi"njo of thk sqdy. ar~p~ Oifficidt ,hr- t- even pill, very wt-. For a i;'- he. sm F.~. , cml" 4-t- f" r 6 i - the experiment was perforated without *a evaluate, as the meflio& were different tabacco sritake exputiure a tignificant iu- frosix those gtjwratly wed to assm an- REFM;: ~crra" iiN i~rsti t9tt! A"d hitioa-preadm ' auVwxv due w various-enVirvornental, pot Andw was initi;W recoided. As. the 5th ineasur- lutants (Lin&all and Radford 19'72). inent after'30 1uinut,~,rxpo,,urc thL blood pressure, in the.,moking envimi)ment -m 2'-5 CONCLUSION found to L-w slightly higfr--r than in dw The review of the literature on C"Iron- stooke-frrt conditicm, but There Was no nwrital tobacco unoke -&monstratrs that Padw. I. i.-h -.aLli.v diffeivnces 'flic nunthtr of 1"tblit~a&vi draling-whit - - r-d )werr smAll (4-5 rim blood pm- A the matter is lairiy large. A variety sam and (i lwats!mia). arid the statistical enviropinents has been studied and wra- L: 302058641 BATCO document for Province of BritiSh Columbia 19 April 1999 -1. Ile dif. luit we as to fty to ihosc ,ell ( 1972) many vff~cts undef ex- even rnore' ~Cco We. Wd 7-15 4 tobacco syruptoms ~ir attitude a rf. , to r! CL -C" that th,-y smoke a ~21 r/r re- said that year age said dtcy rTorted Lori, 12 [oat troul WCM' re- I-Mpg diffittilt. different 34" an - nta, ';01- znviron- ms that Ig with ricty of SurellicriLs, Of. dificit-ni Cf%V?.1lW-tT4- havc (1~7.e) S~ I liand TM,a- hvc-n p,ifoijiwd. Expo,are eff,-ct,; have S-ke: Child,W,.t Rvacri-. Th, la,-.1 been stndi,d with and withto imidta- of S,h,-,,l 11-11h 42 ~5): 284. neous ctntrol mid measurement of the Carnemn, P., Kmtin, J. S.. Z~ks. .1. M., Wolfe, - H., Tighc-, G., ()wlctt. B., St~kr-r. X. ex)iosurc level. .. d Wirimn, J. ( 1969! 'ri,,: i 1-1t), of s ... ok-- When -in attenipt is made to use the r%' and Nori-Smokem' Chiklien. 1--a1 ot available iiiforina6on to evaluate the All, 'igy 43. 336-341. rl~r-terpmfzc asp-- difficuitws anse. C.,,,,,, J.X., Uawhn. J,, BMO~, R.. D a,. C., Many studies rcprt:_,cat exposure condi- Viala, A. and GtiMernie, R. *1970) DvIer- tions where the concentration of environ- inati.., of Ni-tine b~ G.-Pl-, Chron- mgraphy. 11. Applk.ti-, im Frewi,). An- mental tooacco swoke grvatlv cm-cuds con- n.les Pharniarrutiques Fr-jaim, 28(11): centrations that can be empected to pre. 633-640. vail even briefly in real life situations. Cfley, J. R. T. (197-4) Respiem"ry Symptoms Inf-rination concerning the lower and in Children and Parental Smoking and f-mu hridth point of vimy more Phl-_= firii. Afed. 2. 20-1- 205. relevant Patti of the dow-respori~se scale Corviia, F. E. atut rk-Cam, P. F. ~,t%5) 41,regi- is very inconipletc. culobullons Derm3titi. from Tobacco Smoke. For a satisfactory evaluation of the pos- - - journal of th* American Aledirat Amoria- sibJe health hazards of envirorimental to- tion 193 (5): 391-392. bacco sutoke it is them-fore desirable to Feder4l Miation Admini%traticya, Deparuncal, . of Transportation 4nd die National Insti-tute systematically look into all parameters in. for Occupational Safety and Health (1971) volved, namely the vxij.4are agent, "po- .Health JV%pcct. of - 5-okinz in Tra-port sure conditi-ns, effect mechanisms and Aircraft (Report). evidence for effects at mlistic cairon- C"'linma, V. (1964.1 3,4-Benrprww. De--tex, zriental conditions. This was the task un- roination in the Sivoky Atnimphere. of Social - Rona d Rea-rann. A Contri- an dertaken by the participants, of th -mimsness of butim to the Problem of the N Thc different documents PrL- . socalled ilau;v. Smoking. Neopiaima I 1 (5): pared for the Workshop and the Work- 465-468. shop resulus air presented in the fall w- Harke, ll.-P. (1970) The PnA-k- of- -Pamive 8 xnaking". Minchiner Afedii*iwhe 1Vo0c!i7 1119- _ ttT rig,,; :329~2544. . " :- . Harked IL P; Raam A., rrahin, 6, Ntert, If. "d Sdtultz, U%. (1974) Relation batwea6 rimttituitnts Ajid nuaiber..Of Mi&M cigAretta, 144c and room. voJu"w (in Get- Andrion, G. &.d Dgih.mn, (19731 11-tth man). Int. Atih. Arbcit,-wd. 29, 32 3-339. risks d.e to pa~~4- uno~ing '~in Stwji~jj). Harke. 11. P. and Nelchimn, A., (1972) On ilie Liikotlid., 70: 2833~2836. ~problern of pu~xive amoldng (in Gennan). Illue,'j. A. (1970) 0,w.~uc Athma aid T- lat. A,eh. A,beitmcd.. 29. 312-4M. bac 'co AlfeW. Awn.h c4 AllerRy 28 6' Harke, H. P., and Dvnkr,.'D..(J.974) Juvestinatiobt, ot-the--Carban' Uum&%; Nridii, %L. e-i. - bution to. the As&t%mmat of Enpourr uf (in Gennim). Are*. Arbz*jnu'(.' 33: .'in Non-Szriokcrs to Ali- Vallwimt froin Cisar- ettF and'Cigar Imooke iu 0~capied Space,. It. P. and -)!"eis, H., f 1974) The lin- 1 mriromme-fttal Reitarch 3 (2):- M2-20% Poo unlre of S1110king. for We' Cd' Ctinceq- C. 4 r 302058642 BATCO document for Province of British Columbia 19 April '1999 20 U.1i.- in Lla., "t 'I raffi. (in G-U). hm, Nf-xidr fco., R- Air P.11-d by A,,h. 4,b, ~. --,..d. 33: i. 1.4.- S.~Ac. The I.-cet 1: 571, M,!,~P, S. utl I-"- , A. M. (V-74) Infant Sa-1. If. (1970) Clini-I er 0. -- S ~ke. A"I""' ~f 1.6-1 1; 529-- Health 21 (21: 146-14M. Har-, 11. -d E. , 1957) T- Skiff, H. E. (1973) W i.di ..... . f b-. S,-k,- ir Tm-p-w- ,hirle% eigmte ,-d p.11.6- le-6 in i.w,6,y "'d lligb-q AJ-i~,i ...... i., US Archiv fii, ilyg- ..d &A r. loj~r 141 ' D,pr-., of Trartspo-ti.. (Report), (5, 383-400. , ci -:~ . R H U Z , i 1-11. P-l"- sh C P M J . . . . - n q~ . , ., ., , y, Ck-d SI.- 11-Ith Per- (1970) Th~ Chwonnog. Sch-I Child-, x "r-ti- 117-1'2-2. Study: Effects of caunmunity exp-e to Horning, ~'. C., Hom-q, M. G., Czmll, D. I., nitrogen dioxide, 11 inciduict! of -tr Still-JI, R. N. L.,d D,idk, 1. (1',73) Ni- -pirawry illn- 1. Ai, Poll. C-e. .4n. 20- tin, in S..k-., N.n-S,-k- aFjd R-n- 582 588. Air. Lift Sci-- 13 (10): 1331-1346. Speer, F. (19CA) Tb... -d the Non-S-ke, job.-, C. R. nod R..g,, 11. (1%5) Acute A Study of Subjcai~ Symptom, -4 W4- irritation effcct~ of tobaeco ~ke in the ol Environmental Health 16 (3): 443446. rao., Urtuapl~ (in Swedkla). Nordijk Srch, M. (19G7) On the import-tce of cub- II)g. TidA,ill 44 41-5D. -noxid. due t. cig-tt. -king in Lindvall, 1'. and F~dford, F.. P. (1973) (in G-) D,.I,,Ac Z. Gtrrichll. AW. W. k, M-rernent efAn-.-j-ancc Me -~ Exwsure GO: 80 -80. , to EnviroarnentA Factors. F-. Rcscarch %VaM, F. (1999) ILber den Gehalt de, TAk- VC, 4 6: 1-36. .-h- .. K.Id-ox)d. PINS- Arch S. Luquette, A. J., I.andwa, C. W. and %ferki, D. Pkpil. 78: 262-285. J. (1970) ~ S-: hmt!dijtc EffccU or a WHO (1972) Air Quality Ciii-itt and Guido S-Mrig r-i-n, .. Child- of Elc-' for Urban Air Pollutant~ Md. flealth Org. -t-Y Shool Aae. Journal 4 &1-1 7,,h. R". S.-r. 506, p~ 1-35. Malfit 40 (10): 533-53G. Ynwu, c. r. (1955) VemiLatim Requite- N--T.)i-, W.' ..d Dicki.-a, V ' A- -i. for Cigarette Smake. ASRIIAE T-- - ~ (1`972) Dangw~ f- CliiW,- i. Smiting actioni Q: !~Z7-230. ~ 7 4 Fu.ili- C.-n-usj, Aldici., 128 (l)- Z.s-,,. B. M. (1970) Tob.- Semitivity, in ~ 11 0 32-33. d. AU&g;c P.,i~n, A.-I, .1 A14-,Sy 29: , H.. C41r, P. M. ~&ud _371-377- tM) Ab~-Vti.- by f C- Of 302058643 BATCo document for Province of British Columbia 19 April 1999 -r l'olluit'd by 1 : 5 7 6 579. nensitivity to indic~At- of ,18 in int,cn~ ni,b-ati-, U's ~.oc,l Child,- . CxPW1E_*T to Ice Wcute C.W. A- 20: Non-Sokcr. $_,*~, 1-01ft- 3),. 446. ~~cej c.rbon ~jking in can ,~rhtl. Md. It dcx I:abak- ,crj Arch gas ;~L and Guidm H.11h Qg- wm Acquir- WIJET,m- riensitivity 1. 28. 3. Work shop Documents 3.1 Introduction In the following sections the-backgrousid material for the workshop discussions is presented. Initially technical emposure aspects will be di,cumcd in two papers folio-rd by it t*vie~ of bir-lozical far-tots relevant for the inhalation and deposition of environmental tobacco unok-c. Epidern- iot9gical techniques to detect exposure cf- fects in the p6pulaoicri, will then -bw re- viewed followed by an evaluation of two specific aspects; allergic reactions and the exposure to lorw concentrations of caeban inonoxide. Tbe final paper presents a broad review of diffewrit biological r-f- fects of tobacco snioke which acted as a general sourm of infonnation throughout tbe.worksitop. 3.2 -C.haracteristics of Tobacco.. Sidestream Smoke Distribution in Occupied-Space's MORTON CORN 13.2.1. INTRODUCTION the chei" cornixmitiort ol"tobaced'and Tht- ptwpn*~- -4 this - preseniadon 4s, to toluteco, wrieke. 4 to,* dixuswd . 4 cOn. rwTsvilm-Wr6i t.,jij1..vLwJ 4 LYTZ:, 1; -dilLii ette sWestream snr-*c after emission it) However, an effort-is inade here to cx- lite air of occupicd +um The discussion tract those data whith remAl components Q.Uuwt pmoibty present .evciv ;%,, tuajor of tobacco stnuW which have been con- portion c4 all,.tLit is 4iown reLtive to siderud by linvestiptors in studying dw 302058644 BATCo document for Province of British Columbia 19 April 1999 22 A Fig-, 1. P.,61v S,;,- Di:,-,i- hwi- of sid-I.,am UK.-I.~ 0 30- swoke 1&6th and Lk-nid.j. o 0 0 0 0 0 o and pa r, COM- a: to dircci 0 woul'i 5- porny 0 frre "i .06 .00 Ul ID2 0.1 0.9 0.6 Q6 I W 20 -," f 6 PART CLE DIAMETER- MICRONS; o . k exposure of individuals in passive muoking important function of highlighting studies wm Lt or which shoitid 6~- of concern in any which rentain to be performed if we are from future studies. The lack of data stems to get a finn grasp on this subject. The fr6iii the vieve that usItil no%,. becausc of die compkxity of these types of inves- tigations, it has been considered feasible 3-2.2. PARTICULATE MATTER IN -and. suffirient to -trace" the vapor and' CIGARETTE SMOKE particulate pliasc~ of tobacco unoke by The particulate phase of cigawffe side- Whet, - nionitoritig a tracer cornpound which was strea"i smoke is composed of both solid asstimed to bear a siffq)le-relationsWp to, - particles and ~roplets._Xvults reported the other gascous or particulAte phasc through -approximately 1966 were. suin- compounds in the sidestrearn satol- in marized by Wynder ai~d Flofftinui (19G7 Coat 6 ccupicd spates. The mmt widely rited work on particle_ proxin~ A*Wier piirpow of this, disc~t_ is,, in - cigar'PA!~ -sawk-C iizc and-couccuLtatiw licl c - to isolate those ,ariables aLsociated with is that by Keith and Derrick (060). A - have design of -occupied space,,., including se- "conifuge" was used to centrifuga -11y class- ran& ieniilatioa. qs- iA, p.~ajq,6-, -An lwirumental i4:chnIqtr. -tems, in order to W their effcct, eidier Icle size dis- still considered valid. A part; nus dit-ovictically or froncreported itivestiga- b tribution fhvy determined for _%idestfram I - i Fi i h -pi& t e s shown acco cigarette smoke n tionson the emreqtrations a to gure s 0.15 ~,ic 3 inokc Compounds in mlctipicd. T-ace&-lt modal sive i ran aeiudyRantic hot f 'I gfcin3. Largr Ad be recogni7ed that the amount of size based on density 0 I limited. 1he"re- uun-J)c o _pnrti6-% down to 0A 1 )8 mirrdrt .-A fore.. a large part 4.rn)~ prewittation Tnust were observed. ~k 20 power alxw kron-tic. HIM- be RX-rulative. It may uill,,scrve the n,cKt ob~wtkvc und a 25 power compet M'-Xtrd 302058645 BATCo document for Province of BritiSh Columbia 19 April 1999 Sim. oi~t- - Og-- 4"d )),,okk, IN tte side- 1 both solid--. t is re 4 werw (1067). -.on particle r"'tte satokc 960). A - 0 W 1,1 technique le size dis- -Sidriptiram ,urr 1;- the ~rodynantiic ftil. Large or ting si"ft I if we are It. vvc-rr -~d to cotint drrx)siird 1).ir- ticles with a dark-fit,41 lechni(ple. tion ;ajw, -, roll,, tiog Oides werr estab- lishvd ljy calibration w i(IL test awt-ols in- cludin lit-, paraffiii %vax g poi, - Ond dioctyl philialate. Thr deposition ri7v lower limit va, about 0.01 t ... 1. 1( is A- most certain th4t large numbers of smaller particles were present v%ijirh were not rmintcd by this teclinique. However, util- ization of an clectron miernscope for direct observation of coMccied saixaplc would introduce artifacts., stich as eva- poration of particles or material from par- ticles. Keith and Derrick estimated that free burning produces particle: at a rate of 6.3 X 10* per second. The thodal si2e of majustreani -smoke was larger than sidestrearn smoke, ranging from 0.20-0.23 tim for different blends. 'nic coagulation constant K was approx- itaitely 3.4 X (Fq. 1). _~N = - KNI (1) dt Where: N = particle number per wt- t = time, see K = ioagulation constant, ml,'gec CoaguLuion leads to a modal shift of ap- proxiniately.0.3 pm in four miu'utes; par- ticle shifts with longer i;vaO6+;ezz ti,-es hive r..~. i-en reported. The particle size range is extended approxintat.ely 0.7 Wn to the IarW sizes during' four ininntrs.' Thus~ the -partides am-, agglonwra~rtg rapidly and their size is sbiftlhg upwards ~rapidly, The coagulation constant %milki be eipmted to be further enhanced in att accupittl spacc. which is genendly wk- sociated with air *+witivs occurs. Howm,er. at the -anie tidw that the effec- 23 five cong,11"tioil Con."mit file itataber concentration 4ecrra- dne to dilution and it i% difficult if, -trapolatc to the actual raw of coagulitiri-, of thesw partirles after several mitnitc~ if, urcttpicd Npaes. It is known-that the partich-, are high- ly charged. Oh~ervalioit of cite particles in the clec(ron microscope rc,va6 par- ticle chains, a characteristic pa-m sociated u.'411 aerosols canden" frorn supersaturated vapor at high temper- atures. The possible biological effects of clectri- cally charged paiiicles in i(A)a0co smoke has been broaclited by Ringdon (1-461), who estivinted a mainstream generation of approximately 2 x 10" ions/mi. a con- rentration 315OUL 1000 times that preberst in the air of indoor eccupied spncc,. The panicle size of the sidc.~trcata smoke plac" essentially the total disper- sion in what is commonly referrud to as the "respirable particle size range" ( M-4), particles whU will penetrate to the nart- cilived portion of the humall,respiraffoy tfact. There will be losses along the Calke respiratory tract, particularly at bifurca- tions. A question which requires ~orrie aps-em is related to the hy&Trcojair~ of.-,Ihc cigamte SMoke and whether there is. apprecialik growth as theacm%cil travems the.h4uma rViratory -traet- 'Merr are statements in the Uterature that the material is hygr- oicopic but the extent ojHsygroscopicity is not - delineated aiW the additional P~r A;spersitycreated by growth due to' ruois,- turels not known. -W~rmt. dPc%ctaa-j-rrh ;u -our labo. jF at6r" (Oberg 1973) sugg,-ts that the Mason growth equation (I q0) is a reli- able predictor of sufruric sicid aerosol 302058646 BATCo doCumentior ProVince of BritiSh Columbia jq April `1999 t 24 gm,th ill litlow! zics ul, to 99 7". in the air of a rwwl. '-,,ni(- ol tlj,~ tent- 0i gr"-Itll Of TMAW IM11111- ill tile! particles mwill rollidt: -...:rh largev, p;j-ticlr% Only 6. 1~ hii-nan respirator. traci i, a wore cornpli- to be rrinmed by st-Emelilation i~, tile . P",uld, cated rnatwr ai;,' requires fimher in%c,- floor. hy inipactioii u., stirfacvs; wtr.- will UlAte tig3tion to more r0iably detcnnitic sited, diffuse to t1w wall -..herv they ,,ai bc in tile 01 Wposition h- ~tli%~Livc nieth-ds. Upon retained. Othcrs wiii ~t itilmled lj~: r-cell- (Sledil,.1 inlialalion it i~ seenerally a-urned that alvd art a-vrned pall's. 70 7c of Illf- fit alkt-iic~_ approximait-ly 10 ~-f, of smoke particles in to be removed in thin manner. It i, not stcro!, , :, nuainstrearn sw,'- are dcp--t-I ill the known to what clegme panicles from. side- pc Ild'. ~. respiratory tr-ac! and tile rentainder are strearn smoke partilipaw in chrm--) irt-.- and (1kii, exhaled. Becaai~ of the shift to higher actions while suspeloc:td in tile air of oc- COMIN,-, sim, a larger fraction. of inhaled dillited cupied spaces- Tile aving studies th..t have ethers. sidestrrant si-az;k~ partir" shotild be de- been performed on the dijwrsc phase of miscell.n. tobacco smoke been far periods of orgPinic It should IA~ recoghi:7,M iltat the par- minutes after getierAtion and not for peri- as c-.d`i-,, ticle %ize and c1hrmical composition of the ods up to one hour or rhoro-, a- period of disperse pha_~c uf sidestreayn smoke can time relevant to e.Kposure to environ- be gft-atly aittred. when different. smok- mental tobacco sn-,okc. eous ing mpchillc~ zissocialed uith diffewril Particles contributed to tile background tile pill, puff it'ines znd rRm-s of puffing are uti- particle population ))-y cigar siawke con- am thc. ` lized- However. in all thme cases the tain not only carl-n particjcs with ad- and c.: -4 acrxsol product is compmed of particles sortwd condensed organic compounds, but ans%vH' all below approxtruately 3 pm at-m- a number of the products of combustion centrjO dynamic ,equi~.-zlent diameter- and is thus of crystalline and optically js-ofopic in- occupw ' sell toWly T-_-7~ralait. The variations cited organic materials used ill the manufacture ,~ with ti ? are believed to be produ".d by thejern- of reconstituted too-, icro'she6s. Thus~ dia- oz~ pal' perature vaC-.1tions at die cigarette lip. tont, fragments have been, identifk-d in The varial)k.~ ax%ociatcd %%ith the mwk- cigar sinoke (Langer 1971 an&n): =rp -pRff *olwuic, puff,dura: collipc., tiou, and puff frequency. ff we- add. to this the prewrictt-of various tylw4 of fil- 3.2.3. THE VAPOR P14ASF OF -z ters adid aiffe"rit tobuccoa~ the.sim TOBACCO SMOKE data e .., Composition ---Xiadolls of tobacco. %tooke Tetnp'era't urm - %lip ~-(p hAve. bert! of are anders4,,nd&blc. ' measured in the outer ring of a cigamte and r r Once entitted, the disperse phase of (Egerton ct v4. 1%3). SU6imatn syrinke *is ne tobaeco snu)ke is in ihe air of occupied Icaviiig the rigavruq can mach 400'C but coultV ~vh7,e, depending on tile partictkiar is at 100'C si-.k cm, (min the bulming -"-4 area.- their will bt- from 65 cigarette (Nrtiruh 1966). 'Dw degree to 7 t of nautral and lanum, to -180 p, lx,- 'r it;terzirt dur-- genic suspriKkQ particulate matter prc3- ing the 'cooling of Sidizs1rearn 'Map lun, ent. The Ad,-4reata -Aiw4ic will lic mixed not been repomd. but tnAny of the vapor .s 'mpi~l 4- wlh Pe" ollicr sit tied particulaw w on-. lilch could have bLeti initaled are c phrl.." anatter because of iticAurbitlorive pi.-scrit densmi oil die pagd,culate ex- but 302058647 BATCo document for Province of BritiSh Columbia 19 April 1999 25 :ic s-inoke ivat of conclopaiiork and interaction van any minor constituents of mainstream particles ostly be p-tulatt-cl on the b;"is of royn- quinke are Its prm-aleni in sidvsti-vain to I he ig.,mite parne- vnoke. One nuportmit-excelinon Is Un- -orne will ulate rwittr. The number of conilKninds nionia, att important constituctit of side- will bc in the vapor particle phi~t%e exct:edi 1200 stream smoke. by ocxu- (Stedrnan 1968). These luclude alkanes, It is nect-,iry to de(ennine the extent assorned alk,lies, all,-s, aromatic hydnwaii~ons. to whicb thrtr compomids zire clihited It is not steroles and xYgenated koprvnoid com- after emissioti and before Lwing Inhaled by frorn, srde- pounds, RIL01101%, esters, aldchycle-s; ketones human receploni in clos.,- pmximilly to the --mical re- and quinon", t6iric cyclir ethers, sulfur source of sidestreant sinoke. Their is a air of oc- compounds. acids, phenols and pher~olic large array of situations to be considered, thatA~Lv - ethers, a1ah,ids, and oth,-r hmer and from the penmlix directly downwind of the phlaf miscellancow; components. including in- smoker to the individual inhaling well x-riods of organic constituents (irate metals such inixed uid highly diluted Smoke. for peri- -e as cadmium and nickel) and radioacti% Seforr examining these dilution rrwcha- period of conqituents (Stedinan 1968). nisrns~ it is im-cim&iry to review the subject environ- Perhaps the most widely studied gas- of indoor particulate air poflution in. order- cous pollutants which da not.coudense on to place - In ". pmtivr the contribution d. the particulate matter as cooling occurs of tobacco smoke. tokc con- arc tL nitrozen oxides. carbon monoxide with ad- and carbon dioxide. The question to be ,un&. but enswerM it .,hat are the changes in con- !V.2.4. INDOOR VARTICUL.NTE =bUstion centrations of these gases with dilution. in POLLUMON ~t,pic in- occupied sparcs,and-what changes occur, There is a %-ast literature of air pollution nufacture with time, to those compounds condensed measurements outdoon, but relatively few rhus, dia- on pattielm? studies have been. devoted to pollution ,itified in Table -1 is a summary of sidestrearn which enters or originates in buil4ings and mainstream smoke characteristlcs,,~md '!(Bertsm et al..1972). notwithstanding the. composition. as prepared b~ Hoegg (1972) extemive reports of occupational exposure frorn several sDurces in the scientific titer- of workers to Airbome toxic agents, This ature. I hAve --added carbon monoxide is spi7rNing WW6c inost wirban residents data to the tawc..'7111L 1UNA-Ing _variable& ~4*ffd --d* gtr~0,4 fiWrt. if ih-:r dn~ in- ,avc becq of ptiff volume a"4 frequency, butt length doors. It seems appropriate at this time cigarette and tobacco znolsl~ure were staudardized, to. briefly, summarize our- knowlcdgc~ of im smoke noted -to obtain, 11mir-d4tia, Me list pi"-cicuW-v:-pf4iutihit ifisitk~bidtdibgs: 00-C tut c~.Icl bc len wened. 9 d The partide size distributiorts of Pat- I Yn surnrinary, Ims than about 1/3 of the ticks Indoors and outdoors have been dCg, 3 inainstream smokc emerges into the air found to -br.similar,. but show a larger r.act chic'. following' inhaLation bv-, the smoker. The pro )ortion of ~4bml c" partick-s iml n I awke has "s,trom, %moke is assusned to havle, 1957, VIM= Uacobs 1962, Jacobs-e~al- he VaPOIS about- Ow -,w6e r0ationshi f p_ _:y.~por _ c -Ucd Ph"'W, t to particulate p6se weight rrninLO nticrcs w*. ledwique and"" The 'but it 4 much bLss -complex chernicAly; that indoc~ Sampleg citained it larger 7 Z.- I 4 7 .4- 302058648 BATCO document for Province of British Columbia 19 April 1999 j. J 26 TABl.r 1. C-p.6-n .1 ..d C-,-nd (rng,6g) (rng"ig) C..._t A Gmml Ditrati-a (if --ke prMuct- 20 wc 550 =c 27 T.bcco bu-t 347 411 1.2 p- 6g-ue 1.05 x 1011 3-5 x 1011 3.3 B. Particulate p6se *Tar (clilorofc-i- extr.%ct) 20.8 44.1 10.2 34.5 3.4 Filter cigAiette Nicotim 0.92 1.69 1.8 0.46 - 1.27 2.8 Filter cigarette &nzo(a)pyrme 3.5 X 10-1 13.5 X 1" 3.7 Pyrene 13 x 101 39 x 10-1 3.0 TOW phenols 0.229 0.603 2.6 Cdnii~- 12.5 x 10-1 45 x 10-1 3.6 C. t;.- and -apo. Water 7.5 298 39.7 3.5 rag of M -d 5.5 Tor S ift P~,,tk.la te phase, rest in valwar ph- higher. 1, d,,r ulate nuu, concelilral. ter uas as finding u, cooking a," Thi~ LjL__ monstrat-_:, ide (54 1,, than that, . teker ,t a;: Ammbnia 0.16 7.4 46 The -rm' Carbon nrarmide 31.4 148 4.7 63.5 1.3 79.5 Nit- Oxidm 0.014 0.051 3.6 M SideArea. S-A. For 35 in't puff voluAm,_ 2 sm puff duration., aw puff-per ininute and 23 or 30 mw Wt lengilk and I D I,% tolucco mximare. A.OapLe.L H gi; (1972) presurnalAy frwm car- fraction of rjber~, these -structures and for -the eArichmenr (10.-: J . of pets, curta4m vic. An inten,4~v- 3tudy sites ratio. The, des'iguatiops of siunpling j -structmv . indoo~I~Qutdoor air POULkiiallimolvW thrm, . , . a~c -ewhl 6,d g5 [allow.%,: - pairs of buildjap in and arowid Hart- Far outsidL.. rept-ting anibi ent air ford, _-Connecricut. Particidate sarnpics 9' uality in thc =ra of the butkUng. . Offike were evidtIated bv the wei ght increase bf ear outside: located next 19 a window 0 6 Otor~ .. fat .~T papers containing samples and -by- seprafing t!i~ indoor from ihi outdoor Mth .1; .. U optical . evaluation of fater tape stainx envirortinent. Rmilts were mpretwd -a& the. mtib'kif ' I--- lust i"IdL IIW-744"r-iii6w 1, door to ouldogir co=ntrations. , rhme Saulple. t~" typ" of Str"cu""s .%V.M U_wd in the &wdy, located well iz~idc the uruc- Far inside: ix., public hnildings, office btsilding, nrid . lure and, rvpksentitkq Iewls- of pcilut;vuts 1 ; - private luxnws. 'rabic 2 pfesenm w%nits indomm ' frorn- putdom~&-ar generated to for coni-t-titratims iiinde and outside, of which -tlw occupants are L 302058649 BATCo -document for Province of BritiSh Columbia 19 April 1999 inent ,rett Lrette M and 5.5 particulate t in vapor III gencral. daythut, (owewrali.n, ere hight-r. buill indoors atid outdtxmi, than nighttime cmirvatrations. The indtorrmt- door ratio hows s,il,,aamial lo-~ of partic- ul.m., matter in the 1-ciactration process. III conin,"t tr, 1,*-Il -,-ticulat, u-tici concentrations, the organic content (ben- zene-soluble frdetion) of particulaw mai- ter was cariched in the indoor samples as contrasted to outdoor samples. This fii Iding was attributed to smoking and cooking activities indoor.,. The Wf-fif-- of smoke inclotirs was de- ruonstrated to be 143 to 300 minutm, con- siderah4- longer than tha of sulfur diox- ide (54 to 71 mili.) (Wilson 1968). A half-life of sinoke four or i vc tintes longer thwi that of- sulfur dioxId,- is reported clsewliiere (Shepherd c( al. 1958, Biers- ttker et at 1965). The mean particle sin by volume of airl I.),- i.,d,.,z d-t, d,,t,i ... ;ncd by con, hined electron micm,-copy and sedillienta- iion mcthod~. L, k1juut 3 tan. If an ap- praximation to the logarithmic noinial distribution is, a%%umed to be valid, the geoinetrir standard deviation 'Is about 3.0. Thus, 50 rh. of the particles by volume are in the size range. 0.75--9.0 litin. All types of particles are present: the fibrous particle content can vary fr om, 3-35 by number (Whitbv et al. 19381. 3 t.5. GUIDELINES FORTRES11 AIR REQUIREMENTS INDOORS Air requirements for occupied space-, stern primarily from two considerations; heat dissipation ratt's of individuals as a ftfix- lion of their activity and odor coutroL Figure 2 indicates the -minimuni ventila- lion rates suggested on the basis of odor TABLE 2. Suip-drd particulate mancr al indoor and outdoor mjnp"g sites (con cen(ration, jigit::3: indoorloutdoos, ratio; dim,mionkis)* butt length- Sampling Surnmer tau Winter Location Iminj ' , - ' Day Night aay 2'. Night Day N t ish P.Luz L~iilifftc iar outdow 132 82 150 100 425 189 (li4ary-,,air tiRht New outdoor 98 66 115 77 293 13Q pling sites avacture m-cr four, Near indoop 70' .45 - 61 46 4 M. Whwily) .66 43. 57 44 67 45 bi,,,t air Indow'outdoor ~0.50 0.52 0.38 0.*4 0.16 -0.26. Office bailding Fr ~,mdor 104 93 48 124 91 in (16 310ry UnICURIT Near autdwr 118 -90 47 40 43 .7 .80 with air -co-nditioh,j) Near iladoor 49. 49 34 24 39 41 Far indoor 50 46 -.36 27 M 39 Indaw 9uukvr_ d.49 0.49 0.75 e.71 - 0.31 Q41L A9", 65 96 94 U4 86 (in the midst of a Near outdoor 87 65 . 93 70 109 79 ~lte struc. ftem-F interchange Near Wear 67 51 5i .42 '45 32, ~ollusants Far iudoor 70 - 36 54.. - 45 49 35 lwfww~outdoer 0.87 GS6 0.5G 0.61 0.43 0.41 doon to F.,m J. E. aud W. Q (.lot,-. (19 711 4 7, 302058650 BATCo document for Province of British Columbia 19 April 1999 28 h4 w 2. R te% (1-' - kng,.-i.g, -,17). Ad,p.-: G.- 'I". of 0. P 1-.71"". F. SMOKERS (WCOMMCNO 40) R'(~)- and D. I ( ,,gim, N',-n- 24-- I'litinn Rcquir-,ots, T14".%. A N H IT, Vvl. 4 --', pp. 13:1 196, P. Y"Rlmi, Ventilwloo R(41tvirt!- L 7 `nts for Cig-tte Sinokc, ISINT, V.1. 61, pp. 1,955, p, 31. 6 C, 01" 2 lop, ing; 4 100 200 Soo 400 Soo AJR SPACE -CU fT OER PCRACIN coal" (Jorgensen 4970). In practice, re- guidelines or adopted as standards by law. if 11i ts COMMrnd(,d MIcS arp at least 50% higbcr- - the industrial rmironment it. not Con- Coll Ilie air zvqttirernent for odor control is sidemd in this discussion. C=,. gen=4 dia a t hat requ ired to ftimt A"ther .-ruli (4 thunib- appmach to the heating and cooling "cls. desViation of ventilation requirmenliz is I'he designation of cubic feet per ntin- based.0111 the pumber of roo" air chan .9" ute (cfm) Toquirtnien L% f6r smciler; is per hqpr (TAIc, 3) -(Br;cf 1~-A).).. -h-wd -Ximiniv -ab the whr-k-tif vxHablez Im to -Iii. WIWI -(195.~), wbo, uwd panel& of human sube fluence the averawgr and lootal conceritra- jects a;jd collawd subjective vesponses of tions of sidesireasu awke in an ocl;Upied -Yft tw 44tMat - td -Viee ft fiftn"%: the j~tideline of 25 cfm per sniol*r U toL avoid. unde' 4able irsponses by ow"Pants. A. Nutubt; ~f 6noket~ band -dtgme -,of A ' entirely different !~ct -jDf criteria is 14 olanF( v ut Lf =wA. g !,,nd n OL -q -itcy 4t itwol(td toy thtr occupaWnaFenviron- extent, qf cipmme . nuoked T, tnent where Imic: L X the air ni ust be -diltiled to cniscentratitaps C. Fqnn",of toblcro smoked (6.garette, OT ie.' WOW thqw fte-colikirtended as liyffi,~tiic cigar, pipe) - 302058651 BATCo document for Province of British Columbia 19 April 1999 a. V-6u- r"gi ...... g. '--',-d fro- h, E. C. )rnts, Tyan, 4 f '~. P. IMI-o Vol. PP- by law. s~ not coll- _PprcQ to lirctrwrib is air changes ow, n to in- i concentra- ja dtftpied of pkin, 1). Amount of air upplied :r, i-in and TABLY I 17--d 11-61,114- re-mended air chartges E. rif"tiveness A1 distribution of air in Minutes Air F. 4NLturc of 1vall, it, toom (abvorhing or d.ngc p,, ho.r G7-I*Lit,pcramre of room air and supply A,.mbly h.H. 5-10 6-12 air. 3 20 ,-,n 1-3 12--60 Cbiu, 5 12 It iq not limmm if ;111 5mokc componclib C..duit room, 1-10 6-60 dccay at the same r.tte. The limittd data Ditlimr 5-15 4_12 oil this subjt-ct indicaic- that they do not. Dye hwws ~40 6-12 This could be due to inwractions bem-ecil F-adric, 5-15 4-12 paHutanis or if one or another rtacts with G-get 5 12 K,trb,, 2-3 2G_U compohents of air or with interior huiW- Laat~Atories 3-10 6-20 ingsurfaces. Laundrim 3 12 M.chi., hp. 15-20 642 Offices . 5-10 C-12 3.2.6. CALCULATION OF GONCEN- Proic"i- booths 2 so Tunucls 1-10 6-W TKATIONS OF POLLUTANTS Ship, kow. 1.0 6 tNIM'ED FROM TOBACCO COMBUSTION IN OCCUPIED SPACES is not well mixed, there may b~e "pockets" If the air in the romn onder consideration of p-porly inixed air in the room, leading is well njixtd, then after cruission she to several separate air volumes contain- concentration of the pollutant wJJ de- ing smoke, each decaying at a diffemmt- cyra3c as a result of purgiag according to we. This situation has been mkcn jum de equwi-n account 14, Wi7ing a mixing factor, k,. M equa cxp 'C t= - exp (2) where C the coaccutiati1oft, of diur t (tugl~nll~ or pp-) Valtim of k are iu the rauge 113 to 1110, C. itui&ial copcentrinion (t 0) depend6ig oil the air supply system and air supp~y'rate in cubk fre the, nowher of outlet and supply grill" per minute relative to roolll We, as ., wcM a9 othcri V- = moin vrAumc, cubic fevt. lwiinnr IL~ c~iliilg t - tinr_shinat~~_ mippTy'ot air, k 1,2, about the. best value one can,obta;n in practice.. Table 4'lists smue recommendcd values of It. ute. Its recipror4 V.,Q,can be thought %Tallies of k arr usually Jetenuitwd exper- of As related to the avex,%mj#,sidencc inlentally ming a tracer '43 technique. 9 tinw of a~r in ilte room. If the rootn_air. 71se validity.of eq%wicm (2). IWI b" I IT 302058652 SATCo documentfor Pf"ince Of British Columbia J9 April 1999 i6 AA 30 TAIII.r. .1. t,,-,-,-d,d th, hexafltiedide as a trat-f-r. Values of I from ;111 -- 113 to 110 were confirmed for ~rnall jxxims (approxiinitc-ly 1000 cubit- ftmi). Larger motai would presumably have sir)aller k %-alum. PLrf--j 112 If a 1-11lutint I's living genermed (luring T-k -t-, .-ith ---ut, 113 tile time tile room air is being purged. or Tr..k --t-, ~,ith d*ff-- i I" if there is an initia) -concentration of pole A. Natur4l dr.ift and ceiling '.0,-t 116 f... littant present prior to injection of C_ of Infils--ik and nat-1 draft I110 pollu(ant, a more complex eqnation is necessary to describe tile change of pol- repeav-dly verified in practice, most re- lutant concentration with time (Turk centh, by Drivas ct. A ( 1972.i ening sulfur 11963). Equation (3). k I CdQi + G C = C., exp - Qj + EQ) - + exp - (Q + EQ) (3) V E ~ Q + Qr - A wbere V roont volume, cubic feet t tillic. luirlutcs A. C - concentration of pollutant at 1. A constant additional amount of the any firne. njWft5 vapor was generated -idiin (of in- V_ = initial concentration of pol- jected into) thO chaniber pcr unit time. lutant at any time. Mgjft3 2. Ile chamber air was being replaced Ej Ci = concentration of pn1littant-ill with outd(.,,,, air by ventilation or infil- infiltration or venfilation air. tration. nigiff" 3. The chamber air. was 4cingArcated by F efficiency of filLer'in-stopply a'vaix)r reducing device. volume rate of infiltratipri or Equation (3) provides a batis for Ac- venti6tion, cubic feet per' ronwing for tile Ixackqound concentra- 41; tknits a polhit..lts in ouu"r air if the Sk., lit Q, volume rate- of air through intake air supply is not filtered. Sample filter, efm caloulati6ni otsing this procedure are pre- AM' -G CL4AUUtY rate of gencratiort vided by Owens land Rossano ( 190). of pollutant withui rooin, Table 5 is'takenfroni-thii reference and rug/min-, is based-on cah~Wadom for a W (4,by 3D -,k,+h n !f) A. ujg 4) 'A -crv assuined to be ptewnt and ty people % In-the derivation of this.gcmeral equation the minoking nite WLr, w't at 1.29 cipir- for odamn., valint's. Turk et,rusiderrd the eups M hour per per9an (11allpeany and calc cme of :v chamber which contained all 81arwt 1961), Ill,: air circulation. rate, odormis vjpor alka in Wikli:, was 3.0 cAic feet per n'tanute jxF pc!i;om 302058653 BATCo document for Province of BritiSh Columbia 19 April 1999 31 of L. fr.-) TABLE 5. Ci:1-1x,d q.;1ih,i- (0-~n' ..d X.-t- I--.- for small bir fcct) N,t "TTV (ntg'hr per (Ing/nil, purged, 01 A. -1 of pol- Gad--- -i& 48. 5.9 11. (If C~ of C-bft di-i& 3400. 398. IROO. i Amnioni 12 1.42 7. s quatim .T 1 fVd,.,q- cynidt, 0.78 0.09 -kewl_ Niui. ,.idL (NO', 0.35 0.04 22.4 Ni,,.r,, Dw.id,- ISO,) 0.20 0.02 1.8 .1 0- hydrg- pc-6di, 0 0.02 1 0 0.02 7 hicth-c 0.8 OM (3) Alk-ts 17. 2.0 MO. V A-tic, 4.6 0.6 16. Fatif acids 3.7 0.45 95-155 NI-W. 0.2 0.02 4. Acrolein 0.06 0.00 0.02 Acrt.ld,h)dc 3.9 0.45 73. t of the ~ Accio.i-w 0.14 1).OJB 14. ,n (or A . 10.1 1.2 - 480. ,u_ unit finw. I.P.-c wif-thn.1 S.66 0.18 0.45 0.02 52. g replaced Eth-1 0 380. rin or infil- hjrth~-j ChhXjdC. 0187 O'l 42. C-f- &mIh1.ridc 0 is P-wiaWhyd. 0.40. trcated JYY F-aldt,h) dc 0 rhe-1 2.2 0.266 AccWJ,+Yd. 6.6 0.78 7-3.1 -but-c) 2 C if the _';~Uthua __ 7.7 0.9 52, lc Siln A Awk add 22.0 2.6 . p 6.6 0.78 03 PM- C WM Alk- 5.3 '05 0.1 . ~1969~. 21L 7 3.0 -rence and 30.4, 3.6 0 it. by .36: CiSaF-e-ut, subm~al 110 ight. Thir- BWY --dam 2 rcsont'and '7 jp,nny add 302058654 BATCo document for Province of British Columbia 19 April 1999 32 TABLE G. 11""0" P"110,10 W. a.d ha- kg,-.,,d p-Ilut-a ,,,d t. c.l(Wat, Tabir .1 C-, f OW A, 1;,.iy -,nanmin- Pit. G-es Mi-, 4f hv -1~ 1,..- tx~d) P- Z I L, Y (G 1-., 1- 297 278 fvion-smoken) 417 ~.,--k-) HydrcaiL %&t. 0.6 232. hiempt.- ..d hyd-q- ..Ifi& 5. F.tty .6d, 89. I[- Is. background pullutitit conct-ritmtions* Su4tctided particulite matter 140. pSm' Carban numoxidt 19'6m rv%. Mirk oxide .118. Nitwgeti di-ide 80. and Suliur dioxidr. 341. Hydr6nirbom 8,640. Oxid."4 51. t Kued- on 1965 Chicago iir tisafity data. i 'A sured Parn'l. with 5 cfm per pt-rsoyi provided froin the the "jc-ct of this workshop. Hourver, it initia.' out4de.-The mixing factor was --wt at 1/3. is clear that utilizatiou oL thl-. TL%rs In ftnokii.,' Body emanations and the concentrations the last coluiun -of Table 5 is'not ap- ied a I of poflutajjv~ in outdoor air were those plicable to the gencral populatio;i, which In th, shown in Table 6. The maximum jr- includeb a largr iumber-of indivklmlso* commended concentrations 16tvd by thc%e. with respiratory or circulatory ittilwir- was c"'; autbors are, for the muKt. paq, 'Flireshold ments. .2 nil Limit Values designated by the American For lirntiou of Itcluation, purposei of'utt CIL'W- Couk-rence of Goverumcmital Hygienist!, (3), uncertainties ~m_qu it~*!!f umg add " . was nri~ for healtity adult inalc,~ ~~rki;tig ia --tho- ' -iftu kiii'm ~i-this "tinle are: n '. Partic4- a 11m, i rs wr day for fony - los 11w years. Thr calculated %-alues of Q,11 am trale4 --L subject Ao adjusiment on died basis of. aa,- 'I. Wfumnt getteratiou rates ior sioc-7' conce na P-Iro- rsthvi;ites of sidestream. jwo,ke strceirt swokt~- kr pertkn fok. -diffemit emissions, niixing factov,... and removal cf'- tyrws 6f,am-mbkWes, eith r 11~' ficichcies of filters used iu-buiWing air oriunv%, tic. 'Wpply imcirmlation or fresh air intAc 2~ MiKing -factors for different: tiptis and line-s. 11c conclunon rearhed by Oweris sirrs.of room With Mease f( &n4 - Rusano, .Vanwly Ilm hm i.4 Ile- 04 -!~&p' . &P, of vigal pt)~Wnn -via-n-04 occupants in- -its 3. D&ay ratcsof thosii Pollut. t3 judged lkidg, lialing C,,.,, concentratinus is of Courtic, to be of si gilifical ice ip the heskith of "ics IC S.- 02058655 3 BATco document for Province of British Columbia 19 April '1999 orcup-w, aher divy arc ciiiii(m] anti Pr,(I;,Ird CO c.pro-oration; fEquaiioll are subji-vt tti mixing in room air. 31 t,,mpmrd fAv--Wy wiih ihe averim~ 4. Cullvctiwi of g- ahsorheiN "iel-ired CO cotict:ntrations. atid pirticulaie filirrs for polhitants Ns.Lda tind de Oh,eira (1974~ inves- judgvd to Vx- of tx,s6W signif" cance to tigat,-d the validit, of the a,,uniptioa th,- healih of tnad,, by Bridge -4 01 (1972) that rn CD 3nd stispended particulate matter r decay at the sanic rate, in occitpied spacLs.. 3.2.7. hXPERUMENTAL INVESTIGA- Budi 1.4h3tints monitored contin- TION OF VALIDITY OF uousiv in a 9.2 rn3 charnber with stirring FQUATIONS FOR POL- of air for rnixiaig, but without ventilation. LUTANTS EMITTFI) FROM Under these condition, an. error of 10 TOBACCO COMBUSTION IN was ffmnd for the m_~pnWr~d particutatc OCCUPIED SPACES Matter copcentratiou c;.k-ulaird from the Two ilkVCStigati0l1S (.HOCgg 1972, Bfidge r_trbQu wonmdde deta-. rAie. The concen- and Coun- 1972) have been spf-cifically tration half lives of carbon monoxide and devoted to tL-% n aing the validity of Equatio suspendh-d particulate matter under these (3) %ith pollutants prewnt in cigarettc conditiom. were 83.5 and 42.8 minutes, sidestrCalil S1110kC. Hoegg worked in a- 25 Thus. it appvars that a cor- mil waled chamber and periodically nica- rection factor will ht- trece.,,basy for the surra carbon monoxitic noid wspvnded calculation of suspended particulate -niat- particulate matter concentrations after ter frunt CO concentrations in occupied Hw.,,,,r, it initial gencraticm of pollutants with a space-%. Firm ever, die correction factor will T.LV'S in suiolting machine. In otber words. he stud- have to be determined for different ,xn- is not ap- ied a purge type situation (Equation 2). tilation toaditioas. Aon- which In the study by Bridge and C~rn, pol- Penkala and de -Oliveim (1974) con- lutant generation by-cigarette machine eluded. &~ did Hoegg and Bridge and ory JWir- was continuou.,; 4nd ventilatiOn rate for a Com that %heri'auibient air quality cri- 9.2 n-0 chairiber was varird,irom I to 8 teria -arc %wzd. u Lmi-..ZaafiArkon, - of Equation- air ch s per,bout- Gadv-n zhoiwj~!Je_ - -c arbott snotioxide concetitrations hi oc- t6 i; utillzcO, as a tracer for stiVended cupied ~spaces are apt excessive. but "W* particulate ruattcr. I i.i bothof dx-wifud- pe~ded paniculaw- Matier cnn&iii;~tioux ics thevpmtiox* cited abAwe Wem &inom- cait be &&&ivc ia~many occupied spacrs- 7 isted to be good predictorg of pollutant ti whe curs. re unaking 0c ,s for sid- cancen(rationv in thv air of the uccupir4 The 41aong" of to bacco smoke'does im for different cliamber- Initially. it was ijecemry to ' only.after the cozicentratiori'qf chemical r either Hicksum- or to -.Itssunw the pWutant cottipcnients with tinte, it tuateriAlly al, :gelicradon rMe front a siuglc ~igarctte feett- tke qualk QU& it typcs and ..4na lo- theb- obtaitt' ilig t6uL 4"him"t j]i) AJW -J~hcit)- to -annoy, The' -nt typ-zs.uL--- irfc"~~ Ltoin -0is figum. and the number very limiteo data. ;)vailaw on this mil),. of cigAmues 'iert highlight i4, Awed for itivesti~pting 'Ant. judged Widge And Corit C'xtcu&x.1 the chaniber chi4ges of aging tob=~ sintj~c' M-O"u. 2 health of studies to 4 panT situatiott (Tatble 7). pic4 paccs. 302058656 BATCO document for Province of British Colurnbia 19 April `1999 34 TABLE 7. E.,p-i,-n1.1 dw~ ,,ad of -,-Xid, (Hridge ~d C.- 1972) Party I Pan) 2 Du,.U.n 0-.0 1.5 1.5 6.1 Average CO coiirenfi~iion ippan) 7 9 Rarap of CO --tairnti.. (ppan) 5-9 6-16 No. o( p-i~-T.,nts 50 73 un.kn. 25 36 non-"nAe,5 25 37 niales so 42 20 31 Male anok. 53 52 Female mnk- 45 45 i Rom floor nc. (ft') 627 375 in Volume 5570 exhaust rate (cfin) 600 640 Air chRrigriltour 7.0. 10.6 Arcid density (ft2!=wker) 25 10.4 1u_ Volunietric density (fts/unoker) 204 99 . No. of cigi-it- ma.ked 50 63 cigars moked 17 10 -moked'per- Iota r 1.3 1.16 cigar; mioW'prrjon,'hmw 0.45 0.19 811 3.2.& SUMMARY A_NZD of approximately 4 X 10-10 ntlisec imine- 1.~ CONCLUSIONS diately following generation. Within four Although a 6rge number of variablics in minutes (the longest period for which the cigarette coutwt and in die manner -data art, reported) rrmdal particie size is of smoking wntribute to uncertainties in increased about threefold. T'he decay rate' de-lineating miimion ratrs for even major of particulate matter in,a clo", unven-, cordponent% of the particulate and.gas L~atcd 9.2 ni; clmmbcr with stirring.~,vas 2. phases o-f-sideaream -Rtp rtb&nt45rjttjnj iji,.a 66,~awentratjort Z some duja~ which pennit estimates to, be hMf' life was itted as the paftvwtcr to made for emissian of particuktes,, tat, chatacterir~ cluvay. Uadvi-dw same con- ni~ -djag, te=o1a) p4euc. jyr&ne,-phk*is, .,ditions the-concentratkii 'haif life CO 1) of 3. J ;-airbon monnxide, carbon diewide, nitrous was about 84 niinutmi. Thus, there ap- exitim, aninwiiii and water. pears to be need for a correction factor After cmimiou into an occupied space. . whm ope pdllutantjftWii towcco smoke" tobacco snink, pollutants "age", Little is is- used zol a tracer to rstjn~-Ue the con- known about this procts in terms of cuptrution of another pollutant'frozn to, 4 semir;d anct physica _altcratip win -the bacco 4vinko -iR articulate and gm plk+se. T'lie fornier is rection fanor must be detern-liped - for charactuimd loy a itiod?d particle sim, of contlitions "of the verqilation' systrin and about DXvjim and it coalpilmion cosistant space involved- 302058657 BATCO document for Province of British Columbia 19 April 1999 L: 'e I Party 2 5 6-16 73 31 52 15 375 0.6 10.4 99 63 10 1.16 0.19 ~-mllsm Within. four d for which nrtiC)e GiZe is ~he dj it rate - stirriog -was px-AawUr to S.Vic COR- of CO _jS" ap- vctio... tactor ~bacco sawk-C :atr,the con-' Xn-t from tO- ~C6' The Cor- ennined. for tell) and . 35 Thcre is t-vidunce that an equation to he xL-1k-J in X.- 711RENC prvp-i~il 1,y Tuik (i9kij) call tw xi%etl to data ci,), Le u(ilized %%Ith existing equ- predi(i dw conernirations of tobaccu atiolls. Silloku pullutalits ill occupied spaut's if the pollutant genor-ation rales an~ rcliably . k""m-r. the raoin % t iailat;un rate is char- Br-son, F. L l1rade-n, J. J. and C.1d.-M, acterizrd, together with a iiji~xitig factor D. E. Indoor-Ome- Air Mluti.. for the rooin, and the ClUiSSiOll. Of (11C RO.-,tion.-'. i- A Lite.t-.- Review. U.S. pollutant from offier sources or its tni" Pn--wction Agency, NERC, with background air can be "vified. R,-w.-h Iri-gle Park. N.C., Pub. No. Lcyss mechanism in air are not consid- AP-1 12, Bierste,ker, K.. dcrraaf, It. and Nass, Ch. A- G. ered by this equation. The validity of this (19115) 1~!. 1. A~ Waier Poll. 9, 343- 350. -nethe-i of calculation is of major value Britip, D. P. and Corti, M. (1972) Contribu- in evaluating the possible hazard posed tio. to the k--"MMt of F,p-m of'N,.n- by tobaLco combustion products in occu- Sn~iokcrs to Air Pollutiori frc4n Ciguiettc and pied spaces. It also stresses the nmd to Cigar Srn"e in Occupied Spaces. Knr-irfyn. irliably detennine generation rates of pol- I'zs. 5. lw-_'09. Brief, )L S. (1%0', Simple Way to Determine lutants of coritern in sidestream sn"e. Air C-un-i-m Air. Fg. 2, 39. It is concluded that art-as where new Dri,,a,, P. J., Siaunaud,%, P. G. -d Shair, F. It or better data are required if the concen- (1972) EmWianicuW Characterization of % 4 ration and nature of the challenge agent Ventilation Svst"rus in Buildings. E~. Sci. are to be better characterized are: Tr,h.of. 6, 609-614. Egerton, A., Gjpn, K. and W,!inb~rg, J. F. ' (19653) '11. 11-hanisn. of Swoukki-ing in rixation of~ 1. More complete ch~ractc cilprelic& Cmburtion Fi-. 7. 63-68. c-owpositioll of 4idestream smoke and Gorblj2, C. M, Kondrat'ycra, 1. 1. and Pod- generation ra tes of coinponeats older d.1m. ya, L Z. (19641 G- A,:&ity cliffeir"t sruoki The5e co ditions Products~ Ex-ted,by SIan Whm in an Air 4 , n ng T WW Chamber. Prob1cms of Space Biology, data are also neonded for- ciga'!?~,I!~d iA-. -:14 " joint F.blic.Aien Rewavch S,-i", Wad~- 2. Decay rates of tobacco smoke compo- ingwn, D.C. sients.aw fmc&&"d data Telqtcd to H~Jlpenfkt, P. F_ and"itaiTtI6, d lint A h i i ~ Cull ulDl ~f OdOr Alld Irriution Due to mi c ur s allg ng 0 ng ag $make And Othrr Air Pollut~tm ASIZAAE bacco smbkc do not.noW cxist. J..rnal 3, 34-44. While a range of mixing factors for How, V.. IL ;11972) Omiret w Srooke -in -kentilaird spaeft is-available. AWW ill- Clowd fipacm F.&Oot,. 111th, PersPerAircs, fonnation'Is'-needcd Jar -,perific -t-)Trs .117-128. jac,-W. SI, IL, .1kxo4arati. A- &W Opt"ater, air supply wicauuioils. rmw sivet - . I,- . -1 1. L I.A.1964' V -anti ralcn- 00tdoor Dust Cunw'lxlem. 1. Air IV&tex--' 4. Data for rcmowiJ efficiencies of ccwk~ Pollution 6, 20-3-211t, "101i room air cleatient' for p'artic,ttlate J"A's, -NI, B-'~ %"Trm-kn, ~1. M.. Theophil, i1 nd gas conipoticnits.of t olujc~ca untg&e . I tigin and Xle;A-mneut of Piteti(les in (Sty - outdoo r 4ir pollutants %%ould and foo Atnto~phere. A~'j PabVe-9,0h 47, 1,60-. "ist With plVdirtion of. iiuproAsPei;1s 7 ~' 302058658 BATCO document for Province of BritiSh Colurribia 19 April 1999 36 R. (Fd.) (1970) 1-, FnK1i-,1inR, P,-,-Lda. S. d,0li-i,a. (07-1) 7 th k1d.6-, N.ffal. F"'Ar C.,., ih.ff.d.. Call- ;J 14. "d Suq,,-,~drd Keith, C. If. ,.,[ D-i~k, 1. C. (InFO Wa- Cig.nvtt, S- E.,i-,. 16-,. 1. suren."%, of the N.66. Si- 17:- 6-i". and U-..nt.lli- f Uk-tic S- 'k. by Sh,ph-d. R. J., U --. G. C. arid Phair, J. J. the "C-if. 1. C.11. S,i. 15, 3.0-356. , 10W Criti-I h,j,;,,n of - Fill-suip Kingd-, K. H. (196)) sn"'k, S.nyl" -,d in Fl--- Plerni~,V,. Fffrct, ~f HVCJ 14'.df) U~Mltld ill A,,h. Id. lifi,.. 17. 1,3G-242. &-k.. 189, IR41-482. R. L. : -,'P 1 The 0-1 C- A. M., M.,cki-, A. D., K,,fiin, I., I"iti.. f TO. ". and SjnAt:. H:,...,d, E. C. and Selik.ff, J. 0971) Urni. Rev. 68 z , 153 207. Inorg;mic Particles in Cigars and Cigar TuFk. A. (1963; Mcasurernwt of Odwws t Srn,,k,!. 174, 5115 537. 'talmrs ill H-- Charnbem, 1"Leoretical. M-n, B. J. (1962) Clouds. Rain and Rain- ASHRAE 1.-.- 5. 55-58. wkinR. U.iv. Pre-.,% Carrthidg,, p. 39. Whitby, K. T., Aigm-n. A. R., Jordan, K. C. and Morrow, P. (1961.1 Evaluation of Intwlation Aruth, J. C. 1958) of Air 3.3.1 llazar& 8-d Upon the Xe~pir.N~ Dust Cleaners for All Cle-ing nd Vtmlilwin. CL-Mcvg znd thc phik-P.I.Y -d Appii-- jUg., Pipiiig ad Ai, C.adg. S,,- SLW tion of Selecti,e Sampling. Am,,. Ind. Jlyg. sion, P. 171. , Ass". 1. 25, 213-236, Wit-, M. J. G. k'1';3', Wwr Air Pollution. for N"rath, G., Ehmk.:, 14. nd St,hrlc-L-, H. P- R.y. So,. .4 300, 215--221. (1966) Vile, Dcn W-wrph-It Von Haupt- Wynder. E. L. ..d Wffm.,.. 1). - 1967) Ta- Und Ne6en-Strontrauch. Beitragc Tabak- bneco and Tgbe-, Smoke. Acadentic Prc~s. dar,~ lo-h 3, 351. ?Z, Oberg, M. (1973) G-th of Ifygro.%copic Sul- Yagiou. C. P. (1955 Ventilatiott Req,,i,-'nt, furic Ae~vls in Air. Dwtoral Di-LaLion. 1-r Cigmtt, S=,-Ie. ASIMAE T-. 61, Uni-nity of Pittsburgh, Gracludic School 227-230. of Publi. H-11%. Y..-. J. E, CliuL W. L. -W Ct,, W. C. in if- 0%-ens, D. F. and R-ano,.A. T. (1969) Dc- (1971) Ihdoor -I Ontdmr Air Qtntlity to te sign ProceduTes to Control Cigurette Smokc ReLationbbips. Air Poll. Cunttal Aisuc. , and Other Air Pollutanu. AS17RAF fxani. 21, 261-259. 75, Ift"ealt by c.- the Tito- 302058659 BATCo document for Province of British Columbia 19 April 1999 .. (1974) -hair, J. J. -itter-stlip 'CA C.- ro S.oke. R. C. and Air .'en U. W- -ec- Pollution. 11967) To- ~Mic Pren, LqUiM1jj,ntS T,ans. 61, 6 r Quality ,t,.t Aua, 3.3 Reduction ot'Tobacco Srnoke Containinants in Intei-lor Spaces by Means of Filti-aticin* PREs-roN E. MCNAT.I., JR. 3.3.1. FILTER EMCMINCY VOR PARTICULATE MATTER Standard methods have been develolwd for ra-ting the performance of-filters. In thds papcr these iucthods axe diw-usscd in relation to tobacco smoke. The two stan- dard inethods have earlier bccn described in detail (ASHRAE 1968). 3.3.1.1 IF,ight melh~d In this procedurc, an artificial dust i~ fed to the sample filter. 'nw portiou,which passes through the filter is collected and measured. The efficiency can- be expressed paper > 99."_ %v efficient on. filtration of particles down to submicron size. Conta- mination collects an the surface of- the filter paper, causing a stain. This stain is fneastiftcl by g photometer, which ftads opacity (0), definud as the percent reduc. tion in ligla passing through the paper after staining. This metbod heavily fa- vours particles- in the sire rartge of 0.1 pm-3pm and is almost insensitive to larger partiele& Tobacco smoke is almost entirely in. the size range of 1-31tm. Its concentration thus:-correlates- well with".dtit ap,~t mr-A- by calculating Oic weight of du,4t held by~ sMrq_1!Cqts,.whVrcas.it, oc, r the tilier,-divided by that led to the filter. with tlw -weiglit fawthod. Duct spot read, All inedia filter, impmve in efficiency ings can therefore be used to eitimate as they become loaded with contamima t: filt r.rrrfqpnapce f9r tobacco smoke with" ver, the air Dow rellistanrc A!50 in-, practical accuracy. creases and jWriodic cleaning or rrplace- Information oti the efficiency of various ment is necessary- 4illers on different particle sizes is avail- wigle-'and Baudei 1964, B able (F U2UFtt 33.1.2 Amiofpherie 'dust spot efficirncy 1971.. Peterson alid Whiihy 1965)- nifthod -1- _Ally: CON J'AM D, A I JUIN of air through a dense, gass fiber filter UNITS To use duA spot readings. sonse defiiii. 71.6 4 . mndm.4 -xi- -f the -figi..l tions of units are.mvcssary. -The Coh pq)rr Aitht~it mmir of the hiaihrwndc;4t -i, and data. Th, orlgi,W pap;., (,coeffit z.!a of Ham) is arbitraxily defined V. 'as tbe uwcvntrition.'of panicks -in -is-a" it alAe fausai. the 4aOtur. 302058660 BATCo document for Province of BritiSh Columbia 19 April 1999 tube i air MIO ft. It'11j" if cot- Ircied wi a filter paler ecinal in awa it, hv tuVw's sf-ciiwi. %-uld trduct- ibe ight I ......... 6.,ion dwouph th'. pap'.1 I 1~_ ; It i a contan~inntirni cuiict-mimion h-vel and caji Jc valculawd as fiyllows: 101 (0) )1 Cull A where: 01) = Optical Density of [tic filter paper."mple (percent.1100) = Volume of air sampled (ft3) A Area of the filter paper (ft') Mic Coh has no metric eqnivalent. To relaie the Coh value to a particular cotilaminant, the Smott tfoit can be used. Miis is defined as the a6v_Jutc quantity of parfikulate contaminant, which would stain a I W filter Imper to a level of 1 Coh or: Smoll 1000 ft3 Coh For -tobacco smaw, about 5.4 tug' are, equivalent to I Smoh and one-cignrette produces al-ut 7.5.Smoh of_riawataiifi;l~ We now 'have factors to relate the weight of lobacw smok.c in any valudQ- of air to the dust spo! measurement -(or e, Coh can Ckih level). For tobacco smok abo b,! related to,inOn". OP 3,3.3. PREDICTED LEVFLS .+Pox JNATION c Using Ov filier efli ititeit-, and other basic dain, pred'Clions,ciiii be inade of the contantitiatirnt levels in variowt crs due to toliacco stiot,kiiia at varintis r-tir-, (Su!- ton et .11. 1964). Figure J demomtratf, thc relevant paranwwr% for this vilculation. 'File IklatlWnlaticll f.rinulatioi of it), mady ittnt~ cowi,kuatioti (t can be as- C, --V,C.,(l E) 4- N, (2) V,E N." + K where C., Contamination concentra- tion in outside air - any units. V. Infilffaiion air - 63,inin. V, Ventilation air - ft".'min. V, Recirculated air - ft' min. Np Rate of contamination pro- duction inside the spmv- Units consistent with, C.. K Contantinant settling rate - Unit consistent with C_ 9 Filter efficiency Ile space volume. has tio effect on the. ation, but only an steady stme concetatr, th-transient rrapoose. For taining con- jamLiation, such as tobacco. anoke and tim.- staining fraction of atrno~vheric do t, #h- rmncv~d 'L.: . ~eiAmg- is q-u,i te _,nWL. The effect of air iiJiltration and von. tilaritiq depends on die amount nf this a*--Aw eampared wkh the u-nat VE (r,,- circulation rate x filter efficiencyl, as Wei al~ the. cotact!t1taticuk of. contaminant in 1he infiltration and ventilation air. raw lite jitaj,6rity or Iesiden-iial -and c;Y1 -V,9- t--T- 1: 0 mapn 11tappr- Ai=L thi lance- If the xt-eiroilation'rate is Sinall- compared with lh~ inflitralioto and wal. becomes "- i6l- tilation. ratx-_$~ this temi portaist even. with high efficiency filtet-S. It itt c. air I-. of C.. wh~ varp rate alx,,. Irn, HU', nW 302058661 BATCO document for Province of BritiSh Columbia 19 April 1999 duc (hu(- the j C., I i be 2) Ai fo ff,&, Ul f n, -in pro- aee. C.- -ct an he --ut only On aining Con- AerjMF'sl, 'Auite- W?a,, ;i and 11, V,E (re. itiencil, as ,)0tarnir-Int tr- ,ion, 07 ,,-6al and Ig )e" im- "CY fillen'- 39 IC" VWMATtow DOSIDE AIR WCIRCtLAM V. V~ ExF ILTFIA1,UN V SPACC W3_40#4 SPACE CCWEMMTION Nq CONTAMINATION TER M=j ION -YE r E ONIIQ SIMMS pATE _f I ^\- I L----J - COMMMAI ION filtration and cantwu- Cure _,_6c of ,,ic., pc,, icl.ding entiI3 i F iront PrvductiOn, tinuously during I the tests and the CICC' ton It is important to bave a big" -ircIll, ic aif CICaW was turned_oll.at u tin" rate as will AS j, higi, efficiency filter 11V done in - d-ircd i,e, The 51100king -as h e of t in order to keeP du, effctivmcss . It looln With a sinok- the basement ftcMall" uni. air Cie-alling elluipilwilt at a ynaXIM . Machine. The C-h s _ere deter- 9 Equation 2 can be ~J,cd for any set tn. in the return air d-cl. -ahCDA --f 'he uned M air from all the tions and 'Figure 2 shows a case rr of c..di nce 'it air cleaner. The retu ad of id ll d e occul-j ill a res wl,ten smoking air recirculation e a s of the house was Mixe loom CollditiOns in r l i%h two various rAICS W turn of cificiepcy . e he samp the locaLtion Of t e C40h lCVC1 ra re ra,es. Th,,Oirltinishing " g n these tests. repre5c t an aye factor 31)), WO 6 . above 60 r* is n1D T) 9 for the entire- house in dir. bilsemellt rcc~, jind not d1c level i0 a a, TFST~ OF SLD as in ~~Cral others 10 this experi-c" A f IER piedicted*ve~ with the fOnned experiments iod tests and iaboralOrY - also per ~,Oi the wjyvilc air r.Uanpr agrIll; were ndertaken t,, afidat .e die the' 'ry experilnental.-data. th jo#-_d aboVe- dC,:c e iod the clectrank Ric ' the Per During _ hrief sluffjmaq~ FiSure shows lhc i , that the was OU, it ~w*" 01_4~ a n jrsidence under fairly of a trst tn a l leaner c tiow r0- ~01 bjcctiowable~ 3evels l, Mu A ~3 bL11rf)0nl, nilrolled catditiOn" lk Ij hour h d)~. bfwsc. wain a v we singlt~_jcvelhousv with full bascuwnt WP3 throttg :111 k -pi* ~-n "wr ~W ft" qW d,4rud v& quiP-"" "S' Tt, pir rJeaning e 1~. . a , - - - . the I~ Ot the house evept 1 l or vs tyr" "maitce bf~ 4L fed a ~ on. t;ceablv, haze ond the haze - cjc~r of no , -4 ust spot eff~ 10%1 _E1 an W ..u , Ill was lnurh roduad- - kk-cl ip t)w, bjwule eff. =__ r Cleaner (d perfolingkiwe of 'Air () ectronic a' t addition, (he fic.l l in place 80 jujjxj~r filter was . v . BA-fico document jor Provin ce 0 Britits1h C oJuMbia 19 APO '999 05 S662 302 i9 40 clcaunrs mi %t;iiiiing contarninatiou in mr- tinn. I-%,-(, of diem -:re tilikiped inal evvi-N-da, -r ,i, r-!! I'mic ,,, ch"m-rS ;,kid !- Willi I -kld pmj,-rt limm , in a suburb of Dalla%. ftimire fliters. Culi lc-[~ --re n---nd I,, s Tc-7,a~, Th, --w vrry similar- in dwii% p-i-d, of difff rent averag C size, expomire. floor plan ind votistme- of In all (Z~-' dw acti, t" in I000FT3/MIN. FECIR4ULATION ? 50C' FT3/MIN. MULAT ION 1.25 116 16 CIG,/HR. X 4 -2 0 < Z R the I" appligi, uj 3 -Alp w rea, for r-, ism .25- I Colli.-I MR. -0 2o,. 4)D w 8o__ i00 FILTER EFFICIENCY MTAIN),'% 2. 111i'mwetirid cotirem-li.- i.' It nmlt~;- %Sikh cigartmt, All *91", 0 302058663 BATCO docUMent for Province Of British Columbia 19 April 1999 4 t -2.00 andard -asured 'e rat(-- PRE NCTF .. .' - ~ -L ZKA'i'+_ ivity lit ___r -1.50 0 THEORET4AL C __LATIO~ S 1 .25 z (:XPfRIMENTALI RES~LTS 2 < 1.0 z 75 -25 4 z EDIC' D STIIADv WATE ~3 EQICI 0 vft JAC _5 D L .25 -FILTER "10 1 .0 0. 0 3 ME OKKIRS) -is affeetc a high p%~rfo-nce cleCtronic air ctcan- -d b) er with A-x.4prette snioiiiT rate of 12 Wr 1-ir. .75 the homes was %,cry -typical v)f a rrsiden6al more effectively to protect other adjncent application. :The wsults again sh-ed xpace!i. In ca--s where a single room is good, agrccuxlnt.. with the theory, required to be as clean as pos~blc, the air cleaner can a1Q be insmiled in the sup- ply grill or duct,to 1hat room only. 0.5 3:3.5. APPLYING PRACTICAL AIR Many efficient vlectronic air dr~'arlrn 'ri-actical high t n ' I im they mol be rated by th~_ASIIRAE duct -foruia cc air c forrcsidential aiid situtil toazincrcial prem- q.)ot method, and should have efficiencies 41 of. 70. c, -ises, huj~__.WR= devck+,pt, MAiky ~typcs cxcrss are a~ailablc. Media fdt,-rs (usually dcep- These filters must be cleaned jwriodi-, ly pleated iviiesi have a x-ariety of dust enfly, by. .7"hing. They ame rt'vaitablv, with spot efficiency ranges 4rant 50 4;~ to 95 ~~. in-p4%cv %YaJiiug systems with other All of these lacciurrit at regular iribdels the'.,,cells may -be removed and renw!- rep -it (2-- 4'nl~f ' -au be wAshed by hand or in a residetitial dish- interv. O'k. tyl!es t 'Mountm.in the kin. aW air-coivdition;, %vwhrr, Wn~hi)ftg-i&m1d be doW, at. teg- ItIg equTment at its ceuirm tocrttwn, utar IZA mW"h) intervai&- ating th -e systvin. Wier c;iu be -1 jwvy ASRHAL Ventilati.11 Standard i re. v ent6 6. instalb-d - in a retur. grill or duct from 62 -73 (ASRIIAE 1973) his bet.n. pith- C) a bingle::romn, and in this way. operate lishit-cl. w4iich. ertc(Surages -the u.~ of - fit- 30205866 BATCo document for Province of BritiSh Columbia 19 April 1999 42 Wl'atiOll CqLlipllit:llt ill Ofj~!l to Coti~Lvc ilwAts. Wilvil 411C clidj~:,jal iN 6111% i-dvd, .%SRI I %) the enerp- re(pured to li,at and'or (ool funher contaminant ~-ill citlo-r pa ss ,"rN large qti.AnLiLie~ of vitkicn--i all. through or- Lc c-.clLau,,:,d for a ;,txr al, VS R) I ready il. tilt- filter. %'hich rclei.- that A.I. material into the air -treain ag;~iri This 3.3.6. C0X(:!,USi0,N3 iGR exchange process i, %un. cumpi(x and P.A.RTICULATE, explain, thc strangt- ndt)rs whith call CONTAMINATION FROM wmetim- be present in pace ,J.,-re t1w TOBACCO SMOKE air is treated with a ch-cont fiber %vhich H.11p,: 6.1 The rrliintinii shnvx, hrrr mn he lins beconic loadca. filt- all be Cbnt,, used for the prediction of air c1caner per- reactivaied by indu,trially pl~rfornied tm, formance and is ii~eful o,cr a wide range heating. Activated charcoal is ty;rrently J."', of filter efficiencies ineastirtil by the diist the only %s,ell accepted material for vapor D. I spot method. filten. The filtration of vap-)r constituents of 6.2 High llerformance filters (dust spot tobaccu smoke has been xwwd in a lim- bafis) installcd in the c"ai-all ductt-A. ited riumIx-r of tudics (Richardson and can without added ventRation -effettively Middletown 1959, HaUpently ahd StarW4t control tobacco %inoke particulatel; in 1461, O~-ens and Rossano 1969). In these spaces during typical (and even atypical) studies, human subjects, rrported on their social gatherings where miioking is heavy. sem%ations under different experimental conditions. 6.3 It is suggested that the procedurc- be ined to detexminc and quantify the smoLe levels when msearch is performed oil the 3.3.8. CONCLUSIONS ON effLct of environmental tobacco smoke. VAPOROUS T015ACCO CONTAMINATION, 8.1 Equation 2 applies also in the case 3.3.7. CONTROLLING THE VAPOR - of -apor mritamination to pnrdict the con V CONSTITUENTS OF , nirtation levels ill spaces, where the ef- TOBACCO SMOKE IN SPACES . ' fic iency of the filters is kp~.wn. ne analysis prt.--.ented for p artictilwrs~ effiriencV.0f the available devices for the known filter matexial, "ins to ha%v prac- ^ apor amteri.4 ntimevow and complex j,7. tichi. efficierlciej for txpor tobacco irri-~ :V 0 tobacco OYin6 is rim welf'Ziowh and ' tanis aild ixI.r corlsiluzeuts 16T A.,oat rd test meth- no gefienflly accepitA standa that of'tbe device's rating by the ikkistry. &N .exist. Ratitigs are generally made by _ feeding 'a sin% gle or..4 few specific vapori REF~AENCn 4 to mwh filiem PAid mca~,uiug--1hc up- ASRHAL Standatd 52-68 (19GO) "Method of strearn and do%yastreani concentrations. of T,.,6rig Air CAr-ing I-d in 'Generni Vmiil-ti-n Jr Rmnovirlc ftnic- Charcoal. like paIiiins W-r ' - ----- a limited alnullilt Of C011(allk- hold only N_ Y,.,k, N.Y. 10017. 302058665 BATCo document for Province of British Columbia 19 April 1999 !1 y loadvd, ASRII,%E Slu"Id"d 62 73 43 (j!)73, C 19-mr Srn-k~ and vapor al- ASRHAY. 3-17,f_ -17,h st-1 7'r(?nsar- -ase~ that , NX. (to I It- 75. 93 1(j2. iij - Thin T 1111"nett, (1971) Si,,.,y,-d Fili- IL' ISRII C. M. -nd 1%hitby, K. 1'. (19f;5) - . . , jt)urnal 13. 48 50 I r-timal Efficievic\ Charactrristi- of I Init 1 ' plex. and righ-, 11. M. j'. -11 IL1,11111 C 196 J ASR!1AL' J-r 1 7, 42- I" 1 -- hich - can . , . ( 4) a,,d Allpfir-ti f 49. %here tile - o Hith rd.--u- Dry Filt-.. ASR11,1F Ri6-rcho.,. N. A. ..d Middl,t.n, IV. C. IPT Which G, 72-/-5. -1 hlwi~.t for R,m-i. - 1 1 C -UP-1q, P. F. .,.d St-ft P S g Irritants f-m Miluted Air. ASRHAE Trans- 3 C LZ 4 . , . (1961 CrtntTo4 of Odor arof I it i aclion 65, 401 -406. - PC rr it on Dne to Ciga ' lltt~ SuvAi.,g Ab-,d Ai d Sw,-, D. J. t .1. (1964: ..d urrently - t, ASRIJA E 1,mr-1 3, 39 44. Appli-tim, of Air Cka.-, it, for vapor 0,~-,, D. F. ind R.-n., A. T_ 196 9) Dc,si n 0,,upi~d Sp.-, ASIMAE 1-n.1 6, 55 g . -62. ' in a lim- ---n and r l t - n es e d on their t Se V. t n- Lue the ef- and 6~st pholit % -.%IcthQd, of L=q r2rtic- 47 th Sirmt, 302058666 BATCo document for Province of BritiSh columbia 19 April 1999 rj -t AM 3.4 Tobacco Siiioke hihalation DAVI. L. F. NILE, tot'l dq- 01-1. the L.. chell Ptz' ' 3.4.1 INTRODUCTION cmqi~ing gases or particles. this led, Therr. The preo4ng mpprt% have given detaiLs nique draws the inhaled substance further crepanc,' of the characteristics of envirosinsental to- into Oic lFing than if it wete di.,166-U!d ds~ part" bacco smake and of the ventilation of throughout the whole volunte of tidal air. lungs at. romis. Fron, this infrn,.tin die t,xpo- A, fAr as gases ~rc concertsM. thrre in inhaling, !:tire of individuals call be calctilated nnder urilik-IT to be any physiological difference mond p . var fing conditions. This liaprr concerns bet-e--ti tisoinh brew1iing or breath- hih d,--~ rucchani-snis by which the envirotinwinal ing. The uplakt- (if CO is greater thals scopic tobacco snioke acro-I -tes, and dep~it% that rueasured during steady mair breath- Tlis I,i in 4he respiratory tree. ing. Thi, gas is A-bed from the alveoli siW M i bUL -inre on*.y itictut 70 flF of a rictrinal 3.4.2 TBE PULIVIONARY BURDEN tidal breath pesieimk~ bryond the ana- likelihxt' I'lie intrapulnionary deposition. ah~rp- deatr qvce. a proportion of the the ch a" tion and ccretion of the various coulpo- ., CO mhaled during steady state breathing ' IL.O~n , netw~ of~toimcco smoke depends ot) their to tl,,- alveolar cux:~2 1jA have had acce. e~klencc,. _ C st _phys,~zal chara teri ics and oil the pattern surface. A puff of cigawtt. ~lsioke k on 30 /q. mt of bteA~I%. SusA rtm#iv forni a specitO j,"ul, ~Iskh bill not bc, th, dqAhs- of the hsng, by die! fol"irg tobacc,". discvmcd in detad's'inct- particles and "" i " air- and no gasor particl- rinitaiii in if the m"t- is will not enter lite iusigs 'the d"iT volurn,~~ n6 probably held in the mouth. However, muly sntok- . lcad:~ to"a. greater absbi-psion of-CO that& ers %4ia clahn it) avoid inhaling, probably .Ave (about - 50 - 53 If) the nonnal v depth j,* do inlralt- siroke't. a greater --tent than . pmwd d"g ac,dy,statc breathing. ii- Wry they rea tw- The belisiviourof particulate to.itpr in Tile. efr Active snisAing with inhda4ioti consists', tin. respiratory tl,.V.. is ni.re C.MPIC)fThe Pro blt ,td the site it y-d about '45 int in the ustoke (.in xvrnr of of its depmwitiou. dvIxiii.6 on the 6i-,w ol (,aw pf cigisrette,~. is Iito the inoath the pmtick%, an the rat, awl depth of after it if, drawn into,d~.- lungs. Ulicthrr bveathing and on whether it is inhaled is it. is:, -FA 302058667 13 ATCO document for Province of British Columbia 19 April 1999 45 via 0j, wonth (it u), 'nit. vaii-s d- u-, ~utwk, p-i- ih, L.- --rn dr.jtmg ~.v r-ni air 1- ~oniv timr. Furdirr t,xjjvT- in a of publivaiions 1GRl' 1966. i-wal -,A - cq..ired m 'hi, All-t-i , A 11173 a ... I vill n,,t b,- 'FY,, P-e-- ;,-- f migh, orat,d heir, Frcmi the nic-Invd ~i7e di~- be inq.~rvin, fnr 11tv v~.tii-tioti of the trihuti,,.l of flic pailicles in cigarette sino. VIV1,11r, ill 1111 ,,,,k daring If a l.rgv pi-i"Irtio" of the particles i~ mouth brvalhiiig_ N-idd-sugge~j filar [lie f:"-,,d ;~l th, 016C, MOL11--cois of the it tutal dq-tion shoiald be It- diar, 50 ~~ parliculite concenintion pf-r unit volulne with . Girly ,.if-rm di5t,ibution 1hrough- of roont air u ill nut give ilie , orrert rstitn- out the lur X.%. Experimentq with icbacco au~m of the lung bin-den if substances sinoLc. however. have gencrilly gi%rn ~-fiich exsert thtir effect in the deep parts valuer. of 70-90 % (Policlorova 19til, Afit- of the lung. TU dw.% not apply tu colil- chell 19G2) chiring active smoking. pounds such a~ nico(ine, which can be this tech- There may bc two reasons for this dis- af-arbed front the n"il mu~Asa or front I nrft! further crepanq-. Total deposition increases as the bronchial epithelium, depending on the dist,-~utcd the Imi-ticles are-drawit ftitthre into the acittity of the particles. of tidal air. lungs and the "puff" tochnique of. the Two special cases deseme noting: ex- -.cd, there is inhalitig smoker doci exicl)y this. The posure to envirrnmental smoke in young second possilile cauw for the unexpectedly children and in athilis with established ath- high def-itinfT values lies in the hygro- di-~i~e of the hang. Experinic"ts have Uot Qsve re W.1--r"Ate, than scopic naturt of many of the partirl". bCkli LAtried out on the depo4tion -of par. K, -rare bt"th- This kads to a rapid increase in their ticles in die lunge of infano but calcula- it- Ithe al"Coli size as they enter the lungs and -this Lions f *H41opct Al. 1972) suM_n that the ~f a normal rhange is assoriated with aij increased anal) si~c of thei: Ituigs is not asuviated ,,I the all.- likelihood of deposition. Ilic, ex(ent of with any ~rrat cl~wigcs in the total ot of thp the chauge bi particle dianmtee is not regir-al drpositi~ of particle-, Their ral- blift .'i.g kn~u in: detail although them- is sorne ative minute ventilaticlit is greater titan that an averap value might be that oi adults h"-eve tin of (he Iffolar evi r &ad per ft -",h, is Oil 30.% (Alivitell 1962, Sano 19681., body uvight, %'Dung chiltim-A jahAlc- a -,ln-d into pcn~)n cxpobcd-Ad 6wironrrent2l -91UL6- aiii;i~,Wi m any airborue pollumn t 4.i. f"Jit"Tirg tofiacco wuA4 inhales this smoke dis'. than dt, adult.,. ii SOj" with injjt 'Utury Aca, 'c~ r-Ain in tributed througho4i !he tidal lj r and aired vepo ais, P~Axibly probably rn*~Ily by ua.,,ol WeotAiim. Tin- prtc'it- chic 'to ai~ays obstrucrion have of W ft-rn - Prt.~lcss do not penetraiv. to the -saaw- been found 19 havt- grratr;4.0m notmial ~-55 ex- depth as during smoking and a laige,frac- 'intrapulnionary depositiog A par- of inhak -eathing. tion.may ell be filftred out in'thc now. ticles (Uive and Muir 1414) but th~ %iw Ae- matter in The effiLiency of this I'a-I fit"tion is of is shifted" proxi~n.llv - The probably stion, effiricitt tha ii has bcen Stijp- ch& ot al. J971).' arid Ali site posed (Prw,-w ond qtAft 1 71) 4ut aaaw 10--7 rc--qArd,';. to octennitte. t1 w siAe. 4' ill,; p-Kticles. Ac- the prtrtic.J intpli,.k1iolls of Cipos'six-, to ad depth of Curate rstnu-Mcs all, difficult ~incc, their envit-omm,aal tobacco smoke for thuse. :~2eo;it is in4aled is it tht-'Aw d6nibutiou t,,. groups. 302058668 13 ATCo document for Province of Britistj ColuMbia 19 April 1999 4 4 G &-1 ...... K. -d IU-i-, 1). kl'~;3) d,j-i,i- and i_,_ f IS I' I I "I", -k A,, h. 1w. Med L.M'A.' 1-b- NJ. -d Sun- G. I'W2) P-t- natal &-th "'d [.1116.1, .' L1, ---i- ai-)'. 7'h,,,,, 27. 265 274. Int-lati...,d C on R.,di,,'-i-I P- smi.. (196C.) D'..J."ifion .'d 'eteoti.. niode6 fm ioteinal dosimetry of oic hunuin -pirm-y t-t. 111th. Ph),. 12, 173-207. l-, R. G. ..d 1). C. F. 1974) Pri-- sonal cownisinication. Mitchell, R. J. (1972) C..tmlh~d -.-renw.t M. 1961 M att-pt w de- roiu: th, uq-iw.~ ,f LOu-, ,-k~ by of -b-- fil-, in: C. N. D;-- fnh,led pjti,h, d -p,wi, P- N, p. 142- 144. N--. D. 1'. .,d S.il. 1). (1971 1 *11,, n-, 6,f-c, it,,- ,t--phefi, _t. WAt".1 ('d.): ri'l-k'I Nnicks Ill. U.-ii, L-don, p. 59- 70. J., D.I-kh. M., Ch;,I-,, R. and Nc%%Iivtm, M. 1'. 0971) ReKional distribu. fi.o and I..g cle-n- in-hani- in and --.k-, in: IV. H. Walton (ed.): Inhaled Particl~ 111, Unsyin Us-, L..d.., 1, 183-1111. 4 - ii, ati-ktparficir mtention in she -pimtOry SAno. 1. (19GU) Tbac~ sanoke ai~ a p.Ilutant, aact. A- R,r. 1?,,p. Dii. $5, 526-533. Kuld'Saij....p. 1-7. 3.5-L An Cp withee in tab,., koed proach, - - Imm Ot t are 14U, betwM' ciatim' Cult. const it, -this 4 i sitnita . t6 iolw dedbf F, 5. 2 3 . The r 302058669 13 ATCO document for Province of BritiSh Columbia 19 April 1999 N D-i" environ. 3.5 Epidemiological Investigations 1,hnk-d CTI P. on Fnviron-mcnial Tobacco Smoke RUNE CEDFFtL6F AND JOHN COLI FY "b- in 3.5.1 GENERAL ASPECTS tativc population samples tinder fcalistic An epidemiological approach enabit-s as- conditions have not yet bcen studied in sessment of tht, 1witsible h(alth risks of depth and insufficient data are avuilable exposure to environmental tobacco sinoke for discussion. without the artificial corsditions inherent on chronic effects A rc,,icw of studies in laboratory based studies of small, se- - igi%*n in section 3.1. Miring the work- lected group; of individualt.. This ap- shop, data, at that time utipublislici,' from proach lends iL-,,-,U to deAhr-- with pro6. a study of respiratory symptoms in 2,426 lems of the %~pc wli(:rr a number of fac- 6-14. year uld whooldii1dren and their tors in addition to the one, under study parents wat pmsented k(J-011,y 3974). am known to have effects -on health. In- The prevalence Of Cough ill the children 4 vestigatious. of this kind smk associations was fowid to be associateKl ivith their between factor axid disease. 71tough asso- par cim smoking habits; preyalencc, was ons arc often found. drAwing con- C"i clusions about causality can prove diffi- lowest whrn both parents were ndn- sinokefs -and highest were both parents cult. smoktd. A-clesd osn-Haf"ri wZZZZ:Tout~~ n Bebidm inywigatiow- i"-it-ng'jWiterru We twe~n P61rents and children's rrspira- pnnilation iiamples, twin stijdies cnalAe tory ~rnp onip. When p4rents, ;.mpiratDry conaitutional factort to -be controDed. In sYm-p!nmsj,-ew takeft intb amnitnt, e3ipo- --this respect-thc study df (tvin palt, Aith _smm. of the child to eigarette smoke ge-Mr- similar and disimilar exposures-to tobacco ated, by^ the parents stitoking, hao little smoi)ke should be particularly useful -(C~- if any effect upon the child's - resliii-a tary derl6f et,,al. 1971).. associations between par- s) 6(al anokiAg and' childrrnlb respiratory 1"40out-t Mpoitca bY'_Qt6tr 4"A,,n -and 7 3-5.2 INVESTICATIOMS IIN !Li 10cie4.as indicating tbe effects of't". - r vitorinwrital t0xicco sittoke, rilay in fart The rffect~- of 4ion terni rxpcmtYe to 1v wh.lly at) efirct -of parents' ~rpirutoiy etiviroumcntal tobAcco stuoke oil mprestu. diwaw. 302058670 BATCO document for Province of British Columbia 19 April `1999 48 Some lit-t-liminary f inil-ings were sl~ presew,d fro... a stud, of a Inirth roli(irt of 2.200 itifani, ~Iticli' suyi~-tcd that P);- posore to ctivironnic-Tital moke in the first yvar of life. after parents rt-s- piratory symptoins had bccn taken into aCCOUnt Might double tht' Tisk oi an at- tack of pticuinonia or bronchitis. 3.5.3 EVALUATION OF DATA, The first problem discussed was whether existing epiciriniological data provide any reliable evidence of an advcr~e effect oil health of environmental exposure to to- bacco smoke. Most itiv"igations have focused. on children or special sensitive groups such as patient., with ailer- gy; no investigations at all havc bcen dune with healthy adults. As for the possible effect on children, the gencral view was ex- presbec! that existing data %vere suggesti%v of-an effect but not cAmiclusive. Other Jactors may have accounted for the at)- parent effect. The nwthodulogy shoti1q, lye improved. It was also vinpliasized 'that precise quantitative data an exposure %ocre difficult to obtain ill these kinds-of invcs-_ the pit-lure. In addition the ffv~ts of cit- %ironi--titA tobit-cu) snioke may 1W inall in rciation to, the effi-ris of thew other factoi-~. hi these circunist.nit-cs studies on Larzt- popidation samples would Ix, needed to dt-tect effects. lrre~pvctivc oi whether or not existing data have indicated a qualitative eff,-ct of crivinuiruentat exposure to tobacco smoke, data doe., no( ex6t that can Ix! u,ed for aswssivig any dose-responsr~ relationship. As a result any assessment of the dose-re- sponse relationship has to be extrapolated froni existing data on adult smokers or on people exposed to environmental air pollution. The general feeling of the grx)ul) ~as that neither active smoking nor expo- sum to air pollutants could be regarded as an ideal ba~,6 for extriVulation., 14ow- ever. in view of the lack of adequate data. particulate matter front tobacco smoke cmiki not reasonably be regarded a% being less toxic than particulate inauer from air- pollution in gencral. Experience- and cri- terjLt f"mu the r-Atter type of -11-ure could thus In- used as guide-lines for assming exposure effccts. 'tigations. When. further investigatiops are per- 3.5.4 ANNOYANCE REACTIONS index of exposure stich formed, item, in the discusion J an as . COMb, as well as a-me kind of lung func- tion test as a itx-asure of effect. *hould be iticluded. There ittay be difficuitics. however, in detecting GO d .vrived from enviroruni;ntat 14laceo smoke aglijist background levc6 derived f1`011k otlit-l' Sourccs. such as auummobile-&- "a A,. Z-'~.All Z-ft, was An imponint the non,5mblker's jxsrlio4*iaI reactions lo a haa-king viivironnicia. 'llic topic has 6 een touched- uport in the literature Lut Ao extensive and reliable, i"vestikatiujis have Well luldeMakett Io a~sessthr'diinen_ :Ji0uj Of lihe-I)MIllelo. S~Cjj ';lIvestigation" May not be as many non-mmokeii, -will tC4:ar,-. I,." I .,: cr-Stan, I t~cr, )'I arr for, DIM I'll It un,: theze pi- pla% ll.,~ the ni., &Mokc c, bu,&m. i. ".1-i 'i'vs- -.Y .~dicrs of harm to ficalth. utch a% five reactions against _vnfaky euvirmimems. m1 ory syruptottis tkut~ al-x) be influenced The -.,treognh of,the atiltoyance rention by.factors other thatt clivirounitin tat to- iuiy bt~ diffeiclit ill diffcr~ljl enviroll~ bacco. smoke and might thtt, confound menu!. For exatupk., W'oph. mi), ivact 6s 302058671 BATCo document for Province of British Columbia 19 April 1999 J IV "will ba,, I"Mcl, .11irr , 4", col"J."t Dat., (,k. "' ;( 'd It v,-d,d IM, it F" S : W", ., dy f h, 7 4 0 S'nok,, It would bt-j 11,1 Aled. S-d. S,,ppt. a M,,d J. R. T. (1974) y L.ul.l_ - Ploy r 1 n "" J" -if " ,, diling.j.,J, he '"' '"I -.ki "' 'd ""11911, Ai m MIC for Moke l h Af,dj_j 2. 201-205. raP-l-red c~p-um from Other en'if-lumm? burden, ok," r . ~tat' dir C group or regardd 5& How- e da1A, mwk~ P beirig frt TM nu ai r d a n cri. ure could IX AS _-n Iva;. clim, to U ic has t-V -but igwions edi _Su 7 4 0 a eu~ir n- r-t 1- 302058672 BATCo document for Province of British Columbia 19 April 1999 4 3.6 Tobacco Smoke Allergy - Doesit Exist? GEoFfam- TAW Ilk 3.6.1 IN-17RODUCTION smoke. The r,," nov, populatioti Tobacco Zl-vrU inipfies that some responding in this nianner is diffitult to individuals ",e acquited & specificany detenviiie. Potnilations sujdli~d haim usu. altered qate ol"mictiYlly to an agent pres- ally been highly selected, and the responses ent in the smoke. If this were so it would to tobacco smoke hLve been. evaluated be iMport.111L to identify the agent or subjectively. Again die type of "ponse agents in question. This could aho radi- varies from person, to pvrson, from eye cany alter an)- rtcornmendation on con- irritation to severe dy5phom 111, awwer centrwiow of tobacco sajokt in the cn- to a quest6nnaire, 25 f1c of 250 non-aller- vironment in dat an allergic individual gic, rtoii-sinoker3, mported coughing as a would be expected to responO to ccin~idce- rcisponse to tobacco satokc; whitst 4 ably lower concentrations than might pro- experimccd wheezing, and 29 % nasal U. F~ duce effects in nonna-1 indiiduals. symptwits (Six_-er 19691). lit this paper, the rcactknot~ involving In the same survey the. incidence of the reso~atory tracr are considered- lit symptoms in an, allcrgic -gloup of 191 view of. the workhoptapic she pos6blc non-impkers was' much. 'higher. Nasal inmiundlogic.1 "4ationJiips of sjn~~ng symptouls ~OCWHrd i4-A7:%. -iffdagit.. tl herr eir. ~- - aizi"&.-t%iiiis - oblit- 1,*~ and m heezing in 22~5 %. -'rhere appears erans and' skin contact sensitization to to be o%vrall agr&ctnent, that th= is a And to6uco-~,~,U.not be dealt ivitti.- - higher popmti~A of "efiniml reactor,- to The -idea of- tehacco srr",e alfeW tobacco wnoke In an -atopic population ' arose because it is'. coinnion for atopic than in. a nvii-ai0pic. group. the. individuals to complain djar tobacco sftW_ .- ke may prqvoke or exacerbate both uppper Dill,, and- lower respiratorT tract sytaptopim 3.6.2 EV'XLUATION OF ~TH.E,~ 'I'liese paticnt~, who tumally Ww. defiua- RE-SPON.5 _;,Iu 4wg6 -to a. situal"i in Which only a proporrion in will %tiffer front thiulfis or asthma ou . of a poptilation rviponds when rxpostd expostux- to low concentrutions of toba .cco to an agent, which may-have bodi irriunt lit V., 302058673 BATCO document for Province of British ColuMbia 19 April 1999 N_ 7 g X:.~' ..d l.neutiall, cvcral fio,,ihiliii, rnwit lx: ronsidcrvd: 1. Are there anmoinical dill,rence., ir,' a section of- the pop- lation hich r, tilt in cidirr a differ- encc in disLr;5,,tion uf Lliv agent or in a different &..- being r",:i,ed? 2. 1!, there true immunoloe.cal hensitiza- ti,,. of p.,rr.f thc p.puLt:ao" 3. IF there a difference in respr-inst: to tile agent in pirt of the population because of inhemm or acquired differences in the met-i-IL- -f the apn! or in a pharmacological response to the agent? 3.6.3 DOSE DIFFERENCES There is greater retention of small partic- ulate aerosols in per-us with restrictive rways disease than,in. normah (we sec- ai tion, 3.4). This would give such individ- uals a greater likelihood of msponding to the potentiall% irritative or toxic effcts 51 .[,,,r,,ed plau.i ~n- i, cl.,~ t. pecific a nu,,,b,r f -nditi.m chrt.ld a. the plititoinction A-uld be rvptcxluc- tible by an objecti%ci~ mea.%Ujed chal- Wiwe e%j~rimrn? character i,,S agette and carric-d out, where. prac- tical, in a double blind manner. B. Sixcific, ininitinologi(-al rractivity,41-sould be demonstrated in zitTo as the pres. crice of Antibody or of sensitized lyinpho- CytC3. The Specificity bhOtdd, where pos- siur, be sho-i 6v abu"tion studies. c. A good correlation hould exist I*-- tween the in vil- p.- .. ttc. .,.d the phenomenon. Ideally, both the in rilro and in i4vc, o6sexi-ations should b-- quantified and a positive quantitative correlation deinorntraiccl. d. Cotifirmatimi by pascive tratisfer itud- ies, by which the ph-me... k repro- duced in a norinal individual are not usually possible or desirable in man. "ir"ll ive . t-pon- ,,valuated response I rom eye ans.er. 4%, of tobacco smoke- Individuals who habit- Transfer studies in primates may some- nasal uafly mouthbreathe %rill lo~w the value bf times be appmt*We. the na;%M filtcr, and will receive a greatt-~ 0 ;~ dence of dose in ihe loner rc-Tiratory tract- Both In tlw case of tobacio smoke, objective 1 of 1 fitclo,,. would tend to iricrease the doie of clwlk4kgt: expcniments have not.1-n car- 4 putkulam,acrusal jeceivvd bv aa alk4tir V4-0 out. -If S=Ix wcrt-U,-L~ It Udi%,jdual in that. commonly,'he ,ill have gmzt probl-., would arise.in view of the ~ ap;= bckh sonic. aw-re of nasal obtitruction ' i very c~omple% "ture of the smoke. Ratber 'CIT A 3 vi xesWx6c7L- a a d spruc: inmaic in tirw .4 4h3weltallefte4he tbirgrt Aite of ruactiviV;~ k_1 ~artors" to Though, these factors should be considered reseamh h %-e ie. the respirwictry tract_ ~m % when dc-signing future ittvvsii tied relv skin challetige 11 9 as a irritant to 'gauol" into ten on tesung, the effects of "~iv-smlijng, it is un- aftoufh in many gituations skin re- likely that account. for jr. they the very _qxmsivennits docit not courlaw. ver %-e!L inbeh greater incidence of "tlinical re- %,rith wspiratory tract Sensitivity. sponders" -in- ail_-.11nVic ulatiin.- .AlItZ' .,..-d- h.- .4064- variably been de-nic4iuised crude rxtr. X xts of cured tols~cctb leaf. 11h- incidence of 3.6.4 'SENSITIZATION positive wea) and flare skin rcRx--" hm In-order to deintmstram, that clinically varied fixim 7.5 to 21.3 in lion- 302058674 BATCo document for Province of BritiSh Columbia 19 April 1999 71 Ak Ir V T - - -r v r 52 1 4 and hon, 11.4 -Hn 10.;., ;u 11--all"gic ...... l,";. TIW con, tinu, I" sn.ok-,., w-)d C."I co-Ae,;,hI, hined rcsult~ ,! llarla%y t it. (19-12), doubi ,,, tl,,- Sultzi,erg- Ha;-k.-- Id R..na- .-d fla,,! kin ..... , thc cliui-I ncti"', noff (1931) 11-kavy (1931.. S,&1,rT,- P,,.,,t- of Ow -hject I. loha-, nwke M diii. (1934), Tr.-If vt al. (19361, P,,hkin xi.,ure. and and l1a,k-y kI939) What then do th-l-ili- %-:1! ilid tob-c". ive an inciLka- of Ili reacit- iii 9 flare respon%es nivau? Skin pas_%ive trans- non-smokers and 12 5~ in snjokers. fe, test% (Pral-itz-K-Ine') have been The incidence of positive skiii tests in carTied Call by a nuiijl)ci of workers. allergric individuili has N-en reported to Harkavy and his --oi-k- I.- e rep-wd be considejahl) hight-r. Tito%. liarkav). positive P-K tcsts on "any Ccasi.- and lion I (I _%8) relxn-b 32 r,~, poN4i%-e and Fontana have shown (Ilarkavy and Witebsky bilhiy. , et al. (1959) 53.4 17, p-ifi- in idivid- 1935), that in eru- fr--. - .,I i.di~iduiri with .1.1 uals who had rvidt-nre of 1j)perscrisitivity sensitive to multiple allergens. tk- tee- ! tmt, ~ to other allergrns. Peshkin and Landay tivhy to tobacco ex(rar-t can be sp-G"ly (19391 J..nd 72 ~',, of .11,.& ~hildrcn rcxAcd hy al),O~pti.u. 11-1,il,t other in,,$- of pla~~' -acted to tobacco "tract but on the nth- tigators (Peshkin and Laridiy 1939, Zusi~ if wrili or hand. Speer (I 96Z) using the les, smrsi- ... 1970), have c-Ifirwed the P-si- sibl, flill t.- "11CIatCh" niethod of tv~Aing, found IrAnsftrahilitv of skin rvactivity to toLa cco indi, -.I,! o n ly 14.7 % positi%c-i in a group of aller- extract. otlwrs have either failed or ob- thcn,(~!! gic adults. tained inconistant irsults. ThLm may boc! no question of correlation between technical rrisons for failure, and thc ~ijc- if -X-. positive skin te-sts to tobacco cxmic