BAT CDC Documents
Techniques for Tobacco Smoke Inhalation Toxicity Studies
Fields
- Original File
- BATCO002
- URL
- http://outside.cdc.gov/images4/00/02/49/39/doc00001.TIF
- Company
- British American Tobacco
- Date Loaded
- 04 Mar 2003
- Author
- SIMMS RICHARDBRITISH AMERICAN TOBACCO COMPANY LIMITED
- Box
- B2924-6
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TECHNI~ES FOR TOBACCO ~IOKE Z NHALATION
TOXICITY STUDIES
AUthOR
Dr. Richard ~inns
DATE
7. IO. 1974
British--Amerlcan Tobacco Co. Ltd.
Group R. & D. Centre
Southm-pton.
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~NTRODU CTZON
~ODOLOCY
Smoke Expos ure Sys tern
Inhalation Dos isetry
Phys£olos£cal mm£tor£n£
S~ STUDI~S ON A~I2~A3~ Z32OSZD TO ~40KE
Deposition o£ Smoke F~t£culate Hatter
Selection of F~posure CondiC£ons £o= Shore-Term Scudies wich Rats
F~GURES I.-4
TABLES 1-4
CO
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Ci)
(ii)
J
I/~rRODU CTION
The £nfocmac£on conca£ned in ch£s document .is a brief revim,r of
low," of the cechufques being used a~ B-A.T. Co. Lcd., .G.It. & D.C.,
South•upton, £or .studies on ~lacion CoWrie7 of cLzareCte smoke.
Of p~ccicul~ i~porcance are the deecrlpcion of the smoke exposure system
which has recently been deveioped for this type of works and • auzm~ry
of the technique used for demon•craCkS peneCrac£on of smoke particulate
mccec ~nco the lungs of sell laboratory animals.
Work has bern carried our on a number o£ laboratory species, but
in this report the information ~vmn relates ~ainly co me-dies o~ •he
18boracory zac. This an£mal will be used for shore-term inhalation
studles ~equix~d as parr o£ • "So•Be l" submission to the HLuzCer Cous~ccee
on ohm chmrmccer£stlc~ of • substitute smoking mterlels ~o~d
'~ATFLA~Z".
$~aclsed results ~e ~ven of two £mporcanc up•cos of chic work:
prelin~nary dace .on dos~mEry ecud4es ~Ch the race
selection of the exposure cc~d£c£ona Zor au£mals subjected co smoke
£rom one of the ripped ~lue-cured e£sarmCtes Co be used ms the
lOOZ tobacco control sample £or 6-~eek comparative toxLcity studies.
NETHODOLOCY
Smoke E~posure System
A Ken•tel v~ew o£ the smoke e~poeu~e system is given in ¥iSu~e 1.
Eseencia~lys the |yst•m is based on • mod£g£md Maso~ emokin& •chines as
umed fo~ smoke condensate producClon, ~rLch 8 sequence controller which
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operates various valves to 81Zow movement of smoke and diluClnS air co
the exposure chamber around vhich animal holding cubes are attached.
Some advantages of the machine are:
(1) Cigarettes are smoked under closely controlled standard conditions
of pu~£ volume, frequency, etc.
(2) Smoke exposure conditions can eu£ly be varied to give either
conclnuous or ince~uitcenc exposure to smoke. Xntermlttent exposure
can be varied from 5. seconds co 55 seconds in 5 second intervals.
(3) For continuous exposure of animals, which ~ the preferred method
o£ exposure based on respiratory monicorin& studies, the smoke
KeneraCion system ensures ~ atmosphere of fresh smoke.
(4) Smoke mi.X~ £S rapid, with no visible evidence of layerinK or uneven
distribution o£ smoke in the chamber.
(5) Particulate loss in the anClre system, be~veen the buCC end of
the c£saretca and the exhaust port of the chmmber, is approxi~ately
IOZ o£ the TPM zeneraced. There is virtually no loss due to
deposiClon ~rLChin the exposure chamber itself.
(6) The system is readily adaptable for exposure of a wide range of
animal species, and Ir~Ch this machine york has already been caz~iad
ouC ou mice, hamsters, rats and Su/~e8 pigs.
(7) The smoke dilutlon zange can be readily set aC any level ~r~th~
the likely useful =arise 1:5 to 1"20 smoke:a~r. Zf required, dilutions
outside Ch/~ range can be achieved.
(8) KonicorinK o£ chamber atmospheres can be carried out durinB exposure
of animals co smoke.
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(9) Animal holding tubes can be used to monitor breathing patterns
of animals durinK exposure to smoke.
DeCa~ls of operatinK characteristics of the mach£ne are 8vailablej
buC aze not S£~nn in this brief :epo=t.
Inhalation Dosime tr7
A method has been developed* to determlne ,'he penetration of smoke
pazticulate phase into the various :egious of the re•pit•tory system
of animals exposed to smoke. The method also a/low some use•amen,
of the "dose" of particulate me,trial which animal• receive during an
exposure to smokeo
C£garettes are ~'spiked" v£th unlabelled decachlorobiphenyl (DCBP),
• d~ch dur£ng burning of the cisarette transfer• unchanKed to the particulate
phase of smoke.
The tmlabelled particulate phase mLrker i• tetaLned ~th~n the
respiratory system of animals exposed to DCKP-teKsed smoke. After
recovery £rom tissues the DCB~. hence TI~4, load can be determined to
K~ve an indication of smoke "dose" retained by test animals.
In the e~periments described in this report, iuntdi•tely after
exposur• to DCBP-taBad smoke, animals were removed ~d • 8a:qpla of blood
taken for cArboxyhaemoKlobLn (COHb) maanu.t"emant. The an~mAls vere
then killed, rapidly dissected and the luns8, l~rynx and trachea removed.
Heads were skinned and separated into upper head and lover jaw (with
tongue) sections. These smnples vere veiKhed and stored under deep
freeze condltions until requ£red for analysis.
j " j IIIIII I II
* ~ased on Levis, C.I., et el., (1973) Am. J. Kesp. Dis., ~08, 367-370.
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LunK aalpIes vera homDsenised in the presence of cyclohexana and
sodium sulphate and the homogenata yes extracted rich cycIohexana in a
Soxhlet un£t £or 3 hours. All other tissues ware extracted vichout
pretre4~Camnt. The crude extracts were concentrated by evaporation,
s
then applied to colunms of alumina (Activity 1). A first £ract£on yes
collected in cyclohexane and d£scarded; r.he DCKP fraction was eluced
with 15Z ether in cyclohexane.
eluace vss evaporated to small volmm then made up I:o 8 stamdard
volume (5, 10 o: 25 ml) vith added DDD* as £nte:L-nal standard. The solutions
we=e m~alysed £or I)CBP by £njecclng 1 ,I samples onto a glass column
(2 m x 30 san i.d.) packed with 3.8Z OV-I on 80-100 mesh Chromosorb W (I~P)
us£ng a Perkin ELmer Hodel F17 GC ££tCed with a Hi63 electron capture
4erector at 300°.
The amount of DCBP present was determined by comparing the DCBP:DDD
peak height ratio £or the samples wlth chose obcait~ed for a series of
standeds o£ knovn concentration.
PhYs £olosical..H0nitorinS
Systems have been established £or the measurement o£ :eaplraCory
function Lu animals under normal cond£clons and for monitoring changes
in respiratory function during exposLure to smoke.
l~Lonitor£ng of the breathing patterns o£ amimals will be carried
out routinely durins exposure periods. For sho:t-term stud£es terminal
measurement o£ basic pulmonary characteristics, such as C£dal volume and
respiratory rate, ~r~ll also be made on test and control animals.
In addlclon, rapid routine measurements of blood COHb levels can
be tattled out. This parameter KLves an Lndlcmt£on of penecrst£on of
me ,
,
* DDD- p',p- l,l-dichloro 2,2-b£s (parachlorophenyl)ethane
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at least one saseous phase component of smoke into the respiratory
system of exposed Rnimsls, and to some extent this may complement the
particulate phase dosimecry measurements made using DC~P labelled smoke.
SOME STUDZES O~ ANY~ALS EXPOSED TO S~IOK£
Deposlcion of Smoke Particulate Hatter
Work has ken clr~ied out involv~nK exposure of animls to DCBP-
taKKed smDkeo The objectives of these studies were:
(£) to assess the effectiveness of the B-A.T. smoking nuach~e for
exposure o£ test animals to smoke,
(ii) to determine whether the use og ma unlabelled marker material in
smoke could be used got quantitative dos~netry studies.
(iii) to beBin the collection of comparative doslmetry data £rom several
species of laboratory animal, which may in the £uture help in the
selection o£ animals £or inhalation studies,
Experiments on rats ~d hamsters, the two species which are currently
being used most extonsively for J~haletlon studies with tobacco smoke.
~e ~eported briefly here.
S~ test ~imals o£ each species were exposed in p~rs for 10 minutes
to a continuous stream of emeke (l:l& dilution with ~r) from unripped
c~Karette8 (Code BO) u~ich were loaded ~th DCKP (1.95 u~/~K). Control
m~als vt~e exposed to smoke from untreated BO ~Karettes° All c~Karettes
were smoked under stanKard conditions Co a 23 nm butt ma:k. Blood
samples for COHb determ£natLon and tlsst~ samples £or 8nalysl8 £o~ the
particulate phase mrker were taken as described previously.
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A sun~ry of some of the rat data from test animls is ~ven in
Table i. The experiment need not be discussed in detail here.
The
principal points of. interest to be noted ac this stage are:
(i)
(ii)
(iii)
smoke particulate phase marker was detected ac all levels of the
respiratory system examined.
the B-A.T. system was therefore an ef£eetive "system for exposure
o£ tats to dilute smoke ~m~et t/~ condit£on.s described.
~mde= the conditions used, althouKh there was some evidence of
depos£tion of particulate materla2 in the head res£on of tats,
a large proportion o£ DCBP recovered was £ound in the lower respiratory
8y8 ~em.
(iv) cor~iderinK the technical di£Zlculcies in cmrrying out quantitative
inhalation dosimetry studies, the dose o£ particulate material
zeachlnK the lower respiratory system, ezp~essed as ~g DCKP/K
tissue, az~d blood COHb levels veto reasonably consistent in this
study.
A simila= study has been carried out us~nK Syrian Kolden hamsters,
and this allows some interestin8 inter-speciflc comparisons. Essential
detalXs have been condensed into Table 2.
F~fective exposure of animals can reasonably be inferred from the
data presented. In the hamster, deposition of particulate materiel in
the lover respiratory system was hiKh, with mote than 90% of deposited
e
DCBF beinK detested there. There.was therafore less evidence of nasal
filtration in the hamster compared v~th the rat. Particulate load,
expressed as ~K DCBP/E tissue appeared to be 2OZ hisher in the lover
respiratory tract o£ the |~unster compared with the rat, when both species
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were exposed under similar conditions. The deposition is further
sub-divided Co compare "dose" of DCBP to the various regions of the
lower respiratory tract as sho~n in Table 3. This interesting comparison
suggests chat although deposition of particulate matter per unit weight
of tissue was similar in the funks of the two species, deposition
in the trachea end in particular the larynx" of the hamster appeared
Co be greater than in fihe rat.
For both the rat and hamster, blood COHb level tended co increase
as particulate deposition increased in the respiratory system. This
~a noc unexpectedp but to our knowledKe this has not previously been
investigated experimentally in this way. For 8 E/vet lower respiratory
systmn load of particulates, the tendency was for blood COHb to be
hiEher in rats than in hamsters.
The details of dos~metry work are not ~ven here in full, and
the fiKures have not been subjected to detailed analysis. Several
important points of fundamental interest arise from the results obtalneds
but at this point the information 18 given only to demonstrate the
potential of the techniques u~ed for doeimtry work. Hopefully, this
has been made clear in Chls b~iof presentation of dace.
Selection of Exposure Conditions for Short-Term Studies in Rats
Work has been carried out to investiKate the tolerance of rats to
various dilutions of make from a flue-cured tipped cigarette. This
ciearette~ coded G29__~5, is one of the lOOt tobacco cigarettes which will
be used as the standard aeainst which other c£Karette8 containinE added
foamed BATFLAEZ in various proportions will be cqmpared. The experiments
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described briefly here related to the selection of a maxLmum tolerable
exposure level (~frEL) for exposure of rats to smoke from G29_~5 cigarettes.
Tt iS expected that exposure reKimes for studLes with BATFL.q/~-containlng
ciKarettes will be related to the N~KL for G29__~5.
I= planning the work for determination of smoke tolerance of rats,
various conditions were pre-defined :
(1) Continuous cachet than inCermitte=t expoeure to smoke would be
used dur£nS the burn,s8 o£ el••reties Co a standard butt lensth.
Konitor£n$ of breatKin$ patterns dur£ns exposure of animals %ruder
both continuous and .intermittent ¢ond£tions indicated to us that
the former •de would be preferable for this work.
(2) Since episodic exposure to smoke throughout r-he period of the
~erLment is preferable, it was decided to expose animals twice
da~ly, vlth approximately 4 hours between exposures.
(3) E~osures would be carried out on 7 days per week for the short~
tet~n study.
In addition to the smoke tolerance schedule, come race were also
subjected to daily restraint in holding tubes to determine the effect
of th~s stress on the animals. This aspect of the work was done as
part of • study oa the back&round paCbolosy o£ various batches o£ race
kept for several weeks ~n the facilltles which will be used £or the
ma~.n r-omparatlve inhalation experimance.
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