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3-Mo~. im~TIo. Toxzc!~ s~-oY oN xxTs
CI~TE
..~Poe.z so. ~. 14;,;, ~s~zc~D "
23.3.1977
AUTHORS :
Lynda V. Wilton
G. Smith
It. Binns
ISSUED BY: S,R. EveLyn
PROG. REF. : 11.01.02
DTSTR'rBUT$0N:
Dr. S.J. Green
Dr. I.W. Bughes
Dr. R.A. Sanford
R.H. Gibb, Eeq.
R.S. Wade, EIq.
R.G. Nicholla, Esq.
Herr H.E. SotCorf
Dr. F. Seehofer
Dr. C.J.P. de Siquelca
Dr. D.G..Felcon
Library
Copy No. 1
II II 2
" " 3, 4
lell tt ..~
" " 6," 7, 8
" " 9, 10
" " 11
" " 12
" " 13
" " 14
" " 15, 16
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CONTENTS
,| el
SUMMARY AND CONCLUSZONS
INTRODUCTION
MATERIALS AND METHODS
C£gara~te Type
Animals
Exposure System
Experimental Design
Oh servati.ons
Te~m£nal St:udies
RESULTS
Monitoring of Exposure System
Blood C&rboxyhae~oglobin Levels
Growth Races
Food Co~sump¢ion
MorCali¢ies
Microbiological MonLnorinK
Terminal Studies
Bodyvelght s
OrEs= weighcs
Hi• topal:ho lol;y
DZSCUSSION
REFERENCES
PAGE NO.
1
4
4
5
5
5
6
7
8
8
9
11
12
13
17
17
18
19
20
40
51
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Group Research & DeveIopme=t Centre,
BrLtish-American Tobacco Co. Ltd.,
SOU~TON.
23rd March 1977
3-)lOFfE .INitIATION TOXICITY STUDY ON RATS EXPOSED TO
,|.~
s.o r oM a C
(Report No. llD.1477 ltestricted)
~:. ~.~,
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An inhalation Cox£city study has been carried out to determine
how chanses An lung petbolo|Ly Lnduced in rats exposed Co smoke £or
six weeks were affected by continufng exposures for up to 12 weeks
and by termfnating smoke treatment.
Animals were exposed to three dilut£on leve:Ls o£ smoke gram a
standard £1ue-cured cigarette. Honltorfng of the smoke concencratfons
to which an£mals were subjected end blood carboxybaemoglob~n levels
o£ animals imned£acely agcer exposure, confirmed that animals Ln the
varlous treament &coups recelve~ sf&ni£icantly di££erent smoke
dosage levels.
Average daiZy good consumption and growth rate were reduced in
sham-smoked end particularly in smoke-exposed rats. Animals fncreased
the£r food consump=£on and shoved a marked increase in growth rate
when both these treatments were stopped.
Hortal£ty rates were d£rectly related to the concentration o£
smoke to wh£ch animals were exposed. The pattern o£ £nd£vidual
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v
mor~alic£ea showed tha~ throughout the study deaths occurred more often
at: the beginning of the week and became less frequent as the week
progressed.
Exposure to smoke did not produce any significant change in heart
or lung we~ht of animals over the 12-week exposure period. Thymus
weights of sham-smoked and smoke-exposed rats were reduced relative
to those of cage controls.
All lesions of the respiratory systa~ previously showu in rats
exposed to smoke were again recorded in this experiment but their rate
o£ development was shown to be di£ferent. Coblet cell hyperplasia o£
tracheal and bronchial epithelia, increased numbers of alveolar macro-
phages, squamous metaplasia and hyperplasla of the larynx were seen after
two weeks o£ exposure to smoke. With the exception o£ tracheal goblet
cell hy~erplasla, after 6 weeks og exposure all these changes showed
a maximal zesponse. These responses were either maintained (macrophages,
bronchial goblet cells) or possibly reduced (laryngul hyperplasla) as
exposures ~ontinued up .to 12 weeks.
The frequency o£ tracheal goblet cell hyperplasia and alveolar
metaplas~a ~acreussed projrssslvely throughout the study.
~hen exposure to smoke was discont£nued, all smoke induced lesions,
excep~ alveolar :etaplasia, rasressed and tissues approached normality
during a holding period of 6 weeks. In contrast., the frequency of the
alveolar me~spLasia induced during the smoke-exposure pwr£od, comt~nued
to increase even when an/~als were not being exposed to smoke.
The pathology findings presented here from those animals exposed to
smoke diluted T:12 with air will be compared with observations made on
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animals from the same experiment exposed to smoke diluted 1:8 with air,
but assessed by an independent investigator. The final conclusions to
be drawn from these combined results, in relation to the design of
relatively short-term irritancy snudies, will be reported separately.
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V
V
I N'I~, DUCTZON
Eerli.er complrat~ve ~nb211eCion toxicicy studies carried out in
Chess laboratories have involved the treatment of animals with smoke
for approx~matel7 6 weeks (i, 2, 3), as sugiested by guidelines relating
to the assessment of smoke toxicity (4).
These experiments consistently produced smoke-induced changes Ln
rat lunZ structure which wre related Co the duration of exposure
end the desree of d~Lut~on of smoke. However, it was not kno~m vhethez
an exposure period of 6 weeks was, in fact, optimal for such short-term
irrltancy studies. The purpose of the experlmenC described in this
report ~ts three-fold:
(i) Co determine the C~ne-course of the funs pathology chanses
induced over a 6 week period.
(il) to determine how such changes developed as smoke-exposure was
extended up to 12 weeks.
and (iii) to determine the effect of stopping smoke exposure on the
changes in lung structure produced by 6 weeks of treatment.
~TERZALS AND METHODS
Cigarette Type
Filter cigarettes (Code H3gl) used for the exper/~ent were made
from a standard flue-cured blend (Blend 72). TPM delivery from this
cigarette to the sn~nal exposure chamber, when smoked under standard
conditions on the inhalation system, was 19.6 ms/ci2aretce. The cigarette
burned to a bucc length of 25 mm in 10 puffs.
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Animals
White albino rats (Strain CFH~) were suppl~ed by Angl£a Laboratory
Antis. The average weiKhts o£ animals on arrival at the laboratory
were; males 200 S, females 170 g. AC chase weights, the animals were
approximately 50 days old. Animals were kept 6 per case on autoclaved
wood shavinss and had free access to food end water.
Exposure System
In this experlmant, an/~als were subjected to frmsh, diluted smoke
on the 5-port version of the B.A.T exposure sTstem (5). A clean machine,
exclusively fOE the "sham-smokinK" of rats, was used to provide appropriate
treatment-control animals throuehout the study.
Exper imencal DesiEn
The b~sic desist of the study is shown in ¥iKure I.
i. Groups of animals were exposed for varylnK periods up to a
total of 12 weeks (ProKrassion). Ln this part of the
exper£ment, an/male were k£11ed on ~he de7 £mmed£ately
foILowinK their last exposure to smoke.
2. Ocher groups of rats were exposed to smoke for 6 weeks, and
then held for up to 6 weeks without further exposure to
smoke Cl~sression).
~t was not possible to expose aLL the Stoups of animals simultaneously,
therefore the start of the e~per£maut was staKKered. The animals in
Stoups I to 7 and 19, plus those in the approprLate control Eroups,
were delivered at the same time. A second delivery of animals, of slm£1ar
eke and weisht tense, was made 5 weeks Later. These animals £o~med
Stoups 9, iO, Ii and ~heir case conErols. One treatment Stoup (6 weeks
cr~
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exposure) was duplicated (Group I and Group 9) so chat comparisons can be
made between ohm animals of the first delivery and chose o5 the later one.
For each o£ these two phases of the whole experiment, groups of
animals were exposed Co smoke diluted 1 in 8 or 1 in 12 with air. One
mddlcional group (Croup Ig) was exposed at the max/mum toierable smoke
concencratlon (dLluc£ou Level I in 7) for g uetks.
AC all chess dilution levels, animals were routinely given 2
x i0 mLnuCe exposures (4 hours between exposures) pmr day on weekdays,
and I x lO minutes exposure on Saturdays and Sundays. Exposure o£
anneals to smoke began on l~th September 1975 and the experiment was
compleced on lath December 1975.
Each rime smoke-exposed animals were killed, corresponding sham-
smoked end case conCrol cars were also Oaken. All groups comprised 6~
and 6~ rats, except the group exposed ac I in 7 dilut£on, which contained
12c~a~,d 12~ rats. In all 468 animals were used.
Observations
TPI4 deliveries from the cigarette to the puf£ generation unLt of
the inhalation system and to the exposure chamber icsel£ were decermined
gray/metrically, alter collection of particulates on Cambridge ££1cer
pads. Smoke concentration within the exposure chamber was zmasured
regularly £or e~ch o£ the 3 smoke dilutlon levels used in the experiment.
Throughout the experi~nent, blood carboxyhaemoglobin levels of samples
were measured as soon ms possible alter exposure to smoke. Blood samples
£rom anaechetised animals (Ketamine hydrochloride I0 mg/lOO g bodywe£ghc)
were taken [rom the orbital s£nus and analysed using an lnscrumentacion
Laboratories CO-Ox~mecer.
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Growth curves and terminal bodywe£ght data collected from previous
studies have shown that exposure to smoke end sham-smoking of animals
retard their rate of growth. To investigate this effect further,
throuKhou~ this study average food consumption of animals was determined
on alternaue days. Food hoppers on the cakes, were filled with weighed
amounts (400 g) of dried, pelleted food. The food was reweiEhed on the
t
following day and the average food consumaptlon per rat per day calculated.
Individual bodyweights of animals were routinely recorded three
times per week throughout the study and the final bodyweight of each
animal was determined iuusedLately before post-aortae examination. All
mortalities, with appropriate details, were recorded.
This study was the longest experiment to date carried out in our
laboratory. Bearing in mind the potential r£ek of infection of animals
held for lone periods, it was considered worthwhile to monitor the level
of contamination of the air in the downstairs inhalation area of the
Life Sciences Building, as an index of the general standard of cleanliness
within the animal unit. To do this, 9 cm plates of blood egar were
exposed for 15 minutes in the work areas. Plates were incubated at 37°C
and counts of colonies made after 2 and 5 days of incubation.
Te.rminal Studies
Autopsy technique, histological examination and quantitative microscopy
have been described (6). The weights of heart, thymus, combined InnK
and trachea from each animal were recorded az pos~-mDrcem. The following
sections were =ned in dar, a£l for each animal in the study: larynx
(transverse to include the central depression and free edge of vocal
cords), trachea (transverse to include tracheal and thyroid glands),
(single left lobe including the main intrapulmonary bronchus and
the maximum amount from the 3 right lobes).
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In this report the results are siren of the in-house examination of
tissues from those animals exposed to smoke at dilutions of 1 in 7 and
1 in 12. Tissues from rats exposed to smoke at a dilution of 1 in 8 were
given to a consultant pathologist and the results of this examination will
be presented separately (7). Control groups of rats were common to the two
main dilution levels (1:8 and 1:12) and material from these animals was
divided equally for examination by the two pathoLosls~s involved.
The pathological examination of material from the" complete experiment
was split for two reasons: primarily, to obtain an independent view on
the treatlnent-induced changes in lung pathology seen in this relatively
complicated study; secondlyp to check the consistency of observations of
two observers using essentially the same semi-quantitative h£sto--pathological
techniques to examine some co~n (control) material.
RESULTS
MonitorinE of Exposure System
(i) CiBarette TPM Delivery
Mean TPM delivery from the buut end of the cigarette was 24.1 mE/
cigarette. Mean ~ delivery to the exposure chamber was 19.6 n~/ciEarette.
Mean TPM loss due to deposition in the puff generation unit of the
inhalation 8ysta--was &. 5 ~/ctsarette.
The los8 of smoke particulate within the puff Ksneration unit.
before transfer of smoke to the exposure chamber itself, was 18.7Z
of the TPM &enerated from the cigarette.
(ii) Co,ncentrati.on of Smoke in Exposure Chambers
Regular s~ling of expolnaEe ch4Lmbers throughout the course of the
study gave the mean smoke concentrations to which animals were subjected
(Table I).
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TABLE I
SMOKE CONCENTRATIONS ~ ± S.D. :) FOR EAC~I DTLUTION
LEVEL USED DUEING THE EXPERIMENT
Smoke Dilution
Level
(smoke: air/v:v)
1:7
1:8
i:12
Smoke
Concentration
Cms/~)
8.5
(o. 5)
6.7
(0.7)
4.7
(0.4) •
Number of
Observat £ons
25
65"
63
Details of the TPMmonitoring carried out durinK the experiment
are shown in Figure 2. This mhows all individual concentration values
for each smoke dilution level monitored throuBhout the experiment.
Moat values (80Z of all samples) were within ~ IOZ of the total mean
smoke concentration (dotted Zines) for each of the three dilution levels
used. Whenever the values for the chamber smoke concentration fell
outside these limits, checks were made to ensure that the inhalation
nmchine was set properly and functloninK correctly. After any necessary
adjustments had been wade, the chamber smoke concentration was re-monitored
and only when this value was wlChln acceptable limits did the exposure
of the animals begin.
Blood Carboxyhaemoslobin Levels
A summary of the blood carboxyhaemoglobin (CORb) levels in 8amptes
taken after exposure co various concentrations of smoke is shown in
Table 2. Mean values for pooled dace from m ale and fmmale animals are
given, mince analysis showed no significant differences in COHb levels
between sexes.
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TABLE 2
BLOOD CARBO~OGLOBIN LEVELS IN ANIMALS FOLLOWING
EXPOSURE TO THREE CONCENTRATIONS OF CIGARETTE SMOKE
Smoke Concentration (mE/i) and (Dilution Level)
mm
8.5 6.7 4.7
(1:7) (1:8) (1:12)
Blood Carb?xThaemogLobin ~Z)..
"Progression" 37.9
(n) (16)
"ReSts s • ion"
(n)
Total Mean . 37 .____99 .
n = number of observations.
35.6
(39)
31.3
(49)
33.5
27.2 "
(~8)
27.5
(59)
27.4
In those animals exposed to the forest concentration of smoke, all
COBb values ware quite similar, at approximately 27.AZ COHb. Values
were higher, though ~hey rended co be more variable, £n those samples
taken from animals exposed co the two highest smoke concentrations,
particularly in those Stoups (6, 7, 10 and IX) in the "Prosrmssion"
section of ghe study.
Mean blood carboxyhaemoglobln levels in an/male were clearly
related to the concentration of smoke to which animals were exposed.
A~alysis of the data did show hishly eLgn£ficant differences in COHb
levels in the relatively Lares numbers of animals exposed to the t~4o
dilution level• 1:8 ~ad lz12. FollowinK exposure under chase conditions,
Charm were no significant differences in COHb levels in rats from the
two separate batches of animals which toKether made up the complete
axperLment (Append~ TabLe 2). An/mals in the Kroups exposed to different
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smoke concentrations were clearly subjected to different smoke dosage
bevels, since it has been shown Chat for this type of cigarette, blood
COab Level gives an ind~catlon of relative TPM dose to the lower
respiratory system (8). Full details of the analysis o£ COHb figures
are g~.ven ~n the Appendix.
Growth ,Rates
All froth curves for the var£ous groups of smoke-exposed an/~nals
p~otted against the appropr£ace contro~ groups showed a similar pattern.
Examples of such curves for two of the more interesting groups of animals
are shown in Figures 3 and 4,
The £amilfar observation of a reduced growth ~ate in smoke-exposed
rats compared with cage control anfmals, with an £ntermedlate Krowth
rate £n sham-mmokers, was a consisteut gind£ng in this experiment.
Generally, there was not a clear difference between growth rates o£
annuals exposed to ~ifferent dilutions of smoke (Figure 3). For those
animals which were subjected to 6 weeks of exposure to smoke and
subsequently held for • 6 week bold£ng period, a different @ro~h
pattern was recorded (Figure 4). Exposure to smoke again caused a
slower rate of growth of animals over the first 6 weeks of the exper/=ent.
When smoke exposure was stopped, the grolrch rate increased markedly and
the bodywe£ghe Kain was close to that og sham-smoked animals after
approxJ-mately 14 days of recovery.
It is not particularly useful co present the complete set of
bodyweight curves for all an~uaals used in the experiment. An overall
assessment of relative Krowth rates of rats in the various experiJeenCal
groups has been made by a simple visual inspection of these curves and
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is g£ven in Table 5. Further details of the effect of treatments on
the bodyweish~s of rats, as assessed by analysis of the final weight of
animals a~ post-mor~em, are siren below.
TABLE 3
,Asszss .z, OF zz xzvz GRo a ZAT oF FROM
BO~IGHT CURVES
Group N~ber
11
iO
9
7
6
I
2
3
4
5
1.18
1.18
i18
Growth Rate
Males
< 1/12 < sham < cage
I/8
I/8 - 1/12 < sham < cage
S L/12 < sham < cage
< 1/12 < sham < cage
= 1/12 < sham < case
Females
1/I2 < 1/8 < sham < cage
118 < 1112 < sham = cage
1/8 < 1/12 < sham < cage
1/8 - 1/12 < sham < cage
118 < 1/12 < sham < cage
II12 < 1/8 < sham (<cage~
118 < 1/12 < sham < case
1/8 - 1/12 < sham < cage
1/12 s 1/8 < sham < cage
19
*caSe control as for group 3.
Food Consumpclon
II7 < slum < case
1112 S 118 < sham < cage
1/8 • 1112 < sham x cage
1112 s 1/8 < sham (<caSe~
1/8 < 1112 < sham < rage
1/12 < 118 = sham < cage
1/8 < 1/12 < sham < cage
117 < sham < case
In this exparlmenC, for the first c~ane, avexese food consumption
of ra~s in the var£ous experlmeutal groups was measured. De~ails of food
consun~tion rates for eli of the groups are not eesent£al and are not
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given here. Representative curves, which show some of the commonly
observed food consumption patterns are shown in Figures 5, 6, 7 and 8.
These include the patterns for chose animals for which bodyweight gain
curves have already been described.
In male rats (Figures 5 and 6), food consumption of cage control
an~Jnals showed a gradual increase from approxlmately 2~ E to 30 E/rat~day
durinE the experiment. Animals which were sham-smoked throughout had a
food consumption rate which wad approximately 15Z lower than that of
cage controls. Animals exposed to smoke for 12 weeks showed a roughly
25Z reduction compared with the cage controls and had a daily food
consumption of about 20-22 8/rat~day. There was no noticeable difference
in food consumption rate between the grou~s of rats exposed to different
dilutions of smoke (Figure 5).
Male rats subjected to 6 weeks of sham-smokinE or smoke exposure,
in comparison with cage controls, showed a reduction in food consumption.
When either treatment was stopped and the en~nals then held as cage
controls, food consumption rose quiCe markedly ov~T approximately 10
days to reach that of the original cage control race. Again, animals
exposed to two dilutions of smoke responded in essentially the same
manner (Figure 6).
Food conJumpcion of all female rate was lower than ~ha~ of the
males in corresponding groups. Nevertheless, trends in food consumption
were generally s~nilar to chose described above for males (Figures 7
and 8).
Mortalities
A summary of all mortalities recorded during the complete study is
given in Table &. Unless otherwLse staCed, all mortallcies occurred
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during or immediately after exposure of animals to smoke. No sham-
smoked or cage control an~nals died, nor did any smoke-exposed animals
~ie during the post-exposure holdinK period of up to 6 weeks.
TABLE 4
TNCIDENCE OF MORTALITIES IN GROUPS OF RATS EXPOSED
TO DIFFERENT DZLUTIONS TO SMO--KE
Group Number
1:7 l:B
1:12
Total pre--tsrmination deaths
Male Female Male Female Male Female
"~ 1 - - 0 I 0 O
2 - - 3 1 0 0
3 - - O 6 0 O
4 - - 0 3 0 O
5 - - 2 I 0 O
6 - - 1 4 0 1
7 - - 1 1 0 O
9 - - 0 2 O O
10 - - O 2 0 0
.~ II - - 1 3 O O
19 4 8 ....
No. deaths/ 4/12 8/12 8/60 24/60 0/60 1160
i | L
No. exposed 12/24 32/120 1/120
Total deaths/ 45/264
Total exposed
Camments
i rat pre&~ant: killed day 47
Male dead in cage overnight
1 rat pregnant: killed day 41
Female dead in cage overn~Khc
m
!m
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Mortality races were higher amongst the female compared with the
male rats. This sex-related difference in mortality has been reported
in earlier studies.
The overall mortality rate Of animals exposed to smoke was low,
with 45 deaths in a total of 264 animals (17Z). Of these deaths, 2
were not related to treatment with smoke. When incidence of treatment-
related death is related to exposure conditions, mortality rate for both
sexes was clearly proportional to the smoke concentration to which the
animals were subjected (Figure 9).
There was no suggestion from the mortality data that deaths
tended to occur paruicularly early in the experiment(Figure I0). For
those groups (i, 2, 3, 4, 5, 9, i0 and 11) subjected to smoke for up to
6 weeks only, the 24 treatment-related deaths wmre spread fairly evenly
throuEhout the exposure period. In those groups (6, 7 and [9) subjected
to smoke for more than 6 weeks, there were 18 treatment-related deaths,
all except one of which occurred within 7 weeks of startln$ tfull'
exposure.
However, super~J~posed on Ehis overall pattern of a fairly steady
death rate for animals over a 7 week exposure period, there was clear
evidence of deaths occurring more frequently on particular days.
Figure [I shows all treaement-relatadmortalities according to the day
of the week on which they occurred, irrespective of the time during the
exper~nent. Clearly, throushout the study more deaths occurred on ~ndays
and Tuesdays than on any other days. and the number of deaths fell as
the week progressed (3 of the 7 deathm which occurred on Wednesdays
involved animals which reached 'full smoke' exposure on that day).
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RANGE
HERE

-16-
Microbiolo&ical Muonltor£n~ (by P.C. Stauber)
The results of monitoring of the air in the work areas shown in
Figure 12 are siven in Table 5. In Eeneral the hiKhest recoveries of
oraanisms weEe made in the anima~ rooms. The number of fungi recovered
was negliKibleP and neither the numbers nor the t-~pes of bacteria (mainly
Nicro~o¢cus types) were considered to represent a hazard.
TABLE 5
MICROBIOLOGICAL MONITOEING OF AIR IN THE WORK AREAS
USZNG BLOOD A~%R SETTLZNC PLATES
1
2
3
4
$
6
7
8
9
I0
11
12
13
14
15
16
17
18
19
20
21
22
Humber Micro-organisms (as Colonies) per 9 cm Plate
,, J
1 Day of Incubation
20
0
43
45
15 (Spr)
44
3
20
4
O
7
2
6
6
4 (Spr)
I0
4
2
5
2
1
5 Days of Incubation
21 (M)
0
45 (M)
50 (M)
16 (Spr)
44 (M)
3
22 (M)
5
I
8
5
15
21
9 (Spr)
12
4
3
5
4
2
1
(M) -mainly M~crococcus
(Spr) - Spreading organism (inhibicm ErowCh of ocher coloniee)
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-17-
Terminal Studies
Previous experiments and the present one, have shown the effects
of smoke-exposure and 8ham-smokinKs on the growth rate of race. In the
earlier studies, corresponding organ weight changes in smoke-exposed
rats compared with control animals have also been suggested. These
chanses have most often related Co thymus, heart and combined lung and
trachea weights (I, 2 and 3).
There are several difglcultlms in the evaluation Of bodywe/ght and
organ weight data which are worth commenting on st this stage. Because
of the relatively large numbers of animals involved in smoke toxicity
e~udies, and the experimental design (staggered introduction and kiliing
of animals), animals may come into a study at different initial body-
weights. Secondly, the treatment to which animals are subjected durin8
such studies reduces ~heir rate of weight gain compared with cage or
shamosmoked control rats. Clearly such an effect, due largely to a
reduced deposiclon of body fac in smoke-exposed animals, could influence
the relative weight of an organ (weight of organ/lO0 g bodyweight of
animal) in the absence of any real treatment-induced change in the
weight of the organ icself.
In an atte~pn to overcome such problems, statistical analysis of
term/hal bodyveights and organ weights from this study has been based on
the use of absolute values only, with an appropriate correction of .the
iniclal bodyweishcs of the animals.
A gunnery of the findings of this method of analysis is Elves and
details of the statistical work are available if required. The correct
analysis and interpretation of organ weight dace from toxicology studies
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-18-
V
still presents several di££iculties (9, IO) and work is continuing on
this aspect of our investigations.
Bo d~n~e ~ght s
Final bodyweights of animals killed at intervals throughout the
study are shown in Figures 13, 14, 15 and 16. For both sexes, a similar
gro~h pattern emerged. Weights of smoke-exposed rats ~ere s£gni£icantly
lover than the corresponding control animals after 14 days of treatment,
and remained so throughout the exposure period which extendedup to 12
weeks. The weights of animals (both sexes) exposed to both dilutions of
smoke were never significantly different. Initially, sham-maoked and
control animals had similar bodyweishts, but £or both sexes a significant
reduction in body~elghC of sham-smoked animals compared vlth cage controls
occurred a£ter ~2 days of shmm-amoking. Thereafter. the body~eighc of
sham-smoked animals remained intermediate between ChaC of the case control
and the smoke-exposed rats (Figures 13 and 1/+).
In those anJ~za18 which were exposed to smoke for 6 weeks and then
kept for a further 6 weeks holding period, the di££erences £n bodyweight
between s~oke-exposed and controls at the end of the 6 weeks exposure
period were as described above. During the boldi~ period, male rats
previously exposed co smoke recovered in about 3 weeks co achieve the
bodywtight of correspond~ sham-smoked animaZs. Neither of these two
groups grew su~£iclenCly to reach the weiKhc of male cage control rats
over the 6 weeks holding period (Figure 1S). Fmnale smoke-exposed and
sham-smoked animals grew more rapidly and reached the body~eight of
corresponding cage control rats between 3 to 6 weeks after the cessation
of treatment (Figure 16).
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BATES
RANGE
HERE

-19-
OrEan Weight s
Thymus
In all Kroups of animals, control and smoke-exposed, thymus weight
fell throughout the exper~enc. After 2 weeks of smoke exposure, thymus
veishts of both male and female animals were lower than those of the
corresponding cage and sham-smoked controls. As the experlmenc continued
this separac£on pers£sced in the male animals buc ~as less dLsc£ucc,
chouKh comparable in the females.
Those animals exposed =o smoke for 6 weeks showed the reduced
thymus we£gh: compared wlth both sets of control animals. After smoke
exposure had stopped, within 1 week thymus weights of all animals were
noC 8isnif£canCly different, and remained comparable over the remainder
of the post-exposure holdinK period.
Heart
There was no consistent effect of tTsa~nanc, either smoke exposure
or 8ham-smokinK, on heart weiKht of male or female animals subjected to
up co 12 weeks of exposure. Heart weiKhcs in smoke-exposed animals
which were allowed a 6-week post-exposure observation period were not
stKnificantly different from cot'respond~nE 8bent-smoked and caKe-control
r&~s.
Lunls and Trachea
There was no cons£stent effect of treatment, m£ther smoke-exposure
or shaw-smok£nK, on funk and trachea welg.hc of male or female animals
subjected to up to 12 weeks of exposure. Lung and trachea weights in
smoke-exposed animals which were allowed • 6 week post-exposure observat£on
period were noc siK~/fLcancly d~fferenc from correspondlnK sham-smoked
and cake control race.
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H£stopathology
Changes seen in rJhe lungs of animals corresponded with those observed
in previous inhalation studies and can be divided into the following:
I. Peribronchial lymphatic tissue
2. Perivascular lymphatic tissue
Non-smoke
induced chanKes
3. Focal pne~oD/tie
ldi,tce llaneous c~utnKe s
9
6.
7.
Incipient alveolar metaplas~a 1
Alveolar macrophage activity
Goblet cell byperplasia
Smoke induced chan~es
1. Peribronchia!Lymphatic Tissue
Concentrations of lymphocytes were found in aver7 rat especially at
the junction of the bronchi and bronchiolee (Table 6). In certain cases
they a~reSatad between ~he airways and adjacent blood vessels. Larse
foci found in the lamina propria of the main bronchi invaded the smooth
muscle layer, apparently dLvidL~ it into discrete blocks. In @xtrlme
cases the bronchial aplthaLiumwas d£sruptedand there was deciliatlon
and loss of Boblet cells toEether winh attenuation of the columnar
epithelium cell.
C~
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BAT Co LTD - MINNESOTA TOBACCO LITIGATION
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-21-
TABLE 6
NUMBER OF RATS WITH PERIBRONCHIAL LYMPHATIC TISSUE
v
2
11/11
Exposure to Smoke (weeks)
4 6 9
12/12 11111 12/12
12/12
12/12 11111 10/10 12112 12/12
,,,n,
1 4 7 21 42
~lding Period (days) After
6 Weeks of Exposure
All
Sham-
Smoked
Animals
30/30
30130
All
Cage
Control
Animals
30130
All
Sham-
Smoked
Animals
30/30
All
CaEe
Control
Animals
The difficulty in assessing the extant of the lymphocytes (due to
variation ~n 8xact plane of section of the three right lobes) made Kroup
comparison impossible and che£r frequency in 811 jroups could be
regarded as within 'normalt limits,
2. Perivascular L~nphac£c Tissue
In all rats, at least one vessel was assocLated with 8 focus of
'lymphocytes whLch often completely surrounded and penetrated the outer
adventitial layer. The lymphatic tissue was often found between blood
vessels and adjacent broncbioles. Mnltiple per£vascular cuffs (more
than five blood vessels per luns section surrounded by lymphatic t£ssue)
were common end their frequency was reduced by smokm exposure (Table 7).
Eats exposed to smoke for 4-12 weeks had reduced 17mphatic tissue
compared with those exposed to smoke for 2 weeks only end control
SToups. Animals held for up to &2 days after exposure showed varying
amounts of per£vascular lymphatic t£ssue apparently returninK to normal
OQ
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RANGE
HERE

-22-
values (Figuce 17). Variation £n control values however makes detailed
comparison difficult.
TABLE 7
|,.,
NUMBER OF RATS WZTH MULTIPLE PEItZVASCUI.qR CUFFS
2
411o
~3Z
Exposure to Smoke (weeks)
4
0/12
OZ
6
1111
9X
9
o112
OZ
12
0/12
OZ
All
Sham-
Smoked
Animals
1313O
43Z
All
Cage
Control
Animals
8/3O
26Z
1112 2/11 0/I0
8Z 18Z OZ
1 4 7
2112
17Z
21
0112
OZ
42
Holding Period (dmye) After
6 Weeks of Exposure
8/30
26:[
All
Sham-
Smoked
Animals
3/3O
lOZ
All
CaKe
Control
Aulmals
3. Focal Pnmmonicis
Pneumonitis is an tnflumation of the lung and in the rat manifests
itself as lymphatic tissue invading the alveolar wall and eventually
the lumen of the alveoli. There is an increase in macrophage activity and
thickened walls due to infiltration of lymphocytes and/or an increase in
alveolar cells. In extreme cases, the alveolar tissue is lost leavinE
larse areas composed solely of inflammtr.ory cells. Focal pneumouiti8
develops as peripheral extensions of pLTibronch~al and vascular lymphatic
tissue, as wall as from small discrete sub--pleural sites in the alveolar
tissue. Theme sites were co~n but not recorded.
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-23-
In all, 34Z of all the lungs examined showed signs of focal
pneumonicis (Table 8). Of these, 51Z also had multiple perivascular
cuffs. Of the 39 samples of perivascular cuffs, 31 also showed
focal pneumonicLs. The variation in control values made comparison
difficult bur clearly exposure to smoke greatly decreased the incidence
of focal pneumoniuis in the rac lung (Figure 18). RaCe held after
smoke exposure also showed decreased lymphac£e acrivit7 buc Co a lesser
degree than animals continuously exposed Co smoke. D~iug the. pose-
exposure periodm these changes showed signs of return/~g Co normal
values •
TABLE 8
N.m~SER OF RATS Wlrn~OCaL P~EUMONXT~S
Exposure Co Smoke (weeks)
, , e
2 4 6
6/8 3/11 2/11
75Z 27Z 18Z
9
2112
17Z
12
1/12
BZ
&11
Sham-
Smoked
Anlmals
17130
54Z
All
Case
Control
Animals
1313O
46X
3/12
251
1
3/11 3110 [ 3/12
27Z 30Z[ 25Z
4 7 21
4/12
33Z
42
HoldinsPeriod (days) After
6 Weeks of Exposure
12/30
40Z
All
Sham-
Smo ked
Animals
12130
4OZ
All
Cage
Con tro 1
ani,~,l s
The above three leslons are cle.zrly related, there being a progressive
reaction co a viral infecclon (11). This is seen as perlbronch~al infection
leading to vascular and multiple perivascular cuffing whLch in turn
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INDEX
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RANGE
HERE

-24-
produces a pneumonitis. Such a progression appears to be age related
£n 'normal' colonies. Exposure Co dilute cigarette smoke decreased
substantially the reaction of rats to the respiratory infection by a
virus. This is particularly noticeable when animals with both pneumonitls
and multiple cuffing are compared on a group basis (Table 9, Figure 19).
TABLE 9
NUMBER OF RATS WZTH BOTH MULTZPLE PERIVASCULAR CUFFS
AND FOCAL PNEUMONITIS
2
4/10
40Z
Exposure co Smoke (waeks)
4 6
0112 1/11
0% 1%
9 12
o112 oi12
OZ OZ
A11
Sham-
Smoked
Animals
LI/3O
36Z
All
Cage
Contro I
Animal s
7130
23Z
0112 1112 0112 2112
m,,, , ,, '
0112
OZ IZ OX 2Z OZ
1 4 7 21 42
, ,| , _ ,
Holding Period (days) After
6 Weeks of Exposure
6130
20Z
All
Sham-
Smoked
Animals
3/30
IOZ
All
Cage
Contro I
Anisals
4. Mist ellannous Changes
A bone ~obbec embedded in the subpleural alveolar Cissue producing
no inflmmmaCo%7 rmacC£on, occurred in one raC. The evaluation for
possible a~physmua was hoe a~cempCed due co variacions in lun8 inflation.
In two rats mucus filled a number of alv~Imr ducts, ~n one such case
there was also advanced alveolar mecmplasla. Fool of pink macrophages
were nor uncommon in the parenchyma (hlstiocytosis) and blood vessels
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BATES
RANGE
HERE

-25-
occasionally ve~e couSested, probably due to delay in lur~ £nfl&t£on
during autopsy. 1~e presence o£ oedematous tissue is unexplained but
again is probably an artifact produced by the autopsy procedure.
5. Alveolar ~tt&~l~.a£a
Alvevl~ meteplas~ may inic~nlly be confused w~th focal pneumon£Cis
since in both lesions there £s an increase in alveolar walI thickness
and in macrophase acc£vicy. However, they can be d£stLnKuiehed by
cons£dez£~K the s£te o£ occurrence coKether ~r~th the maczophase and
lymphocyte populetiouus.
2n rate exposed to d£1uce smoke for 6 weeks or more, clusters of
macrophaKes were £ound in ~he reKion of the teru~nal bronchioles end
associated 81veolar sacs and ducts (Table IO, Figure 20). They were
large, vee~olated, £rrejular in out1£ne and piKmented, often with jolden
brown cy~oplaa~c inclusions.
~xp,.p- lo
~-~ER OF ~x,S Wn-~ ~n~LZ ~OCZ OF,~C~O.P~CES
2
0112
0]{
Exposure to Smak8 (yacks)
, ,. , --
4
0112
0]{
6
3111
27]{
9
6722"
5OZ
t2
10112
83Z
&11
Shmn-
Smoked
0/30
OZ
All
Cage
Control
Jmizmls
0/30
OZ
3111
27Z
4
2/12' 8/12
17]{ 4AZ 67Z
i | m
1 7 21
Holding Period (days) A~tez
6 Weeks 0£ Exposure
9/12
75Z
&2
1/3o
,3Z
All
Sham-
Smoked
Animals
0130
OZ
All
CaKe
Control
&n~als
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RANGE
HERE

-26-
The number of rats showing multiple clusters of ~crophages incrQased
with both cont£nuous exposure and also during the post-exposure holding
period. At low magnification their distribuCion was clearly seen Co be
adjacent to the alveolar ducts and termfnal bronchloles, especially in
animals exposed for 12 weeks when the lungs in section had a distinctive
mottled appearance. 0f the A5 rats v£th ault£ple clusters of pigmented
macrophages. 32 (71Z) had thLckenad alveo3~r ~mlls. ThLs thickening
appeared usually as d£sor~an£sed hyperplas£8 or =etapias£a, ~rLth the
alveolar epithel£um made up og well-orlen~ated cuboldal cells. Zn one
rat (exposed £or 6 weeks end with 4 days holding period) metaplasia was
advanced with veil developed cuboidal cells surrounding several alveolar
ducts contalning darkly pioneered macrophages. A great deal o£ the
parenchyma consisted of sheets of spindle shaped calls cent=ed around
alveolar ducts and teru~nal bronchi~les. Lymphocytes were often present
in the lesions. The lesions shoved an increase Ln reticulin content,
suggestJ.ug a possible f£broeie.
Incipient mataplas~a or true metaplas~a was not observed in control
=acs or those exposed to dilute smoke for 2 and & weeks. Of the remaining
groups the i~cLdance of ~taplaa~a i~crQased with increased exposure.
For rats held after 6 weeks exposure an /:creased proportion of the
anilnals showed a develoumtent of alveolar metapl,asia even in the absence
o£ further smoke exposure (Table ll, FiSurm 21). 'Homer, on average,
the extent o£ the las£on in any one lun8 d£d noc increxse (Table 12,
Figure 22).
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RANGE
HERE

-27-
TABLE II
m
NUMBER OF RATS WITH ZNCIPXENT ALVEOLAR METAPLASZ.A
2
0/9
OZ
Kxposurt co Smoke (weeks)
4
o112"
OZ
,,,i
6
1111
9%
9 12
,.m
4112 9/12
33:[ 7SZ
All
Sha~-
Smoked
Animals
0130
OZ
A11
Case
Control
A-~,ul8
i •
0130
OZ
.... d
1/12
8Z
1
2111 319 51!2
181 33Z. 42Z
4 7 21
|,
7112
48Z
42
HoldS.rig ¥erlod (days) &feet
6 Week~ of Exposuce
0130
OZ
&11
Sham-
Smoked
An£mals
0/30
OZ
All
CaKe
Cout:rol
Anl.mals
2
0
ii
Ex-posure co Smoke (weeks)
l,
4 6 9
0 16 16
12
35
All
Sham-
Stoked
AnLmLs
O
..... I
18 13 12 2O 15
,. m
1 4 7 21 42
li ii
HoZd£n8 Paziod (days) After
6 Weeks o£ Exposure
• | , .,|
0
&11
Sham-
Smoked
A~imais
Al1
Case
Control
An~nal8
O
0
Al1
Cage
Control
Ani-~- ls
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-28-
6. Alveolar Macrophazes
LunKs vhich were reK•rded •s incompletely £nflated were not assessed.
The n~nber of alveolar macrophages in a sub-pleural strip 3 uzn long (area
0.54 sq. ~) on the fnner surface o£ the left lobe was counted as an index
of the macrophage population. Only cells whose greatest dimension was
10 ~m or more were counted, their shape varying from spherical to
elongate. Usually • central single nucleus was present but binucleate
cel~s were also observed.
The macrophages were often pigmented in the smoke exposed rats (and
occasionally in control rats) and either adhered to the alveolar cells
or were free in the alveolar spaces. Intensity of pigmentation did not
closely relate to the duration of the ezposure perfod. Although
macrophage counts varied cons~dezably within any one group of animals,
group mean values showed an ~ncrease to a max~numat 9-12 weeks of
exposure. Animals held for up to 42 days post exposure showeda fairly
rapfd return to 'normal' values during the holding period (Table 13,
Figure 23). All smoke exposed rats had greater counts than their
equivalent controls.
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BATES
RANGE
HERE

-29-
TABLE 13
GI~OUF MEAN COUNTS OF ~CROPI~GES (> I0 ~am~ in 0.54 sq.
OF suB-PLEur~n P,.~NCHY~ (s .D.
, • ,, •
Exposure to Smoke (veekB)
2
9
(5~
4 6
, i ,
17 20
(93 (8)
9 12
22 22
(12) (8)
All
Sham-
Smoked
Animals
All
Cage
Control
Animals
4
.(2)
21 19 15
(16) (8) (13)
1 4 7
HoldinK Period (days) After
6 Weeks of Exposure
6
(3)
15 7
(8)(5)
2142
All
...... Sham-
(2)
All
CaKe
Control
Animals
7. Bronchial Goblet Ceils
There was no indlc•clon of hyperpl•sia or metaplasi• of the
bronchial epithelium of smoke-exposed rats. Ther• was however • loss of
soblet cells, deciliation and attenuation of the epithelium caused by
perlbronchLal lymphocytes in the underlying lamina propr~a (or the agent
¢aUB~ the foc~ of lymphocyte•?). Altbaush there was some lOBS of
goblet cells due to lymphatic tissue, goblet cell activity in the
bronchi increased due to exposure to dilute smoke.
The goblet cells in the bronchi varied considerably in appearance
and sta£nin$ re•orlon. The majority vere seen only as caps of acl4
KlycoproteLn with basal $ranules of neutral SLycoproteins. Fully
differentiated 'goblet' shaped cells were uncommon. Difficulty •roBe in
interpretation of the nature of the secretory material due to the necessity
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INDEX
HAS
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GAP IN
BATES
RANGE
HERE

-30-
of altering the staining schedule during process£nK. For this reason,
absolute quantification of bronchial goblet cells was not possible. Thus
a method of gradinE was used for a fixed site between junction 1 and 2
on the main left bronchus. No adjustment was made for areas affected
by lymphau£c cissuep but funks not clearly showing the area were discarded.
The grading sysn*m proved Co be accurate and repeatable and a convenient
means of overcominE cell variation.
The soblet cell population of the bronchi increased with /ncreasin8
exposure reaching a maX',hum at 6 weeks. There was no apparent increase
in numbers of fully differentiated Eoblet cells in rats exposed to dilute
smoke for periods lonKer than 6 weeks (Table 14, Figure 24). Tb~se
rats held for 42 days post-exposure showed a reduction in Eoblet cell
activity which was gradual at first but became more marked bmtween 3rd
and 5th weeks post-exposure. All smoke-exposed rats had hlgher values
for Eoblet: cell population than the control Stoups.
TABLE 14
ESTIMATED GOBLET CELL DENSITY IN FIXED SZTE OF
LEFT ZNTRAPULHD~RY BRONCHUS
2
1.2
Exposure to Smoke Cweeks)
|, ,i i m • , m
A 6
2.0 2.6
9 12
, an
2.5 2.7
All
Sham-
Smoked
Animals
0.4
All
CaKe
Contro 1
Animals
0.4
2,5 Z.2 2,3 2.3 1.O
1 4 7 21 42
i
Holding Period (days) After
6 Weeks of Exposure
All
Sham-
Smoked
Animal s
0.4
All
Case
Con fro 1
Animal-.
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-3~-
Trachea
A single transverse section of the trachea was taken near its
~unction with the lar3ntx. The tracheal lumen was lined by pseudo-
stratified ciliated columnar epithelium often with loci of non-cil~ated
columnar calls dorsally. These calls are seen typ£cally in sl£ghtly
more anterior sections. Differences in the exact level of section or
damage due to sectioning precluded the estimation of epithelial height,
which varied considerably. A subjective appraisal suggested a l~ossible
hyperplas£a or hypertrophy of the lining cells of the trachea from the
animals exposed to smoke. The irregular distribution of cillated cells
in chase animals was normal. There was no evidence to suggest ~ncreased
or decreased ciliary activity.
Foci of lymphocytes in the lamina propria were found in both
control and exposed 6roups and their distribution was not smoke-related,
although in one group of cage control rats, 33Z of the sections had
foci of lymphocyces (Table 15). The epithelial cells adjacent to such
loci were in some cases attenuated, uon-ciliated columnar or squamous
in one or two rats. This squamous metaplasia associated with lymphatic
tissue ks not common but has been noted by several authors (12, 13, 14, ~5).
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'v
TABLE 15
N~.R OF RATS WITS FOCr Or LXMPSOC~ZS IN THE
,u az PROPRIA
2
2/12
17Z
Exposure to Smoke (weeks)
4
1/11
9%
6
1110
i0%
9
o/ll
0%
12
2/12
17X
All
Sham-
Smoked
Animals
1/30
3%
2/12 0/12
17Z 0%
1 4
3/12
25%
i,
7
3112
25%
21
0112
0%
Holding Period (days) After
5 Weeks of Exposure
42
2/30
7%
All
Sham-
Smoked
Animals
, ,,,,,
All
Cage
Concrol
Animals
I0 / 30
33%
4/30
13%
All
Cage
Control
Animals
Goblet cells were scarce in this re&ion, again making group
comparisons difficult. In order co indicate any possible variation, a
simple parameter co suggest goblet cell hyperplasia was the presence of
more than five goblet, cells per section. On this basis all the smoke-
exposed groups showed an increase in goblet cells compared with the
control groups. The number of rats per croup showlnE hyperplasia
increased with the duration of exposure over the 12 weeks of the
complete study. Of the rats held after 6 weeks of exposure, the goblet
cell population rama£ned stable for 21 days, and returned to normal
values by the 6th week poet-exposure (Table 16, Figure 25).
In most cats the tracheal mero'a~cum $1ands and ducts varied in
size, distribution and secretory content and the ducts were often
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d£1ated. No group differences were apparent either in the extent of the
glands or the nature o£ their secretory product.
TABLE 16
NUMBER OF RATS SHOWING GOBLET CELL ,,EYPF.RPLASZA
IN TILE , UPPER TRACHEA
3/12
25Z
Exposure to Smoke (weeks)
4 6
2112 4110
17Z 40Z
9
5/12
42Z
12
7/12
58Z
&11
Sham-
Smoked
Animals
, ,m, ,!
1130
3:[
All
CaKe
Contro 1
Animals
,,, , •
L/3o •
3Z
4113 3/10 3110 4/12
331 30Z 30~ 331
1 4 7 21
lioZding Period (days) After
6 Weeks of Exposure
42
I130
3~
Smoked
Animals
1/30
3Z
All
Cage
Centre l
Animals
LarynX,
A transverse section was taken to include the aryteuo£d cartilage,
the free edie of the vocal cords and the ventral depression. Xn this
area the ~ypas of epithelia and their distribution in control animals
were as daacribed prevloualy. In all the rats expoaed to dilute smoke
nhers were rapid, consistent chanses in the larFnxwhich were related to
both the exposure and the holdlns pgrlod. On the ventral surface, the
columnar epithelium of the floor of the larynx was replaced by squamous
cells, often associated wish a fully differentiated strat,-- corneum.
A11 but two of the mke-exposad rata, wen those which had had only
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2 weeks of exposure Co smoke, showed siKns of squamous mecaplasie in the
larynx. This chanKe was sufficient to identify a smokeoexposed animal
instantly (Table 17). In several rats, loci of columnar cells persisted
on the ventral surface. This is referred to as an incomplete metaplasia
and in the animals exposed from 2-12 weeks its frequency was not smoke
related •
In the animals held for up to A2 days following Bmoke exposure
there was a rapid loss of keratin and s decrease in the epithelial width
on the ventral surface. The number of rats with incomplete metaplasla
increased with the length of the hold~ns period. Two animals held for
21 days showed no signs of metaplasia. Of the animals held for 42 days,
only one showed a complete meceplasia at the end of this time. In order
to quantify further 8quamoua metaplasia in the larynx, rats were noted
when the entire larynKeal lumen in section, was Lined with well
d£ffersnciaced squsmou8 cells. Such • marked squamous mer~tplasia
proKreseed and was maximal after 6 weeks of exposure. When smokinK
stopped this particular lesion regressed quickly and was not apparent in
rats held for more than one day after 6 weeks of smoke exposure (Table 18).
AS before, the ventral depression showed no 8iKns of metaplaeia.
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TABLE 17
NUMBER OF RATS W'£TH SqUANOUS HETAPLASZA OF THE
VENTRAL EPTT'I~LIUM ('rNCOMPLETE HE Tj~LASIA)
Exposure to Smoke (weeks)
2 4
11111 12112
(3)
6
_ , t
1O11O
9
11111
(1)
12
IIIIi
(I)
All
Sham-
Smoked
Animals
0/30
A11
OaKe
Contro 1
Animals
0/30
m
12112 1.2112
(1) (3)
1 4
~x/xl 10112
(6) (6)
7 21
IIIii
(1o)
42
Holding Period (days) After
6 Weeks of Exposure
0/30
All
Sham-
Smoked
Animals
0/30
All
CaKe
Control
Animals
v
2
5/i1
TABLE 18
NUM.KR OF RATS WITH FULLY D~,FFE, KENTIATED SqUAMOUS
~x'rem.nm Ln~Zsc "raF. ~XmU~L U~.
Exposure to Smoke (weeks)
4 6
5112 8/10
9 12
.,|
4/11 5/11
&ll
Sham-
Smoked
Anlmals
0/30
All
CaKe
Control
Animals
0/3
ii i= i
9/12 0112 0111 0112 0/11
1 & 7 21 42
Holding Period (days) After
6 Weeks of Exposure
0/30
All
Sham-
Smoked
Animals
O/30
All
CaKe
Control
Animals
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-36-
On the ventral, medial aspect of the vocal cords, which represents
its leading edge, squamous epithelium was normally £ound and was
invariably hyperplastic in smoke-exposed rats. A fully differentiated
stracLuu corueum also developed. There were several examples of
paraker&tos£s which was recoKnlsed by the presence o£ nuclei in the
stratum corneum. Their £requency was not related to the duration o£
exposure. In order to quantify hyperplasia, the th£ckest uniform reKion
o£ epithelium was measured, including the stratum cornaum, if present.
The deKree of hyperplasia in the larTnx reached a umacimum ~cer s£x
weeks o£ exposure and decreased sliKhtly as exposure continued up Co 12
weeks. Kacs not exposed Co smoke a£Cer 6 weeks showed a rapid return Co
'normal' values during the 42 days holding period (Table 19, Figure 26).
The presence o£ a fully d£££ezentiated stratum eorneum £ollowed
the pattern o£ the sqcumous hyparplas~a, but 4t relrassed ac a lascar
rate wheu exposure to smoke ended (Table 20, ¥£gure 27).
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-37-
TABLE 19
~Pz~s~ oF T~ EPrr~LI~, L~NX.G T~ ~VL~ ,sFzc~
OF ,T~ VOCAL CORD. CROUP MEAN THZCK~, SS ZN ~m,(S.D.)
2
41
(16)
Exposure Co Smoke (weeks)
w
4 6
39 54
(8) (t4)
9
44
(9)
12
ii
45
(4)
All
Sham-
Smoked
Animals
25
(8)
A11
Case
Con ~ro I
Animals
22
(8)
51
(tZ)
i
41 30
(7) (8)
4 7
33
(zt)
21
29
(8)
42
~id£n8 Period (days) After
6 Weeks of Exposure
24
(8)
All
Sham-
Smoked
Animals
23
(5)
i,
At1
Case
Cont;rol
An£mals
TABLE 20
NtR~EIt OF RATS WZTH. I~JLL¥ DZI~FEEENTLATED STRATIR~ CORNEI~
ON MEDIAl, ASPECT OF THE VOCAL CORDS
Exposure to Smoke (weeks)
2
4/xx
36Z
4 6
8/12 10/10
67][ IOOZ
9
12
All
Sham-
Smoked
Anlmals
2/30
7Z
All
tale
Control
Animals
0/30
O~
10112 2/12 I/I.]L
83Z 17g 9g
,i ,,,11 ,ll
1 4 7
li~idixtg Period (days) After
6 Weeks of Exposure
3/1.2 0/1.1
25Z Og
21 42
0/30
Og
0/30
OZ
a m i
All
CaEe
Control
Animals
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o'x
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O'x
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................................................... -'T

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HERE

-38-
In the ventral lamina propria £oci of lympbocyces and cysts
(often conca£n~ axudaca £nflmcory cells), were coa~on and observed
~.u bach control and smoke-exposed Stoups. The frequency of 1ymphaC£c
C£ssue did noc appear to be affected by exposure co smoke (Table 21).
TABLE 21
NUMBER OF RATS ~ITTH ¥OCI2 OF LYI41:HOCYTES VENTRAL L~lnqA PROPRLA
2
Exposure ¢o Smoke (weeks)
1/11
9Z
4 6
9
12
2/11
18Z
All
Sham-
Smoked
An~ls
2130
7Z
All
CaKe
Control
Animals
2/30
7Z
z/z2 311z z/lz z112 Zlll
8Z 25Z 9Z 17: 18=
• ,s,
1 4 7 21 &2
BoldLug Period (days) AJ~Cer
6 Weeks o£ Exposure
2/30
7Z
Al1
Sha~-
Smoked
An£ma Is
4/30
13:[
AIZ
Case
Control
An/~als
The frequency of sara-mucous glands in the larynx varLed cons£derably
and no group differences were discernabLe. There was a marked decrease
in number of animals show'eLK mucous glands in r.he vent:al lam£na prop=i.a
vhen compared v~cb prsv£ous jcudiu, due a)Jnosc cercaiJzly 1:o the sections
be:Lng more poscarLor. The am:aug glands of 1:he vocal cord were the
predoa/J~ant for: in Ch£s study.
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-39-
Rats of Group 19 were exposed to smoke at a 1:7 dilucion for 9
weeks and autopsied the day after Chair final smoke. The changes in the
respiratory tract were sim£1ar in type to those found in the rats
exposed to smoke for 9 weeks at a dilution of 1:12 (Group 7).
TABLE 22
COMPARISON OF STAGES TN LUNG PATHOLOGY FOLLOWING EXPOSURE OF ANIIdALS
TO 2 DILUTIONS OF SMOKE FOR 9 WEEKS
V¸
| , ,,
Peribronchial lymphatic tissue
Multiple perivascular cuffs
Focal pne~nlti s
Perivascular cuffing + focal
pneumoni tis
Alveolar meraplasla
Clusters of macrophagas/lung section
of rats with alveolar mataplasia
Alveolar macrophase activity
Bronchial soblet cell index
Lar~ux
Sq uamous msr.aplasia
Squamous byperplasia (vocal cord)
Karatinisanion on the vocal cord
Trachea
Goblet cell hyperplasla
Smoke DiluclonLevel (smoke: air)
1:7
8/8 ClOOZ)
0/7 COZ)
1/7 C14Z)
1/7 C14Z)
7/7 (looz)
42 (approx)
32
3.0
7/7
55 um
5/7 (7~Z)
2/8 (25X)
I
1:12
12112 (100%)
0/12 (OX)
2/12 (17X)
0/12 (ox)
&/12 (33Z)
16
22
2.5
ll/ll (1)
44 ~m
8/11 (73Z)
5/12 (&2Z)
However, the observed chuq;es were senerally more severe in che
hiKher dose Eroups (Table 22). In part£cular, the extent of alveolar
metaplasia increased as did the severity of the lesion. In one rat from
Group 19 c£11aced euboidal cells were seen lining part of the alveolar
O~
C~
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duct. Bronchlal goblet cell and alveolar mscrophage numbers, also
showed a marked increase in those animals exposed to the higher
concentration of smoke. Zn these animals, the larynx 81so showed more
severe squamous hyperplasia, although the percentage of rats per group
shoving signs of keratinisaeion was not increased.
The only parameter to show an apparent decrease in those animals
exposed to smoke at 1:7 dilution was tracheal goblet cell hyperplasia.
DISCUSSION
The TPM figures for average chamber smoke concentration were obtained
by setting the exposure system to produce one of the specified dilutions
of smoke, exactly as for an animal exposure. Prior to any animals being
exposed in 8 morning or afternoon session~ the chamber concentration was
measured and compared to the theoreulcal result which had been calculaUed
assuming each cigarette had an identical TPM and than no losses occurred
during sampling. The results obtained were considered satisfactory £f
they fell within the range _+ lOS of the predicted value. Those results
which fell o,tside of thls baml were /mmedletely notified and the person
who had achieved the result was responsible for dismantling the engine
in quesuion, cleaninK and reassemblinK it. The exposure of the rats to
smoke did not start until the value for the chamber monitored smoke
concentration was winhln fOX of the predicted value. The most conmon
causes of the £nltial variation belnE incorrect.assembly of an engine or
the sampling system, inaccurately set puff volumes, or the presence of
small leaks in the sampling system. Bearing in mind the simple monitoring
technique used to assess smoke concentration, that up co iO different
techniclans were involved with the monitoring and that unselected
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-41-
tiE•reties were used, chamber monitoring showed clearly that animals in
the various Eroups were subjected to dlsvinctly different exposure
conditions, and hence v•ryinK "doses" of smoke.
Monitoring of b~ood COHb levels, which were quite different ~n
animals exposed no the three smoke concentrations used, else confirmed
this. Real differences in treatment of animals subjected to different
exposure conditions are obviouJly • prerequisite for proper interpretation
of any changes in the physiology or patholoKy which u~Kht be 8ttrlbuted
to the inhalation of smoke.
I~ previous experiments comparison of groups of rats receiving the
sane treatment has been for Kroups from different intake batches.
AlthouKh previously no consistent differences in COHb levels in such
£roups have been found, any differences that did occur could have been
taken to be batch dependent. This current study is the first one in
which it has been possible to compare directly COHb levels in Kroups of
animals from the same intake batch which have also received identical
treatment. The results from this experiment indicate clearly that there
may be differences in COHb levels between Kroups £rom • sinKle intake of
rats, with all the animals subjected co the same treatment. (Appendix.
Table I, Groups I-5; &ppendlx, Table 2. Groups 6, 7, I0 and II), which
are statistically 81Kn/ficanr at levels comparable to those seen
previously when between-batch ec~parisonm have been made.
In fact, the COHb dace from this study and also more importantly
the patholoKy findings (top of paKe 4A) show that in this experJJnent
there is no difference beL3eeen batches o£ animals from the same source
taken into the laboratory within a week or two of each other.
0%
CO
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lc is difficult to set an accurate determination of COHb levels in
rats. A cause for concern are the problems associ•ted with, for example,
the rapid change in COHb levels after mmoke exposure is completed, or
differences in behavioural remponse of rats which may influence the
amount of smoke inhaled. Because of such problems •11 blood COHb levels
in studies much •s this should be taken •s • relative index rather than
an absolutely reliable measure o£ smoke dosage.
The familiar observation was 'again made of • reduction in growth
rate of both sham-smoked =_n-d smoke-exposed animals compared with cake
controls. Gro~h race was least Ln smoke-exposed rats, but no
differences were seen in the weight gain of animals subjected to
different concentrations of smoke. Measurements of growth rates of
animals are useful in that the appearance of • recognised response Co
treatment confirms that an experiment appears Co be proceeding satisfactorily.
Unusual growth patterns of indivlduals or groups of animals could possibly
indicate some inconsistency in •tenement. Our experience at this stake
indicates chat the m~amurmRent of bodywe£ght alone is of no value ms an
£ndex of relative toxicity of different dose levels of a smoke, at least
within the range which we c~nly use for our work.
In this study, m~asurament of food consumption showed that weight
loss in sham-smoked and smoke-exposed animals is due Co • reduction in
food intake which is reversed when treaemenc mc~ps. Whether the change
in food consumption accounts for all of the observed changes in body-
weiiht, and whether smoke exposure also causes • simultaneous reduction
in fiha efficiency of food ut41ieation is not known.
Overall, during the study ~ortmlity rates were higher than expected,
particularly in the group of rats exposed co the highest mnok• concentration.
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%_/
An important consideration is thac in this experiment, at each sesslon
an~nals were exposed to smoke for I0 minutes rather than the 9 minute
exposure which we have used previously. For animals experiencing a
near-maximal tolerable dose of smoke, I0 rather than 9 minutes of
exposuce Kay• the unusually high mortality rate in the "hish dose"
group. However, this has not a£fected the general /nterpretation o£
the exper ~nenc.
Another innovation in this study was that for the-first time,
animals were exposed once only on Saturdays end Sundays and t~£ce on
weekdays. A consequence of this red~ct£on ~n weekend dosing seems to
be that animals show a reduced tolerance to the 'tfUl1" Smoking regi~e
early in the £ollo~r£ng week, This is • penalty £or using the modi£ied
treatment, which allows more convenient weekend work yet maintains
treat3nenC £or 7 days par week. However, the use of such 8 compromise
schedule does not prevent the development o£ those dose-related chanKes
in lunK patholoKy which have previously been used success£ully for the
bioassay o£ smoke irriCancy.
The study has answered, at Least partly, the questions set ae the
onset of the exper~m@nt. Patbologlcal thanK•s, partlcularly in the
~&rynx, did occur before 6 weeks, and became more severe •s exposure was
continued beyond the 6 :week exposure period. The mjority o£ the
induced changes regressed niter traat~nent was discontinued (sun~ar£sed
in Table 23). The chanKes observed were those reported in previous
studies, with the exception o£ an advanced nspindle-like" me~aplas£a
in the lung of one rat. The patholoK/~•l changes induced by smoke
exposure and the methods for quanti£yinK the changes were shown
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
Co

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to be reproducible to a high degree. It is worth noting that different
groups with the same exposure to dilute smoke (Groups i and 9) had
similar absolute values for the parameters measured. This was
particularly important to establish since these two groups came from
batches of tats delivered to the laboratory from the same suppliers but
at d/fferent ti~es.
"Normal" lesions seen in the respiratory tract of control animals
were predominantly infl~atory tissue, consistin8 main/y of lymphocytes
and a small number of neutrophils. The distribution and frequency of
such lesions was highly variable in the normal populations examined.
Their distribution in the lung but not in the la~ and trachea, was
altered by exposure to smoke. In the lung, the lymphatic tissue probably
~ndicates a response to a viral infection and represents the early
stages of chronic murlne pneumonia (16, 17). Its signlficance in ~11
amounts is, however. Lmcertain. Eats showing this condition do not have
any visible signs of ill-health. A means of evaluating the extent of
the various futures of "normaZ" lun8 pathology is a useful and sensitive
method of identifyi~ early changes of chronic respiratory disease in rats.
The response of the lymphatic tissue in the lung co dilute cigarette
smoke was rapia, as illustrated by the comparison of group man scores
for rats with multiple per£vascular cuffs plus focal pneumonitls (Table 9).
After only 4 weeks exposure, very few rats showed such lesions coutpared
with I0-26Z in the control groups. The response was uniform in all
smoke-exposed rats, even though the extent of Zymphatic tissue in
"noz~al" animals varied greatly.
Zt has been suggested that the presence of lymphatic tissue may
make the rat unsuitable for lone term inhalation studies on the respiratory
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-45-
epithelium and parenchyma (11). Mowever, the exposure to smoke reduces
the amount of lymphatic tissue, most probably by suppressing the
i---unological response of the rat (18) rather than by removing the
viral antigen. Th~s is compatible with more tenuous evidence from
a previous study (3). This possible loss of immunological response
may produce a rat less suitable for lord-term experiments not because
visible lesions due to inns infection interfere with inteEprer~ation
of any smoke-lnduced chanKes but because the smoke-expoeed rata amy
be more susceptible to infection.
Pathological changes that became evident after only 2 weeks of
exposure to full smoke included squamous mecaplasia and keratinising
hyperplasia in the larynx. The incidence of both these changes was
related to the duration of exposure and reached a peak after 6 weeks
exposure and plateaued or even regressed slightly with continued .
exposure. Squamous mecaplasia and keratinisation of the larynx was
most marked in rats (Groups 1 and 9) exposed to mnoke for 6 weeks
and the larynxes of animals fro~ this group could be easily recosnised
at low magnlfica~ions. -The distingu£shi~K feature was ~he thickness
of the 8quamous epithelium, wh/ch in 80Z of these animals lined the
whole la~eal l~nen of the section. All rats showed keratinisation
of the epithelium on ~he vocal cord. The degree of hyperplaBia was
noticeably greater than has been previously observed. Tt must be noted
however that in this, as in all previous studies, the e~tent of hyperplasi8
was determined by tak£ns measurements of the squamous epithelium
includinK any stratum corneum. Thus chau~es in epithelium thickness
will tend to follow the degree of keratinisation (YiKures 26 and 27).
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-46-
For both these features of the larynx in smoke-exposed rats
(mecaplasia and k~raC£nisatio,) charm was a rapid regression when
exposures stopped and 1&rynxes were apparently normal again in rats
after the 42 days holding period. In those rats held after exposure
there £s a clear increase in the ~ncidenee of incomplete squamous
menapl•si• following complete loss of keratin after & days holding, ks
in •11 previous snudies the ventral depression ~as free from smoke-
induced changes. Subjective appraisal indicated • possible byperplasi•,
but no group comparisons were made.
Both bronchial end tracheal goblet cells were hyperpl•stic after
2 weeks exposure. As before, the problm= of evaluation was evldenc and
very few fully differentiated cells were observed. The response of the
epithelium in the bronchus, measured •t level I in the main lefn
~nCr•pulmonary bronchus (19), was more un£form than that in the era=had
and reached a maxlmum after 12 weeks of exposure to smoke. Both tracheal
and bronchial epithelium initially showed only slight signs of •
reBression of the goblet cell hyperpl•sla when smok/ng stopped but after
21 days holding, both returned to near normal values. &Ithough two
different methods were used to evaluate goblet ce~l hyperp1•sia, the
cesults •re comparable though the siCuat£on is noC ideal.
The mcrophage population in the lung p•renchyma increased slightly
aft•r only 2 weeks exposure to dilute elsareCte smoke, and this response
inareased to • maximum after 9 weeks. &s observed previously, with an
increase £n numbers charm was • sq~nu1~aneous increase in mcrophage size
and degree of pigmentation. In the rats exposed for the longer periods
the macrophagee were particularly veeuoleced and often the cell outline
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MINNESOTA TOBACCO LITIGATION
c~
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-~7-
became indistinct. The piEmentation observed is probably due to an
increase in the number of lysosomes and phagolysosomes. Ul~rastructural
observations have shown these organelles to contain plate-like inclusions
which may be phagocytosed particulate matter (14). The pigmentation may
also be phagocytosed peroxidased lipid (20) and/or iron (7, 21).
There was a gradual reduction Ln the macrophage population over the
A2 days holding period when smoke exposure was stopped.
The most interestinK pathological changes observed in this study
were related to alveolar metaplasia in the lung. ChanKes were not
observed before 6 weeks exposure and were seen initially as clusters of
larks pigmented macrophages £n the region of the terminal bronchioles
and their alveolar ducts. It is of interest that the rats with such
clusters also showed increased macrophage populations in the sub-pleural
site examined. The two parameters seem to be dependent. The number of
rats w~th these clusters of macrophages increased with duration of
exposure end of these approximately 70Z also showed siKns of incipient
alveolar metaplasia. This proBressed to a full mstaplasia in a few
rats in which cuboidel cells were found linir~ the alveolar spaces.
No ciliated cells were observed in these animals. The hyperplasia
and metaplasla seen in smoke-exposed rats may be due to the response
of a number of cell types. The increase in alveolar wall thickness
could be a hyperplasia of 8quamous cells or, as is now thouEht more
likely, type II alveolar cells. The type II cells may also umdergo
metaplasla produc~ the cubo£dal cells. However. these could also
be an extension of bron~hiolar cells into the alveolar duct i.e.
bronchiolisation (15). The clusters of piKmented macrophaKes described
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
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BAT Co LTD - MINNESOTA TOBACCO LITIGATION

-48-
here as an indicator of incipient alveolar metaplasi• are described
in the lungs of younB smokers •s respiratory bronchiolitis (22), In
is postul•ted that this is • precursor of centrianclnar emphysema.
It is interesting to note that respiratory bronchiolitis occurs in an
irregular distribution, whereas in the rats exposed for 12 weeks in
this study distribution was comparatively regular. Of importance is the
increase in the number of rats per group with incipient alveolar
met•pl•si• in those groups held for 6 weeks following exposure. The
number of rats per 8roup showing siKns of alveolar mer~tpl•eia increased
wluh the duration of the holding period, although the severity of the
lesions in any one lunE did not increase. In rats exposed for up to 12
weeks the extent of the lesion in any one lung increased with continued
aX'po sure.
The aplndle-like cell met•pl•si• observed in one rat is •s yet
unexplained. It us found together with a well differentiated cuboldel
metaplasLa of the alveolar epithelial cells and mucus in the alveolar
lumen. The increase in reticulin suKgests • form of fibrosins elveolitis.
In conclusion, amny p•~hologic•l changes occurred after only 2
weeks of exposure to smoke. Some parameters (Table 23) increased in
severity ~rfth up to 12 weeks o£ exposure whilst others appeared to reach
a maximum and then plateau •t 6 weeks. Rapidly induced changes tend to
regress rapidly whilst those lesions which develop more slowly regress
at • slower rate. An g~porcant exception to tb/s general rule was
alveolar metaplasia which, together with lymphocytic activity in the
lunK, ~as the only parameter which showed no regression, in fact the
metaplmsim showed signs of proKresslon durinK • non-smok~n8 period of
seveE•l weeks.
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
C.m
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c~

INDEX
HAS
INDICATED
GAP IN
BATES
RANGE
HERE

-49-
TABLE 23
SUMMARY OF LUNG PATHOLOGY CHANGES OBSERVED DURING
P ROG~E SS ION / REGRESS ION STUDY
Multiple Perivascular
Cuffs + Focal Pneumonitis
Alveolar Metaplasia
Alveolar Macrophages +
Bronchial Goblet Cells ÷
Tracheal Goblet Calls ÷
Squamous Hyparplasia (Larynx) +
Keracinisation (Larynx) +
Exposure Period
in Weeks
(1:12 Dilution)
2 4 5 9
m o m
-- -- ÷ ÷
+ ÷ m
÷ m m
÷ ÷ ÷
+ m ÷
4. m 4-
He idinE Period
in Day s
Following 6 Weeks Exposure
12 1 4 [ 7 21 42
J
- - No Change -
m + Progression +
m 4. Regression 4.
m m Regression ÷
m + Regzession -
+ m Regres s io n +
+ m Regression -
- Lesion absent, 4. Lesion evident, m lesion maximal.
With regard co upe~i~gntal design, this study has illustrated the
need for a larger group sLze (ZO rats/group being desirable lOmale and
I0 female). Inmost cases only 6 rats of any one sex par group were
ava£Lable in ssmke-exposed groups and the examination of possible sex
differences was not poss£ble. The s£tuaCion w&s no better in the control
groups with only 3 race of each sex per group. With the marked regression
of changes once smoklnE was cermlnaced, che period between the lest
exposure to smoke ana autopsy should be as shore as possible. The
incidence of kersCinisacion of the larynx, for example, fell from 38% co
17% within 3 days.
Races of regression do vary from parameter to parameter. No defln£ce
rule can be made but in general autopsies should be carried out within
24 hours of final exposure to smoke.
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
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For the purposes of carrying out bioassay work with s:oke: the
length of exposure may be varied depending on the parameter under
investigation. Six weeks seems co ~axfmise squau~us metap~asia and
kera=inising hyperplasia in the larynx ac the smoke "dosase level" used
in this study, i.e. exposure ~ice per day for 10 ~nutes to a smoke
concencratlon of approximately 4.7 ~/i.
In fact, in ~his stud? measurement of epithelial thickness,
including any keratin present, suggests that squamous hyperplasia
reaches a maximum after 2 weeks exposure and neither decreases nor
increases with continued exposure up to 12 weeks. The uncertainty of
the validlty of the measurements includlng keratin (which can easily be
sloughed off naturally) q~estions the evaluation method. Future
estimations will thus include measurements of the thickest uniform areas
of epithelium including and excluding any keratin present. Both
sets of results will be reported.
Although dosim~cry work was not included in this exper£ment, our
previous studies suSgeec that chose animals exposed to smoke at 1:12
dilutiou from the cigarette used. would receive a TPM dose Co the lower
respiratory system of approximately 400 ~g/g tissue/session. Under such
exposure conditions, bronchial goblet cell hyperplmsia end alveolar
macrophaie numbers appear co reach a ux/mum ac 7 weeks. The remaining
pathological changes (alveolar ~aplasla, tracheal goblet cell hyperplasia)
showed no signs of levellinE off after 12 weeks exposure to smoke at
1:12 dilution. There is thus the need for extending exposure beyond 12
weeks, particularly when considering alveolar metaplasia.
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
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BAT Co LTD -
MINNESOTA TOBACCO LITIGATION
"7-

-51-
'V
P~.F~NCES
1. BAT Report No. KD.I231-R, 2.7.75.
2. BAT Keporc No. RD. 1281 Restricted, 23.10.75.
3. BAT Report No. ~.1328 Resczicced, 13.2.76.
4.
First report of the Independent Co~n£ttee on SmokinK and Health (1975).
Tobacco Substitutes and Additives ~n Tobacco Products.
5. BAT Report No. RD.1246-AR, 27.11.75.
6. Walker, D. (1975), Wickha~Kesearch LaboratoriesReport. BAS1, 12.9.75.
7. Walker, D. (1976), Wickha~n Research Laboratories Report. BA62
and BA63, 2L.1.76.
8. BAT Report No. RD.I&20 Restricted, 16.10.76.
9. Stevens, H.T. (1976), ToxicoIoKy, ~, 311-318.
10. Tr£eb, G., Fapprltz, G. & LUtzen, L. (1976), Tox. Appl. Pharmacol.
3_~5, 531-542.
11. Lib, D. (1975), Lab. An£m. 9, 1-8.
12. Dontenw~11, W., Chevalier, H.J., Harke, M.P., La£renz, V., Rechzeh, G.
and Schneider, B. (1973), J. Nat. Cancer Inst. 5_~1, 1781-1807.
13. liay,ahi, H., Shea, 3., Fhelps, P., Holmes, L., Pochey, V., SornberKer, C.
and Rubez, G. (1975), Clin. Ram. 23, $8&.
14. Brody, A.R. and CraiKhead, J.E. (1975), lab. Invese. 32, 125-132.
15. Yrasca, 3.M., Auarbach, O., Parim, V.R. and J~emon, ~.D. (1974),
Exp. Hol. Pethol. 21, 3OO-312.
16. Tames, J.R.H., HcAdams, A.J. and Yv£ch, P. (I965), Amer. J. Path.
32, 1&1-159.
17. Innes, J.R.M., Garner, F.M. and SCookey, J.L. (1967). In PatholoKy
o~h~racor~ Ra~e end H~ce (Edl. Cotch~n & Roe), Blackve11, Ox£ord.
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GAP IN
BATES
RANGE
HERE

-52-
18. LeuchtenberBer, C. and Leuchtenberger, R. (1974). Ontology,
2_29, 122-138.
19. Lamb, D. and Reid, L. (1969). Brit. Med. J. 1, 33-35.
20. Davies, P. Personal Com=unicat:ion.
21. Mohr, U., Keckar, M.B. and Resnlk, G. ~_nn B.A.T Hamburg Progress
Reporn, July-September, 1%76.
22. Niewoehner, D.E., Klelnerman, J. and Kite, D.B. (1974), New. EnKI.
J. Mad. 291, 755-758.
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
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BAT Co LTD - MINNESOTA TOBACCO LITIGATION
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-53-
APPENDIX TABLE I
sure.my com O..A A. C G SS O." G OUPS)
G¢ou~
1. Number
Heart
S.D.
2. Number
Mean
S.D.
3. Number
Mean
S.D.
4. Number
l~an
S.D.
5. N,~ber
Mean
S.D.
TOTAL
Nund)er
l~az~
S.D.
Number
He--,
S.D.
Male
6
27.1
4.6
3
32.2
1.6
6
27.7
3.9
6
33.3
5.3
4
38.5
S.7
25
31.2
5.9
1:8 1:12
i , m
Female
Female
5
28.7
5.8
5
30.4
4.6
5
28.0
4.4
4
35 • 1
1.6
5
35.7
8.0
24
31.4
5.9
49
31.3
5.9
)',ale
6
22.3
3.1
6
24.9
6.6
5
29.8
3.7
6
30.6,
3.0
6
30.0
8.3
29
27.4
6.1
l
6
22.2
1.6
6
29.6
2.8
6
30.3
3.6
6
25.5
3.6
6
31.3
4.9
30
27.6
4.8
59
27.5
5.4
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
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INDEX
HAS
INDICATED
GAP IN
BATES
RANGE
HERE

-5~-
A~ALYSlS OF C0Hb DATA <"KEGKESSZ0N" GROUPS)
Data
120 animals (60 male, 60 female) were randomly divided into I0
groups wlch 6 males in each and I0 groups with 6 females in each. Five
groups of each sex were then allocated to two treatments, vlz. 1:8 dilution
and 1:12 dilution of smoke.
All zhe animals involved in this part of the experiment were from
one intake.
COHb measurement was taken for each animal approx/macely 4 weeks and
2 days after the smoke acclimatization. The data has been summarised in
Table I. Note that group 5, 1:8, female and group 5, 1:12, male have a
hiKher standard devlation than the rest of the groups, otherwise the date
is fairly consistent.
Analysis
The da~a was created as a 2 x 2 x 5 experf4nenc with treatments and
sex crossed and groups nested w£ch£n treatments and sex. Also, the effects
of sex and :rea~men=s are fixed and groups are random. The analysis of
variance is shown below:
Source of Variation
Treatment
Sex
Treatment x Sex
Groups (within six & trut:ent)
d.f. - desress of freedom
SS - Sum of Squares
MS - Mean Square
F -- F--value
Sir. - SiEnlficance level.
d.f. SS MS F Sir.
1 ASL.20 451.20 5.33 95Z
1 0.02812 0.02812 <1 N.S.
1 0.50766 0.50766 <1 N.S.
16 1355.2 84.698 3.72 99.9Z
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
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INDEX
HAS
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GAP IN
BATES
RANGE
HERE

-55-
Zt should be pointed out that the F-tests for test~nK the siKni£icence
of the sources of variations are slijhtly d£f£erent from the normal tests
when the erro= KS £s used as a divisor for all the other HS's.
In this
model, the F-tests are as eho~n belov:
test Groups e£fecC by Croup MS/Error
test the rest by ~nK @roup I~S as the divisor.
From the Ahoy& t&ble we see that
(i) there is a s£Kn~icant difference between Woups ~th~n sex
and tr earnest.
(£i) the=e £s no s£Kn~£aant sex x treatment and no sLKuig£~ant
diference between sexes. We would have expected this from
the data in Table 1.
(iii) there is a siKn/~icant difference be~een treatments - 1:8
dilution produc4~[ hiKhez COKb count than 1:12 dilu:ion.
the d~ta for the tire groups w~thin sex and creauaents ate
analysed separately by 1-~ay AHOVA we find that:
(i) for 1:8 Hsle, there £s s sLKn££icenc (99.3Z) di£ferenee
he.sen Stoups. This d/~fere~ce £s maLuly accounted for by the
di~feruce betweun Stoup i ~ Kroup 5, 8~oup 3 and Kroup 5.
fo3 ~z8 ~emale, no si~Lf~ant d~feren~e can be detected
between 8Zoups. The siK~Lficance level is 87.3X. It is
feasible that the lazKe variation in K~oup 5 has £n~lated
the ez~or MS, thus mak~n~ tb~ test for dete~t~ difference
be~vee~ Sroups~e~e sensiti~e. ~ the ~r~abLlit7 of this
Kroup was on a par with the no~mal ver~ab~li~y, then a
dLfference at ~OX level of siKnificanct may have been ~ound.
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
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BAT Co
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INDEX
HAS
INDICATED
GAP IN
BATES
RANGE
HERE

-56-
(iii)
(iv)
£o,- I:12, MaZe, ,'ha dJ.~fer~ce be,:ween 8zoupa is 8iSn£Eicaa~
ac 94.4Z level. KEain, Kroup 5 has h~gher variability than
normal.
£o%" 1:12, Female, =he difference between ~zoups i8 |ifnifican~
&C the 99.9Z level.
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-57-
APPENDIX TABLE 2
SUMMARY OF COHb DATA ("PROGRESSZON" GROUPS)
Batch Zntake
Groups
11. N,--be r
Mean
S.D.
10. Number
7 • Number
Mean
S.D.
6. Number
Mean
S.D.
, ,
Batch Tot:a1
Number
Mean
TOTAL
qmmm,mmmm~
Number
MeLn
Treatment Total
Number
Mean
I £n8
s
Male Femal e Ha le Pemal e
im i i
I 2 1 2 1 2 I 2
5
40.7
2.0
4
34.5
7.0
5
36.1
6.7
6
41.0
4.0
1.I 9
38.8 37.9
6 6 6
30.5 24.9 29.1 I
3.5 3.1 2.4
4 6 6
4.1.2 30.1 29.2
3.1 6.0 4.2
5 6 6
30.0 26.5 25.5
3.7 4.1 4.4
4 6 6
30.9 27.3 25.1
2.0 3.4 5.7
LO 9 12 12 12 12
34.7 30.4 27.5 26.9 29.2 25.3
19
32.2
39
35.6
20
38.4
24
27.2
24
27.2
BAT Co LTD - MINNESOTA TOBACCO LITIGATION

INDEX
HAS
INDICATED
GAP IN
BATES
RANGE
HERE

-58-
A.RkLYSIS OF COt~ DATA ("PROGI~ES.SION" GROUPS)
Data
The antis used for collecting the COHb data were the ones used
in the "exposure Clme experLment'. IC is required to cast if there is
a significant difference in COHb from 1:8 and 1:12 (irrespective of
the time of sampling).
A su~mry of the data is shown in Table 1. Treatment, Sex and Batches
ace crossed and have fixed effects and groups are "nested ~riCh~n batches,
sex and treatment. Group is tre~aced as a random var£abls. The A~OVA
for this is shown below:
Source of Variat£on d. £. SS MS
F Sig.
,m
TreaC~tnt 1 1496.2 1496.2
23.47 99Z
Sex 1 128.65 128.65
2.02 N. S.
Treatment x Sex 1 133.04 133.04
2.09 N.S.
Batch 1 156.91 156.91
2.46 N.S.
Treatment x batch 1 5.0162 5.0162
1 N.S.
Sex x batch 1 77.531 77.531
1.22 N.S.
Treatment x sex x batch 1 1.4526 1. 4526
1 N.S.
Groups (within batch act) 8 510.00 63. 750
3.403 99Z
N£thin groups 71 1330.O 18. 733
Note Chat the F-test for the d£fference between groups (w£thin
batches etc.) is $iven by d£viding groups MS/w£th£n groups PLq but the
rest of the affects are tescmd by using Groups NS as the denomlnator.
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BAT Co LTD - MINNESOTA TOBACCO LITIGATION
........................................................ -v--

INDEX
HAS
INDICATED
GAP IN
BATES
RANGE
HERE

FIG. I
DIAGRAM TO SHOW OUTLINE DESIGN
3- NONTH INHALATION STUDY
ii
RD. 1477 RESTR! CTF..D
OF
GROUP
II
PROGRESSION -
ii,
I!
II F"2'-2~ 14
I0 r./i////I 28
I/ / / / / / / /14~
7 v////7",/~.//./AG~
6 v///"//-/?//,/./;'//Ae4
, .... EXPOSURE' PERIOD (DAYS) ,
II
REGRE5510N
' GROUP
i!
I
I !/'//7////III
Z v////'/"//,r~4
3 ~/////'//-zx~?
5 r/.////// 4z
t4ZDAYr~ ID(POSUKt nHOLDING I~RIOD (DAYS),
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Z
>
'-4
0
03
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N
0
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,4
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0
Z
1169c] c]01
C, ONGENTI~TION$
9
8
?
4
Z
0
Ik
I0
(' FIG. e(' RD.I¢?7 RESTRICTED
Of" TPM IN EXPOSURE GHAMBERS FOR EACH Of" THE SHO .KE DILUTION LEVEL, S ,USED
IN THE STUDY
4
4O
N=. oF 055ERVATIONS DURING STUDY
2O
e 1:7 DILUTION
• 1:8 DILUTION
X I: 12 OILUTION
60
--4
5O

FIG. 3 RD. 14.77 RF.,3TRtCTED
GRokrI'H CURVES FOR CONTROL RA'I'5 AND ANIMALS EXPOSED TO
;:' DLLLFF.ION$ OF ,SMOKE FOR APPROXIP'IATELY 12 WEEK,5.(IVIAI.~.E5)
INC.,REASE IN BODYWEICIHT
CAGE C.X)NTROL
÷ 5HAM - ,SMOKE
• I: B DILUTION
x I :12 DILUTION
60 7O 8O
BAT Co LTD - MINNESOTA TOBACCO LITIGATION

FIG. 4- RD. 1477 RF_.STRICTED
GROWTH CURVE5 FOR CONTROL RATS AND /V~IPIAI..5 EXPOSED TO ~. DILUTIONS
OF SMOKE FOR 6 W~_EK5 FOLLOWED BY A POST-EXPOSURE HOLDING
INCR.F_/~E IN I~ODYWEIGHT
('/o)
PER, O0. , (~,u.~
6w~./6~,~.
e CAGE C, ONTROL
+ 5HAM" 5PIOKED
• I: B DILUTION
X I: IZ DILUTION
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
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FOOD CONSUMPTION OF RAT5
FIG. 5
DURING 12
i
RD. 1¢77 RESTRICTED
~/EEK5 OF EXP05URE
e CAGE CONTROL
4. ,SHAH- SMOKED
• 5MOKE EXPOSr:.J::)
FOOD CON,.~MPTION
E6
24
eo
IO
16
! I : : ,,,, , I , I 1
I , I II
0 I0 ~.0 30 40 50 &O
70 80 SO
30~
P.8
Z4.,
20
18
0 I0 20 30 40 50
I'I ME (DAYS)
6O
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
........................................................................ "-T

FOOD CONSUMPTION
FIG. 6
OF RAT5 DURING
i L I I i
6- WEEK,HOLDING
R,D. 14.77
G WEEK3 5HOKE
PERJO,D
RE, STRI C"I"ED
EXP05URE AND
• CAGE CONTROL
+ 5HAM- SMOKED
• ~P1OKE EXPO,$F..D
FOOD CON,$1./M PTON
( 81r T I
28
116
Ilk
1tll
18
I: IZ DILUTION
I | = I
0 IO =0
I II I~ II 1
m, m
114.
la
p'./ sHo.~z-cx .f~soRgq, r-.~O.oZ. / /I. i=o.¢r-~~.o~=~r¢,:oo -l--
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F I G. 7 RD. 1477 I~ESTRICTEO
FOOD CONSUMPTION OF RATS DUPJNG
12 ~/EEKS OF EXPOSURE
e r..,~E CONTROL
+ SHAH - 5HOKED
• SMOKE EXPOSED
FOOD GON,SUMPTION
( s / RATI OAY)
,,.... 2J
24,,
18
16
14.
!,: 12 D!LU,T'ION (FEMALE,S)
- I ,, ;, ,, , .... I , I
"
0 I0 Zo ~o 4o SO 6o 7O BO SO
~.o
18
14
I" 8, DILUTION, ,(FEIMALES)
BAT Co LTD - MINNESOTA TOBACCO LITIGATION

FOOD
FIG. 8
CON5UHPTION OF RATS DURING G WEEKS
G-WEEK HOLDING PERIOD
IKD. 1477 RESTRIC.,TED
SMOKE EXPOSURE AND
i i , ,
e OAr, E. CONTROL
+ 5HAM- SMOKED
• SMOKE EXPOSED
FOOD C.,ON,SUIVIPTI ON
(, / RAT/DAY)
P-4'
~0
I0
IG
14
I: I?- DILUTION
(F~MALBS)
: I ' ' l I I ! I
I !
0 I0 Z.O 30 40 50 60 70
80 50
I:, p DILUTION .(FEMALF.3)
!
" [
14.
Time (DAYS) "-.J
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
................................................. "T

F'tG.9 RD. 1477 RE3TRIC'I'ED
THE RE.LATIONSHIP FE'TWEEN TREATMENT-RELATED MORTALITY ('F..XPRE,~ED A5 A
PERCENTAGE OF AHIMAL~) AND EXPOSURE CHAMBER MEAN SMOKE CONCENTRATION
MORTALITY
(~'o3
80
60
4O
ZO
0 O
5 4. 5 6 7 8
s~oK[ co.c~'r~r~o. (,,~/~)
|
BAT Co
LTD - MINNESOTA TOBACCO LITIGATION
oo

FIG. 10 RD. 1477 RESTRICTED
ALL INDIVIDUAL TREATMENT- RELATED, DEATHS PLOTTED. (FOR ~. 5HOKE
DILUTION LEVELSt bAOCORDING TO F.XPO,SURE DAY NUMBER DURING THE EXPERIMENT
FEHALE
04,. HALE,5
O
L
I
oo
I I I I
I I • I
l
• •o
• 0 • • • •o• • • • ooo
o•
•
o I I o
0 , I !
I I
o • •0 • •
0 I0 ZO 30 40 50 60 70 80 SO
EXPT. DAY' Ne"
BAT Co LTD - MINNESOTA TOBACCO LITIGATION

FIG. II RD. 14.'77 RE3TRICTED
TREATMENT- RELp,.TED DEATHS,
PLOTT,,ED,ACCORDING TO THE DAY ON k/HICH THEY.OOOURED
TOTAL DEATHS
14.
13
IZ
ii
IO
8
7
5
4
3
2
I
0
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
................................................................... -1"

FIG. 12 RD. 1477 RE3TRICTED
5AHPLING P0tNT5 FOR AIR EXP05URE PLATE,S
LIFE ,SC, IENC, E5 BUILDING8 IO 75
I
AUTOCLAVE
CAGE 5TORE
C, ONDITIONING
R00H '
I N~'r'RU]VlE.NT'S
14
CLEAN"
@
13
CORRIDOR
I:,
RE3T ROOPI
•11
INHALATION
5
t
el5
INHALATION
4
4.
ANIHAL
ROOH 4
I
II
m
DIRTY
i,
I
017 ~15
I
INHALATION I INHALATION
@
6
ANIHAL
ROOM 3
I
I
I
#os
I
2
ANIHAL
ROON ?.
!
CORRI DOR
INHALATION
(~UARANTINE
=0
l•
S
BAT Co LTD
- MINNESOTA TOBACCO LITIGATION
Lr'l
o'%
',,.O
r,,,j

ADJUSTED
GROUP MEAN
RD. 1477 REEFRICTED
OF HALE ANIMAL5 ,, KILLED
DURING 12 WEEK EXPOSURE PERIOD
~--- INDICATE5 NO SIGNIFICANT DIFFERENCE
8~ETWEEN THE~E TREATWIENTS.
ADJUSTED
._~uP H~N
~ODYWEIGHT
(s)
~J
I
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
!

ADJUSTED
GROUP
MEAN
FIG. 14 RD. 1477 RESTRICTED
BODY~VEIGHT$ OF FEIvIALE ANIMALS KILLED
DURING IP. WEEK EXPO,SUR[ PERIOD
"------- INDICATE5 NO SIGNIFICANT DIFFERENCE
~?WEEN THESE TREATMENT5
"JUSTED
ouP
~DYWF.IQHT
(s')
00,
2SO,
Z80,
Z'tO
ZOO
ZSO
24o
210
i|
I I' ",,,
I I
14 S8 4~. S.~
E.XPOSURE PERIOD (DAYS)
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
O
O'~
r',,.b
(..M

FIG. 15 RD. 14,77 RESTRICTED
ADJUSTED GROUP MEAN BODYWEIGHT5 OF HALF. RAT5 KILLED DURING
6 VEEK P05T-EXPOSURE HOLDING PERIOD
m ,,
ADJUSTED
GROUP MEAN
~ODY WE.IGHT
C9)
-- iNDICATE5 NO 51CINIFI~ANT DIFFERENCE
~WEF~ THESE TREA~ENTS.
! 4- 7
Zl
HOLDING PERIOD
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
¢.j-1

FIG. I~ RD. 14,77 I~ESTP, iCTED
FINAL W'EIGHT (FEMALES)
----- INDICATE5 NO ,51GNIFIGANT
DIFFERENCE BETWEEN THESE
I"REATMEN'~
ADJUSTED
~'Q, OUP MEAN !~
~DYWEIGHT
r~
I @ 7 II
4=
HOLDING PERJOD (DAYS)
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
O~
',,,c
r'~
cjr'l

FIG. 17 P,D. 14.77 P, ESTRICTED
No. OF RAT5 PER GROUP WITH MULTIPLE PERIVA5CULAR CUFFS (°/o)
• SMOKFJ:) FULL PERIOD
® SMOKE 5TOPPED ~ 6 WEEK.5
• x ,.~HAM-$MOIKED
& CAGE CONTROL
7o
40
3o
I0
O
0 ZO 40 60 80 IOO
N"" OF' DAYS FROM FIRST FULL SMOK[
BAT Co LTD - MINNESOTA TOBACCO LITIGATION

FIG. 18 RD. 14.77 RESTRICTED
No. OF RATS PER GROUP WITH FOCAL pNEUMONITi5 (:/:)
• 5HORED FULL PERIOD
® ,SHOKE 51"0PPED AFTER 6 ~T.E]¢.5
,~ SHAH-SHOKED
A GAGE CONTROL
N°. OF RATS/GROUP
~o
60
7o
50
4o
~o
2o
IO
/
I
/
0
I i I a !
O 20 40 60
No, OF' DAYS FROM FIRST FULL SP1OI'~
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
!
I00
O',,

FIG. I~) RD. 1477 RESTRICTED
No. OF R,6TS PER GROUP WITH BOTH MIJLTIPL.E pERIVASCULAR
CUFF5 AND FOCAL PNEUMONITI5 (%)
• 51'10KED FULL PERIOD
e SMOKE 5TOPPED AFTER 6 WEEK,5
x SHAM - ,SMOKED
A 0A~E CONTROL
NQ- OF" RATS/GROUP
(~.)
~o
8O
70
6o
50
4o
3O
ZO
IO
O
/
I
I \
i \
/
I \
I \
\
/\ \. ,,./ -.,
0
I I I , __
~0 4.0 60 8O
N°. OF' DAYS I:'ROH PIR,ST FULL SMOKE
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
!
I00
c~
",,C.
oo

No. OF FLAT5
PER GROUP WITH
FIG. 20
NULTIPLE
FOCI
RD. 14-77 RE.STRIGTED
OF PIGMENTED NACROPHAGE5 (7°)
• 5MOKED FULL PERIOD
e 5MOKE ..~'OPPE.D AFTER 6 W/EEK5
x ,SHAH-,5 M0 KED
CAGE CONTROL
N" Or RAT,5/CIROUP
8,O
7O
60
5O
4O
~O
tel
I0
O
!
o
---.4~-~---.-~ .... -~
! I ' "' • ; :
4O 6O 80
N" OF DAYS FROM FIRST FULL SMOKE.
I00
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
o',,
r,,,a
",,c

No. OF RAT5
PER GROUP
WITH
FIG. 21 RD. 1477 RESTRICTED
INCIPIENT ALVEOLAR NETAPLASIA (7o)
• ,SHOKF..D FULL PERIOD
~KE STOPPED AFTER G WF..EK,5
x 5HAH-~HOKED
A CA~E CONTROL
N°" OF RAT,S/GROUP
(%)
8O
70
GO
50
4.0
30
10
0
I
0
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
I
IOO
¢,..m
0.%

HEAN
FIG.ZZ
No. OF HAC, ROPHAqE CLUSTERS PER
P.,D. 14.77 RESTRICTED
LUNG 5ECTION
• SMOKED FULL PERIOD
,~>MOKE 5TOPPED/V"I'ER G WEEK,5
X 51t~,M- 5PIOKED
& CAGE CONTROL
HACROPHAGE C, LUS"rER5 / LUNG
SECTION 40
35
3O
25
7.0
15
!0
5
0
0
-----~- 41-----~ .... --~
ZO 40 60 BO
N°. OF DAYS FROM FIRST FULl. SMOKE:
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
I
I00
C~

GROUP MEAN
FIG. Z3 RD. 14.77 RESTRIr~TED
COUNT OF IvlACROPHAGF~ ~" I0 m IN 0"54,~. m~ OF'
SUB-PLEURAL ALVEOLAR Ti$,~UE
• .~IOK,ED FULL PERIOD
SMOKE ,5"I'OPPF.,,D AFTER G WEEKS
51"IAN- .~"IOKED
,s CAGE CONTROL
HEAN N°'OF t"IAr.,ROPHAGF~/GROUP
BAT Co LTD
I • H ' I I I
Z0 40 GO 8o
N"OF DAYS TRDM FIRST FULL SPIOKE
- MINNESOTA TOBACCO LITIGATION
I
I0O
Lr'l
Lr--

F'IG. P.4 RD. 1477 RES"I'Ri GTED
ESTIMATED
GOBLET CELL DENSITY IN FIXED 51TE OF LEFT
ill, , -,,, • im
INTRAPULHONARY BRONCHUS
i i ,.
• E:~IOKE.D FULL PERIOD
® .SMOKE STOPPED AFTER 6 ~i/EEK;5
SHAN- 5MOKE.D
CAGE CONTROL
GOBLET CELL INDEX
3"0
P.-O
I'O
0
O
x-J~" \\_ ,.,&~"
%AI"f "~--- ..~.~
, I I ' I ,, ,, :
Zo 4o t~ 8O
N-. OF" DAYS FR.OH FIRST FULL 5HOKF..
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
IOo
k.jr-
O",

FIG. 25 I:I,D. 14.77 RESTRICTED
No. OF RAT5 PER GROUP WITH GOBLET CELL HYPERPLASIA
IN THE UPPER TRACHEA (°/o.)
• 5HOKED FULL PERIOD
(> 5PIOKE 5TOPPED AFTER G WEEKS
x 5HAM- 8MOKF..D
& CAGE CONTROL
No. OF RAT,S/GROUP
70
60
50
40
3O
%0
I0
0
!
0
.,___,.
I I ! I
20 4O 6O 80
No, OF DAYS FROH FIRST FULL ,~HOKF..
,, !
I00
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
m
O',,
--F-

FIG. ?..G RD. 1477 RESTRICTED
HYPERPLASIA OF THE SQUANOU5 EPITHELIUM LININra
MEDIAL ASPECT OF THE VOCAL CORD
THE
• ~NOKED FULL PERIOD
e 5HOKE ,,%TOPPED AFTER EP WEEKS
X 5~-IAH - SMOKED
& CAGE CONTROL
GROUP MEAN EPITHELIAL
6O
So
40
3o
P.O
THIGKNE~
&--.----~.....
0 El 40 60 8O I00
N¢~ OF DAY'S TROH FIRST FULL SHOKE
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
0%
Lrl

N.o. OF RAT5
EPI THE LUM
FIG. 27 RD. 1477 RE3TRICTED
PER GROUP WITH KERATINISATION OF THE 5CIU~J'IOUS
ON THE MEDIAL ASPECT OF ~)
No. OF RAT~/GROUP WITH
STRATUM CORNEUH
( ,o1
I00 .
~o
80
'70
6o
50
41.o
Zo
IO
0
i=.-~_.-.J~._-T
I I " I ,
,, I .... !
0 ZO 40 6O 80
No. OF' DAYS FROM FIRST FULL SMOKE
BAT Co LTD - MINNESOTA TOBACCO LITIGATION
• ,SMOKED FULL PERIOD
,SMOKE STOPPED AFTER G WEF.K~
,SHAM- SPIOKED
CAGE CONTROL
I
100
r, jr"I
(..M

INDEX
HAS
INDICATED
GAP IN
BATES
RANGE
HERE

BAT Co LTD - MINNESOTA TOBACCO LITIGATION
