Anne Landman's Collection
Reduction of Carcinogenicity on Mouse Skin of Cigarettes Smoke Condensate with Palladium Catalyst
Fields
- Named Organization
- Lm, Liggett & Myers
- NCI, Natl Cancer Inst
- Oster
- Waters Associate
- Whatman
- Ftc, Federal Trade Commission
- Hew, Dept of Health Education and Welfare
- Named Person
- Ames, B.N.
- Bates
- Bentley
- Biros
- Blumer
- Bock
- Collins
- Fuson
- Gori
- Guerin
- Hackney
- Hoffman
- Mold
- Norman
- Oakley
- Rhoades
- Severson
- Spincer
- Wiberley
- Wynder
- Litigation
- Stmn/Produced
- Type
- SCRT, SCIENTIFIC REPORT
- ABST, ABSTRACT
- BIBL, BIBLIOGRAPHY
- CHAR, CHART/GRAPH/MAPS
Document Images
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R1VltEGED AP1D CONFID~~T1A~
REDUCTION OF CARCINOGENICITY ON MOUSE SKIN
f OF CIGARETTE SMOKE CONDENSATE WITH PALLADIUM CATALYST
I
§Life Sciences Division, Arthur D. Little, Inc.,
Cambridge, Mass. 02140; and tResearch Department
Liggett Group, Inc., Durham, North Carolina 27702
ABSTRACT
(0
The carcinogenicity of cigarette smoke condensate (CSC) toward
mouse skin has been dramatically reduced by 79-100% through a com-
bination of palladium metal catalyst with blends high in Burley
tobacco content or with lower Burley tobacco blends supplemented
by the addition of compensating amounts of a nitrate salt. This
lowering of carcinogenicity is associated with decreases in the
level of polycyclic aromatic hydrocarbons (PAH) in the smoke con-
densate.
Through the use of filters designed to complement this additive
combination, the other measured components of the smoke stream are
either lower than or equivalent to those of conventional best
selling US cigarette brands. This is confirmed by lowered in vitro
ciliatoxicity and cytotoxicity responses as well as in vivo sub-
acute inhalation studies with rats.

REDUCTION OF CARCINOGENICITY ON MOUSE SKIN
OF CIGARETTE SMOKE CONDENSATE WITH PALLADIUM CATALYST
§Life Sciences Division, Arthur D. Little, Inc.,
Cambridge, Mass. 02140; and tResearch Department,
Liggett Group, Inc., Durham, North Carolina 27702
4
In a separate report (Mold, 1978), we have described the experi-
mentation which has led us to conclude that the polycylic aromatic
hydrocarbons (PAH) in cigarette smoke are of major significance in
its carcinogenicity toward mouse skin. The complexity of this mix-
ture caused us to direct our further efforts toward a reduction in
the yield of this total class of compounds rather than to attempt
to further subdivide it.
Important requirements of these studies were the availability
of the procedure described in our previous report for rapidly ob-
taining a concentrate of PAH's and the estimation of the quantity
of these present by the Sebaceous Gland Suppression (SGS) test.
A correlation of SGS activity and carcinogenic potency of pure PAH
compounds has been noted (Bock, 1958) and, at the degree of purity
obtained for our PAH concentrate from cigarette smoke condensate
(CSC), we have also found a very good correlation to exist between
the SGS ED50 and the IR absorbance, thus facilitating our studies.
Materials and Methods ~
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Preparation of Tobacco Samples Containing Additives. Solid, sW
water-insoluble additives were ground finer than 100 mesh and added ~
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to a casing mixture consisting of glycerine,propylene glycol, invert
sugar, corn syrup, flavorant materials, and water. Water-soluble
additives were added to the premixed casing solution in a minimum
amount of water. The thoroughly-mixed casing/additive dispersion
was sprayed onto an uncut Bright, Burley, Maryland, and Turkish
(BBMT) tobacco blend at a rate equivalent to 14.14% casing and 1-10%
additives. Reconstituted tobacco was added in some cases and the
treated tobacco was then cut in a laboratory guillotine cutter at
32 cuts per inch and allowed to equilibrate at 60% RH and 68°F for
a minimum of 48 hours.
Preparation of Cigarettes Containing Additives. Soluble addi-
tives were dissolved in water and added to a casing mixture of
glycerin, propylene glycol, invert sugar, corn syrup, flavorant
materials, and water. Insoluble additives were added to the casing
mixture and pebble-milled for a minimum of 12 hours. The contin-
uously stirred casing/additive mixture was applied to a blend of
BBMT tobaccos in a casing cylinder. Reconstituted tobacco was added
to the blend and the blend was cut and driedtwith cut tobacco stems
and expanded tobacco added during the drying operation. In most
cases, non-filter cigarettes were manufactured on factory production
equipment. In certain instances, cigarettes were.manufactured with
filters designed to yield the desired levels of smoke constituents.
Several of the additives were incorporated in a reconstituted
tobacco sheet to maximize catalytic availability. To prepare the
treated reconstituted tobacco, the additives were dry-mixed with
a blend of ground BBMT tobacco strips, a-cellulose, and
sodium
carboxymethylcellulose. A solution of water, propylene glycol, and
glycerine was added to the dry blend and the combination wet-mixed
until the appropriate consistency was achieved. The material was

then pressed into sheets on factory production equipment, cut into
4 inch squares and finally shredded using rotary cutters at a rate
of 32 cuts per inch. The resulting product was used to manufacture
cigarettes.
Tobacco Pyrolysis Procedure. Approximately 160 g of cut tobacco,
equilibrated at 60% RH and 68°F, was packed to a density in the
range of commercial cigarettes in the apparatus shown in Figure 1.
The tobacco was lit at the surface of the screen cylinder and the
rate of combustion was controlled by pulling a vacuum through an
exit tube located at the axis of the cylinder while simultaneously
bleeding N2 into the tobacco mass through the two end screens. The
flow conditions were selected to give a PAH composition similar to
that observed for CSC.
The pyrolysis condensate was collected in two glass traps,
cooled in liquid air, connected in tandem at each end of the exit
tube. After pyrolysis, the traps were washed with redistilled
acetone and the yield of "dry" condensate determined by evaporation
of an aliquot. Preparation of the PAH concentrate was carried out
as described in our previous report for CSC (Mold, 1978), (Standard
Procedure for Preparation of a PAH Concentrate from Cigarette Smoke
Condensate).
Evaluation for PAH content was performed as described previously,
either by the SGS Test, or by measurement of total infrared absor-
bance at 11.9-14.Ou (Fuson, 1956) or the ratio of absorbance at
3050 cm-' to that at 2960 cm-1 (Wiberley, 1961). When the esti-
mation of activity was by SGS, the activity is reported as the ED50.
When the measurement of infrared absorbance was used to predict tne
biological activity, it is reported as the PED50. In order to place

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the PAH level, or activity, on the basis of its concentration in
the pyrolysate or CSC, these results have been expressed in terms
of the number of ED50's per gram of dry condensate (DC).
Mass Spectrometric Analysis of PAH Concentrates. The pro-
cedure used for these measurements was suggested by a publication
by Biros (1970) and is essentially similar to that later described
by Blumer (1975). Over the period of time during which samples
were analyzed by this technique several different instrumental com-
binations were used. The most recent utilized a DuPont 21-490
mass spectrometer in combination with a Finnegan-Incos Model 2300
Data System.
An aliquot of an ether solution was placed in the probe glass
capillary (1.5 mm ID x 19 mm) such that, after careful evaporation
under vacuum, 10 ug of the PAH concentrate and 1.2 ug of o-tolidine
(mol wt 212), used for internal standard, remained. The mass spec-
trometer ionizing voltage was set at 12 e.v. and the data system
was programmed to acquire 150 spectra at the rat e of 1 spectrum
every 6 sec. Scanning was begun, and the sample in the solid sam-
pling probe was introduced through the vacuum lock into the ion
source. The temperature of the sampling probe was manually increased
from 75°C to a final hold temperature of 290°C over a period of
7.5 minutes.
After acquisition of the 150 scans, one hundred consecutive
spectra were averaged by the data system beginning with the spectrum
taken at the time the probe was first introduced into the ion
source. The resultant averaged spectrum was normalized on the
internal standard peak at m/e 212. Figure 3 presents this low

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voltage molecular ion summation for several samples of PAH concen-
trates calculated as the percent of total ion intensity.
Characterization of the PAH Concentrate by High Pressure Liquid
Chromatography (HPLC) and Gas Liquid Chromatography(GLC). The
presence of PAH's in the concentrate was demonstrated as follows.
The concentrate was fractionated by gel permeation chromatography
(GPC) (Severson, 1976). The GLC pattern published by Severson (1976)
was essentially duplicated when the GPC fraction was subjected to
similar conditions. The authors used GC-MS to identify most of the
components as PAH'.s. Further verification was obtained by reverse
phase HPLC analysis of the GPC fraction with detection at wave-
lengths of 340, 308, 384, and 430 nm, allowing identification of
pyrene, chrysene, benzo(a)pyrene (BaP) and anthanthrene by retention
volume. The presence of BaP was additionally confirmed by injecting
a portion of the GPC fraction into the GLC, collecting the BaP
peak, and rechromatographing by reverse phase HPLC using 384 nm
detection. A 30-40% recovery was obtained when 7,10-14C-BaP was
treated in this manner.
Evaluation of CSC for Carcinogenicity by Painting on Mouse
Skin. Cigarettes were equilibrated at 60% RH and 68°F and smoked
to 30mm butts on Liggett & Myers Model 4 smoking machines (Hackney,
1965). Thirtyfive-ml puffs of 2-sec duration were taken at one
minute intervals. The smoke condensate was collected in two liquid
air cooled traps, dissolved in acetone, and the acetone removed
under reduced pressure at 40-50°C. The final "dry" condensate was
2
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dissolved in an appropriate volume of acetone to give 50 mg of ~
condensate per 100 mg of solution. W
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For each test group, 50 Swiss Ha/ICR female albino mice were
used. Hair was clipped from the dorsal test area prior to each
painting using an Oster Co. (Racine, Wis), Model A-2 small animal
clipper with a size 40 blade. The animals were 9 weeks of age at
the start of the experiment. Application of 100 mg of smoke con-
densate solution was accomplished with a Grumbacker No. 6 camel
hair brush. Test materials were applied five days per week for
80 weeks. (Insert Page 6a)
Evaluation of Cigarette Smoke for Cytotoxicity and Ciliatoxicity.
The procedures used were identical to those described in the report
of the U.S. Dept. of HEW, Appendices A and C (Gori, 1976).
Evaluation of Cigarette Smoke for Mutagenicity.
.n
(Described smoke preparation)
The mutagenicity of CSC was examined using histidine auxotrophs
of Salmonella typhimurium. The strains used in this study were
obtained from B.N. Amesb, and are identified as TA-98, TA-100 and
TA-1538. Their properties and the specific
details of the assay
are given by Ames et al. (1975). Briefly, the test organisms,
microsomal preparations (S-9 fraction) where required, and the material
to be assayed was mixed in a culture medium containing insufficient
histidine to allow the bacteria to proliferate sufficiently to give
colonies. After incubation for two days at 37°C, the clones of

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Analyses For Smoke Constituents of Cigarettes. Cigarettes
used for these analyses were equilibrated for at least 24 hours at
60% RH and 68°F prior to smoking for analysis. The nicotine-free
dry smoke (NFDS) and nicotine were determined by procedures
described by Bates (1967) which are essentially identical to those
used by the U.S. Federal Trade Commission (FTC) for reporting "tar"
and nicotine values in commercial cigarettes.
Carbon monoxide was determined as described by Collins (1973).
Catechol was determined essentially as described by Guerin
(1976).
Acetaldehyde and acrolein were determined by the procedure
described by Norman (1968).
Hydrogen cyanide was determined as described by Collins (1973).
Phenols were determined essentially by the colorimetric
procedure described by Oakley (1964) modified to adapt to automation
with Technicon modules.
Formaldehyde was determined as described by Spincer (1971)
modified to adapt to automation with Technicon modules.
For the determination of nitric oxide (NO) in cigarette smoke,
cigarettes were smoked on an 8-port syringe smoker, and each 8x35cc
puff was exhausted into a polyethylene bag enclosed in a glass
aspiration flask. A 12cm X 8mm OD tube containing silica gel was
inserted ahead of the NO analyzer to remove aldehydes and water
which otherwise interfere in the determination. The system was
otherwise identical to that described by Collins (1973) with the
exception that the syringes contained no oil. Within 15 seconds
after a puff, the bag was exhausted through a non-dispersive IR
~
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4
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.s
analyzer (Beckman Model 215A) and the NO concentration calculated
from calibration curves obtained with standard gases. The per
puff values, including clearance puffs, were summed to give ciga-
rette deliveries. Values obtained by this method agree with those
by colorimetric and chemiluminescent determinations on the same
cigarettes. Details of this procedure will be published at a later
date.
For the analysis crf nitrosonornicotine (NNN), cigarette smoke
was collected in aqueous alkali, concentrated by extraction into
benzene-chloroform (9:1) followed by back-extraction from chloroform
into aqueous acid and re-extraction into chloroform at pH 5. Further
separation of NNN was achieved by thin layer chromatography on
silica gel and reverse phase high pressure liquid chromatography.
Detection was by UV at 254 mu with isotope dilution to measure
recovery. Details of this procedure will be published at a later
date.
Smoke was analyzed for N-nitrosodimethylamine (NDMA) using
a method basically similar to that of Rhoades (1972). Smoke samples
were collected in either sodium hydroxide or ascorbic acid solution
to prevent artifactual formation and were cleaned up by distilla-
tions from basic and acidic solutions and by distribution between
solvent pairs prior to GLC analysis for NDMA which was accomplished
with a dual column system and a Hall electrolytic conductivity
detector. Recoveries of NDMA through the cleanup and recovery
procedures were determined using a radioactive tracer technique O^
j
employing NDMA-C14. W
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bacterial outgrowth were counted. Usually, three replicates per
assay level were employed. Dimethylsulfoxide was used to dissolve
the smoke condensates for ali.quoting.
Evaluation of Filter Cigarette Prototypes for Subacute Toxi-
city by Inhalation in Rats. The diagram in Figure 8 shows the
essential features of the inhalation apparatus. Cigarettes were
smoked on a Liggett & Myers Model 4 smoking machine (Hackney, 1965)
modified to smoke 30 cigarettes with 35-m1 puffs of 2-second dura-
tion at one minute intervals. All cigarettes utilized in the experi-
ment were kept refrigerated and sealed until approximately 48 hours
prior to use, when the cigarettes were humidified in a chamber con-
taining a supersaturated solution of sodium bromide in sterile
water. Ten puffs were taken on each cigarette. A peristaltic
pump supplied the pressure differential for the puffing. Air to
dilute the fresh smoke stream was supplied from a reservoir through
a flow regulator which was adjusted to give the desired smoke dilu-
tion.
The inhalation exposure chamber was situated directly beneath
the smoke-mixing chamber and consisted of a cylindrical manifold
into which twenty cassettes, each designed to contain one rat,
could be securely inserted. During the experiment, the animals'
noses were pushed into the manifold where they were secured for
exposure to the smoke stream by means of an adjustable plunger
from the rear. All rats on test were examined twice daily for
general appearance, clinical signs and survival. Body weight and
(Z
food intake of individual animals were monitored weekly. Water con- .~
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sumption was recorded daily. Animals were maintained throughout the V,
. N
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study on Purina Lab Meal and water ad libitum 0
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