Lorillard
Trapping and Determination of Labile Compounds in the Gas Phase of Cigarette Smoke
Fields
- Author
- Horton, A.D.
- Zeldes, S.G.
- Alias
- 89737859/89737862
- Type
- PSCI, SCIENTIFIC PUBLICATION
- BIBL, BIBLIOGRAPHY
- CHAR, CHART/GRAPH/MAPS
- DRAW, DRAWING
- Area
- SPEARS,ALEXANDER/EXEC CONF ROOM STO
- Site
- G65
- Named Organization
- Computer Sciences Division
- Ctr, Council for Tobacco Research
- NCI, Natl Cancer Inst
- Oak Ridge Natl Lab
- Union Carbide
- US Dept of Energy
- Bio Organic Analysis Section
- Centre College Danville
- Chemistry Division
- Named Person
- Baldwinn, W.H.
- Bayne, C.K.
- Ho, C.H.
- Zeldes, S.G.
- Date Loaded
- 12 Feb 1999
- Master ID
- 89737566/7894
- 89737566-7894 Annual Report Collection, Separation, and Elucidation of the Components of Cigarette Smoke and Cigarette Smoke Condensate Part I. Chemical Characterization of Experimental Cigarette Smokes Part II. Inhalation Bioassay Monitoring and Support Part III. Dosimetry and Bioimpact
- 89737577-7588 I. Chemical Characterization of Tobacco Smoke From Beagle Dog Inhalation Exposure Systems
- 89737589 II. Final Data - Series IV Cigarette Smoke and Condensate Chemical Analyses
- 89737590-7599 Topical Report NCI / S&Hp / Ornl Number 52 Final Smoke and Condensate Data for the Fourth Series of Experimental Varia Nts
- 89737600-7602 III. Chemical Analysis of Smokes of Foreign and Domestic Commercial Cigarettes
- 89737603-7606 Topical Report NCI / S&Hp / Ornl Number 49 Tar, Nicotine, Co and Co2 Deliveries of Philippine Cigarettes
- 89737607-7610 Topical Report NCI / S&Hp / Ornl Number 61 Tar, Nicotine, Co and Co2 Deliveries of Philippine Cigarettes
- 89737611-7614 Topical Report NCI / S&Hp / Ornl Number 66 Tar, Nicotine, Co and Co2 Deliveries of Italian Cigarettes
- 89737615-7621 Topical Report NCI / S&Hp / Ornl Number 51-A Chemical Analysis of Smoke From Second Set of Certain Domestic Commercial Low Tar and Nicotine Cigarettes
- 89737622-7624 Topical Report NCI / S&Hp / Ornl Number 53 Chemical Analysis of Smoke From Second Set of Certain Domestic Commercial Low Tar and Nicotine Cigarettes
- 89737625-7632 Topical Report NCI / S&Hp / Ornl Number 68 Chemical Analysis of Smoke From Selected South Florida Variants
- 89737633-7647 Topical Report NCI / S&Hp / Ornl Number 70 Chemical Analyses of Smoke From Selected Foreign Cigarettes United Kingdom, Uk Export, and Developing Nations
- 89737648-7649 IV. Swri Baboon Study Smoking Extremes Experiment
- 89737650-7655 Topical Report NCI / S&Hp / Ornl Number 58 Chemical Analysis of Smoke Delivered by Swri Baboon Study Cigarette Under Three Smoking Conditions
- 89737656-7661 V. Statistical Modeling of Histopathological Probabilities
- 89737669-7682 I. Monitoring of the Chronic Inhalation Exposures
- 89737683-7698 Topical Report NCI / S&Hp / Ornl Number 41 Site Visit I to Battelle Pacific Northwest Laboratories Rat Model Inhalatio N Bioassay Richland, Washington, 770223 - 770224
- 89737699-7714 Topical Report NCI / S&Hp / Ornl Number 44 Site Visit Vi to Veteran's Administration Hospital East Orange, New Jersey, 770502 - 770503
- 89737715-7729 Topical Report NCI / S&Hp / Ornl Number 46 Site Visit IV to Hazleton Laboratory Reston, Virginia, 770521 - 770522
- 89737730-7748 Topical Report NCI / S&Hp / Ornl Number 48 Site Visit I to Enviro Control Inc. Inhalation Laboratories Temple Hills, M Aryland, 770523 - 770525
- 89737749-7760 Topical Report NCI / S&Hp / Ornl Number 54 Site Visit Vii to Veteran's Administration Hospital East Orange, New Jersey, 770808 - 770809
- 89737761-7768 Topical Report NCI / S&Hp / Ornl Number 55 Intercomparison of Tobacco Smoke Dose Beagle Dog Inhalation Bioassays
- 89737769-7777 Topical Report NCI / S&Hp / Ornl Number 59 Inhalation Bioassay of Tobacco Smoke in Pigeons Site Visit I to Beth Israel Hospital (Bih) Boston Massachusetts, 771130 - 771201
- 89737778-7798 Topical Report NCI / S&Hp / Ornl Number 60 Site Visit II to Battelle Pacific Northwest Laboratories Rat Model Inhalati on Bioassay Richland, Washington, 770914 - 770915
- 89737799-7817 Topical Report NCI / S&Hp / Ornl Number 62 Site Visit II to Borriston Research Laboratories Temple Hills, Maryland, 77 1107 - 771109
- 89737818-7833 Topical Report NCI / S&Hp / Ornl Number 64 Site Visit V to Hazleton Laboratories Reston, Virginia, 771105 - 771106
- 89737834-7844 Topical Report NCI / S&Hp / Ornl Number 67 Site Visit I to the Hazleton Laboratories Cofactor Inhalation Bioassay Rest on, Virginia, 780223
- 89737845-7856 II. Instrumental Approaches to Bioassay Monitoring
- 89737857-7858 III. Trapping and Determination of Organic Gas Phase Constituents of Cigarette Smoke
- 89737863-7865 IV. Determination of Nitric Oxide and Nitrogen Dioxide in Cigarette Smoke by Chemiluminescent Analysis
- 89737868-7869 I. Brl - Ornl Collaborative Smoke Particulate Deposition Experiment
- 89737870-7876 II. C Tracer Studies to Develop Sampling Protocols for Quantitative Nicotine Dosimetry Following Smoke Exposure
- 89737877-7884 III. Isolation and Quantitative Analysis of Nicotine and Cotinine in Physiological Fluids
- 89737885-7894 IV. Physiological Fluids Studies: Mutagenicity and Profiling
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ANALYTICAL CHEMISTRY, VOL. 50, NO. 6, MAY 1978 779
Trapping and Determination of Labile Compounds in the Gas
Phase of Cigarette Smoke
Steven G. Zeldes and Arthur D. Florton'
Analytical Ghemistry t7ivision, Oak Ridge National LaGoratory, Oak Ridge, Tennessee 37830
The gas phase of cigarette smoke was trapped and stored on
Tenax-GC for subsequent off-site analyses. Specifically, the
highly labile compounds isoprene, acetaldehyde, and acrolein
were determined quantitatively in the samples which were
thermally desorbed In the injector port of a gas chromatograph
onto a cooled gas chromatographic column. Optimum con-
ditions were determined for adsorption and desorption of the
gas phase, and the effects of aging on the trapped gases were
studied.
It is necessary to chemically characterize the cigarette smoke
offered experitnent..'tl animaLs in inhalation bioassays to define
the extent and quality of the exposure. It is also of interest
to determince the chemical nature of smoke-polluted envi-
ronments to assess the possible impact of smoking on
nonsmokers. Tenax adsorption followed by thermal de-
sorption and gas chromatography has been evaluated as a
method for characterizing the volatile organic gas phase
constituents of smoke.
One of the routine analyses of the gas phase of cigarette
smoke is the determination of isoprene, aeetaldehyde, and
acrolein (t}t the first because of its close correlation to bio-
logical activity of smoke, and the others because of their
ciliatoxicity. If these highly labile compounds can be trapped
and retained, then the less labile components of interest should
most likely he retained also. Breakthrough volumes have been
determined (.3, fi, t:3) for a number of compounds, some of which
appear in cigarette smoke. Double trapping experiments have
shown that our results agree with th<?se authors for compounds
of common interest.
"Penax-f.C° has been used with some success to trap labile
compounds in automobile exhausts (2, 3), ambient air (3, 4),
and stack gases (5).
The traps used for t.hese samples differ only in size, each
consisting of a Pyrex tube packed with Tenax lielc6irr place
by glass wool plar;s. The methodology used at this laboratory
was adapted from that (rf Zlatkis. L.ichtenstein, and Tishhee
N) who used a P' vrex tube I I cm long. 10-mm o.d. and $-rmn
i.d. packed with 4 mL of 35 to 60 me:h Tenax. Samples were
adsorbed throu h a condenser and desorbed in a mcrdifieci
injector port tknttY a cold l)recolutnn. then desorbed a;iecond
time c>nto an open tubular coltarnra. r!t thi,, laboratory, the
traps were desrrrbed in the rnoditied in,iector port directly onto
a packed column carotet.l to ---7t? Qd'.
EXPERIMENTAL
Adsorbent. Tenax-GrC; (Applied Science Laboratories, Inc.,
State College, Pa.), a porous polymer, poly-p-2,6-diphenyi-
phenylene oxide was selected over other common adsorbents
(Porapak, Carbosieve, or activated charcoal) for its several ad-
vantages. Its high temperature limit of 450 °C (6) and low re-
tention volumes (7) allow high-boiling sample components to be
desorbed more rapidly than frorn other adsorbents. In addition,
the effect of water vapor on the efficiency of Tenax (8) is in-
significant.
Preparation of Traps. Traps consisted of Pyrex glass tubing
(9-mm o.d., 5-mm i.d.) cut into 5r/.r-inch lengths and fire-polished
at each end. One end is ground to a taper to form a seal in the
injector port. i15Jf g-inch glass wool plug is placed in the tube at
one end, the tube filled, while vilxatin ;, with 60/80 mesh Tenax
then topped with a', 8-inch glass wool plug.
Traps are conditioned by heating at 250 °C for 30 anin while
purging with nitrogen. Conditioned traps are stored in a des-
iccator.
Sampling Procedure. Samples were collected from weight
selected (1C194 f"() mg) Kentucky Reference (II2Ip cigarettes
conditioned at 75 °F and 60% relative humidity using an ORNL
Single Port Smoking Machine. See Figure 1. Cigarettes are
smoked at a rate of I puff per minute (II puffs x35 mLjput`f)
using a small vacuum pump to draw each puff through a 0..3~-mL
sampling loop. An additional length of tubing is placed before
the inlet to the gas sampling valve in order to collect the sample
from the middle of the puff. Nitrogen carrier gas flows through
1;'h-inch'Peflon tubing to a solenoid valve which, when activated,
directs the flow through the sample loop arxi, when deactivated,
allows the flow to h,ypass the loop while the puff is drawn. The
carrier then travels through connecting tubing to a stainless steel
three-way valve where it is either directed to the modified injector
port (4) of the Perkin-Elmer 3920 gas chromatograph or to a
~amphng port to which a trap is attached. See Figure I..
During a standardizing run (wit.hiautt trapping) (Figure 2), the
carrier containing the sample is directed t:~ the injector port of
the gas chromatograph. A simulated trap, filled completely with
glass wool, is placed in the injector port to reduce its volume. :a
number of such runs serves to establish the expected level of
organic components in an average cigarette. For a run in which
the sample will first be trapped on'Penax, then analyzed (Fit;ure
:3), a reduced carrier flow (10 mLjmin) is used to purge the sample
from the loop into the tapered end of the trap.
Carrier gas flow was 12 rnL,tmin (30 psig). Injector port
temperature was ry:it) °C; and FID temperature 1,50 °C.
Colunrn. G(' C:ralumzn. The column used for thet determinatirm
4 isoprene, acetaldehyde, and acrolein was a modification of one
used rnutinelv (1) for this purpo. se. The ~atatianarv ph&;e
:;,:"'-Itrintethy lenedis'xyDdil:roropic~nitrile was synthesized by
equilibrating a 1:" mixture of acryloinitrile and 1..3-prnpanrdrc7l
,
Pubh9ht:7 ?978 by the Amerscan Chemical Society

780 ANALYTICAL CHEMISTRY, VC3L. 50. NO. 6, MAY 1978
~ :MSrer~i;~k
NNER Sy.lAY
1 i i " _.L.Er:oo
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~ I r~uIA9GE
~ 1 ~ 4!?4.lvME.
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LC+w
~;CMYTittiL i
Af.VE
CFNA-VAC
PUMP
' ..... LRt.(
:
4
. MRF.1:', - N4Y
Figure 1. ORNL single port smoking machine and attached Tenax-Gc
trap
(l 150PHENE
2' ACC7ALUEHY6E ~®
MF4Y.YI. Fcri1t.mTE
GfioPIONALOEHtDE
.3~ 2-ME.iHYLFUR.ANE1HY4.f4'HMATE
.5) Aff PMYLACETATE ~
ACRSX.EM ~
,8ACELQNC
t
~
I TIME
~ .......:.........._...._.......1_.....-_...._.__.(_.__.,......__2,._..~....1.
_:..._...~.~.L_.....__..,._ L_-,i
ao sa 'a0 a° 30 zo 1q 0
TIME(mul
Figure 2. Standard chrornatogram of the gas phase of a Kentucky
reference (1R1) cigarette (not trapped). Vol. of gas phase, 6.7 mL;
injector port, 250 °G, FID, 150 °C; flow rate, ^ 12 mL N2/min
I
y1D 1:40PRF,'NE
(23 eC ETALDEHtDE
i3) MCTHYL FJRMGTE
rROP(aN4LOEHVDE
(g 1 1-. ME TNY L F UR e. N E THYL F0RM4T E
(El ME'+HYC4CET4TE Cl`~
~7( 4CR0LeIN
4CETONE ~
7o 60 3C) 40 30
TIME (mm)
10 0
Figure 3. Chromatogram of the gas phase of a Kentucky Reference
(1R1) cigarette (desorbed from Tenax-GC). Vol. of gas phase, 6.7 mL;
trapping flow rate 10 mL/min; desorption time. 10 min ii; 250 °C (trap,
5'/{-in. X 5-mm i.d. packed with 60/80 mesh Tenax-GC. Other
conditions same as standard run
at room temperature for 72 h, then vacuum distilling and collecting
the fraction boiling at 170 °C at a pressure of 1 man (9). A l5-ft
X 2-mm i.d. Pyrex column was packed with 15 vrk 'To of the liquid '
on 100 to 120 mesh C:hromosorb W(HP), and _ conditioned
overnight at 90 °C and 20 n1L Njrnin. The FID was used for
all analyses.
C'hrorourtepgraphLc Prrrcedurc. Straig;htt runs used for calibration
were performed by sampling as described. The saanple is collected
cryothermally at thee head of the column by cooling the column
to -70 °C with liquid nitrogen. When sampling is complete,
temperature programming begins at 8°C/'min to 10 °(.'., then is
held constant for 4 nxin before programming at I°C f rnin to 70
°C.
Trapped runs are performed by trapping the sample as de-
scribed, then reruoa>ing the simulated trap from the injector port
Table I. Trapping Efficiency Relative to Sample Size"~
Isoprene, Acetaldehyde, Acrolein,
hp34°C bp21°C bp52.5°C
Vol. of gas 4.2 6.7 4.2 6.7 4.2 6.7
phase, mL
Av tcg std run 6.4 10.2 10.7 17.2 1.4 2.2
Avµg 6.3 8.0 8.6 1.0..1 1.4 1.9
trapped run
Recovered, ~`0 98 78 80 59 100 86
a Trapping flow rate 10 mL/min, desorption time,
10 min.
and replacing it with the Tenax trap with its tapered end at tlie
column inlet. Note: The sample is always back-flushed from the
trap. With the spring arid septum cap in place, the carrier gas
is set at 30 psig and the trap is desorbed for 10 min at 250 °C
onto the cold column. When desorption is complete, ternperatr.tre
programming begins and follows that of the straight run.
DISCLISSION
'I`he technique described in this paper requires 12 min for
sampling, 10 rnin for desorption, and lZ h for analysis; a taatal
of less than 2 h. Straightt runs require 1.0 min less since they
do not have to be desorbed. Trapping the sample provides
a means for sampling a source which could not be analyzed
otherwise.
EFFICIENCY
Efficiency of the trap is critically related to the sample size.
method of storage, and the conditions under which it is
desorbed for analysis. These criteria will be discussed in the
order of their importance.
The capacity of a trap cannot be easily defined. Each
constituent has a unique distribution coefficient which de-
scribes the ratio of the amount of that constituent adsorbed
on the Tenax-GC to the amount contained in the gas passing
through the void volume of the trap. The amount of any
compound which can be adsorbed on the Tenax (trap capactiy)
is a function of the concentration of the total sample.
(Concentration in thi..5 system is determined by sample volume
and the rate of carrier flow through the sample trap.`r
Therefore, trap capacities (breakthrough volumes) of sin ;le
components will differ depending upon whether they are
trapped as individuals or are contained in a nlulticornponent
mixture. Optimutn sample size can be determined by plotting
the percentage of the desired component trapped vs. total
sample size. The optimum sample size obtained by these
criteria was 4.2 mL. Each curve should contain a flat
maximum (provided detection limits are not exceeded) along
which the sample size is within the capacity of the trap, thus
allowing one to choose the optimum sample size for any
component. One can assume the trap capacity has not been
exceeded if 95% of the desired component is recovered. If
a lower percentage is recovered, the trap may be overloaded.
See Table 1.
Flow rates between 1.7 mL f min and 250 mL/min were tried
for the carrier gas flow through the trap during sampling.
Multiple determinations were made at 4, 1.3, 15, 20, and 40
mL f rnin. Figure 4 shows the amcbunt. of each constituent
trapped vs. the rate of flow through the trap. Arnotuats
collected in traps filled at less than capacity are also dependent
on the rate of flow but to a lesser degree. The curve tends
to have a broader apex at which the efficiency is more de-
pendent on the total volume of flow rather than the rate of
flow. The apex shifts toward lower flow rates so that the
optimum flow is not the same for all sample sizes.
Other factors which affect efficient Tenax use are con-
trollable by the analystt. Tenax is available in two mesh sizes:
:35 f ti0 and G0;'$tl. The finer mesh size proved to be a better

ANALYTICAL CHEMISTRY, VOL. 50, NO. 6, MAY 1978 781
600
500
ACETALDEHYDE
ISOPRENE
75
65
.__....-.. _. ..... _.......... .
0 5 10 15 20
Nt FLOW RATE DURING TRAPPING (rcofffmin)
Figure 4. Trapping efficiency vs. flow rate
adsorbent, probably because of increased total pore area.
While the trap size is limited to 5t f,; inches by 9-mm o.d. by
the dimensions of the injector port, variations are possible for
the bore diameter and the volume of packing. The first trap
was 7-mm i.d. with about 2 mL of Tenax. Trapping efficiency
was poor and gas chromatographic elution peaks were broad
and tailing. One milliliter of packing was then tried with even
more disappointing results. Double plugs r!f la/2 mL each in
a single trap resulted in a sig aificant improvement, but proved
to be no better than 3 mL in a single plug. This led to the
use of a smaller bore (5 mm) glass tube 51 f.a inches long which
was fully packed with Tenax (2.2 mL), and which resulted in
a large improvement in resolution without a significant loss
of capacity. A 3-mm i.d. trap was tried (0.8 mL'henax) for
which the resolution was even better. 1:3ecause of the loss of
capacity for the 3-mm i.d. trap, however, further work was
done with the 5-mm i.d. fully packed trap.
These results lead to the following conclusions: (1) A
decrease in the bore diameter of a trap increases the resolution.
(2) Greater component retention per unit volume of packing
may be achieved with a decrease in bore diameter (7).
Desorption. Of all the factors related to the desorption
of the trap, the most critical is backflushing of the sample.
No recognizable chromatograms were produced without using
this technique.
The time required for a trap to he desorbed ofitc> the
cryothermal column refers to desorption time prior to ini-
tiating the temperature program on the chreamatagraph. The
trap remains in the hot injector port during the.entire run.
The proper time is important for the analysis of labile
compounds (see Figure 5). Likewise the temperature of the
injector port must be hot enough to release all the components
of interest without inducing decomposition of the more re-
active ones. An injector port tempe.r::ature between 250 °C and
:3t7C1 °C proved to he best for isc,prena::. acetaldehsde, and
acrolein.
It became apparc:ntt after surne time that part of the sample
was not recovered, even though it was completely adsorbed
,:yn the trap. Four possible causes existed: (I) The time
_A¢;ROLEIN
300
4.2m1 OF GAS PHASE I
200 _ f f I
0 5 10 15 20
DESORPTION TIME (min)
Figure 5. Trapping efficiency vs. desorption time
elapsed between placing the trap in the injector port and
replacing the septum cap on the partt allowed some sample
to escape. (2) The sample was retained by chemisorption on
the Tenax packing. (3) The sample reacted with oxygen in
the injector port. (4) The species of interest reacted with other
constituents in the sample.
An injector device for glass traps machined to attach to the
injector port in place of the septum cap allowed purging of
air from the injector port before injecting the trap into the
hot zone and ensuring that the sample did not desorb pre-
maturely nor react with atmospheric oxygen. Experiments
performed here and by others (6) indicated that the sample
clid not react with the Tenax. Thus, it was concluded that
the components of interest were probably reacting with other
labile constituents in the smoke. The loss was not large and
was rectified by using smaller samples and lowerinl; the in-
jector pcartt temperature.
Traps were assumed to be reconditioned after desorption.
Repeated use of up to several dozen times resulted in no loss
of efficiency, as is reported also by Pellizzari, Bunch, Berkley,
and McRae (3).
Aging. Experiments on the aging of trapped samples up
to three days l:arcaduced conflicting data. There was no loss
of components in samples aged for 22 h and for 70 h, re-
spectivelv, while samples aged only 5 h suffered high losses.
Statistical analysis of aging data by the methrrd of least squares
using a linear model showed no trend in the plots of peak areas
c'tf acrolein and acetaldehyde vs. aging time a.ap to three days.
Isvprene showed only a slight downward trend.
Traps were capped with number three polyethylene end
caps and placed on a shelf in the laboratory for aging. Traps
were not protected from rrx,m light. Itt is likely that ;;umc: of
the caps produced a better seal than crthers.` Future work on
aging should provide a meanfi of capping the ends (if the trap
tightly with Teflon seals, orpossihly sealing the t.rap in gl:ass
capsules, and storing them in the dark.
:kgint (tf samples for over one week has been reported with
the trapping of many organic compounds withcsut a signitic°ant.
loss of sample (.3).
i

782 ANALYTICAL CHEMISTRY. VOL, 50, NO. 6, MAY 1978
C'f7NC'L[ISIf3NS
By use rtf the technique de:,x-rihed herein, itt is E7ussible to
trap and recover the mure highly labile c<,rnponents in the gas
phase of cigarette smcakes All of the isufaeene and acrolein and
8(} % of the acetaklehycle was recovered. l'attern rece.,l;nitian
of the chromatograms indicated that other major components
in the gas phase were recovered also. 'I'hee adscrrpttr7n
characteristics of many of these on Tenax have already been
reported (2-8). Improvements need to he made in the storage
of aged samples. Given these, this method should be ap-
plicable to remote sampling of cigarette smc7ke and other gases
for subsequent analyses at another site.
ACKNOWLEDGMENT
The assistance of W. H. Baldwin of C)RNI. Chemistry
Division and C.-H. Ho of the ORNL Bio f Organic Analysis
Section in synthesizinl; the 3,a'-(trimethylenedioxy)di-
prcapionitrile is greatly appreciated. C. K. Bayne, Computer
Sciences Division, perfcsrmed statistical analyses of the data
t
.
v
011 ahing of tlte gas phase in Tenax.
LI'I'ERATURE7 CITEI)
(1) A, U. Horton and M. R. Guerin, Tobacco, 176, 45 (19741 (Tab. Sci. No.
19).
(2) W. Bertsch, R. C. Chang, and A. Ziatkls, J, Chromatogr. Sc1., 12, 175
(1974),
(3) E. D. ReElizzari, J. E. Bunch, R. E. Berkiey, and J. McRae. Anal. Lett.,
9 (1), 45 (1976).
(4) A, ZIatkEs, H. A. Lichtenstein, and A. Tishbee, Chromatoyraphra, 6(2),
67 (1973).
(5) J. S. Parsons and S. Mitzner, Eviron, Sci. Tecdrnol., 9(12), 1053 (1975).
(6) R. van Wijk. J. Ghrama.atorr. Sci., 8, 418 (1970).
(7) L. CY, Butler and M. F. Burke, J. C;hronkstogr. Sc6., 14, 117 (1976),
(8) J. Janak, J. Ruzickova, and J. Novak, J. Chronaatogr., 99, 689 (1974).
(9) "The Chemistry of Acxylonitrile", 2nd ed., American Cyanamid Co., 1959.
RECEIVED for review November 4, 1977. Accepted February
7, 1978. Research sponsored by the National Cancer Institute,
The Council for Tobacco Research--USA, and the Depart-
ment of Energy under contract with Union Carbide Corpcr-
ratiun. S.G.Z. from Centre College, Danville, Ky. 4U-4''2, was
an ORAU summer research participant.
