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Council for Tobacco Research

Progress Report for Ctr-0030---Smoke Inhalation Studies in Mice [Describes Recent Findings]

Date: 15 Mar 1981
Length: 14 pages
CTRMN044474-CTRMN044487
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Ctrmn00043385-4499
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Author
Dinowitz, M., Mai
Henry, C.J., Mai
Kanalingham, K.K., Mai
Kinkai, H., Mai
Kouri, R.E., Mai
Lubet, R.A., Mai
Depository Date
30 Sep 1997
Box
268
Type
SCIENTIFIC REPORT
UCSF Legacy ID
yqt30a00

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Page 11: yqt30a00 Log in for more options!
SF0250162 II. COROLLARY STUDIES A. C'"R 119. Deposition and Distribution of 2Rl and 3al C: carette Smoke Using the Corti.^.uous Exposure Rec_^en . The results from comparative smoke toxicity studies zave shown that the continuous exposure regimen (C';R 101B) resulted in :fai:ly low toxicity to BC3F1/Cum male and female mice (Progress Report, 1980). A dosimetry experiment using 14C-dotriacor.tane (DTC) labeled 2R1 cigarette smoke was therefore required to deter:nine the actual TPM deposition and distribution under the exposure conditions. The tissues for this dosimetry experi^en= were analyzed for radioactive content at MA using the Packard 306 TRI-CARB Tissue Oxidizer. Previous dosimetry experiments ::s:nc the Walton Horizontal Smoking Machine (WHSM) and the tissue oxi- dizer had demonstrated extremely low and uni_orm background values °or all tissues analyzed (Progress Report, 1980). This was in marked contrast to results previously obtained using a:=o- :^.clic-cotassium hydroxide solutions to solub:lize the tissues. Thus the level of sensitivity and detection tor these exper::::er.:s should be greatly improved. As will be discussed below, the higher background levels due to tissue solubilization solution in terac tions obtained previously may have con tribu:.ed to higher :'P!rM deposi=ioc values than actually occurred when the background :evels a:e low. A brief description of the dosimetry experiment fol:.cws. BC3Fl/Cum female mice, 12-14 weeks old, were exposed to the c;r.- t:nuous exposure regimen for 4 weeks prior to the dosimetry experiment. On the day of the experiment, 64 of these mice we:e exposed to radiolabeled 14C-DTC-2R1 cigarette smoke, along w:::: arn addi _ional 10 mice which had never beern exposed to cicare =_e smoke ("uzadapted"). The experiment was designed so that 3-_re wculd be removed from smoke exposure after each r•.:.^ and the =_ss::es analyzed for radioactivity. The deposition and dis=.:ibu- _ior, of 14C-DTC disinteqrations per minute (dpm) is nresen_er :n '^a!:,le 35 _°or 3C3F1/Cum female mice exposed to 14C-DTC-2R1 ciga- -et :.e smoke under the continuous r egi:nen. Deposi =:on in the l.:::g .::creases linearly with increasing smoke exposure time ( corre:.a- .ion coefficient (r)s0.97), with a slope of -260 dpm/120 second xposure time or "run". An average of 74% (cv - 0.04) of the 4C-OTC dpm was found in the lung for all eight "runs". Coef=i- :ents of variation of deposition in the lung ranged from 0.21 to 39 for the individual "runs". A substantially higher cv of 50 was observed in "unadapted" mice. The average 14C-DTC dpm the lung was also substantially -higher in these animals, sug- sting that alterations in respiratory rates occurred with :ger periods of exposure. This is in contrast to previous sults using a different exposure regimen (CTR 100, 30 seconds :ke alternating with 30 seconds of air for 10•minutes), where :e exposed for different periods of time (3 weeks, 3 months, 6 months) were found to have similar TPM deposition and tribution. 8 Q J .Ki~,`i'Ob10iOgRU 1 :U60CiAteS -~ ~ 11N 044484 C f
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Sr026; :n order to convert the 14C-DTC-dpm to micrograms of TP"!, the specific activity of the TPM :aust be determined. A brief review of the mechanics of the procedures will be given here. The specific activity of the TPM is the :4C-D^_'C d=:.. pe_ ,:c TPM. In the WHSM, this is de _er:nined by burning cigare __es before and after mice are exposed, collecting a:+ of --'-.e par=:c;:- lates on a"condi=ioned" Cambridge filter, weighing the filter, eluting the particulates and counting an aliquot to determine =;:e amount of dpm on the filter. These procedures have bee.^n deta:led previously and data presented (Progress Report, 1980). The amounts of TPM collected on the filter is 30-50 mg and is a resonable amount to weigh quantitatively. . Because the SEM is a dynamic smoke exposure machine and t::e smoke is generated in a flowing stream slightly di:fere.^.: oro- cedures must be employed in order to determline the speciric activity. The optical sensor is calibrated to detect ::ze tota_ ar.iour.t of TPM generated from the cigarettes. A samplinc pump w::hdraws (at a known rate ) smoke ...^.rouch 3"cord= :_c.^.ed" C3m- bridce filter. The amount of particulates i.^. _..is filter '_s generally not sufficient to accurately and reproducib'_y we:g;: ;<5 :ng ), however, sufficient radioacti -jity can be detected a: _er e:.._ ::g the particulates and analyzing by scint:liatiorn counting. vicqtine can also be analyzed from this sample. Thus the amount c~ TPM is detbr:ained from the opt:cal sensor data and the pump sampling rate. The amount of radioactivi _y is determined after el;a:.^.g from the filter and counting. These measurements and the calculated specific activity are presen:ed in Table 36 for t::is dosimetry experiment. Using the specific activity calculated in Table 36 to cor.- ver= 14C-DTC-dpm to microgram TPM results in lung depcsi=ior. ..: 4, 9, 11, 19, 24, 29, 31, and 34 ug TPM for 120, 240, 360, 480, 600, 720, 840, and 960 seconds total smoke expos::re time, :esoectively. These values are far lower than expected and :u=_::er evaluation is rea_uired. The specific activity „_ ='.:e labeled cigarettes will be determined aga_n. If these dosimetry data are confirmed, a dosi:netry experi- ment L:sir.g the exposure regimen used for CTR 100 and C^R lOla will be per=ormed before June, 1981. It is most important to verify the previous results with the SEM where the background valses for the tissues were 3-5 times higher than those irn the present studies, suggesting that the deposition values deter- mined previously may have been influenced by the background. Should this experiment be necessary, SEM II time can be scheduled in April. B. CTR 109. Alteration of the I:nmune Resnonse After Exposure to Cigarette Smoke (Dr. H. Herscowitz). Collaborative studies with Dr. H. Herscowitz (Georgetown University, Washington, D.C.) have investigated the 9 ~~ .KiC10biOlO~CRI ASSOcialPS _wjmn CTR HN 044-48"IE-5
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SF025C15^ immunosuppresive effects of cigarette smoke in BC3F1/Cum female mice. The following criteria have beern used to determine the immune reponse: 1) antibody production at the cellular level as reflected by the spleen plaque assay (?FC assay), 2) antibody oroduction in vivo as determined by circulating hemagglut'_:.a- ting antibody 711A7,.and 3) mitogen induced proliferation of spleen cells. Previously Dr. Herscowitz has demonstrated that all 3 responses were significantly suppressed in BALB/c mice after exposure to 1R1 cigarette smoke but not to lAl cigarette smoke using the WHSM (Progress Report, 1979). Exposure of BC3F1/ Cum mice to 2R1 cigarette smoke did not result in a consistent depression of the antibody production (?FC assay) when compared to sham-exoosed controls. :n order to deter:nine whether the lack of deoress;orn of the ?FC respor.se in BC3F1/Cum mice was due to differences :n strains, experiments were designed to expose both 3C3F1/C;:m and 3AL9/c C::- ~nice under the same conditions and at the same time. The 3,a.3;"c :nice would serve as positive controls of _nhib:=iorn and _::e resul :.s f?om the PFC assay for the two str ai.^.s could be .._: ec::1 comDared. As reported previously (Progress Report, 1980), neither ac::te r.or 'czronic e•xposure to 2R1 cigarette smoke caused significant i.-unur.osuoflression in either BALB/Cum or BC3F1,/Cum mice under the conditions employed in these experiments. Further analYsis of these data by Dr. Herscowitz has raised the following issues (CTR 3rant #1045B, Progress Report $2, 1980 Dr. H. Herscowi:z). -f the number of PFC observed are presented per spleen, rat^er than per million spleen cells, a reduction in the number of PFC,' spleen is observed in the smoke-exposed compared to the shar••- exposed animals. The number of cells recovered per spleern decreased 30-50% for smoke-exposed, compared to sha.•n-exposed animals, and the numbers of cells recovered seemed :cw compa:ea to oublished results. Further analysis and in:erpreta::on of these data are in progress. C. C'"R 105. Deoosition, Distribution and Clearance cr 3H- Catechol (CAT in BC3F1 Cum Mice a::er to 3H-CAT-2R1 Cigarette Smoke. As reported previously (Progress Report, 1980), the pharma- cokinetics of inhaled 3H-CAT have been Ieter.^•iined in 3C3F1/Cum mice after exposure to 3H-CA': aerosolized in 2R1 cigarette smoke. CAT, 1,2-dihydroxybenzene, is of interest in that it represents the diphenols in cigarette smoke and is present in moderately high concentrations (220-550 mg/cigarette), and has been reported to be a weak carcinogen (Van Duuren, B.C., Katz, C., and Gold- schmidt, J., J. Natl. Cancer Inst. 51, 703, 1973). More recently, its weak carcinogenicity has been confirmed. It has also been reported to be a potent cocarcinogen (aecht, S.S., Car.nella, S., Mori, H., and Hoffmann, D., J. Natl. Cancer Inst., 66, 163, 1981). 10 ~s .~~~~ .~SSOCiateS fl^~Il .r..-. .....' TR PIN ~'..~. 44• I•....r.x.J'
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~.~ 2 .~ ~ C r U ;~ 3H-CAT in cigarette smoke was rapidly cleared- from the respiratory tract, with rapid redistribution occurring dur:.^.c the 10 minute exposure period (Table 37). The half-life (tli2) of 3H-CAT in the lung was less than 4 minutes. 3H-CA': was absorbed in the blood and rapidly removed. Signi::cant levels of :ad:;- ac:ivity were found in the liver and kidney im.mediately after exposure (Table 37); however, these decreased rapidly. Two hours after exposure, -908 of 3H-label' was recovered in the urine. Further analyses indicated that CAT was metabolized and excreted to a conjugated metabolite, since >90% of the 3H-label was released as authentic CAT after enzymatic digestion with B-glucu- ronidase and arylsulfatase. These studies, along with previous work with 14C-DTC, 14C-Nicotine, and 14C-BaP in cigarette smcke, point out the complex nature of cigarette smokd and the dive=s::v of the oossible biological responses to cigarette smoke expos:::e. D. CTR 128. Evaluation of Chromosomal Damace or Al_era=_on After Exnosure to Whole Cicare:te Smoke ';s:nc a Sister Chromatid Exchance SCE) assav (Dr. W. 3enedict a. introduction The sister chromatid exchange (SCE) assay measures the number of ti:;ies the genetic material of the chromosome is exchanged or recombined per metaphase chromosome. It has beer. suggested that human smokers have an increased number of SCS's ia-their blood lymphocytes compared to non-smokers (:opki^, :.u. and Evans, H.J., Nature 283, 388, 1980). Thus it was of in :.er- est to determine whether mice exposed to various doses of who:e cigaret _e smoke would also display arn inc: ease in SCE' s:n ei _::e= lymphocytes or bone marrow cells. In collaboration with :,r. W. 3enedic: (Children's Hospital of Los Angeles, Los AnceLes, CA), bone .;,a=row cells from :nice exposed to cigarette smoke are ::nde= evaluation for SCE. b. Results to date• Data reported previously (Progress Report, 198C) suc- ges _ed that the SCE rate was two fold higher in BC3Fli C:m Mice exposed to 3A1 cigarette smoke than sham exposed animals. These results have been confirmed, as shown in Table 38. BC3F1/C::m female mice were exposed to 10% 3A1 cigarette smoke using the continuous regimen for a period of 4 weeks. Mice were then shipped to Dr. Benedict and the SCE assay performed. The 3UdR pellets (required for differential staining of the chromosomes) were implanted -24 hours after the last smoke exposure. Experi- ments are in progress to determine whether exposure to 2R1 c::a- rette smoke results in a'similar SCE rate, and the mini:num expo- sure period required to observe this effect. /M( MCrObiOlOgiCal A&SOCiateS ---W~:. CTR MN 04448f` `

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