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Effect of Sapthaparna (Alstonia scholaris Linn) in modulatingthe benzo(a)pyrene-induced forestomach carcinogenesis in
mice
Ganesh Chandra Jagetia *, Manjeshwar Shrinath Baliga, Ponemone Venkatesh
Department of Radiobiology, Kasturba Medical College, Manipal 576119, Karnataka, India
Received 16 January 2003; received in revised form 2 April 2003; accepted 4 April 2003
Abstract
The chemopreventive effect of various doses of hydroalcoholic extract of Alstonia scholaris (ASE) was studied on the
benzo(a )pyrene (BaP) induced forestomach carcinoma in female mice. The treatment of mice with different doses, i.e. 1,
2 and 4 mg/ml ASE in drinking water before, during and after the treatment with carcinogen, exhibited
chemopreventive activity. The highest activity was observed for 4 mg/ml ASE, where the tumor incidence (93.33%)
was reduced by 6.67%. Similarly, the tumor multiplicity reduced (61.29%) significantly (P B/0.02) at 4 mg/ml in the
pre�/post-ASE treated group. However, the pre or post-treatment of mice with 4 mg/ml ASE did not show
chemopreventive activity. These findings are corroborated by micronucleus assay, where treatment of mice with ASE
before, during and after carcinogen treatment reduced the frequency of micronuclei (MN) in the splenocytes in a dose
dependent manner. The MN frequency reached a nadir at 4 mg/ml ASE, the highest drug dose which showed maximum
chemopreventive action. The ASE treatment not only reduced the frequency of splenocytes bearing one MN but also
cells bearing multiple MN indicating the efficacy of ASE in inhibiting mutagenic changes induced by BaP. The pre or
post-treatment of mice with 4 mg/ml ASE also significantly reduced the frequency of BaP-induced MN in the
splenocytes of treated animals.
# 2003 Elsevier Ireland Ltd. All rights reserved.
Keywords: Alstonia scholaris ; Carcinogenesis; Benzo(a )pyrene; Forestomach papillomas; Splenocytes; Micronuclei
1. Introduction
Environment pollutants are one of the main risk
factors for the induction of cancer that is con-
sidered as a major public health concern and
leading cause of death in both developing and
developed countries. These pollutants include
benzo(a )pyrene (BaP), which is a polycyclic aro-
matic hydrocarbon (PAH) formed by the pyrolytic
process during smoking of cigarettes and other
tobacco products as well as in combusted organic
matter in automobile exhaust. BaP is frequently
used as a representative indicator of total PAH
levels. It is a complete carcinogen, as it produces
* Corresponding author. Tel.: �/91-8252-57-1201x22814;
fax: �/91-8252-57-0062/1927.
E-mail address: [email protected] (G.C. Jagetia).
Toxicology Letters 144 (2003) 183�/193
www.elsevier.com/locate/toxlet
0378-4274/03/$ - see front matter # 2003 Elsevier Ireland Ltd. All rights reserved.
doi:10.1016/S0378-4274(03)00205-4
initiation and promotion of carcinogenesis (Halli-
well and Gutteridge, 1989).
Cancer chemoprevention is a mean of cancer
control by pharmacological intervention of the
occurrence of the disease using chemical com-
pounds. Recent events suggest that new emphasis
in the development of medical treatment of human
disease will be intimately connected to natural
products. The use of medicinal plants in modern
medicine for the prevention or treatment of cancer
is an important aspect. For this reason, it is
important to identify anti-tumor-promoting
agents present in medicinal plants commonly
used by the human population, which can inhibit
the progression of tumor.
Alstonia scholaris a tree belonging to the family
Apocynaceae, has been used since time immemor-
ial in the folklore and traditional systems of
medicine in India, to treat several diseases. The
ripe fruits of the plant are used in syphilis insanity
and epilepsy. It is also used as a tonic, antiperiodic
and anthelmintic. The milky juice of A. scholaris
has been applied to treat ulcers. The bark is the
most extensively used part of the plant and is used
in many compound herbal formulations (Nad-
karni, 1976). It is a bitter tonic, alternative and
febrifuge and is reported to be useful in the
treatment of malaria, diarrhea and dysentery
(Satyavati et al., 1987; Warrier et al., 1996;
CHEMEXCIL, 1992; Nadkarni, 1976). A. scho-
laris has also been reported to inhibit liver injuries
induced by carbon tetrachloride, beta-D-galacto-
samine, acetaminophen and ethanol (Lin et al.,
1996). The chief constituents of the bark of A.
scholaris are the alkaloids alstonidine, alstonine,
alstovenine, chlorogenic acid, chlorogenine, ditain,
ditaine, ditamine, echicaoutchin, echicerin, echir-
etin, echitamine, echitein, echitenin, echitin, por-
phyrine, porphyrosine, reserpine, venenatine,
villalstonine pleiocarpamine, O -methylmacralsto-
nine macralstonine O -acetylmacralstonine, villal-
stonine, macrocarpamine, corialstonine and
corialstonidine, and the triterpenoids lupeol linole-
ate, lupeol palmitate and alpha-amyrin linoleate
(Rastogi and Mehrotra, 1990; Gandhi and Vi-
nayak, 1990; Keawpradub et al., 1997, 1999; Rajic
et al., 2000).
As far as the authors are aware, the chemopre-ventive activity of A. scholaris has not been
eva1uated. Therefore, the present study was un-
dertaken to evaluate the chemopreventive activity
of A. scholaris in the mice against the BaP-induced
forestomach carcinoma in mice.
2. Materials and methods
2.1. Preparation of the extract
The identification of the plant A. scholaris R.
Br. (family Apocynaceae) was done by Dr G.K.
Bhat (a well known taxonomist of this area)
Department of Botany, Poorna Prajna College,
Udupi, India and the herbarium specimen hasbeen stored with us. The non-infected stem bark of
the tree was carefully peeled off, shade dried, and
coarsely powdered with the help of a hand club.
The plant material was then extracted with n -
hexane in a Soxhlet apparatus at 55 8C for ten
cycles and dried at 40 8C overnight. The hexane
free plant material was further extracted with 85%
ethyl alcohol in a Soxhlet apparatus extensively for3 days. The cooled liquid extract was concentrated
by evaporating its liquid contents, with an approx-
imate yield of 18%. Henceforth, the extract of A.
scholaris will be called as ASE.
2.2. Animal care and handling
The animal care and handling were done
according to the guidelines set by the WorldHealth Organization, Geneva, Switzerland and
the INSA (Indian National Science Academy,
New Delhi, India). Eight to ten-week-old female
Swiss albino mice weighing 24�/26 g were selected
from an inbred colony maintained under the
controlled conditions of temperature (239/2 8C),
humidity (509/5%) and light (14 and 10 h of light
and dark, respectively). The animals had freeaccess to the sterile water and food (cracked wheat
50%, bengal gram 40%, milk powder 4%, yeast
powder 4%, sesame oil 0.75%, cod liver oil 0.25%,
salt 1%). Four animals were housed in a poly-
propylene cage containing sterile paddy husk
(procured locally) as bedding throughout the
G.C. Jagetia et al. / Toxicology Letters 144 (2003) 183�/193184
experiment. The study was approved by theInstitutional Animal Ethical Committee.
2.3. Induction of BaP-induced forestomach
tumorigenesis
Benzo(a)pyrene [BaP, purity �/98% Cat no. B
1760] was procured from Sigma Chemical Com-
pany, St. Louis, MO, USA. The BaP-induced
forestomach tumorigenesis in mice was performedaccording to Wattenberg et al. (1980) with minor
modifications (Nagabhushan and Bhide, 1987).
The animals were administered with 100 ml sesame
oil or 1 mg of BaP in 100 ml sesame oil by p.o.
gavage twice a week for 4 weeks (a total of eight
administrations). The animals were sacrificed 14
weeks after the last administration of BaP.
2.4. Preparation of drug and mode of
administration
The drug was dissolved in double distilled water
(DDW) and filter sterilized. The sterile drug was
added to cooled autoclaved drinking water. The
drug/drinking water was replaced with fresh drug/
drinking water daily (every 24 h) in amber colored
bottles and the leftover was discarded.
2.5. Experimental
The female Swiss albino mice of 4�/5-week-old
were divided into the following groups.
2.5.1. STW alone
The animals of this group received sterile tap
water (STW) as drinking source throughout the
study period.
2.5.2. SMO alone
The animals of this group were injected with 100
ml of sesame oil (SMO) by oral gavage twice a
week for 4 consecutive weeks.
2.5.3. BaP alone
This group of animals was administered 1 mg of
BaP in 100 ml sesame oil by oral gavage twice a
week for 4 weeks.
2.5.4. ASE (pre�/post treatment)
The animals of this group received 1, 2 and 4
mg/ml of ASE as sole source of drinking water for
5 days a week, for 2 weeks before treatment with
BaP followed by the concomitant treatment with
ASE and BaP or STW for 4 weeks during and 2
weeks after the last dose of BaP or sesame oil.
Once the treatment was over, the mice were
provided with normal sterile drinking water forrest of the study period.
2.5.5. ASE (pre-treatment)
The animals of this group received 4 mg/ml of
ASE as sole source of drinking water for 5 days a
week, for 2 weeks. Forty-eight hours before the
first administration of BaP or sesame oil the ASEsource was withdrawn and the mice were provided
with normal drinking water for rest of the study
period.
2.5.6. ASE (post-treatment)
The animals of this group were provided with
normal drinking water during the carcinogen
treatment for 4 weeks. Forty-eight hours afterthe last administration of BaP or sesame oil, the
animals were administered 4 mg/ml ASE for 8
weeks as described above.
The body weights of the animals from each
group were recorded at the beginning of the
experiment and at the termination of the experi-
ment. The mice were sacrificed 14 weeks after the
last dose of BaP. Ten percent phosphate bufferedformalin was immediately injected into the sto-
mach, so that it would be distended and fixed. The
forestomach was cut open longitudinally and kept
in 10% buffered formalin for 24 h for fixation. The
stomach papillomas that were 1 mm or larger in
diameter were counted under a stereozoom micro-
scope (Leica Microsystems, GmbH, Wetzlar, Ger-
many). Formalin fixed forestomach was embeddedin paraffin wax and processed for histology. The
hematoxylin and eosin stained slides were scored
in blind fashion.
The chemopreventive tumor response was as-
sessed on the basis of tumor incidence, mean and
multiplicity of tumors as follows:
G.C. Jagetia et al. / Toxicology Letters 144 (2003) 183�/193 185
Tumor incidence
�Number of animals having tumors
Tumor Multiplicity
�Total number of tumors scored
Total number of animals with tumors
The tumor incidence and multiplicity were
compared between the animals fed with the BaP
and the ASE treatment groups. The statistical
significance in the alteration in the body weightsafter various treatments was determined using
Student’s t-test. The tumor incidence and multi-
plicity are expressed as the percentage of animals
with tumors and the analysis was carried out using
x2-test.
2.6. Splenocyte culture
The splenocytes were cultured as described by
Jagetia et al. (2001). Briefly, five animals from
each group were killed by cervical dislocation at
the end of the experiment and thoroughly wiped
with 70% ethanol and their abdominal cavity
opened with the help of sterile scissors and forceps
in an aseptic environment. The spleens of theanimals were removed aseptically and washed in
the sterile phosphate buffered saline (PBS). The
splenocytes were isolated and cultured in RPMI-
1640 medium containing 10% fetal calf serum
(FCS) and concanavalin-A as mitogen. The sple-
nocytes were incubated at 37 8C and allowed to
grow for 72 h. Duplicate cultures were set up for
each animal for each drug dose.The micronuclei (MN) were prepared according
to the method of Fenech and Morley (1985) with
minor modifications. Briefly, 40 h after the initia-
tion of the splenocyte culture, 3 mg/ml of cytocha-
lasin-B was added to the cultures. The cells were
allowed to grow for another 32 h. The splenocytes
were centrifuged, subjected to mild hypotonic
treatment (0.7% ammonium oxalate) so as to
retain the cytoplasm and fixed in Carnoy’s fixative
(3:1 methanol, acetic acid). The cells were centri-
fuged again and resuspended in a small volume offixative and dropped on to precleaned coded slides
to avoid observer’s bias.
Cells were stained with 0.125% acridine orange
(BDH, England, Gurr Cat. No. 34001 9704640E)
in Sorensen’s buffer (pH 6.8). The slides were
washed twice in Sorensen’s buffer and observed
under a fluorescent microscope, equipped with
450�/490 nm BP filter set with excitation at 453 nm(Carl Zeiss Photomicroscope III, Germany), using
a 40�/ Neofluar objective. A minimum of 2000
(1000 per culture) binucleate cells (BNC) with
well-preserved cytoplasm was scored from each
animal for each drug dose for the presence of MN
and the frequency of micronucleated binucleate
splenocytes (MNBNC) was determined. A mini-
mum of four animals was used for each drug dose.The MN identification was done according to the
criteria of Countryman and Heddle (1976) and
Krisch-Volders et al. (2000). The statistical sig-
nificance was determined using one way analysis
of variance (ANOVA) with the application of
Bonferroni’s Post-hoc test.
3. Results
3.1. Forestomach carcinogenesis
Female Swiss albino mice were administeredBaP by oral gavage, twice a week for 4 weeks (a
total dose of 8 mg of the carcinogen), so as to
ensure a high incidence as well as high yield of
forestomach tumors per animal. Simultaneously,
the animals were provided with either sterile
drinking water or ASE dissolved in drinking water
Mean�Lowest number of tumors � Highest number of tumors
2
G.C. Jagetia et al. / Toxicology Letters 144 (2003) 183�/193186
to determine their ability to counteract the actionof the carcinogen.
The chemopreventive effect of ASE on the BaP-
induced forestomach papillomas in mice is pre-
sented in Table 1. The administration of 1.0 mg
BaP by oral gavage twice a week for 4 weeks
resulted in 100% incidence of forestomach tumors
with a mean of seven tumors per mouse, which
were histologically considered to be papillomas, asagainst no tumors seen in the SMO, ASE and
STW treated control (without BaP) animals.
The treatment of mice with 1, 2 and 4 mg/ml
ASE as sole source of drinking water for 2 weeks
before, during and 2 weeks after the last dose of
BaP in the pre�/post treatment group brought
about 21.43, 28.57 and 50% reduction in the tumor
multiplicity (Table 1). The reduction in the tumorincidence was observed only in the 4 mg group,
where a reduction of 6.67% was observed.
When 4 mg/ml ASE was given to mice as sole
source of drinking water during the post-initiation
period, starting at 48 h after the last dose of BaP
(post-treatment) and continued for 8 weeks the
tumor multiplicity incidence reduced significantly
(91.93%) when compared with the BaP treated(100%) animals (Table 2). However, the tumor
incidence remained unaltered (100%). The overall
tumor multiplicity was higher in the animals that
were treated with 4 mg/ml of ASE during the post-
treatment (92.85%) than in the pre�/post treatment
group (50%) and was 1.86-fold greater whencompared with the pre�/post treatment group.
Pretreatment of mice with 4 mg/ml of ASE did
not significantly alter the tumor multiplicity and
tumor incidence when compared with the non-
drug treated control.
3.2. Micronucleus assay
The treatment of mice with oil or various doses
of ASE did not significantly alter the frequency of
MNBNC, while treatment of mice with 8 mg of
BaP for the induction of forestomach carcinoma
resulted in 4.75-fold elevation in the frequency of
MNBNC, when compared with spontaneous fre-
quencies (Table 3). The animals that were treated
with different doses of ASE before and after thetreatment of carcinogen exhibited a dose depen-
dent decline in the frequency of MNBNC when
compared with the BaP treated animals, and the
lowest frequency was observed for 4 mg/ml ASE
(Table 3). The treatment of mice with BaP also
induced cells bearing two and three MN, which
were significantly higher than the oil treated
group, while the treatment of mice with differentdoses of ASE before and after BaP treatment
significantly reduced the frequency of MNBNCs
with two and three MN when compared with BaP
alone (Table 3). This reduction was 2 and 6.5-folds
for MNBNC with two and three MN, respectively,
Table 1
Chemopreventive effect of various doses of ASE in the BaP-induced forestomach carcinogenesis in mice
Drug dose (mg/ml) Carcinogen (8 mg) Tumor incidence Mean number Tumor multiplicity Mean body weight (g)
Initial weight Final weight
ASE 0 pre�/post DDW 0 (0/5) �/ �/ 22.119/0.85 32.129/0.92
ASE 0 pre�/post Oil only 0 (0/5) �/ �/ 21.949/0.92 32.259/0.87
ASE 1 pre�/post Oil only 0 (0/5) �/ �/ 22.369/0.69 33.369/0.84
ASE 2 pre�/post Oil only 0 (0/5) �/ �/ 22.819/0.86 33.789/0.68
ASE 4 pre�/post Oil only 0 (0/5) �/ �/ 22.679/0.84 34.219/0.98
ASE 0 pre�/post Oil�/BaP 100 (20/20) 7.0 (100) 6.2 (100) 22.459/0.56 28.869/1.36
ASE 1 pre�/post Oil�/BaP 100 (15/15) 5.5 (78.57)d 5.6 (90.32)d 22.329/0.75 29.489/1.18a
ASE 2 pre�/post Oil�/BaP 100 (15/15) 5.0 (71.43)d 5.2 (83.87)d 22.299/0.68 30.239/1.21b
ASE 4 pre�/post Oil�/BaP 93.33 (14/15)d 3.5 (50)b 3.8 (61.29)b 22.189/0.83 31.759/1.11c
BaP, Benzo(a )pyrene; ASE, A. scholaris extract; a, P B/0.01; b, P B/0.02; c, P B/0.001; d, non significant (comparisons done with
BaP treated group). Number in parentheses in column 3 indicates number of animals with tumor/total number of animals used, while
in column 4 and 5 denotes percent decrease in the occurrence of tumors when compared with the concurrent BaP alone group.
G.C. Jagetia et al. / Toxicology Letters 144 (2003) 183�/193 187
after 4 mg/ml ASE pre- and post-treatment. The
decline in MNBNC with two and three MN was
dose dependent. The higher was the dose the
greater was the decline.
The frequency of MNBNC exhibited a signifi-cant decline in the mice treated with 4 mg/ml ASE
either before or after BaP treatment. The frequen-
cies of MNBNC bearing two MN was significantly
lower in the animals treated with the 4 mg/ml ASE
either before or after BaP administration (Table
3). This decline in the MNBNC bearing two MN
was approximately 2-folds in the post-treatment
group, when compared with the BaP alone treatedgroup (Table 3).
4. Discussion
The most promising approach to reduce the
number of cancer cases worldwide may be to
inhibit the occurrence of cancer by pharmacologi-
cal intervention, i.e. chemoprevention. This can be
achieved by the use of certain chemicals or non-nutrient dietary constituents. Chemoprevention,
therefore, is the means of cancer control in which
the occurrence of disease, as a consequence of
exposure to carcinogens, can be slowed, blocked,
or reversed by the administration of one or more
naturally occurring or synthetic compounds (Wat-
tenberg, 1990; Kelloff et al., 1994; Morse and
Stoner, 1993; Stoner and Mukhtar, 1995). Che-
moprevention also deals with the chemotherapy of
precancerous lesions, which are called preinvasive
neoplasia, dysplasia, or intraepithelial neoplasia,
depending on the organ system (Kelloff et al.,
1994). Chemopreventive agents can be targeted by
intervention at the initiation, promotion, or pro-
gression stage of multistage carcinogenesis (Wat-
tenberg, 1990; Kelloff et al., 1994; Morse and
Stoner, 1993; Stoner and Mukhtar, 1995). The
intervention of cancer at the promotion stage,
however, seems to be the most appropriate and
practical. The major reason for that relates to the
fact that tumor promotion is reversible event at
least in early stages and requires repeated and
prolonged exposure of a promoting agent (DiGio-
vanni, 1992).
The administration of the carcinogen BaP
caused 100% incidence of forestomach tumors,
while the oil treatment did not induce any tumors
in the recipient animals. The tumor multiplicity in
the BaP alone group was also high (6.24). A
similar effect of BaP in tumor induction has been
reported earlier (Wattenberg et al., 1980; Nagab-
hushan and Bhide, 1987; Azuine and Bhide, 1992;
Deshpande et al., 1997; Agha et al., 2001). The
administration of ASE as sole source of drinking
water before, during and after the carcinogen
Table 2
Effect of different administration schedules on the chemopreventive activity of 4 mg/ml ASE in the BaP-induced forestomach
carcinoma in mice
Drug dose (mg/ml) Carcinogen (8 mg) Tumor incidence Mean number Tumor multiplicity Mean body weight (g)
Initial weight Final weight
ASE 0 pre�/post DDW 0 (0/5) �/ �/ 22.119/0.85 32.129/0.92
ASE 0 pre�/post Oil only 0 (0/5) �/ �/ 21.949/0.92 32.259/0.87
ASE 0 pre�/post Oil�/BaP 100 (20/20) 7.0 (100) 6.2 (100) 22.459/0.56 28.869/1.36
ASE 4 pre only Oil only 0 (0/5) �/ �/ 22.679/0.84 32.219/0.98
ASE 4 pre only Oil�/BaP 100 (15/15) 6.5 (92.85)d 6.1 (98.38)d 22.639/0.92 30.419/1.08b
ASE 4 post only Oil only 0 (0/5) �/ �/ 22.079/0.84 31.989/0.98
ASE 4 post only Oil�/BaP 100 (15/15) 6.5 (92.85)d 5.7 (91.93)d 22.239/0.92 30.749/1.08c
ASE 4 pre�/post Oil only 0 (5/5) �/ �/ 22.679/0.84 34.219/0.98
ASE 4 pre�/post Oil�/BaP 93.33 (14/15)d 3.5 (50)b 3.8 (61.29)b 22.189/0.83 31.759/1.11c
a, P B/0.01; b, P B/0.02; c, P B/0.001; d, non significant (comparisons done with BaP treated group). Number in parentheses in
column 3 indicates number of animals with tumor/total number of animals used, while in column 4 and 5 denotes percent decrease in
the occurrence of tumors when compared with the concurrent BaP alone group.
G.C. Jagetia et al. / Toxicology Letters 144 (2003) 183�/193188
treatment suppressed the BaP-induced foresto-
mach tumorigenesis. There was a dose dependent
decrease in the multiplicity of the tumors and the
highest effect was observed for 4 mg/ml ASE,
where the occurrence was lesser than the other two
doses. As far as the authors are aware this is the
first report on the alterations in the chemically-
induced carcinogenesis by ASE.
The second aspect of the study was to ascertain
whether delay in the administration of 4 mg/ml of
ASE, i.e. starting from 48 h after the last dose of
BaP for 8 weeks will also be effective in inhibiting
the formation of multiple gastric tumors induced
by the carcinogen. Our findings indicate that the
ASE can also act at this stage and has been able to
counteract the tumorigenesis as evident by the
reduced multiplicity (5.78) of the tumor when
compared with the BaP alone group (6.24). Inspite
of this reduced multiplicity, the post-treatment of
ASE was not as effective as the pre�/post-treat-
ment regimen. A similar observation has been
reported for the turmeric and its extracts (Desh-
pande et al., 1997).
We were also interested to know whether the
administration of 4 mg/ml of ASE when adminis-
tered continuously for 2 weeks before the admin-
istration of BaP will also inhibit the BaP-induced
tumorigenesis? Our results show that the drug was
ineffective with this schedule and the tumor
incidence remained unaltered. However, the tumor
multiplicity was marginally reduced to 6.13 when
compared with BaP alone group (6.24). This
regime was ineffective when compared with the
pre�/post and post-treatment regimen.These results are supported by the studies on the
micronucleus-induction, which is an index of
DNA damage. The frequency of MN increased
4-folds in the splenocytes of animals treated with
BaP for forestomach carcinogenesis. BaP has been
observed to be an inducer of MN in the spleen
(Benning et al., 1994; Winker et al., 1995; Dertin-
ger et al., 2001). While the treatment of mice with
different doses of ASE before and after signifi-
cantly reduced the frequency of MN, indicating
reduction in the BaP-induced DNA damage. This
may be one of the reasons for the decline in tumor
incidence in pre- and post-ASE treated group.Ta
ble
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/2.5
41
73
.489
/2.8
a
Po
st4
41
.339
/2.7
61
32
.169
/3.9
4f
9.6
69
/0.6
12
0.1
69
/1.9
9e
2.6
69
/0.3
36
.839
/1.8
3b
53
.669
/2.8
51
59
.59
/4.0
2e
Ba
P,
Ben
zo(a
)py
ren
e;A
SE
,A
.sc
hola
ris
extr
act
;S
T,
sham
trea
tmen
t;M
NB
NC
,m
icro
nu
clei
inb
inu
clea
tece
lls;
a,
PB
/0.0
1;
b,
PB
/0.0
2;
c,PB
/0.0
01
;d
,PB
/0.0
001
;e,
PB
/0.0
000
1;
f,n
on
-sig
nif
ica
nt
(wh
enco
mp
are
dw
ith
BaP
alo
ne
trea
tmen
t).
G.C. Jagetia et al. / Toxicology Letters 144 (2003) 183�/193 189
The formation of DNA adducts inflicts loss of
nuclear functioning that leads to mutations and
chromosome aberrations. The mutational events
and chromosomal instability are key steps in
carcinogenesis and many types of cancer have
been associated with the chromosomal aberrations
(Heim and Mitelman, 1987; Heim et al., 1989).
Damage to the chromosomes is expressed as
breaks and fragments which, appear as MN in
the proliferating cells (Heddle and Harris, 1975).
The chromatid breaks and exchanges that lead to
chromosome anomalies, must occur during carci-
nogenesis to attain the neoplastic property. The
tumor cell population is composed of one or few
clones of cells with particular chromosome anoma-
lies and this phenomenon is detectable by an
increased frequency of MN in the proliferating
cells (Countryman and Heddle, 1976; Heim and
Mitelman, 1989). The cell proliferation also allows
endogenous adducts to be converted into muta-
tions and makes more sensitive single-stranded
DNA target for carcinogenesis. Therefore, the
evaluation of MN gives an indication on the
quantitative aspect on the insult to the cellular
DNA. In chronic administration studies, it is
always desirable to study the MN formation in
the spleen, because the irreparable damage to the
cellular DNA gets accumulated, which becomes
manifest when the splenocytes are stimulated to
divide. BaP has been reported to be immunotoxic
and has profound inhibitory effect on the spleen
(Ginsberg et al., 1989; Zhao, 1990). Earlier reports
indicate that the BaP treatment resulted in an
increase in the BaP�/DNA adduct formation and
frequency of mutation in the spleen cells (Benning
et al., 1994; Winker et al., 1995; Dertinger et al.,
2001).The exact mechanism of the chemopreventive
effect of ASE is not known. However, the opera-
tions of these mechanisms cannot be ruled out.
Alterations in the native DNA play an impor-
tant and crucial role in carcinogenesis. The neo-
plastic cells contain high frequencies of
chromosomal aberrations. The treatment of mice
with ASE may have reduced the DNA damage as
evident by a significant reduction in the frequency
of MN. Therefore, protection against the DNA
damage by ASE during tumorigenesis may be oneof the reasons for lesser frequency of tumors.
In this study we have observed that the chemo-
preventive effect was the best when ASE is
administered during and after (pre�/post) the BaP
treatment and this effect may be because of the
involvement of the Phase I and Phase II metabo-
lizing enzymes. A. scholaris has been reported to
inhibit the liver injuries induced by carbon tetra-chloride, beta-D-galactosamine, acetaminophen
and ethanol in mice and rats (Lin et al., 1996).
These agents like BaP are all activated to reactive
forms by the cytochrome P450 (Mehendale, 1995;
Ray and Mehendale, 1990; Thapliyal and Maru,
2001) and the efficacy of ASE in inhibiting the
damage induced by these agents strongly suggests
that the ASE may have down regulated orinhibited the action of cytochrome P450 and
thereby reducing the occurrence of BaP-induced
tumors in the present study.
In our earlier study we have observed that the
ASE was highly effective as a nitric oxide (NO)
scavenger (data not shown). This activity of ASE
may also have been responsible for the chemopre-
ventive activity. A medline study also shows thatthe BaP induces synthesis of NO and its progeni-
tors in vitro and in vivo (Garcon et al., 2001;
Takabe et al., 2001) and the compounds that are
inhibitors like Ginkgo biloba , curcumin, triterpe-
noids, resveratrol, nimesulide, L-nitroarginine
methyl ester and sulforaphane have been observed
to be chemopreventive in different study systems
(Li and Lin-Shia, 2001; Suh et al., 1998; Rao et al.,1999; Lin and Tsai, 1999; Watanabe et al., 2000;
Sharma et al., 2002; Kawamori et al., 2000; Heiss
et al., 2001; Agha et al., 2001).
The ASE contains triterpenoids (Lupeol linole-
ate, lupeol palmitate and alpha-amyrin linoleate) a
class of compounds reported to inhibit the serine
proteases and PKA (Rajic et al., 2000). The
protease inhibitors have been reported to inhibitcarcinogenesis in different study systems and their
mechanism of action is postulated to be due to
suppression of the neoplastic cells and tumor
promotion (Tanaka, 1994). The presence of triter-
penoids in the ASE may also have contributed to
its chemopreventive property. This contention is
supported by earlier observations, where triterpe-
G.C. Jagetia et al. / Toxicology Letters 144 (2003) 183�/193190
noids tubeimoside, abieslactone, 3beta-cis -p -cou-maroyloxy-2alpha, tubeimosides and 23-dihydrox-
yolean-12-en-28-oic acid have been reported to be
chemopreventive in different study systems (Yu et
al., 1992; Suh et al., 1999; Yu et al., 2001; Gu et al.,
2001; Iwai et al., 2001).
The immune system plays an important role in
the maintenance of health. The basic concept of
immunoserveillance is that the development ofcancer cells in the organism stimulates a potent
immune response that locates the cancer cells and
destroys them (Shklar, 1998). A. scholaris has
recently been reported to possess immunostimula-
tory effect and also to enhance the phagocytic
activity in normal as well as in the immunosup-
pressed mice (Iwo et al., 2000). Therefore, the
immunomodulation may also have played somerole in the observed chemopreventive activity of
ASE.
Alstonia has been reported to possess alkaloid
echitamine, which has been reported to be selec-
tively cytotoxic to the tumor cells (fibrosarcoma
and in sarcoma-180), while it had no effect on the
normal cells (Kamarajan et al., 1995; Saraswathi et
al., 1997). Echtamine is also present in the extract(since it is isolated from the ethanolic extract), and
may have inhibited the tumor growth by selec-
tively killing the aberrant cells. Further, the drug
comes in direct contact with the target site of
tumorigenesis so a similar action of ASE in the
present study may not be ruled out. The studies are
underway to identify the active component(s)
responsible for the chemoprotective propertieswith emphasis on the study of their mechanism(s)
of action.
Acknowledgements
We would like to thank Dr G.B. Maru, Head
Tobacco Carcinogenesis Division, Cancer Re-
search Institute, ACTREC, Tata memorial Centre,Kharghar, Mumbai, India for his constant support
and guidance throughout the study. The authors
wish to thank Professor Gopalkrishna Bhat,
Poorna Prajna College Udupi, Karnataka, for
identifying the plant material. The financial assis-
tance in the form of a Senior Research Fellowship
to M.S. Baliga by the Indian Council for MedicalResearch, Government of India, New Delhi, India
to carry out this study is thankfully acknowledged.
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