Preliminary Toxicity Evaluation of Bidens pilosa Extracts
Using Experimental Mice
S. Parimalakrishnan1*, V.D. Sundar2,
I. Ulaganathan2,
S. Nandhakumar2 and Akalanka Dey1
1Annamalai University, Annamalai Nagar-608002, TamilNadu, India
2GIET School of Pharmacy, Rajahmundry, AP, India
ABSTRACT:
The
present study was carried out to evaluate acute and sub-acute toxicity in mice
(Swiss albino mice). In acute toxicity
study, the test material of methanolic extract of B. pilosa (MEBP) (Asteraceae)
was administered orally at dose levels 3, 3.5, 4, 4.5, 5 and 5.5 g/kg, b.wt are observed. The mortality signs behavior using
Finley’s probit analysis LD50 dose was
calculated as 4.5 g/kg b.wt. In the sub-acute
toxicity study, methanolic and petroleum ether
extracts of B. pilosa
(MEBP and PEBP) were administered at dose levels of 200 and 400 mg/kg b.wt, p.o., once a day for 28
days. All the animals were sacrificed on 29th day and blood was
collected and various hematological parameters such as total count of RBC, WBC,
DLC and Hb content were monitored and serum protein
levels evaluated. Histopathological evidence of the
viscera showed congestion and focal necrosis of the liver and renal tubules. It
is apparent from the results that the MEBP is safe; however the depression in respiration mechanism that
lead to the death of the mice needs to be investigated further.
KEYWORDS: Acute, Sub-acute
toxicity, hematological parameters
INTRODUCTION:
Safety pharmacology is a
step ahead than toxicological evaluation because ethics plays an important role
in animal studies and human clinical trials. Therefore safety pharmacology is
implemented animal screening stages. Traditional or folk healing herbal
medicines are used approximately by 60% of the world population both in the
developing and developed countries. The herbal recipes are prepared most often
from a combination of two or more plant products which may contain active
constituents with multiple physiological and biochemical activities and could
be used in the treatment of a various diseases1. They are
administered in most disease conditions over a period of time without proper
dosage monitoring and consideration of toxic effects that might result from
such prolonged usage of drugs.
Bidens pilosa (Family - Asteraceae)
is found in waste lands throughout India. It was been already investigated
because of its wide range of medicinal applications. Its leaves are used as
treatment for rheumatism, sore eyes, abdominal troubles, ulcers swollen glands
and toothaches2, cancer, cough3. It is commonly used for
inflammatory, diuretic, jaundice, conjunctivitis, abscesses, mycosis and
urinary infections and stimulates childbirth4. Emollient,
astringent, fever, malaria, leucorrhea, diabetes, sore throat, tonsillitis and
vaginal infections also treated. Apart from this plant is applied externally
for fungal infections, ulcers, diaper rash, insect bites, and hemorrhoids5.
The scope of the present
study was to evaluate the safety profile of entire plant extract of Bidens pilosa by
carrying out the acute and sub acute toxicity
study in experimental mice for 28 consecutive days. The sub
acute toxicity evaluation is required to establish the potential adverse
effects of this valuable herbal medicine used for this study.
MATERIALS
AND METHODS:
Plant collection and Preparation of Modulator:
The
entire plant of Bidens pilosa was
collected from Sengottai of Tirunelveli
(Dist) Tamil Nadu, India. The plant material was taxonomically identified and
authenticated by the Department of Botany, Annamalai
University, Annamalai Nagar,
India. The samples were cleaned, dried under shade, powdered by a mechanical
grinder and stored in an airtight container. Methanol and petroleum ether was
used as solvent in the extraction process and extracts were prepared by using soxhlet apparatus. The percentage of yield in methanolic and petroleum ether extract was found to be
6.46% w/w and 7.57% w/w.
Animals:
Both
the sexes of mice (8 weeks old) weighing 25-30 g were procured from the central
animal house of the institute. They were kept in standard polypropylene cages
maintained under standard room temperature (22 ± 2°C; relative humidity 60-70%)
in 12 hr. The animals were fed with standard pellet diet and water ad libitum.
All animals and experimental design was approved by the Institutional Animal
Ethical Committee (IAEC) [Register No: 160/1999/CPCSEA & Proposal No: 241].
Phytochemical Studies:
The MEBP and PEBP were subjected to preliminary phytochemical
screening for various plant constituents6, 7.
Acute toxicity studies:
Swiss
albino mice of either sex with the body weights ranging from 18-30g were
selected. Since the compound was insoluble in water, it was mixed evenly in 4 %
v/v Tween 80 solution and administered orally in the doses of 3.0, 3.5, 4.0, 4.5, 5.0 and 5.5 g/kg in different group
(2, 3, 4, 5, 6 and 7) containing three mice each. Group 1 was treated with the
vehicle, served as solvent control. Observations for toxic symptoms and
mortality were observed up to 72 hours. Clinical signs of toxicity as excitation, tremors, and twitches,
motor coordination, righting reflex and respiratory changes also monitored8.
Sub acute toxicity
studies:
Thirty mice of average range
between 26-30g were acclimatized for a week in cleaned cages and randomly
divided into five groups of six animals each. Group I solvent control, Group II
and III were administered MEBP (200 and 400 mg/kg, b.wt,
p.o) Group IV and V animals were administered PEBP
(200 and 400 mg/kg, b.wt, p.o).
Before administration of 1st
dose animals were fasted overnight. All the drugs were administered once a day
for 28 days. Body weight and food intake were monitored at the end of every
week throughout the duration of study9. All the animals were
sacrificed on the day 29, blood sample were collected from abdominal aorta and
frozen in polypropylene tube for evaluating haematological
parameters like haemoglobin (Hb),
white blood cells count (WBC), red blood cells count (RBC), packed cell volume
(PCV) and differential leucocytes count (DLC)10-12. Total protein13
was additionally evaluated.
Histopathological study:
Liver, kidney and small intestine of sacrificed
animals were cut in to small pieces were collected and immediately fixed in 10%
formalin buffered saline, dehydrated in ethanol, cleared in xylene
and embedded in paraffin. Sections 4-5mm
thick were prepared and then stained with hematoxylin
and eosin (H and E) dye for photo microscopic observation.
Statistical analysis:
Results were expressed as
mean ± standard error of mean (SEM). Statistical significance was determined by
one-way analysis of variance (ANOVA) and post hoc least-significant difference
(LSD) test. The data obtained from acute toxicity studies was analyzed using
Student's paired t-test. p<0.05 were considered significant.
RESULTS:
The preliminary phytochemical evaluation showed the entire plants of B. pilosa are rich in Flavonoids
and terpenes. Results are shown in Table 1.
Preliminary chemical investigation of the MEBP showed the presence of
alkaloids, carbohydrates, fixed oils and fats, tannins and phenolic
compounds, whereas the PEBP showed the presence of carbohydrates, fixed oils
and fats, tannins and phenolic compounds, flavonoids and terpenes.
Mortality determination for LD50 estimation:
In acute toxicity study,
MEBP result exhibited 100% death for all the animals that received 5.5 g/kg b.wt of the extract while 10, 40, 70 and 90% deaths were
recorded for the animals that received 3.5, 4.0, 4.5 and 5.0 g/kg b.wt of the extract, respectively. There was no death in
animals administered doses up to 3.0 g/kg b.wt. LD50
of the MEBP was found to be 3.5 g/kg b.wt. PEBP
extract result showed 100% death for all the animals that received 5.5 g/kg b.wt of the extract while 30, 60 and 80% deaths were
recorded for the animals that received 4.0, 4.5 and 5.0 g/kg b.wt of the extract, respectively. There was no death in
the animals that received 3.0 and 3.5 g/kg b.wt. LD50
of the PEBP was calculated to be 4 g/kg b.wt. Results
are shown in Table 2.
Clinical signs of toxicity
observed in all the cases include initial excitement, restlessness, and
difficulty in breathing, loss of appetite, general weakness and depression
which was seen as the doses increased. There were variable changes in the body
weight of the animals in all the treated groups. The Group I gained body weight
during the period of experiment, while the treated Group (II, III, IV and V)
showed significant reduction (p<0.05) in body weight when compared with
Group I (data not shown).
Table
1. Preliminary phytochemical evaluation of MEBP and PEBP
|
Name of chemical tests |
MEBP |
PEBP |
|
Test for Alkaloids |
+ |
- |
|
Test for Carbohydrates |
+ |
+ |
|
Test for Glycosides |
- |
- |
|
Test for Phytcosterols |
- |
- |
|
Test for fixed oils and fats |
+ |
+ |
|
Test for saponins |
- |
- |
|
Test for tannins and phenolic
comounds |
+ |
+ |
|
Test for proteins and free amino acids |
- |
- |
|
Test for Flavanoids |
- |
+ |
|
Test for Liginin |
- |
- |
|
Test for Terpenes |
- |
+ |
+ indicates presence and -
indicates absence
Table
2. Methods of determination
of LD50 dose
of MEBP and PEBP
|
Group |
Number of mice |
MEBP |
PEBP |
||
|
No of death |
% mortality |
No of death |
% mortality |
||
|
1 |
10 |
0 |
0 |
0 |
0 |
|
2 |
10 |
0 |
0 |
0 |
0 |
|
3 |
10 |
1 |
10 |
0 |
0 |
|
4 |
10 |
4 |
40 |
3 |
30 |
|
5 |
10 |
7 |
70 |
6 |
60 |
|
6 |
10 |
9 |
90 |
8 |
80 |
|
7 |
10 |
10 |
100 |
10 |
100 |
The relative weights of the
organs (liver, kidney and intestine) were not significantly different from the
Group I. However, the lungs of the group treated at 3.0 g/kg, b.wt were significantly different (p<0.05) (data not
shown). Histopathological changes were not observed
in any of the organs except congestion in the lungs. Histopathological
examination of the organs did not reveal any abnormalities.
The PCV, DLC (Lymphocytes, Monocytes and neutrophils), Hb, TRBC, TLC and total plasma protein were significantly
(p<0.001) reduced when compared with Group I. However, the white blood cell
and total plasma protein of group treated with 400 mg/kg body weight showed
decreased values. Results were shown in Table 3.
DISCUSSION:
Herbal medicines have
received greater attention as an alternative to clinical therapy leading to
increasing demand14. The exclusive use of herbal remedies are
formulated and distributed by unqualified trained herbalists, for treatment of
certain changes in physiological and pathological conditions is very common in
all over world. Experimental screening method is important in order to
ascertain the safety of herbal products as well as to establish the bioactive
component of these herbal medicines.
The extracts of B. pilosa showed the presence of flavanoids,
alkaloids, carbohydrates, fixed oils and fats, tannins and phenolic
compounds and terpenes. The safety pharmacology of
MEBP and PEBP were monitored as safety dose administration to animals.
In the present acute toxicity study was revealed that LD50 levels
of MEBP and PEBP were high and apparently showed the safety of those extracts.
The zero percent mortality for MEBP and PEBP of both extracts were found in
Group III and IV respectively. The animals were observed continuously for 4 hr
at first, then at an interval of two hours up to 24 hrs to examine any change
in the mice behaviour, lacrimation,
respiration, writhing, CNS stimulation or depression, fighting, aggressiveness,
reflexes, muscle weakness, salivation, nasal secretion and congestion, diarrhoea, skin eruption, food and water intake and
mortality. The causes of death may be due to pulmonary congestion and edema,
mild hydrothorax or intestinal hemorrhage.
In this current study of
acute toxicity of the extract, there were no changes in behavior, sensory
nervous system responses and gastrointestinal effects were observed in the
experimental animals. All the mice were administered the extracts in a group
wise survived beyond the 24 h of observation. The LD50 of the
extracts must be above 3.5 g/Kg b.wt9, 15. The extract can be
classified as non-toxic, since the LD50 was found to be more than
3.5 g/Kg b.wt.
Acute toxicity studies
of B. pilosa were screened through the oral
administration of a single dose of a substance or multiple doses given within
24 hrs15,16. The zero percent mortality for
MEBP and PEBP were found to be 3 g/kg b.wt and 4.5
g/kg b.wt respectively. Optimally, studies were terminated
when animals exhibited clinical signs and symptoms of toxicity. Such endpoints
are generally death or morbidity of animals, since they minimize pain and
distress17.
The results showed that
lower concentrations of both extracts did not show any significant difference
than higher concentration with respect to RBC, hemoglobin and hematocrit parameters. Administration of 400 mg/kg b.wt led to a significant increase in hemoglobin when
compared to that of the control group. In the groups treated with the MEBP of
the plants, the hemoglobin concentrations significantly increased, but red
blood cells decreased. These changes were not seen in the PEBP treated animals.
In mice treated with 400 mg/kg b.wt of MEBP,
lymphocytes and eosinophils were significantly
decreased and neutrophils are increased when compared
with Group I. However, such changes of these values were minor, and most
importantly the alteration of hematological and white blood cell count values
were insignificant and remained within the normal range18.
The double dose elevations
in TLC could be an attestation of the fact that MEBP and PEBP may contain
biologically active principles has found to be the ability to stimulate the
immune system through increasing numbers of defensive leucocytes in blood.
Lymphocyte count was Reduced and compensated by increased in neutrophils count was suggested that MEBP and PEBP may
possess anti-lymphocytic activity19.
Table 3: Hematological parameters and total protein
levels of entire plant extracts of MEBP and PEBP
|
Group |
Hemoglobin (g %) |
RBC (millions cells/mm3) |
WBC (thousands cells/mm3) |
Packed Cell Volume (pg) |
Differential leucocytes count (%) |
Total protein (mg/dl) |
||
|
Lymph ocytes |
Neutr ophils |
Mono cytes |
||||||
|
I |
14.97 ± 0.12 |
6.84 ± 0.19 |
10.23 ± 0.26 |
20.46 ± 0.22 |
80.61 ± 0.17 |
35.49 ± 0.24 |
4.78 ± 0.1 |
8.15 ± 0.23 |
|
II |
11.28 ± 0.20*** |
3.49 ± 0.30*** |
7.52 ± 0.35** |
12.34 ± 0.70** |
55.13 ± 0.51*** |
30.29 ± 0.20** |
2.71 ± 0.5** |
5.98 ± 0.64*** |
|
III |
13.32 ± 0.52** |
4.44 ± 0.36** |
8.42 ± 0.31** |
17.29 ± 0.46** |
65.26 ± 0.30*** |
36.08 ± 0.23* |
1.75 ± 0.2*** |
7.19 ± 0.44* |
|
IV |
10.43 ± 0.26*** |
2.42 ± 0.20*** |
5.97 ± 0.69*** |
14.73 ± 0.21*** |
41.14 ± 0.60*** |
15.48 ± 0.31*** |
4.08 ± 0.4* |
5.29 ± 0.96*** |
|
V |
12.37 ± 0.25** |
3.38 ± 0.28*** |
7.62 ± 0.33** |
15.43 ± 0.41*** |
75.58 ± 0.34** |
23.40 ± 0.23*** |
2.22 ± 0.5** |
6.65 ± 0.49** |
Comparisons
were made between: Group I vs. II, II, III, IV and V, Data are expressed as
mean ± SEM of 6
animals in each group.
Symbols represent statistical significance: *p<0.05, **p<0.01 and ***p<0.001.
There were no significant
changes in the hematological parameters between the control and extracts
treated mice at a dose of 400 mg/kg b.wt, suggesting
that the MEBP treated mice even at a dose of 400 mg/kg b.wt
may not be toxic as they do not affect the circulating red cells, nor the haemopoiesis and leucopoiesis that could otherwise have
caused a megaloblastic anemia, nor changes in PCV and
eosinophils. Plasma levels of total proteins were not
affected when MEBP administered orally at a dose of 400 mg/kg b.wt. All values were found to be within the normal range
for mice and there were no significance between the groups. The above finding
indicates that the normal metabolism of the animals was not affected20.
The biochemical markers
are the index of kidney and liver function21,22.
It is found that the MEBP the plant did not induce toxicity in the internal
organs such as kidneys and liver. To conclude, oral treatment of MEBP entire
plants did not cause acute toxicity in mice.
In the acute toxicity study
of the extract, did not show any alteration in behavior and sensory nervous
system responses. The congruency of the results of acute toxicity study for two
extracts, indicated its reproducibility and on the other hand the results of 2
extracts in the toxicity study showed the validity of the experiments,
coinciding with the results of previous studies23,24.
The validity of the experiments allows affirming that acute toxicity of the
MEBP and PEBP of the plants in study is over 5.5 g/kg, b.wt,
being considered as nontoxic substances under experimental conditions of this
study.
Regarding histological
studies of liver section of Group I showed normal hepatic cells with
well-preserved cytoplasm, prominent nucleus and nucleolus and conspicuous
central vein (Fig 1a) Group III showed mild congestion of endothelial and kuffer cells as compared to control (Fig 1b) Group V having highly differentiated hepatocytes and periportal
chronic inflammatory infiltrate were identified (Fig 1c). Since kuffer cells were
affected this may be the cause of increase in RBC and hemoglobin 400mg/kg b.wt dose.
Whereas, Small
intestines section of Group I showed
normal cellular architecture with the villi and mucinous epithelium appears spindles shaped and inter
connected (Fig 2a). Group III
showed in accumulation of inflammatory cells in villi
of small intestines (Fig 2b). Group V had inflammatory cells in villi of small intestine and damages in tissue (Fig 2c).
Group I showed normal glomeruli and tubules of kidney (Fig 3a). Group III showed
congestion and mild inflammation was observed around the blood vessels of
tubular epithelium cells (Fig 3b). Group III showed congestion and mild inflammation
around the blood vessels and also moderate inflammation around tubular
epithelial cells and mild tissue damages (Fig 3b and 3c respectively), which
are not apparent.
CONCLUSIONS:
It is evident from the haematological, biochemical markers and histopathological
study that animals treated only with 400mg/kg b.wt, p.o., on acute toxicity confirms the depression in CNS and
respiratory activity. Regarding histopathological
observation no organs showed any significant change except insignificant
changes observed in the higher dosed group. From this it is evident that the
plant used for the present study is quiet safe for medicinal use considering
the toxicological profile.
REFERENCE:
1.
Pieme CA et al.
Evaluation of acute and sub-acute toxicities of aqueous ethanolic
extract of leaves of Senna alata (L) Roxb (Ceasalpiniaceae). Afr. J. Biotechnol.
2006; 5(3): 283-289.
2.
Kirtikar KR and Basu BD. Indian
medicinal plants. Publication and Information Directorate, CSIR. New Delhi.
2006; 2nd ed: pp. 1373-1374.
3.
Madhava
Chetty K et al.
Flowering plants of Chittoor district. Students
offset printers, Thirupathi. 2008; pp. 140.
4.
Chin HW, Lin
CC and Tang KS. The hepatoprotective effects of
Taiwan folk medicine ham-hong-chho
in rats. Am J Chin Med. 1996; 24(3): 231-240.
5.
Rivera D. The
ethnopharmacology of Madeira and Porto Santo Islands,
a review. J Ethnopharmacol.
1995; 46(2): 73-93.
6.
Kokate CK. Practical Pharmacognosy. Vallabh
Prakashan. Delhi. 1991; 6th ed: pp. 107-121.
7.
Horbone JB. Phytochemical
methods. Cheppman and hall. London. 1973; 1st ed: pp. 60- 66.
8.
Lorke D. A new approach to practical acute toxicity testing.
Arch. Toxicol. 1983; 54: 275–287.
9.
Klassen CD et al.
Toxicology: The basic science of poison. Mc Graw
Hill, USA. 1995; 8th ed: pp.
13-33.
10.
Ghai CL. A textbook of practical physiology. Jaypee Brothers, India. 1995; pp. 43.
11.
Adams DH. The effect on mouse-liver catalase activity and blood-haemoglobin
level of a milk diet deficient in iron, copper and manganese. J. Biochem.1953; 54: 328–336.
12.
Lewis SM et al. Practical Haematology
Churchill Livingston Edinburgh. 2006.
13.
Lowry OH et al. Protein measurement with the folin phenol reagent. J Biol
Chem. 1951; 193: 265-275.
14.
Mythilypriya R et al.
Oral acute and sub-acute toxicity studies with Kalpaamruthaa,
a modified indigenous preparation, on rats. J. Health Sci. 2007; 53(4):
351-358.
15.
Ghosh MN. Fundamental of Experimental Pharmacology. Scientific Book Agency, Calcutta. 1984.
16.
Jasper W et al. Acute toxicity effects of the methanolic
extract of Fagara zanthoxyloides
(Lam.) root bark. Afr Health Sci. 2003; 3(3): 124-126.
17.
Anonymous. Guidelines for the treatment of animals in
behavioral research and teaching. Anim Behav. 2002; 63:
195–199.
18.
Inala P et al. Hematological analysis of outbreed ICR mouse in the
facility of national laboratory animal centre. The Facility of National
Laboratory Animal Centre. 28th Congress on Science and
Technology of Thailand. 2002.
19.
Garg SK et al.
Anti-lympocytic and immunosuppressive effects of Lantana
camara leaves in rats. Ind
J Expt Biol. 1997; 35: 1315–1318.
20.
Ranjit Madhukar
Bidhe and Sangita
Ghosh. Acute and Sub-chronic (28-Day) Oral Toxicity
Study in Rats Fed with Novel Surfactants. AAPS PharmSci. 2006; 6(2): 10-20.
21.
Angkhasirisap W et al. Blood chemistry analysis of mice and rats given drinking
water that treated with chlorine or hydrochloric acid for contamination
control. 28th Congress
on Science and Technology of Thailand. 2002.
22.
Caisey JD and King DJ.
Clinical chemical values for some common laboratory animals. Clin. Chem.1980; 26: 1877-1879.
23.
Diener W and Schelde
E. Acute toxic class method: alternatives to LD/LC50 tests. Altex.
2000; 16: 129-34.
24.
Monteagudo E et al. Acute toxicity evaluation of six medicinal plants using
three alternative methods. Pharmacology
online. 2006; 3: 639-643.
Received
on 19.07.2010
Accepted on 04.08.2010
© A&V Publication all right reserved
Research Journal of Pharmacognosy and Phytochemistry.
2(5): Sept.-Oct. 2010, 397-402