Evaluation on aucubin accumulation in different ecotypes of plantain (Plantago
sp.)” was carried out on on different ecotypes of plantain collected from
Mongolia and Vietnam. The results showed that: (i) the amount of aucubin had
been increased together with the growth stages. Minimum level of aucubin of P.
depressa was found in vegetative stage (1.66 mg/g), maximum in fruiting stage
(12.46 mg/g); (ii) all of ecotypes of Plantago sp. varied in their aucubin content.
In addition, aucubin content of Mongolian ecotypes was higher than those of
Vietnamese ecotypes’; and (iii) the geo-ecological conditions (Vietnam and
Mongolia) had affected significantly on the aucubin content in different
ecotypes. P. depressa contains higher amount of aucubin than P. major. The
highest aucubin constituent is on P. depressa ecotype which collected in Middle
Khalkh dry steppe, Mongolia (21.87 mg/g) and the lowest on P. major in Thanh
Hoa-Vietnam (2.08 mg/g)
10 trang |
Chia sẻ: thuylinhqn23 | Ngày: 07/06/2022 | Lượt xem: 481 | Lượt tải: 0
Bạn đang xem nội dung tài liệu Comparative Analysis on aucubin content in different ecotyes of plantain plant, để tải tài liệu về máy bạn click vào nút DOWNLOAD ở trên
An Giang University Journal of Science – 2017, Vol. 5 (2), 9 – 18
9
COMPARATIVE ANALYSIS ON AUCUBIN CONTENT IN DIFFERENT ECOTYES
OF PLANTAIN PLANT (Plantago sp.)
Nguyen Van Ay1, Mai Vu Duy1, Do Tan Khang1, Bui Nhi Binh1, Khajidusren Altantsetseg2,
Oyungerel Baatartsogt2, Vanjidorj Enkhchimeg2
1Can Tho University
2Mongolian University of Life Sciences
Information:
Received: 28/11/2016
Accepted: 19/01/2017
Published: 06/2017
Keywords:
Plantain, vegetative growth
stage, geo-ecological
condition, aucubin content
ABSTRACT
Evaluation on aucubin accumulation in different ecotypes of plantain (Plantago
sp.)” was carried out on on different ecotypes of plantain collected from
Mongolia and Vietnam. The results showed that: (i) the amount of aucubin had
been increased together with the growth stages. Minimum level of aucubin of P.
depressa was found in vegetative stage (1.66 mg/g), maximum in fruiting stage
(12.46 mg/g); (ii) all of ecotypes of Plantago sp. varied in their aucubin content.
In addition, aucubin content of Mongolian ecotypes was higher than those of
Vietnamese ecotypes’; and (iii) the geo-ecological conditions (Vietnam and
Mongolia) had affected significantly on the aucubin content in different
ecotypes. P. depressa contains higher amount of aucubin than P. major. The
highest aucubin constituent is on P. depressa ecotype which collected in Middle
Khalkh dry steppe, Mongolia (21.87 mg/g) and the lowest on P. major in Thanh
Hoa-Vietnam (2.08 mg/g).
1. INTRODUCTION
Plantain (Plantago sp.), an important medicinal
plant belonging to the Plantaginaceae family, is a
genus of about 200 species. It is a native plant in
Europe and Asia, but it is now widely distributed
around the world, including temperate climate
areas and some tropical regions (Clapham et al.,
1989). Plantain is quite rich in bioactive
substances, minerals and vitamins, which have
been utilized in Vietnam, Lao, China, Mongolia
and some other countries for traditional and
industrial production in term of health, food
product and medicine (Ho, 2000). Among
bioactive compounds, plantain highly contains of
aucubin belonging to iridoid glucoside group
which is the typical substance for the whole
Plantago genus (Andrzejewska-Golec, 1995,
Taskova et al., 2002, Ronsted et al., 2000 and
Jurisic et al., 2003). It has shown pharmacological
properties, such as hepatoprotective, anti-toxic,
anti-inflammatory, anti-oxidant, anti-aging, wound
healing activity, anti-osteoporosis, neurotrophic,
removal uric acid and diuretic (Kolak et al. 2011).
Environmental factors such as light intensity,
temperature, water availability, type and
composition of soil and several other have a
substantial influence on the quality and
productivity of medicinal plants. They are not
stable in habitats and the consequences of their
variation are difficult to predict (Jolita et al. 2012).
Plants of the same species occurring in different
environments may differ significantly in their
content of particular secondary metabolites
(Szakiel et al., 2010). The evaluation of secondary
An Giang University Journal of Science – 2017, Vol. 5 (2), 9 – 18
10
products accumulation under modified
environment reveals more precise information
about influences of environment factors on
metabolic pathways. Considerable research work
in the last period addresses to various aspects of
modelling these factors using new numerical
methods (Mihailovic & Eitzinger, 2007). The
factors that can be easy to control in greenhouse are
light intensity and temperature. On the other hand,
they are known as the crucial environment factors
strongly related to the phenological development
and secondary metabolism of medicinal plants
(Hornok, 1992; Zobayed et al., 2005). The
stimulating of biosynthesis on secondary
metabolites in medicinal crops by control and
optimization of external and internal factors may
be applied to develop the biotechnologies of high
quality drug production (Poutaraud & Girardin,
2005). On the other hand, research on Plantago sp.
which originated from Mongolia and Vietnam have
been still missing, especially bioactive substance
aspects. Thus, this study was conducted to
comparatively analyze the amount of bio-active
constituent aucubin in different ecotypes of
Plantago sp. which are cultivated in Mongolia and
Vietnam.
2. MATERIALS AND METHODS
2.1 Materials
Seed and whole plant samples of 10 ecotypes of
Plantago sp. were collected in 10 different
experimental sites in Mongolia and Vietnam
(Table 1). Voucher specimens of all samples,
morphologically authenticated by Professor
Altantsetseg, have been deposited at School of
Animal Sciences and Biotechnology, Mongolian
University of Life Sciences, Mongolia. Afterward,
all of ecotypes of Plantago sp. were cultivated in
the greenhouse of Can Tho University (83%
relative humidity, 35oC, light intensity about 5000
lux) and/or Mongolian University of Life Sciences
(51% relative humidity, 20oC, light intensity 2000
lux).
Table 1. Geographical locations of Plantago sp. collected from different locations in Mongolia and Vietnam
Location Country Scientific
name
Location (Latitude, Longitude) Time of
Collection
Middle Khalkh
dry steppe
Mongolia
Plantago
depressa
47.8864° N 106.9057° E July, 2015
Dzungarian Gobi
desert
P. depressa 45.4511° N 95.8506° E July, 2015
Mongolian Altai
Mountain steppe
Plantago
major
48.3983° N 89.6626° E July, 2015
East Mongolia
steppe
P. depressa 47.4658° N 115.3927° E July, 2015
Alashan Gobi
desert
P. major 43.5000° N 104.2861° E July, 2015
Can Tho
Vietnam
P. major 10.0452° N 105.7469° E August, 2015
Ca Mau P. major 9.1527° N 105.1961° E August, 2015
Kien Giang P. major 9.8250° N 105.1259° E August, 2015
Nam Dinh P. major 20.4388° N 106.1621° E August, 2015
Thanh Hoa P. major 20.1291° N 105.3131° E August, 2015
An Giang University Journal of Science – 2017, Vol. 5 (2), 9 – 18
11
2.2 Preparation of samples
Whole plants of the samples were harvested in 4
different growth phases: vegetative (2 months old),
budding (3 months old), flowering (4 months old)
and fruiting stage (5 months old), from 10
randomly selected pots for each phase. All of
selected plants were uprooted and washed under
tap water. Next, the flowers, petioles and roots
were separated from the leaves and dried in a
convectional dryer and mechanically ground to
obtain the homogenous powder.
Aucubin (standard chemical, purity > 98%),
methanol, acetonitrile and other solvents were
purchased from Sigma-Aldrich, USA.
2.3 Extraction of samples
We applied high performance liquid
chromatography (HPLC) to measure iridoid
content in Plantago ecotypes followed by the
modified method (described by Hogedal and
Molgaard, 2000) and Kartini & Azminah (2012).
Fifty mg of dried plant material was added to 10
mL of 100% methanol solution. Samples were
sonicated at 55 °C in a Sonorex Super model RK
52H ultrasonic bath for 60 min and then the extract
mixture was centrifuged at 18,000 rpm in 15 min
to remove particulates. All extract were stored at
4oC until analyzed. Prior to the analysis, all
standards and sample solutions were filtered
through Waters sterile filters with 0.20 µm pores.
2.4 Effect of ecological conditions and
vegetative periods on aucubin content
Observation on P. depressa ecotype collected at
Middle Khalkh dry steppe, Mongolia. This ecotype
was cultivated in 2 different conditions, Mongolia
and Vietnam. To compare the aucubin amount, the
experiment was arranged in a Randomized
Complete Bock Design (RCBD) with 2 factors
including 8 treatments, 5 replications per each
treatment. All treatments were arranged in various
vegetative stages (2, 3, 4 and 5 months old;
vegetative, budding, flowering and fruiting stages,
respectively) and (ii) two ecological conditions.
2.5 Effect of types of ecotypes on aucubin
content
All ecotypes were cultivated in the same conditions
in Vietnam (humidity, temperature, water
availability, fertilizers). After fruiting stage, they
were collected to comparative analyze of aucubin
constituent. The experiment was arranged in a
RCBD with 10 treatments (ecotypes), 5
replications per each treatment.
2.6 Determination of aucubin content by high
performance liquid chromatography
Each 10 μl volume of centrifuged sample was
automatically injected into HPLC system for
analysis. All experiments included in 5 replications
per each ecotype.
A Waters 2847 Dual Wavelength Absorbance
Detector instrument was set to read samples at 202
nm, and flow rate was set to 0.3 μL/min. The
column used in the analysis was a Nova-Pak
reversed-phase C18 column (2 mm x 150 mm, 5
μm particle size; Phenomenex) and the solvent
system consisted of isocratic (non-changing) of 7%
acetonitrile solution (Sigma-Aldrich) in Milli-Q
water. Sample runtime was 25 minutes.
Chromatogram peaks were quantified by
integrating the peak areas. Major peaks other than
the internal standard were assumed to be aucubin,
based on authentic aucubin standard (Fig.1B).
2.7 Building up the standard curve
The stock solutions of reference standards were
prepared by dissolving in methanol. The
concentrations of aucubin reference standard used
for calibration were at 2.5, 5, 10 and 50 mgL-1. The
standard curve was calibrated using the linear
regression equation (Y= 19730X - 54075,
R2=0.9994) derived from the peak areas (Fig 1A).
An Giang University Journal of Science – 2017, Vol. 5 (2), 9 – 18
12
Figure 1. The spectrum of aucubin of reference standard (A) and sample (B)
2.8 Statistical analysis
All the results were performed for the statistical
package for social sciences (Version 16.0 for
windows, SPSS Inc.). The data were subjected to
the analysis of variance (ANOVA). Post-hoc
comparisons of mean quantities were made using
the Duncan Multiple Range Test. A value of p <
0.01 was considered to be significant.
3. RESULTS AND DISCUSSION
3.1 Effect of growth conditions and vegetative
stages on aucubin accumulation
A large number of internal and external factors
effect on the chemical composition of plants and it
is difficult to determine which factor affected
particular changes in chemical compounds. The
factors that can be easy to control in greenhouse are
light intensity and temperature. On the other hand,
they are known as the crucial environment factors
strongly related to the phenological development
and secondary metabolism of medicinal plants
(Hornok, 1992; Zobayed et al., 2005). It is possible
to achieve high production of secondary
metabolites within a very short period of
cultivation under optimized conditions in a
controlled environment system (Afreen, 2005). In
present study, we evaluated the influences of
external factors, as temperature and light intensity
in Vietnam and Mongolia, together with internal
factor – phenological development stages on
accumulation of amount of aucubin in P. depressa
ecotype which originated at Middle Khalkh dry
steppe of Mongolia (Table 2). The present study
revealed that high temperature and light intensity
positively influence the accumulation of aucubin.
The data revealed that the amount of aucubin
(15.83 mg/g) in P. depressa cultivated in Vietnam
is much higher than those in Mongolia (2.04 mg/g),
significantly different at P < 0.01 level.
Table 2. Effect of growth conditions and vegetative stages on the aucubin content (mg/g, dried weight) in plantain (P.
depressa)
Vegetative stages (months old)
Growing place (location) Aucubin content
(mg/g, dried weight) Mongolia Vietnam
2 (Vegetative) 1.00(±0.03) e 2.31(±0.41) cd 1.66(±0.74) d
3 (Budding) 1.60(±0.17) de 19.43(±0.93) b 10.51(±0.94) c
4 (Flowering) 2.51(±0.10) c 19.71(±1.06) b 11.11(±0.90) b
5 (Fruiting) 3.06(±0.19) c 21.87(±0.61) a 12.46 (±0.61) a
0.0 0.5 1.0 1.5 2.0 2.5 3.0 3.5 4.0 4.5 5.0 5.5 6.0 6.5 7.0 7.5 min
0.00
0.25
0.50
0.75
1.00
1.25
1.50
1.75
uV(x100,000)
0.0 0.5 1.0 1.5 2.0 2.5 3.0 3.5 4.0 4.5 5.0 5.5 6.0 6.5 7.0 7.5 min
0.00
0.25
0.50
0.75
1.00
1.25
1.50
1.75
2.00
2.25
uV(x1,000,000)
A B
An Giang University Journal of Science – 2017, Vol. 5 (2), 9 – 18
13
Vegetative stages (months old)
Growing place (location) Aucubin content
(mg/g, dried weight) Mongolia Vietnam
Aucubin content on ecological
conditions (B)
2.04(±0.82) b 15.83(±0.90) a
P(A) **
P(B) **
P(A*B) **
CV (%) 6.43
The data were observated on P. depressa ecotype collected at Middle Khalkh dry steppe, Mongolia; Means with same letters
indicate no significant difference by Duncan’s multiple-range test; ** = significant at 0.01 level.
Medical chemicals are synthesized and
accumulated based on some genes induced by
environmental conditions. It is well known that
light is a physical factor which can affect the
metabolite production. In addition, temperature is
one of the most important environmental factors
controlling plant secondary metabolite production
(Kaplan et al., 2004; Ramakrishna and
Ravishankar, 2011). Temperature significant
influences photosynthetic processes, ontogenetic
development, the carbon balance of plants, and the
influence can be positive or negative (Morison and
Lawlor, 1999). Higher light intensity and
temperature stimulate the photosynthetic
efficiency and accumulation of aucubin in P.
depressa and an increase of aucubin under higher
light intensity and temperature linked to higher
abundance of dark glands, which are considered as
synthesis sites of corresponding compounds
(Briskin and Gawienowski, 2001; Zobayed et al.,
2006). Indeed, according to Anasori and Asghari
(2008) light is a physical factor which can affect
the metabolite production.
The production of secondary metabolites is often
low and depends greatly on the physiological and
developmental stage of the plant (Rao and
Ravishankar, 2002). In Table 11, the result also
shows that significantly different aucubin content
on 4 different vegetative stages. The tendency of
aucubin increases gradually from vegetative to
fruiting stage. Furthermore, the content of aucubin
at fruiting stage were the highest (12.46 mg/g)
among the 4 different vegetative stages while
lowest at vegetative stage (1.66 mg/g), significant
at 0.01 level. It should be noted that various parts
of the plants may differ quantitatively and
qualitatively as far as the content of iridoids is
concerned. Noro et al. (1990) observed that the
overground parts of Plantago asiatica contained
more aucubin than the underground ones, and
young leaves were more than the older ones.
According to Bowers and Stamp (1992), the
contents of aucubin and catalpol in Plantago
lanceolata was determined genetically and it also
depended on the age of leaves. Phylogenetically,
the secondary bioactive compounds in plants
appear to be randomly synthesised – but they are
not useless junk. Several of them are found to hold
important functions in the living plants (Bernhoft,
2010). Thus, according to Jensen (1991) and
Damtoft et al. (1993), in P. major and Scrophularia
racemosa, aucubin is sythesized from a precursor
which is 8-epi-deoxyloganic acid or 8-epi-
iridodial. Afterward, because of being an
intermediate, aucubin can be used to forming
capatal finally or others under specific
circumstances.
Moreover, the interaction of ecological conditions
and vegetative stages on aucubin content of P.
depressa, significant at 0.01 level (Table 2). The
maximum is at fruiting stage (21.87 mg/g)
cultivated in Vietnam, the minimum is at
vegetative stage (1 mg/g) in Mongolia. The present
result shows that P. depressa cultivated in different
An Giang University Journal of Science – 2017, Vol. 5 (2), 9 – 18
14
environments could differ significantly in aucubin
content. Jolita et al. (2012) concluded that the
quality and productivity of medicinal plants can be
affected by environmental factors such as light
intensity, temperature, water availability, type and
composition of soil. Bioactive compounds also are
not stabile in habitats and the consequences of their
variation are difficult to predict. On the other hand,
even the same species growing in different
environments may vary significantly in their
content of particular biosubstance compounds
(Szakiel et al., 2010).
Iridoids belong to terpenoids, which are a class of
secondary metablites found in a wide variety of
plants. Aucubin is one of the most common
iridoids in the plant kingdom. Terpenoids represent
the largest and most diversified class of chemicals
among the innumerable compounds produced by
plants. Plants require terpenoids metabolites for a
variety of basic functions in growth and
development as photosynthetic pigments
(carotenoids), electron carriers (side-chains of
ubiquinone and plastoquinone), regulators of
growth and development (gibberellins, abscisic
acid, strigolactones, brassinosteroids, cytokinins),
in protein glycosylation (dolichols), or as elements
of membrane structure and function (phytosterols),
specialized terpenoid metabolites, in particular,
have been recognized for an array of biological
roles. Moreover, using of terpenoids for more
specialized chemical interactions and protection in
the abiotic and biotic environment (Tholl, 2015;
Loreto et al., 2014; Behnke et al., 2007; Velikova
et al., 2014). On the other hand, the typical defense
compounds of Plantaginaceae are the iridoid
glycosides. In plants, glycosidic defense
compounds and hydrolytic enzymes often form a
dual defense system, in which the glycosides are
activated by the enzymes to exert biological
effects. The concentration of iridoid glycosides as
well as the β-glucosidase activity in leaves of
different ages. The concentrations of defense
compounds as well as the β-glucosidase activity,
were highest in younger leaves and decrease with
increasing leaf age (Buschmann and Muller, 2013).
Thus, all previous research strongly supported for
our results that the aucubin content do differ in
vegetative stages and even ecological conditions.
3.2 Effect of ecotypes on aucubin content
According to Andrzejewska-Golec (1995), among
species of the genus Plantago, there are 38
investigated species, which contain aucubin and
differ in their aucubin content. Beside the
accumulation of secondary metabolites highly
depends on external factors, they also strongly
depend on their gene expression through
environmental interaction. The data in Table 12
indicates that the aucubin content of P. depressa
(21.87, 14.37 and 14.17 mg/g at experimental sites
of Middle Khalkh dry steppe, Dzungarian Gobi
desert and East Mongolia steppe respectively) is
higher than in P. major (12.78, 13.41, 7.43, 4.83,
3.12, 13.67 and 2.08 mg/g; Mongolian Altai
Mountain steppe, Alashan Gobi desert, Can Tho,
Ca Mau, Kien Giang, Nam Dinh and Thanh Hoa
sites, respectively), significant at 0.01 level. The
highest is at Middle Khalkh dry steppe site and the
lowest at Thanh Hoa site. Furthermore, the aucubin
content of plantains originated in Mongolia are
much higher than those in Vietnam (Table 3).
Although in our study we set up all ecotypes in the
same conditions, aucubin content of those differed.
It could be due to some reason: Aucubin is an
iridoid glycoside, which belongs to Terpenoids. In
pathway of biosynthesis of iridoids in plant,
aucubin is an intermediate chemical (Damtoft et
al., 1993). I