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164 Nooralvandi et al.
Int. J. Biosci. 2014
RESEARCH PAPER OPEN ACCESS
The effect of rhizosphere growth promoter bacteria on
enzymes activities of Hordeum vulgare and Brassica napus
plants in polluted soil with Pb
Tohid Nooralvandi1*
, Davood Habibi2
, Touraj Rahimi3
, Parviz Omidnia3
, Mohammad
Hossein Bijeh Keshavarzi4
1
Young Researchers and Elites Club, Karaj Branch, Islamic Azad University, Karaj, Iran
2
Department of Agronomy and Plant Breeding, Karaj Branch, Islamic Azad University, Karaj, Iran
3
Department of Agronomy and Plant Breeding, Shahr-e-Qods Branch, Islamic Azad University,
Tehran, Iran
4
Young Researchers and Elites Club, North Tehran Branch, Islamic Azad University, Tehran, Iran
Key words: Pb, Growth promoter bacteria, Antioxidant, Hordeum vulgare, Brassica napus.
http://dx.doi.org/10.12692/ijb/4.10.164-170 Article published on May 23, 2014
Abstract
Soils and accumulated materials are resources of heavy metals, which are available for absorbance by plants. One
of the potential methods for eliminating heavy metals from polluted places includes usage of resistance creature
to metals which are able to accumulate and absorb high amount of material. Present study was carried out in a
greenhouse format in completely accidental plots with 4 times repetition and 2 plants of Hordeum vulgare and
Brassica napus. This experiment was done in 2011 in Islamic Azad University, Karaj branch. Variance analysis
results showed significant effect of pb levels, growth promoters bacteria and interaction effects of them on
capabilities of Superoxide dismutase (SOD), Catalase (CAT) and Glutathione peroxidase (GPX) enzymes
(P<0.01).
* Corresponding Author: Tohid Nooralvandi  keshavarzi64.mh@gmail.com
International Journal of Biosciences | IJB |
ISSN: 2220-6655 (Print) 2222-5234 (Online)
http://www.innspub.net
Vol. 4, No. 10, p. 164-170, 2014
165 Nooralvandi et al.
Int. J. Biosci. 2014
Introduction
Soils are the sources of heavy metals which are
available for plants to absorb them. To resurrect
polluted environments, some solutions are designed
that include chemical and physical methods or
biological techniques which need interference of
biological factors (Gianfreda and Rao, 2004;
Boularbah et al., 2006). Refining of polluted soils to
heavy metals is a necessary and inevitable issue.
Among different heavy metals, Pb is considered as a
polluted material which accumulates rapidly in soils
(Sharma and Dubey, 2005) and is one of the heavy
metals that has lots of disadvantages for human being
(Lin et al., 2009; Estrella – Gomez et al., 2009;
Brunet et al., 2008).
Antioxidant enzymes are considered as defendant
systems for plants to light against oxidize stress that
is result of metals (Ali et al., 2003). Anti oxidant
system includes some enzymes such as (SOD), (CAT)
and (GPOD).
Produced super oxide radicals have transformed to
H2O2 by SOD function and Ascorbate peroxidase
(APX), CAT, G-POD, GPX enzymes activity prevent
from H2O2 accumulation; therefore balance between
production of ROS and its elimination guarantees
system's survival (Khatun et al., 2008). These
enzymes cooperate in a set of biological processes that
are require for grow and development (Gaetke and
Chow, 2003), and preserve animals from oxidation
damages (Garnczarska and Ratajczak, 2000).
Rhizosphere bacteria that have settled selectively in
one of the three fold sections of rhizosphere, have
negative impacts on plants' function. These bacteria
are called Deleterious Rhizobacteria (DRB). Harmful
effects of this group of bacteria are the result of
metabolites accumulation such as aliphatic, phenolic
acid, sulfuric acid and mostly Hydrocyanic acid (Saleh
Rastin, 2002). Consequently those risobacteria that
lead to enhancement of plants' growth and
improvement of agronomical plants' functions are
called Plant Growth Promoters Rhizobacteria (PGPR)
(Vessey et al., 2003).
The aim of this study is effect of Pb heavy metal and
growth promoter bacteria on activities of Hordeum
vulgare and Brassica napus antioxidant enzymes.
Method and materials
Present study was carried out as a greenhouse study
in 2011 in Islamic Azad University, Karaj branch. The
geographical coordinate of study location were 35o
and 55// latitude, 50o and 54// (longitude) and 1313 m
height from sea level. The relative moisture of
greenhouse 57% and the lowest temperature was
15.5oc and the highest temperature was 30oc. The
experimental soil was loamy and sandy with pH = 7.6,
its conductivity was 2.9 ds.m-1 and pb amount was 2
mg.kg-1 of soil. Preferable Pb concentration was
provided regarding capacity of 5 kg plots, and 2
months before cultivation plots' soils become polluted
with Pb heavy metal by spray.
This experiment was in factorial and completely
accidental format with 4 times repetition. This
experiment included 40 treatments in 160
experimental plots with 2 plants of Hordeum vulgare
and Brassica napus.
Experimental factors included
Growth promoter bacteria in 5 levels:
1st level: control (without insemination of bacteria),
2nd level: insemination with Azosprillium crococum
bacteria, 3rd level: insemination with Azotobacter, 4th
level: insemination with P. putida, 5th level:
insemination with Azosprillum crococum,
Azotobacter, P. putida bacteria; and second factor
included Pb levels in 4 level (0, 250, 500 and 750
mg/kg).
Seeds were disinfected with sodium hypochlorite
(1.5%), and sterilized with water. Growth promoter
bacteria were used in mixing the seed format.
Bacteria were provided from microbe bank of soil's
biological study section of Karaj soil and water
research institute.
7 seeds of Brassica napus and 20 seeds of Hordeum
vulgare were used which 10 mil/lit bacteria
166 Nooralvandi et al.
Int. J. Biosci. 2014
suspension was added to each seed (each mil lit of
inoculum had 107 live and active cells of each type of
bacteria).
Measurement of activity amount of SOD enzyme
Some young leaves were separated and put in an
icebox which its bottom was covered with ice then
they were transferred to laboratory. Then activity
amount of SOD enzymes was measured by Misra and
Fridorich (1979) method.
Measurement of GPX activity amount
Transferred leaves were washed by distilled water.
Immediately after this phase they were entered to
phosphate buffer 0.16 m and its pH was 7.2 then they
were crushed and homogenized). Then in presence of
similar volume of that buffer included Digitonin and
digestive enzymes, digestive process of cell walls was
done. Finally, 0.5 mlit of homogeneous solution was
used to measure protein in terms of mgr/milt. Then
in the rest of extracted solution activity amount of
GPX enzymes was measured by Paglia and Valentine
(1987) method.
Measurement of CAT activity amount
By means of Paglia and Valentine (1987) math CAT
changes amount was determined.
Variance analysis was done with SAS software. In
addition to compare means, Duncan test was used.
Moreover, graphs were drawn by Excel software.
Results
SOD enzyme's activity of Hordeum vulgare
The results of variance analysis (table 1) show that
there is a significant effect of Pb levels, growth
promoter bacteria and their interaction effect on SOD
enzyme's capability (P<0.01). The mixture of growth
promoter bacteria and Pb leads to significant increase
of SOD amount.
Table 1. Result of variance analysis on characteristics measured of Hordeum vulgare.
MS
S.O.V d.f SOD CAT GPX
A (growth promoter bacteria) 4 1371478/8** 93716** 13006/62**
B (Pb level) 3 740425/7** 61951/4** 8326/8**
A*B (Interaction) 12 54107/44** 2706/1** 509/48**
Error 57
c.v. 3/62 4/59 3/97
Note: * and ** indicate significant difference at 5% and 1% probability level, respectively ns is not significant.
According to figure 1, it is observed that the treatment of mixture of growth promoter bacteria lead to
enhancement of SOD amount. Actually, in this relation, when Pb amount of soil is lower the effect of bacteria is
more significant. When we had mixture of bacteria along with 750 mgr/kg Pb, 804.5 SOD was secreted in the
plant, while in the same level of bacteria along with 250 and 500 mg/kg Pb the amount of SOD enhanced to 1436
and 1236 u/mg. pr.
SOD's activity in Brassica napus
The results of variance analysis (table 2) show that
there is a significant effect of Pb levels, growth
promoter bacteria and their interaction effect on SOD
enzyme's capability (P<0.01). The mixture of growth
promoter bacteria and Pb leads to significant increase
of SOD amount.
According to figure 2, it is observed that the
treatment of mixture of growth promoter bacteria
lead to enhancement of SOD amount. Actually, in this
relation, when Pb amount of soil is lower the effect of
bacteria is more significant. When we had mixture of
bacteria along with 750 mgr/kg Pb, 1565.5 SOD was
secreted in the plant, while in the same level of
bacteria along with 250 and 500 mg/kg Pb the
amount of SOD enhanced to 2110.25 and 1843.5
u/mg. pr.
167 Nooralvandi et al.
Int. J. Biosci. 2014
CAT activity in Hordeum vulgare
Results of variance analysis (table 1) indicated that
there is a significant effect of Pb levels, growth
promoter bacteria and their interaction effect on
CAT's capacity in Hordeum vulgare (P<0.01). Figure
3 shows the changes in CAT's amount in different
levels of Pb and bacteria. As it is observable, by
increasing Pb concentration in soil, CAT's amount
decreases and by using growth promoter bacteria, this
amount increases in comparison with control.
Application of growth promoter bacteria along with
Pb element leads to enhancement of CAT's amount.
This procedure is the same as what was happened for
SOD activity in Hordeum vulgare and Brassica
napus.
Table 2. Result of variance analysis on characteristics measured of Brassica napus.
MS
S.O.V d.f SOD CAT GPX
A (growth promoter bacteria) 4
2305628/5** 32253/03** 17774/9**
B (Pb level) 3 1278124/03** 19320/71** 8405/6**
A*B (Interaction) 12 27579/76** 684/3** 635**
Error 57
c.v. 3/44 3/92 6/93
Note: * and ** indicate significant difference at 5% and 1% probability level, respectively ns is not significant. In
soil contains mixture of growth promoter bacteria in the same level of Pb enzyme's activity will be equal to 123.7
u/mg.pr. 250 mg of Pb lonely can lead to 56.9 u/mg.pr activity in plant. If 250 mg/kg of Pb uses along with
growth promoter bacteria, enzyme's activity will reach to 149.82 u/mg.pr (Figure 5).
According to figure 3, it is observed that mixture
treatment of growth promoter bacteria leads to
enhancement of CAT's amount. But in this relation
when Pb amount was lower, the effect of bacteria is
more significant. When mixture of bacteria was used
along with 750 mg/kg Pb 291 u/mg.pr CAT was
secreted, while in the same level of bacteria along
with 250 and 500 mg/kg of Pb. CAT's amount
enhanced to 423.25 and 394 u/mg.pr orderly, and in
when Pb wasn't applied in the soil, this amount
reached to 422.5 mg protein per plant.
CAT activity in Brassica napus
Results of variance analysis (table 2) indicated that
there is a significant effect of Pb levels, growth
promoter bacteria and their interaction effect on
CAT's capacity in Hordeum vulgare (P<0.01).
According to figure 4, it is observed that mixture
treatment of growth promoter bacteria leads to
enhancement of CAT's amount. But in this relation
when Pb amount was lower, the effect of bacteria is
more significant. When mixture of bacteria was used
along with 750 mg/kg Pb 296 u/mg.pr CAT was
secreted, while in the same level of bacteria along
with 250 and 500 mg/kg of Pb. CAT's amount
enhanced to 333.5 and 337 u/mg.pr orderly, and
when Pb wasn't applied in the soil, this amount
reached to 338.75 mg protein per plant.
GPX's activity in Hordeum vulgare
The results of variance analysis showed significant
effect of both Pb and bacteria factors and their
interaction effect on the activity of GPX (P<0.01)
(Table 1).
Figure 5 showed that by increasing Pb concentration,
secretion of this enzymes decreases, in contrast by
application of growth promoter bacteria GPX's
activity increasing. In concentration of 750 mg Pb in
soil and control treatment of bacteria, enzymes
activity was equal to 78.62 (u/mg.pr). If soil contains
mixture of growth promoter bacteria in the same level
of Pb, enzymes' activity reaches to 126.02 u/mg.pr.
168 Nooralvandi et al.
Int. J. Biosci. 2014
250 mg of Pb lonely leads to 92.17 u/mg.pr activity in
plant. 250 mg/kg of Pb along with application of
growth promoter bacteria, enzyme's activity leads to
172.2 (u/mg.pr).
GPX's activity in Brassica napus
The results of variance analysis showed significant
effect of both Pb and bacteria factors and their
interaction effect on the activity of GPX (P<0.01)
(Table 2).
Discussion
Under stress condition, active O2 increases in plant.
In such condition, plant uses different mechanism for
eliminating different types of active O2. On the basis
of this fact, SOD's activity under Pb and bacteria
treatments was considered in 2 plants of Hordeum
vulgare and Brassica napus.
Fig. 1. Interaction effect of Pb and bacteria on SOD
activity in Hordeum vulgare.
SOD catalyzes reaction of transformation O2
- to H2O2
and O2 (Lopez et al., 2005). , between these 2 plants
showed that Brassica napus secreted more SOD's
activity in presence of growth promoter bacteria then
Hordeum vulgare. In present study, by increasing Pb
heavy metal in growth environment, activity of SOD,
which transforms O2 to H2O2, will decrease.
In maximum amount of Pb in soil, released of SOD in
Brassica napus was 1028.8 (u/mg.pr) and in control
treatment this amount reached to 1615.3 u/mg.pr this
amount is 61% more than enzymes' activities of
Hordeum vulgare. SOD's activity in Hordeum
vulgare was in medium amount. It seems that activity
of SOD is the response to harmful effects of produced
oxygen's that are results of application of growth
promoter bacteria. The highest amount of activity of
these enzymes was related to the lowest concentration
of Pb in the soil. Totally, enhancement of Pb
concentration in soil of both plant's types led to
reduction of SOD's activity. Sharma and Dubey
(2005) and Garnczarska and Ratajczak (2000)
reported that SOD's activity will increase under the
poison level of Pb. Enhancement of SOD and CAT's
activity in Brassica napus in comparison with
Hordeum vulgare indicated that enzymes respond to
produced free-radicals in plants under the poison
level of Pb, because Brassica napus absorbed more
Pb in its root and aero organs. Therefore, it seems
that higher productions and activity of these enzymes
is considered as a defendant mechanism against this
element which is attributed to resistance and strategy
of plant. Probably these enzymes because digesting
more O2
- than Hordeum vulgare, and growth
promoter bacteria which are effective in absorbing
more heavy elements in the root, are also effective in
enhancement of enzymes' amount under different
level of Pb.
Fig. 2. Interaction effect of Pb and bacteria on SOD
activity in Brassica napus CAT activity in Hordeum
vulgare.
CAT is on enzyme which will be active under oxide
stress. This enzyme is enable to digested eliminate
H2O2 (Khatun et al., 200). A comparison between
CAT's activity under poison amount of Pb, growth
promoter bacteria treatment indicated that both
above treatments had significant increase than
control treatment. Although both treatment increased
CAT's activity this enhancement wasn't equal for both
plant's types. In Brassica napus CAT's activity was
more than Hordeum vulgare.
169 Nooralvandi et al.
Int. J. Biosci. 2014
Hordeum vulgare had the lowest amount of released
enzymes. Enhancement of Pb concentration also led
to reduction of CAT's activity in both plant's types.
CAT had 30% reduction in 750 mg/kg soil
comparison with control. H2O2 which is poison
product of SOD's yield is used or transformed by CAT
(Garnczarska and Ratajczak, 2000).
Fig. 3. Interaction effect of Pb and bacteria on CAT's
activity in Hordeum vulgare.
GPX preserves lipid membrane against oxide
damages (Mashhadi Akbar Boojar and Goodarzi,
2007). Enhancement of enzymes activity under
bacteria treatment indicates that probably activities of
CAT and GPX prevent accumulation of H2O2, since it
transformed O2
- to H2O2 by SOD yields and
transformed O2
- poisoning effects to H2O and O2.
Therefore, by making a balance between ROS
production and eliminating them, systems survival is
guaranteed, since ROS is poisoning and should
separated by enzymes activity, enhancement of GPX
activity had an important role in reduction of H2O2
through GSH activity (Khatun et al., 2008). It seems
that synthesis of Glutathione was similar in both
plants' types.
Fig. 4. Interaction effect of Pb and bacteria on CAT's
activity in Brassica napus GPX's activity in Hordeum
vulgare
Fig. 5. Interaction effect of Pb and bacteria on GPX
activity in Brassica napus
Comparison between control plants and those which
are grown in Cu environment shows that
enhancement of GPX enzymes is the results of
increasing concentration of Ca. As it was mentioned,
antioxidant enzymes always haven't enhancement
under oxidant stress of heavy metals, and they show
different reaction due to different plant's types, since
antioxidant components that are existed in plants' oils
have different yield and their mechanism mostly is
related to mixture and condition of experimental
system (Wong et al., 2005).
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The effect of rhizosphere growth promoter bacteria on enzymes activities of Hordeum vulgare and Brassica napus plants in polluted soil with Pb - IJB

  • 1. 164 Nooralvandi et al. Int. J. Biosci. 2014 RESEARCH PAPER OPEN ACCESS The effect of rhizosphere growth promoter bacteria on enzymes activities of Hordeum vulgare and Brassica napus plants in polluted soil with Pb Tohid Nooralvandi1* , Davood Habibi2 , Touraj Rahimi3 , Parviz Omidnia3 , Mohammad Hossein Bijeh Keshavarzi4 1 Young Researchers and Elites Club, Karaj Branch, Islamic Azad University, Karaj, Iran 2 Department of Agronomy and Plant Breeding, Karaj Branch, Islamic Azad University, Karaj, Iran 3 Department of Agronomy and Plant Breeding, Shahr-e-Qods Branch, Islamic Azad University, Tehran, Iran 4 Young Researchers and Elites Club, North Tehran Branch, Islamic Azad University, Tehran, Iran Key words: Pb, Growth promoter bacteria, Antioxidant, Hordeum vulgare, Brassica napus. http://dx.doi.org/10.12692/ijb/4.10.164-170 Article published on May 23, 2014 Abstract Soils and accumulated materials are resources of heavy metals, which are available for absorbance by plants. One of the potential methods for eliminating heavy metals from polluted places includes usage of resistance creature to metals which are able to accumulate and absorb high amount of material. Present study was carried out in a greenhouse format in completely accidental plots with 4 times repetition and 2 plants of Hordeum vulgare and Brassica napus. This experiment was done in 2011 in Islamic Azad University, Karaj branch. Variance analysis results showed significant effect of pb levels, growth promoters bacteria and interaction effects of them on capabilities of Superoxide dismutase (SOD), Catalase (CAT) and Glutathione peroxidase (GPX) enzymes (P<0.01). * Corresponding Author: Tohid Nooralvandi  keshavarzi64.mh@gmail.com International Journal of Biosciences | IJB | ISSN: 2220-6655 (Print) 2222-5234 (Online) http://www.innspub.net Vol. 4, No. 10, p. 164-170, 2014
  • 2. 165 Nooralvandi et al. Int. J. Biosci. 2014 Introduction Soils are the sources of heavy metals which are available for plants to absorb them. To resurrect polluted environments, some solutions are designed that include chemical and physical methods or biological techniques which need interference of biological factors (Gianfreda and Rao, 2004; Boularbah et al., 2006). Refining of polluted soils to heavy metals is a necessary and inevitable issue. Among different heavy metals, Pb is considered as a polluted material which accumulates rapidly in soils (Sharma and Dubey, 2005) and is one of the heavy metals that has lots of disadvantages for human being (Lin et al., 2009; Estrella – Gomez et al., 2009; Brunet et al., 2008). Antioxidant enzymes are considered as defendant systems for plants to light against oxidize stress that is result of metals (Ali et al., 2003). Anti oxidant system includes some enzymes such as (SOD), (CAT) and (GPOD). Produced super oxide radicals have transformed to H2O2 by SOD function and Ascorbate peroxidase (APX), CAT, G-POD, GPX enzymes activity prevent from H2O2 accumulation; therefore balance between production of ROS and its elimination guarantees system's survival (Khatun et al., 2008). These enzymes cooperate in a set of biological processes that are require for grow and development (Gaetke and Chow, 2003), and preserve animals from oxidation damages (Garnczarska and Ratajczak, 2000). Rhizosphere bacteria that have settled selectively in one of the three fold sections of rhizosphere, have negative impacts on plants' function. These bacteria are called Deleterious Rhizobacteria (DRB). Harmful effects of this group of bacteria are the result of metabolites accumulation such as aliphatic, phenolic acid, sulfuric acid and mostly Hydrocyanic acid (Saleh Rastin, 2002). Consequently those risobacteria that lead to enhancement of plants' growth and improvement of agronomical plants' functions are called Plant Growth Promoters Rhizobacteria (PGPR) (Vessey et al., 2003). The aim of this study is effect of Pb heavy metal and growth promoter bacteria on activities of Hordeum vulgare and Brassica napus antioxidant enzymes. Method and materials Present study was carried out as a greenhouse study in 2011 in Islamic Azad University, Karaj branch. The geographical coordinate of study location were 35o and 55// latitude, 50o and 54// (longitude) and 1313 m height from sea level. The relative moisture of greenhouse 57% and the lowest temperature was 15.5oc and the highest temperature was 30oc. The experimental soil was loamy and sandy with pH = 7.6, its conductivity was 2.9 ds.m-1 and pb amount was 2 mg.kg-1 of soil. Preferable Pb concentration was provided regarding capacity of 5 kg plots, and 2 months before cultivation plots' soils become polluted with Pb heavy metal by spray. This experiment was in factorial and completely accidental format with 4 times repetition. This experiment included 40 treatments in 160 experimental plots with 2 plants of Hordeum vulgare and Brassica napus. Experimental factors included Growth promoter bacteria in 5 levels: 1st level: control (without insemination of bacteria), 2nd level: insemination with Azosprillium crococum bacteria, 3rd level: insemination with Azotobacter, 4th level: insemination with P. putida, 5th level: insemination with Azosprillum crococum, Azotobacter, P. putida bacteria; and second factor included Pb levels in 4 level (0, 250, 500 and 750 mg/kg). Seeds were disinfected with sodium hypochlorite (1.5%), and sterilized with water. Growth promoter bacteria were used in mixing the seed format. Bacteria were provided from microbe bank of soil's biological study section of Karaj soil and water research institute. 7 seeds of Brassica napus and 20 seeds of Hordeum vulgare were used which 10 mil/lit bacteria
  • 3. 166 Nooralvandi et al. Int. J. Biosci. 2014 suspension was added to each seed (each mil lit of inoculum had 107 live and active cells of each type of bacteria). Measurement of activity amount of SOD enzyme Some young leaves were separated and put in an icebox which its bottom was covered with ice then they were transferred to laboratory. Then activity amount of SOD enzymes was measured by Misra and Fridorich (1979) method. Measurement of GPX activity amount Transferred leaves were washed by distilled water. Immediately after this phase they were entered to phosphate buffer 0.16 m and its pH was 7.2 then they were crushed and homogenized). Then in presence of similar volume of that buffer included Digitonin and digestive enzymes, digestive process of cell walls was done. Finally, 0.5 mlit of homogeneous solution was used to measure protein in terms of mgr/milt. Then in the rest of extracted solution activity amount of GPX enzymes was measured by Paglia and Valentine (1987) method. Measurement of CAT activity amount By means of Paglia and Valentine (1987) math CAT changes amount was determined. Variance analysis was done with SAS software. In addition to compare means, Duncan test was used. Moreover, graphs were drawn by Excel software. Results SOD enzyme's activity of Hordeum vulgare The results of variance analysis (table 1) show that there is a significant effect of Pb levels, growth promoter bacteria and their interaction effect on SOD enzyme's capability (P<0.01). The mixture of growth promoter bacteria and Pb leads to significant increase of SOD amount. Table 1. Result of variance analysis on characteristics measured of Hordeum vulgare. MS S.O.V d.f SOD CAT GPX A (growth promoter bacteria) 4 1371478/8** 93716** 13006/62** B (Pb level) 3 740425/7** 61951/4** 8326/8** A*B (Interaction) 12 54107/44** 2706/1** 509/48** Error 57 c.v. 3/62 4/59 3/97 Note: * and ** indicate significant difference at 5% and 1% probability level, respectively ns is not significant. According to figure 1, it is observed that the treatment of mixture of growth promoter bacteria lead to enhancement of SOD amount. Actually, in this relation, when Pb amount of soil is lower the effect of bacteria is more significant. When we had mixture of bacteria along with 750 mgr/kg Pb, 804.5 SOD was secreted in the plant, while in the same level of bacteria along with 250 and 500 mg/kg Pb the amount of SOD enhanced to 1436 and 1236 u/mg. pr. SOD's activity in Brassica napus The results of variance analysis (table 2) show that there is a significant effect of Pb levels, growth promoter bacteria and their interaction effect on SOD enzyme's capability (P<0.01). The mixture of growth promoter bacteria and Pb leads to significant increase of SOD amount. According to figure 2, it is observed that the treatment of mixture of growth promoter bacteria lead to enhancement of SOD amount. Actually, in this relation, when Pb amount of soil is lower the effect of bacteria is more significant. When we had mixture of bacteria along with 750 mgr/kg Pb, 1565.5 SOD was secreted in the plant, while in the same level of bacteria along with 250 and 500 mg/kg Pb the amount of SOD enhanced to 2110.25 and 1843.5 u/mg. pr.
  • 4. 167 Nooralvandi et al. Int. J. Biosci. 2014 CAT activity in Hordeum vulgare Results of variance analysis (table 1) indicated that there is a significant effect of Pb levels, growth promoter bacteria and their interaction effect on CAT's capacity in Hordeum vulgare (P<0.01). Figure 3 shows the changes in CAT's amount in different levels of Pb and bacteria. As it is observable, by increasing Pb concentration in soil, CAT's amount decreases and by using growth promoter bacteria, this amount increases in comparison with control. Application of growth promoter bacteria along with Pb element leads to enhancement of CAT's amount. This procedure is the same as what was happened for SOD activity in Hordeum vulgare and Brassica napus. Table 2. Result of variance analysis on characteristics measured of Brassica napus. MS S.O.V d.f SOD CAT GPX A (growth promoter bacteria) 4 2305628/5** 32253/03** 17774/9** B (Pb level) 3 1278124/03** 19320/71** 8405/6** A*B (Interaction) 12 27579/76** 684/3** 635** Error 57 c.v. 3/44 3/92 6/93 Note: * and ** indicate significant difference at 5% and 1% probability level, respectively ns is not significant. In soil contains mixture of growth promoter bacteria in the same level of Pb enzyme's activity will be equal to 123.7 u/mg.pr. 250 mg of Pb lonely can lead to 56.9 u/mg.pr activity in plant. If 250 mg/kg of Pb uses along with growth promoter bacteria, enzyme's activity will reach to 149.82 u/mg.pr (Figure 5). According to figure 3, it is observed that mixture treatment of growth promoter bacteria leads to enhancement of CAT's amount. But in this relation when Pb amount was lower, the effect of bacteria is more significant. When mixture of bacteria was used along with 750 mg/kg Pb 291 u/mg.pr CAT was secreted, while in the same level of bacteria along with 250 and 500 mg/kg of Pb. CAT's amount enhanced to 423.25 and 394 u/mg.pr orderly, and in when Pb wasn't applied in the soil, this amount reached to 422.5 mg protein per plant. CAT activity in Brassica napus Results of variance analysis (table 2) indicated that there is a significant effect of Pb levels, growth promoter bacteria and their interaction effect on CAT's capacity in Hordeum vulgare (P<0.01). According to figure 4, it is observed that mixture treatment of growth promoter bacteria leads to enhancement of CAT's amount. But in this relation when Pb amount was lower, the effect of bacteria is more significant. When mixture of bacteria was used along with 750 mg/kg Pb 296 u/mg.pr CAT was secreted, while in the same level of bacteria along with 250 and 500 mg/kg of Pb. CAT's amount enhanced to 333.5 and 337 u/mg.pr orderly, and when Pb wasn't applied in the soil, this amount reached to 338.75 mg protein per plant. GPX's activity in Hordeum vulgare The results of variance analysis showed significant effect of both Pb and bacteria factors and their interaction effect on the activity of GPX (P<0.01) (Table 1). Figure 5 showed that by increasing Pb concentration, secretion of this enzymes decreases, in contrast by application of growth promoter bacteria GPX's activity increasing. In concentration of 750 mg Pb in soil and control treatment of bacteria, enzymes activity was equal to 78.62 (u/mg.pr). If soil contains mixture of growth promoter bacteria in the same level of Pb, enzymes' activity reaches to 126.02 u/mg.pr.
  • 5. 168 Nooralvandi et al. Int. J. Biosci. 2014 250 mg of Pb lonely leads to 92.17 u/mg.pr activity in plant. 250 mg/kg of Pb along with application of growth promoter bacteria, enzyme's activity leads to 172.2 (u/mg.pr). GPX's activity in Brassica napus The results of variance analysis showed significant effect of both Pb and bacteria factors and their interaction effect on the activity of GPX (P<0.01) (Table 2). Discussion Under stress condition, active O2 increases in plant. In such condition, plant uses different mechanism for eliminating different types of active O2. On the basis of this fact, SOD's activity under Pb and bacteria treatments was considered in 2 plants of Hordeum vulgare and Brassica napus. Fig. 1. Interaction effect of Pb and bacteria on SOD activity in Hordeum vulgare. SOD catalyzes reaction of transformation O2 - to H2O2 and O2 (Lopez et al., 2005). , between these 2 plants showed that Brassica napus secreted more SOD's activity in presence of growth promoter bacteria then Hordeum vulgare. In present study, by increasing Pb heavy metal in growth environment, activity of SOD, which transforms O2 to H2O2, will decrease. In maximum amount of Pb in soil, released of SOD in Brassica napus was 1028.8 (u/mg.pr) and in control treatment this amount reached to 1615.3 u/mg.pr this amount is 61% more than enzymes' activities of Hordeum vulgare. SOD's activity in Hordeum vulgare was in medium amount. It seems that activity of SOD is the response to harmful effects of produced oxygen's that are results of application of growth promoter bacteria. The highest amount of activity of these enzymes was related to the lowest concentration of Pb in the soil. Totally, enhancement of Pb concentration in soil of both plant's types led to reduction of SOD's activity. Sharma and Dubey (2005) and Garnczarska and Ratajczak (2000) reported that SOD's activity will increase under the poison level of Pb. Enhancement of SOD and CAT's activity in Brassica napus in comparison with Hordeum vulgare indicated that enzymes respond to produced free-radicals in plants under the poison level of Pb, because Brassica napus absorbed more Pb in its root and aero organs. Therefore, it seems that higher productions and activity of these enzymes is considered as a defendant mechanism against this element which is attributed to resistance and strategy of plant. Probably these enzymes because digesting more O2 - than Hordeum vulgare, and growth promoter bacteria which are effective in absorbing more heavy elements in the root, are also effective in enhancement of enzymes' amount under different level of Pb. Fig. 2. Interaction effect of Pb and bacteria on SOD activity in Brassica napus CAT activity in Hordeum vulgare. CAT is on enzyme which will be active under oxide stress. This enzyme is enable to digested eliminate H2O2 (Khatun et al., 200). A comparison between CAT's activity under poison amount of Pb, growth promoter bacteria treatment indicated that both above treatments had significant increase than control treatment. Although both treatment increased CAT's activity this enhancement wasn't equal for both plant's types. In Brassica napus CAT's activity was more than Hordeum vulgare.
  • 6. 169 Nooralvandi et al. Int. J. Biosci. 2014 Hordeum vulgare had the lowest amount of released enzymes. Enhancement of Pb concentration also led to reduction of CAT's activity in both plant's types. CAT had 30% reduction in 750 mg/kg soil comparison with control. H2O2 which is poison product of SOD's yield is used or transformed by CAT (Garnczarska and Ratajczak, 2000). Fig. 3. Interaction effect of Pb and bacteria on CAT's activity in Hordeum vulgare. GPX preserves lipid membrane against oxide damages (Mashhadi Akbar Boojar and Goodarzi, 2007). Enhancement of enzymes activity under bacteria treatment indicates that probably activities of CAT and GPX prevent accumulation of H2O2, since it transformed O2 - to H2O2 by SOD yields and transformed O2 - poisoning effects to H2O and O2. Therefore, by making a balance between ROS production and eliminating them, systems survival is guaranteed, since ROS is poisoning and should separated by enzymes activity, enhancement of GPX activity had an important role in reduction of H2O2 through GSH activity (Khatun et al., 2008). It seems that synthesis of Glutathione was similar in both plants' types. Fig. 4. Interaction effect of Pb and bacteria on CAT's activity in Brassica napus GPX's activity in Hordeum vulgare Fig. 5. Interaction effect of Pb and bacteria on GPX activity in Brassica napus Comparison between control plants and those which are grown in Cu environment shows that enhancement of GPX enzymes is the results of increasing concentration of Ca. As it was mentioned, antioxidant enzymes always haven't enhancement under oxidant stress of heavy metals, and they show different reaction due to different plant's types, since antioxidant components that are existed in plants' oils have different yield and their mechanism mostly is related to mixture and condition of experimental system (Wong et al., 2005). References Ali BM, Vajpayee P, Tripathi RD, Rai UN, Singht SN, Singhgh SP. 2003. Phytoremediation of lead, nickel, and copper by Salix acmophylla boiss: Role of Antioxidant Enzymes and Antixidant substances. Bull. Environ. Contam. Toxicol. 70, 462- 469. http://dx.doi.org/10.1007/s00128-003-0009-1. Boularbah A, Schwartz C, Bitton G, Aboudrar W, Ouhammou A, Morel JL. 2006. Heavy metal contamination from mining sites in south Morocco: 2. Assessment of metal accumulation and toxicity in plants. Chemosphere 63, 811- 817. http://dx.doi.org/10.1016/j.chemosphere.2005.07.07 . Brunet J, Repellin A, Varrault G, Terrync N, Zuily-fodil Y. 2008. Lead accumulation in the roots of grass pea (Lathyrus sativus): anovel plant for phytoremediation systems?. C.R Biologies, 331, 859- 864.
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