The effects of different disease-resistant cultivars of banana on rhizosphere microbial communities...
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R E S EA RCH L E T T E R
The effects of different disease-resistant cultivars of banana onrhizosphere microbial communities and enzyme activities
Jianbo Sun, Ming Peng, Yuguang Wang, Wenbin Li & Qiyu Xia
Key Laboratory of Biology and Genetic Resources of Tropical Crops, Ministry of Agriculture, Institute of Tropical Bioscience and Biotechnology,
Chinese Academy of Tropical Agricultural Sciences, Long hua District, Hai kou, Hai nan Province, China
Correspondence: Ming Peng, Key
Laboratory of Biology and Genetic Resources
of Torpical Crops, Ministry of Agriculture,
Institute of Tropical Bioscience and
Biotechnology, Chinese Academy of Tropical
Agricultural Sciences, No. 4, Xue yuan Road,
Long hua District, Hai kou, Post code
571101, Hai nan Province, China.
Tel.: +86 0898 66890981; fax: +86 0898
66988081; e-mail: [email protected]
Received 23 May 2013; accepted 3 June
2013. Final version published online 8 July
2013.
DOI: 10.1111/1574-6968.12192
Editor: Yaacov Okon
Keywords
banana; rhizosphere; bacterial community;
T-RFLP; real-time PCR; enzyme activity.
Abstract
To understand the mechanism of soil microbial ecosystem and biochemical
properties in suppressing soilborne plant diseases, the relationship between the
soil rhizosphere microbial communities, hydrolase activities, and different dis-
ease-resistant cultivars was investigated. There were statistically significant dif-
ferences in microbial diversity in the rhizosphere soil between the disease-
tolerant cultivar Fj01 and susceptible cultivar Baxi. The rhizosphere soil of Fj01
showed a trend of higher microbial diversity than that of Baxi. At the same
growth stage, the similar trends of variation in microbial community diversity
between the two different cultivars were observed. The bacterial community
abundance in rhizosphere soil from the two banana cultivars was quantified by
real-time PCR assays. The size of the rhizosphere bacterial population from the
Fj01 was significantly larger than that from the Baxi during the growing stage
from July to September. The activities of urease and phosphatase were analyzed
to study the effects of the two banana cultivars to soil ecosystem functioning.
Urease activity was significantly higher in the rhizosphere soil of Fj01 than that
of Baxi in the period from July to September. However, phosphatase activity
showed no significant difference between the two different rhizosphere soils.
Introduction
Fusarium wilt of banana is a serious and destructive dis-
ease worldwide. It is a vascular wilt disease caused by the
soilborne fungus Fusarium oxysporum f.sp. cubense (Peng
et al., 1999). There are no effective chemical control mea-
sures currently, and the resistance breeding is tedious. It
is therefore necessary to find effective and integrated sus-
tainable methods to control Fusarium wilt of banana. Soil
microbial ecosystem and biochemical properties are seen
to be critical to the maintenance of soil health and quality
(Naeem et al., 1994; Garbeva et al., 2004), and good soil
quality may be helpful to improve the capacity of the dis-
ease suppressiveness (Abawi & Widmer, 2000; Peters
et al., 2003). However, little is known about the relation-
ship between the rhizosphere soil microbial ecosystem,
biochemical properties of different disease-resistant culti-
vars, and the suppressing of Fusarium wilt of banana.
The rhizosphere is a special micro-ecosystem, which
includes plant, soil, and microorganism; meanwhile, it is
the gateway through which soilborne pathogens enter the
crop. Plant species and genotype are significant factors
determining the structure and composition of microbial
communities in the rhizosphere (Smalla et al., 2001;
Garbeva et al., 2004; Mazzola, 2004).
Several studies have shown a correlation between the
microbial communities in the rhizosphere and the disease
caused by soilborne pathogens (Workneh & van Bruggen,
1994; Mazzola & Gu, 2002). One possible strategy is the
management of the diversity and the structure of rhizo-
sphere microbial communities and, as a result, enhances
the antagonism to pathogens activity, leading to a
decrease in plant disease caused by soilborne pathogens.
Various approaches have been developed to analyze
microbial ecosystems in soil microbial communities.
Traditional culture-based methods are based on isola-
FEMS Microbiol Lett 345 (2013) 121–126 ª 2013 Federation of European Microbiological SocietiesPublished by John Wiley & Sons Ltd. All rights reserved
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tion–cultivation approaches. However, only a small
fraction of the microbial cells in soil are cultivable. Alter-
native approaches based molecular fingerprinting meth-
ods provide a complex view of the microbial community
without the need for isolation and cultivation. Terminal
restriction fragment length polymorphism (T-RFLP) anal-
ysis is one of the most rapid and powerful methods for
comparing microbial communities. It has been shown to
be an ideal technique for the rapid analysis of microbial
diversity (Bankhead et al., 2004; Ausec et al., 2009). Ter-
minal restriction fragments of T-RFLP analysis are
detected by fluorescence, and the result of scanning can
be compared with the data stored in databases. In this
research, the microbial diversity was determined by
T-RFLP profiles of the 16S rRNA gene obtained from dif-
ferent soil samples.
Real-time PCR has been used for the detection and
quantification of bacteria in various environments (Becker
et al., 2000). In this study, real-time PCR is used for the
quantification of soil bacterial community.
Soil enzyme activities have been considered as indicators
of soil quality (Bastida et al., 2008). Soil microbial commu-
nities are the primary source of soil enzymes. Here, we ana-
lyzed the enzyme activities of urease and phosphatase to
access functional changes in the rhizosphere microbial
community between two cultivars of banana.
The objective of this research was to compare the
bacterial community structure and hydrolase activities in
the rhizosphere of banana between two different disease-
resistant cultivars against Fusarium wilt disease at differ-
ent growth stages.
Materials and methods
Soil sampling
The samples were collected from the experimental field in
Chinese Academy of Tropical Agricultural Sciences,
Hainan Province, China. The soil type is tropical red loam.
The experiments were carried out during the 2010
growing season. Two cultivars of ‘Baxi’ and ‘Fj01’ were
grown in a randomized plot design with three replications
per cultivar, each containing four plants. The ‘Baxi’ and
‘Fj01’ were susceptible and disease-tolerant cultivars,
respectively.
The plantlets of banana were transplanted into the field
in February. After this, soil samples from the rhizosphere
of banana were collected every month until September.
Samples collected from the cultivars of Baxi and Fj01 at
different month were named B1–B7 and F1–F7 in time
order, respectively.
Soil cores were taken at c. 20 cm from the tree and at
30 cm depth. Each sample was collected at five cores per
tree and three plants per plot. Pieces of root from the
composite sample were picked out, and their tightly
adherent soil was collected. The rhizosphere soil was
homogenized and sieved to remove possible root frag-
ments. Soil samples were stored at �20 °C for subsequent
molecular analyses.
Soil DNA extraction and PCR amplification of
16S rRNA genes
Total DNA was extracted from 500 mg of soil sample
using the Fast DNA SPIN kit for soil (Qbiogene). The
purity and concentration of the DNA were determined
using a spectrophotometer (Jasco, Tokyo, Japan).
For the T-RFLP analysis, the 16S rRNA gene was ampli-
fied with the primers 27F (5′-AGAGTTTGATCCTGGCT-CAG-3′) and 1492R (5′-GGTTACCTTGTTACGACTT-3′;Culman et al., 2006). The 5′ end of the 27F primer was
labeled with 6-carboxyfluorescein (6-FAM) for fluorescent
detection.
The PCR mixtures contained 0.1 lM of each primer,
30 ng of template DNA, 19 PCR buffer, 2.0 mM MgCl2,
200 lM dNTP mix, and 2.5 U of Taq DNA polymerase
(Sangon Biotech, China).
DNA amplification was performed in a thermocycler
(Biometra, Germany) under the following conditions:
initial denaturation at 95 °C for 5 min followed by 30
cycles of denaturation at 94 °C for 1 min, annealing at
52 °C for 1 min, and extension at 72 °C for 1.5 min,
with a final extension at 72 °C for 7 min. Three indepen-
dent PCRs were performed, combined for each, and puri-
fied using a Qiagen gel extraction kit (Qiagen, Germany).
Approximately 200 ng of fluorescently labeled PCR
products was digested with the restriction enzyme HaeIII
at 37 °C for 3 h. The reaction mixtures contained 8 lL of
PCR product, 2.0 lL of 109 restriction enzyme buffer,
3 U of HaeIII, and ultrapure water to a final volume of
20 lL. Digestion products were verified on a 1.5% agarose
gel in 1% TBE buffer. The digested DNA was purified
using a gel extraction kit (Omega). The Three replicates of
the digestion product from each sample were mixed.
T-RFLP analysis
Terminal restriction fragments (T-RFs) were separated on
an ABI 373 sequencer (Applied Biosystems). The peak
results were analyzed using GENEMAPPER software 4.0
(Applied Biosystem). In each sample, only peaks over a
threshold of 100 fluorescence units were considered for
further analysis. The relative abundance of each T-RF was
calculated as a relative percentage by calculating the ratio
of a given peak area to the total peak area within one
sample. T-RFs with relative abundance below 2% were
ª 2013 Federation of European Microbiological Societies FEMS Microbiol Lett 345 (2013) 121–126Published by John Wiley & Sons Ltd. All rights reserved
122 J.B. Sun et al.
regarded as background noise and excluded from analysis.
T-RFs smaller than 50 bp or larger than 600 bp were
excluded from the analysis.
Quantification of bacteria by real-time PCR
Soil samples from the rhizosphere were collected every
2 months from March to September. Total soil DNA was
extracted in the same way as described in Quantification
of bacteria by real-time PCR and using 1 lL of 50-fold
diluted extracted DNA (1–7 ng) as template.
Abundances of bacteria were determined by quantita-
tive real-time PCR analysis of 16S rRNA gene. Each reac-
tion was performed in a 25-lL volume containing
12.5 lL of SYBR� Green PCR Master Mix, 1 lL sample
DNA, and 20 lmol of each primer. The primers used for
the amplification were as follows: 338F: 5′-CCT ACG
GGA GGC AGC AG-3′ and 518R: 5′-ATT ACC GCG
GCT GCT GG-3′ (Seghers et al., 2003).Real-time PCR was performed on a MX3000P real-time
PCR machine (Stratagene, Cedar Creek, TX). Quantitative
PCR were performed under the following conditions:
95 °C for 3 min and 40 cycles of 95 °C for 30 s, 53 °Cfor 40 s, and 72 °C for 1 min. Three independent quanti-
tative PCRs were performed for each soil sample.
The bacterial 16S rRNA gene standard was amplified
with the primers 27F: 5′-AGA GTT TGA TCC TGG CTC
AG-3′ and 1492R: 5′-GGT TAC CTT GTT ACG ACT T-3′(Ahn et al., 2009). The amplified product was then cloned
into the pGEM-T Easy Vector (Promega). Standard curves
were generated with serial dilution series of quantified
plasmid DNA.
Soil enzyme activities in rhizosphere soil
Soil samples from the rhizosphere were collected as the
methods described in Quantification of bacteria by real-
time PCR. Phosphatase activity was determined using p-ni-
trophenyl phosphate disodium (0.115 M) as substrate, and
the released p-nitrophenol (PNP) by phosphatase was mea-
sured spectrophotometrically at 410 nm (Ros et al., 2006).
Urease activity was determined using phenol–sodiumhypochlorite colorimetry (Wang et al., 2009). The released
NHþ4 was measured at a wavelength of 578 nm.
Data analysis
To evaluate the diversity indices of each community, each
different OTU was treated as a different species, and the
peak area for individual T-RFs was normalized to percent
of the total fingerprint area as a relative abundance.
The Shannon–Wiener and Shannon evenness index
were used to evaluate the richness and evenness of each
sample. The Shannon–Wiener index was calculated from
(H′) = �∑pi ln pi, where pi is the proportion of the peak
area for each T-RF out of the total peak area for all
T-RFs. The evenness index was calculated from (E′) = H/
Hmax, where S is the number of T-RFs within a given
profile, Hmax = ln S.
ANOVA was used to analyze the statistical significance of
the data, and multiple comparisons of significant differ-
ences were calculated using Tukey’s t-test at the 5% level
with SPSS 11.5 (SPSS for Windows, version 11.5).
Results
T-RFLP profiles
Bacterial community profiles of the rhizosphere microbial
communities in two different cultivars were analyzed
using the T-RFLP fingerprints of the 16S rRNA genes.
T-RFs with a relative abundance of more than 2% were
considered. For this analysis, a similar trend in diversity
between samples from the disease-tolerant (Fj01) and sus-
ceptible cultivars (Baxi) was observed. Two months after
transplantation, both of the diversities in the rhizosphere
of the two different cultivars were all increased. After this,
the diversities decreased for both cultivars up to
5 months after transplantation and then increased slowly
(Fig. 1). During the tested growing stage, the diversity of
samples in Fj01 was significantly (P < 0.05) higher than
that in the cultivar of Baxi (Table 1).
In the period from March to June, differences in diver-
sities of the T-RF profiles in the two cultivars were also
compared. Some T-RFs were present only at one specific
cultivar. For example, the T-RFs of 73, 208, and 291 bp
were present only in the samples of Fj01. In contrast, the
T-RFs of 196 and 307 bp were only observed in the sam-
ples of Baxi.
Five months after transplantation, the lowest diversities
of samples in two different cultivars were all observed.
During this period, seven of the T-RF profiles were
common to all the samples of Fj01 (64, 73, 193, 208, 231,
Fig. 1. Comparison of the soil diversity in rhizosphere of Baxi and
Fj01. The numbers 1–7 in x-axis indicate the different soil samples
from the rhizosphere collected every month.
FEMS Microbiol Lett 345 (2013) 121–126 ª 2013 Federation of European Microbiological SocietiesPublished by John Wiley & Sons Ltd. All rights reserved
Effect of banana cultivar on rhizosphere soil 123
258, and 291 bp). However, only three T-RFs (72, 196,
and 232 bp) were present in all the samples of Baxi.
In addition, the first five T-RFs and their relative
abundance of each sample were analyzed according to the
T-RF profile (Table 2). In the samples collected from the
Fj01, the T-RFs of 73, 291, 193, 233, 64, 231, and 217 bp
were detected as the dominant components with the
relative abundance of 12.7%, 14.1%, 12.4%, 11.7%,
11.6%, 16.3%, and 14.6% in the different months, respec-
tively. In contrast, samples collected from the susceptible
cultivar in the different months were dominated by 231,
231, 231, 230, 72, 206, and 217 bp and with the relative
abundance of 14.0%, 10.9%, 14.3%, 21.8%, 15.0%,
16.1%, and 25.3%, respectively.
Abundance of bacteria in rhizosphere soil
Rhizosphere soil bacterial community abundance was
detected by real-time PCR assays. The sizes were expressed
as 16S rRNA gene copy numbers. Rhizosphere soil bacte-
rial abundance of Fj01 was higher during the tested grow-
ing stage than that of Baxi. Especially in the period from
July to September, The size of the rhizosphere bacterial
population from the cultivar Fj01 was significantly larger
than that from the cultivar Baxi (Fig. 2).
Soil enzyme activities
The activities of enzymes in the rhizosphere soil are shown
in Table 3. From May to September, the activity of urease
in the rhizosphere soil of Fj01 was higher than that of Baxi;
furthermore, there were significant differences between
Table 1. Diversity indices of the bacterial communities in the
rhizosphere soil based on the data from T-RFLP analysis
Samples Shannon index Evenness
Soil samples from the cultivar
of BaxiaB1 2.63 0.97
B2 2.67 0.99
B3 2.50 0.98
B4 2.47 0.94
B5 2.28 0.99
B6 2.32 0.93
B7 2.35 0.91
Soil samples from the
cultivar of Fj01bF1 2.58 0.98
F2 2.75 0.97
F3 2.64 0.97
F4 2.55 0.97
F5 2.35 0.95
F6 2.49 0.97
F7 2.52 0.98
Different superscript lowercase letters indicate significant (P < 0.05)
differences (univariate analysis of variance). B1–B7 and F1–F7: samples
collected from the cultivars of Baxi and Fj01 at different month,
respectively.
Table 2. Distribution and relative abundance of the first five dominant T-RFs after restriction with HaeIII
Samples T-RF size (bp) [relative abundance (%)]
B1 231 (14.0) 196 (10.7) 307 (8.9) 328 (8.9) 216 (7.8)
B2 231 (10.9) 196 (8.4) 329 (8.2) 216 (8.1) 291(8.1)
B3 231 (14.3) 196 (11.7) 307 (9.8) 232 (8.9) 291 (8.8)
B4 230 (21.8) 330 (12.4) 216 (8.8) 196 (8.3) 307 (7.2)
B5 72 (15.0) 188 (12.4) 66 (11.7) 90 (10.3) 231 (10.3)
B6 206 (16.1) 201 (14.3) 205 (14.0) 233 (13.5) 193 (7.9)
B7 217 (25.3) 231 (8.9) 216 (8.5) 291 (7.6) 307 (7.5)
F1 73 (12.7) 208 (10.8) 296 (10.0) 231 (8.9) 167 (8.0)
F2 291 (14.1) 231 (9.9) 216 (7.5) 64 (7.3) 234 (6.9)
F3 193 (12.4) 73 (11.7) 217 (8.7) 208 (8.0) 168 (7.6) 296 (7.6)
F4 233 (11.7) 193 (10.5) 216 (10.5) 73 (9.8) 208 (9.3)
F5 64 (11.6) 182 (10.5) 146 (10.2) 219 (9.7) 138 (9.6)
F6 231 (16.3) 197 (12.6) 72 (8.4) 74 (8.1) 193 (7.9)
F7 217 (14.6) 90 (10.1) 221 (9.8) 174 (8.5) 170 (8.0)
The relative abundance is the ratio of a given peak area to the sum of all the peak areas in one sample. B1–B7 and F1–F7: samples collected
from the cultivars of Baxi and Fj01 at different month, respectively.
Fig. 2. Quantification of 16S rRNA gene copy numbers in samples
from cultivars Fj01 and Baxi at different growth stages. Different
letters in the same column indicate significant differences at P < 0.05
(Tukey’s test).
ª 2013 Federation of European Microbiological Societies FEMS Microbiol Lett 345 (2013) 121–126Published by John Wiley & Sons Ltd. All rights reserved
124 J.B. Sun et al.
Fj01 and Baxi during the growing stage from July to Sep-
tember. However, there were no statistically significant dif-
ferences in the activities of phosphatase in rhizosphere soil
between Fj01 and Baxi (Table 3).
Discussion
Rhizosphere is a special micro-ecosystem of plant–microorganism interactions. Rhizosphere bacterial com-
munities play an important role in suppressing soilborne
plant diseases and promoting plant growth.
Plant roots release a broad range of compounds into
the surrounding soil. The composition of root exudates is
affected by the plant species and developmental stage (Di
Cello et al., 1997; Siciliano et al., 1998; Yang & Crowle,
2000; Dunfield & Germida, 2001). These root exudates
create unique environments for the microorganisms living
in the rhizosphere. There are differences in utilization of
different compositions of root exudates by the microor-
ganisms, and thus, different rhizosphere communities
were formed (Rumberger et al., 2004; Orlando et al.,
2007).
In this study, significant differences in rhizosphere bac-
terial community structure and diversity of banana in
relation to different disease-resistant cultivars were
observed. One possible explanation for the result might be
due to the difference in root exudates released by the dif-
ferent cultivars. These compounds provided potential car-
bon source to promote microbial growth, thus leading to
different composition and diversity in their rhizosphere.
Seasonal shifts in microbial diversity in the rhizosphere
have also been observed in some studies. Rumberger et al.
(2007) revealed that in the rhizosphere of apple trees, the
composition of bacterial communities was highly variable
in different seasons. In this study, the impact of different
growth stage on bacterial diversity in the rhizosphere was
also observed. With the development of growth stage, the
diversities of the two cultivars in rhizosphere were
decreased.
Several studies have also indicated the relationship
between the plant diseases and the diversity of soil micro-
bial communities. For example, P�erez-Piqueres et al.
(2006) showed that differences in soil suppressiveness to
Rhizoctonia solani disease were related to differences in
microbial composition. Using the T-RFLP fingerprints,
Rotenberg et al. (2007) revealed that the incorporating of
paper mill residuals into soil may improve the bacterial
communities in soil and thus increase the soil’s ability to
suppress root rot disease. In this study, the disease-
tolerant cultivar (Fj01) showed a higher bacterial diversity
in the rhizosphere than that of the susceptible cultivar
(Baxi) during the tested growing stage in general. The
results indicated the relationship between bacterial diver-
sity and the suppressiveness to soilborne diseases in rhi-
zosphere of banana.
Urease and phosphatase play important roles in soil
organic nutrient cycling and are important indicators of
soil quality (Dick et al., 2000). Soil enzyme activities are
greatly affected by root secretion and soil microorganisms
(Ros et al., 2006). In the present study, the difference of
soil urease activity between the two banana cultivars
could be attributed to the changes in soil microbial group
composition and root secretion. The higher activity of
urease increased the ability of organic nutrient cycling in
soil and thus provided a better nutrition environment for
banana growth.
The mechanisms of plant diseases caused by soilborne
pathogens are multiple and complex. A higher biodiver-
sity and good biochemical property have been associated
with better soil quality and thus a greater capacity in
suppressing soilborne diseases. In this study, the disease-
tolerant cultivar (Fj01) showed a significant higher micro-
bial diversity and urease activity compared with the
susceptible cultivar (Baxi). This may be one of the impor-
tant reasons why the fungus is more difficult to infect the
disease-tolerant cultivar compared with the susceptible
cultivar of banana.
Acknowledgement
This work was financially supported by the grant no.
200903049-2 and ITBB110305.
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FEMS Microbiol Lett 345 (2013) 121–126 ª 2013 Federation of European Microbiological SocietiesPublished by John Wiley & Sons Ltd. All rights reserved
Effect of banana cultivar on rhizosphere soil 125
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ª 2013 Federation of European Microbiological Societies FEMS Microbiol Lett 345 (2013) 121–126Published by John Wiley & Sons Ltd. All rights reserved
126 J.B. Sun et al.