New Biotechnology Volume 30, Number 6 September 2013
RESEARCH PAPER
Research Paper
Inoculation with microorganisms of
Lolium perenne L.: evaluation of plant
growth parameters and endophytic
colonization of roots
Francesca Gaggı̀a, Loredana Baffoni, Diana Di Gioia, Mattia Accorsi,
Sara Bosi, Ilaria Marotti, Bruno Biavati and Giovanni Dinelli
Department of Agricultural Sciences, Alma Mater Studiorum-University of Bologna, v.le Fanin 44, Bologna 40127, Italy
Turfgrasses are not only designed for recreation activities, but they also provide beneficial
environmental effects and positively influence the human wellness. Their major problems are
predisposition to tearing out and microbial diseases. The aim of this study was to investigate whether the
inoculation of microorganisms can be effective to improve plant growth and root development of
perennial ryegrass, to evaluate new sustainable practice for green preservation. A microorganism-based
commercial product was used to amend hydroponically grown Lolium perenne L. and results compared
with the use of the same filtered product, a phytohormone solution and an untreated control. Plants
were grown for five weeks, shoots cut and measured at one-week interval and, at the end, roots were
measured for length and weight. Shoot resistance to tearing out was also tested. Moreover, the main
microbial groups present in the product were characterized and the microbial profile of sand and root
samples was investigated by PCR-DGGE. The plants treated with the product showed an increased
resistance to tearing out with respect to other treatments and roots were longer with respect to the
control. Microbial analyses of the product evidenced bacterial and yeast species with plant growth
promoting activity, such as Stenothrophomonas maltophilia, Candida utilis and several Lactobacillus
species. Some Lactobacillus strains were also found to be able to colonize plant roots. In conclusion, the
treatment with microorganisms has a great potential for the maintenance and increased performance of
turfgrass surfaces.
Introduction
Turfgrasses are the primary plant covers for football fields, golf
courses, home lawns, parks, and roadsides and are typically
thought of for recreation and aesthetic value. However, they also
provide a valuable environmental service by preventing soil erosion from wind and rain and improving soil absorption of water
[1]. The turfgrass industry has grown rapidly since the 1970s when
lands were developed to accommodate an expanding suburban
population and to meet the increasing request of sport surfaces.
Unfortunately, high standards for aesthetics and playability,
necessarily rely on preventive chemical treatments (e.g. fertilizers,
Corresponding author Baffoni, L. (loredana.baffoni@unibo.it)
herbicides, fungicides). Some cultural practices can promote, for
example, nitrogen availability but simultaneously increase susceptibility to diseases, such as Phytium blight and brown patch [2].
A new concept on turfgrass management is required to avoid
chemical treatment abuses as well as a biodiversity reduction.
Bio-control and other sustainable intervention measures are currently being studied in turf systems to improve turfgrass management in an environmental sustainable way [3].
The concept of plant–microbe interaction to promote plant
growth and to combat diseases dates back in the 1980s [4] and,
recently, a renewed interest has been dedicated to the use of
microbial inoculants [5]. A wide range of bacteria and fungi has
been the subject of considerable studies and strains belonging to
1871-6784/$ - see front matter ß 2013 Elsevier B.V. All rights reserved. http://dx.doi.org/10.1016/j.nbt.2013.04.006
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Research Paper
different genera have been isolated both from the rhizosphere and
inside plant tissues. Numerous authors reported the plant growth
promoting abilities of such microorganisms as well as their protective role against plant pathogens. The improved cycling of
nutrients and minerals such as nitrogen, phosphate, indole acetic
acid (IAA) production [6], the production of siderophores [7],
stomatal regulation and modification of root morphology are
among the beneficial mechanisms associated with their presence.
Additionally, these microorganisms can produce secondary metabolites including antibiotics, antifungal, antiviral, insecticidal and
immuno-suppressant agents [8]. Diseases of fungal, bacterial, viral
origin and in some instances even damages caused by insects and
nematodes can be reduced following inoculation with bacterial/
fungal endophytes [9–12].
This work is focused on the effect of inoculation of a commercial
product containing a mixture of microorganisms on hydroponically grown perennial ryegrass (Lolium perenne L.), in comparison
with the filtered product, a plant hormone-rich (HRM) solution
and an untreated control. Perennial ryegrass is a cool-season
turfgrass species that is widely used on home lawns, sports fields,
and golf courses due to its rapid establishment and excellent
trampling tolerance. The objective of this study was to collect
data on aboveground and underground biomass to evaluate the
efficacy of the bio-inoculum; a special attention was given to root
development and resistance to tearing out, representing a crucial
issue for the maintenance of lawns and sport fields. Moreover, a
combination of microbiological and molecular analyses has been
applied to characterize and quantify the main microbial groups
declared in the label (lactobacilli, yeasts and aerobic bacteria).
PCR-DGGE analyses were also performed to investigate differences
in the microbial profile of sand and root samples and the endophytic ability of inoculated microorganisms.
Materials and methods
Seed source and plant growth condition
Perennial ryegrass (L. perenne L.) seeds used in this study were
provided by Fratelli Ingegnoli (Milan, Italy). An aggregate hydroponic system with complete recycling of nutrient solution was
used. Seeds were sown in pots of 10 cm diameter 12 cm height,
filled with a bottom layer of 2 cm of pumice stone and a sand layer
on top. The nutrient solution was prepared according to Hoagland
and Arnon [13] and diluted 1:1 (v/v) with distilled water. Plant
water uptake was weekly compensated with fresh nutrient solution. The re-circulating nutrient solution was automatically
pumped by a drip irrigation system in daily irrigations. Plants
were placed in a growth chamber set at 248C and 70% relative
humidity (RH) during the day, and 208C and 50% RH in night
conditions. Light was supplemented to a 12-hour photoperiod
with artificial illumination at 550 mmol photons m 2 s 1.
Treatments and growth measurements
The efficacy of the commercial product EM11 (Punto EM, Sanremo, Italy), composed of a mixture of microorganisms, water and
molasses, was evaluated.
The experimental plan was a completely randomized design
with four treatments, each consisting of eight pots placed in a
random position on a shelf in the growth chamber. Treatments
consist of distilled water (control – CTR), activated EM11 (EM),
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New Biotechnology Volume 30, Number 6 September 2013
filtered/activated EM11 (F-EM) and a commercial plant hormone-rich solution (HRM) containing gibberellic acid (GA3)
(1.65 g/l) and naphthalene acetic acid (NAA) (3.30 g/l) (Fast-Speed
Top, Agrisystem, Lamezia Terme, Italy). Before using the product,
an activation step is required, which consists in the addition of 5%
(v/v) EM11 and 5% (v/v) molasses in water followed by incubation at 35 18C for five days. To prepare the filtered solution, the
activated product was filtered through a 0.20 mm nylon filter
(Millipore). Both activated and filtered solutions were diluted
1:500 (v/v) in water, HRM was diluted 1:2000 (v/v), and used in
the irrigation system.
During the course of the experiment, plants were cut 2 cm above
the soil level with a cutting interval of one week, for five weeks.
After each collection, the shoots (stems + leaves) were measured
(cm) and weighed (fresh and dry weight); total shoot length (SL),
total shoot fresh (SFW) and dry weight (SDW) were determined as
sum of all measurements. At the end of the experiment, roots were
sampled, washed and measured for length (RL), fresh (RFW) and
dry weight (RDW). Finally, shoot resistance to tearing out (TR) was
tested by a dynamometer (PCE Instrument, Lucca, Italy). The
method employed consisted of measuring the load (g) necessary
to tear out a fresh shoot sample.
Enumeration, isolation, purification and maintenance of
microorganisms
Viable cell counts were carried out to determine the bacterial
concentration of the product before and after the activation step.
10 ml of the two solutions were suspended in 90 ml sterile water,
and serial dilutions plated on selected media. Lactobacilli were
enumerated by inoculation on de Man, Rogosa and Sharpe Broth
(MRS, Merck, Darmstadt, Germany) containing 0.2% (w/v) sorbic
acid (Sigma–Aldrich, Milan, Italy) and 0.1% (w/v) cycloheximide
(Sigma–Aldrich) to inhibit growth of yeasts, and incubated anaerobically (2–3 days, 308C). Aerobic mesophilic bacteria were enumerated by inoculation on Nutrient Agar (NA, Merck) containing
0.1% (w/v) cycloheximide and incubated for 3 days at 308C. Yeasts
were enumerated by inoculation on Sabouraud Dextrose Agar
(SDA, Merck) containing 0.1% (w/v) chloramphenicol (Sigma–
Aldrich) after 3–5 day incubation at 258C. Each analysis was
conducted in triplicate. Following incubation the number of
colony forming units (cfu)/ml was recorded and means and standard deviations were calculated. An average of 25 colonies from
the activated product were selected from each medium, re-streaked
and purified for further characterization. For long-term storage
purified isolates were stored at 808C.
Phenotypic characterization of lactobacilli, aerobic and yeasts
isolates
Presumptive lactobacilli isolates were characterized on the basis
of cell morphology, Gram staining, catalase and oxidase reactions. The carbohydrate fermentation profiles were determined
using the commercial API1 50CH test (BioMérieux, Marcy
l‘Etoile, France), followed by APILAB software (version 5.1)
analyses. Aerobic bacteria were also studied considering cell
morphology, Gram staining, catalase and oxidase reactions.
Concerning yeasts, cells grown for 3–5 days on Sabouraud Dextrose Broth (SDB, Merck) were identified using the commercial
API1 C-AUX test (BioMérieux).
New Biotechnology Volume 30, Number 6 September 2013
Cells were harvested from 2 ml of overnight cultures and used for
chromosomal DNA extraction, using the Wizard1 Genomic DNA
Purification Kit (Promega, Madison, USA). Genus-specific PCR was
performed according to Walter et al. [14] to confirm the affiliation
to the genus Lactobacillus. Molecular biology-based grouping of
lactobacilli and aerobic isolates was performed by ERIC-PCR with
primers ERIC-1 (50 ATGTAAGCTCCTGGGGATTCAC-30 ) and ERICII (50 -AAGTAAGTGACTGGGGTGAGCG-30 ) [15]. After electrophoresis (2% w/v agarose gel at 50 V for four hours), gels were
stained with ethidium bromide and visualized with the gel documentation system Gel DocTM XR (Bio-Rad, Hercules, CA, USA).
Images were elaborated with ImageLab software (Bio-Rad) and a
binary matrix has been constructed. Mega 5.1 was employed to
obtain the phylogenetic trees based on neighbor-joining method
[16].
DNA extraction
For PCR-DGGE analysis, bacterial DNA was extracted from sand
and root samples of the four treatments, and from the activated
product. Root samples were previously surface-sterilized with consecutive washes in ethanol 70%, water, NaOCl (2%) and water (3
times) [17], snap frozen in liquid nitrogen and then ground by
mortar and pestle. Metagenomic DNA from approximately 250 mg
sand and 100 mg of roots was extracted using the PowerSoil DNA
kit (Mo Bio Laboratories, Carlsbad, CA, USA) according to the
manufacturer’s instructions with some adjustments. In particular,
5 ml of mutanolysin (100 U/ml, Sigma–Aldrich) and 195 ml of
lysozyme (50 mg/ml, Sigma–Aldrich) were added to the soil and
root powder in the bead solution supplied with the kit. The
suspension was then incubated at 378C on a rotary shaker for
two hours, before chemical (SDS-containing solution) and
mechanical (bead beating on vortex at maximum speed for
10 min) cell lysis. DNA was eluted in 100 ml of TE buffer pH 8.0.
Bacterial DNA was extracted from the activated product, according
to Iacumin et al. [18]. The purity and concentration of extracted
DNA were determined by measuring the ratio of the absorbance at
260 and 280 nm (Infinite1 200 PRO NanoQuant, Tecan, Mannedorf, Switzerland). The DNA was stored at 208C.
16S rRNA gene PCR-DGGE analysis
For bacterial PCR-DGGE analysis on sand and root samples, PCR
amplification of 16S rDNA was performed with universal
primers 357f with GC clamp (50 -CGCCCGCCGCGCCCCGCGCCCGGCCCGCCGCCCCCGCCCCCTACGGGAGGCAGCAG-30 )
and 907r (50 -CCGTCAATTCCTTTGAGTTT-30 ) [19]. A further PCRDGGE targeting LAB (Lactic Acid Bacteria) and using primers Lac1f
(50 -AGCAGTAGGGAATCTTCCA-30 ) and Lac2r with GC clamp (50 CGCCCGGGGCGCGCCCCGGGCGGCCCGGGGGCACCGG-30 )
[14], was performed on: (i) metagenomic DNA extracted from roots;
(ii) activated product; and (iii) lactobacilli isolates. The use of these
primers generates a PCR fragment of about 600 bp and 340 bp
respectively, suitable for a subsequent DGGE analysis. All reactions
for PCR-DGGE were carried out in a 50 ml volume containing 1.5 U
AmpliTaq Gold DNA polymerase (Applied Biosystem), 5 ml of 10
PCR Gold Buffer (Applied Biosystem), 200 mM of each deoxynucleotide triphosphate (Fermentas GmbH, St. Leon-Rot, Germany),
1.50 mM MgCl2 (Fermentas), 0.45 mM of each primer (MWG),
2.5% (w/v) bovine serum albumin (Fermentas), 4 ml DNA template,
and sterile MilliQ water.
The PCR with universal primers was performed under the
following thermocycling program: 5 min initial denaturation at
958C; 35 cycles of 958C for 30 s, 558C for 60 s, 728C for 40 s;
followed by a final elongation step of 728C for 7 min. PCR with
primers Lac1f and Lac2r-GC was carried out according to Walter
et al. [14]. The size and amount of the PCR products were estimated
by analyzing 2 ml samples by 1.5% agarose gel (w/v) electrophoresis and ethidium bromide staining.
The DGGE analysis was basically performed as first described by
Muyzer et al. [20], using a DCode System apparatus (Bio-Rad).
Polyacrylamide gels [7% (w/v) acrylamide:bisacrylamide (37.5:1)
(Bio-Rad)] in 1 Tris-Acetate-EDTA (TAE) buffer were prepared
using a Bio-Rad Gradient Delivery System (Model 475, Bio-Rad),
using solutions containing 35–55% denaturant [100% denaturant
corresponds to 7 M urea (Sigma–Aldrich) and 40% (v/v) formamide
(Sigma–Aldrich)]. The electrophoresis was run at 55 V for 16 hours
at 608C. Gels were stained in a solution of 1 SYBR-Green (Sigma–
Aldrich) in 1 TAE for 20 min and their images captured in UV
transillumination with Gel DocTM XR apparatus (Bio-Rad).
Selected dominant bands were cut from the gel with a sterile
scalpel and DNA was eluted by incubating the gel fragments for
16 hours in 50 ml of sterile deionized water at 48C. 2 ml of the
solution were then used as template to re-amplify the band fragments using the same primers without the GC-clamp and the same
PCR conditions.
Sequence analysis of 16S rDNA of pure cultures and DGGE bands
On the basis of phenotypic and genotypic investigations, representative isolates (lactobacilli and aerobic bacteria) were selected
and the 16S rDNA amplification performed with universal primers
27f and 1492r [21]. The amplified 16S rDNA were then purified
(PCR clean-up; Macherey-Nagel GmbH & Co. KG, Germany) and
sequenced (Eurofins MWG Operon, Ebersberg, Germany). Concerning PCR-DGGE bands, the obtained amplicons were
sequenced with primer 907r and Lac1f. Sequence chromatograms
were edited and analyzed using the software programs Finch TV
version 1.4.0 (Geospiza Inc., Seattle, WA, USA) and obtained
sequences were subjected to taxon classification using RDP classifier, an available tool at the RDP-II website (http://rdp.cme.
msu.edu/classifier/classifier.jsp). Moreover, SeqMatch search was
used to find the closest match for each 16S rRNA fragment (http://
rdp.cme.msu.edu/seqmatch/seqmatch_intro.jsp) [22].
Statistical analysis
The statistical software CoSTAT Version 6.002 (CoHort Software,
Monterey, California, USA) was used for analyses of variance.
Comparisons between the means were conducted using the Student–Newman–Keuls test. Significant differences (P < 0.05)
among treatments were marked with different letters.
Results and discussion
Growth responses and physiological features
The effect of inoculation of the EM product on hydroponically
grown L. perenne L. was evaluated and compared to the use of
the same filtered product, the HRM solution and an untreated
control.
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Genotypic characterization of lactobacilli and aerobic isolates
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TABLE 1
Effects of different amendments (Control = distilled water; EM = activated EM1W, F-EM = filtered EM1W, HRM = phytohormone
mixture) on total shoot fresh (SFW) and dry (SDW) weight, total shoot length (SL), root fresh (RFW) and dry (RDW) weight, root length
(RL) and tearing out resistance (TR) of Lolium perenne L. hydroponically grown under controlled conditions. Data are expressed as mean
values SD (n = 8). Mean values in the same row with common letters are not significantly different (P < 0.05)
Treatment
Control
EM
EM-F
HRM
SFW (g)
10.3 0.9 (c)
13.8 1.6 (b)
13.8 1.5 (b)
17.8 2.0 (a)
SDW (g)
1.62 0.24 (b)
1.85 0.31 (b)
1.86 0.17 (b)
2.77 0.88 (a)
SDW/SFW
0.16 0.02 (a)
0.13 0.01 (b)
0.14 0.01 (b)
0.16 0.04 (a)
SL (cm)
48.5 1.8 (d)
54.3 1.7 (c)
56.6 2.6 (b)
58.4 2.2(a)
Research Paper
RFW (g)
7.9 1.4 (ab)
6.0 2.4 (c)
6.6 1.6 (ab)
8.3 2.1 (a)
RDW (g)
1.28 0.28 (a)
0.86 0.52 (b)
0.86 0.23 (b)
1.02 0.43 (ab)
RDW/RFW
0.17 0.04 (a)
0.14 0.03 (b)
0.13 0.02 (b)
0.12 0.03 (b)
RL (cm)
14.2 1.4 (c)
19.2 2.8 (b)
19.6 3.0 (b)
24.6 1.3 (a)
133.5 12.1 (d)
191.5 16.8 (a)
162.5 23.5 (b)
149.0 18.7 (c)
TR (g)
The HRM treatment induced a significant increase of total shoot
(leaves + culm) length, fresh and dry weight with respect to the
untreated control (Table 1). Even if to a lesser extent, a positive
effect on EM and F-EM concerning aboveground ryegrass growth
was also observed. Data suggested that the inoculated microorganisms stimulated the plant cell extension growth, as evidenced by
the significant decrease of the ratio between shoot dry and fresh
weight. By contrast, HRM did not cause significant perturbation of
the ratio between shoot dry and fresh weight.
With respect to underground biomass, the investigated amendments did not significantly increase fresh and dry root weight; in
particular a decrease of root weight was observed in EM and F-EM.
However, the significant decrease of the ratio between root dry and
fresh weight of EM, F-EM and HRM suggested a stimulation of the
root extension growth. Moreover, ryegrass plants treated with
HRM, EM and F-EM exhibited longer root system than untreated
plants. EM treatments and F-EM induced a considerable increase of
root system length around 35%, while HMR approximately
doubled the length of ryegrass root system with respect to the
untreated plants. These data are in agreement with published
results reporting that some phytohormones, such as IAA, could
promote not only shoot development but also root elongation
[23,24].
Because of their morpho-physiological effects on plant shoot
and root, EM and HMR significantly improved the ryegrass resistance to tearing out (Table 1). The best performance was observed
for plants treated with EM, while F-EM and HRM induced less
evident effects on tearing out resistance (11 and 21% increase of TR
index, respectively). Considering the overall results, EM treatment
best fits with the scope of the experiment.
Microbiological counts and strain identification
Lactobacilli, total aerobic bacteria and yeasts were counted on MRS
agar, SDA and NA, respectively. The counts obtained from concentrated and activated product samples were comparable, evidencing that the activation step revitalized the inoculum but it did not
increase the bacterial number. Lactobacilli were the most represented group of microorganisms, being at levels of 106 cfu/ml,
while total aerobic bacteria and yeasts were counted at 105 cfu/ml
and 104 cfu/ml, respectively.
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All the 25 isolates (referred to LA1–LA25) obtained from MRS
agar were Gram positive, catalase negative, oxidase negative and
had a rod shape at the microscopic analysis. Genus-specific PCR
confirmed for all the isolates the affiliation to the Lactferobacillus
genus. Most of the isolates fermented L-arabinose, ribose, D-xylose,
galactose, glucose, fructose, mannose, melibiose, gluconate and 5cheto-gluconate. Six of the isolates (LA1, LA4, LA5, LA13, LA14,
LA20) fermented only galactose, glucose, fructose after five days
incubation. Six strains (LA6, LA9, LA15, LA17, LA22, LA25) could
also grow on mannitol, maltose, melezitose, raffinose and D-arabitol; in addition LA6 and LA25 ferment melibiose and sucrose. A
group of six isolates was positive to arabinose, ribose, D-xylose,
galactose, glucose, fructose and gluconate. The remaining seven
strains ferment L-arabinose, ribose, galactose, glucose, fructose,
gluconate and 5-ketogluconate and hydrolyze esculin; five of them
were also positive to a-methyl-D-glucoside, cellobiose, maltose,
melibiose and raffinose, while the other two to sucrose and xylitol.
Further, the isolates were genotypically grouped using ERIC-PCR.
Cluster analysis showed that they could be divided into six groups
(Fig. 1), which almost corresponded to the fermentation patterns
obtained. On the basis of fermentation and genotypic results, a
representative isolate from each group (LA1, LA3, LA6, LA7, LA9
and LA12) was selected for sequencing of the 16S rRNA gene. Five
of the six clusters contained microorganisms identified as: Lactobacillus buchneri, Lactobacillus parafarraginis and Lactobacillus diolivorans (Table 2). These species belong to the L. buchneri group
which is mostly linked to food and silage fermentation [25]. For
one cluster, whose members were found to ferment only three
sugars, it was not possible to obtain a clear taxonomic identification but only a similarity of 97% to an uncultured Lactobacillus
spp. Further analyses are required to better characterize these
strains.
Twenty isolates from NA were Gram negative, catalase positive,
oxidase negative and the microscopic analysis showed the presence of motile rods (100%). The remaining 5 were Gram positive,
catalase positive, oxidase negative and the microscopic analysis
showed the presence of rod shaped cells (100%). The genotypic
grouping and the sequencing results allowed the selection of five
groups (Fig. 2). As for lactobacilli, a representative isolate from
each group (A1–A5) was selected for sequencing of the 16S rRNA
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FIGURE 1
Dendrogram obtained by cluster analysis of ERIC-PCR fingerprints of
Lactobacillus strains isolated from the activated product.
gene. Strains belonged to Stenotrophomonas maltophilia (ten isolates, three different strains), Microbacterium trichotecenolyticum
(seven isolates) and Escherichia coli (eight isolates) (Table 2).
Twenty-five yeasts isolated from SDA were identified by API20C
AUX1 as Candida utilis (15 isolates) and Saccharomyces cerevisiae
(ten isolates).
FIGURE 2
Dendrogram obtained by cluster analysis of ERIC-PCR fingerprints of aerobic
strains isolated from the activated product.
The use of lactobacilli as beneficial bacteria for plant growth is
not widespread, although their presence inside plants has been
sometimes detected [26–28]. Considering their efficacy as protective and probiotic cultures in human, animal, food and feed
[29,30], their use in the agronomic field is rapidly increasing.
In vitro studies on their strong activity against plant pathogenic
TABLE 2
Strains isolated from the activated product
Isolatedstrain
bp
La1
1371
La3
809
JX426086
Accession #
Closest match
Accession #
S_ab score
DGGE bandsa
DGGE profile
Uncultured compost bacterium FS423
FN667288
0.972
8
F-EM, EM
Lactobacillus buchneri 482A
HM162413
0.995
p7
EM1W
p5, 3
EM, EM1W
La6
1439
JX426087
Lactobacillus parafarraginis (T) NRIC 0677
AB262734
1.000
La7
808
JX426088
Lactobacillus buchneri TB-H34
AB425940
1.000
La9
1390
JX426089
Lactobacillus parafarraginis (T) NRIC 0677
AB262734
1.000
La12
A1
1441
1382
JX426090
JX426091
Lactobacillus diolivorans NM60-7
Stenotrophomonas maltophilia BAC3155
HM218272
HM355743
0.996
0.999
A2
1386
JX426092
Stenotrophomonas maltophilia BAC3155
HM355743
1.000
A3
1395
JX426093
Stenotrophomonas maltophilia BAC2024
HM355615
0.999
A4
1385
JX426094
Escherichia coli S88
CU928161
0.996
A5
1370
JX426095
Microbacterium trichothecenolyticum M23047
HM032796
0.994
a
DGGE bands in Fig. 4.
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700
TABLE 3
Best-match identification of phylotypes (Seqmatch tool, from Ribosomal Database Project-II) of excised DGGE bands obtained with universal primers
Phylogenetic group
Closest match
Accession #
S_ab
score
Closest described
bacterium
Accession #
S_ab score
DGGE profilea
1
Lewinella (28%)
Uncultured bacterium T2-68
JF502990
0.888
Lewinella marina (T) MKG-38
AB301495
0.605
All sand profiles
2
Hydrogenophaga (100%)
Hydrogenophaga pseudoflava
(T) ATCC 33668
Hydrogenophaga bisanensis (T) K102
AF078770
EF532793
0.990
0.990
3
Fibrobacter (55%)
Uncultured Fibrobacteres
bacterium clone AUVE_12B11
EF651500
0.972
Fibrobacter intestinalis NR9
AJ496284
0.499
All sand profiles
4
Vogesella (100%)
Vogesella sp. SK-2
AM689950
1.000
Vogesella indigofera
(T) ATCC 19706
AM989119
0.97
All sand profiles
5
Polaromonas (97%)
Polaromonas aquatica (T) CCUG 39402
AM039830
0.975
All sand profiles
6
Lactobacillus (99%)
Lactobacillus zeae (T) ATCC15820
Lactobacillus casei (T) ATCC 393
Lactobacillus paracasei (T) JCM 8130
D86516
AF469172
D79212
1.000;
1.000;
1.000
sEM, sHRM
7
Acidovorax (50%)
Uncultured bacterium DR128
JF429172
0.978
Variovorax sp. Z0-YC6806
GQ369074
0.943
all sand profiles
8
Flavobacterium (100%)
Flavobacterium sp. WB 2.1-30
AM167558
1.000
Flavobacterium
psychrolimnae (T) LMG 22018
AJ585428
0.939
rF-EM
9
Leptospira (100%)
Leptospira biflexa (T) ATCC 23582
Leptospira wolbachii (T) ATCC 43284
AY631876
AY631879
1.000;
1.000
10
Emticicia (55%)
Cytophaga sp. GPl-11
AJ456975
0.703
Emticicia sp. IMCC1731
DQ664246
0.615
rF-EM
11
Niastella (100%)
Niastella sp. RHYL-67
EU917053
0.992
Niastella populi (T) THYL-44
EU877262
0.953
rEM, rHRM
12
Ohtaekwangia (90%)
Bacteroidetes bacterium Mo-0.2plat-K3
AJ622888
0.944
Ohtaekwangia koreensis (T) 3B-2
Ohtaekwangia kribbensis (T) 10AO
GU117702
GU117703
0.645;
0.645
rEM
13
Ohtaekwangia (100%)
Ohtaekwangia kribbensis (T) 10AO
GU117703
0.942
all root profiles
14
Hydrogenophaga (100%)
Hydrogenophaga pseudoflava (T) ATCC 33668
Hydrogenophaga bisanensis (T) K102
AF078770
EF532793
0.985;
0.985
rEM
15
Fibrobacteres (44%)
uncultured Fibrobacteres bacterium
clone AUVE_12B11
EF651500
0.972
16
Chloroplast
DGGE
band
DGGE profiles of Fig. 3.
rF-EM
Fibrobacter intestinalis NR9
AJ496284
0.495
rEM, rHRM, rCTR
All root profiles
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a
sF-EM, sEM, sCTR
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commercial crops (maize, sugar cane and wheat) producing
antifungal metabolites against several soil-borne pathogens
[42] and several phytohormones such as IAA, gibberellic acid
and abscissic acid [43]. Moreover, its outstanding nitrogen-fixing capacity and degradation of several organic pollutants show
high biotechnological potential for use in commercial inoculants and bioremediation application [44,45]. M. trichotecenolytcum has been isolated as endophyte from several plant species
[46,47]. Strains belonging to Microbacterium spp. were found to
produce IAA and promote orchid seed germination [48]. Concerning E. coli, which is mostly associated with gut microbiota
and infection, some non-pathogenic strains are used as probiotics because of the production of interesting antimicrobial
compounds [49].
Characterization of bacterial communities by PCR-DGGE
Genomic DNA from sand and surface-sterilized root samples was
used to evaluate the impact of the different amendments (CTR,
EM, F-EM and HRM) on their microbial profile using PCR-DGGE.
Moreover, it was interesting to verify if in the EM treatment the
inoculated lactobacilli, being the most representative group,
could be detected at root level and thus becoming endophytes.
Results, using bacterial universal primers, are shown in Fig. 3.
Sixteen PCR-DGGE bands have been identified by sequencing
(Table 3). PCR-DGGE analysis of bacterial community in sand
samples (Fig. 3a) revealed that all profiles were comparable, thus
indicating that detected microorganisms probably derive from
sand, water or seeds.
TABLE 4
Best-match identification of phylotypes (Seqmatch tool, from Ribosomal Database Project-II) of excised DGGE bands obtained with
Lactobacillus spp. specific primers
DGGE band
Phylogenetic group
Closest match
Accession #
S_ab score
DGGE profilea
1
Lactobacillus (100%)
Lactobacillus pentosus Taj-Apis 359
HM027643
0.926
EM
2
Lactobacillus (100%)
Lactobacillus sanfranciscensis LMG 16002
EU350220
0.985
EM
3
Lactobacillus (100%)
Lactobacillus parafarraginis (T) NRIC 0677
AB262734
0.990
EM, EM1W
4
Exiguobacterium (100%)
Exiguobacterium sp. MH70
EU182898
1.000
F-EM, EM
5
Lactobacillus (100%)
Lactobacillus sanfranciscensis LMG 16002
EU350220
0.970
EM
6
Lactobacillus (100%)
Lactobacillus sanfranciscensis TMW 1.1304
CP002461
0.977
EM
7
Lactobacillus (100%)
Lactobacillus sanfranciscensis LS1
DQ875745
1.000
EM
8
Lactobacillus (100%)
Uncultured compost bacterium FS423
FN667288
1.000
F-EM, EM
p1
Lactobacillus (100%)
Lactobacillus diolivorans (T) JKD6
Lactobacillus farraginis (T) NRIC 0676
AF264701
AB262731
1.000
1.000
EM1W
p2
Lactobacillus (99%)
Lactobacillus parafarraginis (T) NRIC 0677
AB262734
0.966
EM1W
p3
Lactobacillus (100%)
Lactobacillus diolivorans (T) JKD6
Lactobacillus farraginis (T) NRIC 0676
AF264701
AB262731
1.000
1.000
EM1W
p4
Lactobacillus (100%)
Lactobacillus parafarraginis (T) NRIC 0677
AB262734
1.000
EM1W
p5
Lactobacillus (100%)
Lactobacillus parafarraginis (T) NRIC 0677
AB262734
0.980
EM, EM1W
p6
Lactobacillus (100%)
Lactobacillus parafarraginis (T) NRIC 0677
AB262734
1.000
EM1W
p7
Lactobacillus (100%)
Lactobacillus buchneri (T) JCM1115
AB205055
1.000
EM1W
p8
Lactobacillus (100%)
Lactobacillus diolivorans (T) JKD6
Lactobacillus farraginis (T) NRIC 0676
AF264701
AB262731
1.000
1.000
EM1W
p9
Lactobacillus (98%)
Lactobacillus zeae (T) ATCC15820
Lactobacillus casei (T) ATCC 393
Lactobacillus paracasei (T) JCM 8130
D86516
AF469172
D79212
1.000;
1.000;
1.000
EM1W
a
DGGE bands in Fig. 4.
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701
Research Paper
fungi [31,32] are promising for the application of lactobacilli in
real field condition. As in other ecosystems (gut, fermented foods,
among others), they are expected to improve mineral availability
for plants in the rhizosphere through the production of enzymes
and organic acids [33], and control pathogen diffusion with the
production of several compounds. Species isolated in this study (L.
buchneri, L. parafarraginis and L. diolivorans) and those identified
with PCR-DGGE (L. pentosus and L. sanfranciscensis, Table 4) are
often reported in the literature to improve the stability of silages,
thanks to the production of a wide range of metabolites inhibiting
moulds and fungi [34,35]. Moreover, they are frequently isolated
from sourdough, giving to sourdough bread an extended shelf-life
and improved microbial safety [36]. Up to now, only a few studies
have reported the use of lactobacilli as bio-inoculants together
with other bacterial species [37–39].
Concerning yeasts, they are common resident of soil and rhizosphere and they have also been isolated inside plants tissues.
Several studies reported their role as plant growth promoters
and soil-borne fungal antagonists [8,40]. Moreover, it has been
documented the beneficial association of lactobacilli and yeasts in
other ecosystems. In sourdough, when Lactobacillus plantarum is
associated with yeasts (S. cerevisiae or S. exiguus) cell yield and lactic
acid production increase [41]. A higher propionate formation was
observed in sourdough co-fermented with L. buchneri and L.
diolivorans and exhibited increased antifungal properties [34].
The three aerobic species isolated are listed in Table 2. S. maltophilia has been found in strict association with plant hosts; it was
also described as a growth promoter microorganism of some
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New Biotechnology Volume 30, Number 6 September 2013
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FIGURE 4
FIGURE 3
DGGE bands obtained amplifying metagenomic DNA with universal primers
from sand and roots. (a) Sand samples, (b) root samples. CTR, control; HRM,
treatment with hormone rich solution; F-EM, treatment with filtered/
activated product; EM, treatment with activated product.
Concerning root profiles (Fig. 3b), PCR-DGGE analysis revealed
a considerable microbial community complexity in the EM and FEM treatments. Unfortunately, the biggest band corresponded to
chloroplast DNA and the preferential amplification of this DNA
could have reduced the yield of amplification of microbial DNA,
which clearly has given rise to fainter bands, difficult to be excised.
Bands 14 and 15 showed high sequence similarity to bands 2 and 3
of sand profiles (Fig. 3 and Table 3). However, in contrast to sand,
root profiles showed a peculiar band pattern in each treatment
condition, except for band number 13, present in all samples.
Sequencing revealed a close similarity to Ohtaekwangia kribbensisT
(GeneBank accession no. GU117703), firstly isolated from sand
[50]. Sequences from bands 8–10 were closely related to Flavobacterium sp. WB 2.1-30, Leptospira spp. and Cytophaga sp. GP 1-11
(Table 3) and were present only in F-EM. These microorganisms
have been frequently isolated from fresh- and hardwater. The EM
treatment has two typical bands: number 12, closely related to a
Bacteroidetes bacterium recovered from water (GeneBank accession no. AJ622888), and number 14, which can be ascribed to
Hydrogenophaga spp., a root endophyte of several crops [51]. Niastella spp., frequently isolated from soil [52] has been detected in
EM and HRM profiles (band number 11).
702
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DGGE bands obtained amplifying DNA with Lactobacillus spp. specific primers
from root samples, activated EM1W and pure cultures (LA1, LA3, LA9, LA12).
CTR, control; HRM, treatment with hormone rich solution; F-EM, treatment
with filtered/activated product; EM, treatment with activated product;
EM1W, the activated product.
Overall, PCR-DGGE analysis revealed the presence of a large
variety of microorganisms colonizing the rhizosphere and roots,
and most of them have been already reported as endophytes in
different plants [53–55]. To better investigate the presence of
lactobacilli in root samples, specific primers targeting LAB were
used in an additional PCR-DGGE. Fig. 4 shows PCR-DGGE pattern
of DNA extracted from root samples of the 4 treatments, the
activated product and Lactobacillus isolates (Lactobacillus sp.
LA1, L. buchneri LA3, L. parafarraginis LA9 and L. diolivorans LA12).
The analysis of sequenced bands (Table 4) evidenced the root
colonization ability of the following species: (i) L. parafarraginis LA
9 (bands p5 and 3); (ii) Lactobacillus spp. LA1 (band 8); (iii) L.
pentosus (band 1); (iv) L. sanfranciscensis (band 2, 5, 6, 7).
Surprisingly, bands ascribed to Lactobacillus spp. LA1, L. pentosus
and L. sanfranciscensis, in the EM profile, were absent in the PCRDGGE profile of the product. It can be hypothesized that the
activation step led to a selective growth of some species whereas,
after inoculation, an in situ enrichment of other phylotypes gives
rise to a different microbial population. This can explain the
different profiles obtained for the activated product and EM treatment. By contrast, the lack of recovery of some species by plating
(e.g. L. pentosus and L. sanfranciscensis) may reflect the different
sensitivity of diverse species to plate culturing techniques when a
mixed culture is analyzed.
On the whole, the presence of several lactobacilli in the EM
treatment, compared to the CTR and HRM, showed the ability of
these microorganisms to colonize root tissues and become plant
endophytes.
Conclusion
The treatment of hydroponically grown L. perenne L. with a
commercial solution of microorganisms has led to an increased
resistance to tearing out, as well as to an increased root length,
which are particularly favorable features for any essence of
a recreational or sport turfgrass. Identification of isolates clearly
RESEARCH PAPER
showed the presence of species reported in literature as having
plant growth promoting activity and antifungal action. The PCRDGGE analysis targeting LAB evidenced the colonization ability of
four species derived from the product; this is the first time that the
endophytic behavior of inoculated lactobacilli has been assessed.
The inoculation of microorganisms may contribute to the beneficial morpho-physiological effects on plant shoots and roots.
This may lead to the conclusion that bio-inoculants have a great
potential for the maintenance and increased performance of turfgrass surfaces. Further on field investigations are necessary to
confirm the effect of this low-impact technology aimed at developing a more sustainable environmental management of lawn and
sport fields.
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