ArticlePDF Available

Influence of a Bacillus sp. on physiological activities of two arbuscular mycorrhizal fungi and on plant responses to PEG-induced drought stress

Authors:

Abstract and Figures

The effects of bacterial inoculation (Bacillus sp.) on the development and physiology of the symbiosis between lettuce and the arbuscular mycorrhizal (AM) fungi Glomus mosseae (Nicol. and Gerd.) Gerd. and Trappe and Glomus intraradices (Schenck and Smith) were investigated. Plant growth, mineral nutrition and gas-exchange values in response to bacterial inoculation after PEG-induced drought stress were also evaluated. In AM plants, inoculation with Bacillus sp. enhanced fungal development and metabolism, measured as succinate dehydrogenase (SDH) and alkaline phosphatase (ALP) activities, more than plant growth. Under non-stressed conditions, G. intraradices colonization increased all plant physiological values to a higher extent when in dual inoculation with the bacterium. Under stress conditions, the bacterium had an important stimulatory effect on G. intraradices development. Under such conditions, the effects of the bacterium on photosynthetic rate, water use efficiency (WUE) and stomatal conductance of lettuce plants differed with the fungus species. Plant-gas exchange was enhanced in G. intraradices- and reduced in G. mosseae-colonized plants when co-inoculated with Bacillus sp. Thus, the effects of each fungus on plant physiology were modulated by the bacterium. Stress was detrimental, particularly in G. intraradices-colonized plants without the bacterium, reducing intra and extraradical mycelium growth and vitality (SDH), as well as plant-gas exchange. Nevertheless, Bacillus sp. inoculation improved all these plant and fungal parameters to the same level as in non-stressed plants. The highest amount of alive and active AM mycelium for both fungi was obtained after co-inoculation with Bacillus sp. These results suggest that selected free-living bacteria and AM fungi should be co-inoculated to optimize the formation and functioning of the AM symbiosis in both normal and adverse environments.
Content may be subject to copyright.
Mycorrhiza (2003) 13:249–256
DOI 10.1007/s00572-003-0223-z
ORIGINAL PAPER
Astrid Vivas · Adriana Marulanda ·
Juan Manuel Ruiz-Lozano · Jos Miguel Barea ·
Rosario Azcn
Influence of a
Bacillus
sp. on physiological activities
of two arbuscular mycorrhizal fungi and on plant responses
to PEG-induced drought stress
Received: 24 May 2002 / Accepted: 8 January 2003 / Published online: 15 February 2003
Springer-Verlag 2003
Abstract The effects of bacterial inoculation (Bacillus
sp.) on the development and physiology of the symbiosis
between lettuce and the arbuscular mycorrhizal (AM)
fungi Glomus mosseae (Nicol. and Gerd.) Gerd. and
Trappe and Glomus intraradices (Schenck and Smith)
were investigated. Plant growth, mineral nutrition and
gas–exchange values in response to bacterial inoculation
after PEG–induced drought stress were also evaluated. In
AM plants, inoculation with Bacillus sp. enhanced fungal
development and metabolism, measured as succinate
dehydrogenase (SDH) and alkaline phosphatase (ALP)
activities, more than plant growth. Under non-stressed
conditions, G. intraradices colonization increased all
plant physiological values to a higher extent when in dual
inoculation with the bacterium. Under stress conditions,
the bacterium had an important stimulatory effect on G.
intraradices development. Under such conditions, the
effects of the bacterium on photosynthetic rate, water use
efficiency (WUE) and stomatal conductance of lettuce
plants differed with the fungus species. Plant-gas ex-
change was enhanced in G. intraradices- and reduced in
G. mosseae-colonized plants when co-inoculated with
Bacillus sp. Thus, the effects of each fungus on plant
physiology were modulated by the bacterium. Stress was
detrimental, particularly in G. intraradices-colonized
plants without the bacterium, reducing intra and extrarad-
ical mycelium growth and vitality (SDH), as well as
plant-gas exchange. Nevertheless, Bacillus sp. inoculation
improved all these plant and fungal parameters to the
same level as in non-stressed plants. The highest amount
of alive and active AM mycelium for both fungi was
obtained after co-inoculation with Bacillus sp. These
results suggest that selected free-living bacteria and AM
fungi should be co-inoculated to optimize the formation
and functioning of the AM symbiosis in both normal and
adverse environments.
Keywords Alkaline phosphatase · AM fungus ·
Bacterium co-inoculation · PEG-induced drought stress ·
Succinate dehydrogenase
Introduction
The rhizosphere is a site at which symbiotic and non-
symbiotic microorganisms can interact (Jeffries and Barea
1994). Ubiquitous arbuscular mycorrhizal (AM) fungi and
plant-growth-promoting rhizosphere bacteria are compo-
nents of natural systems that benefit the host plant (Barea
and Jeffries 1995). As a result of microbial-plant associ-
ations, crop production can be increased and mixed
inocula have been recommended for re-vegetation pur-
poses (Bowen and Rovira 1999). The cooperation of AM
fungi and bacteria in nutrient uptake by plants may be due
to specific attributes of microorganisms, such as the
ability of certain bacteria to stimulate mycorrhizal
formation and development (Azcn-Aguilar and Barea
1985; Garbaye 1994), as well as mycorrhizal effects on
the associated bacterial population (Amora-Lazcano and
Azcn 1997; Amora-Lazcano et al. 1998). There is a
growing interest in improving understanding of the
diversity and significance of microbial populations in
soil and their involvement in nutrient cycling. The
manipulation of certain bacteria and AM fungi is
important with regard to sustainability issues (Bowen
and Rovira 1999; Barea et al. 2002).
Many authors have correlated the plant growth
responses to mycorrhization with high amounts of AM
roots and fungal physiological activity, which is closely
related to mycorrhizal functioning (Tisserant et al. 1993;
A. Vivas · A. Marulanda · J. M. Ruiz-Lozano · J. M. Barea ·
R. Azcn ())
Departamento de Microbiologa del Suelo y Sistemas Simbiticos,
Estacin Experimental del Zaidn, CSIC,
Profesor Albareda 1, 18008 Granada, Spain
e-mail: Rosario.Azcon@eez.csic.es
Tel.: +34-958-121011
Fax: +34-958-129600
Guillemin et al. 1995). It is well known that microbial
activities can affect the formation of mycorrhiza (Azcn
et al. 1978; Azcn 1989), but there is no information
about the effect of bacterial inoculation on metabolic
characteristics of AM fungi.
AM colonization is normally quantified by assessing
the level (frequency and intensity) of fungal infection in
plant roots after trypan blue (TB) staining (Phillips and
Hayman 1970). However, Vierheilig and Ocampo (1989)
reported that TB staining was not a good indicator of AM
efficiency and, in AM studies related to the functional
aspect of symbiosis, vital staining techniques have been
suggested (Tisserant et al. 1993; Boddington and Dodd
1998). Succinate dehydrogenase (SDH) and alkaline
phosphatase (ALP) activities, linked to active metabolic
fungal performance, have been proposed as useful indices
for the analysis of efficient arbuscular endomycorrhizal
infection (Smith and Gianinazzi-Pearson 1990; Tisserant
et al. 1993; Vzquez et al. 2000).
Mycorrhizal symbiosis is considered a key factor in
helping plants cope with adverse environmental condi-
tions (Jeffries and Barea 1994). Although an effect of AM
endophytes on drought alleviation has been reported
(Ruiz-Lozano et al. 1995a, 1995b, 2001), no information
is available on the ability of plants dually inoculated with
AM fungi and mycorrhiza-helper bacteria to support
drought stress. The bacterium assayed here (Bacillus sp.)
was isolated from a desert area (Alicante, Spain) and
shown to stimulate growth of red clover plants (Vivas et
al., unpublished results). An experimental area was
chosen within a desertification-threatened region in
southeast Spain for studying the role of the most common
natural saprophyte and symbiotic microbial isolates in
sustaining vegetation cover in such stressed environ-
ments. The AM fungi selected for this study were Glomus
mosseae and G. intraradices, which are well adapted to
the dry conditions of Mediterranean areas (Ruiz-Lozano
et al. 1995a, 1995b).
The aim of this study was to determine the effect of
inoculation with a Bacillus sp. from a desert area on the
growth, vitality and activity of the above-mentioned
fungi. An additional objective was to determine the
possible importance of the bacterium in combined
bacterial and mycorrhizal inocula for plant tolerance to
drought stress and to define the possible mechanisms
involved.
Materials and methods
Experimental design and statistical analysis
At sowing time, plants were inoculated with either G. mosseae or G.
intraradices and/or Bacillus sp. The bacterium and each of the
mycorrhizal fungi were assayed alone or in dual fungus-bacterium
combinations. Thus, there were five microbial treatments plus one
control treatment without inoculation. Ten replicates of each
treatment were made giving a total of 60 pots. Half of the pots
were cultivated without PEG application and half exposed to PEG
prior to harvesting.
Data were subjected to an analysis of variance (ANOVA)
followed by Duncan’s multiple range test (Duncan 1955). Percent-
age values were arcsin transformed before statistical analysis.
Soil and biological material
Lettuce (Lactuca sativa L. cv Romana) was grown for 2 months in
300 g sand/vermiculite/sepiolite (1:1:1) inert medium, previously
washed and sterilized by autoclaving.
The bacterial inoculum was isolated from a desert soil in
Alicante province (Spain) using standard techniques following
serial dilutions of the soil. The inoculum was grown on a rotary
shaker (150 rpm) at 28C for 28 h in a 250-ml flask containing
50 ml of nutrient broth (8 g l–1) solution. Aliquots (1 ml) of the
bacterial culture containing 108CFU ml–1 were added to each pot.
Mycorrhizal fungal inoculum from each endophyte was multi-
plied in an open-pot culture of Lactuca sativa L. and consisted of
soil, spores, hyphae and AM root fragments. The AM species were
G. mosseae (Nicol. and Gerd.) Gerd. and Trappe, isolate BEG 122
and G. intraradices (Schenck and Smith) isolate BEG 121. Aliquots
(5 g) of each inoculum, with similar infective characteristics (an
average of 50 propagules g-1 according to the most probable
number test), were placed below the seeds of Lactuca sativa L. This
amount of inoculum was selected in preliminary tests as producing
an optimal infection level according to the total amount of soil in
the pot. Non-mycorrhizal treatments received the same quantity of
autoclaved inoculum together with a 2-ml aliquot of a filtrate (less
than 20 m) of the AM inoculum, in an attempt to provide a general
microbial population free of AM propagules. Two seeds were sown
and thinned after emergence to one seedling per pot.
Growth conditions
The plants were grown in a controlled-environment chamber under
conditions of 50% relative humidity, day and night temperatures of
27C and 18C, respectively, and a photoperiod of 14 h. Photo-
synthetic photon flux density (PPFD) was 500 mol m–2 s–1 as
measured with a light meter (LICOR, model LI-188B).
Drought stress was induced by adding PEG solution (15% PEG)
to half of the pots at two growing stages (1 week and 24 h before
harvesting) as described elsewhere (Ruiz-Lozano and Azcn 1997),
so that the two PEG applications had accumulative effects. A PEG
solution (purified PEG 6,000 Merck, molecular weight 5,000–
7,000) was used as osmoticum to induce stress. The rest of the pots
were kept as controls without PEG.
The plants were given a nutrient solution (Hewitt 1952) at half-
P concentration with the pH adjusted to 6.8–7. This mineral
solution has been found to give high levels of infection in plants
inoculated with G. mosseae and G. intraradices (Ruiz-Lozano and
Azcn 1996). Mineral solution was supplied twice a week (25 ml
per pot) to maintain the required water and nutrient levels
throughout the experiment. A rock phosphate source from Morocco
with 19 mg P2O5kg–1 (Olsen and Dean 1965) was applied to each
pot by mixing 1 g with the sand/vermiculite/sepiolite medium
before sterilizing. This soil-less substrate was selected as growth
medium since it provides little benefit to the AM host plant and
thus allows a more direct interpretation of the mechanisms of the
bacterial-fungal interaction.
Parameters measured
Before harvest, the CO2exchange rate, transpiration rate, sub-
stomatal cavity CO2concentration and instantaneous water use
efficiency (WUE) were measured on the fourth leaf below the apex
of each plant. Atmospheric CO2was measured 5 m above ground
level. PPFD was 1,180 mmol m–2 s–1, which ensured that no
limitation in photon irradiance occurred (Long and Hallgren 1987).
Light was provided by a halogen lamp (General Electric 300 PAR
56/WFL). A model LCA-3 portable integrated infrared CO2
250
analyzer (Analytical Development Co., Hoddesdon, UK) was used
for these determinations. Measurements were made 2 h after the
light was turned on.
At harvest (8 weeks after planting), the root system was
separated from the shoot and the fresh and dry weights of each were
recorded. The roots were carefully washed and then divided into
three batches: one was stained by the normal non-vital TB staining
of all fungal tissues (Phillips and Hayman 1970) and the others
were used for histochemical vital staining of the mycorrhizal roots
to measure living (SDH) and functional (ALP) mycorrhizal fungal
development.
SDH activity was revealed by the procedure described by Smith
and Gianinazzi-Pearson (1990). The roots were immersed in a
freshly made solution of 0.2 M Tris-HCl pH 7.0, 2.5 M sodium
succinate 6-hydrate, 4 mg ml-1 nitro blue tetrazolium, 5 mM MgCl2.
Root fragments were stained overnight at room temperature and
then rinsed for 15–20 min in a 3% active chlorine solution of
sodium hypochlorite.
ALP was determined according to the procedure described by
Tisserant et al. (1993). The roots were immersed in a freshly made
solution containing 50 mM Tris-citric acid, pH 9.2, 1 mg ml-1 a-
naphthyl acid phosphate (monosodium salt), 0.05% MgCl2anhy-
dro, 0.05% MnCl2tetrahydrate and 1 mg ml-1 fast blue RR salt.
Root fragments were stained overnight at room temperature and
then rinsed for 15–20 min in a 1% active chlorine solution of
sodium hypochlorite.
Mycorrhizal development, after either non-vital or vital staining
procedures, was evaluated by the method of Trouvelot et al. (1986)
(for more information, see http://www.dijon.inra.fr/bbceipm/Mych-
intec/Mycocalc-prg/). An estimate of the length of root colonized by
the fungus (the colonization frequency, F%) is given as the ratio
between colonized root fragments and the total number of root
fragments observed. The colonization intensity (m%) is an estimate
of the amount of root cortex that became mycorrhizal, relative only
to the mycorrhizal root fraction, while M% is the colonization
intensity relative to the whole root system. Arbuscule abundance (a%
and A%) is an estimate of arbuscule richness in the mycorrhizal root
fraction and in the whole root system, respectively.
The extraradical mycelium in the soil was determined by an
adaptation of the method described by Jones and Mollison (1948).
Briefly, 1 g of dry soil was treated with sodium hexametaphosphate
and trypan blue (0.05%) in lactic acid. The sample was heated in a
water bath at 90C for 30 min and then sieved through a 50-m-
mesh sieve. The remaining mycelium was mixed with bacterio-
logical agar for quantification using a gridline intersection method
described by Newman (1966).
Proline content in leaves and roots was determined by
colorimetry (Bates et al. 1973). Concentrations of N (micro-
Kjeldahl), P (Olsen and Dean 1965) and K (Lachica et al. 1973) in
the shoots were measured.
Molecular identification of the bacterial strain
Total DNA from the bacterial isolate was obtained as described by
Giovannetti et al. (1990) and characterized by 16S ribosomal DNA
sequence analysis. PCR was carried out with the eubacterial
primers 27f and 1495r (Lane 1991), located at the 5’ and 3’ ends of
the ribosomal rDNA sequence, respectively, which enabled us to
amplify almost the entire gene. Amplification reactions were done
in a 20-l volume containing 0.5 M of each primer, 100 M
dNTPs, 1 PCR buffer (Sigma, St. Louis, Miss., USA), 2.5 mM
MgCl2, 10 ng of genomic DNA and 0.25 U Taq DNA polymerase
(Sigma). A Perking-Elmer/Cetus DNA Thermal Cycler was used
with the following parameters: initial denaturation at 95C for
4 min, followed by 30 cycles of denaturation at 94C for 30 s,
annealing at 56C for 45 s, elongation at 72C for 1 min and a final
elongation at 72C for 5 min. The amplified DNA was purified
following electrophoresis through a 1.2% agarose gel with the
QIAEX II Gel Extraction Kit (Qiagen, Hilden, Germany) and
cloned into the pGME plasmid (Promega) for sequencing. Database
searches for 16S rDNA sequence similarity, using FASTA and
BLAST algorithms, unambiguously identified the bacterial isolate
as a member of the genus Bacillus. However, the exact species must
still be elucidated by complementary studies.
Results
The inert mixture used in this study as rooting medium was
a good substrate for mycorrhizal performance. Mycorrhizal
plants grew better than non-mycorrhizal plants and devel-
oped abundant AM (Fig. 1, Table 1). Inoculation with
Bacillus sp. alone also increased shoot and root growth and
proved to be the most effective treatment for enhancing
root growth in stressed plants (Fig. 1). Plants colonized by
G. intraradices alone showed the highest shoot growth,
particularly under non-stressed conditions (Fig. 1). In PEG
treatments, the two AMF increased shoot biomass with
similar efficiencies when inoculated independently. Bacil-
lus sp. increased plant growth more effectively in non-
mycorrhizal plants (Fig. 1).
In the absence of bacteria and PEG, the total infective
parameters (TB staining) were highest in plants colonized
by G. intraradices (Table 1). Nevertheless, the same
infective values were attained when Bacillus sp. and G.
mosseae were co-inoculated. Greatest infectivity was not
Fig. 1 Shoot and root fresh weight (g) in lettuce plants subjected or
not to PEG-induced drought stress. Treatments are described as C
(control), B(Bacillus sp.), Gm (G. mosseae), Gi (G. intraradices),
Gm+B (G. mosseae +Bacillus sp.) and Gi+B (G. intraradices +
Bacillus sp.). Means not followed by a common letter differ
significantly (P=0.05) from each other according to Duncan’s
multiple range test (n=5)
251
always related to mycorrhizal response (Table 1, Fig. 1).
Bacterial inoculation did not increase shoot growth in
mycorrhizal plants but did enhance mycorrhizal infective
parameters compared with those of roots colonized by G.
mosseae or G. intraradices alone (Table 1). The bacteria
enhanced both live (SDH) and active (ALP) mycorrhizal
fungal biomass (Table 1) in all treatments. Bacterial
inoculation almost doubled ALP activity in both types of
mycorrhizal root. Highest ALP activity was found in the
absence of PEG in plants co-inoculated with Bacillus sp.
and G. intraradices.
With regard to AM-colonizing parameters, G. in-
traradices-colonized roots showed higher ALP activity
than G. mosseae-colonized roots under stress conditions,
despite the fact that vital SDH activity was higher in G.
mosseae- than in G. intraradices-colonized roots. Thus,
the ratio of activity (ALP) to vitality (SDH) in G.
intraradices-colonized plants was higher than in G.
mosseae-colonized plants. Bacterial inoculation enhanced
the metabolic characteristics of G. intraradices under
stress conditions to a greater extent than in the absence of
PEG. Most noticeable was that Bacillus sp. widely
enhanced AM colonization and fungal metabolic activity
in the mycorrhizal tissue (Table 1). Lettuce roots
colonized by either of the AMF reached maximum
infection and live and active mycelium in the presence
of Bacillus sp.
Concerning plant-gas exchange, the transpiration rate
was hardly affected by the microbial treatment, both
under stress and non-stress conditions (Table 2). In
contrast, the photosynthetic rate, WUE and stomatal
conductance were considerably increased by both myc-
orrhizal fungi under non-stress conditions. The bacterial
treatment had different effects on these parameters
depending upon the associated Glomus species. Co-
inoculation with Bacillus sp. increased photosynthesis,
WUE and stomatal conductance in G. intraradices-
colonized plants but not in G. mosseae-colonized ones.
However, under stress conditions, G. mosseae-colonized
plants showed the highest gas-exchange values (Table 2).
Drought stress decreased plant-gas exchange to a
higher extent in plants colonized by G. intraradices than
in those colonized by G. mosseae. Under such conditions,
considerable differences were found in CO2exchange and
WUE between the least effective (G. intraradices) and the
most effective (G. mosseae) fungal species (Table 2). Co-
inoculation with Bacillus sp. increased photosynthesis,
WUE and stomatal conductance in G. intraradices-
colonized plants relative to mycorrhizal inoculation alone,
but not in the case of G. mosseae-colonized plants.
Under non-stress conditions, the proline content in
leaves reached its maximum value in plants dually
inoculated with G. intraradices and Bacillus sp. Under
stress conditions, maximum proline accumulation was
reached in the leaves of plants inoculated with G. mosseae
alone (Fig. 2).
The highest amount of extraradical mycelium pro-
duced by G. intraradices in the absence of PEG correlated
with the highest ability of this fungus for intraradical
colonization. Bacillus sp. did not affect extraradical
mycelium development. In contrast, under stress condi-
tions, the bacterium increased the length of the mycelium
produced by G. intraradices (Fig. 3).
The N, P and K contents were also affected by the
microbial treatments (Fig. 4). Under non-stress condi-
tions, N was only significantly increased by dual G.
mosseae-Bacillus sp. inoculation, while no effect was
observed under stress conditions. Plant P content was
Table 1 Effect of Bacillus sp. on arbuscular mycorrhizal coloni-
zation as measured by trypan blue (TB), succinate dehydrogenase
(SDH) or alkaline phosphatase (ALP) staining in lettuce roots
subjected or not to PEG-induced drought stress. Treatments were
Gm (G. mosseae), Gi (G. intraradices), Gm+B (G. mosseae +
Bacillus sp.) and Gi+B (G. intraradices +Bacillus sp.).Within each
parameter, means with the same letter are not significantly different
according to Duncan’s multiple range test (P=0.05, n=3) (%F the
colonization frequency, given as the ratio between colonized root
fragments and the total number of root fragments observed, %m
colonization intensity, as an estimate of the amount of root cortex
that became mycorrhizal, relative only to the mycorrhizal root
fraction, %M the colonization intensity relative to the whole root
system, %a arbuscule abundance as an estimate of arbuscule
richness in the mycorrhizal root fraction, %A arbuscule abundance
as an estimate of arbuscule richness in the whole root system)
Staining %F %M %m %a %A
TB
No PEG
Gm 98 a 46.4 c 47.3 c 68.0 c 31.5 c
Gm+B 97 a 87.6 a 90.3 a 98.0 a 85.8 a
Gi 99 a 73.4 ab 74.1 ab 84.0 b 61.6 b
Gi+B 99 a 87.6 a 88.5 a 99.0 a 86.7 a
PEG
Gm 97 a 44.1 c 45.5 c 88.0 ab 38.8 bc
Gm+B 97 a 69.9 b 72.0 b 89.8 ab 62.8 b
Gi 99 a 42.4 c 42.8 c 84.0 b 35.6 c
Gi+B 97 a 72.0 ab 74.2 ab 100.0 a 72.0 a
SDH
No PEG
Gm 99 a 33.0 c 33.3 c 67.4 c 22.2 d
Gm+B 99 a 73.0 a 73.7 a 97.1 a 70.9 a
Gi 98 a 69.7 a 71.1 a 80.5 b 56.1 b
Gi+B 97 a 76.7 a 79.0 a 97.7 a 75.0 a
PEG
Gm 97 a 42.9 c 44.2 c 87.7 b 37.4 d
Gm+B 98 a 60.4 b 61.6 b 83.1 b 50.2 b
Gi 98 a 34.7 c 35.4 c 83.8 b 29.1 cd
Gi+B 99 a 71.7 a 72.4 a 96.1 a 68.9 a
ALP
No PEG
Gm 97 a 18.3 c 18.8 c 61.4 c 11.2 d
Gm+B 97 a 34.3 b 35.3 b 71.4 b 24.5 b
Gi 99 a 18.5 c 18.7 c 84.8 a 15.7 c
Gi+B 97 a 48.2 a 49.6 a 82.2 a 39.7 a
PEG
Gm 99 a 17.5 c 17.6 c 60.8 c 10.6 d
Gm+B 98 a 47.4 a 48.3 a 76.7 b 36.4 a
Gi 98 a 30.0 b 30.6 b 62.1 c 18.5 c
Gi+B 98 a 42.2 a 43.0 a 80.9 ab 34.1 a
252
increased by all the microbial treatments compared with
the uninoculated controls under non-stress conditions.
Again, no effect on P was found under stress conditions.
The K content under non-stress conditions was also
increased by all treatments. In contrast, under stress
conditions, plants inoculated with G. intraradices alone or
those dually inoculated with G. mosseae and Bacillus sp.
had the highest K content.
Discussion
We have shown that a rhizospheric bacterium isolated
from a desert soil and identified as Bacillus sp. can
influence the development and activity of two Glomus
species. No information is available about the mode of
action of mixed inocula on plant and/or fungal physio-
logical status or effects on plant performance under
drought stress. Under our experimental conditions, the
bacterium was as effective as G. mosseae in increasing
shoot growth and nutritional status. It also stimulated
Fig. 2 Proline content (mg g
FW–1) in lettuce plants subject-
ed or not to PEG-induced
drought stress. Treatments as in
Fig. 1. Means not followed by a
common letter differ signifi-
cantly (P=0.05) from each other
according to Duncan’s multiple
range test (n=5)
Table 2 Effect of Bacillus sp. and PEG-induced drought stress on
transpiration rate (mmol H20m
1 s1), photosynthetic rate (mmol
CO2m2 s1), water use efficiency (mmol CO2mol H201) and
stomatal conductance (mol H2Om
1 s1) of lettuce plants.
Treatments as in Table 1 plus C(control) and B(Bacillus sp.).
Within each parameter, means with the same letter are not
significantly different according to Duncan’s multiple range test
(P= 0.05, n=5)
Microbial treatments Transpiration Photosynthetic rate Water use efficiency Stomatal conductance
No PEG
C 2.59 a 8.92 e 3.45 d 7.43 d
B 2.36 b 5.79 f 2.46 e 12.14 c
Gm 2.32 b 10.48 c 4.52 c 14.26 ab
Gi 2.34 b 12.35 b 5.28 b 13.45 b
Gm+B 2.32 b 9.81 d 4.22 c 14.09 ab
Gi+B 2.25 b 12.86 a 5.75 a 15.19 a
PEG
C 2.22 b 4.52 bc 1.79 c 7.95 d
B 2.31 a 3.59 d 1.56 d 12.33 c
Gm 2.06 e 5.50 a 2.67 a 16.15 a
Gi 2.23 b 2.52 e 1.23 e 14.22 b
Gm+B 2.17 cd 4.22 c 1.95 c 15.04 ab
Gi+B 2.12 de 4.73 b 2.23 b 15.95 a
Fig. 3 Extraradical mycelium
production (cm g soil–1)by
mycorrhizal plants subjected or
not to PEG-induced drought
stress. Treatments as in Fig. 1.
Means not followed by a com-
mon letter differ significantly
(P=0.05) from each other ac-
cording to Duncan’s multiple
range test (n=5)
253
considerably the metabolic activity of the intraradical
mycelium developed in G. mosseae- and G. intraradices-
colonized roots, as well as the development of the
extraradical mycelium of G. intraradices. In fact, the
inoculation of AM plants with Bacillus sp. enhanced
fungal development and metabolism (in terms of SDH
and ALP) more than plant growth. The ability of Bacillus
sp. to increase the proportions of both alive and active
intraradical mycelium suggests a direct bacterial effect on
the metabolic status of these fungi. Thus, the production
of active metabolites such as vitamins, amino acids and
growth substances (e.g. indoleacetic acid) by this bacte-
rium (Vivas et al., unpublished results) could directly
stimulate the growth and metabolic capacity of AM
endophytes. The bacterium appears to act as a mycorrhi-
za-helper microorganism (Garbaye 1994; Barea 1997).
Another possibility is that the enhanced photosynthetic
rate found in plants dually inoculated with G. intraradices
and the bacterium affects the translocation of soluble
sugars to host roots, thus increasing fungal growth and
activity in the root (Amijee et al. 1989; Hetrick 1989).
Nevertheless, co-inoculation of this bacterium with G.
mosseae did not increase plant gas-exchange parameters
and, curiously, it enhanced intraradical fungal growth and
metabolism. The specific interactions between the bacte-
rium and each Glomus sp. on plant physiology and
metabolism were independent of drought stress and, thus,
seem not to be related to fungal growth.
The increases in photosynthetic rate, WUE and
stomatal conductance induced by bacterial inoculation
of G. intraradices-colonized plants, and the contrasting
effects on G. mosseae-infected plants, cannot be attribut-
ed to general stimulation by this bacterium of mycelial
growth and metabolic activity in the intraradical fungal
biomass developed by each endophyte. The effect seems
to be due to a specific microbe-microbe interaction that
modulates the effectivity of each AMF on plant physiol-
ogy. The specific microbial compatibilities determined
Fig. 4 N, P and K shoot contents (mg plant–1) in lettuce plant
subjected or not to PEG-induced drought stress. Treatments as in
Fig. 1. Means not followed by a common letter differ significantly
(P=0.05) from each other according to Duncan’s multiple range test
(n=5)
254
were not translated into a higher shoot biomass under the
experimental conditions used. We only found an in-
creased plant capacity for nutrient uptake, perhaps
because of higher fungal metabolic activity.
The lack of response by plants co-inoculated with G.
mosseae and Bacillus sp. may be explained by the fact
that the AM fungus plus the bacterium used plant
carbohydrates during early plant development and, thus,
created a carbon drain on the plant, as reported by
Johnson et al. (1997). In plants colonized with specific
microbial groups, the microbial carbon requirements and
below-ground respiration seem to be higher (Pang and
Paul 1980) and represent an important carbohydrate cost
for the plant. However, in treatments without PEG, the
mycorrhizal association stimulated photosynthetic rate
(see Table 2) and compensated the C cost, as pointed out
by Tinker et al. (1994). Thus, the assimilation, translo-
cation and utilization of fixed C are integrated processes
with a more complex interpretation in mycorrhizal plants
(Smith and Gianinazzi-Pearson 1990).
The decrease in photosynthetic activity as a conse-
quence of drought stress was greater in mycorrhizal plants,
particularly in those colonized by G. intraradices. This
photosynthetic depression caused by stress negatively
affected both extraradical fungal development and in-
traradical activity (SDH). Wright et al. (1998) estimated
that 4–20% of the total photosynthesized C was used by the
AM endophyte, and the fungal consumption of carbohy-
drates can be critical for plant physiological processes
when environmental conditions are limiting. The present
results suggest that, under stress conditions, either the
fungal respiration rate increased in G. intraradices-colo-
nized roots or the high C requirements in these roots
(Olsson and Johansen 2000) decreased more than the
amount of C fixed in tissues colonized by this fungus
(Smith and Smith 1996). Here, the differences in intrarad-
ical colonization levels do not explain differences in the
photosynthetic rate between the mycorrhizal treatments
under stress and non-stress conditions. However, plants
would respond differently to colonization by AM fungi
having different carbon requirements (Dodd et al. 2000).
The difference in the interactions between the bacte-
rium and each AM fungus was also evident in proline
accumulation in plant leaves. Proline accumulation is
involved in osmotic cellular adaptation, but no clear
relationship between proline, AM colonization and envi-
ronmental stress has been found (Ruiz-Lozano et al.
1995a). In this study, the increasing proline content under
PEG-induced drought stress is an indication of adjustment
of leaf osmotic potential, required for enhanced intracel-
lular osmotic balance. Plants exposed to drought stress
usually reduce the stomatal aperture to avoid water loss,
but we found no significant effect of PEG on this
parameter. In contrast, stressed plants increased drought
resistance by maintaining high levels of proline, photo-
synthetic activity and WUE. All these processes are
mechanisms by which plants can cope with drought stress
(Gale and Zeroni 1985; Ruiz-Lozano et al. 1995a).
The relative effectiveness of the two AM fungi results
from the development of arbuscules for nutrient transfer
between the symbionts (Varma and Hoock 1998).
According to our study, both the quantity and activity
of these arbuscules were increased by bacterial inocula-
tion. As a result, changes in nutrient transfer to the plant
and the equilibrium in the transfer of carbohydrates to the
fungus must occur in dually inoculated plants. But in the
soil-less medium used, with no nutrient limitation,
nutrient acquisition via AM fungus was not significant
for the plant. However, the effect of Bacillus sp.
enhancing intra- and sometimes extraradical fungal
growth and activity resulted in enhancement of the
nutrient content of G. intraradices-colonized plants.
In conclusion, it has been proposed that plants must be
mycorrhizal to thrive in degraded nutrient-poor and arid
soils (Barea 1991, 2000) and that mycorrhizal effects can
be improved by co-inoculation with mycorrhiza-helper
bacteria, which can play an important role in stressed
areas (Requena et al. 1996; Barea 1997). Results from this
present study show that co-inoculation of selected free-
living bacteria isolated from adverse environments and
AM fungi can improve the formation and function of the
AM symbiosis, particularly when the conditions for plants
growth are also adverse. Hence, to restore a self-
sustaining vegetation cover and to combat desertification,
we recommend dual AM fungus-bacterium inoculation.
Acknowledgements This work was financed by UE (Project
ICA4-CT-2001-10057). A.V. is grateful to Fundacin Gran
Mariscal de Ayacucho (Venezuela) and A.M. to ICI (CICYT,
Spain) for their respective research grants.
References
Amijee F, Tinker PB, Stribley DP (1989) The development of
endomycorrhizal root systems.7. A detailed study of the effect
of soil phosphorus on colonization. New Phytol 111:435–446
Amora-Lazcano E, Azcn R (1997) Response of sulphur cycling
microorganisms to arbuscular mycorrhizal fungi in the rhizo-
sphere of maize. Appl Soil Ecol 6:217–222
Amora-Lazcano E, Vzquez MM, Azcn R (1998) Response of
nitrogen transforming microorganisms to arbuscular mycor-
rhizal fungi. Biol Fertil Soils 27:65–70
Azcn R (1989) Selective interaction between free-living rhizo-
sphere bacteria and vesicular-arbuscular mycorrhizal fungi.
Soil Biol Biochem 21:639–644
Azcn R, Azcn-Aguilar C, Barea JM (1978) Effects of plant
hormones present in bacterial cultures on the formation and
responses to VA mycorrhiza. New Phytol 80:359–369
Azcn-Aguilar C, Barea JM (1985) Effect of soil microorganisms
on formation of VA mycorrhizas. Trans Br Mycol Soc 84:536–
539
Barea JM (1991) Vesicular-arbuscular mycorrhizae as modifiers of
soil fertility, In: Stewart BA (ed) Advances in soil science, vol
15. Springer, New York Berlin Heidelberg, pp 1–39
Barea JM (1997) Mycorrhiza-bacteria interactions on plant growth
promotion, In: Ogoshi A, Kobayashi K, Homma Y, Kodama F,
Kondo N, Akino S (eds) Plant growth promoting rhizobacteria.
Present status and future prospects. OECD, Paris, pp 50–158
Barea JM (2000) Rhizosphere and mycorrhizal of field crops, In:
Toutant P, Balazs E, Galante E, Lynch JM, Shepers JS, Werner
D, Werry PA (eds) Biological resource managements, connect-
255
ing science and policy (OECD). INRA and Springer, Berlin
Heidelberg New York, pp 110–125
Barea JM, Jeffries P (1995) Arbuscular mycorrhizas in sustainable
soil plant systems. In: Varma A, Hock B (eds) Mycorrhiza:
structure, function, molecular biology and biotechnology.
Springer, Berlin Heidelberg New York, pp 521–559
Barea JM, Gryndler M, Lemanceau P, Schepp H, Azcn R (2002)
The rhizosphere of mycorrhizal plants, In: Gianinazzi S,
Schepp H, Barea JM, Haselwandter K (eds) Mycorrhizal
technology in agriculture. From genes to bioproducts.
Birkhuser, Basel, pp 1–18
Bates LS, Waldren RP, Teare ID (1973) Rapid determination of
free proline for water stress studies. Plant Soil 39:205–207
Boddington CL, Dodd JC (1998) A comparison of the development
and metabolic activity of mycorrhizas formed by arbuscular
mycorrhizal fungi from different genera on two tropical forage
legumes. Mycorrhiza 8:149–157
Bowen GD, Rovira AD (1999) The rhizosphere and its manage-
ment to improve plant growth. Adv Agron 66:1–102
Dodd JC, Boddington CL, Rodriguez A, Gonzalez-Chavez C,
Mansur I (2000) Mycelium of arbuscular mycorrhizal fungi
(AMF) from different genera: form, function and detection.
Plant Soil 226:131–151
Duncan DB (1955) Multiple range and multiple F-tests. Biometrics
11:1–42
Gale J, Zeroni M (1985) The cost to plants of different strategies of
adaptation to stress and the alleviation of stress by increasing
assimilation. Plant Soil 89:57–67
Garbaye J (1994) Helper bacteria: a new dimension to the
mycorrhizal symbiosis. New Phytol 128:197–210
Giovannetti L, Ventura S, Bazzicalupo M, Fani R, Materassi R
(1990). DNA restriction fingerprint analysis of the soil
bacterium Azospirillum. J Gen Microbiol 136:1161–1166
Guillemin JP, Orozco MO, Gianinazzi-Pearson V, Gianinazzi S
(1995) Influence of phosphate fertilization on fungal alkaline
phosphatase and succinate dehydrogenase activities in arbus-
cular mycorrhiza of soybean and pineapple. Agric Ecosyst
Environ 53:63–69
Hetrick BAD (1989) Acquisition of phosphorus by VA mycorrhizal
fungi and the growth responses of their host plants. In: Boddy
L, Marchand RM, Read DJ (eds) Nitrogen, phosphorus and
sulphur utilization by fungi. Cambridge University Press,
Cambridge, pp 205–226
Hewitt EJ (1952) Sand and water culture methods used in the study
of plant nutrition. Tech Comm 22. Commonwealth Agricultural
Bureaux, Farnham Royal, UK
Jeffries P, Barea JM (1994) Biogeochemical cycling and arbuscular
mycorrhizas in the sustainability of plant-soil systems. In:
Gianinazzi S, Schepp H (eds) Impact of arbuscular mycor-
rhizas on sustainable agriculture and natural ecosystems.
Birkhuser, Basel, pp 101–115
Johnson NC, Graham JH, Smith FA (1997) Functioning of
mycorrhizal associations along the mutualism-parasitism con-
tinuum. New Phytol 135:575–586
Jones PCT, Mollinson JE (1948) A technique for the quantitative
estimation of soil micro-organisms. J Gen Microbiol 2:54–69
Lachica M, Aguilar A, Yaez J (1973) Anlisis foliar, mtodos
utilizados en la Estacin Experimental del Zaidn. Anal Edafol
Agrobiol 32:1033–1047
Lane DJ (1991) 16S/23S rRNA sequencing. In: Stackebrandt E,
Goodfellow M (eds) Nucleic acid techniques in bacterial
systematics. Wiley, New York, pp 115–147
Long SP, Hallgren JE (1987) Measurements of CO2 assimilation by
plants in the field and the laboratory. In: Coombs J, Hall DO,
Long SP, Scurlock JMO (eds) Techniques in bioproductivity
and photosynthesis, 2nd edn. Pergamon, Oxford, pp 62–94
Newman EI (1966) A method of estimating the total length of root
in a sample. J App Ecol 3:139–145
Olsen SR, Dean LA (1965) Phosphorus. In: Black CA, Evans DD,
White JL, Ensminger LE, Clark FE, Dinauer RC (eds) Methods
of soil chemical analysis, part 2. American Society of
Agronomy, Madison, Wis, pp 1035–1049
Olsson PA, Johansen A (2000) Lipid and fatty acid composition of
hyphae and spores of arbuscular mycorrhizal fungi at different
growth stages. Mycol Res 104:429–434
Pang PC, Paul EA (1980) Effects of vesicular-arbuscular mycor-
rhiza on C14 and N15 distribution in nodulated fababeans. Can
J Soil 60:241–250
Phillips JM, Hayman DS (1970) Improved procedure of clearing
roots and staining parasitic and vesicular-arbuscular mycor-
rhizal fungi for rapid assessment of infection. Trans Br Mycol
Soc 55:159–161
Requena N, Jimenez I, Toro M, Barea JM (1997) Interactions
between plant-growth-promoting rhizobacteria (PGPR), arbus-
cular mycorrhizal fungi and Rhizobium spp. in the rhizosphere
of Anthyllis cytisoides, a model legume for revegetation in
Mediterranean semi-arid ecosystems. New Phytol 136:667–677
Ruiz-Lozano JM, Azcn R (1996) Viability and infectivity of
mycorrhizal spores after long term storage in soils with
different water potentials. Appl Soil Ecol 3:183–186
Ruiz-Lozano JM, Azcn R (1997) Effect of calcium application on
the tolerance of mycorrhizal lettuce plants to polyethylene
glycol-induced water stress. Symbiosis 23:9–22
Ruiz-Lozano JM, Azcn R, Gmez M (1995a) Effects of arbus-
cular-mycorrhizal Glomus species on drought tolerance: phys-
iological and nutritional plant responses. Appl Environ
Microbiol 61:456–460
Ruiz-Lozano JM, Gmez M, Azcn R (1995b) Influence of
different Glomus species on the time-course of physiological
plant responses of lettuce to progressive drought stress periods.
Plant Sci 110:37–44
Ruiz-Lozano JM, Collados C, Barea JM, Azcn R (2001)
Arbuscular mycorrhizal symbiosis can alleviate drought-in-
duced nodule senescence in soybean plants. New Phytol
151:493–502
Smith FA, Smith SE (1996) Mutualism and parasitism: diversity in
function and structure in the ’’arbuscular’’ (VA) mycorrhizal
symbiosis. Adv Bot Res 22:1–43
Smith SE, Gianinazzi-Pearson V (1990) Phosphate uptake and
arbuscular activity in mycorrhizal Allium cepa L. Effects of
photon irradiance and phosphate nutrition. Aust J Plant Physiol
17:177–188
Tinker PB, Durall DM, Jones MD (1994) Carbon use efficiency in
mycorrhizas: theory and sample calculations. New Phytol
128:115–122
Tisserant B, Gianinazzi-Pearson V, Gianinazzi S, Gollotte A (1993)
In planta histochemical staining of fungal alkaline phosphatase
activity for analysis of efficient arbuscular mycorrhizal infec-
tions. Mycol Res 97:245–250
Trouvelot A, Fardeau JC, Plenchett C, Gianinazzi S (1986)
Nutritional balance and symbiotic expression in mycorrhizal
wheat. Physiol Veg 24:300
Varma A, Hoock B (1998) Mycorrhiza: structure, function,
molecular biology and biotechnology. Springer, Berlin Heidel-
berg New York
Vzquez MM, Bejarano C, Azcon R, Barea JM (2000) The effect of
a genetically modified Rhizobium meliloti inoculant on fungal
alkaline phosphatase and succinate dehydrogenase activities in
mycorrhizal alfalfa plants as affected by the water status in soil.
Symbiosis 29:49–58
Vierheilig H, Ocampo JA (1989) Relationship between SDH
activity and VA mycorrhizal infection. Agric Ecosyst Environ
29:439–442
Wright DP, Scholes JD, Read DJ (1998) Effects of VA mycorrhizal
colonization on photosynthesis and biomass production of
Trifolium repens L. Plant Cell Environ 21:209–216
256
... It has been reported that some volatile organic compounds emitted from Bacillus regulate Na + recirculation in the whole plant under saline conditions (Zhang et al. 2008). Bacillus bacteria applied externally in lettuce plants exposed to salt stress were effective in stem development of the plant (Vivas et al. 2003). In another study, it was determined that different Plant Growth-Promoting Rhizobacteria promoted the development of plant height and stem height in pepper plants against salt stress (Hahm et al. 2017 (Ayaz et al. 2022). ...
Article
Full-text available
Salinity is an important abiotic stress factor that negatively affects plant growth and yield. The study, the effect of microbial fertilizer containing Bacillus subtilis bacteria, commercially named Subtima, on salt stress in pepper was observed. Two different saline solutions (100 mM and 200 mM) were prepared to create salt stress in the plant growing medium. The fertilizer solution was applied to the plants in 4 different concentrations (300, 400, 500 and 600 ppm) from the leaves in the form of a spray. Morphological parameters such as plant height, stem length, leaf length, leaf width, and petiole length were measured. It was found that salt stress resulted in a decrease in plant morphological characteristics compared to the control group (0 mM salt + 0 ppm fertilizer). It was found that the most effective fertilizer dose to increase plant height (25.23 cm) at 100 mM salt stress was 400 ppm. At 200 mM salt stress, it was found that the most effective fertilizer dose for increasing plant height (22.67 cm) was an application of 300 ppm application. In general, fertilizer applications were found to be effective in reducing the negative effects of salt on the morphological traits studied.
Chapter
Managing abiotic stresses in agroecosystems is a critical challenge in modern agriculture. Climate change exacerbates these conditions, making it difficult to cultivate crops in productive areas. Arbuscular mycorrhizal fungi (AMF) have emerged as a promising solution to this problem. The symbiotic relationship between AMF and plants can increase nutrient efficiency, reduce water use, and promote soil health. However, certain questions require further exploration, such as: (a) How does AMF enhance plant resilience against abiotic stresses? (b) How can we favorize the occurrence of AMF in soils and boost the colonization of plant roots in agroecosystems? This chapter explores the role of AMF in the management of abiotic stress in agroecosystems. This review examines the edaphoclimatic factors contributing to abiotic stress, and reviews how AMF can improve plant growth and stress tolerance. With a better understanding of these mechanisms, AMF can be applied to improve plant growth and stress tolerance in agroecosystems. It is also necessary to develop more efficient and cost-effective methods for AMF inoculation. AMF can help farmers overcome the challenges of modern agriculture and achieve sustainable crop production in the face of climate change. This chapter also outlines the current challenges and limitations of AMF technology, as well as future perspectives and directions for research.
Chapter
Full-text available
There is a demand for novel fertilizers that can enhance agricultural productivity while simultaneously being more ecologically friendly than synthetic fertilisers. Nano-fertilizers are especially useful in precision agriculture for precise nutrient management, as they match the crop development stage for nutrients and may deliver nutrients throughout the crop growth cycle. Nano-fertilizers boost the surface area accessible for different metabolic processes in the plant, resulting in a higher rate of photosynthesis and greater crop dry matter and yield. It also defends the plant against numerous biotic and abiotic stressors. According to research, utilising Nano-fertilizers boosts nutrient utilisation efficiency, lowers soil toxicity, minimises the probable negative repercussions of overdosage, and reduces the frequency of application. Therefore, Nanotechnology offers a lot of potential for accomplishing sustainable agriculture, especially in impoverished countries.
Chapter
Full-text available
There is a demand for novel fertilizers that can enhance agricultural productivity while simultaneously being more ecologically friendly than synthetic fertilisers. Nano-fertilizers are especially useful in precision agriculture for precise nutrient management, as they match the crop development stage for nutrients and may deliver nutrients throughout the crop growth cycle. Nano-fertilizers boost the surface area accessible for different metabolic processes in the plant, resulting in a higher rate of photosynthesis and greater crop dry matter and yield. It also defends the plant against numerous biotic and abiotic stressors. According to research, utilising Nano-fertilizers boosts nutrient utilisation efficiency, lowers soil toxicity, minimises the probable negative repercussions of overdosage, and reduces the frequency of application. Therefore, Nanotechnology offers a lot of potential for accomplishing sustainable agriculture, especially in impoverished countries.
Book
Full-text available
Agronomy, the science of crop production and soil management, has witnessed significant advancements in recent years, driven by the growing global demand for food, coupled with the need for sustainable and resource-efficient agricultural practices. This book provides an overview of the key developments in agronomy that contribute to increased productivity, resource optimization, and environmental stewardship.
Article
Full-text available
1 ‫الكتخراتا‬ ‫استخخدام‬ ‫كفاءة‬ Bacillus subtilis ‫ية‬ ‫الفيتيولو‬ ‫ا‬ ‫المموراتة‬ ‫تفاة‬ ‫ال‬ ‫اتص‬ ‫تا‬ ‫اثارير‬ ‫ممتو‬ ‫كمتظم‬ ‫الخمر‬ ‫مخيل‬ ‫لفيائل‬ (Phoenix dactylifera L.) ‫واد‬ ‫اال‬ ‫ظراف‬ ‫ثحت‬ ‫الملحص‬ ‫اس‬ ‫سال‬ ‫ص‬ ‫ما‬ ‫صالح‬ ‫دااد‬ ‫الرحمن‬ ‫عكد‬ ‫مياعد‬ ‫أسخاذ‬ ‫مياعد‬ ‫أسخاذ‬ ‫اق‬ ‫العر‬ / ‫رة‬ ‫الك‬ ‫امعة‬ / ‫الظخيل‬ ‫أبحاث‬ ‫مركز‬ : ‫االلكخرامص‬ ‫الكراد‬ alhamadabd5@gmail.com ‫الميخخلص‬ : ‫للموسم‬ ‫ة‬ ‫البصر‬ ‫جامعة‬ ‫النخيل‬ ‫ابحاث‬ ‫لمركز‬ ‫البالستيكي‬ ‫البيت‬ ‫و‬ ‫ات‬ ‫مختبر‬ ‫في‬ ‫اسة‬ ‫الدر‬ ‫يت‬ ‫اجر‬ 2016-2017 ‫يا‬ ‫البكتر‬ ‫فعالية‬ ‫تقييم‬ ‫الى‬ ‫وهدفت‬ Bacillus subtilis ‫تحمل‬ ‫في‬ ‫التمر‬ ‫نخيل‬ ‫فسائل‬ ‫ة‬ ‫قدر‬ ‫تحسين‬ ‫في‬ ‫الف‬ ‫الصفات‬ ‫تحسين‬ ‫في‬ ‫لها‬ ‫االيجابية‬ ‫ات‬ ‫التأثير‬ ‫اسة‬ ‫در‬ ‫وكذلك‬ ‫الملحي‬ ‫االجهاد‬ ‫ظروف‬ ‫المختلفة‬ ‫سيولوجية‬ ‫يا‬ ‫البكتر‬ ‫ة‬ ‫قدر‬ ‫ية‬ ‫المختبر‬ ‫اسة‬ ‫الدر‬ ‫نتائج‬ ‫.اظهرت‬ B.subtilis ‫بلغ‬ ‫،اذ‬ ‫ة‬ ‫المختبر‬ ‫الملحية‬ ‫اكيز‬ ‫التر‬ ‫في‬ ‫النمو‬ ‫على‬ ‫يا‬ ‫البكتر‬ ‫اعداد‬ ‫معدل‬ 0.55 ‫و‬ 0.44 ‫و‬ 0.43 × 10 8 ‫ة‬ ‫مستعمر‬ ‫تكوين‬ ‫وحدة‬. ‫مل‬-1 ‫الملحية‬ ‫اكيز‬ ‫التر‬ ‫عند‬ 5 ‫و‬ 10 ‫و‬ 15 ‫م‬ ‫ديسيمنز‬-1 ‫نتا‬ ‫اظهرت‬ ‫كما‬ ‫الي‬ ‫التو‬ ‫على‬ ‫يا‬ ‫البكتر‬ ‫فعالية‬ ‫البالستيكي‬ ‫البيت‬ ‫بة‬ ‫تجر‬ ‫ئج‬ B.subtilis ‫الى‬ ‫ادت‬ ‫اذ‬ ‫معنوي‬ ‫وبشكل‬ ‫ة‬ ‫المذكور‬ ‫الملحية‬ ‫اكيز‬ ‫التر‬ ‫في‬ ‫بها‬ ‫المعاملة‬ ‫النباتات‬ ‫في‬ ‫النمو‬ ‫ات‬ ‫مؤشر‬ ‫تحسين‬ ‫على‬ ، ‫الجذري‬ ‫و‬ ‫الخضري‬ ‫المجموعين‬ ‫من‬ ‫لكل‬ ‫الجاف‬ ‫و‬ ‫الطري‬ ‫ن‬ ‫الوز‬ ‫معدالت‬ ‫يادة‬ ‫وز‬ ‫النباتات‬ ‫ال‬ ‫اطو‬ ‫معدل‬ ‫يادة‬ ‫ز‬ ‫يادة‬ ‫ز‬ ‫كذلك‬ ‫الكلوروفيل‬ ‫صبغات‬ ‫من‬ ‫الكلي‬ ‫اق‬ ‫االور‬ ‫محتوى‬ b+a ‫الملحية‬ ‫اكيز‬ ‫بالتر‬ ‫المعاملة‬ ‫النباتات‬ ‫مع‬ ‫نة‬ ‫مقار‬ ‫فقط‬ ‫ة‬ ‫المذكور‬. ‫بتخراا‬ ‫الخمر،‬ ‫مخلة‬ ‫المفخاحية:‬ ‫الكلمات‬ Bacillus subtilis ‫الملحص.‬ ‫واد‬ ‫اال‬ ، Impact of growth promoting Bacillus subtilis on the growth and physiological characteristies of Date palm plantlets (Phoenix dac-tylifera L.) under salt stress conditions. Abstract: The present study has been conducted at the lab. And green house of date palm research central Basrah University to evaluate the efficiency of Bacillus subtilis in date palm plantlets growth promoting, as well as, their effect on salt stress tolerance for treated date palm plants; during the season of 2016-2017. Results of lab. Experiments revealed the ability of B.subtilis to grow on various salt concentrations ,the colony forming units were 0.55, 0.44 and 0.43×10 8 cfu/ml of examined
Chapter
For a variety of reasons, more and more individuals are searching for alternatives to synthetic chemicals. In addition to other factors, synthetic chemicals used in disease prevention and control have the potential to have harmful effects on the environment. As a remedy for plant illnesses that are spread through the soil, plant growth-promoting rhizobacteria (PGPR) are discussed in this chapter. Pesticide-resistant gram-positive bacteriophages and biocontrol agents, as well as biopesticides, biofertilizers, and soil inoculants, are among the various concepts and nomenclatures examined in this study. Biological control agents, biopesticides, and soil inoculants are all investigated in this study. As a biocontrol agent, PGPR has its advantages and disadvantages. We also discuss the possible hazards of utilizing PGPR. Metabolites of PGPR are examined in this study, as is their role in the control of soilborne illnesses. It accomplishes this by presenting many case studies that act as examples. For the use of growth-promoting rhizobacteria to combat soilborne diseases, there are several more interesting case studies included in this collection. The biocontrol activities of PGPR have been extensively documented. Among these are the creation of antibiotics, siderophores, and enzymes that dissolve cell walls, as well as the development of systemic resistance, the efficacy of root colonization, and rhizosphere competency.
Article
Full-text available
To date, the effect of Olive-Mill-Wastewater-Compost (OMWW-Compost) application combined with rhizospheric soil micro-organisms on tomato fruits biochemistry and quality under drought conditions has not been evaluated. The objective of this study is to highlight the effect of arbuscular-mycorrhizal-fungi (pure strain (M) and consortium (M’)), and/or plant growth-promoting-rhizobacteria (Actinomycetes (A) and consortium of two bacterial strains (B)), and/or OMWW-compost (C), on production, quality, fruits biochemistry and antioxidant richness under drought stress. The application of CM’A and CM’B increased the carotenoid content to 94 and 79%, as well as increased the phenol content to 66 and 51% respectively, compared to the control under stress conditions. The CM’A improved total tocopherols and ascorbic acid contents in fruits to 57 and 85% respectively, compared to the control under water stress. Dual inoculation of bacteria and mycorrhizal fungi combined with OMWW-compost appears to be a suitable alternative for drought stress management. The application of OMWW-compost in combination with rhizosphere microorganisms seems to offer the hope of a relatively cheap, easy to apply and effective way to alleviate drought stress and improve tomato fruits quality.
Chapter
Full-text available
The world's population is predicted to reach more than nine billion people by 2050, a third more people than there are now to feed (FAO, 2018). Therefore, advances in biologically based technology need to be implemented immediately if we are to boost crop output, attain worldwide food safety, and guarantee enough nutrition. Intense and commercial agriculture's overreliance on chemical fertilisers and pesticides has been linked to the emergence of new environmental dangers and climate change. As a sustainable method for the creation of eco-friendly substitutes to synthetic fertilisers, the direct and indirect utilisation of advantageous microbial inoculants is quickly receiving attention. The ability of multiracial growth-promoting microbial consortium-based biofertilizers to promote soil nutrients, reduce biotic and abiotic stresses, increase soil microbial diversity, and ensure food safety is what makes them so admired. Growing organic agriculture and consumer perceptions of safe and healthful foods in the wake of the pandemic COVID-19 incidence are the key factors driving the enormous demand for microbiological inoculants or biofertilizers around the world. This chapter critically assesses the state-of-the-art in the application of microbial strains of bacteria and fungus as microbial consortium biofertilizers and the significant contributions made by these beneficial microbes to preserving soil fertility and boosting crop output.
Article
Full-text available
Although the effect of arbuscular-mycorrhizal (AM) fungi on drought alleviation has been studied, there is little information on the role of Ca as a drought stress reliever in mycorrhizal symbiosis. Lactuca sativa plants were grown in a soil/sand mixture (1/9 v/v) with application of a nutrient solution containing increasing amounts of Ca. The water stress was imposed by dipping the plant root systems in the appropriate polyethylene glycol (PEG) solution for 22 h. The calcium increase in the medium decreased the colonizing ability of the fungi (Glomus mosseae and G. fasciculatum) assayed, but did not affect the growth of the mycorrhizal plants. In contrast, the control plants decreased their growth when the calcium reached 8 mM. Under both severe and moderate stress, mycorrhizal plants had decreased proline accumulation in response to the increase in Ca availability, indicating that mycorrhizal plants suffered less from the detrimental effect of PEG-induced water stress as a consequence of the Ca increase in the medium. Results of treatments on relative water content (RWC) paralleled those of proline. With 4 mM Ca in the medium, the mycorrhizal plants were more negatively affected by PEG application than the control plants, but above this calcium level the proline content decreased and the RWC increased in mycorrhizal plants. In the control plants the behaviour was reversed. This response could be due to the higher membranous surface area in mycorrhizal plants than in nonmycorrhizaI plants. In conclusion, the application and uptake of increasing amounts of Ca enhances the tolerance of mycorrhizal plants to PEG-induced water stress.
Article
Full-text available
A great diversity of plants and fungi engage in mycorrhizal associations. In natural habitats, and in an ecologically meaningful time span, these associations have evolved to improve the fitness of both plant and fungal symbionts. In systems managed by humans, mycorrhizal associations often improve plant productivity, but this is not always the case. Mycorrhizal fungi might be considered to be parasitic on plants when net cost of the symbiosis exceeds net benefits. Parasitism can be developmentally induced, environmentally induced, or possibly genotypically induced. Morphological, phenological, and physiological characteristics of the symbionts influence the functioning of mycorrhizas at an individual scale. Biotic and abiotic factors at the rhizosphere, community, and ecosystem scales further mediate mycorrhizal functioning. Despite the complexity of mycorrhizal associations, it might be possible to construct predictive models of mycorrhizal functioning. These models will need to incorporate variables and parameters that account for differences in plant responses to, and control of, mycorrhizal fungi, and differences in fungal effects on, and responses to, the plant. Developing and testing quantitative models of mycorrhizal functioning in the real world requires creative experimental manipulations and measurements. This work will be facilitated by recent advances in molecular and biochemical techniques. A greater understanding of how mycorrhizas function in complex natural systems is a prerequisite to managing them in agriculture, forestry, and restoration.
Chapter
Providing that appropriate carbon substrates are available, microbial communities are able to develop a range of activities which are crucial in maintaining a biological balance in soil (Bowen and Rovira 1999), a key issue for the sustainability of either natural ecosystems or agroecosystems (Kennedy and Smith 1995). Soil-borne microbes have a particular microhabitat in which to flourish. In particular, they are bound to the surface of soil particles or found in soil aggregates, while others interact specifically with the plant root system (Glick 1995). The root-soil interface is actually a dynamic changing environment, a microcosm where microorganisms, plant roots and soil constituents interact (Lynch 1990; Azcón-Aguilar and B area 1992; Linderman 1992; B area 1997, 2000, Kennedy 1998; Bowen and Rovira 1999; Gryndler 2000), to develop what is known as the rhizosphere (Hiltner 1904). The rhizosphere, therefore, is the zone of influence of plant roots on the associated microbiota and soil components, and is clearly a different physical, chemical and biological environment from the bulk soil (Bowen and Rovira 1999), where an altered microbial diversity and increased activity and number of microorganisms is characteristic (Kennedy 1998).Actually, the structure and diversity of populations of fluorescent pseudomonads associated with roots were shown to differ significantly from those of soil populations. Rhizosphere and non-rhizosphere populations could be discriminated on the basis of their ability to use specific organic compounds (Lemanceau et al. 1995; Latour et al. 1996), to mobilize ferric iron (Lemanceau et al. 1988) or to reduce nitrogen oxides (Clays-Josserand et al. 1995).
Article
A time-course pot experiment was designed to compare the effect of two Rhizobium meliloti strains, the wild type (WT) and its genetically modified (GM) derivate, on the physiological activity of the arbuscular mycorrhizal (AM) fungus Glomus mosseae during the colonization of alfalfa (Medicago sativa L.) roots as affected by the water status in the growing medium using histochemical staining methods as succinate dehydrogenase (SDH) and alkaline phosphatase (ALP) enzyme markers. At each harvest time, and for each water level, there were no significant differences in plant growth response between the effect of the two rhizobial WT and GM treatments on AM-plants. This is an unexpected result because the GM strain usually behaves as an improved rhizobial inoculant. Nodulation followed already described patterns, i.e. the GM strain produced less, but bigger, nodules than the WT strain. In spite of the lack of an improved growth response to the GM strain, this did not adversely affect the development of the AM symbiosis (Glomus mosseae-Medicago sativa). It was also found that, under well-watered conditions, about 80% of the AM mycelium in plants inoculated with the GM Rhizobium was alive (SDH activity) throughout the experiment, while only 10-20% of the intraradical mycelium remained alive in plants inoculated with the WT strain. Both rhizobial strains behaved similarly under water-limiting conditions in regard to AM development.
Article
This chapter discusses the measurement of carbon dioxide (CO2) assimilation by plants in the field and the laboratory. Growth of crops is usually determined from dry weight change during destructive harvesting. CO2 uptake provides an alternative and direct measure of productivity, with important advantages over measurements of dry-weight change: it is instantaneous, non-destructive, and it allows separate investigation of individual leaves and separation of photosynthetic gain from respiratory losses. The majority of CO2 exchange studies have involved enclosure methods. The rate of CO2 assimilation by the material enclosed is determined by measuring the change in the CO2 concentration of the air flowing across the chamber. Alternatively, CO2 exchange of large areas of vegetation may be measured without enclosure, using micrometeorological techniques. Meteorological principles have been widely applied in the prediction of water and heat exchange from crop canopies. These principles may also be applied to the study of CO2 transfer.
Chapter
It has become clear that microbial activity must be considered a key component among those conferring “soil fertility,” i.e., the ability of a given soil to support plant development and nutrition (Pauli, 1967). The major components interacting to determine “soil fertility” are depicted in Figure 1. Accordingly, “fertility” can be considered an inherent property of a given soil. However, the plant itself is able to modify soil fertility in two different ways. One is based on the “rhizosphere effect” exerted by the plant, which can alter the fluxes of energy and the supply of substrates for soil microorganisms. The other way is based on the inherently different growth rates and metabolism of the different plant species that are known to “change” the capacity of the soil to provide each particular plant with nutrients (Hayman, 1975).