|
Background and Objectives:
Use of plant growth promoting rhizobacteria (PGPR) as
microbial inoculant to increase agricultural production, biocontrol of
plant pathogens and aid in bioremediation is getting world wide
attention. Potential positive impacts of PGPR have been demonstrated in
crops like radish, potato, sugarbeet, bean, barley, vegetables, canola,
pea, peanut and many other crops. Although PGPR may reveal huge
potential for crop production, for a microbial inoculant to be
commercially feasible, it must be economically mass-produced and
formulated into a cost-effective, uniform and readily applicable form
(Walter and Paau 1997). Success of microbial inoculant for enhanced
crop production is also greatly influenced by the number of viable cells
introduced into soil (Duquenne et al. 1999) as biological activity may
decline rapidly with handling and storage procedure. Thus, it is
critical that a PGPR inoculant product be in such a formulation, which
would not only deliver adequate bacterial population but also have
enough product shelf life.
Presumably the most successful and recognizable PGPR
to be used as microbial inoculant for agricultural crops is that based
on Rhizobium spp. through symbiotic nitrogen fixation (Chanway et
al. 1989). Several other mechanisms like phytohormone production (Brown
1974), extracellular siderophore production (Kloepper et al. 1980),
effects on ion uptake by roots (Lifshitz et al. 1987) and induced
systemic resistance (Wei et al. 1996) have also been credited for their
growth promoting activity. Although the mechanism of enhanced sulfur
oxidation by PGPR resulting in increased crop performance (Grayston and
Germida 1991; Banerjee 1995) little information is available on
successful application of sulfur-oxidizing PGPR as inoculant for
agricultural crops.
Canola (Brassica napus L. cv), like other oil
seed crops has high sulfur (S) demand. Crop growth and production
decline when canola is grown in S deficient soils in Europe and
elsewhere (Scherer 2001). The fertilizer industry is promoting
elemental S fertilizer to replenish S deficiency because of its
concentrated form, slow release characteristics and that it is an
available industrial by-product. However, elemental S must be oxidized
to sulfate form to become plant available. This conversion is generally
carried out by S-oxidizing soil microorganisms that need 18-24 months.
To accelerate the process of S oxidation, BioBoost, a S-oxidizing PGPR
(Banerjee and Yesmin 2002) inoculant was utilized as canola seed
treatment to meet the plant S requirement and to increase canola
production. Others have isolated and identified canola PGPR for canola
growth promotion (Kloepper et al. 1988; Bertrand et al. 2001), but our
research selected and used S-oxidizing PGPR to produce the first
commercial inoculant for canola. Much work is needed to demonstrate the
mass production of this S-oxidizing inoculant to be technologically and
commercially viable.
Procedure and
Project Activities:
BioBoost Inoculant
The active ingredient of the product BioBoost is the
S-oxidizing rhizobacteria identified as Delftia acidovorans
RAY209 using 16S rDNA method. The strain RAY209 is inoculated to the
gamma irradiated sterile Canadian sedge peat powder of 300 mesh. The
inoculated packets are incubated at 28oC for 7 days for
microbial proliferation and are ready to use for seed inoculation.
Field Trials
To test the efficacy of the product BioBoost in the
Canadian prairies, four field trials in year 2002 (Dauphin, Miami, La
Salle and MCDC) and seven field trails in year 2003 (Dauphin, Neepawa,
La Salle, Elm Creek, Gladstone, MacGregor and Millet) were carried out.
The trials were laid as Randomized Complete Block Design (RCBD) with
six to eight replications in each site. Each replication was considered
as a block and the treatments were randomized within each block. Sulfur
fertilizer was added either as elemental sulfur (ES) or as sulfate
sulfur (SO4) at seeding. Elemental S was applied with seed,
and, sulfate S was broadcast and raked into the soil. Fungicide (Helix)
treated, herbicide-tolerant canola, cultivar Libred 799 RR was used in
these trials. The seeding rate of the canola used was 6 lbs/ac (6.72
kg/ha). The ratio of canola seed: sticker: peat inoculant was 1000 g :
40 ml : 60 g. Coating of seeds with peat inoculant was done on the
field site just before seeding. Seeding was done using plot seeder.
During the experiments, all the plots were maintained following the
standard maintenance for canola production in the region. All the plots
were harvested singly with plot combine. For each plot, harvested seed
samples were bagged separately and weighed to get yield per plot basis.
Seed moisture was measured to get moisture corrected yield result (8.5%
seed moisture basis).
Nutrient Uptake and Seed Quality
From each plot small sub samples were prepared for
seed nutrient and quality analyses. Seed nutrient analyses were done
using acid digestion and Inductively Coupled Plasma Atomic Emission
Spectroscopy (ICP-AES) method, and, other seed quality analyses were
done using Near Infra Red Spectroscopy (NIRS) method.
Results and Discussion:
Table 1. 2002 Field trials: canola yield (kg/ha).
|
Treatment |
Location |
|
Dauphin |
Miami |
La Salle |
MCDC |
|
Control (C) |
988.14 |
1348.53 |
2336.41 |
2145.45 |
|
C+ES |
970.34 |
1322.75 |
2367.25 |
2154.65 |
|
C+SO4 |
1115.00 |
1344.18 |
2398.62 |
2160.76 |
|
C+BioBoost |
1096.63 |
1358.65 |
2367.92 |
2165.10 |
|
C+ES+BioBoost |
1120.13 |
1497.61 |
2411.15 |
2222.69 |
|
C+SO4+BioBoost |
1132.59 |
1378.67 |
2524.65 |
2209.72 |
|
LSD (5%) |
71.63 |
33.55 |
58.66 |
NS |
BioBoost is a contaminant free peat inoculant for
canola containing 100 million (1X108) viable cells of a
selected strain of Delftia acidovorans per gram of peat and
optimized to survive to the desired level in peat bag over five months
from the date of production. Table 1 showed that the BioBoost inoculant
increased canola yield in different field trials in the year 2002. The
bacteria alone or in combination with other S fertilizers has increased
canola yield by 109-145 kg/ha, 10-149 kg/ha, 32-188 kg/ha and 20-77
kg/ha in Dauphin, Miami, La Salle and MCDC, respectively. Although not
all the increases were significant, positive trends in canola production
were observed in all the sites upon bacterial inoculation. When
inoculant was used in combination with elemental S or sulfate S yield
increase was more evident over control. Inoculant in combination with
ES showed significant (p<0.05) yield increase above control in Dauphin,
Miami and La Salle.
Table 2. 2003 Field trials: canola yield (kg/ha).
|
Treatment |
Location |
|
Dauphin |
Neepawa |
La Salle |
Elm Creek |
Gladstone |
MacGregor |
Millet |
|
Control (C) |
1492.55 |
796.60 |
2161.01 |
2649.93 |
1342.17 |
2336.81 |
1489.39 |
|
C+ES |
1467.60 |
1083.41 |
2163.70 |
2650.13 |
1599.46 |
2464.88 |
1560.86 |
|
C+SO4 |
1603.88 |
1095.67 |
2270.58 |
2700.36 |
1788.35 |
2507.55 |
1639.01 |
|
C+BioBoost |
1574.24 |
1238.22 |
2248.75 |
2700.44 |
1705.04 |
2439.46 |
1733.14 |
|
C+ES+BioBoost |
1625.25 |
1295.72 |
2280.19 |
2811.76 |
1722.05 |
2583.83 |
1771.21 |
|
C+SO4+BioBoost |
1618.14 |
1301.12 |
2265.34 |
2648.27 |
1903.51 |
2541.23 |
1682.47 |
|
LSD (5%) |
70.56 |
123.58 |
89.18 |
81.81 |
287.50 |
NS |
NS |
Table 2 also showed that the BioBoost inoculant
increased canola yield in different field trials in the year 2003.
Although not all the increases were significant but positive trends in
canola production were observed in all seven sites upon bacterial
inoculation. Significant (p<0.05) increases in canola yield were
obtained due the bacterial inoculation in Dauphin, Neepawa, La Salle,
Elm Creek and Gladstone. When inoculant was used in combination with ES
or sulfate S yield increase over control was also quite evident. Inoculant
in combination with ES showed significant (p<0.05) yield increase above
control in Dauphin, Neepawa, La Salle, Elm Creek and Gladstone.
Results of the field seed samples analyzed for S
concentration and seed quality showed that with yield increase, use of
inoculant increased S uptake (Table 3) and retained all quality aspects
of canola seed (Table 4). Thus, BioBoost inoculant with ES combination
not only increase canola yield significantly compared to control but
also compete with sulfate S treatment.
Table 3. Seed sulfur uptake of canola inoculated
with BioBoost in 2002 Dauphin field trial site.
|
Treatment |
S concentration
(%) |
S uptake
(kg/ha) |
% Change in S uptake from control |
|
Control (C) |
0.43 |
4.25 |
0 |
|
C+ES |
0.43 |
4.13 |
-2.8 |
|
C+SO4 |
0.46 |
5.10 |
20.0 |
|
C+BioBoost |
0.44 |
4.83 |
13.7 |
|
C+ES+BioBoost |
0.43 |
4.84 |
13.9 |
|
C+SO4+BioBoost |
0.46 |
5.18 |
21.9 |
|
LSD (5%) |
NS |
0.42 |
- |
Table 4. Seed quality of canola inoculated with
BioBoost in 2002 Dauphin field trial site.
|
Treatment |
Oil Content (%) |
Protein Content (%) |
Oleic Acid (%) |
Linolenic Acid (%) |
Glucosinolate Content (μmol/g) |
|
Control (C) |
49.13 |
22.10 |
58.35 |
7.77 |
14.45 |
|
C+ES |
48.43 |
23.08 |
57.65 |
7.93 |
14.52 |
|
C+SO4 |
48.22 |
23.45 |
58.08 |
8.27 |
15.02 |
|
C+BioBoost |
48.57 |
22.57 |
58.23 |
8.25 |
15.45 |
|
C+ES+BioBoost |
48.93 |
22.25 |
57.83 |
8.02 |
14.97 |
|
C+SO4+BioBoost |
48.45 |
23.08 |
58.72 |
8.85 |
15.48 |
|
LSD (5%) |
NS |
NS |
NS |
NS |
NS |
Conclusion:
The overall field efficacy results with BioBoost
evidently showed that this inoculant can work as canola PGPR to enhance
canola production in Western Canada. This naturally occurring
S-oxidizing rhizobacterial inoculant retained all the seed quality
aspects of canola. The BioBoost peat inoculant can also provide farmers
with agronomic benefits of reduced input cost and better crop yield in
an environment friendly manner. Thus, this research has developed a new
microbial inoculant that is the first S-inoculant for canola to the best
of our knowledge.
Acknowledgements:
This project was made possible due to funding from
the Government of Manitoba and Canada through the Canada-Manitoba
Agri-Food Research and Development Initiative (ARDI).
References:
Banerjee MR (1995). Sulfur-oxidizing bacteria as a
potential canola plant growth promoting rhizobacteria. In
‘Phytochemicals and Health’. (Eds. D. L. Gustine and H. E.Flores), pp.
179-181. (American Society of Plant Physiologists).
Banerjee MR and Yesmin L (2002). Sulfur oxidizing
rhizobacteria: an innovative environment friendly soil biotechnological
tool for better canola production. Proceedings of AGROENVIRON 2002,
October 26-29, pp. 1-7. (Cairo, Egypt).
Bertrand H, Nalin R, Bally R and Cleyet-Marel JC
(2001). Isolation and identification of the most efficient plant
growth-promoting bacteria associated with canola (Brassica napus).
Biology and Fertility of Soils 33, 152-156.
Brown ME (1974). Seed and root bacterization. Annual
Review of Phytopathology 12, 181-197.
Chanway CP, Hynes RK and Nelson LM (1989). Plant
growth-promoting rhizobacteria: Effects on growth and nitrogen fixation
of lentil (Lens esculenta Moench) and pea (Pisum sativum
L.). Soil Biology and Biochemistry 21, 511-517.
Duquenne P, Chenu C, Richard G and Catroux G (1999).
Effect of carbon source supply and its location on competition between
inoculated and established bacterial strains in sterile soil microcosm.
FEMS Microbial Ecology 29, 331-339.
Grayston SJ and Germida JJ (1991). Sulfur-oxidizing
bacteria as plant growth promoting rhizobacteria for canola. Canadian
Journal of Microbiology 37, 521-529.
Kloepper JW, Leong J, Teintze M and Schroth MN
(1980). Enhanced plant growth by siderophores produced by plant
growth-promoting rhizobacteria. Nature (London) 286, 885-886.
Kloepper JW, Hume DJ, Scher FM, Singleton C, Tipping
B, Aliberte MI, Frauley K, Kutchaw T, Simonson C, Lifshitz R, Zaleska I
and Lee L (1988). Plant growth-promoting rhizobacteria on canola
(rapeseed). Plant Disease 72, 42-46.
Lifshitz R, Kloepper JW, Kozlowski M, Simonson C,
Carlson J, Tipping EM and Zaleska I (1987). Growth promotion of canola
(rapeseed) seedlings by a strain of Pseudomonas putida under
gnotobiotic conditions. Canadian Journal of Microbiology 33, 390-395.
Scherer HW (2001). Sulphur in crop production –
invited paper. European Journal of Agronomy 14, 81-111.
Walter JF and Paau AS (1997). Microbial inoculant
production and formulation. In ‘Soil Microbial Ecology: Applications in
Agricultural and Environmental Management’. (Ed. F. B. Metting Jr), pp.
579-594. (Marcel Dekker, Inc., New York).
Wei G, Kloepper, JW and Tuzun S (1996). Induced
systemic resistance to cucumber diseases and increased plant
growth-promoting rhizobacteria under field conditions. Phytopathology
86, 221-224.
|