Previous Article | Next Article 
Applied and Environmental Microbiology, April 2000, p. 1527-1531, Vol. 66, No. 4
0099-2240/00/$04.00+0
Copyright © 2000, American Society for Microbiology. All rights reserved.
Increased Growth of the Microalga Chlorella vulgaris
when Coimmobilized and Cocultured in Alginate Beads with the
Plant-Growth-Promoting Bacterium Azospirillum
brasilense
Luz E.
Gonzalez1 and
Yoav
Bashan2,*
Department of Biology, Pontificia Universidad
Javeriana, Santafe de Bogota, Colombia,1 and
The Center for Biological Research of the Northwest (CIB), La
Paz, B.C.S. 23000, Mexico2
Received 27 October 1999/Accepted 20 January 2000
 |
ABSTRACT |
Coimmobilization of the freshwater microalga Chlorella
vulgaris and the plant-growth-promoting bacterium
Azospirillum brasilense in small alginate beads resulted in
a significantly increased growth of the microalga. Dry and fresh
weight, total number of cells, size of the microalgal clusters
(colonies) within the bead, number of microalgal cells per cluster, and
the levels of microalgal pigments significantly increased. Light
microscopy revealed that both microorganisms colonized the same
cavities inside the beads, though the microalgae tended to concentrate
in the more aerated periphery while the bacteria colonized the entire
bead. The effect of indole-3-acetic acid addition to microalgal culture
prior to immobilization of microorganisms in alginate beads
partially imitated the effect of A. brasilense. We
propose that coimmobilization of microalgae and
plant-growth-promoting bacteria is an effective means of
increasing microalgal populations within confined environments.
 |
INTRODUCTION |
Microalgae have many uses. They can
serve as water bioremediation agents (40), as feed for
aquaculture (17), as food for humans and animals
(10), in pigment production (25), in bioremoval of heavy metals (49), and in agriculture (33). It
is usually desirable to establish large populations of microalgae,
especially in aquatic environments where they are often employed. One
means of increasing microalgal populations may be to inoculate them with other microorganisms, a strategy that is being tested for its
potential to increase yields of agriculturally important plants (5, 23, 32).
One candidate microorganism for coinoculation with microalgae is
Azospirillum brasilense, a member of the group of plant
rhizosphere bacteria known as plant-growth-promoting bacteria (PGPB)
(6, 20, 29). This relatively well-studied diazotrophic
bacterium (5) promotes the growth of many terrestrial plants
upon seed or root inoculation and increases the yields of numerous crop plants (8, 37). All the known Azospirillum
species produce plant hormones, mainly auxins, as do many other PGPB.
It is thought that interference with the hormonal metabolism of the
host plant is one of the major ways in which PGPB affect plant growth
(15, 41).
The aim of this study was to increase the growth of the freshwater
microalga Chlorella vulgaris, an important organism in tertiary wastewater treatment (21, 30, 44) and for several industrial research studies (27, 48), by inoculating it with A. brasilense when grown within a confined environment. This
study is the first report of the deliberate inoculation of
Chlorella sp. with a terrestrial PGPB, perhaps because of
the different origins of the two microorganisms. C. vulgaris
is not known to harbor any associative beneficial bacteria, and
Azospirillum sp. is rarely used for inoculation in aquatic
environments (42).
To ensure the close proximity of the two microorganisms in the liquid
medium essential for C. vulgaris, they were coimmobilized in
alginate beads and were cocultivated under controlled conditions suitable for both, in batch cultures and in continuous flow cultures in
a chemostat. Alginate beads of various forms and shapes are convenient
inoculant carriers for use in numerous industrial, environmental, and
agricultural applications (3, 13, 19, 31, 45). Immobilized
A. brasilense has been proposed for semiarid agricultural
uses (2, 9), but this work is still in the experimental
stage (3, 19). Chlorella sp. coimmobilized with other microorganisms is used in industrial processes where the microalga generates oxygen for the accompanying microorganism involved
in compound transformation (14, 28, 39). Continuous culture
techniques have been used both for diazotrophic bacteria such as
Azospirillum (46, 51) and for microalgae
(34).
 |
MATERIALS AND METHODS |
Microorganisms and axenic growth conditions.
C.
vulgaris Beijerinck (UTEX 2714) was isolated from a secondary
effluent of a wastewater treatment stabilization pond near Santafe de
Bogota (21) and was purified from associative bacteria using
an antibiotic package (L. E. Gonzalez, V. K. Lebsky, J. P. Hernandez, J. J. Bustillos, and Y. Bashan, unpublished data). Prior to immobilization in beads, axenic C. vulgaris was
cultivated in a sterile mineral medium (C30) as previously described
(21) for 5 days. A. brasilense Cd (DSM 7030) was
grown in liquid nutrient broth (Sigma) or N-free OAB medium at 30 ± 2°C for 16 h by standard methods (7) and was used
for immobilization after a washing in sterile saline solution (0.85% NaCl).
Immobilization of microalgae into alginate beads and bead
solubilization.
Microorganisms were immobilized using the method
described by Bashan (2). Briefly, 20 ml of axenically grown
cultures of C. vulgaris containing 6.0 × 106 cells/ml were mixed with 80 ml of a sterile, 6,000-cP
2% alginate solution (a solution made of alginate mixed at 14,000 and
3,500 cP) and stirred for 15 min. The solution was dripped from a
sterile syringe into a 2% CaCl2 solution (11)
with slow stirring. The beads formed were left for 1 h at 22 ± 2°C for curing and then washed in sterile saline solution.
A. brasilense cultures (approximately 109
CFU/ml) were immobilized similarly. Because immobilization normally reduces the number of microorganisms in the beads (2), a
second incubation step was necessary, overnight in OAB medium for beads containing A. brasilense and 18 h in 6.5 mM phosphate
buffer for beads containing C. vulgaris. The low
concentration of phosphate and the short incubation period were
insufficient to dissolve the beads. Where cocultures of A. brasilense and the microalga were used, the same concentration of
each microorganism used in pure cultures was mixed prior to
incorporation with alginate and bead formation, but the volume of each
microbial culture was reduced to 10 ml before adding the alginate.
Where appropriate, indole-3-acetic acid (IAA) (10
4,
10
5, and 10
6 M; Sigma), dissolved in 100 ml
of C30 medium, was added prior to immobilization of C. vulgaris into alginate beads.
Beads were solubilized for cell counts by immersing five beads (one
bead per milliliter) in a solution of 0.25 M phosphate-buffered saline
(PBS) (pH 7.0 ± 0.2) for 1 h at 30 ± 2°C. A. brasilense was counted by plating a series of dilutions (in PBS)
on nutrient agar plates (Difco, Detroit, Mich.), and C. vulgaris was counted using a Neubauer hemocytometer.
Culture conditions for coimmobilized microorganisms or organisms
alone.
Coimmobilized microorganisms or C. vulgaris
organisms alone were grown in the mineral salts of residual water
medium (21) containing the following (in milligrams per
liter): NaCl, 7; CaCl2, 4; MgSO4 · 7H2O, 2; K2HPO4, 21.7;
KH2PO4, 8.5; Na2HPO4,
33.4; and NH4Cl, 10. These were grown either in batch
cultures or in continuous culture in a chemostat. The level of
phosphate in the medium was insufficient to dissolve the constructed
beads. Batch cultures (500 ml) were incubated in nonbaffled Erlenmeyer
flasks at 22 ± 2°C and 150 rpm and with a light intensity of 60 µmol/m2/s for 7 days. Cultures in a chemostat (Virtis,
Gardiner, N.Y.) were grown at 28 ± 2°C and 90 rpm with 100%
dissolved oxygen, a light intensity of 30 µmol/m2/s, and
a medium exchange rate of 1.5 ml/h. Samples for analysis were taken
aseptically. Batch cultures were run for 7 to 9 days, and chemostat
cultures were run for 5 to 10 days.
Location of C. vulgaris inside the bead.
Random
samples of beads from both batch and chemostat cultures were
transversely cut and immediately mounted on a glass slide at ambient
temperature (23 ± 2°C) for light microscopy (Zeiss) at a
magnification of ×400. The location and numbers of C. vulgaris clusters and individual cells within the bead were
determined both in the outer periphery (0.5 mm) of the bead and in its interior.
Pigment analysis.
The effect of coculturing with A. brasilense on the quantity of some pigments of C. vulgaris was determined by high-pressure liquid chromatography
(series 1100; Hewlett-Packard) (47) after 7 days of
incubation. Chlorophylls a and b,
-carotene,
lutein, and violoxanthin were analyzed.
Biomass determination.
Ten grams of beads containing
coimmobilized microalgae and bacteria was dissolved in 100 ml of PBS as
described above. The suspension was then filtered through a 3-µm
(pore size) plankton net leaving a pellet of microalgae on the net.
This pellet was resuspended in 100 ml of PBS. Aliquots (10 ml) were
centrifuged for 3 min at 1,400 × g in tubes containing
filter paper (Jecaber 5098) at the bottom. The supernatant containing
the bacteria was discarded. The dry weight of the microalgae was
measured after extracting and drying the filter paper containing the
microalgal pellet at 105°C for 1 h.
Experimental design and statistical analysis.
Batch cultures
were prepared in triplicate where a single flask served as one
replicate, and each experiment was repeated five times. Routine
controls were prepared similarly but without microorganisms in the
beads. Controls of heat-killed bacteria had no effect on microalgal
growth and therefore were not used routinely. Each of the chemostat
runs was repeated twice. Five beads were taken randomly (from each
culture) for counting of the total number of clusters and the number of
cells within each cluster. In each of the five beads, 10 microscopic
fields were chosen randomly for counting of microalgae. The dry weight
of the microalgae was measured in triplicate, where 10 g of beads dissolved in 100 ml of PBS served as a single replicate. Pigment content was also analyzed in triplicate where the levels of pigments in
five dissolved beads served as one replicate. Experiments in which IAA
was added to C. vulgaris batch cultures were repeated twice
(three flasks per experiment). Results of all repetitions were combined
and analyzed by one-way analysis of variance (ANOVA) or by Student's
t test (P
0.05).
 |
RESULTS |
Multiplication of C. vulgaris within alginate beads
under batch and continuous growth conditions.
C. vulgaris
grew continuously within the alginate beads for 9 days, reaching a
population of 7 × 106 cells/bead in batch cultures
and only 5 × 106 cells/bead under continuous growth
conditions. After 5 days of incubation, significantly more cells
developed under batch culture (Fig. 1).
Both culture types are useful for the study of C. vulgaris colonization and behavior inside alginate beads.

View larger version (15K):
[in this window]
[in a new window]
|
FIG. 1.
Multiplication of C. vulgaris within alginate
beads under batch and continuous growth conditions. Points on each
curve denoted by a different lowercase letter differ significantly at
P 0.05 in one-way ANOVA. Points denoted by different
capital letters after each day of incubation differ significantly at
P 0.05 in Student's t test. The
experiment was repeated five times, and the results presented are from
a representative experiment. Bars represent the standard error (SE).
When the SE bar is absent, the SE is smaller than the point.
|
|
Location and multiplication of C. vulgaris within
alginate beads when immobilized alone or when coimmobilized with
A. brasilense.
During solidification of the alginate into
beads, numerous internal cavities of various sizes are formed randomly.
Analysis of these cavities revealed that C. vulgaris
preferred to grow in the periphery of the bead. In this area there were
significantly more algal clusters (colonies) (Fig.
2A), and each cluster contained more
microalga cells (Fig. 2B).

View larger version (15K):
[in this window]
[in a new window]
|
FIG. 2.
Multiplication of C. vulgaris in the
periphery and in the interior of alginate beads under continuous
culture conditions. Points on each curve denoted by a different
lowercase letter differ significantly at P 0.05 in
one-way ANOVA. Points denoted by different capital letters after each
day of incubation differ significantly at P 0.05 in
Student's t test. The experiment was repeated five times,
and the results presented are from a representative experiment. Bars
represent the SE. When the SE bar is absent, the SE is smaller than the
point.
|
|
A. brasilense multiplied within the beads over time as was
observed previously (
2), increasing linearly (
y = 3.98
x 
2.55;
r2 = 98.8) from 1.9 × 10
7 to 1.35 × 10
8 CFU/g of beads after
96 h of incubation. When the two microorganisms
were coimmobilized
in the same bead, significant promotion of
C. vulgaris
growth occurred within 1 day and continued for 6 days.
The total
numbers of algal cells (Fig.
3A) and
clusters significantly
increased, both in the periphery and in the
interior of the bead
(Fig.
3B and C). Similarly, the number of cells
per algal cluster
significantly increased both in the periphery and in
the interior
of the bead (Fig.
3D and E). Fresh weight approximately
doubled
(from 9 mg of beads per g to 18.9 mg of beads per g), and the
dry weight increased even more dramatically (from 0.1 mg of beads
per g
to 2.4 mg of beads per g). Addition of the auxin significantly
increased the multiplication of
C. vulgaris within the bead,
an
effect similar to that observed following coimmobilization with
A. brasilense. An IAA concentration of 10
5 M
gave the highest growth promotion (Fig.
4).

View larger version (27K):
[in this window]
[in a new window]
|
FIG. 3.
Multiplication of C. vulgaris and A. brasilense coimmobilized in the same alginate bead under
continuous culture conditions. (A) Total number of cells; (B) number of
alga clusters in the periphery; (C) number of alga clusters in the
interior of the bead; (D) number of cells per cluster in the periphery;
(E) number of cells per cluster in the bead interior. Points on each
curve denoted by a different lowercase letter differ significantly at
P 0.05 in one-way ANOVA. Points denoted by different
capital letters after each day of incubation differ significantly at
P 0.05 in Student's t test. The
experiment was repeated five times, and the results presented are from
a representative experiment. Bars represent the SE. When the SE bar is
absent, the SE is smaller than the point.
|
|

View larger version (15K):
[in this window]
[in a new window]
|
FIG. 4.
The effect of addition of IAA (10 4,
10 5, and 10 6 M) on C. vulgaris
growth in batch culture. Points on each curve denoted by a different
lowercase letter differ significantly at P 0.05 in
one-way ANOVA. Points denoted by different capital letters after each
day of incubation differ significantly at P 0.05 in
Student's t test. Bars represent the SE. When the SE bar is
absent, the SE is smaller than the point.
|
|
Increase in C. vulgaris pigment production when
coimmobilized with A. brasilense.
The microalgal pigment
concentration in a mixture of C. vulgaris and A. brasilense coimmobilized in alginate beads was compared to an
axenic culture of C. vulgaris immobilized in similar beads in batch cultures. Table 1 shows that the
concentration per cell of the five microalgal pigments evaluated
significantly increased as a result of coimmobilization of the two
microorganisms in the same bead.
View this table:
[in this window]
[in a new window]
|
TABLE 1.
Pigment production by the microalga C. vulgaris after coimmobilization with A. brasilense in
alginate beads and incubated under batch culture for
7 daysa
|
|
 |
DISCUSSION |
The use of PGPB to enhance plant growth and crop yield is
predicted to become a major activity in contemporary agriculture in the
near future (35). These bacteria may also prove useful for
increasing the production of microalgae that have important application
in aquaculture, environmental cleanup, and the human food and animal
feed industries (12, 16). Attempts to increase microalgal
biomass have employed various technological, physical, molecular, and
environmental methods (16, 40), albeit microalgal growth has
limitations under any culture conditions (43).
Our working hypothesis was that some PGPB affect agricultural
terrestrial plant performance by interfering with the host plant's hormonal metabolism (41). This hypothesis may be extended to include unicell aquatic plants, such as the microalga C. vulgaris, which, following inoculation with PGPB, may also exhibit
enhanced cell proliferation and increased biomass production.
Microalga-growth-promoting bacteria have not previously been
identified; thus, we chose a nonspecific PGPB, A. brasilense, as a candidate bacterium. In liquid media, both
microorganisms disperse: the microalgae through currents
(36) and the bacterium by its own motility (4,
50). Effectiveness in industrial and water bioremediation
applications would be improved if these free-moving microorganisms were
confined to environments where their activities could be better
controlled. Furthermore, where mutual effects are expected, it is
essential that the microorganisms are in close proximity, as provided
by small alginate spheres (26).
We show here that coimmobilization of the two microorganisms in the
same bead resulted in enhanced microalgal proliferation, larger
quantities of pigment production, and increased culture biomass,
effects similar to those found for terrestrial plants following
inoculation with Azospirillum sp. Thus, one may speculate that phytohormones such as IAA, produced by A. brasilense
(22), may play a role in the stimulation of microalgal
growth. This idea is supported by the growth promotion seen following
application of exogenous IAA (this study) and the observation that
algae are capable of using and being affected by angiosperm hormones
(1, 18, 24). Oxygen diffusion is known to be limited inside
gel spheres (38), and this may explain why the majority of
C. vulgaris proliferation occurred in the periphery of the
bead. This indicates that smaller beads may be better for increasing
microalgal biomass.
In summary, this study highlights the potential for using a new
agricultural technology, PGPB treatment, to increase microalgal biomass
production in aquatic conditions when immobilization is required, as in
several bioremediation and industrial processes. This has important
implications for industry and the environment. The ability of PGPB to
affect unicell plants extends the usefulness of these organisms beyond
their original agricultural uses.
 |
ACKNOWLEDGMENTS |
We thank Carlos Quitiaquez and Juan Pablo Hernandez for excellent
technical assistance, Jesus J. Bustillos for pigment analysis, Ricardo
Vazquez-Juarez for assembly of the chemostat, Ellis Glazier for editing
the English-language text, and Cheryl Patten for critical reading of
the manuscript.
This study was supported by Instituto Colombiano para el Desarrollo de
la Ciencia y la Tecnología, Francisco José de Caldas (COLCIENCIAS) (Colombia), Consejo Nacional de Ciencia y
Tecnología (CONACyT) (Mexico) contracts 26262-B and 28362-B,
and the Bashan Foundation.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: The Center for
Biological Research of the Northwest (CIB), P.O. Box 128. La Paz,
B.C.S. 23000, Mexico. Phone: (112) 53633, X3663. Fax: (112) 54710. E-mail: bashan{at}cibnor.mx.
Y. Bashan participated in this study in memory of the late Avner
Bashan of Israel.
 |
REFERENCES |
| 1.
|
Bajguz, A., and R. Czerpak.
1996.
Effect of brassinosteroids on growth and proton extrusion in the alga Chlorella vulgaris Beijerinck (Chlorophyceae).
J. Plant Growth Regul.
15:153-156.
|
| 2.
|
Bashan, Y.
1986.
Alginate beads as synthetic inoculant carriers for the slow release of bacteria that affect plant growth.
Appl. Environ. Microbiol.
51:1089-1098[Abstract/Free Full Text].
|
| 3.
|
Bashan, Y.
1998.
Inoculants of plant growth-promoting bacteria for use in agriculture.
Biotechnol. Adv.
16:729-770[CrossRef].
|
| 4.
|
Bashan, Y., and G. Holguin.
1994.
Root-to-root travel of the beneficial bacterium Azospirillum brasilense.
Appl. Environ. Microbiol.
60:2120-2131[Abstract/Free Full Text].
|
| 5.
|
Bashan, Y., and G. Holguin.
1997.
Azospirillum-plant relationships: environmental and physiological advances (1990-1996).
Can. J. Microbiol.
43:103-121.
|
| 6.
|
Bashan, Y., and G. Holguin.
1998.
Proposal for the division of plant growth-promoting rhizobacteria into two classifications: biocontrol-PGPB (plant growth-promoting bacteria) and PGPB.
Soil Biol. Biochem.
30:1225-1228[CrossRef].
|
| 7.
|
Bashan, Y.,
G. Holguin, and R. Lifshitz.
1993.
Isolation and characterization of plant growth-promoting rhizobacteria, p. 331-345.
In
B. R. Glick, and J. E. Thompson (ed.), Methods in plant molecular biology and biotechnology. CRC Press, Boca Raton, Fla.
|
| 8.
|
Bashan, Y., and H. Levanony.
1990.
Current status of Azospirillum inoculation technology: Azospirillum as a challenge for agriculture.
Can. J. Microbiol.
36:591-608.
|
| 9.
|
Bashan, Y.,
H. Levanony, and O. Ziv-Vecht.
1987.
The fate of field-inoculated Azospirillum brasilense Cd in wheat rhizosphere during the growing season.
Can. J. Microbiol.
33:1074-1079.
|
| 10.
|
Becker, E. W.
1992.
Micro-algae for human and animal consumption, p. 222-256.
In
M. A. Borowitzka, and L. J. Borowitzka (ed.), Micro-algal biotechnology. Cambridge University Press, Cambridge, United Kingdom.
|
| 11.
|
Bettman, H., and H. J. Rehm.
1984.
Degradation of phenol by polymer entrapped microorganisms.
Appl. Microbiol. Biotechnol.
20:285-290[CrossRef].
|
| 12.
|
Borowitzka, M. A., and L. J. Borowitzka (ed.).
1992.
Micro-algal biotechnology.
Cambridge University Press, Cambridge, United Kingdom.
|
| 13.
|
Cassidy, M. B.,
H. Lee, and J. T. Trevors.
1996.
Environmental applications of immobilized microbial cells: a review.
J. Ind. Microbiol.
16:79-101[CrossRef].
|
| 14.
|
Chevalier, P., and J. De la Noüe.
1988.
Behavior of algae and bacteria co-immobilized in carrageenan, in a fluidized bed.
Enzyme Microb. Technol.
10:19-23.
|
| 15.
|
Costacurta, A., and J. Vanderleyden.
1995.
Synthesis of phytohormones by plant-associated bacteria.
Crit. Rev. Microbiol.
21:1-18[Medline].
|
| 16.
|
De la Noüe, J., and N. De Pauw.
1988.
The potential of microalgal biotechnology: a review of production and uses of microalgae.
Biotechnol. Adv.
6:725-770.
|
| 17.
|
De Pauw, N., and G. Persoone.
1992.
Micro-algae for aquaculture, p. 197-221.
In
M. A. Borowitzka, and L. J. Borowitzka (ed.), Micro-algal biotechnology. Cambridge University Press, Cambridge, United Kingdom.
|
| 18.
|
Dibb-Fuller, J. E., and D. A. Morris.
1992.
Studies on the evolution of auxin carriers and phytotropin receptors: transmembrane auxin transport in unicellular and multicellular Chlorophyta.
Planta
186:219-226.
|
| 19.
|
Fages, J.
1992.
An industrial view of Azospirillum inoculants: formulation and application technology.
Symbiosis
13:15-26.
|
| 20.
|
Glick, B. R.
1995.
The enhancement of plant growth by free-living bacteria.
Can. J. Microbiol.
41:109-117.
|
| 21.
|
Gonzalez, L. E.,
R. O. Cañizares, and S. Baena.
1997.
Efficiency of ammonia and phosphorus removal from Colombian agroindustrial wastewater by the microalgae Chlorella vulgaris and Scenedesmus dimorphus.
Biores. Technol.
60:259-262[CrossRef].
|
| 22.
|
Hartmann, A., and W. Zimmer.
1994.
Physiology of Azospirillum, p. 15-39.
In
Y. Okon (ed.), Azospirillum/plant associations. CRC Press, Boca Raton, Fla.
|
| 23.
|
Holguin, G., and Y. Bashan.
1996.
Nitrogen-fixation by Azospirillum brasilense Cd is promoted when co-cultured with a mangrove rhizosphere bacterium (Staphylococcus sp.).
Soil Biol. Biochem.
28:1651-1660[CrossRef].
|
| 24.
|
Jacobs, W. P.
1986.
Are angiosperm hormones present in and used by algae?, p. 218-226.
In
M. Bopp (ed.), Plant growth substances. Springer-Verlag, Berlin, Germany.
|
| 25.
|
Johnson, E. A., and G. H. An.
1991.
Astaxanthin from microbial sources.
Crit. Rev. Biotechnol.
11:297-326.
|
| 26.
|
Kaya, V. M.,
J. De la Noüe, and G. Picard.
1994.
A comparative study of four systems for tertiary wastewater treatment by Scenedesmus bicellularis: new technology for immobilization.
J. Appl. Phycol.
7:85-95.
|
| 27.
|
Kayano, H.,
T. Matsunaga,
I. Karube, and S. Suzuki.
1981.
Hydrogen evolution by co-immobilized Chlorella vulgaris and Clostridium butyricum cells.
Biochim. Biophys. Acta
638:80-85[CrossRef].
|
| 28.
|
Khang, Y. H.,
H. Shankar, and F. Senatore.
1988.
Enhanced beta-lactam antibiotic production by coimmobilization of fungus and algae.
Biotechnol. Lett.
10:867-872[CrossRef].
|
| 29.
|
Kloepper, J. W.,
J. Leong,
M. Teintze, and M. N. Schroth.
1980.
Enhanced plant growth by siderophores produced by plant growth-promoting rhizobacteria.
Nature
286:885-886[CrossRef].
|
| 30.
|
Lau, P. S.,
N. F. Y. Tam, and Y. S. Wong.
1997.
Wastewater nutrient (N and P) removal by carrageenan and alginate immobilized Chlorella vulgaris.
Environ. Technol.
18:945-951.
|
| 31.
|
Leenen, E. J. T. M.,
V. A. P. Dos Santos,
K. C. F. Grolle,
J. Tramper, and R. H. Wijffels.
1996.
Characteristics of and selection criteria for support materials for cell immobilization in wastewater treatment.
Water Res.
30:2985-2996[CrossRef].
|
| 32.
|
Lippi, D.,
I. Cacciari,
T. Pietrosanti, and W. Pietrosanti.
1992.
Interactions between Azospirillum and Arthrobacter in diazotrophic mixed culture.
Symbiosis
13:107-114.
|
| 33.
|
Metting, B.
1992.
Micro-algae in agriculture, p. 288-304.
In
M. A. Borowitzka, and L. J. Borowitzka (ed.), Micro-algal biotechnology. Cambridge University Press, Cambridge, United Kingdom.
|
| 34.
|
Moo-Young, M. (ed.).
1988.
Bioreactor immobilized enzymes and cells: fundamentals and applications.
Elsevier Applied Science, New York, N.Y.
|
| 35.
|
Ogoshi, A.,
K. Kobayashi,
Y. Homma,
F. Kodama,
N. Kondo, and S. Akino (ed.).
1997.
Plant growth-promoting bacteria present status and future prospects.
Hokkaido University Press, Sapporo, Japan.
|
| 36.
|
Oh-Hama, T., and S. Miyachi.
1992.
Chlorella, p. 3-26.
In
M. A. Borowitzka, and L. J. Borowitzka (ed.), Micro-algal biotechnology. Cambridge University Press, Cambridge, United Kingdom.
|
| 37.
|
Okon, Y., and C. A. Labandera-Gonzalez.
1994.
Agronomic applications of Azospirillum: an evaluation of 20 years of worldwide field inoculation.
Soil Biol. Biochem.
26:1591-1601[CrossRef].
|
| 38.
|
Omar, S. H.
1993.
Oxygen diffusion through gels employed for immobilization. 2. In the presence of microorganisms.
Appl. Microbiol. Biotechnol.
40:173-181.
|
| 39.
|
O'Reilly, A. M., and J. A. Scott.
1995.
Defined coimmobilization of mixed microorganism cultures.
Enzyme Microb. Technol.
17:636-646[CrossRef].
|
| 40.
|
Oswald, W. J.
1992.
Micro-algae and waste-water treatment, p. 305-328.
In
M. A. Borowitzka, and L. J. Borowitzka (ed.), Micro-algal biotechnology. Cambridge University Press, Cambridge, United Kingdom.
|
| 41.
|
Patten, C. L., and B. R. Glick.
1996.
Bacterial biosynthesis of indole-3-acetic acid.
Can. J. Microbiol.
42:207-220[Medline].
|
| 42.
|
Puente, M. E.,
G. Holguin,
B. R. Glick, and Y. Bashan.
1999.
Root surface colonization of black mangrove seedlings by Azospirillum halopraeferans and Azospirillum brasilense in seawater.
FEMS Microbiol. Ecol.
29:283-292[CrossRef].
|
| 43.
|
Raven, J. A.
1992.
Limits to growth, p. 331-356.
In
M. A. Borowitzka, and L. J. Borowitzka (ed.), Micro-algal biotechnology. Cambridge University Press, Cambridge, United Kingdom.
|
| 44.
|
Tam, N. F. Y.,
P. S. Lau, and Y. S. Wong.
1994.
Wastewater inorganic N and P removal by immobilized Chlorella vulgaris.
Water Sci. Technol.
30:369-374.
|
| 45.
|
Tanaka, A., and H. Nakajima.
1990.
Applications of immobilized growing cells.
Adv. Biochem. Eng. Biotechnol.
42:97-131[Medline].
|
| 46.
|
Ueckert, J., and I. Fendrik.
1995.
Continuous culture application in physiological investigations on diazotrophic bacteria, p. 291-298.
In
I. Fendrick, M. Del Gallo, J. Vanderleyden, and M. de Zamaroczy (ed.), Azospirillum VI and related microorganisms. Genetics-physiology-ecology. NATO Series, vol. G37. Springer-Verlag, Berlin, Germany.
|
| 47.
|
Vidussi, F.,
H. Claustre,
J. Bustillos-Guzman,
C. Cailliau, and J. C. Marty.
1996.
Determination of chlorophylls and carotenoids of marine phytoplankton: separation of chlorophyll a from divinyl-chlorophyll a and zeaxanthin from lutein.
J. Plankton Res.
18:2377-2382[Abstract/Free Full Text].
|
| 48.
|
Wikstrom, P.,
E. Szwajcer,
P. Brodelius,
K. Nilsson, and K. Mosbach.
1982.
Formation of keto acids from amino acids using immobilized bacteria and algae.
Biotechnol. Lett.
4:153-158.
|
| 49.
|
Wilde, E. W., and J. R. Benemann.
1993.
Bioremoval of heavy metals by the use of microalgae.
Biotechnol. Adv.
11:781-812.
|
| 50.
|
Zhulin, I. B., and J. P. Armitage.
1992.
The role of taxis in the ecology of Azospirillum.
Symbiosis
13:199-206.
|
| 51.
|
Zimmer, W.,
M. P. Stephan, and H. Bothe.
1984.
Denitrification by Azospirillum brasilense Sp7. I. Growth with nitrate as respiratory electron acceptor.
Arch. Microbiol.
138:206-211[CrossRef].
|
Applied and Environmental Microbiology, April 2000, p. 1527-1531, Vol. 66, No. 4
0099-2240/00/$04.00+0
Copyright © 2000, American Society for Microbiology. All rights reserved.
This article has been cited by other articles:
-
de-Bashan, L. E., Bashan, Y.
(2008). Joint Immobilization of Plant Growth-Promoting Bacteria and Green Microalgae in Alginate Beads as an Experimental Model for Studying Plant-Bacterium Interactions. Appl. Environ. Microbiol.
74: 6797-6802
[Abstract]
[Full Text]