Zaragoza : CIHEAM
Cahiers Options Méditerranéennes; n. 45 2000
pages 305-314
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--- Howieson J.G., O'Hara G.W., Loi A. Th e legu me-rh izobia relation sh ip in th e Mediterran ean basin . In : Sulas L. (ed.). Legumes for Mediterranean forage crops, pastures and alternative uses . Zaragoza : CIHEAM, 2000. p. 305-314 (Cahiers Options Méditerranéennes; n. 45)
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The legume -
Basin
J.G. G.W. A.
Studies, of Science &
6150,
WA, South 6151, and
The of Nedlands, 6907,
Summary
-
To effectively the value of symbiotic N-fixation we need to G2 X E, G to the genotypes of both legume and and E the edaphic in which the symbiosis is to function. the basin is evidence that despite co-evolution of legumes andthe is not always optimal. options to N-fixation depending on
the of the limitation to legume words: legume, N-fixation,
- renforcer la valeur de la fixation synlbiotique de l'azote, il est nécessaire de comprendre le produit G2 x 02 G correspond génotyyes de la légumineuse et de son associé, et l'environnement édaphique dans lequel la symbiose doit avoir Dans le bassin méditerranéen, est évident que malgré une Co-évolution des légumineuses et de leur rhizobium, l 'association n'est pas toujours optimale. alternatives de recherche sontproposées afin d'anzéliorer la fixation de l'azote en fonction du type de contrainte lirnitant lespe$ornlances de la légumineuse ou du rhizobium.
légumineuse, fixation d'azote,
The adaptation of plants to climate is often discussed in of G X E -the
Genotype X When dealing with the legume - the
becomes one of the second i.e. G' X E, G to the genotypes of both the legume and its To effectively the potential of this symbiosis, we must fully these multiple
The capacity to fix N2 in symbiosis with plants is found in of
the (Allovhizobiz.m,
and Sinovhizobizlm,), actinomycetes (Frankia) and (Anabaena,
(Young, 1996). legumes the of the N%-fixed in
in a that is not leached.
is also supplied in equivalent amounts, ton of N
consumes 1.3 ton of oil equivalents and Cocking, 1997). Thus, the inputs of N into systems by N-fixation in nodulated legumes fundamental to sustainable and economic
At least some of the legumes of the basin have been studied
in to (e.g. and Cocks, 1990; et al. 1993).
the most astonishing aspect of the of the basin is how little we
know about ecology! Given to in that as well as
in that a climate, it is that so few
studies of the ecology of in the basin have been Of the many
studies of legume ecology that have been basin, few have focussed upon the symbiosis, whilst even have investigated symbiotic with the The publication by Loi et al., (1999) is a notable exception. The aim of this
is to outline to and manipulating the
in
N optimally?
has been that genotypes adapted to soil
conditions and may be advantaged both and competitively conditions that suit
them, of the symbiotic with host 1999). we follow this
statement to its logical conclusion it that symbiotic effectiveness a selection upon a population than does adaptation to soil and climate.
This is intuitively logical and was, in a sense, implied in a study by and
(1987) that soil a in nodule
occupancy. all -what advantage does a being fully effective at N-fixation than '75% effective? As long as the host has sufficient N to and to compete with its the photosynthate supply to the nodules is and
the well We cannot assume that in any given
the legume symbiosis is optimised simply because both and
have evolved in that evidence this
1 shows that was no yield advantage in Biserrula pelecinus L.
inoculation with a collected as its host. The genotype of B.
yelecim~s yielded well with and vice vemz. fact, the data
indicate that the effective at fixing N per se than those
This possibility needs to be investigated.
This to be the d e than the exception. et al., (1999) that monospecific genus, Hyrnenocarpus circinnatus L. (Savi) the
of high effectiveness gave no indication of specificity. Eight
isolated H. circimatus collected in the Cyclades of nodulated nine
host ecotypes only one actually fixed
Sulas et al., (1998) the yield of coronarium L. on a soil in inoculation with selected high N-fixation, indicating the soil in that a effective suite of
examples populations of N-fixation in the
basin et al. 1995; et al. 1995; and 1991) and
et al. 1999).
1 4 0
1 T 95GCN68
¿# 60
9
40F
20 O
Y
- -
Figure l. Yield of two genotypes of Biserrula pelecinus (95GCN68 and
when inoculated with collected as
is yield of tops as a of the inoculant in
(Loi, Yates and unpublished data).
is scope N-fixation in legumes within the
basin, as is legumes have been
then can this optimisation be best achieved? is in G2 X E that will
be made and we have developed a set of this we must
the status quo with to the symbiosis as it applies to legume of
2 outlines common leading to options that when
investigating legume nodulation and N-fixation:
1
a high population of OOO/g soil)
Select a host legume genotype to nodulate effectively with soil
I
Select a host legumegenotype that has no
Figure 2. A schematic of to N-fixation in legumes
selection of the host genotype.
1 the soil contains a high population of effective that cause 2 the soil contains a low population of effective that 3 the soil does not contain capable of nodulating with the host W-fixation
nodulation and N-fixation legume of and hence inoculation is
each a of options legume nodulation, with
the most likely option to succeed denoted by line density in 2. Some examples the options A-F have been successful in given in Table 1.
Of exist. example, is. a high population of effective
and no to inoculation (the case with many pulse legumes in Asia)
the legume of is with N and inoculation is
ineffectual (e.g. vulgaris in inoculation is
and having decided upon the a of techniques available to select adapted
Table 1. examples applying the pathways A-F in Fig. 2 have been successful in developing symbiotic N-fixation in
A
Bi, Bii
C
F
Trifolium nzichelianum Lotus ornithopodiodes, Biserrula pelecinus
Ornithopus spp Trifolium spp
Vicia, Lens polymorpha
Cicer, Hymenocarpus, Scorpiurus, Biserrula, Hedvsarum. etc.
2000, this issue
Loi unpubl., et al.
1995
(unpubl.) et al. 1999 Watlun 1999
et al. 1999 and Ewing 1986
and Ewing 1989
CV. well adapted to the medic population in alkaline soils
legumes which avoid with a
effective medic
population on soils 6-9.
Good nodule occupancy in the of sowing on acid soils.
A host
selected new
and to
WU95.
Selection of adapted inoculants acid soils An acid inoculant was selected to colonise soils
combination with E, a symbiotically competent legume was selected the soils of 4-5.
The with
many legumes in
4.5-6
Techniques for selecting and evaluating rhizobia to match strains with both legume hosts and soil conditions
The genetic of populations can now be investigated with
methodologies (Vinuesa et al. 1998). This, time, ecologists to follow population dynamics, population and investigate genetic
doing so, ecologists can that
inoculant quality, of
1. high NZ-fixation with the intended host species without
2. adaptation to the edaphic host;
The needed in inoculant-quality species;
3. genetic stability in and soil;
4. and in inoculant and
5. competitiveness with indigenous soil
l . Selecting effective rhìzobìal strains with broad host-range characteristics To genetic compatibility NZ-fixation between host and
uses a lit, glasshouse than
pouches. We emphasise fundamental aspects:
0 the must be limiting only in plant available N
0 we expect within species NZ-fixation
0 we acknowledge the necessity to select that will not
existing legumes in the
We symbioses nodulation and NZ-fixation in sand et al., 1995)
than because it has to optimise
conditions each “new” legume studied. The method consists of steamed, sand held pots, with a system in the base and alltathene beads on the
The beads minimise losses and contamination
Autoclaved plant solution added as a capped tube. This
system can be utilised legumes of all seed sizes. is with seeded legumes
(>5 mg) to select size and of attention
must be paid to hygiene in the glasshouse to avoid contamination by Effectiveness of NZ-fixation is by yields and %N of inoculated plants with
and uninoculated
2. Screening edaphic adaptation
many symbioses, the challenge is to develop a consistent nodulation
the legume in the selection focusses on
effective and then between them on the basis of
ability to in, and to colonise, soils. The methodology has been
the technique as by and Ewing (1986).
to the soil as inocula at a site of chemical and physical
and of the species of of the site should
be in the host-legume, if this is likely to be a upon
Soils with a sandy (5-10% clay) expedite of examination of the nodules and also place upon inoculant
the bio-assay the plots sown as 2m lines of inoculated legume seed
by l m and with all and except N.
allowed to a full season which top weight and N-fixation can be assessed. the soils low in available N, the biomass of the tops is an
excellent of symbiotic This can valuable given that
in stage 1 was based upon N-fixation conditions. the soil contains N, then the abundance method (Unkovich and 1998) can
indicate symbiotic is possible that in
abilities to on the seed in the legume in difficult soils, hence data on situ essential the selection of elite
Following a (usually in the soil, the individual
and movement away of to the soil using a nodulation bio-
assay this assay, uninoculated, seeds sown the line at two
points.
l 2
Figure 3. A schematic of the technique. lines seed sown inoculated 1) uninoculated 2).
plants excavated 10-12 weeks sowing and the nodulation
design can be as blocks, adjusted to take advantage of spatial analysis techniques (Cullis and Gleeson 1991).
3. Genetic stability in culture, storage and soil
sometimes on media that can genetic
changes that affect symbiotic Whilst it is that must
use such media to to such media should be minimised
because the of change is example, in leguminosarunz bv.
viceae non-nodulating in 30% of colonies only 10
comm.). is to at -8OCO in as vacuum-
(Vincent 1970).
Genetic stability in soils is a much difficult to evaluate. lotì
to have a to genetic of a “symbiosis island”
to (Sullivan and 1998). this is amongst
species is a the of substantial genetic in
populations of Sinorhizobium nzeliloti, 1. trijiolii and Bradyrlzizobium sp (Lupinus) anecdotal evidence that genetic exchange these species. Given
of this phenomenon, it may soon be possible to identify the genetic
disposing to gene and to to this
4. Satisfactoly growth and sumival in irlocularzt rnanllfncturing procedures
is evidence that the can affect the adaptation of
inoculants to the soil example, in the if the
is exposed to a it may initiate a of physiological and
biochemical that it to handle an acid soil This is
the adaptive acid in by
and Glenn (1994). Not all possess the capacity to the acid trifolii does, the acid sensitive TA1 does not (Watlin 1999).
5. Cornpetitiveness with indigenous soil rhizobia
Of to the basin is how we can N-fixation
the of competitive of A to study competition is to
label with a such as GUS (Wilson, 1995) and visualise the outcome of competition have been selected on the basis of adaptation to the is a chance they can be competitive with indigenous and less effective genotypes.
the does not have access to technology,
a means to between they
to use a of this (Vinuesa et al.
1998).
Conclusions
is evidence that legumes do not always fix N optimally in the
We should not assume that because of co-evolution, the legume and its
matched to fix N. is not, selection
on optimal N-fixation. view of this, we have discussed
to symbiotic N-fixation developing an of G2 X E
and then applying some elite selection.
AS., (1987). of lime and phosphate on nodulation of soil-
Trifolium subterrarzmeum L. by indigenous 53,
Cullis, Gleeson, A.C. (1991). Spatial analysis of field and extension to two dimensions. Biometrics 47, 1449-1460.
J.C. (1999). abundance and symbiotic effectiveness of legunzinosarum bv. trifoZii alkaline
soils in South Aust. (in
T., Cocks, (1990). of annual legumes in
J.G., Ewing, (1986). Acid in the -
2090-209’7.
J. Appl. 27,578-591.
symbiosis. Aust. J. 37, 55-64.
J.G., Ewing, (1989). Annual species of in ability to nodulate on acid soils. Aust. J. 40, 843-50.
J.G., Loi, A., S.J. (1995). Biserrzda pelecinus L. -a legume species with potential acid, duplex soils which is nodulated by unique Aust. J.
Agric. 46, 997-1007.
J.G. (1999). The S.J. Cocks (Eds.)
of and Forage Legumes, Academic
pp. 96-106.
J.G., G.W. and C m , S.J. (1999). Changing legumes in
an Field
(in
L.A., N., and Altuntas, S. (1995).
The of in legume in the West Asian highlands.
methods and 3 1,473-483.
Cocking, E.C. (1997). : The Global Challenge &
Needs, A position The Foundation
Lake Como, 8-12, 1997. 1-86451-364-7.
Loi, A., Cocks, J.G., S.J. (1999). Genetic in populations of two annual legumes and associated AUS. J. 50, 305- 315.
L.A. and (1991). in two annual legumes, as
affected by inoculation and seed density. Field Crops 26,253-262.
L.A., N., and Altuntas, S. (1995).
The of in legume in the West Asian highlands.
meliloti. Agric. 3 1, 493-99.
G.W., Glenn, (1994). The adaptive in nodule
and 161,286-292.
E., Spanu, F., L. (1993). and of
populations Sicily, 68,43-5 1.
Sulas, L., C.A., Loi, A., J.G. (1997). The selection of optimal
inoculants yield of Hedysarum coronarium (sulla). 17"'
of 18-21, 1997.
Sullivan, J.T., C.W. (1998). Evolution of by acquisition of a 500-kb symbiosis island that into a gene. Acad. Sci. USA, 95,5145-5149.
Unkovich, J.S. (1998). Symbiotic effectiveness and to season
in indigenous populations of S.W. Soil
Biol. Biochem. 30, 1435-1443.
Vinuesa, J.L.W., de F.J., (1998). Genotypic of
Bradyrhizobizm nodulating endemic woody legumes of the by length analysis of genes encoding 16s
and 16s-23s genomic
and 16s sequencing. Appl. 64,2096-2104.
Vincent, (1970). A manual the study of
15, Scientific
Watkin, E.L.J., (1999). field and physiological studies to acid in bv. trifolii. Thesis.
Wilson, (1995). techniques the study of ecology in the field. Soil
Young, and taxonomy of Soil 186,45-52.
Biol. Biochem. 27, 501-514.