THE
EFFECT OF SALINITY ON RHIZOBIUM SURVIVAL, NODULE FUNCTION AND NODULE
FORMATION IN THE SOYBEAN‑RHIZOBIUM JAPONICUM SYMBIOSIS |
A
DISSERTATION SUBMITTED TO THE GRADUATE DIVISION OF THE UNIVERSITY
OF HAWAII IN PARTIAL FULFILLMENT OF
THE REQUIREMENTS FOR THE DEGREE OF DOCTOR
OF PHILOSOPHY IN
AGRONOMY AND SOIL SCIENCE AUGUST
1982 |
By Paul
W. Singleton Dissertation
Committee: B. Ben Bohlool, Chairman Duane P. Bartholomew Samir A. E1 Swaify Douglas Friend Jake Halliday |
ACKNOWLEDGEMENTS This
work was supported in part by Grants AID/DSAN‑G‑0100 (211‑d)
and AID/ta‑C‑1207 (NifTAL Project) from the United States Agency
for International Development. The
conclusions reached within this study do not necessarily represent the views
of the granting agency. |
ABSTRACT Symbiotic
nitrogen fixation may be adversely affected by saline environments. This dissertation describes experiments
that assess the salt sensitivity of: 1) Rhizobium as free living
organisms; 2) soybean nodule function; and 3) soybean nodule formation. In addition, a split‑root plant
growth system is described which can be used to separate the effects of
salinity stress on host yield potential from the effects of salinity on
nodule processes. The
growth rate of Rhizobium in culture media is slowed by the addition of
NaCl. Some strains were incapable of
growth at the highest level of salt used (120 mM NaCl). However, all withstood substantial osmotic
shock and most survived for extended periods in saline solutions equivalent
to the concentration of sea water.
The results show that the effects of increasing moisture tension and
salinity on Rhizobium survival in soil are additive. By
independently subjecting nodules and shoots to salinity stress it was
possible to show that the soybean‑Rhizobium japonicum
nodule system was not greatly affected by exposure to 120 mM NaCl. The main reduction in nitrogen fixation
was the indirect effect of salinity on leaf expansion, shoot yield potential
and the sink for nitrogen. The
early processes of nodule formation were extremely sensitive to NaCl in the
rooting medium. When only 26.3 mM
NaCl was added to the nutrient solution two hours prior to inoculation,
nodule number and mass were reduced by 50% and 79.9 mM NaCl reduced nodule
number, |
|
mass and nitrogen fixation to less
than 10% of the controls. Rhizobium
japonicum, reisolated from nodules from the high salt treatment did not
form more nodules under saline conditions than isolates from controls. By
independently subjecting the various processes of the symbiosis to salinity
stress it was determined that the early steps in nodule formation are the
most sensitive to salinity. This
sensitivity indicates that high quality irrigation water must be used during
the establishment of symbiotic legumes. |
|
TABLE
OF CONTENTS
Page ACKNOWLEDGEMENTS
................................................. ......2 ABSTRACT................................................................ 3 LIST
OF TABLES ....................................................... ..6 LIST
OF ILLUSTRATIONS ........................ .........................7 CHAPTER
I. INTRODUCTION .............................................8 CHAPTER
II. EFFECT OF SALINITY ON GROWTH AND
SURVIVAL OF RHIZOBIUM ................................... .19 CHAPTER
III. A SPLIT‑ROOT GROWTH SYSTEM FOR
EVALUATING THE EFFECT OF SALINITY
ON COMPONENTS OF THE SOYBEAN RHIZOBIUM JAPONICUM SYMBIOSIS .......................... .38 CHAPTER
IV. THE EFFECT OF SALINITY ON THE
FUNCTIONAL COMPONENTS OF THE
SOYBEAN‑RHIZOBTUM JAPONICUM
SYMBIOSIS ............................................... .53 CHAPTER V. THE EFFECT OF SALINITY ON NODULE
FORMATION
................................................69 |
|
LIST OF TABLES Table Page II‑1 Source of Cultures ............................. 31 II‑2 Effect of NaCl on Rhizobium Growth ............. 32 II‑3 Salt Tolerance of Legumes ...................... 33 III‑1 Ineffective and Effective Rhizobium on Half‑Root Systems ........................... 46 III‑2 Effect of NaCl to Half‑Root
Systems on Plant Ψπ
.................................... 47 IV‑1 Effect of NaCl to Half‑Root
Systems on Plant Growth ................................ 59 IV‑2 Effect of NaCl to Half‑Root
Systems on Nitrogenase Activity and Leaf Expansion ...................................... 60 IV‑3 Effect of NaCl to Half‑Root
Systems on Accumulation of Na, Cl, and K ............... 62 V‑1 Effect of NaCl on Rhizobium Survival in the Rooting Medium .......................... 81 V‑2
Salt Tolerance of Isolates from High Salt Treatments ............................... 85 |
|
LIST OF ILLUSTRATIONS Figure Page II‑1 Survival of Rhizobium in Salt Solutions .................................... 34 II‑2 Survival of Rhizobium in a
Salt Affected Oxisol
........................35 III‑1 A Split‑Root Growth System ................... 45 V‑1 Effect of NaCl at Inoculation on Plant Growth .............................. 82 V‑2 Effect of Salt and Inoculation
on Nodule Formation and Activity ..................................... 83 V‑3
Effect of NaCl to Half‑Root Systems on Root Weight and Water Uptake ................................. 84 |
CHAPTER
I INTRODUCTION There
are an estimated 4 x 106 km2 of saline lands in the
world today. This figure does not include large areas of the world's major
deserts nor areas where agricultural practices have generated saline soil
conditions (secondary salinization) (Flowers et al., 1977). Salinity limits production on 25% of
irrigated land in the USA (Carter, 1975).
Secondary salinization can be considered to be a more acute problem
since this process results in either the loss or reduced productivity of
improved land. There
are two approaches to solving salinity problems. The first involves management practices to reduce the level of
salts in the root zone as outlined by the U. S. Salinity Laboratory (U. S.
Salinity Laboratory Staff, 1954). The
second approach requires manipulation of the biological component of
agricultural systems to find plant material capable of economic yields under
ever increasing levels of salinity.
The first approach is a temporary solution to the problem since many
large irrigation projects end up recycling salts, which over time, increase
salt concentrations in irrigation waters, and subsequently, they accumulate
in the root zone. The long term solution to crop production under increasing
salinity lies in understanding and manipulating the mechanisms that enable
some plants to grow under saline conditions.
This requires an understanding of the physiology of the salt mediated
growth suppression of glycophytes as well as an understanding of the
mechanisms of salt tolerance found in halophilic |
species. This knowledge combined with genetic
manipulation of plants will
enable desirable agronomic characters to be combined with salinity tolerance. Economic yields could thus be sustained in
areas of natu- rally
occurring salinity or secondary salinization. Causes of Soil Salinity The
U. S. Salinity Laboratory (Staff, 1954) defines a saline soil as one in which
the soil solution at saturation has an electrical conductivity (EC) of 4
mmhos/cm or more, and less than 15% exchangeable Na. Saline souls are generally not Ca
deficient. The soluble salts can be
of any species, however, Na salts and especially NaCl usually predominate. Sources
of soluble salts are varied. Most agricultural land becomes salinized as a
result of fertilizer application and poor quality irrigation water. Arid conditions where evaporation rates
are high and inadequate wader is available for leaching result in
concentration of salts in the root zone. Excessive accumulation of Na can
compound the problem due to deterioration of soil structure and restricted
drainage. High water tables in arid
areas also can create saline soil conditions, through capillary rise of water
and salts (Carter, 1975). Growth Responses of Plants to Salinity The
tolerance of plant species to soluble salts varies. All marine plant life carries on photosynthesis and other
metabolic functions at an electrical conductivity (EC) in excess of 40
mmhos/cm. (= 40 m eq dissolved salts/liter). Some terrestrial species grow in
a salt |
concentration near that of sea water as
evidenced by the plant life at the sea wader's edge. Most yields decline when crops are grown
in the presence of much lower concentrations of salts. Despite large variation between crop
species (Bernstein, 1964) none approach the tolerance shown by halophytes
such as Atriplex vericaria which produced near normal yields in
700 mM NaCl (Black, 1960). Some
halophilic alga can grow in 4 M NaCl (Johnson et al., 1968). Shoot
growth for many plants is inversely and linearly related to increases in
osmotic pressure of the growth solutions: Sorghum bicolor
(Patel et al., 1975); Glycine wightii (Gates et al., 1966;
Wilson, 1970); Phaseolus vulgaris (Lunin and Gallatin, 1964); Glycine
max (Able and Mackenzie, 1964; Bernstein and Ogata, 1966); Wheat,
(Aceves et al., 1975) all show this type of response. The effect of salinity on plant growth is
characterized by a decline in the ratio of shoot weight to root weight with
increasing salt concentrations (Wilson, 1967; Wilson, 1970; Gates et al.,
1966). Glycophytes
grown in saline conditions exhibit dramatic reduction in leaf area compared
to controls (Wilson, 1970; Wignarajah et al., 1975). The reduction in leaf area of plants from
salinity is due to both a reduced rate of cell division and cell
enlargement. It is not, however, the
internal accumulation of high levels of ions per se that limit leaf
expansion. The main scheme of salt
tolerance in holophytes is the accumulation of inorganic ions in the cell
sap, while glycophytes tend to exclude excessive non‑nutrient ions
(Greenway, 1973). |
Plant Water Relations and Salinity According to early concepts of salt effects on
plant growth, low soil osmotic potentials decrease water activity and water
uptake by plants (physiological drought) which reduced cell turgor and cell
expansion (U. S. Salinity Laboratory Staff, 1954). This has been shown to be incorrect since Bernstein (1961) and
more recently Aceves et al., (1975) and Bower and Tamimi (1979) have shown that
plants adjust their cellular osmotic potential to maintain a constant
differential between the plant and soil solution. This differential is necessary if transpiration and turgor
pressure are to be maintained. Salt
stunted plants in moderately saline environments are not usually wilted since
adequate turgor pressure is maintained (Kirkham et al., 1974). Osmo regulation is the process whereby plants
maintain potential gradients between their tissues and environment. This regulation is due to the accumulation
of both inorganic and organic solutes and the subsequent transport of these
solutes within the plant. Plants subjected
to low matric potential cannot accumulate soil ions in sufficient quantities,
so osmo regulation results from the synthesis of organic solutes more than
plants under osmotic stress. Glycophytes under osmotic stress tend to
maintain water potential gradients more with organic acids, especially
malate, proline, and some ammonium compounds than do halophytes (Bar‑Nun
et al., 1977; Flowers and Hall, 1978; Wignarajah et al., 1975; Storey and
Jones, 1977). Storey and Jones (1977) examined 14 plant species
with a wide range of salt sensitivities.
They found that all species adjusted to |
osmotic stress by accumulation of Na
salts. Betaine was found in
significant quantities in halophytes and semi‑resistant species following
salinization and proline was accumulated in all species. Flowers and Hall (1978) found that betaine
accumulated rapidly when NaCl was added to the halophyte Suaeda maritima. These compounds can also serve as energy
sources and precursors for the synthesis of other organic substances
following the removal of the stress. Bar‑Nun and Mayber (1977) found
that proline content increased in Tamarix that was salt stressed and
water stressed. Proline accumulation,
however, was less and Cl- accumulation greater when the water
potential was lowered with NaCl as compared to polyethylene glycol, an
osmoticum, that is not taken up by the plant. Part
of the osmo regulation process involves differential translocation of ions
and solutes to various plant parts and to cell compartments. Wignarajah et
al., (1975) found that Phaseolus vulgaris when transferred to
48 mM NaCl solution first accumulated high concentrations of Na in the first
trifoliate along with higher concentrations of glucose and inositol than the
leaves of control plants. All these
solutes declined subsequently; Na was translocated out (to the stem), the
sugar and sugar‑alcohol probably was metabolized. The first trifoliate also tended to
accumulate more K and Ca when salt was applied to the media. Salinized Glycine
wightii (22 varieties) partitioned relatively more Cl than Na to the
shoots. The ability to regulate ion
content was associated with salt tolerance.
More tolerant cultivars tended to exclude Na from the shoot to a
greater degree than less |
tolerant varieties. (Gates et al., 1970). Sodium is
accumulated in the roots of many glycophytes in concentrations sufficient to
account for much of the osmotic adjustment of this tissue (Bernstein,
1963). Glycophytes excluding Na from
leaves tend to accumulate K, Cl and organic solutes in the shoots. These ions may also mediate other plant
processes involving turgor such as stomatal movement. Photosynthesis
and Gas Exchange Jensen
(1975a, 1975b, 1976, 1977) has clearly shown that net photosynthesis per unit
leaf area by Phaseolus vulgaris declines 22% with an osmotic
potential of ‑3.9 atm compared to controls (‑.4 atm). This decline was correlated with an increase
in leaf resistance (r1) and mesophyll resistance (rm)
(Jensen, 1975a). One‑third of the reduction in net photosynthesis
(Pnet) was due to r1 and two‑thirds due to increasing rm. Dark respiration per unit fresh and dry
weight of leaves declined significantly when plants were grown under saline
conditions. Increased energy for ion pumping for synthesis of organic
osmoticums then probably explains the decline in dry matter accumulation of
salt stressed plants. Neither increasing irradiance (Jensen, 1975b), changing
leaf temperature (Jensen, 1976) nor changing root temperature (Jensen 1975b)
countered the effects of salinity on photosynthesis or diffusive
resistance. Gale et al., (1967)
showed that net photosynthesis could be increased in salinized bean and
cotton plants by increasing the CO2 concentration of the
atmosphere. Salinized plants that
were CO2 fertilized had: carbon exchange rates (CER) approaching
controls without CO2 fertilization. The fact that r1 and rm increase with
salt stress |
and that CO2 fertilization can
overcome some of this stress suggests that the light reactions of
photosynthesis are not sensitive to salts. It
has been proposed that the enzymes of halophytes were more tolerant of
salinity than glycophytes (Greenway, 1968). Weinberg (1975), however, isolated 6 enzymes associated with the
photosynthetic process in Pisum sativum. The specific activities of these enzymes
were the same in salt stressed plants as in controls. Flowers (1972) compared 4 enzymes from Suaeda
maritima and Pisum sativum and found that no in vitro
differences existed for the tolerance to salt of the enzymes from the two
species. Flowers and Hall (1978)
found that PEP carboxylase from Suaeda maritima was inhibited
by salt concentrations in vitro that were lower than those measured in plant
cells. This suggests that salts are
compartmentalized in vacuoles and other non‑inhibitory osmoregulators
maintain cytoplasmic water potentials at sufficiently low levels to maintain
turgor. Betaine and proline additions
up to 1 M failed to inhibit the function of PEP carboxylase. Conclusions Although
salinity retards growth of most crop plants some other species can flourish
in highly saline environments. Growth
suppression is characterized by a reduction in leaf area, and lower
shoot/root ratios. Salts
reduce carbon assimilation of glycophytes due to an increase in resistance to
gas exchange, mostly in the mesophyll.
Biochemical processes and enzyme activities do not appear to be
sensitive in the range of osmotic potentials which inhibit plant growth. Halophytes, |
therefore, differ from glycophytes in that
they can adjust osmotically to high concentrations of salts by ion uptake,
then isolate or protect plant processes from these accumulated salts. Since
Pnet of legumes grown in saline environments is reduced it is not surprising
that total symbiotic N accumulation is also reduced (Wilson, 1970). Symbiotic
legumes, however, have additional processes and requirements that may be
affected by salinity stress. For
example, survival and growth of the Rhizobium, infection of root hairs
and root‑nodule development, and the functioning of the nodule enzyme
system may be differentially susceptible to soluble salts. The purpose of the research presented in
this dissertation was to identify salt susceptible steps in the soybean‑Rhizobium
japonicum symbiosis. |
LITERATURE
CITED Able, G. H., and A. J. Mackenzie. 1964. Salt
tolerance of soybean varieties during germination and later growth. Crop Sci.
4:157‑161. Aceves, E. N., L. H. Stolzy, and G. R. Mehuyr.
1975. Effects of soil osmotic potential produced with two salt species on
plant water potential growth and grain yield of wheat. Plant Soil 42:619‑627. Bar‑Nun, N., and A. Poljakoff‑Mayber.
1977. Salinity stress and the content of proline in roots of Pisum sativum
and Tamarix tetragyna. Ann. Bot. 41:173‑179. Bernstein, L. 1961. Osmotic adjustment of
plants to saline media. Am. J. Bot. 48:909‑918. Bernstein, L. 1963. Osmotic adjustment in plants
to saline media II. Dynamic phase. Am. J. Bot. 50:360‑370. Bernstein, L. and G. Ogata. 1966. Effects of
salinity on nodulation, nitrogen fixation and growth of soybeans and alfalfa.
Agron. J. 58:210‑203. Black, R. F. 1960. Effects of NaCl on the ion
uptake and growth of Atriplex vesicaria. Aust. J. Biol: Sci. 13:249‑264. Bower, C. A. and Y. N. Tamimi. 1979. Root
adjustments associated with salt tolerance in small grains. Agron. J. 71:690‑693. Carter, 0. L. 1975. Problems of salinity in
agriculture. p. 25‑39. In A. Poljakoff‑Mayber and J. Gale (ed.)
Plants in saline environments. Springer‑Verlag, New York. Flowers, T. J. 1972. Salt tolerance in Suaeda
martima (L.). Dum. J. Exp. Bot. 23:310‑21. Flowers, T. J., P. F. Troke, and A. R. Yeo. 1977.
The mechanism of salt tolerance in halophytes. Ann. Rev. Plant Physiol. 28:89‑121. Flowers, T. J. and J. L. Hall. 1978. Salt
tolerance in the halophyte Suaeda martima (L.). Dum: The influence of
the salinity of the culture solution on the content of various organic
compounds. Ann. Bot. 42:1057‑1063. Gale, J., H. C. Kohl, and R. M. Hagan.
1967. Changes in the water balance and photosynthesis of onion, bean, and
cotton plants under saline conditions. Plant Physiol. 20:408‑420. |
Gates, C. T., K. P. Haydock, and I. P. Little.
1966. Response to salinity in Glycine. Aust. J. Exp. Agric. Anim.
Husb. 6:261‑265. Gates, C. T., K. P. Haydock, and M. F. Robins.
1970. Salt concentration and the content of phosphorus, potassium, sodium,
and chloride in cultivars of _G. wightii. Aust. J. Exp. Agric.
Anim. Husb. 10:99‑109. Greenway, H. 1968. Growth stimulation by
high chloride concentrations in halophytes. Israel J. Bot. 17:169‑177. Greenway, H., and C. B. Osmond. 1972. Salt
responses of enzymes from species differing in salt tolerance. Plant Physiol.
49:256‑259. Greenway, H. 1973. Salinity, plant growth
and metabolism. J. Aust. Inst. Agric. Sci. 39:24‑34. Jensen, C. R. 1975a. Effects of salinity in
the root medium I. Yield, photosynthesis and water relationships at moderate
evaporative demands and various light intensities. Acta. Agric. Scand. 25:3‑10. Jensen, C. R. 1975b. Effects of salinity in
the root medium II. Photosynthesis, and transpiration in relation to
superimposed water stress from change of evaporative demands and root
temperature for short periods. Acta. Agric. Scand. 26:196‑202. Jensen, C. R. 1977. Effects of salinity in the
root medium IV. Photosynthesis, and leaf diffusive resistance in relation to
C02 concentration. Acta. Agric. Scand. 27:159‑164. Johnson, M. K., E. L. Johnson, R. D. MacElroy, H.
L. Speer, and. B. S. Bruff. 1968. Effect of salts on the hallophillic alga Dunalielea
viridis. J. Bacterial. 95:1461‑1468. Kirkham, M. B., W. R. Gardner, and G. C. Gerloff.
1974. Internal water status of kinetin treated salt‑stressed plants.
Plant Physiol. 53:241‑243. Lunin, J., and M. H. Gallatin. 1964.
Salinity‑fertility interactions in relation to the growth and
composition of beans. I. Effect of N, P, and K. Agron. J. 339‑342. Patel, P. M., A. Wallace, and E. F.
Wallihan. 1975. Influence of salinity and N ‑P fertility levels on
mineral content and growth of sorghum in sand culture. Agron. J. 67:622‑625. Storey, R., and R. G. Wyn Jones. 1977. Quaternary
ammonium compounds in plants in relation to salt resistance. Phytochem.
16:447‑453. |
U. S. Salinity Laboratory Staff. 1954.
Diagnosis and improvement of saline and alkali soils. USDA Handbook 60. Weinberg, R. 1975. Effect of growth in
highly salinized media on the enzymes of the photosynthetic apparatus in pea
seedlings. Plant Physiol. 54:301‑306. Wignarajah, K., D. H. Jennings, and T. F. Handley.
1975. The effect of salinity on growth of Phaseolus vulgaris L.
I. Ann. Bot. 39 :1029‑3i8. Wilson, J. R. 1967. Dry matter accumulation
in three Australian species and _G. Javinica. Aust. J. Exp.
Agric. Anim. Husb. 7:50‑56. Wilson, J. R. 1970. Response to salinity in
Glycine. Aust. J. Exp. Agric. Anim. Husb. 21:571‑82. |
CHAPTER
II EFFECT
OF SALINITY ON GROWTH AND SURVIVAL OF RHIZOBIUM Abstract This
study examines the effect of salinity on the growth and survival
of Rhizobium in culture media and soil.
Eleven isolates from
saline and non‑saline environments were compared. The growth (mean
doubling time, MDT) of all strains and species tested decreased when
the electrical conductivity (EC) of the culture medium (yeast mannitol,
YEM, medium) was raised from 1.2 mmhos cm‑1 to 6.7 mmhos cm-l
(15% sea water equivalent) and 13.1 mmhos cm-l (28% sea water equivalent).
Three out of 11 strains failed to grow at 13.1 mmhos cm-1. Although growth was affected by salinity,
four selected strains could
survive in extremely high concentrations of salt. Two salt- sensitive
and two salt‑tolerant strains from the growth rate study were inoculated
into solutions with EC's up to 43.0 mmhos cm-l (92% sea water
equivalent). Not only did all four
strains survive the initial osmotic
shock (5 hours after inoculation), it was not until 27 days after
inoculation that the sensitive strains exhibited a significant reduction
in viable numbers. The salt‑tolerant
strains survived for over
65 days with no reduction in viable counts.
The interaction between soil
moisture tension and soil salinity on Rhizobium survival in
gamma irradiated soil was also examined.
Six treatment combinations ranged
from –0.1 bars and 0.2 mmhos cm-1 to ‑15 bars and 12 mmhos
cm-1. Sensitive
strains declined from 107/g to 105/g of soil after 84
days of
incubation at ‑15 bars and 12 mmhos cm-1. Tolerant strains |
survived the dame period with no loss in
viable numbers. Results
Of these experiments indicate that many strains of Rhizobium can grow
and survive at salt concentrations which are inhibitory to most agricultural
legumes. Research emphasis concerning
the effects of salinity on symbiotic nitrogen fixation should, therefore, be
directed to other aspects of the symbiosis than the survival of the Rhizobium. Introduction Excessive
soluble salts affect more than 4 x 106 km2 of the
world's potentially arable lands (Flowers et al., 1977). The agricultural potential of these lands
is generally not limited by lack of solar radiation or temperature and if
managed properly, these lands can become productive. Measurements of soil salinity are commonly
made by determining the electrical conductivity (EC) in mnhos cm-1 or
equivalent osmotic pressure in bars of the soil solution at saturation (U.S.
Salinity Laboratory Staff, 1954). Sea
water at 20o has an EC of 46.6 mmhos cm‑1 (Thomas
et al., 1934). Actual concentrations
of soluble salts that are present in soil moisture films fluctuate with
changes in soil water content. Little
work has been done concerning the effect of salinity on the legume‑Rhizobium
symbiosis. That nitrogen accumulation
by the symbiotic systems of soybean, alfalfa and Glycine javanica
is reduced by salinity has been well documented (Bernstein and Ogata, 1966;
Steinborne and Roughley, 1975). |
Saline
conditions, may limit the symbiosis by: 1) affecting survival and
proliferation of Rhizobium in the soil and rhizosphere; 2) inhibiting
the infection process; 3) directly affecting root‑nodule function;
and/or 4) reducing plant growth, photosynthesis and demand for nitrogen. Since soil salinity may directly affect
either symbiont or affect their interaction it is essential to identify the
processes most sensitive to salinity.
Efforts then may be directed toward improving the tolerance of the
most sensitive symbiont or process of the symbiosis. Reported
effects of salts and soil moisture tension in the literature are mixed. Enhancement of growth by Rhizobium
spp. in media with l% NaCl (approximately 19 mmhos cm‑1) was
reported by Pillai and Sen (1973).
Steinborne and Roughley (1975) showed a reduction in growth rates of
R. trifolii and R. meliloti in the presence of salt. Bhardwaj (1972) claimed that isolates from
non‑saline soils could not proliferate or survive salt affected
soils. Carr and Ballard (1979) found
that a strain of R. trifolii was able to withstand short exposure to
fertilizer solutions with EC's in excess of 60 mmhos cm-1. This
paper compares rhizobia isolated from salt affected soils with random
inoculum strains from non‑saline areas for their ability to grow and
survive in salt solutions and in saline soil with different moisture
tensions. Salinity treatments were,
for the most part, selected to encompass a range of tolerance found in
agricultural legumes. Although
salinity slowed growth of all strains tested in these experiments, there was
considerable variation within the species tested |
for tolerance to salt. Salt tolerance of the strains was not
related to their ecological origins nor their growth rates in normal
media. Rhizobia were able to
withstand large changes in osmotic concentrations with little reduction in
viable numbers. Sensitive strains
were only affected after 5 days exposure to salt solutions which approached
the concentration of sea water. There
appears to be no interaction between soil moisture tension and salinity in
relation to rhizobial survival in clay soil.
A reduction in total water potential, whether due to osmoticum or high
moisture tension, is the factor that affects rhizobial survival. Both "tolerant" and
"sensitive" strains are much more tolerant of soil salinity and dry
soil conditions than are their leguminous hosts. Material and Methods Source of Cultures Isolates
of rhizobia were made from legumes growing on beach sands and salt affected
irrigated fields on the island of Oahu.
Many of the isolates from beach sands were made close to standing sea
water. Rhizobium isolation and
plant infection tests were carried out as described by Vincent (1970). All isolates were confirmed as rhizobia on
Macroptilum lathyroids except 17E which was confirmed on its
host, Leucaena leucorcephala.
Sources of standard cultures from non‑saline soils are given in
Table II‑1. All cultures were
maintained on yeast extract mannitol, YEM, slants (Vincent, 1970). |
Enumeration Viable
counts were performed using standard serial dilutions and plated by the drop
plate count method (Vincent, 1970).
The entire content of incubated soil vials were diluted; solution
cultures were sub‑sampled. All
serial dilutions of salt treatments were made using isotonic diluents. Effect of Salt on Growth Inocula
of 11 strains were diluted and one ml of each diluted culture was added to
tubes containing 9 ml YEM broth ammended with either 0 (1.2 mmhos cm‑1),
50 mM NaCl (6.7 mmhos cm-1) or 100 mM NaCl (13.1 mmhos cm‑1). Initial cell density was 1 x 103
viable cells ml‑1.
Mean doubling times (MDT) were determined by viable counts made 3
times during the log phase of growth of each strain. The relative tolerance of different
strains were expressed as the ratio of MDT at 13.1 mmhos cm‑1
to MDT at normal YEM broth (1.2 mmhos cm-1). Effect of Concentrated Saline Solutions on
Survival of Rhizobia Four
strains from the growth rate experiment were selected: 17E (fast‑growing,
salt tolerant); Hawaii 5‑0 (fast‑growing, salt sensitive); 21A
(slow‑growing, salt tolerant); USDA 110 (slow‑growing, salt
sensitive). Cultures were grown in YEM broth, diluted to 1 x 107
cells ml‑1 in solutions containing only YEM broth salts,
then inoculated into tubes containing broth salts only (1.4 mmhos cm‑1),
broth salts plus 233 me 1‑1 total salts NaCl + CaCl2
(18.4 mmhos cm-1), and broth |
salts plus 564 me 1-1 total
salts NaCl + CaCl2 (43.0 mmhos cm‑1). Proportions of NaCl and CaCl2
were adjusted to maintain a constant Na activity (SAR) as defined by the U.
S. Salinity Laboratory Staff (Thomas et al., 1934). Viable counts were made 5 hours, 5 days, 27 days and 65 days
after inoculation. Growth and Survival of Rhizobia in Saline
Soil at Two Moisture Tensions Wahiawa
subsoil (Tropeptic Eutrustox, clayey kaolinitic isothermic) was air dried and
passed through a 2 mm sieve. A
moisture release curve was developed fusing hanging water columns and a
membrane pressure plate apparatus (Childs and Collis‑George,
1950). The soil was also calibrated
for the EC when increasing amounts of CaCl2 and NaCl were added at
a constant Na activity (SAR=10). Air‑dried soil samples each weighing
34.4 g (30 g dry soil at 65o C) were added to 120 ml glass vials
with air tight polyethylene caps.
Vials and soil were gamma irradiated with 6 x 106 rads, and
inoculated with appropriate mixtures of salt solutions and dilutions of YEM
suspension cultures of strains 17E, 21A, Hawaii 5‑0 and USDA 110 to
impose treatments of ‑.1 and ‑15 bars moisture tension and EC's
of 0.2, 5.0 and 12.0 mmhos cm‑1 in all combinations. Initial inoculum densities ranged between
1.5 and 5.2 x 106 viable cells gram‑1 of oven dry
soil. Viable
counts were made at 3, 7, 24 and 82 days after inoculation for fast‑growers
Hawaii 5‑0 and 17E and at 6, 29, 49 and 86 days for slow‑growing
strains USDA 110 and 21A. |
Results The
addition of NaCl to YEM broth increased the mean doubling time (MDT) for all
strains tested (Table II‑2).
Sensitive strains such as Hawaii 5‑0, Web 48 and 8 failed to
grow in the highest level of salt.
Isolates from saline soils were not consistently more tolerant to salt
stress than other isolates. Strain 8
did not grow at 13.1 mmhos cm-1 and 7B grew very slowly. TAL 425,
an isolate from an acid soil, grew well at 13.1 mmhos cm-1. Figure
II‑1 shows that all four strains selected from the growth rate
experiment (17E, 21A, Hawaii 5‑0, USDA 110) were able to survive
initial exposure (5 hours) to solutions with an EC of 43 mmhos cm-1. Only after 5 days exposure of USDA 110 to
solutions at 43 mmhos cm‑1 and after 27 days exposure for Hawaii
5‑0 was any significant decline in viability detected. Viability of
tolerant strains, 17E and 21A, was maintained in all the treatment solutions
for the duration of the experiment.
Viable numbers in YEM broth cultures (no salt) declined over time. Survival
of strains USDA 110 and 21A was affected in soil but only at the most extreme
treatment combination of 12 mmhos cm‑1 and ‑15 bars
moisture tension (Figure II‑2).
All strains grew slightly when exposed to less extreme conditions. |
Discussion The
salt tolerance of each symbiont of the legume‑Rhizobium
symbiosis may differ. It is
practical, therefore, to examine the tolerance of one symbiont in relation to
the tolerance of the other. Table II‑3
shows that despite a large range in tolerance to salts between species of
legumes there are no agricultural legumes that can be considered as highly
salt tolerant. Comparing the sensitivity of the microsymbiont, Rhizobium,
with that of the legume host will then indicate the relative importance of
efforts to increase rhizobial tolerance to salts in strain selection
programs. The
growth of all rhizobia tested was slowed by the presence of NaCl (Table II‑2). These results are contrary to those
obtained by Pillai and Sen (1973) who showed that the growth rate of Rhizobium
spp. increased with 1% NaCl added to broth media (EC = 18.0 mmhos cm-1). Steinborne and Roughley (1975), on the
other hand, have shown that the growth of both R. trifolii and R. meliloti
was slowed with the addition of salt. Relative
tolerances to salt are given in Table II‑2 to allow comparison of the
effect of salt on growth of strains with large differences in inherent
MDT's. Large increases in MDT, or
growth suppression was not observed for any of the strains until the broth EC
reached 13.1 mmhos cm‑1 (28% sea water equivalent). This solution is in excess of solution
concentrations in which agricultural legumes can sustain an economic yield. |
Slow‑growing
strains were not more tolerant to salt than fast-growing strains. Isolates from saline environments were not
consistently more tolerant to salt than isolates from non‑saline
soils. Isolates 7B, 8 and 14E from
saline environments, either did not grow, or grew poorly in broth with an EC
of 13.1 mmhos cm-1. Strain
TAL 425, an isolate from an acid tropical soil, had a MDT at 13.1 mmhos cm-1
only 2.4 times that in normal media. Subjecting
two salt "tolerant" isolates (17E and 21A) and two
"sensitive" strains (Hawaii 5‑0 and USDA 110) to an extreme
reduction in osmotic potential had no effect on survival over 5 hours (Figure
II‑1). The solution with an EC
of 43.0 mmhos cm‑1 has a salt concentration equivalent to
92% of sea water (Thomas et al., 1934).
Since rhizobia can withstand large reduction in osmotic potential,
they must be able to rapidly regulate and adjust their internal solute concentration. Vincent et al., (1962) showed that R. trifolii
populations fell from log 4.35 to log < 1.0 in 160 mM NaCl (EC
= 16.0 mmhos cm-1) solution following a 48‑hour
exposure. Suspensions were, however,
equilibrated with an atmosphere of 20% relative humidity which reduced the
water content of the suspension to minimal amounts and left cells exposed to
pure NaCl. Our results agree with
Carr and Ballard (1979) who found that a strain of R. trifolii could
survive short term exposure to fertilizer solutions with EC's approaching 60
mmhos cm-1. Normal
YEM broth cultures with initial densities in excess of 1 x 109
cells ml‑1 lost viability over time; declining until numbers
were equal to, or less than, numbers in most salt treatments. |
two symbionts. While the host legume produces seed and enters dormancy at the
onset of the dry season; its microsymbiont, the Rhizobium, in order to
survive, must be able to encounter much higher levels of salts in the soil
solution as the soil dries. |
Examination of rhizobial tolerance to
stress in liquid culture, therefore, should not begin with cell densities of
109 ml-1 since these numbers cannot be maintained even
in ideal conditions. There
is an inverse relationship between soil moisture tension and
salinity in micro‑environments.
Reducing soil moisture content necessarily
concentrates salts in the soil solution.
Inoculum placed into
soil at planting encounters immediate fluctuations in soil water potential
(the sum of matric and osmotic potentials).
Treatment combinations
selected to test the effects of both soil moisture tension and
salinity on the survival of Rhizobium range from soil conditions which
may be considered optimum for plant growth (EC = 0.2 mmhos cm‑1 and
‑0.1 bar) to an extreme condition which is unacceptable for sup- porting
adequate growth of agricultural legumes (EC = 12 mmhos cm‑1 and
‑15 bars). None of the four
strains tested (17E, Hawaii 5‑0, USDA
110, and 21A) lost viability rapidly even with the most extreme treatment
(Figure TI‑2). R. leguminosarum
strain Hawaii 5‑0 which was sensitive
to salt in both the growth rate study and exposure to salts in
solution grew slightly and survived well in this clay soil. Isolate 21A
which showed good tolerance to solutions with EC's of 43.0 mmhos cm‑1
lost viability over time with the combined effects of high salinity and
dessication. The decline was not
strictly due to the low moisture content
since 21A survived well at ‑15 bars and 5.0 mmhos cm-1. R.
japonicum strain USDA 110 lost viability as a function of increasing stress
from both the osmotic and matric components of soil water potential. The fast‑growing isolate 17E was
completely resistant to all
levels of stress in this experiment. |
Marshall (1964) and Bushby and Marshall
(1977) concluded that slow‑growing rhizobia tolerated dessicated sandy
soil better than fast-growing species.
All species survived dessication better when sandy soil was ammended
with montmorilloinite. Our study shows
that a strain's inherent growth rate does not determine its resistance to low
soil moisture content or salinity. Both 17E and B73 survived the combination
of high salinity and increased moisture tension in this clay soil better than
slow‑growing strains USDA 110 and 21A. Mahler and Wollum (1980, 1981) showed that
even clay soil at ‑15.0 bars moisture tension was detrimental to the
survival of many strains of R. japonicum and R. leguminosarum. Their soil was, however, autoclaved for
270 minutes after which soil samples used for incubation of rhizobia were
contaminated with other bacteria.
Growth of other bacteria in the incubation vessels decreased as a
function of decreasing soil moisture content (Mahler and Wollum, 1980). We have found that by maintaining sterile
conditions in gamma irradiated soil none of the strains tested was affected
by either soil moisture tension or salinity levels used in this study. There appears to be no differential effect
of moisture tension and salinity on rhizobial survival. The reduced survival of USDA 110 and 21A
seems to be caused by the additive effects of increasing salinity and
moisture tension. The results of the above experiments
emphasize that many strains of Rhizobium not only can withstand, but
may even grow at, salt concentrations in excess of those tolerated by most
agriculturally important legumes.
This is consistent with the life‑cycle characteristics of the |
|
TABLE II-1. -- |
Source
of cultures. |
|
|
Culture |
Host |
Soil
Environment |
Location |
Source |
17Ea |
Leucaena leucocephala |
beach
sand |
Kualoa,
Oahu |
b |
Hawaii
5-0 |
Lens esulenta |
acid
tropical soil |
Molokai |
c |
7Ba |
Indigofera suffruticosa |
beach
sand |
Kualoa,
Oahu |
b |
Web
48 |
Glycine max |
soybean
field |
Midwest,
USA |
d |
TAL
425 |
Vigna radiata |
acid
tropical soil |
Thailand |
e |
23Ba |
Macroptiium lathyroides |
flood
plain |
Kahuku,
Oahu |
b |
8a |
Mimosa pudica
|
beach
sand |
Kualoa,
Oahu |
b |
14Ea |
Croatalaria mucronata |
irrigated
cane field |
Ewa,,
Oahu |
b |
TAL
426 |
Vigna unguiculata |
acid
tropical soil |
Thailand |
e |
21Aa |
Canavalia spp. |
beach
sand |
Laie,
Oahu |
b |
USDA
110 |
Glycine max |
soybean
field |
Florida,
USA |
f |
aIsolate
from bThis
study. cS.
N. May, M. dB.
B. Bohlool, eCulture
fCulture
|
saline
soil, EC of saturation extract > 5.0 mmhos S.
Thesis, University of Hawaii, 1979. M.
S. Thesis, University of Minnesota, 1979. collection,
NifTAL Project, Paia, Hawaii. collection,
USDA, Beltsville, Maryland. |
cm-1. |
|
|
TABLE II-2. -- |
Effect of NaCl on the mean doubling time
(MDT) of
of 11 strains of Rhizobium. |
||
|
Mean
Doubling Time (Hours) |
|
|
Strain |
0 mM NaCl 50 mM NaCl (1.2 mmhos) (6.7 mmhos) |
100 mM NaCl (13.1 mmhos) |
Relative Tolerancec |
17Ea |
2.7 5.3 |
8.4 |
3.1 |
Hawaii 5-0 |
3.9 11.8 |
N.G.b |
--- |
7Ba |
6.0 7.7 |
69.7 |
11.6 |
Web 48 |
8.7 11.9 |
N.G. |
--- |
TAL 425 |
7.4 7.5 |
17.4 |
2.4 |
23Ba |
6.2 7.9 |
10.1 |
1.6 |
8a |
5.9 7.1 |
N.G. |
--- |
14Ea |
7.4 7.8 |
69.0 |
9.3 |
TAL 426 |
8.4 7.5 |
26.4 |
3.1 |
21Aa |
10.3 12.6 |
17.6 |
1.7 |
USDA 110 |
5.5 6.3 |
27.2 |
5.0 |
aIsolated
from bNo
growth. cThe
ratio of |
salt affected soils. MDT at 13.1 mmhos cm-l: MDT |
at 1.2 mmhos |
cm-1. |
|
TABLE 11-3. -- The salinity tolerance of
some Crop |
agricultural plants.a ECb |
Barley |
16 |
Birdsfoot
Trefoil |
10 |
Sesbania |
9 |
Soybean |
9 |
Alfalfa |
8 |
Clover |
4 |
Kidney
Bean |
3 |
Peas |
2 |
aBernstein (1). bEC (mmhos cm-1)
associated with 50% decline |
in yield. |
|
|
|
LITERATURE CITED Bernstein, L. 1964. Salt tolerance of
plants. USDA Agric. Inf. Bul. 283. U. S. Government Printing Office, Washington, D. C. Bernstein, L., and G. Ogata. 1966. Effects
of salinity on nodulation, nitrogen fixation and growth of soybeans and
alfalfa. Agron. J. 58:201‑203. Bhardwaj, K. K. R. 1972. Note on the growth
of Rhizobium strains of dhaincha (Sesbania cannabina (Retz.)
Pers.) in a saline‑alkali soil. Ind. J. Agric. Sci. 42:432‑433. Bushby, H. V. A., and K. C. Marshall. 1977.
Some factors affecting the survival of root‑nodule bacteria on
dessication. Soil. Biol. Biochem. 9:143‑147. Carr, W. W., and T. M. Ballard. 1979.
Effects of fertilizer salt concentration on viability of seed and Rhizobium
used for hydroseeding. Can. J. Bot. 57:701‑704. Childs, E. C., and N. Coll is‑George.
1950. The control of soil water. Ad. Agroni. 2:234‑269. Flowers, T. J., P. F. Troke, and A. R. Yeo.
1977. The mechanism of salt tolerance in halophytes. Ann. Rev. Plant Physiol.
28:89‑121. Mahler, R. L., and A. G. Wollum II. 1980.
Influence of water potential on the survival of rhizobia in a Goldsboro
loamy sand. Soil Sci. Soc. Am. J. 44:988‑992. Mahler, R. L. and A. G. Wollum II. 1981.
The influence of soil water potential and soil texture on the survival of Rhizobium
japonicum and Rhizobium leguminosarum isolates in
the soil. Soil Sci. Soc. Am. J. 45:761‑766.. Marshall, K. C. 1964. Survival of root‑nodule
bacteria in dry soils exposed to high temperatures. Aust. J. Agric. Res.
15:273‑281. Parker, C. A., M. R. Trinick, and D. L.
Chatel. 1977. Rhizobia as soil and rhizosphere inhabitants. _In R. W. F.
Hardy and A. H. Gibson (ed.). A treatise on dinitrogen fixation, vol. IV.
John Wiley & Sons, New York. Pillai, R. N., and A. Sen. 1973. Salt
tolerance of Rhizobium from Dolichos lablab. Zbl. Bakt. Abt. II. 128:538‑542. Steinborne, J., and R. J. Roughley. 1975.
Toxicity of sodium chloride ions to Rhizobium spp. in broth and peat
culture. J. Appl. Bact. 39 :133‑13.8. |
Thomas, B. D., T. G. Thompson, and C. L.
Utterbuck. 1934. The electrical conductivity of sea water. Int. Coun. Expl.
Sea. 9:28‑35. United States Salinity Laboratory Staff.
1954. Diagnosis and improvement of saline and alkali soils. USDA Handbook
60, U. S. Government Printing Office, Washington, D. C. Vincent, J. M., J. A. Thompson, and K. 0. Donovan.
1962. Death of root‑nodule bacteria on drying. Aust. J. Agric. Res.
13:258‑270. Vincent, J. M. 1970. A manual for the practical
study of the rootnodule bacteria. Blackwell Scientific Publications, Oxford. Wilson, J. R. 1970. Response to salinity in
Glycine VI. Aust. J. Exp. Agric. Anim. Husb. 21:571‑582. |
CHAPTER
III A
SPLIT‑ROOT GROWTH SYSTEM FOR EVALUATING THE EFFECT OF SALINITY ON
COMPONENTS OF THE SOYBEAN‑RHIZOBIUM JAPONICUM SYMBIOSIS Abstract Study
of the effects of salinity on symbiotic processes is complicated by the high
degree of integration between shoot and nodules. Shoot photosynthetic capacity determines not only the amount of
photosynthate available to the nodule, but the strength of the sink for nodule
products. Salinity may also directly
affect functional processes within the nodule. Two
experiments were undertaken which employed a split‑root solution
culture assembly that confined nitrogen fixation to one‑half of soybean
root systems. In one experiment, one‑half
of the root system was inoculated with non‑nitrogen fixing strain
(ineffective) of Rhizobium japonicum, SM‑5, 48 hours
prior to inoculating the other side with effective strain USDA 110. Nodulation and nitrogen fixation by USDA
110 when in combination with SM‑5 was significantly suppressed compared
to a second treatment where one‑half of the root system was inoculated
with USDA 110 and the other half remained uninoculated. Root development was significantly greater
on the side producing effective nodules than that of the uninoculated or SM‑5
nodulated half‑root systems. In
another experiment, half‑root systems were nodulated with USDA 110
and the opposite side with SM‑5.
After nodule development, NaCl (120
mM) was added to the nutrient solutions of: 1) neither half, 2)
effective nodule (USDA 110) half, 3) ineffective nodule (SM‑5) half, |
or 4) both half‑root systems. Osmotic potentials (Ψπ) of
roots, nodules and leaves were measured.
Leaves of plants with only half their roots salinized had Ψπ
(‑10.3 bar and ‑11.1 bar treatments 2 and 3 respectively)
comparable to the non‑salinized control (‑9.3 bar). Leaf Ψπ of plants with both root halves in salt
solutions was ‑17.9 bar.
Nodules exposed to salt solutions had Ψπ values ranging from ‑9.3 to ‑12.2
bar while Ψπ of nodules in
normal solutions ranged from ‑6.1 to ‑7.8 bar. Ineffective nodules always had a lower
Ψπ than similarly treated
effective nodules. These results
demonstrate that functional components of the soybean‑Rhizobium japonicum
symbiosis can be independently subjected to salinity stress. This methodology can be used to evaluate
the relative sensitivity of the components of the symbiosis. Introduction The
legume‑Rhizobium symbiosis is a highly integrated system. Soil stress may act on the symbiosis
indirectly by reducing plant growth potential and the availability of
photosynthate, or act directly on nodule function and/or the infection
process. In order to increase
tolerance of the symbiotic system to a stress, the most stress‑sensitive
component(s) need to be identified.
This can be done by subjecting shoot photosynthetic capacity and
nodule functioning to differential levels of stress and partitioning the
effects of stress to the components of the symbiosis. Split
root growth systems have been used to study the effects of various stresses
on plant growth and root development: salinity (Eaton, 1941; Kirkham et al.,
1972); moisture tension (Volk, 1947; nutrient |
availability (Gile and Carrero, 1917;
Hackett, 1972). Hinson (1975)
confined nodulation to half the root system of soybeans grown in vermiculite
to study the localized effect of mineral N on nodule development. Such a system is not, however, suitable
for studying the effect of salinity on the symbiosis since migration of salts
in the rooting medium may create zones of variable osmotic potential, so that
nodules and roots will not be exposed to a uniform stress. This
paper describes two experiments using a solution culture, split‑root
growth system suitable for examining the effects of various stresses on
components of the legume‑Rhizobium symbiosis. The technique was used for two
experiments. The first examines two
methods of confining nitrogen‑fixing root nodules to one‑half of
soybean root systems and the effect that nodulation has upon root
development, water uptake, and nitrogen fixation. A second examines the effect of applying NaCl to either half or
whole root systems on leaf, nodule and root osmotic potential Materials
and Methods Growth System Steel
containers (20 liters) were coated inside and out with an elastomeric
protective coating USDA has approved for potable water (Vabar 792, United
Coatings). The top of each container
was removed except for an 8.0 cm strip along one side (Figure III‑1). This strip had eight 2.54 cm holes to
receive one end of a PVC elbow (21.0 mm 0. D., 6.0 cm sides), packed with
sterile vermiculite. A planting hole
(10 mm |
dia.) was drilled on the joint of each
elbow. Planting holes were to receive
seedling radicles. The ends of elbows
were fitted with a rubber washer to stabilize the elbows which spanned two
containers. A sight glass was fitted
to each container and calibrated volumetrically to the nearest 0.5 liter.
Each container had an aquarium airstone connected to a flexible plastic
lateral air line to create a constant splash of solution on the ends of the
PVC elbows. The solutions were
saturated with oxygen as measured with a YSI oxygen meter. Lids for the containers were made from
2.54 cm sheets of polystyrene. The
bottom lid was covered with black polyethylene. Seeds
of soybean (Glycine max (L.) Merr. 'Davis') were treated for 5
min. with 70% ethanol, rinsed, planted hilum down in sterile vermiculite and
at 28 C for 48 hours. The tips of the
seedling radicles were removed to induce branching and seedlings were then
inserted into the planting holes.
Sterile water was applied to the seedling to ensure capillarity
between the cut radicle and vermiculite.
The sides of the elbows were covered with foil to maintain the same
temperature on both sides. Preparation of Inoculum Cultures
of Rhizobium japonicum, ineffective strain SM‑5 (W. J.
Brill, University of Wisconsin, Madison) and an effective strain USDA 110
(USDA, Beltsville, Md.) were grown in yeast extract mannitol broth and
counted by the drop plate method (Vincent, 1970) then centrifuged for 10 min.
at 12,100 x g and 4 C. The cells were
resuspended in |
water and inoculated into appropriate
containers to the final numbers stated for each experiment. Nutrient Solution A
nitrogen‑free nutrient solution was used consisting of: 0.5 mM P; 0.96
mM K; 1.56 mM S; 0.82 mM Mg; .75 mM Ca.
Sources were: K2HPO4; MgSO4·7H2O;
CaSO4. Micronutrients were
added according to Broughton and Dilworth (1971). Effective vs Ineffective Rhizobium
Experiment Five
days after planting roots emerged from elbows into the containers. At this time, designated containers were
inoculated with SM‑5 at the rate of 1.5 x 106 viable
cells/ml of plant nutrient solution.
Forty‑eight hours later USDA 110 was inoculated at 4.4 x 104
cells/ml in containers to institute as two treatment combinations: 1) USDA
110 on one side and no inoculation on the other, 2) USDA 110 on one side with
ineffective SM‑5 on the other.
Inoculation with SM‑5 preceeded that of USDA 110 so that some of
the early processes of infection would be complete and reduce the chance of
formation effective nodules on the non‑nitrogen fixing (SM‑5)
side. Containers were arranged in a
completely randomized design and replicated three times. Both experiments were carried out in a
glasshouse during the months of June and July. Solution pH was monitered but never declined below 5.8. Solution temperatures ranged from 26 C ‑
28 C at 2 p.m. Nutrient solutions
were changed at 20 and 40 days from planting followed by harvest at 60 days. |
Containers were inoculated to the original
cell density with the appropriate Rhizobium, after each solution
change. At
harvest, the containers were drained, shoots were cut and dried at 60 C. Roots were removed and immediately
incubated in 2.3 liter plastic vessels containing 5% acetylene. Ethylene production was determined by gas
chromatography. Nodules were removed
from roots, oven dried, counted and weighted. Salinization
of Half‑Root Systems The planting procedure was
identical to that in the first experiment. Solutions were changed at 21 and
34 days from planting. Each container
of a pair was inoculated with either SM‑5 or USDA 110. Salt
treatments were instituted at Day 34 by adding NaCl to designated containers
over a 48‑hour period to a final concentration of 120 mM NaCl (normal
solution osmotic pressure (OP) = ‑0.15 bar, salinized solutions OP = ‑5.5
bar). Four combinations of salt treatments to half‑root systems were
instituted: 1) No salt to either side, 2) salt to the non‑nitrogen
fixing half‑root system (SM‑5), 3) salt to nitrogen-fixing half‑root
system (USDA 110), 4) salt to both half‑root systems. The
osmotic potential (Ψπ) of the most recently expanded trifoliate,
nodules and roots were sampled at Day 45.
Nodule and root samples were blotted dry and each placed in 8 cm
lengths of 12 mm I. D. flexible plastic tubing. Leaves were placed directly
into a tube. Tubes were plugged at
both ends with rubber stoppers after expressing most of the air and then
frozen on dry ice. Samples were thawed for 20 minutes, |
pressed at 1050 kg/cm2, and the
expressed sap was sampled with filter paper discs which were placed in a
Wescor Model 5130 vapor pressure osmometer. Results Plants
with half their roots inoculated with ineffective strain SM‑5 had
reduced shoot, root, and nodule dry weights.
The number, mass and nitrogenase activity of nodules formed by
effective strain USDA 110 was reduced when the other half of the root system
had SM‑5 nodules (Table III‑1).
Uninoculated half‑root systems remained free of nodules. Development of half‑root systems was
stimulated by inoculation with USDA 110.
Water consumption followed a similar pattern. No nitrogenase activity was detected on
either the uninoculated or the ineffectively nodulated half‑root
system. Leaf
Ψπ (‑10.3 and ‑11.1 bar) of plants with half of their
root system exposed to 120 mM NaCl was not different than the control (‑9.3
bar) (Table III‑2). Leaf
Ψπ was reduced to ‑17.9 bar when both root halves were
exposed to salt. Nodule Ψπ
was a function of the solution to which they were exposed. When USDA 110 nodules were exposed to NaCl
nodule Ψπ was ‑10.9 bar and ‑12.2 bar respectively for
half and whole-root salt treatments.
Ineffective nodules (SM‑5) had nodule Ψπ of ‑9.3
bar for both half and whole‑root salt treatments. Ψπ of non‑salinized USDA
110 nodules was ‑7.8 bar and ‑6.1 bar for non‑salinized SM‑5
nodules. Water absorption by half‑root
systems was reduced by the addition of 120 mM NaCl. This reduction was compensated for by increased uptake on the
non‑salinized side. |
|
TABLE
III-1. -- Rhizobium japonicum
|
Effect
of on
shoot |
inoculating
soybean half-root systems weight,
root and nodule development, |
with
effective and ineffective strains of nitrogenase
activity and total water use.a |
||||||
Inoculation of Half-Root System |
Shoot |
Dry Weight Root |
Nodule |
Nodule Number |
Nitrogenase Activity |
Water Consumption |
|||
|
|
---------g/Pot---------- |
|
no/pot |
µMC2H4/pot/h |
1/pot |
|||
I |
|
|
|
|
|
|
|||
Uninoculated
Side |
|
1.2 |
trace |
1 |
0 |
13.0 |
|||
USDA
110 Side |
|
2.0 |
1.30 |
621 |
56 |
18.0 |
|||
Total |
18.8 |
3.2 |
1.30 |
622 |
|
31.0 |
|||
II |
|
|
|
|
|
|
|||
SM-5
Side |
|
0.5 |
0.15 |
424 |
0 |
10.0 |
|||
USDA
110 Side |
|
0.7 |
0.23 |
191 |
11 |
11.0 |
|||
Total |
5.1 |
1.2 |
0.38 |
615 |
|
21.0 |
|||
LSD .05 |
13.0 |
0.6 |
0.54 |
233 |
23 |
5.0 |
|||
aThe
ineffective of
the effective |
strain,
SM-5, was inoculated into strain,
USDA 110, to the opposite |
the
designated side |
side
48 hours before the |
application |
|
TABLE III-2. -- Effect of 120
potential (Ψπ) of leaves, |
mM NaCl added nodules, roots |
to half-root systems and water consumption |
of nodulated subsequent |
soybean on the osmotic to NaCl addition. |
||
Salt
Treatment To
Half-Root System
Growing: |
|
|
Potential |
(Ψπ) |
|
Water |
Nodules Nodules |
Leaves |
Nodule
USDA 110 SM-5 |
USDA 110 |
Root
SM-5 |
Consumption
USDA 110 SM-5 |
|
mM NaCl |
|
|
bar |
|
|
liter/day |
0 0 |
-9.3 |
-7.8 |
-6.1 |
-5.4 |
-6.0 |
0.61 0.44 |
0 120 |
-10.3 |
-7.8 |
-9.3 |
-5.5 |
-7.5 |
1.10 0.23 |
120 0 |
-11.1 |
-10.9 |
-6.9 |
-7.1 |
-5.8 |
0.32 0.98 |
120 120 |
-17.9 |
-12.2 |
-9.3 |
-8.1 |
-7.1 |
0.29 0.33 |
LSD
.05 |
-3.2 |
-1.2 |
|
-1.3 |
|
|
Discussion To
test the effects of salinity on the integrated processes of the legume‑Rhizobium
symbiosis, it is necessary to isolate and independently subject
photosynthetic and nodule processes to the stress. A growth system suitable for such purposes must meet two
requirements. First, all nitrogen‑fixing
nodules must be confined to a portion of the root system. Secondly, the
salinity stress must be uniformly applied to the nodules with a minimal
effect on the photosynthetic apparatus. Solution
culture systems are advantageous for salinity studies since uniform osmotic
potentials in the root environment can be maintained. By employing a split‑root technique
which confines rhizobial inoculation and subsequent nodulation to one‑half
of the root system, it is possible to subject the functional processes of the
nitrogenase system to salinity while maintaining the shoot under less
stressful conditions. Kirkham et al.,
(1969) demonstrated that although leaf water potential of Phaseolus vulgaris
with half the root system in salinized medium was reduced, the potential more
closely resembled the no salt control than the leaf potential of plants with
both root halves in salinized media.
Using tritiated water, Sprent (1972) concluded that nodules received
water en route from roots to leaves. This would imply that nodules are at a
lower water potential than surrounding roots. However, given the large amount of phloem transport taking place
from shoot to nodule (Minchin and Pate, 1974), it seems plausible that |
the osmotic potential of nodules in the
localized stress environment of differentially salinized plants may not
adjust to their environment. This
study examines two methods of maintaining nitrogen‑fixing nodules on half
the root system of soybean. In
addition, we evaluate the osmotic adjustment of roots, nodules and leaves of
plants with differentially salinized root systems. Effective
vs Ineffective Rhizobium Experiment Inoculation
of half the root system with an ineffective strain (SM‑5) 48 hours
before the introduction of the effective strain (USDA 110) on the opposite
side caused a reduction in the number, weight and activity of the resulting
effective nodules (Table III‑1).
Total nodule number (effective and ineffective) however, remained the
same regardless of the treatment.
Weight of effective nodules was reduced when SM‑5 was inoculated
to the other side. Apparently, total nodule number on a soybean root system
is controlled by the host and strains of Rhizobium compete for limited
nodule sites. Competition for nodule
sites exists even when there is spatial separation of the strains on the root
system. The competitive advantage of
SM‑5 when inoculated first indicates that events early in the infection
and nodule development processes determine what proportion of the nodules
will be formed by each strain. When
SM‑5 was used as a method to confine effective strain USDA 110 to one‑half
the root system the proportion of total nodule number (USDA 110 nodules plus
SM‑5 nodules) that was formed by USDA 110 was less than 30%. Singleton and Stockinger (1982) have shown
that despite the existence of a compensating mechanism for ineffective
nodulation, |
effective nodule mass and nitrogen fixation
is seriously reduced when effective nodules were less than 50% of the
total. The design of the growth
system maintained the uninoculated half‑root system sufficiently free
of contaminant nodules so that the source of symbiotic nitrogen can be
isolated and inoculation with an ineffective strain on one side is not
necessary. Root
development was stimulated by effective nodules. Root weight was consistently greater on the side where the
effective nodules were present compared to uninoculated and ineffectively
nodulated sides. Total water
consumption followed the same pattern (Table III‑1). Increased flow of carbon to active nodules
and the increased localized availability of nitrogen from active nodules may
be the reason for increased root development. Drew (1975) showed that application of nitrate and ammonium had
a localized stimulatory effect on root development. When the source of symbiotic nitrogen is localized there
appears to be a similar stimulation of root development. Salinization
of Half‑Root Systems Application
of 120 mM NaCl to half‑root systems reduced the osmotic potential (Ψπ)
of roots and nodules exposed to these solutions. Nodules were always at a lower potential than their respective
roots. Leaf was more negative than
the Ψπ of both nodules and roots when only those half‑root
systems were exposed to NaCl. The
potential gradient necessary for transport of fixation products between
nodule and shoot is therefore maintained. |
Shoots
of plants with half their root system in salinized solutions had leaf
Ψπ values closer to those of the non‑salinized control, than
to leaf Ψπ of plants with the complete root system in salinized
solutions. Increased water uptake by
the non‑salinized half‑root system compensated for salinity
stress on the opposite half‑root system (Table III‑2). These results indicate that the nodule
system can be subjected to salinity stress while maintaining a relatively
unstressed photosynthetic apparatus. In
conclusion, the growth system design described in this paper provides
sufficient control of localized nodulation to confine the source of symbiotic
nitrogen fixation to half‑root systems of soybean. Osmotic adjustment by roots, nodules and
leaves of differentially salinized soybeans with split‑root systems
allows observation of nodule processes under stress when the shoot is under
normal conditions. The use of this
type of growth system may prove useful in the study of the effects of other
soil stress factors on symbiotic processes. |
LITERATURE CITED Broughton,
W. J., and M. J. Dilworth. 1971. Control of leghemoglobin synthesis in
snakebeans. Biochem. J. 125:1075‑1080. Drew,
M. C. 1975. Comparison of the effect of a localized supply of phosphate,
nitrate, ammonium and potassium on the seminal root system and the shoot in
barley. New Phytol. 75:479‑490. Gile,
P. L., and J. 0. Carrero. 1917. Absorption of nutrients as affected by the
number of roots supplied with the nutrient. J. Agric. Res. 9:73‑95. Hackett,
C. 1972. A method of applying nutrients locally to roots under controlled
conditions, and some morphological effects of locally applied nitrate on the
branching of wheat roots. Aust. J. Biol. Sci. 25:1169‑1180. Hinson,
K. 1975. Nodulation responses from nitrogen applied to soybean half‑root
systems. Agron. J. 67:799‑804. Kirkham,
M. B., W. R. Gardner, and G. C. Gerloff. 1969. Leaf water potential of
differentially salinized plants. Plant Physiol. 44:1378‑1382. Kirkham,
M. B., W. R. Gardner, and G. C. Gerloff. 1972. Stomatal conductance of
differentially salinized plants. Plant Physiol. 49:345‑347. Minchin,
F. R., and J. S. Pate. 1974. Diurnal functioning of the legume root nodule.
J. Exp. Bot. 25:295‑308. Singleton,
P. W., and K. R. Stockinger. 1982. Compensation against ineffective
nodulation in soybean. Crop Sci. In Press. Sprent,
J. I. 1972. The effects of water stress on nitrogen fixing root nodules. IV.
Effects on whole plants of Vicia faba and Glycine max.
New Phytol. 71:603‑611. Vincent,
J. M. 1970. A manual for the practical study of the rootnodule bacteria.
Blackwell Scientific Publications, Oxford. Volk,
G. M. 1947. Significance of moisture translocation from soil zones of low
moisture tension to zones of high moisture tension by plant roots. Agron. J.
39:93‑106. |
CHAPTER
IV THE
EFFECT OF SALINITY ON THE FUNCTIONAL COMPONENTS OF
THE SOYBEAN‑RHIZOBIUM JAPONICUM SYMBIOSIS Abstract A
split‑root solution culture system was used to partition the effects of
salinity on the functional components of the soybean (Glycine max
(L.) Merr) ‑Rhizobium japonicum symbiosis. Nodules were confined to half of the root
system. After nodules were well
developed (40 days from planting), salt, at 120 mM NaCl, was applied to the
half‑root systems in the following combinations: 1) unstressed, no salt
to either half‑root system; 2) partially stressed shoot and unstressed
nodules, salt to only the non‑modulated half‑root system; 3)
partially stressed shoot and stressed nodules, salt to only the modulated
half‑root system; 4) stressed shoot and nodules, salt to both half‑root
systems. Osmotic
potentials (Ψπ) of leaves for the four treatments were: 1) ‑10.2;
2) ‑11.2; 3) ‑12.3; and 4) ‑18.3 bar. Nodule Ψπ for the treatments were: 1) ‑7.0; 2)
‑7.2; 3) ‑11.2; and 4) ‑12.1 bar. While total and specific nitrogenase activity as well as shoot
nitrogen content were suppressed slightly in Treatment 3, the greatest
reduction in activity and shoot nitrogen was observed when the plant was
stressed by having both half‑root systems in salt (Treatment 4). The rate of leaf expansion in Treatment 4
was half the rate observed in other treatments. We conclude that reduced nitrogen fixation by modulated
soybeans growing in saline environments was more a result of the effect |
of salt on leaf Ψπ and expansion,
than the direct action of salt on the functional processes of the nitrogenase
system. Introduction The
legume‑Rhizobium symbiosis is a highly integrated process
involving a complex interaction between the host and microorganism. A constant exchange of metabolites takes
place between plant photosynthetic organs and root‑nodules.
Photosynthate enters the nodule by phloem transport where it is either
respired for nodule growth, maintenance and reduction of N2 or re‑exported
to the shoot as amino compounds (Pate, 1976). The production and flow of amino compounds, as with other
assimilates, is regulated and ultimately partitioned to growth points and
reproductive sinks in relation to growth potential (Lewis and Pate,
1973). Therefore, any stress which
reduces photosynthesis and plant growth will undoubtedly affect nitrogen
fixation. Soil
stress may reduce symbiotic activity to levels below the genetic potential of
a host‑Rhizobium strain combination. The stress could reduce the accumulation of symbiotically
derived nitrogen by either affecting shoot photosynthesis and yield potential
or by directly affecting processes within the nodule. Due to the integrated nature of the
functional processes of the symbiosis it becomes difficult to assess the
relative sensitivity of host and microorganism to stress. By identifying which components or
processes of the symbiosis is most sensitive to the soil stress, efforts to
increase nitrogen fixation in these environments may then focus on the proper
component. |
Sprent
(1972) observed a 50% decline in nitrogenase activity within 19 minutes of
exposing the entire nodulated root system of soybean plants to 120 mM
NaCl. Exposure of detached soybean
nodules to 1 M NaCl also depressed nitrogenase activity. Lauter
et al., (1981) showed that salinity adversely affected nodule weight and
total nitrogenase activity of chickpea (Cicer arietinum L.).
Similar results were obtained for soybean and alfalfa (Medicago sativa
L.) by Bernstein and Ogata (1966) and for Glycine wightii by
Wilson (1970). Since salinity is
known to reduce photosynthesis and growth of most plants (Gale, 1975), the
above studies do not determine how salinity limited the symbiosis. This
study was conducted to assess the effects of salinity on the components of
the soybean‑Rhizobium japonicum symbiosis. We partitioned the effects of salinity on
nitrogen fixation into effects that directly relate to nodule function versus
indirect effects which are mediated through the host photosynthetic apparatus. Materials and Methods Plant Culture The
split‑root solution culture growth system which confined the nodules to
half the root system of soybean (Glycine max (L.) Merr C. V.
Davis) and the planting procedure have been described earlier (Chapter III).
At planting NH4NO3 (7.1 mM N) was added to the basal
nutrient solution: (mM) 0.5 P; 0.96 K; 1.56 S; 0.82 Mg; 0.75 Ca. Solutions
were changed 22 days from planting and one‑half of the |
split‑root system was inoculated with
Rhizobium japonicum strain USDA 110 (USDA Beltsville MD) at a
density of 9.7 x 105 cells/ml of culture solution. The opposite
half of the root system remained uninoculated. NH4NO3
(.75 mM N) was added to the basal nutrient solution of the uninoculated half
to supply the plant with nitrogen during nodule development. Significant nodule development was
observed 40 days from planting. At
this time solutions were changed, nodulated sides reinoculated (7.1 x 104
cells/ml) and NaCl was introduced over a two‑day period to designated
containers to a final concentration of 120 mM NaCl. No nitrogen was supplied to plants after treatment
initiation. Solutions were again
changed at Day 46, reinoculated (1.7 x 105 cells/ml) and
designated containers resalinized.
Plants were harvested at 50 days from planting. Salinity
Treatments to Half‑Root Systems Four
treatment combinations between the source of symbiotic nitrogen and salinity
were instituted and are displayed in Table IV‑1. Treatments were arranged in a completely
randomized design and replicated three times. Measurement
of Leaf Expansion Leaflets
of the most recently emerged trifoliate of three plants selected at random
were tagged and their initial leaf area determined with a Licor area
meter. The initial measurement was
performed 3 days |
after the initiation of salinity
treatments. The same trifoliates were
measured 5 days later. Results were expressed as expansion in cm2/day. Measurement
of Osmotic Potential (Ψπ) Eight
days after treatment initiation leaf, nodule and root were determined. The most recently expanded trifoliate of
three plants not used for measurement of leaf expansion were removed, and
nodules and root samples blotted dry and placed in 9 cm lengths of Tygon R‑3603
tubing (12 mm I. D., 2 mm wall). The
tubes were sealed with rubber stoppers and frozen on dry ice. Tubes were thawed (20 minutes), pressed at
1052 kg/cm2, and the expressed sap sampled with filter paper discs
which were placed in a Wescor 5130 vapor pressure osmometer. Harvest Shoots
were cut and oven dried at 65 C. Root
halves were removed, placed in 2 liter plastic bottles, and incubated for 30
minutes in 5% acetylene. Ethylene production was determined by gas
chromatography. Roots
and nodules were separated and oven dried.
K and Na contents of nodules were determined by flame photometry from
water extracts of ground tissue.
Chloride in nodules was determined potentiometrically using the
titrating method in conjunction with an Ag‑AgCl electrode and a glass
reference electrode (Chapman and Pratt, 1971). |
Results Shoot
dry weight and the concentration of N in the shoot declined when half‑
and whole‑root systems were exposed to NaCl (Table IV‑1). Leaf
osmotic potential (Ψπ) of plants with only half the root system
salinized was between 1 and 2 bar lower than the non‑salinized
control. With the whole‑root
system salinized leaf Ψπ was 8 bar lower than the control (Table IV‑2). Nodules exposed to salt had a Ψπ
4 bar lower than non‑salinized nodules. Nitrogenase
activity was reduced when the modulated half‑root system was exposed to
salt. However, there was a much
greater decline in nitrogenase activity when the whole‑root system was
salinized (Table IV‑3).
Specific nitrogenase activity was reduced when nodules were exposed to
salt. Specific activity of nodules on
plants with both half‑root systems salinized was approximately half of
that of nodules on plants with only the modulated half salinized (Table IV‑2). Leaf
expansion, while affected slightly by salinizing either half the root system,
was reduced by 50% when both half‑root systems were salinized (Table IV‑2). Data
for the concentrations of Na+, Cl- and K+ in
shoots and nodules are given in Table IV‑2. |
TABLE IV-1. -- The of soybean on |
effect
of NaCl (120mM) shoot dry weight and |
applied
to half-root systems shoot
nitrogen. |
Treatment to Half-Root Systema Nod Non-Nod |
Shoot Dry Weight |
Shoot Nitrogen |
|
g pot-l |
g pot-1 % |
1. - - |
150.6 |
4.1 2.69 |
2. -
+ |
118.3 |
3.2 2.70 |
3. + - |
130.9 |
2.6 2.01 |
4. + + |
80.5 |
1.8 2.29 |
LSD
.05 |
34.9 |
1.2 0.53 |
aHalf-root
systems nodulated normal
nutrient solution Salt
treatments instituted 50
days. |
(Nod)
or non-nodulated (Non-Nod) in either (-)
or nutrient solution plus 120 mM NaCl (+). at
Day 40 from planting until harvest at |
|
TABLE IV-2. -- The effect |
of shoot and nodule osmotic potential (Ψπ)
on nitrogenase and leaf expansion of soybean. |
||
Treatment
to Half-Root
Systema
Nod Non-Nod |
Ψπ Leaf Ψπ Nodule |
Nitrogenase Activity Totalb
Specificc |
Expansion of
new Trifoliate |
|
bar |
µMC2H4 |
cm2
days-1 |
1.
- - |
10.2 7.0 |
319 67 |
34 |
2.
- + |
11.2 7.2 |
217 57 |
31 |
3.
+ - |
12.3 11.2 |
168 43 |
31 |
4.
+ + |
18.3 12.1 |
47 23 |
16 |
LSD
.05 |
3.9 1.5 |
149 27 |
12 |
aHalf-root systems nodulated
nutrient solution (-) or
instituted at Day 40 from bTotal
nitrogenase activity cSpecific nitrogenase
activity: |
(Nod) or non-nodulated nutrient solution plus 120 planting until harvest of nodulated half-root µMC2H4 (g nodule |
(Non-Nod) in either mM NaCl (+). Salt at Day 50. systems: µMC2H4pot-1h-1
dry weight)-1h-1. |
normal treatments |
|
Discussion Studies
on the effect of salinity on the legume‑Rhizobium symbiosis have
always subjected the entire symbiotic system to the stress. Increasing salinity results in a reduction
of nodule number, nodule weight and total N fixed by Glycine wightii
(Wilson, 1970). Bernstein and Ogata
(1966) and Lauter et al., (1981) observed similar effects of salinity on
nodulation and nitrogen fixation by Glycine max and Cicer
arietinum respectively. In
both studies NO3‑fed plants subjected to salinity had higher
relative yields than similarly treated symbiotic plants. This suggests that the processes of the
symbiosis are relatively more sensitive to salinity than the mechanisms of
uptake and metabolism of mineral N.
The sensitivity of particular symbiotic processes cannot be determined
from these studies since both the shoot and nodule were stressed
simultaneously. To identify the
symbiotic process most susceptible to salinity, it is necessary to subject
shoot and nodules to salinity stress independently. Huang
et al., (1975b) partitioned the effects of soil moisture tension to
photosynthesis and nodule function of soybean. Photosynthesis of drought stressed plants was enhanced by CO2
enrichment which resulted in an increase in nitrogenase activity. Their methodology, however, requires a
great deal of preliminary investigation and more complex procedures than the
split‑root technique used in this study. Since
symbiotic nitrogen fixation is dependent on recently‑fixed
photosynthate (Minchin and Pate, 1974; Huang et al., 1975a) root |
TABLE IV-3. -- The on the |
effect
of NaCl (120 mM) applied to half-root systems of soybean
concentration of shoot and nodule Na, C1, and K. |
||
Treatment to Half-Root Systema Nod Non-Nod |
Shoot Nodule |
Cl-
|
K+ Shoot Nodule |
|
|
% |
|
1. - - |
0.05 0.2 |
0.21 0.03 |
2.3 2.13 |
2. - + |
0.18 0.4 |
0.88 0.05 |
2.2 1.72 |
3. + - |
0.23 3.7 |
1.05 0.44 |
1.9 0.88 |
4. + + |
0.98 3.7 |
3.35 0.49 |
2.5 0.82 |
LSD .05 |
0.36 0.15 |
0.59 0.16 |
0.22 0.43 |
aHalf-root systems nutrient solution (-) instituted from Day |
nodulated
(Nod) or non-nodulated (Non-Nod) in or
nutrient solution plus 120 mM NaCl (+). 40
from planting until harvest at Day 50. |
either
normal Salt
treatments |
|
environment stress which reduces
photosynthesis (or the translocation of photosynthate) to the nodules will
have a rapid effect on nodule function. Despite osmotic adjustment of roots
and shoots to reduced water potentials in the root environment (Bernstein,
1961), photosynthetic assimilation of carbon by glycophytes such as soybean
is adversely affected (Sung and Krieg, 1979; Jensen, 1975; Gale, 1975; Turner
et al., 1978). Sung and Krieg (1979)
concluded that photosynthesis was reduced with water stress in sorghum and
cotton prior to any reduction in translocation rates. Reduced photosynthesis by plants in saline
environments is characterized by reduced leaf expansion (Jensen, 1975; Hawker
and Walker, 1978) and increased leaf resistance to CO2
assimilation (Jensen, 1975). The
osmotic potential of shoots and nodules (Table IV‑2) indicate that
leaves and nodules of the same plant could be subjected to differential
salinity stress. Nodules of
Treatments 2 and 3 are functioning at a 4 bar Ψπ differential while
leaves of both treatments have approximately the same Ψπ.
Treatments 3 and 4 have nodules at the same Ψπ but leaves carrying
on growth and photosynthesis at a 5 bar difference. Turner et al., (1978) and Huang et al., (1975a) found that
photosynthetic rates in soybean were reduced substantially when leaf water
potentials were below 14 bar. Exposing
either the nodulated or non‑nodulated half of the root system to salt
resulted in a reduction in both shoot dry weight and total shoot N (Table IV‑1). When only the nodulated half was salt
stressed (Treatment 3) shoot N concentration was reduced. Apparently, |
the stressed nodules (Ψπ = ‑11.2
bar) could not supply adequate nitrogen to meet the growth requirements of
the relatively unstressed shoot. The
greater percent N in the shoot when both half‑root systems were
stressed (Treatment 4) indicates that it was not N availability that was
limiting shoot growth in this treatment. The
direct effects of salinity on nodule function can be determined by comparing
nitrogenase activities of Treatments 2 and 3. Total and specific nitrogenase activity was reduced when salinization
of modulated half‑root systems resulted in a ‑4 bar change in
nodule Ψπ. When the whole
symbiotic system was salt stressed (Treatment 4), however, a large reduction
in nitrogenase activity was observed.
This reduction can best be explained by the large reduction in leaf
Ψπ and leaf expansion rather than nodule Ψπ. Low
water potentials in the root environment affect both photosynthetic rates
(Boyer, 1970) and leaf expansion (Hawker and Walker, 1978). Since shoots are both the source of energy
for the nitrogenase system and the "sink" for nodule products, leaf
expansion can be considered as a measure of change in photosynthetic capacity
and strength of the "sink" for fixed nitrogen. The effect of
reducing leaf Ψπ on leaf expansion is illustrated in Table IV‑2.
Although leaf expansion rates were slightly affected when one‑half the
root system was exposed to salt and a leaf Ψπ declined by 1 or 2
bar, a 50% reduction in expansion rate was observed when leaf Ψπ
declined to ‑18.3 bar. Nitrogenase activity in the soybean‑R. japonicum
symbiosis is therefore limited by salinity through a reduction in leaf
Ψπ and shoot |
growth. The nitrogenase system can withstand
substantial reductions in
Ψπ from exposure to extremely saline environments provided the shoot
remains relatively unstressed. Tissue
analysis of shoots and nodules help to explain these results (Table IV‑3). Nodules, like roots (data not shown),
accumulated more Na+ and excluded Cl- relative to the
shoot. Uptake of Na+ by
nodules was negatively correlated with nodule K+. Shoot K+ was not greatly
affected by the salinity treatments. Our results show that nodule activity
can proceed at near normal rates despite the presence of high concentrations
of Na+, and an apparent reduction in K+. In
conclusion, differentially salinized soybeans with nodules confined to one‑half
the root system provide a simple system in which the processes of the
symbiosis may be subjected to stress independently. Plants with half their roots exposed to salt had leaf
Ψπ and shoot yield potentials approximately equivalent to non‑salinized
controls. Nodule Ψπ was a
function of the Ψπ of the solutions to which they were exposed
regardless of leaf Ψπ.
Nitrogenase activity of salinized nodules was more a function of the
degree of stress in the shoot rather than the direct effect of salt on nodule
processes. Even with the high
concentration of salt used in this experiment (120 mM NaCl), there appears to
be little direct effect of salt on nodule function. Reduced nitrogenase activities observed in plants with the
whole root system salt stressed was due to salt limiting leaf expansion,
shoot growth and demand for nitrogen.
The relative tolerance of established nodules to low water potentials
may have evolutionary and ecological relevance. |
Annual legumes such as soybean may mature
using water deep in the soil profile while, as the surface soil dries,
nodules must adjust and function in an environment of declining soil matric
and osmotic potentials. |
LITERATURE CITED Bernstein,
L. 1961. Osmotic adjustment of plants to saline media: I. Steady state. Am.
J. Bot. 48:909‑918. Bernstein,
L., and G. Ogata. 1966. Effects of salinity on nodulation, nitrogen fixation,
and growth of soybean and alfalfa. Agron. J. 58:201‑203. Broughton,
W. J., and M. J. Dilworth. 1971. Control of leghemoglobin synthesis in
snakebeans. Biochem. J. 125:1075‑1080. Boyer,
J. S. 1975. Differential sensitivity of photosynthesis to low leaf water
potentials in corn and soybean. Plant Physiol. 46:236‑239. Chapman,
H. D., and P. F. Pratt. 1971.
Methods of analysis for soils, plants and waters. University of California
Press. Gale,
J. 1975. Water balance and gas exchange of plants under saline conditions. In
A. Poljakoff‑Mayber and J. Gale (ed.) Plants in Saline
Environments. Chapter 9. Springer‑Verlag, New York. Hawker,
J. S., and R. R. Walker. 1978. Effect of sodium chloride on expansion rates
and invertase activity of leaves. Aust. J. Plant Physiol. 5:73‑80. Huang,
C. Y., J. S. Boyer, and L. N. Vanderhoff. 1975a. Acetylene reduction and
metabolic activities of soybean having various leaf and nodule water
potentials. Plant Physiol. 56:222‑227. Huang,
C. Y., J. S. Boyer, and L. N. Vanderhoff. 1975b. Limitation of acetylene
reduction by photosynthesis in soybean having low water potentials. Plant
Physiol. 56:228‑232. Jensen,
C. R. 1975. Effects of salinity in the root medium: I. Yield, photosynthesis
and water relationships ,at moderate evaporative demands and various light
intensities. Acta. Agric. Sci. 25:3‑10. Lauter,
D. J., D. N. Munns, and K. L. Clarkin. 1981. Salt response of chickpea
as influenced by N supply. Agron. J. 73:961‑966. Lewis,
0. A., and J. S. Pate. 1973. The significance of transpirationally derived
nitrogen in protein synthesis in fruiting plants of pea (Pisum sativum
L.). J. Exp. Bot. 24:596‑606. Minchin,
F. R.,' and J. S. Pate. 1974. Diurnal functioning of the legume root
nodule.J. Exp. Bot. 25:295‑308. |
Pate,
J. S. 1976. Physiology of the reaction of nodulated legumes to the environment. In P. S. Nutman
(ed.) Symbiotic nitrogen fixation. J. Exp. Bo‑t. 24:596‑606. Sprent,
J. I. 1972. The effects of water stress in nitrogen fixing root nodules. New
Phytol. 71:451‑460. Sung,
F. J., and D. R. Krieg. 1979. Relative sensitivity of photosynthetic
assimilation and translocation of 14Carbon to water stress. Plant Physiol.
64:852‑856. Turner,
N. C., J. E. Begg, H. M. Rawson, S. D. English, and A. B. Hern. 1978.
Agronomic and physiological responses of soybean and sorghum crops to water
deficit : III. Components of leaf water potential, leaf conductance, 14co2
photosynthesis, and adaption to water deficits. Aust. J. Plant Physiol. 5:179‑194. Wilson,
J. R. 1970. Response to salinity in glycine: VI. Some effects of a range of
short‑term salt stresses on the growth, nodulation and nitrogen
fixation of Glycine wightii. Aust. J. Agric. Res. 21:571‑582. |
CHAPTER V THE EFFECT OF SALINITY ON NODULE FORMATION
Abstract A
split‑root growth system was employed to evaluate the effect of NaCl on
nodule formation by soybean. By
applying the salinity stress and rhizobial inoculum to only one‑half
the root system the effects of salinity on shoot growth were eliminated in
the nodulation process. Rhizobium
colonization of root surfaces was not affected by the salt treatments (0.0,
26.6, 53.2, and 79.9 mM NaCl). While
shoot dry weight remained unaffected by the treatments, total shoot N
declined from 1.26 g N/pot at 0.0 mM NaCl to 0.44 g N/pot at 79.9 mM
NaCl. The concentration of N in the
shoot declined from 3.751 N (control) to 1.261 N at 79.9 mM NaCl. Reduced shoot N was attributed to a sharp
decline in nodule number and dry weight.
Nodule number and weight were reduced by approximately 50% at 26.6 mM
NaCl, and by more than 90% at 53.2 and 79.9 mM NaCl. Nodule development, as evidenced by the
average weight of a nodule was not as greatly affected by salt as was nodule
number. Total nitrogenase activity (C2H2
reduction) declined in relation to nodule number and dry weight. Specific nitrogenase activity, however,
was less affected by salinity and was not depressed significantly until 79.9
mM NaCl. Isolates of R. japonicum
reisolated from nodules formed at 79.9 mM NaCl did not show increased
nodulation of roots under salt stress than did nodule isolates from normal
media. The early steps in nodule
initiation are, therefore, extremely sensitive |
to even low concentrations of NaCl. The sensitivity is not related to
rhizobial survival and is probably due to the salt sensitivity of root
infection sites. Introduction The
successful initiation of nodulation and nitrogen fixation by a genetically
compatible legume‑Rhizobium combination has two prerequisites:
colonization of root surfaces and attachment of rhizobia to roots followed by
infection of root hairs. Stress
factors such as soil salinity may have an adverse effect on these two
processes and limit nitrogen fixation by reducing nodule number. Rhizobium
growth and survival are generally more tolerant in vitro to high osmotic pressures
than their respective host legumes (Carr and Ballard, 1979; Lauter et al.,
1981). Tu (1981), however, observed
reduced colonization of soybean root surfaces by Rhizobium japonicum
when plants were grown in a salinized culture medium. Legumes
grown in saline environments have reduced yield potential and reduced numbers
and weight of root nodules (Tu, 1981; Lauter et a1., 1981; Balasubramanian
and Sinha, 1976; Lakshmi et al., 1974; Wilson, 1970). There were, however, serious limitations
in the above studies for evaluating the effects of salinity on the early
stages of nodule formation. With the
exception of the work of Lakshmi et al., (1974), inoculation of seedlings
with Rhizobium preceded the salinization of the rooting medium. It is likely that in these studies some
critical steps of rhizobial attachment and infection thread formation could
have |
occurred prior to the introduction of the
salt stress. Plant growth in the
study of Lakshmi et al., (1974) was so restricted that even non‑salinized
control plants of Medicago sativa had less than two nodules per
plant. All
the previous work concerning the effects of salinity on nodule initiation
suffer from the fact that plant yield potential was affected by the salinity
treatments. Reduced shoot growth
resulting from non‑soil related stress such as low light intensity also
reduces nodule number (Sprent, 1973).
This relationship between shoot yield potential and nodule initiation
requires therefore, that the stress imposed upon the site of nodule initiation
does not affect shoot growth. In
this paper, the sensitivity of rhizobial colonization of root surfaces and
nodule initiation to salinity were examined.
Plant growth potential as a confounding variable was eliminated by
employing a split‑root growth system described in Chapter III. This system permitted the application of
increasing salt concentrations to the site of root‑Rhizobium
interaction without affecting plant growth potential. In addition, isolates which formed nodules
under high salt conditions were tested to determine whether these were
variants (mutants) capable of producing nodules under salinity stress. |
Materials and Methods Plant
Culture Eight
soybean (Glycine max (L.) Merr. 'Davis') were planted in a
split‑root solution culture growth system (20 liter capacity on each
side) as described in Chapter III.
The nutrient solution consisted of: 0.5 mM P; 0.96 mM K; 1.56 mM S;
0.82 mM Mg; .75 mM Ca. Sources were:
K2HPO4; MgSO4 . 7H2O; CaSO4.
Micronutrients were added according to Broughton and Dilworth (1971). Nitrogen (3.57 mM) NH4NO3
was added to each container at planting.
Eighteen days after planting solutions were replaced with N‑free
nutrient solution. Salt was added to
one container of the split‑root assembly at concentrations of: 0.0,
26.6, 53.2, or 79.9 mM NaCl. Two
hours later the salinized side was inoculated with Rhizobium japonicum
strain USDA 110 at a viable cell density of 1.2 x 106 cells/ml
nutrient solution. Two days later 0.7
mM N as NH4NO3 was added to the uninoculated side to
maintain leaf area and vigorous plant growth during the early stages of
nodule formation. Solutions were
sampled for enumeration of Rhizobium and changed at 46 days from
planting. Samples were frozen. Re‑inoculation
of salinized half‑root systems
was at 9.9 x 104 cells/ml solution. The four treatments were
replicated three times in a completely randomized design. Water uptake was
monitered daily and solutions were replenished when the level fell by 2
liters. |
Harvest Shoots
and roots were cut. Roots were
immediately placed in 5.0% acetylene in 2.0 liter plastic containers and
incubated for 30 minutes. Ethylene production was determined by gas
chromatography. Nodules and roots
were subsampled for reisolation and a Rhizobium colonization study and
stored at 4 C. The remaining nodules
were removed from roots and nodules, roots, and shoots were dried at 65
C. Shoot N was determined by micro‑Kjeldahl. Rhizobium Culture Yeast
extract mannitol (Vincent, 1970) broth cultures were counted by the drop
plate method (Vincent, 1970) and then centrifuged at 12,100 x g and 4 C.
Cells were resuspended in water for inoculation. Enumeration of Rhizobium in Plant Nutrient
Solution Frozen
nutrient solution samples were thawed, 1 ml aliquots were diluted in
distilled H2O and filtered through a 0.4 m Nucleopore
polycarbonate membrane filter that had been stained with Irgalan Black. Filters were treated with USDA 110
fluorescent antibody (F. A.) prepared according to the methods of Schmidt et
al., (1968). Cell counts were made by
fluorescence microscopy. Colonization of Root Surfaces by Rhizobium Root
sections (2 cm) that had been subsampled and stored at 4 C were incubated for
30 minutes in an Eriochrome Black solution prepared |
according to the method of Goldman (1968)
with the exception that dimethyl‑sulfoxide (DMSO) was substituted for
N, N‑dimethylformamide. Roots
were rinsed in water until all excess dye was removed, then treated with
gelatin‑rhodamine isothiocyanate (Bohlool and Schmidt, 1968). Root sections were then incubated with
USDA 110 fluorescent antibody. Random
microscope fields (100) were examined for positive antibody reaction. A field with any fluorescent cells was
counted as being colonized. Isolation
and Testing of Rhizobium japonicum Strain USDA 110 from Nodules
Formed in Highly Salinized Rooting Medium Isolates
from surface sterilized nodules were made from the unsalinized controls and
from the few nodules formed when the nodule initiation process was exposed to
79.9 mM NaCl. Isolates were
identified as being strain USDA 110 by immunofluorescence microscopy (Schmidt
et al., 1968). Two isolates from
unsalinized controls and two from the 79.9 mM NaCl treatment were then
inoculated to half‑root systems with either no NaCl or 79.9 mM NaCl in
the rooting medium. The plant growth
system has been described earlier. Inoculation was at 20 days from
planting. Nutrient solutions were
changed prior to inoculation and NaCl at 79.9 mM was added to designated half‑root
systems 2 hours prior to inoculation.
Cell densities were 9 x 105/ml nutrient solution for both
strains. Nitrogen (0.35 mM) as NH4NO3
was added to the uninoculated side at 23 and 27 days from planting. |
Results There
was no treatment effect on the fluorescent antibody counts of Rhizobium
japonicum strain USDA 110 in the nitrogen‑free nutrient solution
(Table V‑1). Cell densities in
all treatments declined from 106 cells/ml at inoculation to 104
cells/ml at 46 days from planting.
Colonization of roots was similarly not affected by salinization of
the rooting medium. Roots exposed to
the most concentrated level of salt were heavily colonized. Total
shoot N and concentration of N in the shoot declined as the concentration of
NaCl applied to the half‑root system increased (Figure V‑1).
Shoot weight was not affected by the salinity treatments. Exposing
the infection process to NaCl caused a sharp reduction in nodule number,
nodule mass, and total nitrogenase activity (Figure V‑2). The decline was considerable even at the
lowest concentration of salt (26.2 mM NaCl).
Specific nitrogenase activity was more resistant to salt stress; a
significant reduction was not evident except at the highest level of salt
employed (79.9 mM NaCl). Nodule
development expressed as the average weight of a nodule was reduced as much
as 50% by exposure to NaCl (Figure V‑2 inset). The relative effect of salinity on nodule
development was not as great as the effect of salinity on nodule number. Exposure
of a half‑root system to increasing concentrations of NaCl reduced root
growth by that side (Figure V‑3).
Reduced growth on the salinized side was completely compensated for by
increased |
root proliferation on the non‑salinized
side. Water uptake by the two sides
followed a similar trend. Isolates
made from root‑nodules that developed in the 0.0 and 79.9 mM NaCl
treatments in the first experiment were not different in their ability to
nodulate the host with 79.9 mM NaCl in the rooting medium (Table V‑2). With no NaCl in the medium, the isolates
from 79.9 mM NaCl treatments show increased total and specific nitrogenase
activity. Discussion Nodule
initiation in the legume‑Rhizobium symbiosis involves a complex
interaction between host root, rhizobial strain and the environment. The processes of attachment and
proliferation of rhizobia on root surfaces followed by infection thread
formation in susceptible host root cells may be sensitive to the
environment. Since the host supply of
photosynthate required for shoot growth, nodule initiation, development and
nodule function is also sensitive to salinity (Jensen, 1975), evaluation of
symbiotic processes exposed to stress requires that the processes be
independently subjected to the stress.
By utilizing a split‑root growth system we were able to
independently subject the nodulation process of the soybean‑Rhizobium
japonicum symbiosis to salinity and eliminate shoot stress as a
variable in nodule initiation. Shoots
of plants with their roots split between normal and salinized mediums have approximately
the same shoot growth as plants with all their roots in a normal rooting
medium (Kirkham et al., 1969). |
The
reduction in nodule initiation caused by NaCl salinity was not related to the
survival of strain USDA 110 within the range of NaCl concentrations used in
this experiment (Table V‑1).
This agrees with results reported by Carr and Ballard (1979) who
reported that many Rhizobium could survive salt solutions approaching
the concentration of sea water. Tu
(1981) claimed that rhizobial colonization of soybean roots was a limiting
factor in nodule formation; however, the salt concentration employed (179 mM
NaCl) was excessive for the growth of soybean (Chapter IV). This study shows that nodule initiation is
adversely affected by NaCl concentrations which are not inhibitory to
rhizobial colonization. The
accumulation of N in the shoot was greatly reduced by imposing salinity
treatments to half‑root systems prior to the introduction of the
rhizobial inoculum (Figure V‑1).
Total shoot N was correlated with shoot N concentration rather than
shoot dry weight. Nitrogen
stress in the shoot was due to insufficiency in numbers and mass of nodules
caused by increasing salinity in the rooting medium during nodule
initiation. Our experiment shows that
the process of nodule initiation in soybean is extremely sensitive to
NaCl. A reduction in nodulation of
50% compared to maximum nodule number and mass occurred with only 26.6 mM
NaCl. Tu (1981) found that up to 102
MM NaCl in the rooting medium of soybean did not result in a decline in
nodule number. Inoculation of the
rooting medium with Rhizobium japonicum, however, was performed
prior to the institution of salinity treatments. Sensitive steps in the nodule initiation process may have
already been |
completed by the time roots were exposed to
salt. Hence, Tu's experiment examined
the effects of NaCl on nodule development. The
development of nodule tissue following infection is more resistant to
salinity (Figure V‑2 inset).
Nodule size at 79.9 MM NaCl was 50% of the no‑salt control while
nodule number was less than 10% of the control. It has been shown that reduced numbers of nodules on soybean
roots is compensated for by an increase in the average weight of a nodule so
that total nodule weight remains approximately constant as the number of
nodules declines (Singleton and Stockinger, 1982). Apparently,
NaCl stress limits this compensatory response so nodule weight declines with
nodule number. Total
nitrogenase activity was a function of nodule number and mass (Figure V‑2). The nitrogenase system was more tolerant
of exposure to NaCl. Nodule specific
activity was not affected except at the highest level of salinity (Figure V‑2). This is consistent with the results of
Chapter IV which showed that nodule function was relatively resistant to salt
stress. Data
for root growth and water uptake in the split‑root system explain how
plants with one‑half the root system exposed to salt can have shoot
growth similar to the non‑salinized control (Figure V‑3). Reduced root growth and water uptake by
salinized half‑root systems were compensated by increased root growth
and water uptake by the non‑salinized side. Shoot osmotic potential of split‑root plants is
relatively unaffected when even 120 mM NaCl is applied to only one‑half
the root system of soybean (Chapter III). |
Some
workers have tested a number of rhizobial strains to determine if strain
selection could increase nitrogen fixation in saline environments (Lauter et
a1., 1981; Bhardway, 1975). Isolates
were made from nodules formed in the 79.9 mM NaCl treatment of the first
experiment to determine whether these isolates were variants of the original
culture and capable of increased nodule formation under salinity stress. Although the isolates from the salinity
treatment formed more nodules in 79.9 mM NaCl (Table V‑2) than isolates
made from the non‑salinized treatment, the difference was small and
nitrogenase activity was not appreciably enhanced. Isolates from the non‑salinized control produced more
nodules and greater nodule weight in the 0.0 mM NaCl treatment of this
experiment yet had substantially reduced acetylene reduction activity than
isolates from 79.9 mM NaCl. The
isolates made from the first experiment have variable symbiotic properties; this
did not include, however, an increased ability to form nodules in saline
culture medium. In
conclusion, the processes involved in nodule formation are extremely
sensitive to NaCl. Even low
concentrations (26.6 MM NaCl) cause significant reductions in nodule number
and weight. As a result, shoot
nitrogen yield was limited by insufficient nodule tissue to meet the N
requirements of unstressed shoots.
Nodule development as evidenced by the average weight of a nodule and
nodule function (specific nitrogenase activity) were relatively less
sensitive to salt than nodule initiation.
The ability of Rhizobium japonicum strain USDA 110 to
survive and colonize root surfaces was not affected by salinity. The use of isolates made from the high
salt treatment as inoculum in a |
saline environment indicates that
nodulation failure was due primarily to the effects of salinity on plant root
infection sites. |
TABLE V-1. |
-- The effect of NaCl in the rooting medium
on
strain USDA 110 and colonization of |
survival of Rhizobium japonicum soybean roots. |
NaCl (mM) |
Log
no. cells (ml) |
Fields
colonized (percent) |
0.0 |
4.11 |
92 |
26.6 |
3.96 |
76 |
53.2 |
4.36 |
82 |
79.9 |
4.02 |
91 |
|
LSD .05 N. S. |
|
|
|
|
|
|
|
|
TABLE V-2. -- Relative salt |
tolerance
of isolates from high nodules
in saline solutions. |
salt
treatments to form |
|
Isolate Half-root from: exposed to: |
Nodule number |
Nodule dry weight |
Nitrogenase activity 1 2 |
mM NaCl |
number pot-1 |
g pot-1 |
|
0.0 0.0 |
1229 |
2.97 |
176 65 |
79.9 0.0 |
974 |
2.55 |
271 108 |
0.0 79.9 |
47 |
0.25 |
6 57 |
79.9 79.9 |
10 |
0.18 |
2 59 |
LSD .05 |
411 |
0.76 |
34 |
1Total
nitrogenase activity, 2Specific
nitrogenase activity, |
Mol
C2H4 pot-1 hr-1. Mol
C2H4 (g nodule) |
-1
hr–1. |
|
|
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