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Applied and Environmental Microbiology, December 1999, p. 5604-5606, Vol. 65, No. 12
Laboratory of Soil Microbiology, Department
of Ecology, National Grassland Research Institute, Nishi-nasuno,
Tochigi, 329-2793,1 and University Farm,
School of Agricultural Sciences, Nagoya University, Aichi,
470-0151,2 Japan
Received 21 June 1999/Accepted 6 September 1999
The amount of polyphosphate in the intraradical and extraradical
hyphae of Gigaspora margarita was estimated from successive extractions with trichloroacetic acid (TCA), EDTA, and
phenol-chloroform (PC). In the intraradical hyphae, most of the
polyphosphate was present in TCA- and EDTA-soluble (short-chain and
long-chain) fractions, whereas most of the polyphosphate in the
extraradical hyphae was present in EDTA- and PC-soluble (long-chain and
granular) fractions.
The enhanced growth of plants
colonized by arbuscular mycorrhizal (AM) fungi has been recognized to
result from the supply of absorbed mineral nutrients, particularly
phosphorus, by extraradical hyphae (22). It is now widely
accepted that phosphate present in the soil is taken up into the
extraradical hyphae by a phosphate transporter (12),
subsequently condensed into polyphosphate (poly-P), and translocated by
protoplasmic streaming into the intraradical hyphae (6-8).
Thus, poly-P is considered to be a key phosphorus compound in the
translocation processes. However, since the pioneering work in the
1980s, no quantification of poly-P in the hyphae of AM fungi has been
performed. Because of the obligately symbiotic nature of AM fungi, the
preparation of hyphae, particularly intraradical hyphae, is a major
obstacle in studying their poly-P concentration. However, by a
combination of enzyme digestion and Percoll centrifugation, a method
which enables the investigation of the enzymes and the metabolic
activities of intraradical hyphae in vitro (9, 10, 13, 23)
was developed (20). In this study, therefore, we quantified
poly-P in the hyphae of an AM fungus, Gigaspora margarita,
and we employed a successive extraction procedure which does not
hydrolyze long-chained poly-P to shorter chains (5).
Onion (Allium cepa L.) plants were inoculated with G. margarita MAFF 520054 and grown for 6 and 9 weeks after
transplanting, as described previously (23). The
intraradical hyphae were collected by a combination of enzyme digestion
and Percoll centrifugation (20, 23). Extraradical hyphae
were collected by the wet-sieving and decanting method (1).
The fresh weight of hyphae was recorded after careful removal of excess
moisture with small pieces of filter paper. Hyphal length was measured
by the grid intersection method (23). Specific hyphal length
was calculated from these measurements.
Different poly-P fractions in the hyphae were successively extracted
with trichloroacetic acid (TCA), EDTA, and phenol-chloroform (PC),
based upon the method of Clark et al. (5), except that the
samples were first ground in ice-cold 2% aqueous TCA with zirconia
beads by using a Bead-beater (Biospec Products, Bartlesville, Okla.).
The extracted poly-P in aqueous solution was precipitated by adding
Tris-HCl (1 M, pH 7.6) to a final concentration of 0.2 M and 2 volumes
of acetone. The mixture was frozen at Gel electrophoresis of RNase-treated samples was performed with Tris
borate buffer and 10% polyacrylamide gels (1 by 120 by 150 mm). Ten
microliters of the extract was loaded with glycerol, xylene cyanol, and
bromophenol blue, and electrophoresis was performed at 120 V for about
75 min or until the sample dye, xylene cyanol, had migrated 2.5 cm and
the reference marker dye, bromophenol blue, had migrated 5 cm. Poly-P
on the gel was stained pinkish purple according to the method of Pepin
and Wood (18).
Mycorrhizal colonization was 64% at 6 weeks and 73% at 9 weeks after
transplanting. The extraradical hyphal biomass was almost half the
intraradical hyphal biomass, because spore biomass was not included
(Table 1). Specific hyphal length was
within a range of 5.2 to 5.9 km g
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Copyright © 1999, American Society for Microbiology. All rights reserved.
Polyphosphates in Intraradical and Extraradical
Hyphae of an Arbuscular Mycorrhizal Fungus, Gigaspora
margarita

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ABSTRACT
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80°C for more than 15 min,
melted, and then centrifuged for 10 min. The residue was air dried,
dissolved with water, and kept at
20°C until analysis. The poly-P
content in the extracts was determined by measuring the metachromatic
reaction of toluidine blue at 630 nm (11). The extracts were
first treated with RNase A at 37°C for 45 min, and then the assay was
performed by adding 10 µl of the poly-P sample to tubes containing
0.75 ml each of acetic acid (0.2 M) and toluidine blue (30 mg
liter
1). The amount of poly-P was determined within 15 min of color development by comparison with a standard curve produced
by using 1 to 5 µg of type 35 poly-P for the short-chain and type 65 for the long-chain poly-P fractions. Synthetic poly-P glasses of types 65, 35, and 15 were obtained from Sigma Chemical Co. Total P
concentrations in hyphae were determined by digestion of the hyphae
(ca. 20 to 40 mg [fresh weight]) in concentrated
H2SO4 by using H2O2 as
an oxidant for 1 h at approximately 200°C. Inorganic phosphate
concentrations in the digests were colorimetrically determined
(25).
1 (fresh weight). The
differences in specific hyphal length between intraradical and
extraradical hyphae or between sampling times were not large.
TABLE 1.
Hyphal biomass, length, and poly-P contents in
G. margarita
Poly-P was successively extracted into TCA-, EDTA-, and PC-soluble
fractions. The recovery test, in which standard poly-P was added in
each extraction step, revealed a >95% recovery rate. The enzyme
digestion process of hyphae did not affect poly-P content or
composition in any fraction. Poly-P in mycorrhizal hyphae showed a
smear band which stained pinkish purple with toluidine blue (
-metachromasy), indicating a range of poly-P molecules with different chain lengths in each extract (Fig.
1). Although the bands of poly-P in TCA-,
EDTA-, and PC-soluble fractions overlapped each other in relative
mobility, the poly-P band migrated with increasing speed in this order.
Thus, we can assign short-chain, long-chain, and long-chain granular
poly-P approximately to TCA-, EDTA-, and PC-soluble fractions,
respectively, according to the system of Clark et al. (5).
The band from the TCA-soluble fraction showed relatively faint staining
compared to the others. This may have been due to the lower
metachromasy of short-chain poly-P than that of long-chain poly-P
(15).
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The quantification of poly-P in each fraction by the toluidine blue assay clearly demonstrated the differences in the composition of poly-P fractions between intraradical and extraradical hyphae. It was first observed that the proportion of short-chain poly-P to total poly-P was higher in the intraradical hyphae and that the proportion of long-chain poly-P was higher in the extraradical hyphae (Table 1). This suggests that poly-P synthesis to form long chains occurred in extraradical hyphae, possibly because long-chain granular molecules are more efficient in transporting phosphorus into the intraradical part of the fungi.
Poly-P was often determined as acid-hydrolyzable phosphate in the extracts (5). However, almost half of poly-P in EDTA- and PC-soluble fractions was not easily hydrolyzed with 1 N HCl, while poly-P in the TCA-soluble fraction was almost completely hydrolyzed (data not shown). Poly-P molecules in the hyphae of AM fungi have been considered to be mainly present in a granular form in vacuoles, based upon transmission electron microscopy (7, 19). However, it was reported that poly-P granules found in ectomycorrhizal fungal hyphae prepared for transmission electron microscopy were artifacts of the fixation processes (17), although this has been disputed recently (2). The present result suggests that, at least from the viewpoint of hydrolyzability, granular poly-P is present in the hyphae of AM fungi.
Poly-P concentrations in the hyphae of G. margarita ranged from 5.4 to 17.3% of total P content and were within the range reported earlier for the hyphae of mycorrhizal fungi, including Glomus mosse (4), some ericoid mycorrhizal fungi in culture (24), and some ectomycorrhizal fungi in culture (16).
Two possible mechanisms may account for the higher proportion of short-chain poly-P in intraradical hyphae. Firstly, the long-chain poly-P may be partly hydrolyzed into shorter chains with endopolyphosphatase (3, 14). Depolymerized short-chain poly-P may be further hydrolyzed with exopolyphosphatase to liberate inorganic phosphate. Secondly, long-chain poly-P may act as a phosphoryl donor for poly-P glucokinase so that only short-chain poly-P remains. Poly-P glucokinase of the anaerobic bacterium Propionibacterium shermanii uses long-chain poly-P preferentially, followed by the accumulation of short-chain poly-P (18). Poly-P glucokinase activity was previously found in the crude extract of mycorrhizal roots (4), and glucose is used by intraradical hyphae (21, 23). Glucose-6-phosphate produced from poly-P and glucose can serve as an intermediate both for liberation of inorganic phosphate and for glucose assimilation (9). Both mechanisms may operate in the hyphae of G. margarita.
In the present study, we have, for the first time, quantified the poly-P contents in both intraradical and extraradical hyphae of the AM fungus G. margarita, and we have also found that the poly-P chain was shorter in intraradical hyphae than in extraradical hyphae. The latter observation may be related to phosphate metabolism in arbuscular mycorrhizas. Investigation of the expression and regulation of the enzymes involved in poly-P metabolism may shed light on the storage, transport, and metabolism of phosphate in AM systems.
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ACKNOWLEDGMENTS |
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M.Z.S. is grateful to the Japan Science and Technology Corporation for providing a postdoctoral fellowship. This study was also partly supported by a grant-in-aid (Bio-media program) from the Ministry of Agriculture, Forestry and Fisheries, Japan.
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FOOTNOTES |
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* Corresponding author. Mailing address: Department of Ecology, National Grassland Research Institute, Nishi-nasuno, Tochigi, 329-2793, Japan. Phone: 81-287-36-0111. Fax: 81-287-36-6629. E-mail: msaito{at}ngri.affrc.go.jp.
Present address: Faculty of Bioresources, Mie University, Tsu, Mie,
514-8507, Japan.
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