First published online November 14, 2002; 10.1104/pp.007088
Plant Physiol, December 2002, Vol. 130, pp. 1951-1957
Humic Acids Isolated from Earthworm Compost Enhance Root
Elongation, Lateral Root Emergence, and Plasma Membrane
H+-ATPase Activity in Maize Roots1
Luciano Pasqualoto
Canellas,
Fabio Lopes
Olivares,
Anna L.
Okorokova-Façanha, and
Arnoldo Rocha
Façanha*
Centro de Ciências Tecnologias Agropecuárias,
Laboratório de Solos (L.P.C.), Centro de Biociências
Biotecnologia, Laboratório de Biologia Celular e Tecidual
(F.L.O., A.R.F.), and Laboratório de Fisiologia
Bioquímica de Microrganismos (A.L.O.-F.), Universidade Estadual
do Norte Fluminense, Avenida Alberto Lamego, 2000, CEP
28015-620, Campos dos Goytacazes, Rio de Janeiro, Brazil
 |
ABSTRACT |
Earthworms (Eisenia foetida) produce humic
substances that can influence plant growth by mechanisms that are not
yet clear. In this work, we investigated the effects of humic acids
(HAs) isolated from cattle manure earthworm compost on the earliest stages of lateral root development and on the plasma membrane H+-ATPase activity. These HAs enhance the root growth of
maize (Zea mays) seedlings in conjunction with a marked
proliferation of sites of lateral root emergence. They also stimulate
the plasma membrane H+-ATPase activity, apparently
associated with an ability to promote expression of this enzyme. In
addition, structural analysis reveals the presence of exchangeable
auxin groups in the macrostructure of the earthworm compost HA. These
results may shed light on the hormonal activity that has been
postulated for these humic substances.
 |
INTRODUCTION |
Earthworm (Eisenia
foetida) compost strongly affects soil fertility by increasing
availability of nutrients, improving soil structure and water-holding
capacity (Landgraf et al., 1999 ). It has been suggested
that earthworms can increase the velocity of decomposition of organic
residues (Vinceslas-Akpa and Loquet, 1997 ) and also
produce several bioactive humic substances (e.g. Cacco and
Dell'Agnola, 1984 ; Nardi et al., 1994 ;
Masciandaro et al., 1999 ). These substances are endowed
with hormone-like activity that improves plant nutrition and growth
(Vaughan and Malcolm, 1985 ; Chen and Aviad,
1990 ). Humic acids (HAs) comprise one of the major fractions of
humic substances. They are characterized by dark-colored,
alkali-soluble, acid-insoluble, and high-Mr
humified organic matter (Schnitzer, 1991 ). In fact, it
has been known since the early 1900s that HA can display auxin-like
activities (Bottomley, 1917 ; Dell'Agnola and
Nardi, 1987 ; Muscolo et al., 1999 ). In turn, it
has been proposed that one of the mechanisms by which auxins can
stimulate plant growth is by inducing an increase in the amount of
plasma membrane (PM) H+-ATPase, which acidifies
the apoplast and thereby loosens the cell wall, allowing cell
elongation (Hager et al., 1991 ; Frias et al.,
1996 ). Activation of the H+-ATPase can
also improve plant nutrition by enhancing the electrochemical proton
gradient that drives ion transport across the cell membrane via
secondary transport systems (for review, see Sze, 1985 ;
Morsomme and Boutry, 2000 ).
Previous reports have demonstrated that some
low-Mr humic substances (essentially fulvic
acids) can stimulate the H+-ATPase of PM vesicles
isolated from roots of several plants. This effect was attributed to a
dissipation of the electrical potential and an increase in membrane
permeability (Nardi et al., 1991 ; Varanini et
al., 1993 ) or to enzyme modulation by an undefined posttranslational mechanism (Pinton et al.,
1999 ; Nardi et al., 2000 ). Although a
large body of evidence indicates that HA can also directly affect
enzymatic activities in several metabolic pathways (Vaughan and
Malcolm, 1985 ), relatively little attention has been paid to
the biochemical effects of the HA fraction on plant metabolism and development.
In the present work, the PM H+-ATPase activity
and the induction of mitotic sites associated with the earliest stages
of lateral root development have been investigated as a basis for
analysis of a possible hormonal effect of earthworm compost HA on
lateral root proliferation.
 |
RESULTS |
HA Structural Features
According to elemental composition analysis of HA, the values for
total carbon, oxygen, nitrogen, hydrogen, and ash were 48.5%, 42.2%,
3.2%, 5.6%, and 0.51% (on a dry weight basis), respectively. The
carboxyl and phenolic groups account for 496 and 170 centimol charge kg 1 of the total acidity (666 Cmolc kg 1).
13C NMR analysis (Fig.
1) revealed weak absorption in the
hybridization state of the atom C (sp3) C atom region
( C-0-40) because of CH2
and CH3 groups in long alkyl chains. Around
C-15, the spectra showed signals
characteristic of terminal methyl groups and between
C 20 and 30 due to the presence of
(CH2)n groups. Curiously, a
very large peak was observed in the region
C-44 to -57, which is not typical of
13C NMR spectra from pedogenic HA and, thus,
revealed the low humification stage of HAs isolated from earthworm
because of an increase in C bonded to mono- and di-O. The signals at
C-44, -53, and -55 can be attributed to
sp3 carbon atoms, including C bound to N in amino
acids; at C-57, they are because of
OCH3 groups bound to the hybridization
state of the atom C (orbital sp2 bound). The signal around
C-65 can be attributed to carbinolic C of
primary alcohols and polysaccharides. The signal at
C-70.6 indicates sp3 C
atoms bound to N. The signals present around
C-100 suggest sp3 carbon
atoms bound to two atoms of oxygen (anomeric carbon), as found in
carbohydrates. The peak centered at C-130 is
because of aromatic carbons. The high field peaks at
C-150 to -160 are because of carbon bonded to
phenolic OH groups. The C-160 to -190 region
shows signals because of the presence of differently substituted
carbonyl-C atoms. Quantitatively, the spectra revealed 8.7% carboxyl,
7.4% phenolic, 41.9% aromatic, 31.5% peptide and carbohydrate, and
17.5% other aliphatic carbons. In comparison with typical values
reported for an average soil HA (Schnitzer, 1991 ), the
earthworm compost HA had a low content of C in alkyl chains and
carboxylic functions and a high content of aromatic and mono- or di-O-C
alkyl and N-C atoms. However, this HA-earthworm compost fraction is
endowed with the characteristic structural network described for most
HAs isolated from different sources of organic matter (e.g.
Clapp and Hayes, 1999 ). This is consistent with the
notion that the same pathways for the formation of HA may operate in
all environments resulting in a substance with defined identity
(Stevenson, 1994 ).

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Figure 1.
13C NMR spectrum from HA
extracted from earthworm compost. The spectrum is divided into regions
corresponding to specific chemical classes: aliphatic C, 0 to
50; N-alkyl and methoxyl C, 50 to 60;
aliphatic C-O (carbohydrates), aromatic C, 110 to 145;
phenolic C, 150 to 165; and carboxyl, esters, and
amides C, 165 to 190.
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Detection of 3-Indole Acetic Acid (IAA) in Earthworm Compost
HA
The presence of IAA in the HA structure was identified by gas
chromatography (GC)-mass spectrometry (MS; Fig.
2). To reduce the polarity, standard
methylated IAA and methylated HA were produced, and revealed similar
retention times of 7.48 to 7.51 min and mass spectra with the molecular
ion [M+]· at 189 m/z with the base peak at 130 m/z. These data are compatible with the presence
of the ion formed by fragmentation by elimination of the
CO2Me radical, confirming the presence of IAA
in the HA structure. This is in agreement with recent reports on IAA
detection by immunoassay in humic substances extracted from different
sources (Muscolo et al., 1998 ; Pizzeghello et
al., 2001 ). However, it is worth noting that in our case, a
low-Mr molecule is detected here after
dialysis of the HA fraction with a membrane having a molecular
mass cutoff of 14 kD. These exchangeable IAA molecules have to
be linked to the HA macrostructure by means of hydrophobic interactions
in clusters intrinsic to the supramolecular structure of HA (e.g.
Schulten and Schnitzer, 1995 ; Piccolo,
2002 ).

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Figure 2.
Gas chromatogram of the standard methylated IAA
(A) with the respective mass spectra (B), and the gas chromatogram of
the methylated HA isolated from earthworm compost (C) with the
respective mass spectra (D).
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Root Length and Surface Area
Total radicular length for each seedling was
calculated as the sum of the lengths of all radicular nodal segments,
using automatic linearization with SIARCS software (Empresa Brasileira
de Pesquisa Agropecuária-Centro Nacional de Pesquisa e
Desenvolvimento da Instrumentação Agropecuária,
São Carlos-SP, Brazil; Cruvinel et al.,
1996 ). In maize (Zea mays) seedlings treated for
7 d with different HA concentrations, both elongation and
proliferation of secondary roots were stimulated, resulting in enhanced
root surface area (light columns in Fig.
3), and the increase in total radicular
length (gray columns in Fig. 3).

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Figure 3.
Effect of different HA concentrations on roots
length (light columns) and radicular superficial area (gray columns) of
maize seedlings analyzed by SIARCS software. Total root length was
calculated as a sum of the length of primary and lateral roots. Data
are expressed as percentage (±SE) of control (plants grown
without HA) and represent normalized means from six independent
experiments performed with maize seedlings (25 plants per treatment in
each case).
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HA-Induced Sites of Lateral Root Emergence
The elongation differentiation zone of the root includes small,
densely meristematic cells that are in continuous metabolic activity
and are more susceptible to lateral root formation. We have measured
the proliferation of the mitotic sites in this zone of roots treated or
not with 40 mg L 1 earthworm HA (Fig.
4). Despite the tendency for HA to induce more sites of lateral root emergence, no statistical significance was
obtained until 3 d after maize root exposure to HA in the growth
medium, when HA treatment clearly stimulated the number of sites of
lateral root emergence to a level ranging from 7 to 12 times the
control values. This marked effect on the root morphology was mainly
observed at the elongation/differentiation zone (data not shown). The
hyperinduction of sites of lateral root emergence after HA treatment
can be observed in Figure 4B. Figure 4C shows a single mitotic site
before lateral root emergence highlighted in an untreated root.

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Figure 4.
Effect of HA on the root growth pattern evaluated
by quantification of lateral root mitotic sites. A, Control roots
showing some mitotic sites. Bar = 1 mm. B, Hyperinduction of
mitotic sites in a maize root after HA incubation (40 mg
L 1). Bar = 1 mm. C, Single mitotic site
before lateral root emergence. Bar = 200 µm. D, Counting of root
mitotic sites. Light columns represent control roots and gray columns
represent HA-treated roots.
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HA Effect on H+-ATPase Activity
PM vesicles isolated from maize roots treated for 7 d with 40 mg L 1 HA exhibited a clear stimulation of the
vanadate-sensitive ATPase activity (Fig.
5A) as well as of the formation of an
ATP-dependent proton gradient, measured as a quenching of ACMA
fluorescence (Fig. 5B). The initial rate of gradient formation and ATP
hydrolysis were enhanced by 2- to 3-fold in response to treatment with
earthworm compost HA. Interestingly, addition of HA to the reaction
medium in vitro inhibited both the ATPase activity as well as the
proton gradient formation in PM-enriched vesicles isolated from roots grown under control conditions (dashed lines in Fig. 5). Western-blot analysis using antibodies raised against
H+-ATPase PMA2 isoform from Nicotiana
plumbaginifolia Viv. (Morsomme et al., 1996 )
revealed that the amount of immunoreactive protein at the PMA locus
(approximately 96 kD) also increased almost 3-fold in the membrane
vesicles isolated from maize roots treated with HA (Fig.
6). It is worth noting that no change in
total protein content was found because the yield from 20 g fresh
weight was approximately 3 mg of protein for both control and treated
preparations (data not shown). Taken together, these results suggest
that earthworm compost HA treatment can affect the
H+-ATPase activity indirectly by promoting an
increase in the concentration of H+-ATPase in
membrane vesicles.

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Figure 5.
Effects of HA on PM
H+-ATPase activity and proton pumping.
Vanadate-sensitive ATP hydrolysis (A) and proton transport (B) were
measured in PM vesicles isolated from maize roots treated ( ) or not
(µ) with 40 mg L 1 HA for 7 d. Dashed
line shows the ATPase activity from control vesicles recorded in the
presence of 40 mg L 1 HA in vitro. In A, the
reaction medium contained 50 mM HEPES-KOH (pH 6.5), 3 mM MgSO4, 100 mM KCl, and
1 mM ATP. In B, the same medium was used, except for the
buffer concentration (10 mM HEPES-KOH) and the presence of
2.5 µM 9-amino-6-chloro-2-methoxyacridine (ACMA), a
fluorescent pH probe. Arrows indicate the addition of 1 mM
ATP to start the reaction and of 3 µM carbonyl cyanide
p-(trifluoromethoxy)phenylhydrazone, a protonophore,
which dissipates the proton gradient. A and B are representative
experiments of at least four independent preparations of PM from maize
roots. Differences are significant at P < 0.001 (Student's t test).
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Figure 6.
Western blot of PMs isolated from maize roots
treated (+) or not ( ) with 40 mg L 1 HA for
7 d. Fifty micrograms of vesicle protein was separated by 7.5%
(w/v) SDS-PAGE and transferred to a nitrocellulose membrane.
Immunoblots were probed with antibodies against PM
H+-ATPase and developed with
peroxidase-conjugated secondary antibody. The immunoresponse was
quantified densitometrically (upper) as described in "Materials and
Methods."
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DISCUSSION |
Although the stimulatory effect of earthworm composts on plant
development is attributed historically to their nutrient content, specific effects of the HA fraction from these composts on plant metabolism is usually unrelated to its ash content (Vaughan and Malcolm, 1985 , and refs. therein). In this study, we explored the structure and function of the HA fraction isolated from an earthworm compost. This fraction induces the proliferation of sites of
lateral root emergence in maize roots (Fig. 3). These differentiation
sites are precursors of lateral roots and are formed by meristematic
cells that have a PM enriched with H+-ATPases
(Jahn et al., 1998 ). Therefore, it is possible that the enhancement of the PM H+-ATPase content (Fig. 6)
might be associated with the induction of mitotic sites by HA (Fig. 4).
Because the total protein content of the PM-enriched fraction (relative
to the fresh weight) was not significantly modified by HA treatment, it
is likely that HA can enhance the expression of the PM
H+-ATPase gene. Furthermore, addition of HA to
the reaction medium promotes inhibition of both ATP hydrolysis and
H+ transport (dashed lines in Fig. 5), suggesting
that if HA could gain access to the cytoplasm, this enzyme probably
would be inhibited. This may mean that the stimulatory effect of HA can
be triggered by an association of these
high-Mr molecules with specific receptors on the cell surface. Another possibility would be a release of small
bioactive molecules from the HA macrostructure; these small molecules
might interact with receptors on the PM or even inside the cell.
Using GC-MS, we have detected the presence of auxin groups in HA
extracted from earthworm compost. Although HA are considered macromolecules consisting mainly of long alkyl chains containing aromatic groups, the occurrence of hydrophobic clusters in their supramolecular structural conformation also has been described (Schulten and Schnitzer, 1995 ; Clapp and Hayes,
1999 ). The presence of intrinsic small bioactive molecules such
as IAA clustered within the HA supramolecular arrangement might be
related to both the induction of root mitotic sites and
H+-ATPase activation. Previously, IAA was also
detected by immunoassay in humic substances extracted from other
sources (Muscolo et al., 1998 ). However, the separation
of IAA from HA by GC means that this small molecule can be released by
polarity changes in the HA microenvironment. In field conditions, such
changes of polarity can occur by interactions between soluble HA and
root exudates (Nardi et al., 2000 ; Cozzolino et
al., 2001 ).
The phytohormone auxin is a key regulator of lateral root development
(Blakely et al., 1982 ; Laskowski et al.,
1995 ). It has been demonstrated that root basipetal and leaf
acropetal auxin transport activities are required during the initiation
and emergence phases, respectively, of lateral root development
(Casimiro et al., 2001 ; Bhalerao et al.,
2002 ). On the other hand, the acid growth theory postulates
that the acidification of the apoplast caused by activation of the PM
H+-ATPase can induce cellular expansion (for
review, see Rayle and Cleland, 1992 ). This phenomenon
has been associated with an auxin-induced activation of the P-type
H+-ATPase by an as-yet-unclear mechanism
(Morsomme and Boutry, 2000 ). It has been reported
that auxin can induce de novo synthesis of the PM
H+-ATPase in plant tissues (Hager
et al., 1991 ), correlated with an induction of
H+-ATPase mRNA of the major isoform (MHA2)
expressed in maize (Frias et al., 1996 ). Although this
effect was studied in coleoptiles, it has been shown that growth
depends on extracellular pH in maize roots also (Peters and
Felle, 1999 , and refs. therein). Moreover, in maize
protoplasts, a receptor that binds auxin from outside the PM was
identified through which the H+-ATPase could be
activated (Ruck et al., 1993 ).
Taking our data together with those from the literature, it is tempting
to speculate that, like endogenous auxins (Ruck et al.,
1993 ; Goldsmith, 1993 ; Abel et al.,
1994 ), HA-IAA groups may access plant receptors and trigger a
cascade that activates transcription factors and protein synthesis and
at the same time alters the activity of particular enzymes like the PM
H+-ATPase. The ultimate physiological response
would involve a higher level of cell activity and tissue
differentiation resulting in root growth. However, despite the
observation that auxins and earthworm compost HA share such functional
similarities, we cannot rule out the possibility that other bioactive
groups that may be present in the complex HA structure can also
contribute to induction of lateral root development and
H+-ATPase activation.
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MATERIALS AND METHODS |
Materials
A mixture of plant residues from Panicum maximun
Jacq. and cattle manure 5:1 (v/v) was used for earthworm
(Eisenia foetida) compost preparation. The organic
residues were mixed and earthworms were added at a ratio of 5 kg worms
per m3 of organic residue. A bed of worms and organic
residues was first prepared in a container and additional layers of
organic residue were subsequently distributed over the pile at times
depending on the temperature until the pile reached 50 cm. At the end
of transformation process (3 months after distribution of the last organic residues), the worms were removed by placing a pile of fresh
organic residue (plant + cattle manure) in a corner of the container.
The organic matter composition of the earthworm compost was: pH 6.2, 134 g kg 1 total organic carbon, 13.3 g
kg 1 total nitrogen, 10:1 C:N ratio, and 16.4 g HA
carbon kg 1.
Extraction of HAs
The humic substances were extracted as described by the
International Humic Substance Society (Schnitzer and Skinner,
1982 ). In brief, 10 volumes of 0.5 mol L 1 NaOH
was mixed with 1 volume of earthworm compost, under N2
atmosphere. After 12 h, the suspension was centrifuged at
5,000g and acidified to pH 1.5 using 6 mol
L 1 HCl. The solubilization and precipitation of HA were
repeated three times and the last pellet was mixed with 10 volumes of a diluted mixture of HF-HCl solution (5 mL L 1
HCl [12 M] + 5 mL L 1 HF [48%, v/v]).
After centrifugation (5,000g) for 15 min, the sample was
repeatedly washed with water until a negative test against
AgNO3 was obtained, followed by dialyzing against deionized water using a 12- to 14-kD cutoff membrane (Thomas Scientific, Swedesboro, NJ). The dialyzate was lyophilized and characterized chemically. Then, the HA powder was solubilized with 50 to 100 mL of
0.05 mol L 1 NaOH and the pH was adjusted to 5.5 with 0.1 M HCl.
HA Structural Features
The elemental composition was determined using a CHN
Perkin-Elmer autoanalyzer (Perkin-Elmer, Foster City, CA). Total
acidity [Ba(OH)2 method] and carboxylic acidity
[Ca(Oac)2 method] were determined according to
Schnitzer and Gupta (1965) followed by a potentiometric
titration. The phenolic acidity was obtained by the difference. The
13C NMR spectra were run in solution using an AC-200
spectrometer (50.30 MHz for 13C, Bruker Instruments,
Billerica, MA), and 150 mg of HA dissolved in 1 mL of NaOH (0.5 mol L 1) containing 9:1 (v/v) water:D2O. The
analysis was performed using the INVGATE sequence (inverse decoupling),
with a pulse of 90o, acquisition time of 0.2 s, 16 K of size, and about 200,000 transients for each sample. The
chemical shift ( 13C) was expressed on a scale relative
to tetramethylsilane ( 13C = 0).
Detection of IAA in HA
Methylated HA was prepared by treatment with acetyl chloride in
methanol suspension HA (30 mg dry weight) and methanol (7 mL) were
mixed in a 100-mL flask in an ice bath. One milliliter of acetyl
chloride was slowly added to the resulting suspension. The flask was
shaken for 4 h at 25°C. This procedure was repeated three times,
except that the last reaction was carried out overnight. The suspension
was centrifuged for 30 min at 2,680g. The clear brown
solution was dried in a rotary evaporator and dissolved in 10 mL of
methanol. The methylated HA solution was analyzed by GC-MS (QP5050A
equipped with DB1 column, 30-m × 0.25-mm i.d., Shimadzu,
Columbia, MD). The oven temperature was programmed to increase
from 100°C to 280°C at a rate of 15°C min 1. Helium
at a flow rate of 1 mL min 1 was used as carrier gas. The
ionizing voltage of the MS was 70 eV. Pure IAA from Sigma (St.
Louis) was methylated as described above for HA and subjected to
GC-MS. IAA detection in the chromatogram of methylated HA was
accomplished by comparing retention time and mass spectra with those of
the purified methylated IAA sample.
Plant Growth and HA Treatment
Maize (Zea mays var. BR 106) seeds provided by
Empresa Brasileira de Pesquisa Agropecuária (Seropedica,
Brazil) were surface sterilized by soaking in 0.5% (w/v) NaClO
for 30 min, followed by rinsing and then soaking in water for 6 h.
Afterward, the seeds were sown on wet filter paper and germinated in
the dark at 28°C. Four-day-old maize seedlings with roots
approximately 0.5 cm long were transferred into a solution containing 2 mM CaCl2 and either 0, 20, 40, or 80 mg dry
weight L 1 HA extracted from earthworm compost. Previous
experiments showed that seedlings treated for 7 d with 40 mg dry
weight L 1 exhibited the maximum rate of relative root
elongation (data not shown). It is worth noting that HA can improve the
plant growth in water as well as in complete nutrient solution. The
stimulation (in water) in the presence of HA exceeded that obtained in
nutrient solution (for review, see Chen and Aviad,
1990 ). A minimal medium (CaCl2, 2 mM)
has been used in this work to avoid any interference from nutrient
constituents that could function synergistically along with HA on plant
growth and metabolism (e.g. Pinton et al., 1999 ).
Root Growth Measurement
On the 7th d, the roots were collected to estimate their lengths
and areas using SIARCS software image analyzer (Cruvinel et al.,
1996 ). Other samples of root seedlings were collected and used
for further experiments.
Frequency of Sites of Lateral Root Emergence
Seeds of maize were germinated for 4 d in wet filter paper
and rooted in a medium containing 0 or 40 mg L 1 of HA.
The whole root systems (three replicates) of both treatments were
harvested every day during a period of 7 d to evaluate the number
of mitotic sites, as follows: The entire root system was washed in
water and cleared by boiling at 75°C for 20 min in KOH (0.5%, w/v).
Afterward, root samples were rinsed in water and stained for 14 h
in the dark in hematoxylin staining solution. Then, they were rinsed in
water and destained in 80% (w/v) lactic acid at 75°C for 30 to 90 s. Individual specimens were transferred to petri plates
containing water and observed using stereoscopic microscopy at 40× to
evaluate the number of mitotic sites, visible as red dots on a pink to
white background of root tissue. Hematoxylin stock solution consisted
of 1 g hematoxylin, 0.5 g ferric ammonium sulfate, and 50 mL
of 45% (w/v) acetic acid, and was stored in the dark at room
temperature. Stain was prepared by diluting the stock solution 40-fold
in water.
PM-Enriched Vesicles
PM vesicles were isolated from roots grown with and without 40 mg L 1 HA using differential centrifugation as described
by De Michelis and Spanswick (1986) , with
some modifications (Façanha and de Meis, 1995 ). In
brief, about 15 g (fresh weight) of maize roots was homogenized
using a mortar and pestle in 30 mL of ice-cold buffer containing 250 mM Suc, 10% (w/v) glycerol, 0.5% (w/v)
polyvinylpyrrolidone-40 (40 kD), 2 mM EDTA, 0.5%
(w/v) bovine serum albumin, and 0.1 M Tris-HCl
buffer, pH 8.0. Just before use, 150 mM KCl, 2 mM dithiothreitol (DTT), and 1 mM
phenylmethylsulfonyl fluoride were added to the buffer. The
homogenate was strained through four layers of cheesecloth and
centrifuged at 8,000g for 10 min. The supernatant was
centrifuged once more at 8,000g for 10 min and then at
100,000g for 40 min. The pellet was resuspended in a
small volume of ice-cold buffer containing 10 mM Tris-HCl
(pH 7.6), 10% (v/v) glycerol, 1 mM DTT, and 1 mM EDTA. The suspension containing membrane vesicles was layered over a 20%/30%/42% (w/w) discontinuous Suc gradient that contained, in addition to Suc, 10 mM Tris-HCl buffer (pH
7.6), 1 mM DTT, and 1 mM EDTA. After
centrifugation at 100,000g for 3 h in a swinging
bucket, the vesicles which sedimented at the interface between 30% and
42% (w/w) Suc were collected, diluted with 3 volumes of
ice-cold water, and centrifuged at 100,000g for 40 min.
The pellet was resuspended in a buffer containing 10 mM
Tris-HCl (pH 7.6), 10% (v/v) glycerol, 1 mM DTT, and 1 mM EDTA. The vesicles were either used immediately or
frozen under liquid N2 and stored at 70°C until use.
Protein concentrations were determined by the method of Lowry et
al. (1951) .
ATPase Activity
ATPase activity in PM vesicles was determined by measuring the
release of Pi colorimetrically (Fiske and Subbarow,
1925 ). Between 80% and 95% of the PM vesicles' ATPase
activity measured at pH 6.5 was inhibited by vanadate (0.1 mM), a very effective inhibitor of the PM P-type
H+-ATPase (Sze, 1985 ). In all experiments,
the ATPase activity was measured at 30°C, with and without vanadate,
and the difference between these two activities was attributed to the
PM H+-ATPase.
ATPase H+ Pumping
The electrochemical H+ gradient generated by the
H+-ATPase was estimated from the initial rate of quenching
of the fluorescent pH probe ACMA (2 µM, 415-/485-nm
excitation/emission), and expressed in percentage quenching per minute.
The assay medium contained 10 mM HEPES-KOH (pH 6.5), 100 mM KCl, 3 mM MgCl2, 2.5 µM ACMA, and 0.05 mg L 1 PM vesicles
protein. The reaction was triggered by addition of 1 mM ATP.
Western Blot
PM vesicles isolated from maize roots, treated or not with HAs,
were incubated at 65°C for 10 min, separated on 7.5% (w/v) SDS-PAGE, and transferred to a nitrocellulose membrane. After blocking
(5% [w/v] dry milk in phosphate-buffered saline), the nitrocellulose membrane was probed with anti-H+-ATPase PMA2
(from Nicotiana plumbaginifolia Viv.) polyclonal antibodies. These PMA2 antibodies recognized all the isoforms of the
enzyme (Morsomme et al., 1996 ) at a dilution of 1:5,000. The detection of the H+-ATPase was carried out with the
rabbit peroxidase-linked secondary antibodies revealed using
diamino-benzidine tetra-hydrochloride. The spots on the
nitrocellulose membrane were quantified densitometrically as described
by Retamal et al. (1999) .
 |
ACKNOWLEDGMENTS |
We gratefully acknowledge Dr. Martha M. Sorenson (Universidade
Federal do Rio de Janeiro, Brazil) for revision and helpful discussion
of the manuscript, and Dr. Marc Boutry (Université Catholique de
Louvain, Belgium) for providing the PM H+-ATPase antibody.
We are also grateful to Dr. Victor M. Runjanek (Universidade Federal
Rural do Rio de Janeiro, Brazil) and Dr. Jan Schripsema (Universidade
Estadual do Norte Fluminense Darcy Ribeiro, Brazil) for assistance in
spectroscopic measurements.
 |
FOOTNOTES |
Received April 11, 2002; returned for revision June 16, 2002; accepted August 5, 2002.
1
This work was supported by Fundação
de Amparo à Pesquisa do Estado de Rio de Janeiro
(research fellowship no. 26.619.150/99 to L.P.C. and grant no.
172.333/00 to A.R.F.) and by Conselho Nacional de Desenvolvimento
Científìco e Tecnológico (grant no.
475522/01-0 to A.R.F.).
*
Corresponding author; e-mail arnoldo{at}uenf.br; fax
55-22-27261514.
Article, publication date, and citation information can be found at
www.plantphysiol.org/cgi/doi/10.1104/pp.007088.
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