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Plant Physiol, August 2001, Vol. 126, pp. 1391-1402
Molybdenum Sequestration in Brassica
Species. A Role for Anthocyanins?1
Kerry L.
Hale,
Steve P.
McGrath,
Enzo
Lombi,
Stephen M.
Stack,
Norman
Terry,
Ingrid J.
Pickering,
Graham N.
George, and
Elizabeth A.H.
Pilon-Smits*
Department of Biology, Anatomy/Zoology Building, Colorado State
University, Fort Collins, Colorado 80523 (K.L.H., S.M.S., E.A.H.P.-S.);
Agriculture and Environment Division, Institute of Arable Crops
Research-Rothamsted, Harpenden, Hertfordshire AL5 2JQ, United
Kingdom (S.P.M., E.L.); Department of Plant and Microbial Biology, 111 Koshland Hall, University of California, Berkeley, California 94270 (N.T.); and Stanford Synchrotron Research Laboratory (SSRL), Stanford
Linear Accelerator Center, P.O. Box 20450, Stanford, California
94309 (I.J.P., G.N.G.)
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ABSTRACT |
To elucidate plant mechanisms involved in molybdenum (Mo)
sequestration and tolerance, Brassica spp. seedlings
were supplied with molybdate, and the effects on plant physiology,
morphology, and biochemistry were analyzed. When supplied with
(colorless) molybdate Indian mustard (Brassica juncea)
seedlings accumulated water-soluble blue crystals in their peripheral
cell layers. Energy dispersive x-ray analysis showed that Mo
accumulated predominantly in the vacuoles of the epidermal cells.
Therefore, the blue crystals are likely to be a Mo compound. The x-ray
absorption spectrum of the plant-accumulated Mo was different than that
for molybdate, indicating complexation with a plant molecule. Because
the blue compound was water soluble and showed a pH-dependent color
change, possible involvement of anthocyanins was investigated. An
anthocyanin-less mutant of Brassica rapa ("fast
plants") was compared with varieties containing normal or high
anthocyanin levels. The anthocyanin-less mutant did not show
accumulation of a blue compound when supplied with molybdate. In the
anthocyanin-containing varieties, the blue compound colocalized with
anthocyanins in the peripheral cell layers. Mo accumulation by the
three B. rapa varieties was positively correlated with
anthocyanin content. Addition of molybdate to purified B.
rapa anthocyanin resulted in an in vitro color change from pink
to blue. Therefore, Mo appears to be sequestered in vacuoles of the
peripheral cell layers of Brassica spp. as a blue compound, probably a Mo-anthocyanin complex.
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INTRODUCTION |
Molybdenum (Mo) is an essential
micronutrient for plants, bacteria, and animals. Mo-deficient plants
exhibit poor growth and low chlorophyll and ascorbic acid content
(Marschner, 1995 ). Mo is also a component of some bacterial
nitrogenases, and therefore is especially important for plants that
live in symbiosis with nitrogen-fixing bacteria. The major metabolic
function for Mo in eukaryotic organisms is as an essential component of
the mononuclear Mo enzymes (Hille, 1996 ), which play roles in many key
metabolic processes such as sulfur detoxification, purine catabolism,
nitrate assimilation, and phytohormone synthesis in plants (Stallmeyer et al., 1999 ). These enzymes usually (but not always) catalyze two-electron redox reactions that are coupled to the transfer of an
oxygen atom to or from substrate and the metal, during which the Mo
cycles between the Mo(VI) and Mo(IV) oxidation states. In these
systems, Mo is bound to the dithiolene of a novel pyranopterin cofactor
that is known as molybdopterin (Hille, 1996 ). Although a
low-Mr species containing both Mo and
molybdopterin has never been properly characterized, this complex is
known as the Mo cofactor (Moco). These enzymes are unrelated to the
Mo-containing nitrogenase of nitrogen-fixing bacteria that contain a
Mo-iron-sulfur cluster.
A mutational block in the early steps of Moco biosynthesis leads to the
combined loss of function of Mo enzymes. As a result, plant cells can
no longer assimilate inorganic nitrogen and have altered levels of
certain phytohormones (Seo et al., 1998 ). However, a change in proteins
catalyzing the last step of Moco synthesis, i.e. the transfer and
incorporation of Mo into molybdopterin, leads to a molybdate repairable
phenotype (Falciani et al., 1994 ), whereby the addition of molybdate is
sufficient to overcome the negative effects of the mutation. Therefore,
molybdate is thought to be the source of Mo for incorporation into Moco
(Kuper et al., 2000 ).
In plants, Mo is readily mobile in xylem and phloem for long-distance
transport (Kannan and Ramani, 1978 ), though little is known of the
mechanisms involved in Mo homeostasis. Molybdate competes with sulfate
for uptake at the root surface, suggesting a common uptake mechanism
(Stout et al., 1951 ). However, it has also been suggested that
molybdate is taken up by a phosphate transporter (Heuwinkel et al.,
1992 ). Furthermore, a recent study by Palmgren and Harper (1999)
suggests the presence of a Mo-specific metal transporter, AMA1, in
Arabidopsis. T-DNA knockout mutants, where AMA1 was rendered
ineffective, showed 5-fold reduced Mo accumulation, but no reduction in
any other essential micronutrients.
The Mo content of plants is a direct reflection of the bioavailability
of Mo in the soil. The relation of Mo influx versus concentration is
approximately linear in soil systems (Barber, 1995 ). Bioavailability of
Mo is positively correlated with soil pH (Karmian and Cox, 1978 ). In
acidic soils, Mo deficiency in plants is common. On the other hand, in
some soils of high pH, plants may accumulate enough Mo for ruminants
feeding on the plants to develop molybdenosis. Molybdenosis is caused
by an imbalance of Mo and copper in the ruminant diet, which induces a
copper deficiency (Stark and Redente, 1990 ). Plants supplied with
adequate Mo usually contain 1 to 2 mg kg 1 Mo;
plant material containing an excess of 5 mg kg 1
Mo is sufficient to cause molybdenosis in ruminant animals (Barber, 1995 ). Molybdenosis in livestock occurs in the western U.S., often in
soils with poor drainage and high organic matter (Gupta and Lipsett,
1981 ). Mo pollution due to mining and stainless steel industry poses a
serious environmental problem at several locations in the U.S.,
including several Superfund sites (polluted sites in the U.S.
designated by the U.S. Environmental Protection Agency for high
priority remediation). Plant samples from a mining site near Empire, CO
were found to contain up to 400 mg kg 1 Mo
(Trlica and Brown, 2000 ). Phytoremediation, the use of plants to
remediate environmental pollution, may prove to be a viable strategy
for remediating Mo in these areas, either via phytoextraction (accumulation in harvestable plant parts) or phytostabilization (in
situ immobilization).
To use plants optimally for Mo remediation, we need to know which
processes are involved and where rate limitations may occur. The goal
of this study was to obtain a better understanding of plant mechanisms
that control accumulation, tolerance, and biotransformation of Mo in plants.
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RESULTS |
When Indian mustard (Brassica juncea) seedlings were
grown on agar medium containing different concentrations of colorless ammonium molybdate, they showed blue coloration, especially at the base
of the hypocotyl and around the petioles (Fig.
1, A-C). Cross sections of the
Mo-treated seedlings showed that the blue compound was present in a
crystal-like form (Fig. 1, C and D), localized predominantly in the
epidermal and subepidermal tissues (Fig. 1E). Seedlings grown without
Mo did not show this blue coloration (Fig. 1F). A similar distribution
was observed when mature plants were supplied with ammonium molybdate,
with the blue coloration being most pronounced in the stem and near
vascular tissue in the leaves (results not shown).

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Figure 1.
Indian mustard seedlings grown for 7 d in
agar medium, with (A-E) or without (F) 60 mg
L 1 ammonium molybdate. A, Seedling. B, Close-up
of petiole. C, Close-up of hypocotyl. D, Longitudinal section of
hypocotyl at higher magnification to show irregular blue precipitate in
some epidermal cells. The black line connects the precipitate at low
and high magnification. E, Cross section of hypocotyls showing blue
color in the peripheral cell layers. F, Hypocotyl cross section of a
seedling grown without Mo.
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To determine whether the blue compound contained Mo, we used two
approaches. First, we compared the Mo concentrations in tissues of
bluer seedlings with those of seedlings that had less blue coloration
from the same treatment (Fig. 2). Stem
and leaf samples from bluer seedlings contained significantly higher Mo
concentrations than did those for less blue seedlings. In the second
approach, energy dispersive x-ray analysis (EDXA) was used to determine the localization of Mo. Mo was accumulated primarily in the epidermal cells of the hypocotyl (Fig. 3),
correlating with the location of the blue compound. Dot maps of EDXA
analyses show that the concentration of Mo was low in the cell walls,
whereas most Mo was located in the vacuoles. No association with K or P
was observed (Fig. 3). The concentration of Mo in the vacuoles of
epidermal cells was calculated to be 33.7 ± 5.4 mM
(SE; n = 23). Larger cells (30-50 µm)
contained significantly higher Mo concentrations (49.6 ± 6.1 mM) than smaller (approximately 10 µm) cells
(13.1 ± 2.4 mM). The concentration of Mo in
the mesophyll was below the EDXA detection limit for Mo (<10
mM). Thus, results from this approach again
indicate that the blue color results from the presence of Mo.

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Figure 2.
Tissue Mo concentration in Indian mustard
seedlings grown for 7 d on agar medium containing 60 mg
L 1 ammonium molybdate. Stem or leaf tissue
collected from bluer seedlings contained higher Mo concentrations
(P < 0.05, n = 3) than comparable
organs of less blue seedlings. Values represent the mean ± SE of three samples pooled from 36 seedlings
each.
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Figure 3.
EDXA images of hypocotyl sections of Indian
mustard seedlings grown for 7 d on agar medium containing 130 mg
L 1 ammonium molybdate. Mo is present mainly in
the epidermis (top right image), whereas K and P are evenly distributed
throughout the tissue (bottom).
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X-ray absorption spectroscopy (XAS) was used to provide details of the
chemical form of Mo present in the plant tissues. Molybdate in aqueous
solution exists as the
[MoO4]2 anion in basic
conditions, but at acidic pH levels (i.e. below about pH 6) the
[MoO4]2 anion
protonates to form water and polymolybdate anions, the simplest of
which is paramolybdate
[Mo7O24]6 ,
which is formed of seven edge-sharing octahedra. The coordination geometry of Mo thus changes from pure tetrahedral high pH, to octahedral at low pH, and the mean number of oxo groups per Mo is
reduced from four to two for
[Mo7O24]6 ,
or to even smaller values for the higher polymolybdate anions. As shown
in Figure 4A, the Mo K near-edge spectrum
from the plant differs from that of aqueous
[MoO4]2 and
[Mo7O24]6
standards, with some resemblance to the polymolybdate. In particular, the pronounced pre-edge peak observed in both molybdate spectra is
somewhat lower in intensity in the shoot spectrum. This peak can be
assigned to a 1 s 4 d transition, which is dipole
forbidden with a small quadrupole-allowed intensity, although in
non-centrosymmetric environments mixing of 5 p with 4 d
levels confers significant dipole-allowed intensity (Kutzler et al.,
1980 ). The intensity of this feature has been observed to correlate
with the number of Mo = O (oxo) ligands to Mo, which is consistent
with the smaller intensity observed for
[Mo7O24]6
versus [MoO4]2 . In the
plant spectrum, its reduced presence suggests a smaller number of oxo
groups (e.g. around two).

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Figure 4.
XAS of Mo in Indian mustard seedlings grown
for 7 d on agar medium containing 60 mg L 1
ammonium molybdate. A, Mo K x-ray absorption near-edge spectra of: a,
Molybdate in aqueous solution at pH 8 (solid line) and pH 4 (dashed
line); b, Indian mustard seedlings; c, Brassica rapa
anthocyanin-less mutant; and d, aqueous extracts of Indian mustard at
pH 8 (dashed line), pH 6 (solid line), and pH 4 (dot-dashed line). B,
Results of extended x-ray absorption fine structure (EXAFS) curve
fitting of shoots of Indian mustard seedlings. Inset, The
k3-weighted Mo K-edge EXAFS oscillations
for the experimental data (solid line) and the best fit (dashed line)
according to the parameters in Table I. The main panel shows the
corresponding Fourier transforms, phase corrected for the first shell
Mo-O interactions.
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The EXAFS spectrum (Fig. 4B) of Mo in plant shoots confirms that the Mo
is modified from the simple
[MoO4]2 structure,
which consists of four Mo = O interactions at 1.76 Å. The shoot
spectrum indicates several different interactions in the first shell,
and there is also evidence for longer range interactions at >3 Å.
Curve fitting of the data (Table I)
indicates three different Mo O distances in the first shell, at
1.72, 1.96, and 2.23 Å, and models the outer shells as two different Mo... . Mo interactions at 3.15 and 3.35 Å.
This is consistent with a polymolybdate-type cluster in the plant.
[Mo7O24]6 ,
for example, has Mo = O bonds at 1.71 to 1.72 Å, with Mo-O bonds cis to oxo ligands at about 1.89 to 2.00 Å and Mo-O bonds trans to
Mo = O bonds at 2.1 to 2.5 Å. Considering the heterogeneity in
bond lengths, this is in excellent agreement with our curve-fitting results. The Mo-Mo distances in
[Mo7O24]6
form two obvious groups at 3.20 to 3.28 Å and 3.41 to 3.45 Å, which
compares reasonably well with our analysis, especially because the
EXAFS from these will include multiple scattering that was neglected in
our simple analysis. Taken together, the spectroscopic evidence
strongly suggests the presence of a polymolybdate species in the
plant.
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Table I.
EXAFS curve fitting of molybdate and molybdate
transformed in plant shoots
Coordination no. was fitted to the nearest integer. The nos. in
parentheses after the distances and Debye-Waller factors indicate the
precisions, expressed as three times the estimated SDs
(obtained from the diagonal elements of the covariance matrix) in the
last digit(s) of the values. The accuracies will be larger than, and
related to, the precisions, and will typically be less than ±0.02 Å for interatomic distances.
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To further investigate the chemical nature of the blue compound
produced by Indian mustard when exposed to Mo, ground plant tissue was
extracted with different solvents (water, methanol, acetone, and
chloroform). The blue compound was found to be most soluble in water,
though it appears to precipitate at higher concentrations, forming
crystal-like structures as those seen in Figure 1. Alteration of the pH
with either HCl or NaOH caused the color of the aqueous extract to
change from blue to either pink (pH < 3.4) or yellow (pH > 7.2). This color change was reversible (results not shown). Mo K
near-edge spectra of the extracts at different pH are shown in Figure
4A. As expected from simple chemistry (see above) the spectrum of the
high pH (yellow) extract resembled that of aqueous [MoO4]2 , whereas those
of both pink and blue low-pH forms were slightly different from each
other, similar to the spectrum of the shoots, and are consistent with polymolybdates.
Because pH-dependent color change is a property of anthocyanins, we
wanted to test the involvement of anthocyanins in the formation of blue
compounds, Mo tolerance, and Mo accumulation. To this end, we made use
of different varieties of rapid-cycling B. rapa ("fast
plants") that vary in anthocyanin production. A mutant unable to
produce anthocyanin (C1-108) was compared with intermediate anthocyanin
(C1-34) and high anthocyanin (C1-67) varieties. When grown in the
presence of Mo, the anthocyanin-less mutant did not show the blue
coloration, and the high anthocyanin variety was bluer than the variety
containing intermediate anthocyanin levels (Fig.
5A). Thus, the degree of blueness was
related to anthocyanin content. The Mo K near-edge spectrum of shoot
tissue of the B. rapa anthocyanin-less mutant (Fig. 4A)
appeared similar to that of the Indian mustard shoot tissue, but with a
less pronounced pre-edge peak.

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Figure 5.
Mo-induced blueness is correlated with anthocyanin
content. A, B. rapa seedlings were grown for 7 d on
agar medium in the absence (left) or presence (right) of 30 mg
L 1 ammonium molybdate. Three varieties were
used, with different anthocyanin levels: anthocyanin-less (C1-108),
intermediate anthocyanin content (C1-34), and high anthocyanin
content (C1-67). B, Cross sections of different B. rapa varieties grown for 7 d on agar medium with or without
60 mg L 1 ammonium molybdate. Left,
anthocyanin-less mutant (C1-108) grown in the presence of molybdate;
middle, right, high-anthocyanin variety (C1-67) grown in the absence
(middle), or the presence (right) of molybdate. Blue crystals similar
to those found in Indian mustard were present in the Mo-treated
B. rapa C1-67 seedlings, although difficult to see at this
magnification.
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To visualize the distribution of the colored compounds, B. rapa varieties grown with and without Mo were cross-sectioned and the presence of blue compounds and anthocyanins were compared. anthocyanin-less mutants exposed to Mo showed no accumulation of the
blue compound (Fig. 5B, left). There was no observable difference between treated and non-treated (not shown) cross sections of anthocyanin-less plants. In the anthocyanin-containing varieties, the anthocyanin was shown to be concentrated in the peripheral cell
layers (Fig. 5B, middle), as was the blue compound that was produced
when the plants were treated with Mo (Fig. 5B, right). Therefore, the
tissue distribution of anthocyanin is similar to that of the blue compound.
To determine the possible role of anthocyanins in Mo accumulation and
tolerance, we compared shoot Mo concentrations, fresh weights, and root
lengths of the three B. rapa varieties. In a first
experiment, seeds were sterilized using a standard procedure with
ethanol and bleach. The results showed a distinct relationship between
anthocyanin content and Mo tolerance (Table
II) and accumulation (Fig.
6A). There was no difference in tolerance
to the bleach treatment alone; therefore, it is unlikely that the
relationships between anthocyanin and Mo tolerance or accumulation is
an artifact of differential bleach tolerance. However, because
germination frequencies were rather low after the bleach and ethanol
treatment (especially for C1-108), a second experiment was done where
seeds were sterilized using plant preservative mixture (PPM) to deter infection without the potential harm that bleach and ethanol may cause.
Again, there was a significant difference in
Mo accumulation between the anthocyanin-less and
anthocyanin-containing varieties (Fig. 6B). However, there
was no clear correlation between Mo tolerance and anthocyanin content,
except for fresh weight at 60 mg L 1 Mo (Table
III) Please note that because we were
unable to grow C1-34 seedlings without infection on PPM, no data are
available for that genotype. In a last experiment, no sterilization
procedure was used. Every box of seedlings used for this experiment had some microbial infection; therefore, growth data were not recorded. Individual seedlings that were not infected were removed, washed, and
tested for Mo content. Once again, there was a relationship between Mo
accumulation and anthocyanin content (Fig. 6C). Please note that there
were no C1-34 seedlings left uninfected after 7 d; therefore,
C1-34 data are not shown.
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Table II.
Mo tolerance of bleach-sterilized B. rapa varieties
Seedlings were grown for 7 d on agar medium containing 30 mg
L 1 Mo ammonium molybdate. Values shown represent relative
growth, calculated as: (growth + Mo/growth Mo) × 100% (mean ± SE, n = 36).
P values represent a statistical comparison with the
C1-108 line. C1-108, Anthocyaninless variety; C1-34, wild type; C1-67,
high anthocyanin variety.
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Figure 6.
Shoot Mo concentrations in seedlings of different
B. rapa varieties grown for 7 d on agar medium with
ammonium molybdate. The seeds were either bleach sterilized (A), plant
preservative mixture (PPM; Plant Cell Technology, Inc., Washington,
DC) sterilized (B), or not sterilized (C). The Mo concentration
in the anthocyanin-less mutant (C1-108) was significantly lower than in
C1-34 or C1-67 in all cases (P < 0.05, n = 5) except in experiment B at 30 ppm Mo,
where P < 0.10 (n = 5).
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Table III.
Mo tolerance of PPM-sterilized B. rapa varieties
Seedlings were grown for 7 d on agar medium containing ammonium
molybdate. Values shown represent relative growth, calculated as:
(growth + Mo/growth Mo) × 100% (mean ± SE, n = 36). P values represent
a statistical comparison with the C1-108 line. C1-108, Anthocyaninless
variety; C1-67, high anthocyanin variety. NS, Not significant
(P > 0.05).
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Because it is not known which step in the anthocyanin biosynthesis
pathway is affected in mutant C1-108, several experiments were
performed to confirm that anthocyanins are responsible for the observed
effects, and not some other product of this pathway. First, seedlings
of the three varieties were treated with a methanol/HCl solution
overnight to extract anthocyanins (and other flavonoids). This crude
extract was brought up to vacuolar pH 5 (Fig.
7A, left), and molybdate was added. The
anthocyanin-less extract remained colorless even after the addition of
Mo, whereas the C1-34 and C1-67 extracts immediately turned bright blue
(Fig. 7A, middle). The pH of the extracts after Mo addition did not
change significantly; therefore, this phenomenon is not the result of a
simple change in pH. Extract from the C1-34 variety was further
purified using paper chromatography, brought up to vacuolar pH, and
molybdate was added. The blue color change immediately occurred (Fig.
7A, right) giving further evidence that anthocyanins are involved in
the formation of blue compounds in these B. rapa
seedlings.

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Figure 7.
Anthocyanins appear to be involved in formation of
a blue Mo compound. A, Anthocyanin extracts made from B. rapa C1-34 seedlings grown for 7 d on agar medium without Mo.
Left, Extracts; middle, after in vitro addition of molybdate; right,
after purification, before and after addition of molybdate. B,
Detection of flavonols in the different B. rapa varieties
grown for 7 d on agar medium without Mo. Left, Cross sections of
hypocotyls, stained with diphenylboric acid-2-aminoethyl ester,
visualized using a UV light source and
4,6-diamidino-2-phenylindole (DAPI) filter. The white arrows
indicate the presence of flavonols, which stain orange. Note that other
autofluorescence seen here is probably caused by sinapate esters
(blue), chlorophyll (red), and xylem (white). Right, Paper chromatogram
of flavonoid extracts, obtained using butanol:acetic acid:water (4:1:5,
v/v) as the liquid phase.
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Second, to determine the presence of flavonols (direct precursors of
anthocyanins) within the plant tissue of the C1-108 mutants, seedlings
of each B. rapa variety were treated with
diphenylboric-acid-2-aminoethyl ester (DPBA) to visualize the
fluorescence of flavonols. In cross-sectional comparisons with C1-34
(and C1-67, not shown), the anthocyanin-less mutants appear to have
greater accumulation of flavonols (Fig. 7B, left), which stain
orange-yellow under a UV light source with a DAPI filter. Therefore,
flavonols appear to be present in the C1-108 mutant, and, because they
appear to be accumulated, the mutation may be at the dihydroflavonol
reductase step (conversion of flavonols to leucoanthocyanidins). We
also used paper chromatography of crude anthocyanin extracts from all
three varieties, and compared autofluorescence under a UV light source.
Apart from the absence of the pink anthocyanin spot, the C1-108
mutant's chromatogram did not show any differences in flavonoid
pattern compared to C1-34 and C1-67 (Fig. 7B, right).
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DISCUSSION |
Indian mustard and B. rapa plants supplied with
colorless molybdate accumulated a blue compound in the peripheral cell
layers. This compound appears to be associated with Mo because the blue color intensity was correlated with Mo content of the seedlings (Fig.
2). Also, EDAX data showed accumulation of Mo in the epidermal layer
(Fig. 3). XAS data indicated that Mo is accumulated in the form of
polymolybdate(s) in the plant (Fig. 4). The blue color most likely
arises from complexation of the polymolybdate(s) with anthocyanins
(polymolybdates are colorless), for anthocyanin-less B. rapa
mutants did not exhibit the blue coloration when supplied with
molybdate (Fig. 5A). Furthermore, in anthocyanin-containing B. rapa varieties, the blue compound colocalized with the
anthocyanins in the epidermal cell layer (Fig. 5B). Anthocyanin levels
were positively related to Mo concentration in the three B. rapa varieties (Fig. 6). Our data were not conclusive with respect
to a possible role of anthocyanins in Mo tolerance, for anthocyanin
levels were positively correlated with Mo tolerance under some but not
all experimental conditions tested.
The compound responsible for the observed effects appears to be
anthocyanin, rather than some other flavonoid, for the following reasons. First, a purified anthocyanin extract showed an in vitro color
change from pink to blue upon addition of molybdate (Fig. 7A). Second,
based on fluorescence microscopy, the anthocyanin-less mutant appears
to be able to produce flavonols (Fig. 7B), which are the last
intermediates in the anthocyanin biosynthesis pathway before
leucoanthocyanidins are formed (Dooner and Robbins, 1991 ). Also, paper
chromatography showed that the anthocyanin-less seedlings contain all
the UV-fluorescent products of the anthocyanin-containing varieties,
but no anthocyanin (Fig. 7B). Anthocyanins in the plant are mostly
dissolved in cell fluids, but are sometimes present as crystals
(Shibata et al., 1919 ). This is in accordance with what we have found
because the blue compound exists as a water-soluble, crystalline precipitate.
This is the first time that anthocyanins have been proposed as having a
function in metal accumulation or tolerance, although metal
complexation has long been known to have a role in determining anthocyanin color (Elhabiri et al., 1997 ). Proposed roles for anthocyanins include attraction of pollinators and seed dispersers (Mol
et al., 1996 ), UVB protection (Klaper et al., 1996 ), modification of
the quality and quantity of captured light (Barker et al., 1997 ),
defense from herbivory (Coley and Kusar, 1996 ), protection from
photoinhibition (Dodd et al., 1998 ), and free radical scavenging (Yamasaki, 1997 ). It is known that anthocyanins are produced in response to stress (Chalker-Scott, 1999 ), and may be sequestered in
response to ethylene (Zhou and Goldsbrough, 1993 ). Therefore, it is
quite feasible that anthocyanins play a role in stress resistance.
The involvement of anthocyanins in Mo accumulation may be direct,
through binding of the Mo, or indirect. Binding of Mo to anthocyanins
may explain the color change to blue. Our XAS data indicate a change
from four- to six-coordinate Mo, as well as longer range interactions.
These observations, together with the vivid blue color of the plant
material, initially suggested the possibility of in vivo formation of
Mo blues or heteropoly blues. The former comprise a family of soluble
molecules consisting of oxygen-coordinated polyhedra of Mo linked
together to form giant wheel-shaped clusters (Müller and Serain,
2000 ), whereas the latter also involve
MoOn polyhedra, and additionally a heteroatom such as four-coordinate phosphorus. However, the presence of these complexes is not consistent with the pH-dependent reversible color changes of the aqueous plant extracts observed in the present work
(Müller and Serain, 2000 ). These observations are more
consistent with the formation of a Mo-catecholate complex, such as a
Mo-anthocyanin complex, in which there may be binding of one or more Mo
of a polymolybdate anion at the ortho-dihydroxyl group on the B ring on
the anthocyanin. A similar complexation of metals with anthocyanins has
been reported for magnesium (Kondo et al., 1992 ), iron (Everest and
Hall, 1921 ), and aluminum (Takeda et al., 1985 ). In each case, binding
of these metals also resulted in a color change to blue. Therefore, it
is likely that the anthocyanins directly bind the Mo, resulting in a
blue product. In fact, molybdate is used in colorimetric assays of
phenolics or lipids, in which the resulting product turns blue (Rouser
et al., 1970 ). The involvement of anthocyanin is not expected to be
obvious in the XAS data because both Mo-OH and
Mo-O-(anthocyanin) would be expected to have very similar bond lengths, and only one Mo in the polymolybdate need be
involved for effective complex formation.
The location of the Mo in the vacuoles of the epidermis (EDXA, 33 mM) corresponds with the intracellular location of
anthocyanins (Alfenito et al., 1998 ). Other studies have also shown
accumulation of metals in the vacuoles of the epidermis. For example,
Heath et al. (1997) reported similar localization of nickel in the
epidermis of Thlaspi montanum var sikiyouense
leaves and Küpper et al. (1999) found zinc to compartmentalize in
the epidermal vacuoles of the zinc hyperaccumulator, Thlaspi
caerulescens. The observed correlation between dimension of cells
and Mo content is also in agreement with results concerning Zn
accumulation in T. caerulescens leaves, as reported by
Küpper et al. (1999) , who propose that vacuolation of epidermal
cells may promote preferential Zn accumulation. Thus, sequestration of
excess metals in the vacuoles of epidermal cells appears to be a common
mechanism of metal accumulation and may play a role in tolerance. It is
not clear what chelating agents are involved in accumulating various
metals in the epidermal vacuoles. So far, compounds shown to be
involved in the chelation of toxic metals are mostly peptides or
organic acids (e.g. Steffens, 1990 ; Salt et al., 1995 ; Zenk, 1996 ;
Larsen et al., 1998 ; Sagner et al., 1998 ; von Wiren et al., 1999 ). To
our knowledge, this is the first time that a role for anthocyanin is
proposed in metal sequestration.
The anthocyanin-containing B. rapa varieties accumulated
more Mo in their shoots than anthocyanin-less plants because their Mo
concentration was higher, and their biomass was equal or greater. It is
feasible that anthocyanins facilitate vacuolar sequestration of Mo,
thereby allowing plants to separate Mo from vital biochemical processes
in other cell compartments. This separation reduces metal toxicity,
resulting in better growth. Faster growth, in turn, is likely to
enhance Mo accumulation because metal translocation through the xylem
is thought to be driven by transpiration (Salt et al., 1995 ).
There are still many questions surrounding plant Mo uptake and
metabolism. The requirement of plants for Mo is lower than that for any
of the other mineral nutrients, except nickel (Marschner, 1995 ). Still,
plants are fairly tolerant to Mo. Therefore, there must be some
mechanism in plants whereby the toxic effects of Mo are reduced. This
study suggests anthocyanin to be a part of that mechanism, and thereby
sheds new light on both Mo metabolism and anthocyanin function in plants.
 |
MATERIALS AND METHODS |
Plant Material
Indian mustard (Brassica juncea) seeds (accession
no. 173874) were obtained from the North Central Regional Plant
Introduction Station (Ames, IA). Brassica rapa seeds
(accession nos. C1-108, C1-34, and C1-67) were obtained from the
Crucifer Genetics Cooperative Department of Plant Pathology (University
of Wisconsin, Madison). The accession nos. correspond accordingly:
C1-108 = anthocyanin-less variety, C1-34 = wild type, and
C1-67 = high-anthocyanin variety.
Seedling Growth Experiments
Indian mustard seeds were sterilized by rinsing in 96% (v/v)
ethanol for 30 s, then in 0.65% (w/v) hypochlorite
solution for 30 min, and subsequently in sterile deionized water
for 5 × 10 min, all on a rocking platform (Pilon-Smits et
al., 1999 ).
B. rapa seeds were either sterilized using the procedure
described above, or by soaking the seeds in 2% (w/v) PPM and
incorporating 0.1% (w/v) PPM into the growth medium.
Fifty seeds were sown in a grid pattern in Magenta boxes (Sigma, St.
Louis) on one-half-strength Murashige and Skoog medium with
10 g L 1 Suc and 4 g L 1 Agargel
(Sigma), pH 5.8, with or without ammonium heptamolybdate tetrahydrate
[(NH4)6Mo7O24]
(Aldrich, Milwaukee, WI). Please note that one-half-strength
Murashige and Skoog contains 0.125 mg L 1 Mo; therefore,
the untreated controls were not Mo depleted. Indian mustard seedlings
were supplied with 60 mg L 1 Mo and B. rapa
seedlings were supplied with 30 or 60 mg L 1 Mo. Mo
concentrations were chosen to give approximately 50% growth inhibition. For Indian mustard, this concentration was 60 mg
L 1 Mo. B. rapa seedlings were more
sensitive to Mo: 50% inhibition was reached at 30 mg L 1
Mo. Still, some experiments with B. rapa were carried
out using 60 mg L 1 Mo to compare with Indian mustard.
After 7 d at 25°C at 16-h-light and 8-h-dark photoperiod,
individual seedlings were harvested, washed, and weighed, and the root
length was measured. Roots were removed and the shoots were dried
overnight at 70°C for elemental analysis.
Mo Analysis
For the analysis of Mo content, dried plant samples (30 mg) were
acid digested according to the method of Zarcinas et al. (1987) . Mo concentrations were analyzed in the acid digests
using inductively coupled plasma atomic emission spectrometry according to the method of Fassel (1978) .
EDXA
Seeds of Indian mustard were germinated under sterile conditions
as described above, on agar medium containing 130 mg L 1
Mo. This Mo concentration is higher than that used for other experiments with Indian mustard because EDXA requires high levels of Mo
in the plant tissue for useful dotmaps to be collected. The seedlings
were grown in a controlled environment under the following conditions:
16-h day length with a light intensity of 350 µmol photons
m 2 s 1 supplied by fluorescent tubes,
20°C/16°C day/night temperature, and 60% to 70% relative
humidity. After 10 d the seedlings were removed and x-ray
microanalysis was performed on the stems (n 3).
Sections of plant stems were excised and mounted in an Al vice. Samples
were then rapidly (within less than 1 min after excision) frozen in
liquid nitrogen and transferred to a fracturing chamber cooled to 170°C. A blade was used to cut through the cells.
Samples subsequently were coated evaporatively with carbon. EDXA
analysis was performed in a scanning electron microscope (XL 40, Philips, Eindhoven, The Netherlands) on a cryostage
( 160°C to 180°C), using an acceleration voltage of 30 kV and
a working distance of 10 mm. Spectra from 0 to 20 keV were collected at
increments of 10 eV per channel with the electron beam focused on a
rectangular area in the center of selected cells. The spectra were
analyzed using the program Superquant (EDAX, San Francisco). A
calibration between peak/background ratios for specific elements and
their concentrations in the standard solutions was used to quantify the
data recorded (Boekestein et al., 1984 ; Van Steveninck and Van
Steveninck, 1991 ). The distribution of selected elements across a
section of a sample was measured semiquantitatively by displaying the
count rate within a narrow spectrum window within its peak (0.6× peak
one-half width) along a line transect. A two-dimensional distribution
pattern was also recorded by scanning an area of the specimen
repeatedly for up to 2 h and integrating the counts for Mo, P, and
K within their respective spectrum windows into dot maps.
XAS Analysis
Shoot and root tissues were collected from 7-d-old Indian
mustard seedlings supplied with 60 mg L 1 Mo. The samples
were frozen in liquid nitrogen, ground, and stored at 80°C.
Comprehensive XAS of frozen plant tissues was carried out on beam line
4-3 of the SSRL, with a Si(220) double crystal monochromator, an
upstream aperture of 1 mm, and no focusing optics. Samples, either
ground plant material or dilute solutions of standards, were
transferred to lucite cuvettes with mylar tape for windows. During data
collection, the cuvettess were maintained at approximately 15 K in a
flowing liquid helium cryostat. X-ray absorption spectra were measured
in fluorescence using a 13-element germanium detector. Energy
calibration was achieved by collecting the spectrum of elemental Mo in
transmittance simultaneously with the data; the first energy inflection
of the Mo K edge was assumed to be 20,003.9 eV.
XAS data were analyzed using the EXAFSPAK suite of programs
(http://www-ssrl.slac.stanford.edu/exafspak). Extended EXAFS data were
quantitatively fit (Pickering et al., 1999 ) using phase and amplitude
functions generated using the program feff7 (Mustre de Leon et al.,
1991 ; Rehr et al., 1991 ).
Plant Extractions and Flavonoid Analysis
To extract the blue compound, Indian mustard seedlings treated
with 60 mg 1 L Mo were ground in liquid nitrogen using a
mortar and pestle. Samples (0.5 g) were transferred to microcentrifuge
tubes. One-milliliter aliquots of various solvents (methanol,
chloroform, and water) were added to individual samples. The solutions
were mixed, centrifuged to remove cell debris, and the supernatant was
transferred to a new tube. We considered this solution to be a crude
cell extract. The blue compound was most soluble in water; therefore,
aqueous extracts were used for pH titration experiments. The pH of the solutions was changed gradually by adding dilute solutions of HCl or
KOH, and color changes were monitored.
Anthocyanins and other flavonoids were extracted overnight at room
temperature from fresh, untreated 7-d-old B. rapa
seedlings in a 70% (v/v) methanol/1% (w/v) HCl solution. Plant
material was removed via centrifugation, and the solutions were brought up to pH 5, using KOH, to mimic vacuolar conditions.
The resulting crude anthocyanin extracts of each B. rapa
variety were spotted on chromatography paper (#1 Whatman Inc., Clifton, NJ). The chromatogram was developed in butanol:acetic acid:water (4:1:5, v/v), and viewed using a UV light source. Anthocyanins from
C1-34 seedlings were isolated using the same procedure. The pink spot
on the paper was cut out and placed in 1 mL of 70% (v/v) methanol/1%
(w/v) HCL solution to allow the anthocyanins to elute. The
purity of this anthocyanin isolate was confirmed by paper chromatography, using 1% (w/v) HCl as the liquid phase. To test the capacity of anthocyanins to form a blue product with Mo, ammonium molybdate crystals were added to the crude or pure anthocyanin extracts, and color changes were monitored visually.
Flavonol staining was done using 0.25% (w/v) DPBA and 0.02%
(v/v) Triton X-100 solution (Murphy et al., 2000 ). The solution was
mixed with gentle agitation for 48 h at room temperature (25°C) prior to use. Cross sections of seedlings were stained with the DPBA
solution immediately before visualization under a UV light source
with a DAPI filter (excitation 340-380 nm, suppression 430 nm).
Statistical Analysis
Student's t tests were performed using the
statistical software program JMP-IN from the SAS Institute (Cary, NC).
 |
ACKNOWLEDGMENTS |
We thank Lorrie Anderson for her help making the microscopic
images. We also thank Jan Maas, Wendy Peer, and Angus Murphy for their
helpful advice concerning flavonoid detection. We thank Mark de Souza,
Adel Zayed, and Steve Whiting for their help with the XAS analyses, and
the Crucifer Genetics Cooperative, Department of Plant Pathology
(University of Wisconsin, Madison) for supplying seeds of the B.
rapa varieties. We also thank Marinus Pilon and Dr. Edward I. Stiefel for helpful suggestions and for critically reading the manuscript.
 |
FOOTNOTES |
Received January 22, 2001; returned for revision April 9, 2001; accepted April 30, 2001.
1
This work was supported by the National
Science Foundation (Career Development Grant no. 9982432) and by the
Environmental Protection Agency (Research Grant no. G8A11586 to
E.A.H.P.-S.). The XAS experiments were made possible through SSRL
Synchrotron beam time (granted to N.T.). SSRL is funded by the U.S.
Department of Energy, Offices of Basic Energy Sciences and Biological
and Environmental Research; by the National Institutes of Health; by
the National Center for Research Resources, by the Biomedical Technology Program; and by the National Institute of General Medical Sciences. The Institute of Arable Crops Research-Rothamsted
receives grant-aided support from the Biotechnology and Biological
Sciences Research Council of the UK.
*
Corresponding author; e-mail: epsmits{at}lamar.colostate.edu; fax
970-491-0649.
 |
LITERATURE CITED |
-
Alfenito MR, Souer E, Goodman CD, Buell R, Mol J, Koes R, Walbot V
(1998)
Functional complementation of anthocyanin sequestration in the vacuole by widely divergent glutathione S-transferase.
Plant Cell
10: 1135-1149[Abstract/Free Full Text]
-
Barber SA
(1995)
Soil Nutrient Bioavailability: A Mechanistic Approach. John Wiley & Sons, Inc., New York
-
Barker DH, Seaton GGR, Robinson SA
(1997)
Internal and external photoprotection in developing leaves of the CAM plant Cotyledon orbiculata.
Plant Cell Environ
20: 617-624[CrossRef]
-
Boekestein A, Thiel F, Stols ALH, Aouw E, Stadhouders AM
(1984)
Surface roughness and the use of a peak to background ration in the x-ray analysis of bio-organic bulk specimen.
J Microsc
134: 327-333
-
Chalker-Scott L
(1999)
Environmental significance of anthocyanins in plant stress response.
Photochem Photobiol
70: 1-9
-
Coley PD, Kusar TA
(1996)
Anti-herbivore defenses of young tropical leaves: physiological constraints and ecological tradeoffs.
In
SS Mulkey, RL Shazdon, AP Smith, eds, Tropical Forest Plant Ecophysiology. Chapman and Hall, New York, pp 305-335
-
Dodd IC, Critchley C, Woodall GS, Stewart GR
(1998)
Photoinhibition in differently colored juvenile leaves of Syzgium species.
Exp Bot
49: 1437-1445[Abstract/Free Full Text]
-
Dooner HK, Robbins TP
(1991)
Genetic and developmental control of anthocyanin biosynthesis.
Annu Rev Genet
25: 173-199[CrossRef][ISI][Medline]
-
Elhabiri M, Figueiredo P, Toki K, Saito N, Brouillard R
(1997)
Anthocyanin-aluminum and -gallium complexes in aqueous solution.
J Chem Soc Perkin Trans
2: 355-362
-
Everest AE, Hall AJ
(1921)
Anthocyanins and anthocyanidins: Part IV. Observations on (a) anthocyan colors in flowers and (b) the formation of anthocyans in plants.
Proc R Soc B
92: 150-162
-
Falciani F, Terao M, Goldwurm S, Ronchi A, Gatti A, Minoia C, Li Calzi M, Salmona M, Cazzaniga G, Garattini E
(1994)
Molybdenum (VI) salts convert the xanthene oxidoreductase apoprotein into the active enzyme in mouse L929 fibroblastic cells.
Biochem J
298: 69-77
-
Fassel VA
(1978)
Quantitative elemental analysis by plasma emission spectroscopy.
Science
202: 183-191[Abstract/Free Full Text]
-
Gupta UC, Lipsett J
(1981)
Molybdenum in soils, plants and amimals.
Adv Agron
34: 73-115
-
Heath SM, Southworthe D, D'Allura JA
(1997)
Localization of nickel in epidermal subsidiary cells of leaves of Thlaspi montanum var sikiyouense (Brassicaceae) using energy-dispersive X-ray microanalysis.
Int J Plant Sci
158: 184-188[CrossRef]
-
Heuwinkel H, Kirkby EA, Bot JL, Marschner H
(1992)
Phosphorous deficiency enhances molybdenum uptake by tomato plants.
Plant Nutr
15: 549-568
-
Hille R
(1996)
The mononuclear molybdenum enzymes.
Chem Rev
96: 2757-2816[CrossRef][ISI][Medline]
-
Kannan S, Ramani S
(1978)
Studies on molybdenum absorption and transport in bean and rice.
Plant Physiol
62: 179-181[Abstract/Free Full Text]
-
Karmian N, Cox FR
(1978)
Adsorption and extractability of molybdenum in relation to some chemical properties of soils.
Soil Sci Soc Am J
42: 757-761[Abstract/Free Full Text]
-
Klaper R, Frankel S, Barenbaum MR
(1996)
Anthocyanin content and UVB sensitivity in Brassica rapa.
Photochem Photobiol
63: 811-813
-
Kondo T, Yoshida K, Nakagawa A, Kawai T, Tamura H, Goto T
(1992)
Structural basis of blue-color development in flower petals from Commelina communis.
Nature
358: 515-518[CrossRef]
-
Kuper J, Palmer T, Mendel R, Schwarz G
(2000)
Mutations in the molybdenum cofactor biosynthetic protein Cnx1G from Arabidopsis thaliana define functions for molybdopterin binding, molybdenum insertion, and molybdenum cofactor stabilization.
Proc Natl Acad Sci USA
97: 6475-6480[Abstract/Free Full Text]
-
Küpper H, Zhao F, McGrath SP
(1999)
Cellular compartmentation of zinc in leaves of the hyperaccumulator Thlaspi caerulescens.
Plant Physiol
119: 305-311[Abstract/Free Full Text]
-
Kutzler FW, Natoli CR, Misemer DK, Doniach S, Hodgson KO
(1980)
Use of one-electron theory for the interpretation of near edge structure in K-shell x-ray absorption spectra of transition metal complexes.
J Chem Phys
73: 3274-3288[CrossRef]
-
Larsen PB, Degenhardt J, Tai C-Y, Stenzler LM, Howell SH, Kochian LV
(1998)
Aluminum-resistant Arabidopsis mutants that exhibit altered patterns of aluminum accumulation and organic acid release from roots.
Plant Physiol
117: 9-17[Abstract/Free Full Text]
-
Marschner H
(1995)
Mineral Nutrition of Higher Plants. Academic Press, San Diego
-
Mol J, Jenkins G, Schäfer E, Weiss D
(1996)
Signal perception, transduction, and gene expression involved in anthocyanin biosynthesis.
Crit Rev Plant Sci
15: 525-557
-
Müller A, Serain C
(2000)
Soluble molybdenum blues: "des Pudels Kern."
Accounts Chem Res
33: 2-10[CrossRef]
-
Murphy AS, Peer WA, Taiz L
(2000)
Regulation of auxin transport by aminopeptidases and endogenous flavonoids.
Planta
211: 315-324[CrossRef][ISI][Medline]
-
Mustre de Leon J, Rehr JJ, Zabinsky SI, Albers RC
(1991)
Ab initio curved-wave x-ray-absorption fine structure.
Phys Rev
B44: 4146-4156
-
Palmgren MG, Harper JF
(1999)
Pumping with plant P-type ATPases.
J Exp Bot
50: 883-893[Abstract]
-
Pickering IJ, Prince RC, George GN, Rauser WE, Wickramasinghe WA, Watson AA, Dameron CT, Dance IG, Fairlie DP, Salt DE
(1999)
X-ray absorption spectroscopy of cadmium phytochelatin and model systems.
Biochim Biophys Acta
1429: 351-364[CrossRef][Medline]
-
Pilon-Smits EAH, Hwang S, Lytle CM, Zhu Y, Tai JC, Bravo RC, Chen Y, Leustek T, Terry N
(1999)
Overexpression of ATP sulfurylase in Indian mustard leads to increased selenate uptake, reduction, and tolerance.
Plant Physiol
119: 123-132[Abstract/Free Full Text]
-
Rehr JJ, Mustre de Leon J, Zabinsky SI, Albers RC
(1991)
Theoretical x-ray absorption fine structure standards.
J Am Chem Soc
113: 5135-5140[CrossRef]
-
Rouser G, Fleisher S, Yamamoto A
(1970)
Two-dimensional thin layer chromatographic separation of polar lipids and determination of phospholipids by phosphorous analysis of spots.
Lipids
5: 494-496[ISI][Medline]
-
Sagner S, Kneer R, Wanner G, Cosson J-P, Deus-Neumann B, Zenk MH
(1998)
Hyperaccumulation, complexation and distribution of nickel in Sebertia acuminata.
Phytochemistry
47: 339-347[CrossRef][ISI][Medline]
-
Salt DE, Price RC, Pickering IJ, Raskin I
(1995)
Mechanisms of cadmium mobility and accumulation in Indian mustard.
Plant Physiol
109: 1427-1433[Abstract]
-
Seo M, Akaba S, Oritani T, Delarue M, Bellini C, Caboche M, Koshiba T
(1998)
Higher activity of an aldehyde oxidase in the auxin-overproducing superroot1 mutant of Arabidopsis thaliana.
Plant Physiol
116: 687-693[Abstract/Free Full Text]
-
Shibata K, Shibata Y, Kasiwagi I
(1919)
Studies on anthocyanins: color variation in anthocyanins.
J Am Chem Soc
41: 208-220[CrossRef]
-
Stallmeyer B, Schwarz G, Schulze J, Nerlich A, Kirsh J, Mendel RR
(1999)
The neurotransmitter receptor-anchoring protein gephyrin reconstitutes molybdenum cofactor biosynthesis in bacteria, plants and mammalian cells.
Proc Natl Acad Sci USA
96: 1333-1338[Abstract/Free Full Text]
-
Stark JM, Redente EF
(1990)
Copper fertilization to prevent molybdenosis on retorted oil shale disposal piles.
J Environ Qual
19: 50-504[Abstract/Free Full Text]
-
Steffens JC
(1990)
The heavy metal-binding peptides of plants.
Annu Rev Plant Physiol Mol Biol
41: 553-575[ISI]
-
Stout PR, Meagher WR, Pearson GA, Johnson CM
(1951)
Molybdenum nutrition of plant crops: I. The influence of phosphate and sulfate on the absorption of molybdenum from soils and solution cultures.
Plant Soil
3: 51-87
-
Takeda K, Kariuda M, Itoi H
(1985)
Blueing of sepal color of Hydrangea macrophylla.
Phytochemistry
24: 2251-2254[CrossRef]
-
Trlica MJ, Brown LF
(2000)
Reclamation of URAD molybdenum tailing: 20 years of monitoring change.
In
W Keammerer, ed, Proceedings of the High Altitude Revegetation Workshop, No. 14, Fort Collins, CO. Cooperative Extension Resource Center, Colorado State University, Fort Collins, CO, pp 82-133
-
Van Steveninck RFM, Van Steveninck ME
(1991)
Microanalysis.
In
JL Hall, C Hawes, eds, Electron Microscopy of Plant Cells. Acad Press, London, pp 415-455
-
von Wiren N, Sukhbinder K, Bansal S, Briat J-F, Khodr H, Shiori T, Leigh RA, Hider RC
(1999)
Nicotianamine chelates both FeIII and FeII: implications for metal transport in plants.
Plant Physiol
119: 1107-1114[Abstract/Free Full Text]
-
Yamasaki H
(1997)
A function of color.
Trends Plant Sci
2: 7-8
-
Zarcinas BA, Cartwright B, Spouncer LR
(1987)
Nitric acid digestion and multi-element analysis of plant material by inductively coupled plasma spectrometry.
Comm Soil Sci Plant Anal
18: 131-146
-
Zenk MH
(1996)
Heavy metal detoxification in higher plants: a review.
Gene
179: 21-30[CrossRef][ISI][Medline]
-
Zhou J, Goldsbrough PB
(1993)
An Arabidopsis gene with homology to glutathione S-transferase is regulated by ethylene.
Plant Mol Biol
22: 517-523[CrossRef][ISI][Medline]
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