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Plant Physiol, July 2000, Vol. 123, pp. 1087-1096
Characterization of Sulfate Assimilation in Marine Algae Focusing
on the Enzyme 5'-Adenylylsulfate Reductase1
Yu
Gao,*
Oscar M.E.
Schofield, and
Thomas
Leustek
Biotechnology Center for Agriculture and the Environment and
Institute of Marine and Coastal Sciences, Rutgers University, New
Brunswick, New Jersey 08901-8520
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ABSTRACT |
5'-Adenylylsulfate (APS) reductase was characterized in diverse
marine algae. A cDNA encoding APS reductase from Enteromorpha intestinalis (EAPR) was cloned by functional complementation of an Escherichia coli cysH mutant. The deduced amino acid
sequence shows high homology with APS reductase (APR) from flowering
plants. Based on the probable transit peptide cleavage site the mature protein is 45.7 kD. EAPR expressed as a His-tagged recombinant protein catalyzes reduced glutathione-dependent reduction of APS to
sulfite, exhibiting a specific activity of approximately 40 µmol
min 1 mg protein 1 and Michealis-Menten
kinetic constants of approximately 1.4 mM for reduced
glutathione and approximately 6.5 µM for APS. APR activity and expression were studied in relation to the production of
3-dimethylsulfoniopropionate (DMSP), a sulfonium compound produced by
many marine algae. A diverse group of DMSP-producing species showed
extremely high enzyme activity (up to 400 times that found in flowering
plants). Antibodies raised against a conserved peptide of APR strongly
cross-reacted with a protein of 45 kD in several chlorophytes but
insignificantly with chromophytes. In the chlorophyte Tetraselmis sp., APR activity varies significantly
during the culture cycle and does not follow the changes in cellular
DMSP content. However, a positive correlation was found between
cell-based APR activity and specific growth rate.
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INTRODUCTION |
S is an essential nutritional
element for plant growth and development. Available in the environment
primarily as sulfate it is imported into cells where it is incorporated
into organic molecules as sulfate (e.g. extracellular polysaccharides
like agar) or is reduced to sulfide before being incorporated as the thiol group of Cys. Cys serves as the central intermediate from which a
diversity of primary and secondary metabolites and coenzymes are
derived (Leustek and Saito, 1999 ). S-containing metabolites participate
in a variety of cellular processes, including disease resistance
(Alsher, 1989 ; Booth and Walker, 1997 ), tolerance to oxidation
(Lappartient and Touraine, 1997 ), heavy metals (Ruegsegger and Brunold,
1992 ; Schafer et al., 1997 ), water stress (Storey et al., 1993 ), and
developmental signaling (Bouarab et al., 1999 ).
Although S research in vascular plants has a 30-year history, only
recently has the process been studied at the molecular level. Molecular
and biochemical evidence has demonstrated significant differences in
the first enzyme-catalyzing sulfate reduction among vascular plants,
bacteria, and fungi. In all of the organisms, sulfate assimilation
begins with the enzyme ATP sulfurylase (EC 2.7.7.4) that catalyzes the
adenylation of sulfate to 5'-adenylylsulfate (APS). Adenylation is
necessary because sulfate is relatively unreactive. APS is then reduced
by APS reductase (APR; EC 1.8.99.-) in plants and some bacteria
(Bick and Leustek, 1997 ; Abola et al., 1999 ; Bick et al., 2000 ),
whereas in other bacteria and fungi APS is further phosphorylated at
the 3' position forming 3'-phospho-5'-adenylylsulfate (PAPS) before
being reduced by PAPS reductase. Plant APR is unique in that it is able
to use reduced glutathione (GSH) as a source of electrons. By contrast,
bacterial APR and PAPS reductase require the redox factors thioredoxin
(Trx) or glutaredoxin (Grx) as a source of electrons. The
GSH-dependency of plant APR is probably mediated through a carboxyl
terminal domain that functions as a Grx, which is lacking in the
bacterial and fungal enzymes. In flowering plants, APR is thought to be
a primary regulation point for the sulfate assimilation pathway
(Leustek and Saito, 1999 ).
Most of what is known about sulfate assimilation in plants is from
research on flowering plants. Little is known about the process in
algae. Marine algae metabolize S in unique ways, thus they likely have
special S requirements. For example, many produce large amounts of
sulfated extracellular polysaccharides like agar. Others produce and
accumulate in abundance a sulfonium compound known as
3-dimethylsulfoniopropionate (DMSP). DMSP synthesis is limited to
very few species of flowering plants (Hanson and Gage, 1996 ) but is
widespread among marine algae (Keller et al., 1989 ; Gröne, 1995 ).
It probably serves as a compatible intracellular osmolyte and can
accumulate to very high concentrations. Up to 0.5 M has
been reported for some species (Keller et al., 1989 ). DMSP is
synthesized from Met (Gage et al., 1997 ), therefore, it is dependent
ultimately on the activity of the sulfate assimilation pathway. There
is evidence that in some species DMSP synthesis is stimulated under
N-limiting conditions (Gröne and Kirst, 1992 ). DMSP is the
primary source for one of the most important biogenic gases in the
atmosphere, dimethylsulfide (DMS), accounting for nearly 50% of the
global biogenic S input into the atmosphere (Andreae and Raemdonck,
1983 ; Malin et al., 1992 ; Gröne, 1995 ).
As the first step toward understanding S metabolism in marine algae APR
was studied in a variety of species, and a cDNA encoding the enzyme was
cloned from the marine chlorophyte Enteromorpha intestinalis. The cDNA clone was used to express the enzyme for study and for production of a specific antibody. This antibody was used
to study the regulation of APR in relation to DMSP production in
another chlorophytic species Tetraselmis sp.
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RESULTS |
Cloning and Analysis of an APR cDNA from E.
intestinalis
Functional complementation of an Escherichia coli cysH
mutant with a cDNA library prepared from E. intestinalis
resulted in the isolation of approximately 100 positive clones after
screening 1 × 106 independent
transformants. Twenty-five clones were selected for sequence
analysis. All were found to be derived from the same gene but varied in
the length of their 5' and 3' ends. The longest clone, referred to as
EAPR, was 1,525 bp. It shows a continuous open reading frame
beginning from nucleotide 1 to the termination codon at 1,336 to 1,338. Therefore, the translation initiator is not possible to predict,
although a Met codon exists at position 68 to 70. An alignment of the
EAPR open reading frame with Arabidopsis APR3 (Fig.
1) shows that the two have a high level
of homology (56% identity, 63% similarity). The first 41 amino acids
of EAPR show the properties of a transit peptide for plastid
localization with a possible cleavage site at position 32 to 35 (LRAG) (Von Heijne et al., 1989 ). APR is known to be plastid
localized in flowering plants (Rotte, 1998 ). If the EAPR protein were
processed at the putative cleavage site (LRAG) the mature protein
would be 411 amino acids with a predicted mass of 45.7 kD.

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Figure 1.
Alignment of the deduced E. intestinalis EAPR amino acid sequence with Arabidopsis APR3
(AF01628). The sequence was aligned with PileUp program (Genetics
Computer Group, Madison, WI). Putative reductase-domain and
Grx-domain are positioned between amino acid numbers 36 to 116 and 117 to 446, respectively. Residues of important to the catalytic function
and tertiary structures are indicated with dots, asterisks, or
diamonds.
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The alignment in Figure 1 shows that EAPR contains all of the hallmarks
of plant APRs. The region from amino acids 83 to 310 is homologous with
the sulfate assimilatory APR and PAPS reductase of bacteria and fungi
(Berendt et al., 1995 ; Bick et al., 2000 ). This region has been defined
as the reductase domain of plant APR (Bick et al., 1998 ) and
includes a PP motif (indicated by dots), likely involved in
nucleotide binding, and a region conserved in all of the assimilatory
(P)APRs (indicated by asterisks) that is important for catalytic
activity (Berendt et al., 1995 ). The region from amino acids 311 to 445 shows homology with Trx and Grx including the active site sequence
(indicated with diamonds).
The genomic organization of the EAPR gene was studied in E. intestinalis by Southern blotting using the EAPR cDNA as a probe. A simple hybridization pattern was observed with all of the restriction enzymes tested (data not shown). This indicates that the sequence homologous to the EAPR cDNA likely exists as a single locus in the alga.
Characterization of the EAPR Product
E. coli JM96 strain (cysH mutant) is devoid
of the enzyme responsible for the reduction of sulfate to sulfite (PAPS
reductase). However, the strain expressing EAPR showed an APR activity
of approximately 2 × 10 3 units
mg 1 in the crude bacterial extract. Comparable
APR activity was observed with a deletion subclone of the EAPR cDNA
from which 249 bp was removed from the 5' end (SstI site,
indicated by an arrow in Fig. 1), indicating that the catalytic core of
the enzyme lies beyond the 84th amino acid.
Plant APRs are unable to function with electrons donated from sources
other than thiol compounds despite the existence of a C-terminal domain
with sequence homology to Trx. To determine what electron donor EAPR
protein uses during complementation, a test was performed using
E. coli strains with mutations in gshA ( -glutamyl-Cys
synthetase) or gshB (GSH synthetase) required for GSH synthesis, or
trxB (Trx reductase). The result indicates that EAPR cDNA clone was
able to complement a cysH mutant of E. coli that
also carries the trxB mutation (Fig. 2).
However, it was unable to complement the strains lacking GSH (E. coli strains carrying cysH and gshA or gshB), although
active EAPR protein was expressed in these bacterial strains as
demonstrated by the in vitro APR activity measurements. Consequently,
it is concluded that EAPR protein uses GSH, rather than Trx reductase,
for catalysis.

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Figure 2.
Complementation of E. coli cysH by
E. intestinalis APR requires GSH, but not Trx. wt refers to
the cysH strain carrying wild-type alleles for
trxB, gshA, and gshB. The others are
cysH strains carrying the designated mutation. The cultures
were incubated for 40 h at 30°C on M9 plate without Cys.
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The purified recombinant EAPR product has no PAPS reductase activity
and exhibited a specific APR activity of approximately 40 units
mg 1. This activity is significantly greater
than the reported activities of APR products from Arabidopsis (0.2-4
units mg 1; Bick et al., 1998 ) but similar to
APS reductase from Lemna (Suter et al., 2000 ). Moreover, the EAPR
protein is not sensitive to inactivation by freeze thawing and storage
in the thawed state as are Arabidopsis APRs, suggesting that the algal
enzyme is a much more active and robust form of APR. The kinetics of
the algal APR, however, is comparable with that reported for
Arabidopsis APRs with apparent Kms of 1.39 mM for GSH and 6.5 µM for APS.
A strong temperature dependence of the activity was observed for the
purified recombinant APR (Fig. 3). A
sharp break was found between 20°C to 25°C with an apparent
Ea, estimated from the slope of the
Arrhenius plot, of 10.1 kcal mol 1 for the
temperatures between 0°C to 20°C (slope = 5.098, r2 = 0.97, Fig. 3A). The
Q10 below 20°C was estimated to be 1.9 (slope = 0.0276, r2 = 0.97, Fig. 3B),
comparable with those found for many other biological processes (Berry
and Raison, 1981 ). Similar responses were observed for APR activity in
cell-free extracts of the phytoplankton Tetraselmis sp. and
Emiliania huxleyi (data not shown).

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Figure 3.
Temperature dependence of APR activity of purified
EAPR recombinant protein. A, Arrhenius plot; B, log transformation. APR
activity was determined as described in the "Materials and Methods"
at the temperatures indicated in the graph.
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Enzyme Activity and Antigenicity of APR from E. intestinalis and Several Marine Phytoplankton
APR and PAPS reductase activity were determined in several major
groups of marine algae, including three chlorophytes (E. intestinalis, Tetraselmis sp., and Dunaliella
salina), two diatoms (Thalassiosira weissflogii and
Thalassiosira oceanica), two prymnesiophytes (I. galbana and E. huxleyi), and one dinoflagellate
(Heterocapsa triquetra). These algae are from diverse
phylogenetic origins and have different capacities for DMSP production
(Table I). The results showed that most
of the species tested have high APR activities ranging from
approximately 100 up to 500 × 10 3 units
mg 1, except for the dinoflagellate species
(Table I). These activities are 100-fold greater than that from young
leaves of two species of flowering plants Arabidopsis and Indian
mustard (approximately 1 × 10 3 units
mg 1). No significant PAPS reductase activity
(< 1% of that for APR activity) was detected in any of the species
examined, indicating that APR is likely the primary route for sulfate
reduction in these organisms.
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Table I.
Comparison of APS reductase activity among different
plant species
Arabidopsis and all phytoplankton species were laboratory-grown
materials, whereas E. intestinalis were collected from the
field (see "Materials and Methods"). Species with no capacity of
DMSP synthesis were indicated with an asterisk. The range of activity
was determined from samples collected at different growth stage,
therefore reflecting the biological variations of the activity in
different species.
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The cross-reactivity of an APR-specific peptide antiserum (Fig. 1) was
tested against cell lysates from the algal species. The antibody
cross-reacted significantly only with the chlorophytic species. The
cross-reacting peptide in these species was approximately 45 kD (Fig.
4A), a size that is consistent with the
mass of the mature protein predicted from the EAPR cDNA clone. The
strongest cross reactivity was found with Tetraselmis sp.,
correlating with the extraordinarily high APR activity found in this
species (Table I), suggesting that this high activity is achieved in
part by high expression level of APR in this organism. Weak, specific cross-reactivity was observed with the prymnesiophyte, diatom, and
dinoflagellate species examined (Fig. 4B), suggesting that APR from
these species are divergent in the peptide sequence region (IAFSGAEDVA)
conserved among APR from flowering plants and green algae. Similar
species divergence in enzyme antigenicity has been observed for enzymes
involved in other assimilatory pathways in marine algae, such as
nitrate reductase and Gln synthetase (Gao et al., 1993 ; Robertson et
al., 1996 ). The current result also supports the idea of a diverse
evolutionary history for marine organisms.

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Figure 4.
Comparison of ARS reductase protein antigenicity
from marine algae. All of the lanes were loaded with equal amount of
protein (6 µg) except for Ulva pertusa (30 µg) and the
purified recombinant protein from pET-EAPR (2 ng). Odd-numbered lanes
are controls blotted with preimmune antiserum, whereas even-numbered
lanes are blotted with APR antiserum. A, EI (E. intestinalis): total activity was 120 pmol
min 1; UP (U. pertusa): total
activity was 16 pmol min 1; Tetra
(Tetraselmis sp.): total activity was 1,300 pmol
min 1; Dun (D. salina): total
activity was 390 pmol min 1; Pure APR (purified
recombinant protein from pET-EAPR): total activity was 90 pmol
min 1. B, Tetra (Tetraselmis sp.):
total activity was 1,300 pmol min 1; Iso
(I. galbana): total activity was 1,480 pmol
min 1; Ehux (E. huxleyi): total
activity was 1,500 pmol min 1; TW (T. weissflogii): total activity was 1,400 pmol
min 1; TO (T. oceanica): total
activity was 800 pmol min 1; HT (H. triquetra): total activity was 30 pmol
min 1.
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Regulation of APR Activity and DMSP Production in
Tetraselmis sp.
The high APR activity found in most marine algae examined in this
study may reflect the special S needs of these organisms. Most of the
species examined are known to produce large amounts of DMSP when N is
limiting in the environment (Gröne, 1995 ). DMSP synthesis may
ultimately be dependent on the activity of APR as it was demonstrated
earlier that this is the first enzyme involved in sulfate reduction in
these organisms and is most likely the regulation point in the sulfate
assimilation pathway of flowering plants (Brunold, 1981 ; Brunold and
Suter, 1984 ). As a first step toward understanding environmental
regulation of APR and its role in the production of DMSP in marine
organisms APR activity and intracellular DMSP contents were examined in
Tetraselmis sp. cultures grown with limiting or sufficient N
supplies. These conditions are known to alter the organism's ability
to synthesize DMSP.
Shown in Figure 5 is APR activity in
Tetraselmis sp. cells grown with abundant and limiting N
supply during a culture cycle. For both of the treatments the highest
activities were observed during the early log growth phase, the most
rapid growth stage of batch cultures. As the cultures became depleted
in N (d 3-5), APR activity decreased to <40% and reached a 10% to
25% level when the cultures reached stationary phase. For the abundant
N treatment the pattern for cell-based APR activity was similar to that
based on cellular protein content in these cultures (Fig. 5A, compare
white circles with black circles). In contrast, APR activities in the
cells grown with limited N supply, when expressed on cellular protein
basis, did not change significantly during the culture cycle (Fig. 5B,
compare black squares with white squares), although slightly higher
activities were observed during the mid-log growth phase of these
cells. The APR activities were comparable with those found in the early
log growth-phased cells with abundant N supply. When the APR activity
was expressed on a per-cell basis, the pattern of the activity change
was similar to that found for cultures grown with abundant N supply
with maximal activity during the rapid growth stage and low activity
after N was depleted from the cultures. This result may reflect the
organisms' ability to quickly mobilize cellular proteins after
encountering N shortage. Since APR activity on protein basis was
maintained through out the culture cycle, the results suggest that it
may be spared from deactivation or proteolysis. Immunoblot analysis
revealed that the changes in APR activity observed here are paralleled
by changes in APR protein abundance (data not shown).

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Figure 5.
APR activity from Tetraselmis sp.
cultures grown with abundant N supply (A) and limited N supply (B).
Dotted lines indicate the nitrate level in the cultures. Dash lines
with small white circles or white squares are growth curves of the
cultures indicated by the cell densities of the cultures. Black circles
or squares represent APR activities normalized to cellular protein
content, whereas white circles or squares represent APR activities
based on cells. Each data point was the average of six measurements
from four independent cultures.
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It is interesting that under both of the growth conditions, APR
activity on cell basis began declining when medium nitrate was reduced
to approximately 35 µM and reached a plateau 1 d
after the depletion of N from the media, suggesting a coordinated
regulation between sulfate and nitrate assimilation. Moreover, the
cell-based APR activity in cells grown with limited N supply plateaued,
upon the depletion of nitrate from media, at a level twice that in cells grown with abundant N supply.
Given the observation that cell-based APR activity is inversely
correlated with the growth curve and N availability under both of the
growth conditions, a close coupling of grow rate and cell-based APR
activity was hypothesized. Comparison of specific growth rate (µ)
with cell-based APR activity (Fig. 6)
further support the hypothesis. The result suggests that cell-based APR activity can be used as an index for estimating growth rate and thus
productivity as well as the N-nutrition state of the cells.

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Figure 6.
Correlation of APR activity and specific growth
rate (µ). White circles were data points from cultures grown with
abundant N supply, whereas white squares were data points from cultures
grown with limited N supply. Each data point represents the average of
six measurements from four independent cultures.
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Intracellular DMSP content in Tetraselmis sp. cells grown
under limited or abundant N supply conditions is illustrated in Figure
7. Both of the cultures exhibited
similar intracellular DMSP content (approximately 15 fmol
cell 1) when N was present in the medium.
However, the increase in DMSP content after N was depleted was much
more rapid in cells grown with limited N supply than those grown with
abundant N supply. Further, after reaching stationary phase, the
N-limited cultures attained a higher intracellular DMSP content
compared with cells grown with abundant N. The changes in cellular DMSP
content (Fig. 7, solid lines) did not correlate with the changes in APR
activity, suggesting that APR does not directly limit or regulate DMSP
synthesis and that the synthesis of DMSP may be partly or entirely
supported by intracellular resources of assimilated S.

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Figure 7.
APR activity and intracellular DMSP content during
a growth cycle in batch cultures of Tetraselmis sp. grown
under N-sufficient supply (A) and N-limited supply (B) conditions.
Cell-based APR activity is indicated as the dashed lines, whereas
intracellular DMSP content is indicated as the solid lines with white
circles or squares. Dotted lines indicate the nitrate level in the
cultures. Each data point was the average of six measurements from four
independent cultures.
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DISCUSSION |
S metabolism is important to marine algae in that they produce and
accumulate to high concentrations S compounds that most terrestrial
plants do not produce. Unlike most terrestrial crop plants, many marine
algae live in habitats that are characterized by limited N and abundant
S supply. The concentration of sulfate in seawater is approximately 40 mM (Pickard and Emery, 1988 ). In response to this
environment, many have evolved the ability to produce DMSP, a
functional analog of the N-containing osmolyte Gly betaine. In those
species that accumulate it, DMSP is likely a major sink for assimilated
S in addition to protein, especially when N is not available. The
ability to synthesize DMSP may play a critical role in the survival of
these organisms in their environmental niches.
In the present study, as the first attempt to understand sulfate
assimilation in marine organisms, a cDNA (EAPR) from E. intestinalis was cloned. The result indicates the
structural and functional similarities between algal APR from marine
chlorophyte algae and flowering plants. In addition, the result
demonstrated the use of functional complementation approach as a
powerful tool in investigating molecular and biochemical features of
processes in marine algae.
Examination of temperature response of APR activity showed that the
enzyme activity is strongly temperature dependent with a maximal
activity at 20°C to 25°C. A sharp break at low temperatures (<30°C) for enzyme activity has only been observed for nitrate reductase (EC 1.6.6.1) previously, the first enzyme involved in nitrate
reduction (Gao et al., 1993 ), but not for other enzymes that are also
important in assimilatory processes in plants, e.g. RuBP carboxylase,
PEPC Kinase, Gln sythetase, and Glu dehydrogenase (Ahmed et al., 1977 ;
Descolas-Gros and De Billy, 1987 ; Cabello-Pasini, 1996 ; Robertson et
al., 1996 ). However, unlike APR where a similar pattern was seen
in both of the chlorophyte and chromophyte, a sharp break at low
temperatures (15°C) for nitrate reductase was only observed in
chromophytes. The chlorophytic nitrate reductase activity was linear up
to 35°C (Gao et al., 2000 ). Such large differences in temperature
dependence for important assimilatory enzymes may have significant
impact on the geographic distribution and seasonal abundance of these
organisms in the marine environment.
A significant correlation between the specific growth rate and APR
activity on a per cell basis was found in Tetraselmis sp. cultures. Together with the observation that APR activity declines as N
is depleted from the medium in cells grown with both of the limiting
and the abundant N supply, the results suggest a coordinated regulation
between sulfate and nitrate assimilation. Regulatory interactions
between assimilatory S and N reduction have been observed in previous
studies with various flowering plants (Reuveny et al., 1980 ;
Neuenschwander et al., 1990 ; Brunold, 1993 ; Prosser et al., 1997 ; Lee,
1998 ; Koprivova et al., 2000 ). These interactions were thought to
reflect a mechanism to coordinate and balance the flow of the two
essential elements (S and N) into protein (Reuveny et al., 1980 ;
Brunold and Suter, 1984 ). The previous studies showed that low nitrate
concentration causes a drastic decrease in the specific APR activity
after 24 h (Brunold and Suter, 1984 ) as well as the influx of
sulfate into cells (Clarkson et al., 1989 ) in flowering plants. The
reduction in APR is due to a decrease in the steady-state level of mRNA
and protein (Lee, 1998 ). These results are consistent with our finding
that high level of APR activity in the marine alga
Tetraselmis sp. was observed when nitrate is plentiful. It
is interesting that cell-based APS activity in cells grown with limited
N supply plateaued at a level twice that found in cells grown with
abundant N supply. One possible explanation for this observation is
that APR is spared from proteolysis relative to other proteins in these cells.
The experiments did not reveal a direct correlation between APR
activity and DMSP production as indicated by the intracellular DMSP
content. This may be explained in part by the possibility that
intracellular DMSP content does not represent accurately the rate of
DMSP production. It also, in part, suggests an ability of the alga to
mobilize intracellular S resources under the stress of N shortage. In
this regard, the extraordinarily high APR activity, compared with
flowering plants, may be of significance. Thus, whereas APR does not
directly limit or regulate DMSP synthesis, its high activity may
reflect a process for building an intracellular pool of reduced S,
which could serve as a resource for support of DMSP biosynthesis when
needed. To obtain a comprehensive understanding of the role of APR in
DMSP production and its regulation in the marine organisms that have
special S needs, further studies are required.
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MATERIALS AND METHODS |
Algal Materials and Growth Conditions
Enteromorpha intestinalis and Ulva
pertusa were collected in early summer at the intertidal zone
of the Gateway National Recreation Area at Sandy Hook, New Jersey (U.S.
Department of the Interior collection permit no. SHU-98-03). The
tissue was rinsed with ultrapure water and frozen immediately with dry
ice. Frozen samples were stored at 80°C until use. Phytoplankton
species (Tetraselmis species, CCMP897; Dunaliella
salina, ATCC30861; Isochrysis galbana, CCMP1323; Emiliania huxleyi, CCMP1299,
Thalassiosira weissflogii CCMP1336, Thalassiosira
oceanica CCMP1005, and Heterocapsa triquetra CCMP449) were grown in f/2-enriched seawater medium (Guillard, 1975 ) at 19°C on a 12-h:12-h light:dark cycle at 200 µmol
m 1 s 1, using NO3
as the sole N source. Artificial seawater medium (Sigma S-9883) with
f/2-enrichments was used in the experiments assessing the role of APR
in relation to DMSP production. The species with CCMP designations were
obtained from the Provasoli-Guillard National Center for Culture of
Marine Phytoplankton (Bigelow Laboratory for Ocean Sciences, West
Boothbay Harbor, ME). D. salina was obtained from the
American Type Culture Collection (Fairfax, VA). All of the samples for
analysis were harvested at noon by centrifugation, frozen in liquid
N2, and stored at 80°C.
Construction of a cDNA Library from E. intestinalis and Cloning of EAPR
Total RNA was prepared as follows. Twenty-three grams (fresh
weight) of frozen E. intestinalis was ground into powder
with liquid N2 then mixed with 60 mL of extraction buffer
containing 4 M guanidine thiocyanate, 25 mM
sodium citrate (pH 7.0), 0.5% (w/v) sarcosyl, and 0.7% (v/v)
-mercaptoethanol. Then 0.1 volume of 2 M sodium acetate
(pH 5.0) was added. The mixture was extracted with 40 mL of phenol
(diethyl pyrocarbonate-water saturated) followed by an addition of 8 mL
of chloroform:isoamyl alcohol (49:1). The mixture was centrifuged at
5,000g for 20 min at 4°C. The upper aqueous phase was
transferred into a clean tube and re-extracted with 40 mL of
chloroform:isoamyl alcohol (49:1). Total RNA was precipitated with an
equal volume of ice-cold isopropanol. The RNA pellet was dissolved in
20 mL of extraction buffer and reprecipitated with 2 volumes of
ethanol. The cDNA library was constructed in TriplEx
using the EcoRI (5') and XbaI (3')
cloning sites. The library contained 1.2 × 106
independent clones.
The -phage cDNA library from E. intestinalis was
converted to plasmid form by mass excission according to the
manufacturer's instruction (CLONTECH Laboratories, Palo Alto, CA). The
resulting plasmid library was then used to screen for clones that
complement the Cys requirement of Escherichia
coli strain JM96 (cysH), following the procedure
described by Setya et al. (1996) . JM96 was provided by the Coli Genetic
Stock Center (Yale University, New Haven, CT).
DNA Sequencing and Nucleic Acid-Blot Analysis
DNA sequencing was carried out on both of the strands using
plasmid primer sites with the original EAPR cDNA clone as well as
deletion subclones on the parent vectors, using a DNA sequencer (model
373, Applied Biosystems, Foster City, CA).
For Southern blotting, E. intestinalis genomic DNA was
isolated from materials obtained as described earlier (see "Algal
Materials and Growth Conditions"). Four grams of tissue (frash
weight) was first pulverized in liquid N2 and then mixed
with 23 mL of preheated (65°C) extraction buffer containing 100 mM Tris [Tris(hydroxymethyl)-aminomethane]-HCl (pH 8.0),
500 mM NaCl, 8.3 mM NaOH, 1.25% (w/v) SDS, and
0.38% (w/v) sodium bisulfite. The mixture was then incubated at 65°C for 15 min, and 7 mL of 5 M potassium acetate was added.
After standing on ice for 20 min, the mixture was centrifuged at
4,000g for 10 min. The DNA in the supernatant was
precipitated by adding 0.7 volume of prechilled isopropanol and washed
with 70% (v/v) ethanol. The DNA pellet was then resuspended in
T5E buffer (50 mM Tris-HCl, pH 8.0, and 10 mM
EDTA), containing DNase-free RNase A (final concentration of 20 µg/mL) and incubated at 37°C for approximately 1 h. The DNA
was then subjected to buffer-saturated phenol/chloroform extraction
twice and reprecipitated with ethanol. The final DNA pellet was
resuspended in TE buffer (10 mM Tris HCl, pH 8.0, and 1 mM EDTA) and used for Southern blotting.
After digestion with the appropriate restriction enzymes, the
genomic DNA were electrophoresed in 0.8% (v/v) agarose gels and
transferred onto Zeta-Probe membrane (Bio-Rad Laboratories, Hercules,
CA). The DNA probe, labeled by the random primer method (Life
Technologies/Gibco-BRL, Cleveland) using
[ -32P]dCTP, was made from the full-length cDNA of
EAPR1. Hybridization was performed in 2× SSC containing 7% (w/v) SDS
at 50°C.
Construction of Expression Plasmids and Purification
of Recombinant EAPR
The EAPR cDNA, after removing 189 nucleotides from the 5' end,
was sucloned as a 1,360-bp NotI fragment into pET-30b
(Novagen, Madison, WI). The plasmid, pET-EAPR was transformed into
BL21(DE3) plysS. Transformants were grown at 37°C to an optical
density of approximately 0.4 at 600 nm and then expression was induced with 1 mM isopropyl- -D-thiogalactoside for
2 h before harvesting. Because of the association of a 55-amino
acid-long fragment (which contains His-tag, thrombin, S-tag, and
enterokinase cleavage site) with the recombinant EAPR enzyme, it is
estimated that the resulting polypeptide is 466 amino acids with a
predicted mass of approximately 52 kD.
The purification of recombinant EAPR enzyme was conducted using
Ni-agarose (TALON, CLONTECH Laboratories). All of the procedures were
carried out at room temperature (22°C-25°C). The bacterial cell
pellet from a 100-mL culture was lysed by sonication in 10 mL of 20 mM Tris-HCl, pH 8.0, and 100 mM NaCl. The
lysate was centrifuged at 12,000g for 10 min, and the
supernatant was incubated with 1.5 mL of TALON resin for 30 min on a
rotating shaker. The resin was washed with 5 volumes of lysis buffer
and then packed into a disposable column. The column was further washed
with 5 volumes of lysis buffer containing 10 mM imidazole.
EAPR protein was eluted with lysis buffer containing 50 mM
imidazole, then the buffer was replaced with 100 mM
Tris-HCl, pH 8.5 containing 1 mM EDTA using
microconcentrator unit (Microcon-30, Millipore, Bedford, MA). The pure
protein was stored at 80°C.
The EAPR cDNA was also subcloned as a 1,310-bp (SstI and
HindIII) fragment into pET-30a. The plasmid was
transformed into BL21(DE3) plysS and induced only for APS activity determination.
(P)APS Reductase Activity and Protein Assays
Algal cells were harvested, frozen in liquid N2, and
stored in 70°C before analysis. Algal cells were lysed in 100 mM Tris-HCl, pH 8.5, 1 mM EDTA, and the
supernatant collected after centrifugation at 14,000g
for 15 min. Microalgae were lysed by sonication. Macroalgae were ground
to a fine powder in liquid N2. Enzyme activities were measured as described by Bick et al. (1998) using GSH (1 mM) as the electron donor and [35S]APS
(approximately 500 Bq nmol 1) as subtrate. One
unit of enzyme activity is defined as micromoles of product formed per
minute. Apparent Km values were calculated by direct-fit to the Michaelis-Menten equation using Sigma-Plot (Jandel
Scientific, version 5.0, SPSS, Inc., Chicago). Protein was
estimated by Bradford assay (Bradford, 1979 ) using a bovine serum
albumin standard.
Antibody Preparation and Immunoblotting
Antibodies were prepared in rabbits by Biosynthesis
(Lewisville, TX) using the MAP peptide method. A peptide sequence
conserved among APRs from flowering plants and EAPR was chosen for the
procedure (NH2-IAFSGAEDVA).
Immunoblotting was carried out as described by Wang et al. (1993) . The
antibody was used at a dilution of 1:5,000. The secondary antibody was
horseradish peroxidase-linked goat anti-rabbit diluted 1:10,000. The
immune complexes were detected with the Renaissance Kit (DuPont NEN,
Inc., Boston) and quantified with a densitometric video camera
(model: Datavison 261 from Fernon Electronic Imaging, St. Michaels, MD)
and the software NIH Image (version 1.0) provided by the National
Institutes of Health (Bethesda, MD).
DMSP Measurements
DMSP content was measured indirectly as DMS produced after
alkaline treatment of algal cells (White, 1982 ). Algal cells were collected by centrifugation and resuspended in 100 mM
Tris-HCl, pH 8.0. Five to 10 µL of the cell suspensions was placed
onto filter papers (8-mm diameter disc). The filter papers were placed into 2-mL glass vials containing 0.4 mL of 25% (w/v) NaOH and capped
with Teflon-coated septum. The vials were incubated at room temperature
for 4 h and then placed at 4°C overnight. DMS produced in the
head space of the vials was removed with a gas-tight syringe and
measured by gas chromatography on a Poraplot Q, fused silica column
(10 × 0.53 mm, Chrompack, The Netherlands) using a
Shimadzu GC-17A gas chromatograph outfitted with a flame ionization detector.
 |
ACKNOWLEDGMENTS |
We would like to thank Dr. Julie-Ann Bick for numerous helpful
discussions and technical assistance and Dr. John Reinfielder (Rutgers Environmental Sciences Department) for generously sharing his
culture collection.
 |
FOOTNOTES |
Received January 10, 2000; accepted March 10, 2000.
1
This work was supported by the National Science
Foundation (grant nos. IBN-9601146 and IBN-9817594), the Office of
Naval Research (grant no. N00014-96-0212 to T.L.), and the
Agricultural Research Service cooperative agreement (grant no.
58-6435-6-028 to O.M.E.S.).
*
Corresponding author; e-mail gao{at}aesop.rutgers.edu; fax
732-932-0312.
 |
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