Previous Article | Next Article 
Appl Environ Microbiol, February 1998, p. 569-574, Vol. 64, No. 2
0099-2240/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
Reverse Transcription-PCR Analysis of the
Regulation of the Manganese Peroxidase Gene Family
Jessica M.
Gettemy,
Biao
Ma,
Margaret
Alic, and
Michael H.
Gold*
Department of Biochemistry and Molecular
Biology, Oregon Graduate Institute of Science and
Technology, Portland, Oregon 97291-1000
Received 21 July 1997/Accepted 24 November 1997
 |
ABSTRACT |
Manganese peroxidase (MnP) gene expression in the lignin-degrading
fungus Phanerochaete chrysosporium is regulated by nutrient nitrogen levels and by Mn(II), the substrate for the enzyme, as well as
by heat shock and other factors. Reverse transcription-PCR (RT-PCR) of
total RNA can distinguish the mRNAs of each of the three sequenced
P. chrysosporium mnp genes, i.e., mnp1,
mnp2, and mnp3. Quantitative RT-PCR
demonstrates that each of the three transcripts is present at a similar
low basal level in nitrogen-sufficient cultures, with or without Mn,
and in nitrogen-limited cultures lacking Mn. However, in 5-day-old,
nitrogen-limited, stationary cultures supplemented with 180 µM Mn,
the levels of the mnp1 and mnp2 transcripts
increased approximately 100- and 1,700-fold, respectively, over basal
levels. In contrast, under these conditions, the level of the
mnp3 transcript did not increase significantly over the
basal level. Quantitative RT-PCR of total RNA extracted from
nitrogen-deficient, Mn-supplemented cultures on days 2 through 7 demonstrates that whereas the mnp1 transcript was present
at relatively low levels on days 3 through 7, the mnp2
transcript level peaked on day 5 and the mnp3 transcript
level peaked on day 3. Comparison of total RNA extracted on day 5 from
nitrogen-deficient, Mn-supplemented stationary and agitated cultures
indicates that in stationary cultures, mnp2 was the major
expressed mnp gene, whereas in large agitated cultures,
mnp1 was the major expressed mnp gene.
 |
INTRODUCTION |
The white rot basidiomycete fungus
Phanerochaete chrysosporium has been studied extensively for
its ability to degrade lignin (19, 26) and a wide variety of
aromatic pollutants (23, 25, 47). Two families of
peroxidases, lignin peroxidase (LiP) and manganese peroxidase (MnP),
and an H2O2-generating system are the major
components of the extracellular lignin-degrading system of this
organism (19, 22, 26). P. chrysosporium MnP isozyme 1 is a well-characterized
H2O2-requiring heme glycoprotein with an
Mr of ~46,000 (16, 19, 22, 48, 49).
The enzyme oxidizes Mn2+ to Mn3+; the latter,
complexed with an organic acid chelator such as oxalate, which is
secreted by the fungus, oxidizes the terminal phenolic substrate
(16, 29, 30, 50) and also possibly nonphenolic substituents
via a radical mediator (2, 51). X-Ray crystallographic
(44) and site-directed mutagenesis (28, 31)
studies have defined the Mn-binding site of MnP.
MnP occurs as a series of isozymes encoded by a family of closely
related genes, and the sequences of cDNA (35, 37, 39, 40)
and genomic clones (1, 18, 35) of three different mnp genes from P. chrysosporium have been
determined. MnP expression is regulated at the level of gene
transcription by the depletion of nutrient nitrogen (40). In
addition, MnP activity is dependent on the presence of Mn2+
in the culture medium (5, 10), and mnp gene
transcription is regulated by Mn2+ (9, 10, 14,
17). To date, this is the only system of Mn regulation of gene
transcription to be studied at the molecular level. MnP also is
regulated at the level of gene transcription by heat shock
(11), H2O2, and other chemical
stresses (33). However, there has been no previous study on
the differential regulation of mnp gene transcription by Mn,
nitrogen limitation, or culture agitation in defined medium.
Reverse transcription-PCR (RT-PCR) has facilitated the analysis of
differential expression between and within families of genes involved
in lignocellulose degradation, both in liquid cultures (6-8, 12,
41, 43, 45) and in pollutant-contaminated soil (3, 4,
32). In addition to its ability to distinguish among very similar
mRNAs, RT-PCR has been shown to be 103- to
104-fold more sensitive than Northern blotting techniques
(15, 42).
In this study, RT-PCR was used to further our investigations of
mnp gene expression with greater sensitivity and specificity than was possible with our previous northern blot analyses (9-11, 33). Competitive RT-PCR was used to compare differential
regulation by Mn of the transcription of genes encoding three MnP
isozymes from P. chrysosporium, i.e., mnp1,
mnp2, and mnp3, in stationary and agitated
cultures.
 |
MATERIALS AND METHODS |
Culture conditions.
The P. chrysosporium
wild-type strain OGC101 (ATCC 201542), a derivative of BKM-F-1767, was
maintained as described previously (20). Stationary cultures
were grown at 37°C from conidial inocula in 20 ml of medium in 250-ml
Erlenmeyer flasks (10, 27). The medium contained mineral
salts with trace elements lacking Mn, with 2% glucose as the carbon
source, 1.2 mM (limiting nitrogen) or 12 mM (sufficient nitrogen)
ammonium tartrate, and 20 mM sodium-2,2-dimethyl succinate (pH 4.5) as
the buffer (10, 27). The cultures were grown in the presence
or absence of 180 µM Mn as indicated. Cultures were incubated under
air for 2 days and purged on day 3 with 100% O2 for 10 min. For the temporal expression experiments, the cultures were
incubated under air for 2 days, after which they were purged daily with
100% O2 for 10 min. Agitated cultures were grown at 28°C
from an inoculum of mycelial fragments in 1 liter of medium in 2-liter
Erlenmeyer flasks, as described previously (16, 21). The
medium was as above, except that it contained 6× trace elements (50), yielding a final Mn concentration of 180 µM, and
0.1% Tween 80. Benzyl alcohol (3 mM) was added on day 3 (50). The cultures were incubated under air for 3 days, then
purged daily with 100% O2, and harvested on day 5.
RNA extraction.
The mycelia from 20-ml liquid cultures
(~100 mg/culture) were filtered through Miracloth (Calbiochem), dried
between layers of paper towel, frozen rapidly in liquid nitrogen, and
stored at
80°C. The frozen mycelia from each of two flasks were
separately homogenized with acid-washed glass beads (1 gm) in a
mini-bead beater in the presence of 580 µl of guanidinium thiocyanate
(Fluka, Inc.) denaturing solution (24), together with 580 µl of diethylpyrocarbonate (DEPC)-treated water-saturated phenol
(U.S. Biochemical) and 100 µl of 2 M sodium acetate (pH 4). The
supernatants were extracted once with chloroform and once with
phenol-chloroform, and the RNA was precipitated with isopropanol. An
overnight 4 M LiCl wash of the precipitated RNA aided in the removal of
carbohydrates, genomic DNA, and large rRNA. The precipitated RNA was
washed with 75% ethanol and solubilized in DEPC-treated water. The
absorbance was measured at 260 and 280 nm to quantitate the RNA (~40
µg/culture).
RT-PCR.
RT-PCR amplifications were performed for RNA samples
from each culture for the mnp1, mnp2, and
mnp3 mRNAs. As a control, RT-PCRs also were carried out for
the gpd mRNA, encoding glyceraldehyde-3-phosphate dehydrogenase (36). Oligonucleotide primers and probes were synthesized at the Oregon Regional Primate Research Center, Beaverton, Oreg. For the annealing reaction (10 µl in DEPC-treated water), 2 µg of total RNA and 3 pmol each of a conserved mnp 3'
primer and a 3' primer from the gpd coding region (Table
1) were heated at 70°C for 5 min and
then cooled slowly to 30°C. The RT reaction (25 µl) was initiated
by the addition of 100 U of Moloney murine leukemia virus reverse
transcriptase and buffer (GIBCO BRL) and 28 U of RNasin (Promega
Biotech) in 10 mM dithiothreitol-1 mM deoxynucleoside triphosphates
(U.S. Biochemical) (13), followed by extensions at 42°C
for 60 min and 52°C for 30 min. Following the RT reaction, the volume
was increased to 100 µl with DEPC-treated water. PCR mixtures (50 µl) contained 1 µl of cDNA, 1 U of Deep Vent polymerase and buffer
(New England Biolabs), 30 pmol each of the appropriate gene-specific 5'
primer and the conserved mnp or gpd 3' primer
(Table 1), and deoxynucleoside triphosphates to a final concentration
of 400 µM. The PCR temperature program was 94°C for 6 min, 54°C
for 2 min, and 72°C for 40 min for 1 cycle followed by 94°C for 1 min, 54°C for 2 min, and 72°C for 5 min for 35 cycles and with a
final 15-min extension at 72°C (43). Following
amplification, 5 µl of each PCR product was analyzed by
electrophoresis in a 1.5% agarose gel and stained with ethidium
bromide. The gels were visualized with UV light and photographed.
Competitive RT-PCR.
Competitive RT-PCRs were conducted as
above, except that a series of known concentrations of plasmids
containing the full-length genomic sequences for each gene (1, 18,
35, 36) were added as competitive templates to the appropriate
amplification reaction mixtures (15). Introns within the
competitive templates allowed the cDNAs and the genomic products to be
separated on agarose gels (Fig. 1). For
quantitation, photographs of the ethidium bromide-stained gels were
scanned and densitometry was performed using IPLab Gel software (Signal
Analytics Corp.). The transcript concentrations were estimated by
determining the concentration of competitive DNA at which the
intensities of the gDNA and cDNA targets (PCR fragments) were equal,
taking into account the increased ethidium bromide staining of the
larger gDNA target (15). Since transcript concentrations
were expressed as picograms per 20 ng of total RNA, adjustments for the
relative molar concentrations of the competitive genomic DNAs and the
cDNAs and their respective targets were also made.

View larger version (15K):
[in this window]
[in a new window]
|
FIG. 1.
Strategy for PCR amplification of three mnp
genes and the gpd gene from P. chrysosporium. The
ATG translation start codons and the TAA stop codons are indicated.
Solid boxes represent introns. Positions of the upstream primers ( ),
downstream primers ( ) and gene-specific oligonucleotide probes ( )
are indicated.
|
|
Southern blot analysis.
Southern blots of the mnp
PCR products were analyzed with gene-specific oligonucleotide probes
(Table 1) to ensure the specificity of each primer pair for its target
sequence. PCRs were performed as described above, with each of the
mnp primer pairs and P. chrysosporium genomic DNA
(100 ng) as the template. RT-PCRs were performed as described above,
with each of the mnp primer pairs and total RNA extracted
from 5-day-old, nitrogen-limited, Mn-sufficient cultures. A 5-µl
portion of each PCR product and 500 pg each of the
EcoRI-linearized mnp genomic plasmids were
separated on a 1.5% agarose gel and stained with ethidium bromide. The
DNA was transferred to Magna NT membranes (Micron Separations, Inc.).
Identical blots were hybridized with oligonucleotide probes
corresponding to each mnp gene (Table 1). The probes (10 pmol) were end labeled with [
-32P]dATP (Andotek Life
Sciences), using T4 polynucleotide kinase (New England Biolabs, Inc.).
Hybridizations were carried out at 55°C in 5× SSC (1× SSC is 0.15 M
NaCl plus 0.015 M sodium citrate)-1% sodium dodecyl sulfate-5×
Denhardt's solution-25 mM sodium phosphate (pH 7.0)-100 µg of
herring sperm DNA per ml. The blots were washed in 6× SSC-1% sodium
dodecyl sulfate three times at room temperature for 5 min each followed
by twice at 50°C for 2 min each. The washed blots were exposed to
Kodak XAR film.
 |
RESULTS |
Expression of individual mnp transcripts in stationary
cultures.
Nitrogen-sufficient and nitrogen-limited stationary
cultures of P. chrysosporium OGC101 were grown at 37°C in
the absence of Mn and in the presence of 180 µM Mn. On day 5, the
cultures were harvested separately and the RNA was extracted. By using RT-PCR with mnp gene-specific primer pairs, the three
mnp transcripts of the predicted sizes (Table 1; Fig. 1)
were detected under all conditions tested. Southern blot hybridizations
with mnp gene-specific oligonucleotide probes (Table 1)
confirmed the identities of the PCR products and the specificities of
the PCR primer pairs. No genomic DNA contamination was detectable among
the PCR products derived from total RNA (Fig.
2).

View larger version (29K):
[in this window]
[in a new window]
|
FIG. 2.
Southern blots of mnp genomic plasmids, PCR
amplification of P. chrysosporium genomic DNA, and RT-PCR of
total RNA extracted from 5-day-old, nitrogen-limited, Mn-sufficient
cultures probed with mnp gene-specific oligonucleotide
probes. (A) Ethidium bromide-stained agarose gel. (B) Southern blot of
the gel in panel A, probed with the mnp1-specific
oligonucleotide. (C) Southern blot of the gel in panel A, probed with
the mnp2-specific oligonucleotide. (D) Southern blot of the
gel in panel A, probed with the mnp3-specific
oligonucleotide. Lanes: 1, molecular size markers, indicated on the
left of panel A in base pairs; 2 to 4, EcoRI-linearized
plasmids containing the mnp1 gene (lane 2), the
mnp2 gene (lane 3), or the mnp3 gene (lane 4); 5 to 7, PCR amplification of P. chrysosporium genomic DNA with
the conserved mnp downstream primer and the mnp1
(lane 5), mnp2 (lane 6), and mnp3 (lane 7)
upstream primers; 8 to 10, RT-PCR of total RNA with the conserved
mnp downstream primer and the mnp1 (lane 8),
mnp2 (lane 9), and mnp3 (lane 10) upstream
primers. Sizes (in base pairs) of the probed plasmids and genomic and
cDNA amplification products are indicated on the left of panel B
through D. Oligonucleotide probes and primers are listed in Table 1.
|
|
Competitive RT-PCR was used to quantitate the three
mnp
transcripts derived from duplicate cultures grown under each set of
conditions. The RT reactions were as above, except that a 3'
gpd primer was included in addition to the conserved
mnp 3' primer
(Table
1). For each of the four cDNA
templates, eight identical
PCR mixtures were spiked with serial
dilutions of the appropriate
competitive genomic template. A ninth
reaction mixture lacked
cDNA and was used as a control. The PCR
products were analyzed
by gel electrophoresis and ethidium bromide
staining. The initial
concentration of each cDNA was determined by
observing the dilution
of the genomic template at which the genomic and
cDNA products
were equivalent (Fig.
3A).
After adjustments for the relative
intensities of the larger genomic
PCR products and for the relative
molar concentrations of the genomic
plasmids, the gDNA targets,
the cDNAs, and the cDNA targets, the
mnp transcript concentrations
ranged from 10
3
to 25 pg/20 ng of total RNA. The
gpd transcript
concentration
was between 1 and 2 pg/20 ng of total RNA under all
conditions
tested (Fig.
3B and C). The transcript concentrations in
RNAs
extracted from two identical cultures varied by less than 25%.
The PCR target concentrations from two parallel PCRs of RNA from
the
same culture were essentially identical. The results with
stationary
cultures in Fig.
3B and C demonstrate that under nitrogen-sufficient
conditions, the concentrations of the
mnp transcripts were
unaffected
by the presence of Mn, with levels ranging from
10
2 pg for
mnp2 to 2 × 10
3
pg for
mnp3. However, under nitrogen-limited conditions, the
addition of Mn to the culture medium resulted in an approximate
100-fold increase in the level of the
mnp1 transcript and a
1,700-fold
increase in the level of the
mnp2 transcript.
Less than a twofold
increase of
mnp3 transcript was observed
on day 5 under nitrogen-limited
conditions in the presence of Mn (Fig.
3B and C).

View larger version (31K):
[in this window]
[in a new window]
|
FIG. 3.
Competitive RT-PCR and quantitation of mnp
and gpd transcripts in total RNA extracted from 5-day-old
stationary cultures of P. chrysosporium. (A) Ethidium
bromide-stained gels of competitive RT-PCR products (5 µl) obtained
with the mnp2-specific upstream primer (Table 1). Cultures
were nitrogen sufficient (HN) or nitrogen limited (LN) and contained 0 or 180 µM Mn, as indicated. RT-PCRs were performed as described in
the text. Lanes: 1 to 8, PCR mixtures were spiked with 100, 50, 10, 5, 1, 0.1, and 0.05 pg, respectively, of plasmid containing the
mnp2 gene; 9, the PCR mixture lacked both cDNA and plasmid
DNA. The sizes of the genomic and cDNA PCR products are indicated. (B)
Bar graph of transcript levels, determined from gels as shown for
mnp2 in panel A. (C) Log scale bar graph of the transcript
levels in panel B. Culture conditions: HN, no Mn ( ); HN, 180 µM Mn
( ); LN, no Mn ( ); LN, 180 µM Mn ( ).
|
|
Temporal expression of mnp transcripts.
To
determine the expression profiles over time of the mnp
transcripts under nitrogen limitation, cultures of OGC101 were grown at
37°C in the presence of 180 µM Mn. cDNA was prepared from RNA isolated from each of two flasks on days 2 to 7 following inoculation, and competitive PCRs were performed as above. The transcript
concentrations determined for RNAs extracted from duplicate cultures
were averaged. There was less than a 25% variation between duplicate
cultures. All three mnp transcripts were detectable at very
low levels on day 2 (Fig. 4). The
mnp3 transcript level, 0.1 pg/20 ng of RNA, was the highest
level for the three transcripts on day 2. The mnp1
transcript level increased on day 3 by approximately 300-fold over day
2 and remained relatively constant through day 7. The mnp2
transcript level increased gradually on days 3 and 4, peaking on day 5 at approximately 1,000-fold higher than the level on day 2 and then
declining on days 6 and 7. The mnp3 transcript level peaked
on day 3 at approximately 75-fold higher than the level on day 2, returning to low levels on days 4 to 7. The levels of gpd
transcript remained approximately constant on days 2 to 7 (Fig. 4). The
compression of the basal-level data in Fig. 4 slightly misrepresents
the increases in the mnp1 and mnp2 transcript levels described above.

View larger version (13K):
[in this window]
[in a new window]
|
FIG. 4.
Time course of mnp and gpd
transcript levels. Nitrogen-limited, Mn-sufficient stationary cultures
of P. chrysosporium were harvested and the RNA was extracted
on the indicated days. Competitive RT-PCRs and quantitation were
performed as described in the text. Symbols: , mnp1; ,
mnp2; , mnp3; , gpd.
|
|
Expression of mnp transcripts in agitated
cultures.
Competitive RT-PCR was performed on RNA extracted from
5-day-old, nitrogen-limited, Mn-sufficient cultures grown under
agitated conditions, and the mnp transcript levels were
compared with those from 5-day-old stationary cultures (Fig.
5). The mnp1 transcript level
from agitated cultures was approximately threefold higher than that
from stationary cultures. In contrast, the level of the mnp2
transcript from agitated cultures was approximately 34-fold lower than
that from stationary cultures. Low levels of the mnp3 transcript were detected under both conditions. The levels of the
gpd transcript were not affected (Fig. 5).

View larger version (13K):
[in this window]
[in a new window]
|
FIG. 5.
Bar graphs of mnp and gpd
transcript levels in total RNA extracted from 5-day-old,
nitrogen-limited, Mn-sufficient agitated ( ) or stationary ( )
cultures of P. chrysosporium. Competitive RT-PCRs and
quantitation were performed as described in the text.
|
|
 |
DISCUSSION |
The lignin-degradative system of P. chrysosporium is
expressed during secondary metabolic (idiophasic) growth, whose onset is triggered by limiting nutrient nitrogen (19, 26).
Likewise, LiP and MnP activities are detectable in the extracellular
culture medium only during the secondary metabolic phase of growth
(19, 26), and Northern blot analysis demonstrates that LiP
and MnP expression is controlled at the level of gene transcription by nutrient nitrogen (34, 40). It has been reported that
lip genes are differentially regulated in response to carbon
and nitrogen (43). In addition, enzyme assays and Western
blotting results have suggested that the MnP protein isozymes may be
differentially regulated by carbon and nitrogen (38). The
latter study also suggested that MnP isozymes might be differentially
regulated by Mn, although this was not quantitated. In contrast, a
recent report suggests that mnp genes are coordinately
expressed during the bioremediation of contaminated soil by P. chrysosporium (3). The results of the present study
constitute the first report of differential regulation of
mnp gene transcription by any culture factor including Mn.
The mnp1, mnp2, and mnp3 promoter
regions contain multiple putative consensus metal response elements
(MREs) (1, 18, 35) that are identical to the
cis-acting sequences responsible for heavy metal induction
of mouse and other metallothionein genes (46). The
mnp1, mnp2, and mnp3 promoters also
contain putative heat shock elements (1, 18, 35). In this
study, we used competitive RT-PCR to examine nitrogen and Mn regulation
of the expression of individual mnp genes with greater
sensitivity than is possible by Northern blot analysis.
Our earlier studies indicated that MnP activity and mnp RNA
are observed only in nitrogen-limited cultures in the presence of Mn
and reach a maximum in 5-day-old cultures (9, 10, 16). Our
quantitative RT-PCR results in Fig. 3 demonstrate that all three
mnp transcripts are present at very low levels on day 5 under nitrogen-sufficient conditions in the presence or absence of Mn,
as well as under nitrogen-limited conditions in the absence of Mn.
These levels (<0.02 pg/20 ng of total RNA) are below the usual limits
of detection by Northern blot analysis. Furthermore, we did not detect
MnP activity in the extracellular medium under these conditions
(10). Thus, the three mnp genes are expressed at
a basal level in the presence of sufficient nitrogen when the lignin-degradative system is not active, and this basal expression appears to be unaffected by Mn (Fig. 3), suggesting that the
Mn-responsive MnP regulatory system is not functional under
nitrogen-sufficient conditions. Low basal-level expression of a
lip gene from P. chrysosporium also has been
detected by RT-PCR under nitrogen-sufficient conditions (8).
The results in Fig. 3 also demonstrate that in the presence of 180 µM
Mn, the levels of mnp1 and mnp2 transcripts from
5-day-old nitrogen-limited stationary cultures increase approximately
100- and 1,700-fold, respectively, over the basal levels. These
transcript levels correlate well with previous estimates, indicating
that under secondary metabolic conditions, MnP constitutes at least 2%
of the total protein in P. chrysosporium (40).
Under these conditions, the level of mnp3 transcript on day
5 is not increased significantly over the basal levels (Fig. 3B and C),
suggesting that the mnp3 gene may not be regulated by Mn.
The mnp3 promoter lacks paired putative MREs (1).
In contrast, the mnp1 promoter has two pairs of putative
MREs (18) and the mnp2 promoter has one pair
(35).
Our earlier results with Northern blots (9, 10) indicate
that mnp gene transcription in nitrogen-limited,
Mn-sufficient cultures is first detectable on day 3 and peaks on day 5. The results in Fig. 4 confirm that total mnp mRNA level is
highest on day 5. However, Fig. 4 demonstrates that this peak is caused almost entirely by mnp2 mRNA; mnp1 mRNA is
present at relatively low levels from days 3 through 7, and the
mnp3 mRNA level peaks on day 3. In contrast to these
results, RT-PCR of RNA isolated from soil-grown P. chrysosporium indicated the coordinate regulation of these
mnp genes (3). However, as demonstrated above,
other culture conditions appear to significantly affect the regulation of individual mnp genes.
The above experiments yielded consistently higher levels of
mnp2 transcript, compared with mnp1 transcript,
in stationary cultures. In contrast, MnP1 is the primary MnP isozyme
isolated from large agitated cultures of P. chrysosporium,
which are grown at 28°C to maximize MnP1 protein production (16,
19). Therefore, quantitative RT-PCR was performed on RNA
extracted from 5-day-old cultures grown under both conditions. The
results shown in Fig. 5 demonstrate that the levels of mnp1
transcript are approximately threefold higher in large agitated
cultures than in small stationary cultures. Furthermore,
mnp2 transcript levels are approximately 34-fold lower in
agitated cultures. Therefore, in agitated cultures, the level of the
mnp1 transcript is approximately 5-fold higher than the
level of the mnp2 transcript whereas in stationary cultures, the level of the mnp2 transcript is approximately 17-fold
higher than the level of the mnp1 transcript. The levels of
the mnp3 transcript apparently are unaffected by these
culture conditions. Furthermore, the low levels of mnp3 do
not appear to be regulated by Mn in agitated or stationary cultures.
Stationary and agitated cultures differ in several aspects, including
the type of inoculum and the growth temperature. However, mycelium
grown either at 28 or at 37°C in agitated culture yields similar
levels of the mnp transcripts (data not shown). The mycelial
mat that forms under stationary conditions may differ from the mycelial
pellets that form under agitated conditions in uptake of O2
or nutrients.
In conclusion, the results demonstrate that the mnp1 and
mnp2 genes from P. chrysosporium are regulated by
Mn in nitrogen-limited, 5-day-old cultures whereas the mnp3
gene does not appear to be significantly regulated by Mn. The
mnp3 transcript peaks on day 3 and then returns to basal
levels. In contrast, the mnp2 transcript predominates in day
5 stationary cultures and the mnp1 transcript predominates
in agitated cultures. These results indicate that the P. chrysosporium mnp genes are differentially regulated at the
transcriptional level in response to Mn and other culture conditions.
These results support the hypothesis that multiple mnp genes
are required to ensure expression under different environmental conditions. The results also demonstrate that the mnp3 gene
is not strongly regulated, if at all, by Mn. The exact physiological conditions under which mnp3 is expressed are under
investigation. The dramatic difference between mnp1 and
mnp2 transcription in agitated and stationary cultures may
be significant in attempts to overexpress single isozymes in large
fermentors.
 |
ACKNOWLEDGMENTS |
This work was supported by grants MCB-9405978 and
MCB-9723725 from the National Science Foundation.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Department of
Biochemistry and Molecular Biology, Oregon Graduate Institute of
Science and Technology, P.O. Box 91000, Portland, OR 97291-1000. Phone: (503) 690-1076. Fax: (503) 690-1464. E-mail:
mgold{at}bmb.ogi.edu.
 |
REFERENCES |
| 1.
|
Alic, M.,
L. Akileswaran, and M. H. Gold.
1997.
Characterization of the gene encoding manganese peroxidase isozyme 3 from Phanerochaete chrysosporium.
Biochim. Biophys. Acta
1338:1-7[Medline].
|
| 2.
|
Bao, W.,
Y. Fukushima,
K. A. Jensen, Jr.,
M. A. Moen, and K. E. Hammel.
1994.
Oxidative degradation of non-phenolic lignin during lipid peroxidation by fungal manganese peroxidase.
FEBS Lett.
354:297-300[Medline].
|
| 3.
|
Bogan, B. W.,
B. Schoenike,
R. T. Lamar, and D. Cullen.
1996.
Manganese peroxidase mRNA and enzyme activity levels during bioremediation of polycyclic aromatic hydrocarbon-contaminated soil with Phanerochaete chrysosporium.
Appl. Environ. Microbiol.
62:2381-2386[Abstract].
|
| 4.
|
Bogan, B. W.,
B. Schoenike,
R. T. Lamar, and D. Cullen.
1996.
Expression of lip genes during growth in soil and oxidation of anthracene by Phanerochaete chrysosporium.
Appl. Environ. Microbiol.
62:3697-3703[Abstract].
|
| 5.
|
Bonnarme, P., and T. W. Jeffries.
1990.
Mn(II) regulation of lignin peroxidases and manganese-dependent peroxidases from lignin-degrading white-rot fungi.
Appl. Environ. Microbiol.
56:210-217[Abstract/Free Full Text].
|
| 6.
|
Broda, P.,
P. R. Birch,
P. R. Brooks, and P. F. Sims.
1995.
PCR-mediated analysis of lignocellulolytic gene transcription by Phanerochaete chrysosporium: substrate-dependent differential expression within gene families.
Appl. Environ. Microbiol.
61:2358-2364[Abstract].
|
| 7.
|
Broda, P.,
P. R. Birch,
P. R. Brooks, and P. F. Sims.
1996.
Lignocellulose degradation by Phanerochaete chrysosporium: gene families and gene expression for a complex process.
Mol. Microbiol.
19:923-932[Medline].
|
| 8.
|
Brooks, P.,
P. Sims, and P. Broda.
1993.
Isozyme specific polymerase chain reaction analysis of differential gene expression: a general method applied to lignin peroxidase genes of Phanerochaete chrysosporium.
Bio/Technology
11:830-834[Medline].
|
| 9.
|
Brown, J. A.,
M. Alic, and M. H. Gold.
1991.
Manganese peroxidase gene transcription in Phanerochaete chrysosporium: activation by manganese.
J. Bacteriol.
173:4101-4106[Abstract/Free Full Text].
|
| 10.
|
Brown, J. A.,
J. K. Glenn, and M. H. Gold.
1990.
Manganese regulates expression of manganese peroxidase by Phanerochaete chrysosporium.
J. Bacteriol.
172:3125-3130[Abstract/Free Full Text].
|
| 11.
|
Brown, J. A.,
D. Li,
M. Alic, and M. H. Gold.
1993.
Heat shock induction of manganese peroxidase gene transcription in Phanerochaete chrysosporium.
Appl. Environ. Microbiol.
59:4295-4299[Abstract/Free Full Text].
|
| 12.
|
Covert, S. F.,
A. Vanden Wymelenberg, and D. Cullen.
1992.
Structure, organization, and transcription of a cellobiohydrolase gene cluster from Phanerochaete chrysosporium.
Appl. Environ. Microbiol.
58:2168-2175[Abstract/Free Full Text].
|
| 13.
|
Frohman, M. A.,
M. K. Dush, and G. R. Martin.
1988.
Rapid production of full-length cDNAs from rare transcripts: amplification using a single gene-specific oligonucleotide primer.
Proc. Natl. Acad. Sci. USA
85:8998-9002[Abstract/Free Full Text].
|
| 14.
|
Gettemy, J. M.,
D. Li,
M. Alic, and M. H. Gold.
1997.
Truncated gene reporter system for studying the regulation of manganese peroxidase.
Curr. Genet.
31:519-524[Medline].
|
| 15.
|
Gilliland, G.,
S. Perrin, and H. F. Bunn.
1990.
Competitive PCR for quantitation of mRNA, p. 60-69. In
M. A. Innis, D. H. Gelfand, J. J. Sninsky, and T. J. White (ed.), PCR protocols: a guide to methods and applications.
Academic Press, Inc., San Diego, Calif.
|
| 16.
|
Glenn, J. K., and M. H. Gold.
1985.
Purification and characterization of an extracellular Mn(II)-dependent peroxidase from the lignin-degrading basidiomycete, Phanerochaete chrysosporium.
Arch. Biochem. Biophys.
242:329-341[Medline].
|
| 17.
|
Godfrey, B. J.,
L. Akileswaran, and M. H. Gold.
1994.
A reporter gene construct for studying the regulation of manganese peroxidase gene expression.
Appl. Environ. Microbiol.
60:1353-1358[Abstract/Free Full Text].
|
| 18.
|
Godfrey, B. J.,
M. B. Mayfield,
J. A. Brown, and M. H. Gold.
1990.
Characterization of a gene encoding a manganese peroxidase from Phanerochaete chrysosporium.
Gene
93:119-124[Medline].
|
| 19.
|
Gold, M. H., and M. Alic.
1993.
Molecular biology of the lignin-degrading basidiomycete Phanerochaete chrysosporium.
Microbiol. Rev.
57:605-622[Abstract/Free Full Text].
|
| 20.
|
Gold, M. H.,
T. M. Cheng, and M. B. Mayfield.
1982.
Isolation and complementation studies of auxotrophic mutants of the lignin-degrading basidiomycete Phanerochaete chrysosporium.
Appl. Environ. Microbiol.
44:996-1000[Abstract/Free Full Text].
|
| 21.
|
Gold, M. H.,
M. Kuwahara,
A. A. Chiu, and J. K. Glenn.
1984.
Purification and characterization of an extracellular H2O2-requiring diarylpropane oxygenase from the white rot basidiomycete, Phanerochaete chrysosporium.
Arch. Biochem. Biophys.
234:353-362[Medline].
|
| 22.
|
Gold, M. H.,
H. Wariishi, and K. Valli.
1989.
Extracellular peroxidases involved in lignin degradation by the white rot basidiomycete Phanerochaete chrysosporium.
ACS Symp. Ser.
389:127-140.
|
| 23.
|
Hammel, K. E.
1989.
Organopollutant degradation by ligninolytic fungi.
Enzyme Microb. Technol.
11:776-777.
|
| 24.
|
Janssen, K.
1987.
Single-step RNA isolation from cultured cells or tissues, p. 4.2.4-4.2.6. In
F. M. Ausubel, R. Brent, R. E. Kingston, D. D. Moore, J. G. Seidman, J. A. Smith, and K. Struhl (ed.), Current protocols in molecular biology.
Greene Publishing Associates, Brooklyn, N.Y.
|
| 25.
|
Joshi, D. K., and M. H. Gold.
1993.
Degradation of 2,4,5-trichlorophenol by the lignin-degrading basidiomycete Phanerochaete chrysosporium.
Appl. Environ. Microbiol.
59:1779-1785[Abstract/Free Full Text].
|
| 26.
|
Kirk, T. K., and R. L. Farrell.
1987.
Enzymatic "combustion": the microbial degradation of lignin.
Annu. Rev. Microbiol.
41:465-505[Medline].
|
| 27.
|
Kirk, T. K.,
E. Schultz,
W. J. Connors,
L. F. Lorenz, and J. G. Zeikus.
1978.
Influence of culture parameters on lignin metabolism by Phanerochaete chrysosporium.
Arch. Microbiol.
117:277-285.
|
| 28.
|
Kishi, K.,
M. Kusters-van Someren,
M. B. Mayfield,
J. Sun,
T. M. Loehr, and M. H. Gold.
1996.
Characterization of manganese(II) binding site mutants of manganese peroxidase.
Biochemistry
35:8986-8994[Medline].
|
| 29.
|
Kishi, K.,
H. Wariishi,
L. Marquez,
H. B. Dunford, and M. H. Gold.
1994.
Mechanism of manganese peroxidase compound II reduction. Effect of organic acid chelators and pH.
Biochemistry
33:8694-8701[Medline].
|
| 30.
|
Kuan, I. C., and M. Tien.
1993.
Stimulation of Mn peroxidase activity: a possible role for oxalate in lignin biodegradation.
Proc. Natl. Acad. Sci. USA
90:1242-1246[Abstract/Free Full Text].
|
| 31.
|
Kusters-van Someren, M.,
K. Kishi,
T. Lundell, and M. H. Gold.
1995.
The manganese binding site of manganese peroxidase: characterization of an Asp179Asn site-directed mutant protein.
Biochemistry
34:10620-10627[Medline].
|
| 32.
|
Lamar, R. T.,
B. Schoenike,
A. Vanden Wymelenberg,
P. Stewart,
D. M. Dietrich, and D. Cullen.
1995.
Quantitation of fungal mRNAs in complex substrates by reverse transcription PCR and its application to Phanerochaete chrysosporium-colonized soil.
Appl. Environ. Microbiol.
61:2122-2126[Abstract].
|
| 33.
|
Li, D.,
M. Alic,
J. A. Brown, and M. H. Gold.
1995.
Regulation of manganese peroxidase gene transcription by hydrogen peroxide, chemical stress, and molecular oxygen.
Appl. Environ. Microbiol.
61:341-345[Abstract].
|
| 34.
|
Li, D.,
M. Alic, and M. H. Gold.
1994.
Nitrogen regulation of lignin peroxidase gene transcription.
Appl. Environ. Microbiol.
60:3447-3449[Abstract/Free Full Text].
|
| 35.
|
Mayfield, M. B.,
B. J. Godfrey, and M. H. Gold.
1994.
Characterization of the mnp2 gene encoding manganese peroxidase isozyme 2 from the basidiomycete Phanerochaete chrysosporium.
Gene
142:231-235[Medline].
|
| 36.
|
Mayfield, M. B.,
K. Kishi,
M. Alic, and M. H. Gold.
1994.
Homologous expression of recombinant manganese peroxidase in Phanerochaete chrysosporium.
Appl. Environ. Microbiol.
60:4303-4309[Abstract/Free Full Text].
|
| 37.
|
Orth, A. B.,
M. Rzhetskaya,
D. Cullen, and M. Tien.
1994.
Characterization of a cDNA encoding a manganese peroxidase from Phanerochaete chrysosporium: genomic organization of lignin and manganese peroxidase-encoding genes.
Gene
148:161-165[Medline].
|
| 38.
|
Pease, E. A., and M. Tien.
1992.
Heterogeneity and regulation of manganese peroxidase from Phanerochaete chrysosporium.
J. Bacteriol.
174:3532-3540[Abstract/Free Full Text].
|
| 39.
|
Pease, E. A.,
A. Andrawis, and M. Tien.
1989.
Manganese-dependent peroxidase from Phanerochaete chrysosporium. Primary structure deduced from cDNA sequence.
J. Biol. Chem.
264:13531-13535[Abstract/Free Full Text].
|
| 40.
|
Pribnow, D. G.,
M. B. Mayfield,
V. J. Nipper,
J. A. Brown, and M. H. Gold.
1989.
Characterization of a cDNA encoding a manganese peroxidase, from the lignin-degrading basidiomycete Phanerochaete chrysosporium.
J. Biol. Chem.
264:5036-5040[Abstract/Free Full Text].
|
| 41.
|
Reiser, J.,
I. S. Walther,
C. Fraefel, and A. Fiechter.
1993.
Methods to investigate the expression of lignin peroxidase genes by the white rot fungus Phanerochaete chrysosporium.
Appl. Environ. Microbiol.
59:2897-2903[Abstract/Free Full Text].
|
| 42.
|
Sooknanan, R.,
L. Malek,
X. H. Wang,
T. Siebert, and A. Keating.
1993.
Detection and direct sequence identification of BCR-ABL mRNA in Ph+ chronic myeloid leukemia.
Exp. Hematol.
21:1719-1724[Medline].
|
| 43.
|
Stewart, P.,
P. Kersten,
A. Vanden Wymelenberg,
J. Gaskell, and D. Cullen.
1992.
Lignin peroxidase gene family of Phanerochaete chrysosporium: complex regulation by carbon and nitrogen limitation and identification of a second dimorphic chromosome.
J. Bacteriol.
174:5036-5042[Abstract/Free Full Text].
|
| 44.
|
Sundaramoorthy, M.,
K. Kishi,
M. H. Gold, and T. L. Poulos.
1994.
The crystal structure of manganese peroxidase from Phanerochaete chrysosporium at 2.06-Å resolution.
J. Biol. Chem.
269:32759-32767[Abstract/Free Full Text].
|
| 45.
|
Tempelaars, C. A.,
P. R. Birch,
P. F. Sims, and P. Broda.
1994.
Isolation, characterization, and analysis of the expression of the cbhII gene of Phanerochaete chrysosporium.
Appl. Environ. Microbiol.
60:4387-4393[Abstract/Free Full Text].
|
| 46.
|
Thiele, D. J.
1992.
Metal-regulated transcription in eukaryotes.
Nucleic Acids Res.
20:1183-1191[Free Full Text].
|
| 47.
|
Valli, K.,
H. Wariishi, and M. H. Gold.
1992.
Degradation of 2,7-dichlorodibenzo-p-dioxin by the lignin-degrading basidiomycete Phanerochaete chrysosporium.
J. Bacteriol.
174:2131-2137[Abstract/Free Full Text].
|
| 48.
|
Wariishi, H.,
L. Akileswaran, and M. H. Gold.
1988.
Manganese peroxidase from the basidiomycete Phanerochaete chrysosporium: spectral characterization of the oxidized states and the catalytic cycle.
Biochemistry
27:5365-5370[Medline].
|
| 49.
|
Wariishi, H.,
H. B. Dunford,
I. D. MacDonald, and M. H. Gold.
1989.
Manganese peroxidase from the lignin-degrading basidiomycete Phanerochaete chrysosporium. Transient-state kinetics and reaction mechanism.
J. Biol. Chem.
264:3335-3340[Abstract/Free Full Text].
|
| 50.
|
Wariishi, H.,
K. Valli, and M. H. Gold.
1992.
Manganese(II) oxidation by manganese peroxidase from the basidiomycete Phanerochaete chrysosporium: kinetic mechanism and role of chelators.
J. Biol. Chem.
267:23688-23695[Abstract/Free Full Text].
|
| 51.
|
Wariishi, H.,
K. Valli,
V. Renganathan, and M. H. Gold.
1989.
Thiol-mediated oxidation of nonphenolic lignin model compounds by manganese peroxidase of Phanerochaete chrysosporium.
J. Biol. Chem.
264:14185-14191[Abstract/Free Full Text].
|
Appl Environ Microbiol, February 1998, p. 569-574, Vol. 64, No. 2
0099-2240/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
This article has been cited by other articles:
-
Ma, B., Mayfield, M. B., Godfrey, B. J., Gold, M. H.
(2004). Novel Promoter Sequence Required for Manganese Regulation of Manganese Peroxidase Isozyme 1 Gene Expression in Phanerochaete chrysosporium. Eukaryot Cell
3: 579-588
[Abstract]
[Full Text]
-
Steffen, K. T., Hatakka, A., Hofrichter, M.
(2003). Degradation of Benzo[a]pyrene by the Litter-Decomposing Basidiomycete Stropharia coronilla: Role of Manganese Peroxidase. Appl. Environ. Microbiol.
69: 3957-3964
[Abstract]
[Full Text]
-
Schlosser, D., Hofer, C.
(2002). Laccase-Catalyzed Oxidation of Mn2+ in the Presence of Natural Mn3+ Chelators as a Novel Source of Extracellular H2O2 Production and Its Impact on Manganese Peroxidase. Appl. Environ. Microbiol.
68: 3514-3521
[Abstract]
[Full Text]
-
Cohen, R., Yarden, O., Hadar, Y.
(2002). Lignocellulose Affects Mn2+ Regulation of Peroxidase Transcript Levels in Solid-State Cultures of Pleurotus ostreatus. Appl. Environ. Microbiol.
68: 3156-3158
[Abstract]
[Full Text]
-
Johansson, T., Nyman, P. O., Cullen, D.
(2002). Differential Regulation of mnp2, a New Manganese Peroxidase-Encoding Gene from the Ligninolytic Fungus Trametes versicolor PRL 572. Appl. Environ. Microbiol.
68: 2077-2080
[Abstract]
[Full Text]
-
Ma, B., Mayfield, M. B., Gold, M. H.
(2001). The Green Fluorescent Protein Gene Functions as a Reporter of Gene Expression in Phanerochaete chrysosporium. Appl. Environ. Microbiol.
67: 948-955
[Abstract]
[Full Text]
-
Noda, S., Ohkuma, M., Usami, R., Horikoshi, K., Kudo, T.
(1999). Culture-Independent Characterization of a Gene Responsible for Nitrogen Fixation in the Symbiotic Microbial Community in the Gut of the Termite Neotermes koshunensis. Appl. Environ. Microbiol.
65: 4935-4942
[Abstract]
[Full Text]
-
Ruiz-Dueñas, F. J., Guillén, F., Camarero, S., Pérez-Boada, M., Martínez, M. J., Martínez, A. T.
(1999). Regulation of Peroxidase Transcript Levels in Liquid Cultures of the Ligninolytic Fungus Pleurotus eryngii. Appl. Environ. Microbiol.
65: 4458-4463
[Abstract]
[Full Text]
-
Lee, G.-C., Tang, S.-J., Sun, K.-H., Shaw, J.-F.
(1999). Analysis of the Gene Family Encoding Lipases in Candida rugosa by Competitive Reverse Transcription-PCR. Appl. Environ. Microbiol.
65: 3888-3895
[Abstract]
[Full Text]
-
Sollewijn Gelpke, M. D., Mayfield-Gambill, M., Lin Cereghino, G. P., Gold, M. H.
(1999). Homologous Expression of Recombinant Lignin Peroxidase in Phanerochaete chrysosporium. Appl. Environ. Microbiol.
65: 1670-1674
[Abstract]
[Full Text]
-
Collins, P. J., O'Brien, M. M., Dobson, A. D. W.
(1999). Cloning and Characterization of a cDNA Encoding a Novel Extracellular Peroxidase from Trametes versicolor. Appl. Environ. Microbiol.
65: 1343-1347
[Abstract]
[Full Text]
-
Janse, B. J. H., Gaskell, J., Akhtar, M., Cullen, D.
(1998). Expression of Phanerochaete chrysosporium Genes Encoding Lignin Peroxidases, Manganese Peroxidases, and Glyoxal Oxidase in Wood. Appl. Environ. Microbiol.
64: 3536-3538
[Abstract]
[Full Text]