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Applied and Environmental Microbiology, August 2000, p. 3408-3414, Vol. 66, No. 8
0099-2240/00/$04.00+0
Copyright © 2000, American Society for Microbiology. All rights reserved.
Accumulation of
Poly[(R)-3-Hydroxyalkanoates] in Pseudomonas
oleovorans during Growth with Octanoate in Continuous Culture at
Different Dilution Rates
Roland
Durner,1
Bernard
Witholt,2 and
Thomas
Egli1,*
Department of Microbiology, Swiss Federal
Institute for Environmental Science and Technology (EAWAG),
Dübendorf,1 and Institute of
Biotechnology, Swiss Federal Institute of Technology (ETH),
Zürich,2 Switzerland
Received 14 April 2000/Accepted 30 May 2000
 |
ABSTRACT |
Pseudomonas oleovorans ATCC 29347 was grown in
chemostat culture at different dilution rates with mineral media
varying in their ratios of octanoate to ammonia
(C0/N0 ratio). At all dilution rates tested,
three distinct growth regimes were observed: (i) carbon limitation with
NH4+ in excess at low
C0/N0 ratios, (ii) purely nitrogen-limited
growth conditions at high C0/N0 ratios with
residual octanoate in the culture supernatant, and (iii) an
intermediate zone of dual-nutrient-limited growth conditions where both
the concentration of octanoate and that of ammonia were very low. The
dual-nutrient-limited growth zone shifted to higher
C0/N0 ratios with decreasing dilution rates, and the extension of the dual-nutrient-limited growth zone was inversely proportional to the growth rate. The cells accumulated the
storage compound medium-chain-length
poly[(R)-3-hydroxyalkanoate] (mcl-PHA) during dual (C and
N)-nutrient-limited and N-limited growth conditions. Within the
dual-nutrient-limited growth zone, the cellular mcl-PHA contents
increased when the C0/N0 ratio in the feed was
increased, whereas the cellular mcl-PHA level was independent from the
feed C0/N0 ratio during N-limited growth. The
monomeric composition of the accumulated mcl-PHA was independent of
both the dilution rate and the feed C0/N0 ratio
and consisted of 12 mol% 3-hydroxyhexanoic acid and 88 mol%
3-hydroxyoctanoic acid. Accumulation of mcl-PHA led to an increase in
the cellular C/N ratio and to changes in elemental growth yields for
nitrogen and carbon.
 |
INTRODUCTION |
Pseudomonas oleovorans is
able to accumulate medium-chain-length
poly[(R)-3-hydroxyalkanoates] (mcl-PHAs) as intracellular carbon and energy storage compounds when grown with alkanes (9, 24), mcl-alkanoates (3, 21), n-alkanols
(16), or many derivatives thereof (27, 38).
mcl-PHAs are hydrophobic polyesters and are attracting increasing
interest for their possible application as biologically produced and
inherently biodegradable substitutes for conventional plastic materials
(6, 8, 10, 20, 32). Particularly, when subjected to nitrogen
limitation in batch (22, 24) and chemostat culture (17,
33, 34), P. oleovorans has been reported to accumulate
high cellular mcl-PHA contents.
The nature and availability of essential nutrients are important
parameters in determining the extent of storage compound accumulation
in P. oleovorans (23, 24). Generally, the
production of microbial cell mass is limited by the restricted
availability of a particular nutrient. In batch culture, the exhaustion
of a specific nutrient terminates the exponential-growth phase, whereas in chemostat culture the biomass concentration is usually controlled by
the permanent limitation of a single defined nutrient, typically the
carbon and energy source. However, several authors have shown that two
or more nutrients can simultaneously limit the production of biomass
(for a summary, see reference 14). This phenomenon has also been observed for P. oleovorans, where we have
found that under defined chemostat steady-state cultivation conditions, the biomass concentration and the cell composition were influenced by
simultaneous limitations of the available carbon and nitrogen (12).
All of the previous reports have emphasized that dual-nutrient-limited
growth depends on the ability of a microorganism to adjust its cellular
composition to different degrees of nutrient limitation. If a
microorganism is very flexible in this respect, an extended
dual-nutrient-limited growth regime between two single-nutrient limitations should be observed in continuous culture. It is known (19) that the flexibility in cellular composition increases with decreasing growth rates. Therefore, it was predicted
(14) that the range of dual nutrient limitation should also
depend on the chemostat dilution rate. In order to test this hypothesis and to investigate the influence of the growth rate on the
physiological adaptation and mcl-PHA accumulation pattern of P. oleovorans, cells were cultivated in the chemostat at different
dilution rates and at various ratios of octanoate to ammonia in the
feed medium.
 |
MATERIALS AND METHODS |
Bacterial strain, media, and growth conditions.
P.
oleovorans ATCC 29347, kept as frozen stock in 15%
glycerol-citrate E medium at
80°C, was used for all experiments.
Modified E medium (39) contained, per liter, 3.5 g of
NaNH4HPO4 · 4H2O, 7.5 g
of K2HPO4, 3.7 g of
KH2PO4, and 2.9 g of Na3
citrate · 2H2O. The pH was adjusted to 7.1 with 10 mM NaOH. This mineral medium was autoclaved and then supplemented with
1 ml of filter-sterilized MgSO4 (1 M) and 1 ml of MT trace
element stock solution, which contained, per liter, 2.78 g of
FeSO4 · 7H2O, 1.47 g of
CaCl2 · 2H2O, 1.98 g of
MnCl2 · 4H2O, 2.81 g of
CoSO4 · 7H2O, 0.17 g of
CuCl2 · 2H2O, and 0.29 g of
ZnSO4 · 7H2O in 1 M HCl.
Continuous cultivation conditions.
We used a 50-ml cell
suspension grown overnight at 30°C in medium E in 300-ml shaking
flask batch cultures as inocula for chemostat experiments. After an
initial start-up batch, the bioreactor was switched to continuous mode.
The following medium was used for continuous culture cultivations;
1 g of KH2HPO4/liter 0.708 g of
(NH4)2SO4/liter (equals 150 mg of
N/liter), 50 ppm of silicone antifoam, and variable amounts of sodium
octanoate or trisodium citrate dihydrate. After autoclaving, 1 ml of 10 mM FeSO4 · 7H2O (in 1 M HCl), 1 ml of 1 M MgSO4, and 1 ml of continuous culture trace metal (CCTM)
stock solution were added to the medium by filter sterilization. CCTM
stock solution consisted of 1.47 g of CaCl2 · 2H2O/liter, 1.98 g of MnCl2 · 4H2O/liter, 2.81 g of CoSO4 · 7H2O/liter, 0.17 g of CuCl2 · 2H2O/liter, 0.29 g of ZnSO4 · 7H2O/liter, and 10 g of EDTA/liter at pH 4. The
continuous culture experiments were done in a 3-liter laboratory
bioreactor (MBR, Wetzikon, Switzerland) with a working volume of 2 liters equipped with automated pH control, a dissolved oxygen tension
electrode, a magnetic coupled stirrer, and dilution rate control by an
automatic balance.
The carbon source octanoate was not included in the mineral medium, but
filter-sterilized octanoate was injected directly into the culture with
a syringe pump (Perfusor Secura; B. Braun, Melsungen, Germany) through
a thin needle (diameter, ca. 0.5 mm) to ensure a continuous carbon
supply. The C0/N0 ratio of the medium was
calculated from the pump flow rate and the measured nitrogen concentration in the mineral medium.
Sample preparation.
Cell samples were taken in ice-cooled
flasks and spun down at 10,000 × g for 15 min at
4°C, and the culture supernatant was analyzed for residual nutrient
concentrations. The cell pellet was washed twice with 10 mM
MgCl2, frozen in nanopure water, and lyophilized.
Dry weight of cells.
The biomass concentration (measured in
dry weight of cells [CDW]; also abbreviated as X) in the culture was
measured by filtering an appropriate amount of cell suspension (3 to 8 mg, CDW) through a preweighed 0.2-µm-pore-size polycarbonate filter.
The filter was washed once with 10 ml of a 10 mM MgCl2
solution and dried overnight at 105°C. The weight difference after
cooling the filter in the exsiccator over silica gel was measured to
calculate the concentration of CDW in the culture. All CDW measurements
of chemostat experiments were done in triplicate. The relative error
was below 5%. CDW determinations in batch cultures were done only once
per sample because of the limiting amount of culture volume. Biomass concentration measurements were double-checked by optical density measurements at 450 nm and CDW determination. The results of the two
techniques agreed well.
Analysis of substrates in medium and culture supernatant.
Ammonium was measured according to the indophenol method described by
Scheiner (37). The detection limit of this method was 0.12 mg of N/liter. The method was linear up to concentrations of 2 mg of
N/liter. Sample dilutions were done in nanopure water if necessary. The
identity of acetate was verified by an enzymatic standard assay
(Boehringer, Mannheim, Germany). Octanoate and acetate were measured by
a gas chromatography (GC) method by direct injection of acidified
aqueous samples (column, Permabond FFAP-0.35, 25 m by 0.32 mm;
Macherey-Nagel, Basel, Switzerland). Butyric acid served as the
internal standard, and a calibration curve for sodium octanoate in E
medium was used as the external standard. Samples and standards were
mixed in a 1:1 ratio with a solution containing 1 g of butyric
acid/liter and 15 vol% orthophosphoric acid. The detection limit of
this method was 50 mg of octanoic acid and acetic acid/liter, and the
calibration curve was linear up to 4 g/liter. Dissolved organic carbon
(DOC) in culture supernatants was measured using a TOCOR 2 total
organic carbon analyzer (Maihak AG, Hamburg, Germany). For this purpose
10 ml of sample was acidified with 150 µl of concentrated HCl and
stripped from CO2 with nitrogen gas. The linear
concentration range was 5 to 100 mg of DOC/liter, and dilutions, if
necessary, were made in nanopure water.
Elemental analysis.
The elemental cell composition was
measured with a Carlo Erba (CHNS) elemental analyzer (model EA1108;
Carlo Erba, Milan, Italy).
PHA analysis.
The PHA content and monomeric composition of
the cells were analyzed by a GC method initially described by Braunegg
et al. (4) and adapted for mcl-PHAs by Lageveen et al.
(24). Methylbenzoate served as the internal standard, and
pure mcl-PHA obtained by chloroform extraction and methanol
precipitation was used as a methanolysation standard. This standard PHA
was weighed and treated in the same way as the lyophilized cell
samples. The identities of the monomers were checked with GC-mass
spectrometry (MS) measurements (GC-MS MD 800; Brechbühler, AG,
Schlieren, Switzerland).
Gas analysis.
The exhaust gas stream of the chemostat
experiments was continuously analyzed for its CO2 (by
infrared spectroscopy; IR-Binos; Leybold-Heraeus, Hanau, Germany) and
O2 (paramagnetically) contents with a standard gas analyzer
(Oxymat 3; Siemens, Erlangen, Germany).
 |
RESULTS |
P. oleovorans was grown in chemostat culture at five
different dilution rates ranging from 0.05 to 0.4 h
1 with
a mineral medium and octanoate as the sole source of carbon and energy.
The carbon-to-nitrogen ratio of the supplied growth medium
(C0/N0, given in moles per moles) was adjusted
by keeping the concentrations of ammonium (N0 = 10.7 mM) and all other inorganic nutrients constant and by varying the
concentration of octanoate stepwise (by varying the octanoate feed pump
flow rate). Up to at least 2 g of dry PHA-free biomass
liter
1, this medium was clearly limited by either C or N
under the experimental conditions used (42). Culture
parameters, such as residual concentrations of octanoate and ammonium,
biomass produced, and cellular PHA contents were assessed under
steady-state conditions (defined as constant concentrations of residual
substrates and biomass concentrations).
Three distinct nutritional growth limitations.
When the
C0/N0 ratio of the inflowing growth medium was
increased from low to high values, a typical pattern was observed at
all dilution rates tested (Fig. 1): in
addition to pure carbon limitation at low C0/N0
ratios in the medium feed with unutilized ammonium in the culture
supernatant and pure nitrogen limitation with residual octanoate at
high C0/N0 ratios, an intermediate zone of dual
nutrient limitation was observed. Under these conditions both carbon
and nitrogen were used to completion, and their concentrations in the
culture supernatant were below the detection limit. The data clearly
demonstrate that the width and location of the dual-nutrient-limited growth zone (Fig. 1) were functions of the growth rate. At a dilution rate of 0.4 h
1, the width of the zone was only 1.6 C0/N0 units, whereas at 0.1 h
1,
the zone extended over 9.8 C0/N0 units. Both
the lower and the upper boundaries of the dual-nutrient-limited growth
zones shifted to higher C0/N0 values as the
growth rate decreased.

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FIG. 1.
Growth and PHA content of P. oleovorans in
chemostat culture at different dilution rates, as a function of the
carbon-to-nitrogen ratio of the medium feed
(C0/N0, in moles per moles) with octanoate as
the sole source of carbon and energy and ammonium as the only source of
nitrogen. The concentrations of nitrogen and all other inorganic
nutrients in the feed were kept constant (N0 = 10.7 mM), whereas the concentration of octanoate was varied. The zone of
dual-nutrient-limited growth (shaded) was calculated from the slopes of
residual nitrogen (lower boundary) and octanoate (upper boundary). The
upper boundary at a D of 0.05 h 1 could not be
determined due to by-product formation and unstable growth (see the
text).
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Determination of the boundaries of dual-nutrient-limited
growth.
The boundaries of dual-nutrient-limited growth were
estimated by two different procedures.
First, the boundary between carbon limitation and dual nutrient
limitation (the lower boundary) was calculated by linear regression
of
residual ammonium versus the C
0/N
0 ratio in the
feed medium
and determination of the C
0/N
0
ratio at an NH
4+ concentration of zero.
Likewise, the boundary between dual-nutrient-limited
growth and pure
nitrogen limitation (the upper boundary) was calculated
as the
intercept of the best linear fit of the residual octanoate
versus the
C
0/N
0 ratio in the feed medium with the
C
0/N
0 axis.
Second, elemental yield coefficients obtained under
single-nutrient-limited growth conditions were used to calculate the
boundaries
of the dual-nutrient-limited growth zone according to the
method
of Egli and Quayle (
13). For a particular dilution
rate, the
growth yield coefficients for nitrogen
(
YX/N) and carbon (
YX/C)
were constant under single-nutrient-limited conditions and changed
within the dual-nutrient-limited growth zone:
YX/C decreased,
whereas
YX/N increased (
12). Additionally,
the yield factors
were dependent on the dilution rate (Fig.
2).
YX/C increased
with
increasing growth rates both for carbon- and for nitrogen-limited
growth conditions. Under carbon limitation,
YX/N
remained almost
constant at all growth rates, but
YX/N decreased by 38% for cells
grown under
nitrogen limitation when the growth rate was increased
from 0.1 to 0.4 h
1 (Fig.
2).

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FIG. 2.
Elemental yield coefficients for nitrogen and carbon
determined for P. olevorans during growth in the chemostat
with octanoate and ammonium under either nitrogen- or carbon-limited
conditions, as a function of the dilution rate. Symbols: ,
YX/N for carbon-limited growth; ,
YX/N for nitrogen-limited growth; ,
YX/C for carbon-limited growth; ,
YX/C for nitrogen-limited growth; ,
YX/N of PHA-free biomass for carbon-limited
growth; , YX/N of PHA-free biomass for
nitrogen-limited growth.
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|
Figure
3 depicts the zone of
dual-nutrient-limited growth as a function of the dilution rate and the
C
0/N
0 ratio in the growth
medium. The
boundaries obtained from residual nutrient concentrations
are compared
to the values determined from elemental growth yield
coefficients.

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FIG. 3.
Extension of the dual (carbon and
nitrogen)-nutrient-limited growth zone for the cultivation of P. oleovorans with octanoate and ammonium as a function of the
dilution rate and the C0/N0 ratio (in moles per
moles) of the medium feed. Measured boundaries were obtained from the
slopes of either residual nitrogen (lower boundary) or octanoate (upper
boundary) versus the C0/N0 ratio in the medium
feed. Alternatively, the boundaries from the carbon and nitrogen yield
coefficients were calculated according to the method of Egli and Quayle
(13). The growth yield coefficients for the maximum growth
rate (µmax) were determined in batch culture as described
in reference 12 and refer to the non-PHA biomass produced during
exponential growth. Lower boundary: , calculated from yield
coefficients; , determined from residual nitrogen concentration
pattern. Upper boundary: , calculated from yield coefficients; ,
determined from residual octanoate concentration pattern.
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Elemental cell composition.
The elemental cell composition
with respect to carbon and nitrogen was strongly dependent on the
cellular PHA content (Table 1 and Fig.
4). The C/N ratio of the biomass was
constant under single-nutrient-limited growth conditions and increased
with increasing cellular PHA contents. In contrast, the calculated C/N
ratio of the non-PHA biomass remained almost constant. This indicates
that some of the surplus octanoate supplied to the culture in the
dual-nutrient-limited growth zone was accumulated as mcl-PHA, and
accumulation of this storage compound was the most significant factor
of the change in the cellular composition with respect to carbon and
nitrogen.
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TABLE 1.
Culture parameters, elemental growth yields, elemental
cellular composition, cellular PHA content, and PHA composition during
growth of P. oleovorans in continuous culture at different
dilution rates with octanoate and ammonium under either carbon- or
nitrogen-limited conditions
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FIG. 4.
Cellular C/N ratio of P. oleovorans grown
with octanoate at different dilution rates as a function of the mcl-PHA
content. , C/N ratio of whole freeze-dried cells; , C/N ratio of
the non-PHA biomass.
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|
mcl-PHA accumulation as a function of the
C0/N0 ratio and dilution rate.
PHA
accumulation was detected in cells of P. oleovorans under
all growth conditions tested (Fig. 5).
Low cellular PHA contents were measured even during carbon-limited
growth at low C0/N0 ratios. The cellular PHA
content under carbon-limited growth conditions was a function of the
dilution rate. It was below 2 wt% at a D of 0.05 h
1, exhibited a maximum of more than 10 wt% at a growth
rate of 0.3 h
1, and decreased again to 7.6 wt% at 0.4 h
1. For all dilution rates, the cellular PHA content
increased within the dual-nutrient-limited growth zone and remained at
the maximum level under pure nitrogen limitation (Fig. 5; compare also
Fig. 1). For cells grown under distinct nitrogen limitation, the
mcl-PHA content was inversely proportional to the growth rate and
decreased from more than 56% at a growth rate of 0.1 h
1
to less than 21% at 0.4 h
1.

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FIG. 5.
Cellular mcl-PHA contents of P. oleovorans
grown in continuous culture with octanoate and ammonium, as a function
of the growth-limiting nutrient at different dilution rates. PHA
content was measured under carbon ( )- and nitrogen ( )-limited
growth conditions.
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Composition of the accumulated polymer.
The monomeric
composition of the accumulated mcl-PHA was independent of the dilution
rate and consisted of 88 mol% 3-hydroxy-octanoic acid (3OH-8) and 12 mol% 3-hydroxy-hexanoic acid (3OH-6). Only when the cellular PHA
content was below 3 wt% was no 3OH-6 detected by GC analysis. However,
this was possibly due to analytical limitations of the method and not
to the total absence of 3OH-6 in the polymer itself.
By-product formation under nitrogen-limited growth conditions at
low dilution rates.
At dilution rates equal to or lower than 0.1 h
1 and C0/N0 ratios in the feed
medium that were close to or above the upper boundary of dual nutrient
limitation, significant by-product formation was detected. This
excretion of by-products always went along with a visible browning of
the culture supernatant and an exceptionally low
YX/C. Although no distinct absorption maxima
were observed, UV/visible spectrometry of the culture supernatant
showed that the excreted products resulted in an increase in absorption
at wavelengths below 450 nm. Size exclusion chromatography indicated that the major fraction consisted of by-products with molecular masses
below 250 Da. Acetate was identified as the main by-product by ion
chromatography and enzymatic assay. However, because the absolute
amount of excreted carbonaceous compounds is unknown, the fraction of
acetate can only be estimated to be approximately 60% of the excreted
carbon. When the chemostat dilution rate was increased above 0.1 h
1 or the C0N0 ratio in the
medium feed was decreased below a critical value, the brown color
disappeared according to a washout curve. Due to this phenomenon, no
purely nitrogen-limited steady-state conditions could be achieved at a
dilution rate of 0.05 h
1.
 |
DISCUSSION |
Dual-nutrient-limited growth zones and their boundaries.
The
cultivation of P. oleovorans in chemostat culture with
octanoate and ammonium at different C0/N0
ratios of the medium feed led to steady-state growth not only under
clearly C- or N-limited conditions. In addition, in between the two
single-substrate-limited growth regimes, a stable zone of growth was
observed where both nutrients were utilized to completion (referred to
as a dual-nutrient-limited growth zone).
With decreasing dilution rates, the lower as well as the upper boundary
of the dual-nutrient-limited growth zone shifted to
higher
C
0/N
0 ratios and the zone broadened (Fig.
3).
The boundaries
obtained from the residual nutrient concentrations were
in good
agreement with the results calculated from nutrient yield
coefficients
measured under single-nutrient-limited growth conditions
as described
by Egli and Quayle (
13). They proposed a simple
empirical equation
(equations 1 and 2) which allows an estimation of
the borders
of dual nutrient limitation on a
C
0/N
0 axis from the elemental
growth yields
derived from single-nutrient-limited growth under
the condition that
these yields are constant under the respective
limitation. The
steady-state biomass at the border of dual nutrient
limitation (see
Fig.
1) can be calculated from the elemental growth
yield factor and
the amount of the respective nutrient used.
|
(1)
|
Assuming that the concentrations of the residual nutrients at the
border of dual nutrient limitation are close to zero, the
equation can
be rearranged to yield the C
0/N
0 ratio of the
feed
medium at which the boundary should be observed:
|
(2)
|
Equation
2 implies that the zone of dual-nutrient-limited growth
should become more extended as the difference in the yield
coefficients
between the two single nutrient limitations becomes
more pronounced,
which is increasingly the case as the dilution
rate is lowered
(
19).
The general shape of the dual-nutrient-limited growth zone presented
here for the growth of
P. oleovorans with octanoate and
ammonium (Fig.
3) is in good agreement with the predictions made
earlier by Egli (
14). From reports in the literature of
growth
yield factors obtained for single-nutrient-limited growth of
Klebsiella pneumoniae with glycerol and
NH
4+, this author predicted a similarly shaped
zone of dual-nutrient-limited
growth
conditions.
From Fig.
2 and on the basis of equation 2, two main parameters can be
seen to influence the extension and location of the
dual-nutrient-limited growth
zone.
First, under carbon limitation, the change of
YX/C determines the location of the lower
boundary of the dual-nutrient-limited
growth regime, because under
these conditions
YX/N is constant
at all
dilution rates.
YX/C is the sum of a
growth-associated
term and the maintenance coefficient
(
31), and the fraction
of maintenance energy with
respect to the total yield coefficient
increases with decreasing growth
rate. Therefore, the shift of
the boundary between the C- and the
C/N-limited growth zone with
decreasing growth rates is predominantly
caused by the maintenance
energy
coefficient.
Second,
YX/C and
YX/N
obtained for N-limited conditions both changed with different dilution
rates (Fig.
2). As described
above,
YX/C
increased with increasing growth rate due to the dwindling
influence of
the maintenance energy coefficient. In contrast,
YX/N measured under nitrogen limitation for
whole cells decreased
with increasing growth rates, because the
cellular PHA content
also decreased as the dilution rate increased.
When the nitrogen-based
growth yield was calculated for the non-PHA
biomass (
YB/N), it
remained constant at all
growth rates. This indicates that the
accumulation of mcl-PHA was the
main cause for the change in
YX/N under nitrogen
limitation and that this affected the position
of the upper boundary of
the dual-nutrient-limited growth
regime.
mcl-PHA accumulation under carbon-limited growth conditions.
At growth rates approaching the maximum growth rate
(µmax), the cells produced a considerable amount of
mcl-PHA under purely carbon-limited growth conditions (Fig. 5). As we
have shown elsewhere (12), P. oleovorans also
accumulates mcl-PHA in batch culture during unrestricted growth in the
exponential phase. Both observations might result from the fact that in
cells cultivated with mcl-fatty acids at high growth rates, the
intracellular metabolite pools relevant for PHA accumulation are
saturated, and overflow metabolism directs
-oxidation metabolites
into mcl-PHA precursors and polymer. A similar explanation has been put
forward for the growth-associated poly (hydroxybutyric acid) (PHB)
accumulation in Methylobacterium rhodesianum (1),
where a postulated metabolic bottleneck diverted intermediates into PHB
formation. Page and Knosp (29) explained the PHB
accumulation during unrestricted growth of Azotobacter vinelandii strain UWD by its deficient capacity to oxidize NADH and the resulting high ratio of NADH to NAD+. This excess
of reducing power in the cell feeds back on the tricarboxylic acid
(TCA) cycle, which in turn promotes the condensation of acetoacetyl
coenzyme A (CoA) that allows PHB synthesis as an alternative electron
sink (see also reference 30). In both cases PHB was
formed as an overflow product of central metabolic pathway intermediates. Several other authors detected growth-associated PHB or
mcl-PHA accumulation in the exponential phase of batch cultures in
various microorganisms (2, 4, 22, 26, 41).
mcl-PHA accumulation under nitrogen limitation.
When cells
were subjected to pure nitrogen limitation, the extent of mcl-PHA
stored increased with decreasing growth rates. Although the absolute
PHA contents reported differed slightly, the same observation has been
made previously for P. oleovorans growing under conditions
of carbon excess at different dilution rates in a two-liquid-phase
chemostat with octane (33). Similar observations have also
been reported by Ramsay et al. (35), who cultivated P. oleovorans with octanoate at different dilution rates at a fixed
C0/N0 ratio of 14.7 (this
C0/N0 ratio was calculated from the
experimental data reported by these authors).
The phenomenon of dilution rate-dependent PHA accumulation can be
attributed to the generally observed fact that the microbial
cell
composition is more flexible at lower growth rates (
19).
The
calculated specific PHA accumulation rates of the non-PHA
biomass are
around 14 wt%/h(Table
1) for intermediate dilution
rates (0.1, 0.2, and 0.3 h
1). This indicates that
P. oleovorans
produces PHA at a maximum
rate at these growth rates. At a dilution
rate of 0.4 h
1 the specific PHA accumulation rate was
below 11%/h, which suggests
that at this dilution rate, which is close
to µ
max, the intracellular
nitrogen limitation is
probably not as strong as at lower dilution
rates.
Dual nutrient limitation as a tool for growth medium
optimization.
The phenomenon of growth under dual-nutrient-limited
conditions at a constant dilution rate has been described previously (7, 11, 13, 15, 25, 28, 36, 40). It has also been
conjectured that the zone of multiple-nutrient limitation should be a
function of the growth rate (13, 14). However, only one
report is known which actually presented some experimental evidence for
this hypothesis (28). Here, we conducted the first investigation focusing on the relation between the growth rate and the
extension of the dual-nutrient-limited growth zone in combination with
the accumulation of a nutrient storage compound.
The work reported here has several important implications. First, the
data clearly demonstrate that the design of a microbial
growth medium
for chemostat cultures needs close attention. For
instance, a
carbon-limited growth medium used for low dilution
rates can become
dual nutrient limited or even nitrogen limited
at higher dilution
rates. Second, it is obvious that the concentrations
of residual
nutrients are also dependent on the dilution rate.
This is of special
interest for inhibitory or even toxic substrates,
where very low
(actual) concentrations in the culture supernatant
are of crucial
importance. For example, the decrease of formed
CDW above the
dual-nutrient-limited growth zone at dilution rates
of 0.4 and 0.3 h
1 may have been caused by the inhibitory effect of
residual octanoate
(compare reference
35).
Additionally, it has been pointed out
recently that for the industrial
production of mcl-PHA, the amount
of carbon substrate used must be
minimized because the price of
the carbon source has a major influence
on the production costs
of the end product (
8,
17).
Cultivation of the cells at the
upper boundary of the
dual-nutrient-limited growth zone satisfies
both requirements: low
actual concentrations of possibly unfavorable
nutrients and optimum
utilization of the growth substrates
supplied.
 |
ACKNOWLEDGMENT |
This research was supported in part by the Swiss Priority
Programme for Biotechnology, grant NF-5002-37951.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Department of
Microbiology, EAWAG, Überlandstrasse 133, CH-8600
Dübendorf, Switzerland. Phone: 41 1 823 51 58. Fax: 41 1 823 55 47. E-mail: egli{at}eawag.ch.
 |
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Applied and Environmental Microbiology, August 2000, p. 3408-3414, Vol. 66, No. 8
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