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First published online August 30, 2006
Journal of Experimental Biology 209, 3516-3528 (2006)
Published by The Company of Biologists 2006
doi: 10.1242/jeb.02404
Metabolite uptake, stoichiometry and chemoautotrophic function of the hydrothermal vent tubeworm Riftia pachyptila: responses to environmental variations in substrate concentrations and temperature
1 Harvard University, 16 Divinity Avenue, Biological labs room 3085,
Cambridge, MA 02138, USA
2 University of California Santa Barbara, Department of Ecology, Evolution
and Marine Biology, Santa Barbara, CA 93106, USA
* Author for correspondence (e-mail: pgirguis{at}oeb.harvard.edu)
Accepted 26 June 2006
| Summary |
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Key words: metabolism, stoichiometry, Riftia, hydrothermal vent, chemoautotrophy, symbiosis
| Introduction |
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Accordingly, Riftia must acquire both reduced and oxidized
substrates for chemoautotrophic metabolism and therefore thrives in diffuse
flow regimes, positioning its plume-like gill at the interface of vent flow
and bottom-water mixing (Childress et al.,
1991
). However, this niche is spatially and temporally
heterogenous (Johnson et al.,
1986
). Environmental chemistry in diffuse flows is wildly variable
on short-time scales (Johnson et al.,
1986
; Johnson et al.,
1988
), with dissolved inorganic carbon concentrations ranging from
2 to >12 mmol l-1, hydrogen sulfide from undetectable to 725
µmol l-1, and dissolved oxygen and nitrate concentrations
ranging from 0 to 110 µmol l-1 and 0 to 40 µmol
l-1, respectively (Shank et
al., 1998
; Luther et al.,
2001
; Mullineaux et al.,
2003
; Le Bris et al.,
2006
). Temperatures at diffuse flow sites have been observed to
vary between 2 to 25°C, and also to change rapidly over time
(Chevaldonne et al., 1991
;
Johnson et al., 1988
).
Prior physiological studies of Riftia have largely focused on
characterizing the physiological and biochemical adaptations of host to
symbiont, as well as elucidating which metabolites are used by the symbioses
(Arp, 1988
;
Arp and Childress, 1983
;
Childress et al., 1984
;
Childress and Fisher, 1992
;
Childress et al., 1993
;
Felbeck et al., 1981
;
Fisher and Childress, 1984
).
To date, little is known about how environmental conditions such as metabolite
concentrations, pH and temperature influence the metabolism (and ultimately
growth) of Riftia and its symbionts. The aforementioned spatial and
temporal environmental variability makes it impractical to ascertain such
relationships in situ. Accordingly, the experiments presented here
examined the relation between Riftia metabolite uptake, symbiont
chemoautotrophic function, seawater metabolite concentrations, pH and
temperature using a shipboard high-pressure respirometry system. We conducted
our experiments over a range of environmentally relevant chemical
concentrations and temperatures to examine how thermal and chemical
fluctuations in situ might influence host metabolite uptake and
symbiont autotrophic function. We also examined the stoichiometric relations
among the major metabolites, as well as which chemical species are
preferentially acquired by Riftia.
| Materials and methods |
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Experimental apparatus
In all respirometry experiments, two of the pressurized aquaria contained
tubeworms while the third served as the control. To simulate the seawater
chemistry found in situ, 0.2-µm filter-sterilized seawater was
pumped into an acrylic gas equilibration column and bubbled with carbon
dioxide, hydrogen sulfide, oxygen and nitrogen or helium to achieve the
desired dissolved gas concentrations
(Kochevar et al., 1992
).
Seawater pH was adjusted by using a proportional pH controller and isoosmotic
HCl and NaOH solutions (Prominent Inc., Pittsburgh, PA, USA). A sodium nitrate
solution (in 0.2-µm filtered-sterilized seawater) was pumped into the
equilibration column to produce final seawater nitrate concentrations between
40 and 65 µmol l-1. Seawater from the equilibration column was
delivered to the three aquaria by high-pressure pumps (American Lewa, Inc.,
Holliston, MA, USA). High-pressure aquaria temperatures were maintained at
15°C by immersing them in a circulating waterbath, while aquaria pressures
were maintained at 27.5 MPa via diaphragm backpressure valves (Circle
Seal, Inc., Corona, CA, USA). Vessel effluents were directed through a
computer-controlled stream-selection valve that diverted one stream to the
analytical instrumentation every 7 min.
During the HOT 96 and HOT 97 expeditions, the analytical system consisted
of a membrane-inlet quadrupole mass spectrometer to determine all dissolved
gas concentrations, an inline pH electrode and a spectrophotometer for nitrate
analyses (Girguis et al.,
2002
; Girguis et al.,
2000
). During the LARVE 98 expedition, inorganic carbon
concentrations were measured using a carbon dioxide specific electrode
(pHoenix, Inc., Houston, TX, USA) mounted in a water-jacketed flow-through
cell. Hydrogen sulfide concentrations were determined by a quantitative
spectrophotometric assay (Guenther et al.,
2001
) using a Gilson spectrophotometer with a 250 µl
flow-through cell. Oxygen concentrations were determined by a silver/silver
chloride electrode (Cameron Instruments Inc., Guelph, ON, Canada) mounted in a
2 ml flow-through cell. All carbon dioxide, hydrogen sulfide and oxygen
measurements were confirmed and calibrated using a Hewlett-Packard 5890 Series
II gas chromatograph (Childress et al.,
1984
). During both experiments, pH was measured using a
double-junction pH electrode mounted in a water-jacketed flow-through cell,
and connected to Orion model 920A or Radiometer PHM 93 pH meter, while nitrate
was analyzed from discrete samples collected every 30 min using a quantitative
spectrophotometric assay (Girguis et al.,
2000
; Karlsson et al.,
1995
). Temperature was measured and recorded by a digital
thermometer (Fisher, Inc., Hampton, NH, USA).
Riftia acclimation and sampling, pre- and post-experimentation
Prior to all experiments, Riftia were placed in the respirometer
aquaria, and were maintained in conditions typical of those in situ.
These `typical' conditions are: total dissolved inorganic carbon (i.e.
CO2)=5.5-6 mmol l-1, total dissolved sulfide
(i.e.
H2S)=250-300 µmol l-1, dissolved
O2=90-180 µmol l-1, dissolved NO3=40-50
µmol l-1, pH=6.5, temperature=12°C, pressure=27.5 MPa.
Riftia were maintained in these conditions until `autotrophic'.
Autotrophic Riftia exhibit a net uptake of dissolved inorganic carbon
(DIC), oxygen and sulfide, as well as net elimination of proton equivalents.
This regularly occurs after 12 h following incubation.
During each experiment, while one or more factors were being varied, all
other dissolved substrate concentrations, as well as pH and temperature, were
held at the `typical' conditions previously described. Also during all
experiments, tubeworms were maintained at each interval for at least 1 h, or
until uptake rate reached a steady state. At the end of each experiment, worms
were promptly removed, weighed on a motion-compensated shipboard balance
(Childress and Mickel, 1980
),
dissected and frozen in liquid nitrogen for later analysis. In some cases,
empty worm tubes were returned to the pressure vessels for several hours, and
subjected to the same experimental conditions to determine what fraction, if
any, of the observed flux rates are attributable to bacterial growth or other
phenomena associated with the tubes. No significant contribution of bacteria
to the observed metabolite flux rates was measured in this or prior studies
(Girguis et al., 2000
). All
mass-specific rates are expressed in terms of wet mass.
Effect of varying environmental metabolite concentrations on metabolite flux rates
Sulfide
To determine which chemical species of hydrogen sulfide is taken up by
Riftia (sulfide, H2S, or bisulfide, HS-), as
well as the duration of uptake, four Riftia weighing 11.9-18.1 g each
were placed into two of the high-pressure aquaria immediately after being
collected during both the HOT 96 and HOT 97 expeditions (two worms were placed
into each vessel). During the HOT 96 expedition, tubeworms were maintained
until autotrophic and then
H2S was reduced to 50 µmol
l-1, while seawater pH was reduced to 5.66 over a 4 h period.
Afterwards, seawater
H2S was increased to 465 µmol
l-1 over a period of 18 h, at increments of 25-50 µmol
l-1. Next, seawater
H2S was again lowered to 50
µmol l-1 for 4 h while the pH was increased to 7.4 and seawater
CO2 was increased to 24 mmol l-1 (to maintain an
equivalent dissolved carbon dioxide concentration)
(Childress et al., 1993
;
Goffredi et al., 1997b
).
Seawater
H2S was then increased incrementally to 480 µmol
l-1 over a period of 11 h. During the HOT 97 expedition, tubeworms
were maintained until autotrophic and then seawater pH was maintained at 5.8
while
H2S was held at 359.3±8.26 µmol
l-1. pH was then increased and maintained at 7.48 over a 4 h period
while
H2S was maintained at 346.7±14.16 µmol
l-1.
To examine the relation between seawater
H2S
concentrations and
H2S uptake, four Riftia weighing
13.4-15.1 g were maintained at typical in situ conditions for 10 h
during the HOT 97 expedition. Seawater
H2S was then
increased from 0 to 870 µmol l-1 over a period of 12 h, at
increments between 50 and 100 µmol l-1.
To determine the duration that chemoautotrophy can be sustained by
blood-bound sulfide, three Riftia weighing 12.5-14.5 g each were
placed into high-pressure aquaria during the HOT 97 expedition (the two
smaller worms were placed in one vessel). Seawater
H2S was
lowered by decreasing the flow of sulfide gas into the equilibration column.
Seawater
H2S was monitored constantly until it decreased to
below our level of detection (ca. 5 µmol l-1)
(Childress et al., 1984
). pH
was maintained at 6.1, and all other factors were held at the `typical'
conditions previously described.
To examine the relation between oxygen and
H2S uptake
over a range of experimental
H2S concentrations, two
experiments were conducted during the HOT97 expedition. In the first
experiment, two Riftia weighing 12.2-17 g each were placed into the
high-pressure respirometers (one worm per chamber) and maintained in 80
µmol l-1
H2S. All other substrates were held
at `typical' concentrations. Next,
H2S was incrementally
increased from 80 µmol l-1 to 208 µmol l-1 over 23
h. In the second experiment, two Riftia weighing 9.1-13.6 g each were
placed into the high-pressure respirometers (one worm per chamber) and
maintained in 200 µmol l-1
H2S. All other
substrates were held at `typical' concentrations. Next,
H2S
was incrementally increased from 200 µmol l-1 to 843 µmol
l-1 over 26 h. During both experiments, pH was maintained at
6.1.
Oxygen
To examine the stoichiometric relation between the other major substrates
and oxygen uptake, five Riftia weighing 7.3-12.1 g each were placed
into two of the high-pressure aquaria during the HOT 96 expedition (three
worms were placed into one vessel and two worms were placed into the other
vessel). Seawater oxygen concentration was increased from 40 to 210 µmol
l-1 over a period of 23 h, at increments between 15 and 40 µmol
l-1. pH was maintained at 5.9, while all other factors were held at
the `typical' conditions previously described.
To determine the duration that chemoautotrophy can be sustained by blood-bound oxygen, three Riftia weighing 11.4-14.2 g each were placed into high-pressure aquaria during the HOT 97 expedition. Seawater oxygen was then quickly decreased to below our level of detection by gas chromatography (about 5 µmol l-1) by stopping the flow of oxygen and increasing the flow of N2 into the equilibration column. pH was maintained at 5.9, while all other factors were maintained at typical in situ conditions.
Inorganic carbon
To examine the relation between Riftia CO2 uptake and
experimental
CO2 concentrations, three Riftia
weighing 16-17 g each were placed into high-pressure aquaria during the HOT 96
expedition. Seawater
CO2 was increased from 2.1 to 16.5 mmol
l-1 over a period of 25 h (at 1 to 2.5 mmol l-1
increments) while maintaining pH at 5.9 via proportional pH
control.
To examine the relation between Riftia bicarbonate uptake and
experimental
CO2 concentrations, the aforementioned
Riftia were subject to the same experiment previously described,
except that seawater pH was maintained at 6.6 for the duration of the
experiment. In both these experiments, all other substrates were maintained at
typical in situ concentrations.
Temperature
To examine the effects of temperature on Riftia host and symbiont
metabolism, two experiments were conducted during the HOT 96 and LARVE 98
expeditions. During the HOT 96 experiment, four Riftia weighing
10.5-15 g each were placed into two of the high-pressure aquaria (two worms in
each aquaria). Initially, temperature was decreased to 5°C for 7 h,
increased to 10°C for 4 h, and then to 20°C for 3 h. During the LARVE
98 expedition, four Riftia weighing 12-16 g each were placed in
high-pressure aquaria (two in each aquaria). After the onset of autotrophy,
temperature was increased to 20°C for 2 h, 27.5°C for 3 h, 30°C
for 2 h and 35°C for 2 h.
Individual variation in Riftia metabolite uptake
In order to assess the variation in substrate uptake rates among individual
Riftia collected from different sites, we collected twelve
Riftia weighing 12.2-14.1 g, from three different geographical
locales, during our HOT 96, HOT 97 and LARVE 98 expeditions. The HOT 96, HOT
97 and LARVE 98 worms were collected from tubeworm clumps located near 12.48N,
103.56W, 9.46N, 104.16W, and 9.50N, 104.17W, respectively, at approximately
2250 m. All worms were collected via the DSV Alvin, and
brought to the surface in a thermally insulated container. All Riftia
were maintained in our high-pressure respirometry system at typical conditions
until autotrophic, during which time metabolite uptake and elimination were
recorded for 7 h or more.
Energetics of Riftia symbiont carbon metabolism
To examine the relation between environmental substrate concentration and
Riftia net carbon fixation (primary productivity), three experiments
were conducted during the HOT 97 expedition in which Riftia were
maintained in different experimental conditions that mimic `typical', `better'
and `best' habitats for chemoautotrophic function. In each experiment, four
Riftia were placed in the high-pressure flow-through aquaria until
the onset of autotrophy. Seawater conditions were then adjusted to simulate
the conditions at different diffuse flow sites. `Typical' conditions were
CO2=3.5±0.5 mmol l-1,
H2S=67±12.1 µmol l-1,
O2=97±9.2 µmol l-1, temperature= 10°C,
NO3-=40 µmol l-1, pressure=27.5 MPa.
`Better' conditions were
CO2=4.6±0.7 mmol
l-1,
H2S=167± 14.2 µmol l-1,
O2=112±7.2 µmol l-1, temperature=15°C,
NO3-=40 µmol l-1, pressure=27.5 MPa.
`Best' conditions were
CO2=10.8±0.5 mmol
l-1,
H2S=256±12.7 µmol l-1,
O2= 197±24 µmol l-1, temperature=15°C,
NO3-=40 µmol l-1, pressure=27.5 MPa. All
conditions were maintained for at least 15 h. Metabolite uptake rates recorded
after the first 8 h were used to calculate mean metabolite uptake rates. All
rates are expressed in terms of wet mass.
Data collection, statistics and plots
Data were collected by Labview 4.0. Rates were calculated using Microsoft
Excel, and all statistical analyses and regression plots were rendered on
Statview 5.0 (SAS Inc., Cary, NC, USA). 3-dimensional plots were rendered on
Transform (Fortner, Inc., Boulder, CO, USA)
| Results |
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H2S uptake occurs over a wide range of
H2S
concentrations at both pH 5.66 and 7.48 and increases with increasing seawater
H2S concentration (Fig.
1A,B). At pH 5.66, Riftia's
H2S uptake
rate is more responsive to increasing sulfide concentrations (as seen by the
steeper slope in Fig. 1A). At
both pH values the relation between
H2S uptake and
increasing environmental
H2S concentration appeared linear
between 100 and 450 µmol l-1
(Fig. 1A,B). In a separate
experiment, when pH was maintained at either 5.73 or 7.73 and seawater
H2S concentrations were held constant, Riftia
H2S uptake was continuous for over 14 h but there were no
significant differences in proton elimination rates or oxygen uptake rates
(P>0.05; Spearman correlation and Mann-Whitney U-test,
Table 1).
|
|
While increasing seawater sulfide concentrations up to 600 µmol
l-1 stimulated sulfide and oxygen uptake as well as proton
elimination (Fig. 2), higher
sulfide concentrations resulted in the diminishment of both
H2S and O2 uptake rates
(Fig. 2). During all
experiments,
H2S uptake rate correlated to oxygen uptake
rate (P=0.0017; Spearman correlation).
CO2 uptake,
however, did not linearly correlate to
H2S or O2
uptake, and appeared to decrease at higher seawater
H2S
concentrations.
|
When
H2S concentrations were reduced to below the limits
of detection (BLD) (Childress et al.,
1984
), O2 uptake rates were reduced to 2.88±0.89
µmol g-1 h-1
(Table 2). However,
CO2 uptake was sustained for 5.3 h and O2 uptake
was sustained for 3.5 h (after which O2 uptake continued at
approximately 20% of its original rate;
Table 2).
|
Oxygen
O2 uptake strongly correlated with seawater oxygen concentration
(P=0.0001; Spearman correlation;
Fig. 3). Total
H2S uptake also strongly correlated with oxygen uptake rate
at oxygen concentrations between 50 and 200 µmol l-1
(P=0.0001, Spearman correlation;
Fig. 3). Proton elimination
rate also correlated with seawater oxygen concentration (P=0.04;
Spearman correlation; Fig. 3).
No significant linear correlation was found between
CO2
uptake and O2 uptake rate (Fig.
3).
|
H2S uptake was >2 at environmental
H2S
concentrations between 100 and 200 µmol l-1 (autotrophic
O2 uptake was determined by subtracting the heterotrophic
O2 uptake rates measured prior to the onset of autotrophy;
Fig. 4A). At higher
concentrations of environmental
H2S, however, the ratio
dropped to <2 (Fig. 4B).
|
CO2 uptake correlated with CO2
but not HCO3- concentrations
(Fig. 5).
CO2
uptake appeared to plateau at 8 mmol l-1 CO2
concentrations, or approximately 16 mmol l-1 total inorganic carbon
(Fig. 5) with a maximum
CO2 uptake rate of about 34 µmol g-1
h-1 between 7 and 8 mmol l-1
(Fig. 5). Experiments at higher
CO2 were attempted but not completed due to problems with
gas solubility and decreased analytical resolution.
|
H2S uptake rates of 3.88±0.66 and 1.18±0.73
µmol g-1 h-1, respectively, and net
CO2 production (not uptake) of 1.09±0.80 µmol
g-1 h-1 (Fig.
6). At 10°C
CO2 uptake was 1.75±0.52
µmol g-1 h-1. From 10 to 25°C,
CO2,
H2S and O2 uptake rates
increased, with a Q10 of approximately 2.3. The sharp increase of
CO2,
H2S and oxygen uptake that occurs at
25°C is a marked departure from the trend at lower temperatures. Optimal
temperature for maximal Riftia
CO2 uptake is
approximately 27°C. Temperatures above 28°C resulted in sublethal
reductions in all three measured metabolite uptake rates. Lethal temperature
was reached between 30 and 35°C.
|
The energetics of Riftia symbiont carbon metabolism
Riftia maintained in three different environmental conditions (`typical',
`better' and `best') exhibited significant differences in metabolite uptake
rates as well as proton elimination rates
(Table 3). Molar ratios of
CO2 uptake to
H2S uptake ranged from 0.42
at the lower conditions to 1.06 at optimal conditions. Percent energy devoted
to carbon fixation was calculated from the energy required to reduce the
inorganic carbon to sucrose (-495 kJ mol-1)
(Kelly, 1982
) and from the
energy available from the oxidation of bisulfide to sulfate via
oxygen (-995 kJ mol-1) (Kelly,
1982
), and ranged from 21% to 53% at the typical and optimal
conditions, respectively.
|
Variability in Riftia metabolite uptake among individual specimens
No significant differences in
H2S,
CO2,
and oxygen uptake rates were observed between the Riftia collected
from the `BIOTRANSECT 2' site and the `13 North' site
(Table 4). However,
Riftia collected from the `BIOTRANSECT 1' site exhibited metabolic
uptake and elimination rates that were significantly different from the other
two individuals (P=0.0001, Mann-Whitney U-test) and were on
average 40-66% lower than the other two individual Riftia
(Table 4). Significant
differences in proton elimination rates were observed among all three
Riftia tubeworms (Table
4). While there were no superficial differences among the
Riftia, during subsequent dissections post-experimentation the
Riftia collected during the LARVE 98 cruise were found to contain
blackened trophosome in stark contrast to the green and red trophosomes of the
other worms (black trophosomes likely indicate poor symbiont health)
(Fisher et al., 1988a
).
|
While we experimented on worms ranging from 4 g to 19 g, this range was not to examine the effects of scaling on metabolic processes.
| Discussion |
|---|
|
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H2S and oxygen uptake
H2S and O2
uptake are highly correlated to one another when seawater
H2S and O2 concentrations are between 10 and 400
µmol l-1 (Fig.
3). These concentrations are largely representative of those found
in situ (Shank et al.,
1998
H2S uptake, and that sulfide oxidation cannot be
sustained solely by nitrate reduction
(Girguis et al., 2000
Because Riftia flourishes in the vent-seawater mixing regimes,
simultaneous exposure to both sulfide and oxygen is not likely to be
continuous and there may be periods of time in which Riftia is not
exposed to one substrate or the other
(Arndt et al., 1998
). However,
when we reduced seawater
H2S concentrations to below our
level of detection, Riftia
CO2 uptake was sustained
for 5.3 h, after which Riftia exhibited net
CO2
production and decreased oxygen consumption (the remaining oxygen uptake is
the host's aerobic respiration; Table
2). We believe this lag time reflects the consumption of
hemoglobin-bound sulfide in the vascular and coelomic hemolymph pools
(Arp and Childress, 1983
;
Childress et al., 1984
;
Zal, 1998
). A prior study
found that Riftia typically consists of 13.9% vascular blood and
19.5% coelomic fluid (Childress et al.,
1984
), and recent studies have found that vascular and coelomic
hemoglobin concentrations in Riftia are 3 and 0.5 mmol
l-1, respectively (J.J.C., unpublished). Using these values and
binding stoichiometries, and assuming that sulfide uptake rates prior to the
removal of sulfide reflect symbiont sulfide usage, we estimate that a worm
weighing 15 g should have enough bound sulfide to sustain autotrophy for
approximately 6 h, a figure comparable to our experimentally determined
value.
Although the presence of sulfide is a prerequisite to successful
colonization and growth of Riftia, exposure to elevated
H2S concentrations in situ may be detrimental to
Riftia's survival. Our data suggest that inhibition of symbiont
metabolism may have occurred after seawater
H2S
concentrations reached 700 µmol l-1
(Fig. 2). This is higher than
the 300 µmol l-1
H2S concentrations that
inhibited isolated symbionts in a prior study
(Fisher and Childress, 1984
).
After exposure to high sulfide concentrations, Riftia's oxygen uptake
rate was comparable to the oxygen uptake rates measured after eliminating
sulfide, further suggesting that symbiont sulfide oxidation was diminished.
Accordingly, the remaining oxygen uptake likely represents the heterotrophic
contribution of the host to total oxygen consumption. While we cannot
precisely ascertain the effect of elevated sulfide concentrations on the
Riftia's aerobic respiration, the similarity to the rates observed in
the absence of sulfide suggests that Riftia is not prone to sulfide
toxicity at 700 µmol l-1 seawater
H2S
concentrations (Fig. 2).
Nevertheless, we observed that all Riftia exposed to
H2S concentrations greater than 1.7 mmol l-1 in
our high-pressure aquaria quickly die. While prior measurements of sulfide
concentrations around Riftia clumps in situ have shown that
concentrations vary from 0 to 500 µmol l-1 in the water
surrounding the worms (Johnson et al.,
1988
), other studies have measured sulfide concentrations around
Riftia clumps of approximately 2 mmol l-1
(Shank et al., 1998
). These
observations suggest that Riftia may be exposed to higher levels of
sulfide in situ than previously thought, and may experience symbiont
sulfide inhibition in situ.
Oxygen inhibition of symbiotic function was not observed to occur at
environmentally relevant oxygen concentrations
(Fig. 3) even though these are
much higher than the concentrations shown to inhibit such function in symbiont
preparations (Fisher and Childress,
1984
; Fisher et al.,
1989
; Scott et al.,
1994
). While these prior studies demonstrated the role of oxygen
in sustaining sulfide oxidation by isolated symbionts, they also showed that
they are microaerophilic, using oxygen as a terminal electron acceptor in
sulfide oxidation but being inhibited at low concentrations of free oxygen.
Although no data are available on the free oxygen concentrations (i.e. unbound
oxygen) within the bacteriocytes of intact associations, the present data
support previous suggestions that free oxygen concentrations within the
trophsosome are very low due to the high concentrations of very high oxygen
affinity hemoglobins in Riftia vascular and coelomic fluids.
|
H2S
uptake rates over a range of environmental
H2S
concentrations at both acidic and basic pH values, (ca. 5.5 and ca. 7.6;
Fig. 1 and
Table 1). At pH 5.5,
approximately 99% of the
H2S is hydrogen sulfide (the
pKa is approximately 6.8 at the conditions in our respirometer
system). At pH 7.6, approximately 90% of the
H2S is
bisulfide. Riftia's uptake rates at each pH demonstrate that both
H2S and HS- can be acquired because the uptake of the
minor sulfide species could not support the observed mass-specific
H2S uptake rates. Although Riftia may possess
mechanisms that reduce the influx of membrane-permeable hydrogen sulfide in
order to limit sulfide toxicity (Menon et
al., 1995While the precise role of each of these mechanisms remains to be determined, epithelial mitigation of H2S diffusion, together with the high-affinity HS- binding hemoglobins, may be the most effective means by which Riftia minimizes the effects of sulfide toxicity on host aerobic pathways while maintaining a large pool of sulfide available for symbiont metabolism.
We also observed higher ratios of oxygen uptake to
H2S
uptake at lower seawater
H2S concentrations
(Fig. 4A). Because the
oxidation of sulfide to sulfate stoichiometrically requires 2 O2
per sulfide, O2 uptake:
H2S uptake ratios >2
can support the complete oxidation of
H2S to sulfate. This
observation supports the prior hypotheses that sulfide oxidation yields
sulfate as an end product (Girguis et al.,
2002
; Goffredi et al.,
1997a
; Wilmot and Vetter,
1990
). However at higher seawater
H2S
concentrations, when the ratio dropped to <2
(Fig. 4B), we posit that a
fraction of the
H2S may be oxidized to elemental sulfur.
Elemental sulfur is commonly found in high concentrations in the trophosome of
healthy Riftia, and is thought to be a means of storing substrate
(Fisher et al., 1988a
;
Childress et al., 1991
). In
addition, some fraction of the reductive potential from sulfide oxidation is
likely used in inorganic carbon fixation, and that may lead to a shift in the
ratio of oxygen uptake to
H2S uptake. Thus, the data shown
in Fig. 4 suggest that the end
product of sulfide oxidation gradually shifts from sulfate to sulfur at higher
seawater
H2S concentrations, and that carbon fixation may
increase as the reductive potential from sulfide is more available.
Riftia
CO2 uptake
Our data demonstrate that CO2 is the chemical species of
inorganic carbon that is acquired (Fig.
5), which is consistent with previous in vitro and whole
animal studies (Childress et al.,
1993
; Fisher et al.,
1988b
; Fisher et al.,
1990
; Goffredi et al.,
1997b
; Scott,
2003
). There is no indication that bicarbonate is acquired, even
at higher pH. The
CO2 uptake rate appears highly correlated
to environmental CO2 concentrations
(Fig. 5). Because higher
environmental CO2 concentrations would provide a larger gradient
and thus more rapid diffusion (Goffredi et
al., 1997b
), the asymptote of
CO2 uptake rates
at 8 mmol l-1 environmental carbon dioxide concentrations may
reflect a physiological or biochemical limitation in symbiont carbon fixation,
although further studies would be required to verify this hypothesis.
Although linear correlations between Riftia
CO2
uptake rate and
H2S or oxygen uptake rate were never
observed (Fig. 5), our data
show that Riftia carbon uptake is stimulated by exceeding `threshold'
seawater
H2S and oxygen concentrations
(Fig. 7). Future studies should
continue to interrogate the relation between energy production (via
sulfide oxidation) and carbon fixation.
The issue of carbon limitation in Riftia has been debated for some
time (Fisher et al., 1988b
;
Fisher et al., 1990
;
Scott, 2003
). While our data
show that Riftia acquires only 12.5% of the available CO2
(implying that Riftia is not carbon limited), Riftia's
CO2 uptake rate consistently responded to increasing
seawater
CO2 throughout the duration of the experiment (up
to 16 mmol l-1
CO2). However, this observation
that Riftia
CO2 uptake is, strictly speaking,
responsive to changes in seawater
CO2 concentrations does
not imply that Riftia is carbon limited. This may be attributable to
limitations in another substrate besides DIC. Furthermore, we did not
determine if increasing seawater
CO2 concentrations led to
biomass accumulation or, alternatively, glycogen accumulation, so the precise
relation between increased carbon uptake (and presumably fixation) and growth
remains unresolved. This too warrants further investigation.
Temperature effects on Riftia uptake rates
The strongest determinant of metabolite flux, besides limiting substrate
concentrations, was temperature. Fig.
6 shows that a sharp increase in
CO2,
H2S and oxygen uptake occurs at 25°C, a marked departure
from the trend at lower temperatures. These data suggest that optimal
temperature for maximal Riftia uptake, presumably a reflection of
symbiont primary productivity, is between 25 and 27°C. Prolonged exposure
to temperatures above 32 to 35°C appears to be lethal as all
Riftia maintained at these temperatures were dead after 2 h. While a
prior study suggested that Riftia tubeworms were growing rapidly in
diffuse vent flows with temperatures ca. 35°C
(Shank et al., 1998
), diffuse
vents are complex thermal regimes and it is unlikely that Riftia
encounters chronic exposure to these high temperatures. Instead,
Riftia may tolerate acute exposure to high temperature in order to
acquire the sulfide necessary to sustain symbiont autotrophic metabolism. It
is notable that Riftia's maximal metabolite uptake (and therefore
symbiont primary production) occurs at temperatures near their maximal thermal
tolerance.
Thermodynamic efficiency
At steady state, when both the experimental conditions and Riftia
metabolite uptake have remained constant for several hours,
CO2 and
H2S uptake are reliable proxies
for carbon fixation and sulfide oxidation rates because they represent the
continuous rate of substrate utilization by the symbionts. Accordingly, we
determined the mean molar ratios of Riftia
CO2 and
H2S uptake to examine the stoichiometric relation between
carbon fixation and substrate oxidation by the chemoautotrophic symbionts
(Table 3). In our experiments,
Riftia's
CO2:
H2S uptake ratio
varied from 0.42 to approximately 1.06 over a range of environmentally
relevant substrate concentrations (Table
3). In a prior study of the bivalve Solemya reidii, a
clam with chemoautotrophic symbionts in its gill filaments,
CO2 and
H2S uptake molar ratios of
0.86-0.92 were measured (Anderson et al.,
1987
). These ratios can also be expressed as `efficiencies', in
which the energy utilized in carbon fixation (the conversion of CO2
to organic carbon) is expressed as a percentage of the total energy available
from the oxidation of sulfide to sulphate
(Kelly, 1982
). Riftia
efficiencies range from 21% to 53% at `typical' and `best' conditions,
respectively. In general, it has been observed that more than 80% of the total
energy budget of non-hydrogen-oxidizing chemolithotrophs is used in converting
carbon dioxide to carbohydrates (Kelly,
1982
). The allocation of this energy has been used to explain why
the growth yields of chemolithotrophs (already limited by the relatively low
molar energy yield of their substrates) are in general rather meager
(Kelly, 1990
). However, our
data demonstrate that Riftia symbionts allocate a smaller percentage
of their total energy to carbon fixation and nitrate reduction when compared
to free-living chemolithotrophic bacteria
(Kelly, 1990
). This may be
attributable to their symbiotic lifestyle since these bacteria do not have to
support a myriad of other energy intensive tasks (e.g. spinning flagellae)
common among free-living bacteria. These data, as well as the high rates of
substrate utilization by Riftia, may explain how Riftia
sustains its rapid growth.
Variability in Riftia metabolite uptake among individual specimens
We observed substantial individual variation in metabolite flux. Under
identical experimental conditions, individual Riftia exhibited
differences in
CO2 uptake that ranged from 4.3 to 15.7
µmol g-1 h-1
(Table 4). The differences in
these carbon uptake rates may reflect the history of the habitat at different
collection sites, and those worms with the highest
CO2
uptake rates may have been collected from tubeworm clumps growing atop ample
diffuse flow and as such have more metabolically active symbionts. Our
observation of blackish trophosomes in the worms with the lowest
chemoautotrophic metabolic rates supports this supposition. In situ
conditions are highly variable and as such can strongly affect Riftia
symbiont metabolism.
The net effect of environmental conditions on Riftia primary productivity
At steady state, Riftia net
CO2 uptake reflects
the rate of chemoautotrophic carbon fixation, and can be considered net
primary productivity. After placing freshly collected Riftia into the
high-pressure aquaria and prior to the onset of autotrophy, we measured the
response of
CO2 flux to increases in either
H2S or O2 uptake, and observed no discernable
change in
CO2 flux. However, we observed that concomitant
increases in both
H2S and O2 uptake correlated
with
CO2 uptake. Specifically,
CO2 uptake
drastically increases after seawater
H2S and oxygen
concentrations exceed 86 and 95 µmol l-1, respectively
(Fig. 7). In every respirometry
experiment conducted to date, the onset of autotrophy was preceded by a rapid
increase in Riftia
H2S and O2 uptake
(enough to consume much of the dissolved metabolite in the aquaria). Whereas
in a prior study Riftia required
H2S concentrations
greater than 90 µmol l-1 to support net carbon fixation
(Childress et al., 1991
), the
current study measured net
CO2 uptake occurring at
substantially lower levels of sulfide and oxygen, e.g. 50 µmol
l-1 and 70 µmol l-1 respectively
(Fig. 3), but only after the
threshold
H2S and oxygen concentrations had been exceeded
prior to being reduced. The observed phenomenon suggests that (i) carbon
fixation is directly mediated by the binding and loading of oxygen and sulfide
by Riftia hemoglobins or, alternatively, (ii) that Riftia
(or its symbionts) actively modulates inorganic carbon uptake in response to
seawater substrate concentrations, maintaining modest carbon fixation until
seawater substrate concentrations are sufficient to support elevated primary
productivity. Further studies are required to better address these
hypotheses.
In concert, these data demonstrate that Riftia metabolite uptake is strongly governed by environmental substrate availability and temperature. Riftia symbiont carbon fixation was observed to be highest after sufficient oxygen and sulfide has been acquired by Riftia, and when temperatures are relatively high. While the relation between symbiotic function and environmental variability is both facilitated and complicated by the presence of the host, the ultimate constraint on symbiont autotrophic function is the availability of substrates from the environment, and in general Riftia is extremely well-poised to buffer the spatial and temporal variations that are characteristic of diffuse flow regimes. Future studies using longer time-averages of metabolite flux may allow us to develop predictive models of environmental conditions based upon biota observations and, conversely, models of Riftia primary productivity based on in situ chemical and temperature measurements.
| Acknowledgments |
|---|
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|---|
|
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