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First published online July 20, 2006
Journal of Experimental Biology 209, 2939-2951 (2006)
Published by The Company of Biologists 2006
doi: 10.1242/jeb.02342
Feeding and osmoregulation: dual function of the marine teleost intestine
Rosenstiel School of Marine and Atmospheric Science, University of Miami, 4600 Rickenbacker Causeway, Miami, FL 33149-1098, USA
* Author for correspondence (e-mail: jtaylor{at}rsmas.miami.edu)
Accepted 22 May 2006
| Summary |
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Key words: acid-base balance, alkaline tide, Cl-/HCO -3 exchange, Gulf toadfish, Opsanus beta
| Introduction |
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In addition to digestion, the gastrointestinal tract of marine fish plays
an important role in osmo- and iono-regulation, as hypo-osmoregulating fish
have long been known to drink seawater to replace water lost diffusively to
their environment. Ingested seawater passes through the gastrointestinal tract
and ions must be differentially absorbed across the intestinal epithelium to
facilitate water absorption. A large portion of Cl- and water
absorption in the intestine is accomplished via apical
Cl-/HCO -3 exchange
(Grosell et al., 2005
), making
intestinal anion exchange an important addition to long-recognized
cotransporters Na+-Cl- and
Na+-K+-2Cl- in the marine teleost intestine.
The HCO -3 that is consequently secreted into the
intestinal lumen is present at levels approximately five- to tenfold plasma
concentrations (Wilson et al.,
2002
; Taylor and Grosell,
2006
) in starved fishes, indicating an active transport mechanism
(for a review, see Grosell,
2006
).
Bicarbonate secretion also seems to play a role in calcium homeostasis,
inhibiting intestinal Ca2+ absorption by precipitating
CaCO3, which is subsequently excreted
(Wilson et al., 2002
;
Wilson and Grosell, 2003
).
This carbonate precipitation in itself also promotes water absorption,
lowering osmolality by removing Ca2+ and CO
2-3 from solution
(Wilson et al., 1996
;
Wilson et al., 2002
;
Marshall and Grosell, 2006
).
High Ca2+ concentrations alone
(Wilson et al., 2002
) and
elevated ambient salinity (Walsh et al.,
1991
; McDonald and Grosell,
2006
; Taylor and Grosell,
2006
) have been shown to stimulate HCO -3
secretion, which is not surprising considering the role of intestinal anion
exchange in Cl- and water absorption
(Grosell et al., 2005
) (for a
review, see Grosell, 2006
).
In designing our experiments we considered the potential of high salinity in general, and high Ca2+ concentrations specifically, to stimulate Cl-/HCO -3 exchange, along with the great osmoregulatory challenge we imagine must be associated with ingesting a large meal and associated salts. We aimed to explore the effects of a high Ca2+ and a low Ca2+ diet (and feeding in general) on intestinal HCO -3 secretion and osmoregulation in Gulf toadfish Opsanus beta. By investigating the effects of feeding on gastrointestinal fluid chemistry, and thereby gaining more information about intestinal anion exchange, we aim to better understand the function, regulation, and mechanism(s) of apical Cl-/HCO -3 exchange. Gastrointestinal fluids and blood plasma were sampled in a detailed time course post-feeding to reveal the timeline for organic and inorganic nutrient absorption across the intestine for differing diet composition. In addition, a detailed time course of blood plasma chemistry allowed for investigation of the possibility of postprandially disturbed acid-base balance and osmoregulatory compromise.
| Materials and methods |
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, mean and range) and fed their respective experimental
diet (see below) to satiation once weekly, for approximately 3 weeks prior to
experimentation.
General experimental procedures
Two natural experimental diets were determined based on our knowledge of
Ca2+-induced HCO -3 secretion in European
flounder. A squid diet (Loligo forbesi, see
Table 1 for inorganic ion
composition) represented a low Ca2+ meal, while a fish diet
(Sardina pilchardus, see Table
1 for inorganic ion composition) corresponded to a relatively high
Ca2+ meal. Both experimental diets represent realistic meals for
O. beta. Gulf toadfish were starved for 12 days prior to feeding to
ensure resting conditions. In the initial experiment, 60 fish (mass
64±3.5 g, mean ± s.e.m.) were fed one of the two experimental
diets to satiation (all uneaten food was removed after 30 min) and terminally
sampled in groups of five fish pre-feeding (12 days following their last
meal), 1, 2, 3, 6 and 9 days after feeding. Based on the results of this first
experiment, followup sampling was done on another 50 toadfish (mass
80±3.5 g) fed the same two diets and sampled in groups of five fish
prefeeding (again 12 days following their last meal), 3, 6, 12 and 24 h after
feeding. The final data set comprises timepoints 0, 3, 6, 12, 24, 48, 72, 144
and 216 h post-feeding. Data reported in the 24 h timepoint were taken
exclusively from the second experiment as sample time was monitored more
precisely in this more detailed trial. Experimental fish were euthanized by a
tricaine methane sulfonate overdose (0.5 g l-1 MS-222, pH 8.0),
after which a blood sample (200-400 µl) was obtained by caudal puncture
into a heparinized syringe fitted with a gauge 22 needle, and placed on ice.
The entire gastrointestinal tract was then carefully removed and ligated with
silk ligatures into stomach, anterior, mid, posterior and rectal segments as
previously described (Grosell et al.,
2004
). Each section was removed and contents were drained into 2
ml plastic microcentrifuge tubes (15 ml Falcon tubes for stomach contents) for
analysis. At the 3 h timepoint, while most of the ingested meal remained in
the stomach, contents were weighed to estimate meal size relative to body
mass. Our experimental design was such that fish sampled at each timepoint
(N=5) were taken exclusively from one 75 liter tank containing only
these fish. Thus, any effects of dominance/hierarchy on food intake would have
revealed themselves amongst the five fish from each diet sacrificed at 3 h
post-feeding and used to estimate meal size.
|
Sample analysis
All blood samples were promptly analyzed for hematocrit and then
centrifuged (2 min at 15 700 g). Plasma was retained in
addition to gastrointestinal fluid samples (only the supernatant of
gastrointestinal fluid samples was retained after centrifugation to eliminate
reaction with solid meal remains) for immediate analysis of pH (Accumet pH
electrode connected to a Radiometer PHM220 pH meter, Copenhagen, Denmark).
Total CO2 was analyzed using a Corning 965 Carbon Dioxide Analyzer
(Corning, NY, USA) and osmolality was measured using a vapor pressure
osmometer (Wescor Vapro 5520, Logan, UT, USA). Samples were stored at
-20°C for subsequent analysis of inorganic anions (Dionex DX-120,
Sunnyvale, CA, USA) and cations (Fast Sequencial atomic absorption
spectrophotometry, Varian FS220, Palo Alto, CA, USA) after appropriate
dilution.
Osmotic coefficient calculation
Osmotic coefficients of representative monovalent (NaCl) and divalent
(MgSO4) solutions were calculated by making, in triplicate, 150
mmol l-1 solutions of each and measuring osmolality using a vapor
pressure osmometer (Wescor Vapro 5520). The osmotic coefficient was calculated
by dividing the measured osmotic pressure of each solution by 300 mOsm (the
expected osmotic pressure assuming an osmotic coefficient=1).
Statistical analyses
Due to variable amounts of fluid present in each gastrointestinal segment
at different stages after a meal, means were generally from five samples
(except for the control timepoint, in which up to ten samples were collected
for each parameter), but at times, some samples were too small to be analyzed
for every parameter. Of a total 720 means, 8% (59) contained 10 samples; 3%
(19) contained 9 samples; <1% (2) contained 8 samples; 63% (455) contained
5 samples; 17% (119) contained 4 samples; 5% (36) contained 3 samples, 3% (21)
contained 2 samples, 1% (8) contained 1 sample, and <1% (1) means were
omitted because no samples contained sufficient fluid for analysis. Data are
presented as means ± 1 s.e.m. In analyses of organic nutrient
absorption, total inorganic ion concentration was calculated from the
inorganic ion concentrations measured in each sample for each time point
(including only samples in which sufficient fluid was collected to measure
every ion). This provides a conservative estimate of osmotic pressure exerted
by inorganic ions by assuming an osmotic coefficient of one. Because data were
not normally distributed, Kruskal-Wallis one-way analysis of variance (ANOVA)
on ranks was used to evaluate all data, followed, where applicable, by
comparisons of each parameter at each time point to control values by Dunn's
method. When only two groups were compared, a Mann-Whitney Rank Sum test was
used to determine statistically significant differences. Means were considered
significantly different at P<0.05. For the sake of clarity,
significant differences are not noted in figures or tables but rather are
described in detail in the Results section.
| Results |
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Postprandial intestinal Cl-/HCO -3 exchange
In both high and low Ca2+ diets, pH
(Fig. 1) and total
CO2 (HCO -3 equivalents,
Fig. 2) levels in
gastrointestinal fluids indicated that postprandially increased HCO
-3 secretion acted as a buffer for H+
secreted and subsequently released from the stomach with chyme. Between 3 and
24 h post-feeding, intestinal fluid HCO -3 equivalents
were reduced to as little as 50% of control levels
(Fig. 2,
Table 2), a decrease that was
statistically significant only in the mid intestinal fluid 3 h after feeding a
squid diet. Luminal pH was also slightly depressed at these timepoints,
especially in the anterior and mid intestinal fluid
(Fig. 1,
Table 2), where pH was
significantly reduced from control levels 3 h after feeding sardines.
Correspondingly, 48 h after feeding (presumably once stomach secretions were
neutralized), a dramatic increase in HCO -3 equivalents
was measured relative to control levels. Bicarbonate equivalents on average
were present at 231% and 204% of control levels in the anterior intestinal
fluid 48 h after feeding fish and squid diets, respectively
(Fig. 2,
Table 2), although limited
sample sizes prohibited statistical significance. This rise over control HCO
-3 concentrations was most dramatic in the anterior
intestine of both diets 48 h post feeding, and was sequentially less
pronounced in the more posterior sections, indicating that postprandial HCO
-3 secretion might be prevalent in the anterior
intestine. Notably, these HCO -3 measurements are based
exclusively on intestinal fluid concentrations, and neglect to account for any
additional increases in HCO -3 concentration accounted
for by CaCO3 precipitation. Overall, HCO -3
concentrations of intestinal fluids ranged from 4- to 20-fold control plasma
levels (Tables 2 and
3, respectively).
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Postprandial luminal Cl- concentrations (Fig. 3, Table 2) in both diets support an increase in intestinal Cl-/HCO -3 exchange post-feeding. Intestinal fluid Cl- concentrations were reduced from control levels between 3 and 48 h post-feeding in both squid and sardine diets. This difference from control conditions was statistically significant in the anterior, mid and posterior intestinal fluid between 6 and 24 h post-feeding in toadfish fed a squid diet, and at 12 h and 24 h timepoints in toadfish fed sardines. Additionally, a slight (though not statistically significant using Kruskal-Wallis one-way ANOVA on ranks) increase in plasma Cl- concentration over control levels was measured between 12 and 48 h post feeding in toadfish fed squid (Table 3).
|
While luminal Cl- concentrations were reduced post-feeding, no such trend was observed for Na+ concentrations (Fig. 4, Table 2), yielding additional evidence for enhanced postprandial apical Cl-/HCO -3 exchange as opposed to Na+-Cl- cotransport.
|
Consequences of high dietary Ca2+ and K+ loads
While unfed (control) toadfish maintained low intestinal Ca2+
concentrations, fed toadfish experienced up to a tenfold postprandial increase
in intestinal Ca2+ concentrations
(Fig. 5,
Table 2). In toadfish fed a
squid diet, Ca2+ concentrations were significantly elevated over
control conditions at 24 h post-feeding in the anterior intestine fluid, 12
and 24 h post-feeding in mid and posterior intestine fluid, and 48 h
post-feeding in rectal fluid. In toadfish fed sardines, however,
Ca2+ seemed to be liberated into the intestinal fluid sooner, as
concentrations were significantly elevated at 6 and 12 h post-feeding in the
anterior and mid intestine fluid, and 24 h post-feeding in the rectal fluid. A
notable difference in diet composition was evident in stomach Ca2+
concentrations, which were significantly higher in fish fed sardines and
maximal 12 h post-feeding (77.4±6.52 mmol l-1) in these fish
(Fig. 5B). In toadfish fed a
squid diet, stomach Ca2+ concentrations were maximal 3 h
post-feeding (6.8±0.32 mmol l-1;
Fig. 5A). Despite the intense
Ca2+ load to the gastrointestinal tract of toadfish fed sardines,
no increase in plasma Ca2+ concentration was observed in fish fed
either diet (Table 3).
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Intestinal water absorption and divalent ion concentration
Immediately following feeding, mean intestinal Mg2+ and SO
2-4 concentrations were reduced to as little as 36% and
42% of control concentrations, respectively, in toadfish fed a squid diet
(Fig. 7A and
Fig. 8A, respectively, and
Table 2). This decline in both
Mg2+ and SO 2-4 concentrations was
statistically significant only in the mid intestinal fluid 3 h post-feeding. A
postprandial reduction in intestinal Mg2+ and SO
2-4 concentrations was also noted in toadfish fed
sardines (Fig. 7B and
Fig. 8B, respectively, and
Table 2), though these ions
were only reduced to as little as 65% and 50% control conditions,
respectively, and exhibited no statistically significant differences from
control concentrations. By 48 h post feeding, however, water absorption rather
than secretion appears to have resumed in full force as intestinal
Mg2+ and SO 2-4 concentrations return to and
even exceed their high levels in control fish.
|
Osmotic coefficients in monovalent and divalent solutions
Our experimental determination of divalent and monovalent solution osmotic
coefficients yielded an osmotic coefficient of 0.91 (±0.002) for the
monovalent solution NaCl, and an osmotic coefficient of 0.56 (±0.004)
for the divalent solution MgSO4. Thus a replacement along the
gastrointestinal tract of monovalent ions with divalent ions will facilitate
water absorption by lowering osmotic pressure in the lumen.
Organic nutrient absorption
By calculating the difference between measured osmolality and the sum of
inorganic ion concentrations in a given sample, we were able to conservatively
predict the concentration (mEqv) of organic solutes present in the sample.
Measured plasma osmolality is consistently significantly higher than the sum
of inorganic ions (Fig. 9A) of
fish fed both diets. In toadfish fed a squid diet
(Fig. 9Ai), there is a
statistically significant rise in plasma osmolality 12 h post-feeding, but not
a significant increase in the sum of inorganic ion concentration.
|
Disturbed acid-base balance?
Plasma pH (Table 3) did not
exhibit strong trends in toadfish fed either diet, although it was
significantly increased over control conditions at 3 h post-feeding in
toadfish fed a squid diet. No statistically significant changes were seen in
plasma pH of toadfish fed sardines. Also, no significant changes in plasma HCO
-3 (Table
3) were measured postprandially in either diet.
| Discussion |
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Postprandial intestinal Cl-/HCO -3 exchange
While we anticipated an influx of Cl- to the anterior intestine
due to the passage of gastric HCl secretions, we measured intestinal
Cl- concentrations that markedly decreased immediately (by 3 h)
following feeding and remained depressed for at least 48 h. Based on these
reduced luminal Cl- concentrations and on measurements of unchanged
Na+ concentrations between 3 and 48 h post-feeding, we presume that
elevated levels of intestinal HCO -3 at 48 h
post-feeding cannot be accounted for by pancreatic-like secretion. Pancreatic
secretions at least in higher vertebrates consist of a NaHCO3-rich
solution (Steward et al.,
2005
). Buffering of highly acidic chyme entering the intestine
from the stomach to circumneutral and alkaline pH likely consumes much of the
HCO -3 secreted into the intestine. Increased apical
Cl-/HCO -3 exchange may be stimulated
postprandially either by a signal directly related to the act of feeding, by
reduced luminal pH as has been shown in European flounder
(Wilson and Grosell, 2003
), or
by osmoregulatory challenges to the gastrointestinal tract that result from
ingesting a large meal. Regardless of the mechanism of stimulation, intestinal
Cl-/HCO -3 exchange appears beneficial both
in neutralizing luminal pH and in serving Cl- and water absorption
across the intestinal epithelium between 3 and 48 h after feeding. Immediately
(3 h) postfeeding, the anterior intestine of toadfish fed sardines becomes
more acidified (Fig. 1) and has
a higher Cl- concentration (Fig.
3) than that of toadfish fed a squid diet. These observations
together seem to indicate elevated gastric HCl secretion in fish fed sardines.
Correspondingly, toadfish fed sardines experienced the highest intestinal HCO
-3 levels we measured during these experiments at 48 h
postfeeding (Fig. 2B,
Table 2). While stomach pH was
not significantly different between fish fed the two diets at any time point,
we imagine that a larger volume of acid would be required to acidify chopped
fish (buffered by carbonate and phosphate salts characteristic of cycloid
scales and bone) to a similar pH as chopped squid. Common sense attests that
increased gastric acid secretion and/or a prolonged gastric holding time
should increase assimilation efficiency for a more difficult to digest meal
(i.e. a fish diet containing scales and bone). This topic has so far only been
discussed with reference to the potential of diet acidification to increase
phosphorus (as bone phosphate in fish meal) assimilation in aquaculture as a
means of reducing eutrophication by undigested P in these systems
(Vielma and Lall, 1997
;
Vielma et al., 1999
;
Sugiura and Hardy, 2000
). A
review of the pylorus (Ramkumar and
Schulze, 2005
) indicates that, at least in mammals tested to date,
the pylorus adjusts gastric outflow resistance to meet physiological needs as
a function of chemical (acidification) and physical (mechanical) action by the
stomach. We assume that the release of chyme is controlled by a similar
mechanism in toadfish which, like most teleosts, possess a true stomach and
pyloric sphincter. Notably, because our fish were fed to satiation, we
observed upon dissection that the stomach of nearly all fish was so distended
as to indicate the possibility that small amounts of chyme had entered the
anterior intestine regardless of the state of contraction of the pyloric
sphincter -a likely explanation for the immediate decrease in anterior
intestine pH following feeding. Many ectothermic vertebrates also experience
very large meals (often containing bone) at infrequent intervals; an
exceptionally high volume of gastric acid secretion and long holding time are
likely reasons for an especially pronounced alkaline tide response in these
animals (for a review, see Wang et al.,
2001
).
Intestinal HCO -3 secretion may also act in part to regulate acute dietary Ca2+ influx. In addition to a larger influx of HCl to the intestine of toadfish fed sardines, maximal Ca2+ concentrations (reached 6 h post-feeding) in the anterior intestine were over twofold those in fish fed a squid diet, yielding another possible reason for a larger peak of postprandial HCO -3 levels in toadfish fed sardines. This may suggest an additional role of postprandial intestinal HCO -3 secretion in leading to increased CaCO3 precipitation to serve Ca2+ excretion during digestion of high calcium meals, as plasma Ca2+ concentrations were not increased postprandially in either diet (Table 3). Notably, Ca2+ concentrations in the posterior intestinal and rectal fluids never reached levels as high as those measured in the anterior and mid intestine fluid (Table 2). This difference could be accounted for by increased CaCO3 precipitation, which was unaccounted for by our measurements, and likely is a main route of Ca2+ excretion in the absence of major Ca2+ absorption to the extracellular fluid.
Disturbed acid-base balance?
The statistically significant yet transient increase in plasma pH we
measured 3 h post-feeding in toadfish fed a squid diet
(Table 3A) indicates the
possibility of a postprandial alkaline tide; however, the inconsistency in
both control and treatment plasma pH values is a cause for reservation. The
absence of plasma alkalinization in toadfish fed sardines
(Table 3B), and unchanged
plasma HCO -3 concentrations in fish fed both diets
(Table 3), suggest that
feeding-induced acid-base balance disturbance is lacking in Gulf toadfish even
when fed a 9% (of body mass) meal. Notably, due to the nature of the caudal
puncture technique, blood samples may have contained a variable mixture of
arterial and venous blood and may also have been influenced by tissue lactic
acid release following anesthetic overdose. While our measurements indicated
the absence of acid-base balance disturbance, plasma pH and HCO
-3 concentrations were increased between 3 and 9 h after
feeding in Pacific spiny dogfish (Wood et
al., 2005
), with virtually no evidence of respiratory compensation
that is common among other vertebrate classes
(Andrade et al., 2004
).
It has been shown in fishes that ventilatory adjustments have only a small
effect on blood PCO2 levels
(Perry and Wood, 1989
;
Wood et al., 2005
) and thus we
would expect an alkaline tide to reveal itself exclusively in plasma pH and
HCO -3 concentrations as in the spiny dogfish
(Wood et al., 2005
). We
suggest additional experiments employing a more detailed time course, along
with cannulation to provide for continual sampling, on a larger number of
fish, before concluding the presence or absence of a postprandial alkaline
tide in Gulf toadfish. It is possible that plasma alkalinization might be
absent or reduced by branchial base efflux, although this was not measured in
our experiments. Metabolic HCO -3 is secreted by the
gastric oxyntopeptic cell (gastric epithelial cells in nonmammalian
vertebrates, secreting both HCl and pepsinogen) basolaterally into the
extracellular fluid as a mechanism of alleviating cellular alkalosis. This HCO
-3 may be immediately transported across the gill,
assumedly via either a Cl-/HCO -3
exchanger or Na+-HCO -3 cotransport [NBC; see
Evans et al. (Evans et al.,
2005
)], thus no plasma alkalinization would be measured. If this
is indeed the case, one may expect a more pronounced alkaline tide in
freshwater fish, in which branchial anion exchange would presumably be limited
by low environmental Cl- concentrations.
Another possible explanation for the lack of alkaline tide response lies in
intestinal HCO -3 secretion. As apical acid secretion by
the gastric oxyntopeptic cell prompts basolateral secretion of metabolic HCO
-3 into the extracellular fluid, it is possible that
this HCO -3 provides additional substrate for intestinal
Cl-/HCO -3 exchange, which appears to be
enhanced during digestion. This hypothesis, however, has several caveats. One
involves the uncertainty of possible mechanisms responsible for transporting
HCO -3 to the intestine from the serosal side of the
gastric oxyntopeptic cell. In fact, the mechanism transporting HCO
-3 to the systemic blood circulation thus creating an
alkaline tide has not yet been described (for a review, see
Niv and Fraser, 2002
). A
second caveat lies in the mechanism of HCO -3 entry into
the intestinal epithelium cell. Recent reports show that the majority of HCO
-3 secreted into the intestinal lumen to serve
osmoregulation arises from hydration of endogenous CO2 in the
epithelial cells of the intestine (Wilson
et al., 2002
; Grosell and Genz,
2006
) (reviewed by Grosell,
2006
). Therefore, we suppose that HCO -3
secreted basolaterally by the gastric parietal cells would have to either be
dehydrated to CO2 to enter the intestinal epithelium cell
diffusively, or an additional transport pathway, such as basolateral NBC, must
be supplying the intestinal epithelial cells with excess HCO
-3 during the period of postprandially stimulated HCO
-3 secretion. Clearly, postprandial acid-base balance in
seawater and freshwater fishes deserves additional attention.
Gastrointestinal water and monovalent ion absorption and divalent ion concentration
Intestinal Mg2+ and SO 2-4 concentrations
are good markers for water absorption
(Smith, 1930
), as these
divalent ions see only very modest absorption across the intestinal
epithelium, and are not known to precipitate to the extent that
Ca2+ does in intestinal carbonate pellets
(Walsh et al., 1991
). A drop
in luminal Mg2+ and SO 2-4 concentrations
between 3 and 48 h after feeding presumably indicates an influx of gastric,
biliary, intestinal and perhaps pancreatic secretions in addition to transient
diffusive water gain. The intestinal lumen and certainly the stomach contents
are hyperosmotic to the extracellular fluids, which would facilitate diffusive
water movement into the gastrointestinal tract. Additionally, seawater
ingestion has been shown both prandially via incidental intake and
postprandially via drinking
(Kristiansen and Rankin, 2001
).
Together, it appears that these factors act to temporarily dilute the divalent
ions that normally persist in marine teleost intestinal fluids
(Marshall and Grosell, 2006
).
An increase in Mg2+ and especially SO 2-4
concentrations over control levels at 48 h post-feeding, though not
statistically significant, indicates the possibility of a period of highly
increased intestinal water absorption. This is conveniently the same time
point at which intestinal HCO -3 levels are maximal,
luminal Cl- concentrations are still reduced, and organic nutrients
have been largely absorbed. Anterior intestinal fluid in both starved and fed
fish is composed predominantly of monovalent ions Cl- and
Na+, while a notable shift towards divalents Mg2+ and SO
2-4 occurs posteriorly. Based on our calculated osmotic
coefficients for monovalent and divalent solutions, an intestinal fluid rich
in divalent ions will act to facilitate water absorption in the posterior
intestine by enhancing the transepithelial osmotic gradient by reducing the
effective osmolality on the luminal side.
Organic nutrient absorption
Osmolality and inorganic ion sum measurements of gastrointestinal fluids
allow us to predict a timeline for organic nutrient absorption. Organic
nutrient absorption seems to occur in the greatest magnitude in the stomach of
toadfish fed a squid diet (Fig.
9Bi), and be completed in all segments of the intestine by 48 h
post feeding in both diets (Fig.
9C-F). In addition to diminishing over time, the amount of organic
solutes in the fluids of each intestinal segment at any given time is slightly
reduced in progressively posterior intestinal sections. This not only
indicates a consistent ability of the entire length of the intestinal
epithelium to absorb organic nutrients, but also indicates that organic
nutrients are truly being absorbed and not just passed along to posterior
sections of the gastrointestinal tract. In addition, we saw a clear shift in
intestinal fluid composition between 24 and 48 h post-feeding in which
osmolality decreases markedly and is exceeded by the sum of inorganic ions.
This indicates a trend towards divalent ions, which have a lower osmotic
coefficient than monovalents and thus account for the difference between
inorganic ion sum (which assumes an osmotic coefficient of one) and actual
osmolality. This difference between inorganic ion sum and actual osmolality is
elevated progressively in posterior sections, indicating that in addition to
organic nutrient absorption, water absorption also is consistent and
cumulative along the intestine.
A transient but significant increase in plasma osmolality 12 h post-feeding in toadfish fed a squid diet in the absence of a significant increase in inorganic ion sum might be attributed to a high amino acid content in squid, although organic solute concentrations were not measured directly in these experiments.
Conclusions
Above all, we have shown with these experiments that feeding transiently
and acutely alters the gastrointestinal physiology of Gulf toadfish, and that
these physiological changes are dependent upon diet composition. In addition
to dramatically changing both the inorganic and organic ionic composition
along the gastrointestinal tract, we also saw evidence for transient changes
in water and solute secretion and absorption across the gastric and intestinal
epithelia as time passed after feeding. By demonstrating a limited or lack of
postprandial alkaline tide, we have raised questions about postprandial
disruption to acid-base balance in seawater and freshwater fish, and the fate
of metabolic HCO -3 secreted basolaterally by gastric
oxyntopeptic cells. The next question begging an answer is the regulation of
intestinal HCO -3 secretion. Since we have shown strong
evidence that apical Cl-/HCO -3 exchange is
stimulated in the intestine by feeding, regardless of the diet, it is possible
that intestinal anion exchange is stimulated by parameters relating to
ingestion of a meal itself and/or by the osmoregulatory and acid-base
challenges that result. Conjecture might tie these questions of acid-base
balance and anion exchange together by explaining the lack of an alkaline tide
with increased intestinal HCO -3 secretion, although
this remains to be documented.
| Acknowledgments |
|---|
| References |
|---|
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|---|
Andrade, D. V., De Toledo, L. F., Abe, A. S. and Wang, T.
(2004). Ventilatory compensation of the alkaline tide during
digestion in the snake Boa constrictor. J. Exp. Biol.
207,1379
-1385.
Dabrowski, K., Leray, C., Nonnotte, G. and Colin, D. A. (1986). Protein digestion and ion concentrations in Rainbow trout (Salmo Gairdnerii Rich.) digestive tract in sea- and fresh water. Comp. Biochem. Physiol. 83A, 27-39.[CrossRef]
Evans, D. H., Piermarini, P. M. and Choe, K. P.
(2005). The multifunctional fish gill: dominant site of gas
exchange, osmoregulation, acid-base regulation, and excretion of nitrogenous
waste. Physiol. Rev. 85,97
-177.
Grosell, M. (2006). Intestinal anion exchange
in marine fish osmoregulation. J. Exp. Biol.
209,2813
-2827.
Grosell, M. and Genz, J. (2006). Ouabain sensitive bicarbonate secretion and acidic fluid absorption by the marine teleost intestine play a role in osmoregulation. Am. J. Phys. Regul. Physiol. In Press.
Grosell, M., O'Donnell, M. J. and Wood, C. M. (2000). Hepatic versus gallbladder bile composition: in vivo transport physiology of the gallbladder in rainbow trout. Am. J. Physiol. 278,RI674 -RI684.
Grosell, M., McDonald, M. D., Wood, C. M. and Walsh, P. J. (2004). Effects of Prolonged copper exposure in the marine gulf toadfish (Opsanus beta). I. Hydromineral balance and plasma nitrogenous waste products. Aquat. Toxicol. 68,249 -262.[CrossRef][Medline]
Grosell, M., Wood, C. M., Wilson, R. W., Bury, N. R., Hogstrand, C., Rankin, C. and Jensen, F. B. (2005). Bicarbonate secretion plays a role in chloride and water absorption of the European flounder intestine. Am. J. Physiol. 288,936 -946.
Kristiansen, H. R. and Rankin, C. J. (2001). Discrimination between endogenous and exogenous water sources in juvenile rainbow trout fed extruded dry feed. Aquat. Living Resour. 14,359 -366.[CrossRef]
Marshall, W. S. and Grosell, M. (2006). Ion transport and osmoregulation in fish. In The Physiology of Fishes (ed. D. Evans), pp. 177-230. Boca Raton, FL: CRC Press.
McDonald, M. D. and Grosell, M. (2006). Maintaining osmotic balance with an aglomerular kidney. Comp. Biochem. Physiol. 143A,447 -458.
McDonald, M. D., Grosell, M., Wood, C. M. and Walsh, P. J. (2003). Branchial and Renal handling of urea in the gulf toadfish, Opsanus beta: the effect of exogenous urea loading. Comp. Biochem. Physiol. 134A,763 -776.
Niv, Y. and Fraser, G. M. (2002). The alkaline tide phenomenon. J. Clin. Gastroenterol. 35, 5-8.[CrossRef][Medline]
Novak, I. (2000). Keeping up with bicarbonate.
J. Physiol. 528,235
.
Perry, S. F. and Wood, C. M. (1989). Control and co-ordination of gas transfer in fishes. Can. J. Zool. 67,2961 -2970.
Ramkumar, D. and Schulze, K. S. (2005). The pylorus. Neurogastroenterol. Motil. 17, 22-30.
Shehadeh, Z. H. and Gordon, M. S. (1969). The role of the intestine in salinity adaptation of the rainbow trout, Salmo gairdneri. Comp. Biochem. Physiol. 30,397 -418.[CrossRef]
Smith, H. W. (1930). The absorption and
excretion of water and salts by marine teleosts. Am. J.
Physiol. 93,480
-505.
Steward, M. C., Ishiguro, H. and Case, R. M. (2005). Mechanisms of bicarbonate secretion in the pancreatic duct. Annu. Rev. Physiol. 67,377 -409.[CrossRef][Medline]
Sugiura, S. H. and Hardy, R. W. (2000). Environmentally friendly feeds. In Encyclopedia of Aquaculture (ed. R. R. Stickney), pp.299 -310. New York: John Wiley & Sons.
Taylor, J. R. and Grosell, M. (2006). Evolutionary aspects of intestinal bicarbonate secretion in fish. Comp. Biochem. Physiol. 143A,523 -529.
Thomas, H. A. and Machen, T. E. (1991). Regulation of Cl/HCO3 exchange in gastric parietal cells. Cell Regul. 2,727 -737.[Medline]
Vielma, J. and Lall, S. P. (1997). Dietary formic acid enhances apparent digestibility of minerals in rainbow trout, Oncorhynchus mykiss (Walbaum). Aquac. Nutr. 3, 265-268.
Vielma, J., Ruohonen, K. and Lall, S. P. (1999). Supplemental citric acid and particle size of fish bone-meal influence the availability of minerals in rainbow trout Oncorhynchus mykiss (Walbaum). Aquac. Nutr. 5, 65-71.
Walsh, P. J., Blackwelder, P. K., Gill, A., Danulat, E. and Mommsen, T. P. (1991). Carbonate deposits in marine fish intestines: a new source of biomineralization. Limnol. Oceanogr. 36,1227 -1232.
Wang, T., Busk, M. and Overgaard, J. (2001). The respiratory consequences of feeding in amphibians and reptiles. Comp. Biochem. Physiol. 128A,535 -549.
Wilson, R. W. and Grosell, M. (2003). Intestinal bicarbonate secretion in marine teleost fish -source of bicarbonate, pH sensitivity, and consequence for whole animal acid-base and divalent cation homeostasis. Biochim. Biophys. Acta 1618,163 -193.[Medline]
Wilson, R. W., Gilmour, K. M., Henry, R. P. and Wood, C. M. (1996). Intestinal base excretion in the seawater-adapted rainbow trout: a role in acid-base balance? J. Exp. Biol. 199,2231 -2343.
Wilson, R. W., Wilson, J. M. and Grosell, M. (2002). Intestinal bicarbonate secretion by marine teleost fish -why and how? Biochim. Biophys. Acta 1566,182 -193.[Medline]
Wood, C. M., Kajimura, M., Mommsen, T. P. and Walsh, P. J.
(2005). Alkaline tide and nitrogen conservation after feeding in
an elasmobranch (Squalus acanthias). J. Exp.
Biol. 208,2693
-2705.
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