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COMPARATIVE AND EVOLUTIONARY PHYSIOLOGY
Department of Biology, McMaster University, Hamilton, Ontario, Canada
Submitted 30 March 2006 ; accepted in final form 1 August 2006
| ABSTRACT |
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90%) of dietary Na+ and K+ was absorbed in the stomach, whereas subsequent large fluxes of Na+ and Cl into the anterior intestine corresponded to a large flux of water previously observed. The estimated concentration of Na+ in fluids secreted into the anterior intestine was
155 mmol/l, equivalent to reported hepatic bile values, whereas the estimated concentration of Cl (
285 mmol/l) suggested seepage of HCl acid from the stomach in advance of the chyme front. Net absorption of K+ in the stomach occurred following the cessation of Cl secretion, providing indirect evidence of K+ involvement with HCl acid production. Overall, 8090% of the K+ and Cl contents of the meal were absorbed on a net basis, whereas net Na+ absorption was negligible. Chyme-to-plasma ion concentration gradients were often opposed to the direction of ion transport, especially for Na+ and Cl. Ballotini beads; inert markers; ionoregulation; Oncorhynchus mykiss
Potentially, drinking associated with feeding (32) could create water gain and salt loss due to the osmotic differences that exist with the surrounding environment (44). On the other hand, recent measurements of high osmolality of partially digested food, or chyme (3), suggest that exactly the opposite might occur (i.e., salt gain and water loss by the extracellular fluid of the fish) during digestion of a meal, and indeed, these results suggest a loss of endogenous water. Earlier, Wood (55) speculated that ingestion of a fish meal could create dietary electrolyte loads up to 10 times higher than baseline renal excretion rates, if all electrolytes were absorbed. Dietary uptake of ions has been found to be especially important in maintaining internal electrolyte homeostasis during chronic low environmental pH exposure, a circumstance which specifically decreases branchial Na+ and Cl uptake (8, 9, 11). Pyle et al. (43) and Kamunde et al. (28, 29) have presented evidence that dietary NaCl is very important in mitigating the pathological effects of sublethal Cu exposure.
Overall, under nonfeeding conditions, the marine teleost intestine exhibits a net absorption of Na+ and Cl and secretion of K+ and HCO3 (10, 49) under symmetrical conditions in vitro. The absorption of electrolytes by the intestine is believed to originate with a basolateral Na+-K+-ATPase transporter, or sodium pump, that creates an inwardly directed Na+ electrochemical gradient, generating movement of Na+ and Cl into the enterocyte (34) through a variety of apical transporters, one of which is the Na+-K+-2Cl transporter (e.g., 40). Both are subsequently secreted into the serosal fluid, Na+ by the sodium pump, and Cl by a possible combination of three transporters: Cl channel, K+-Cl symporter, and Cl/HCO3 antiporter (10, 35, 49). New evidence from Grosell et al. (22) suggests a role for a basolateral H+ extrusion, either via a Na+/H+ exchanger or an H+ pump, responsible for energizing Cl/HCO3 exchange. In contrast, K+ may enter the cell via the apical Na+-K+-2Cl cotransporter, but is believed to exit the enterocyte mainly via diffusion, possibly back into the intestinal lumen (17, 40). However, these models are based largely on seawater teleosts, under nonfeeding conditions and in vitro preparations, and evidence exists that in vivo these models require modification. For example, the concentration of K+ in the intestinal fluid of marine teleosts (under nonfeeding conditions) is lower than seawater values (e.g., 23), indicating that absorption might be occurring in vivo (e.g., 44), in contrast to the secretion seen in vitro (10, 49). Additionally, little is known about ion transport via the GI tract of freshwater teleosts under feeding conditions in vivo.
Recent findings of large biphasic fluxes of water in various sections of the tract during digestion of a meal (3) suggest that coinciding fluxes of Na+, Cl, and K+ might occur. Therefore, the primary objective of the present study was to provide a quantitative description of the processing of three monovalent ions (Na+, K+, and Cl) along the GI tract of a freshwater rainbow trout during digestion. Analysis of the electrolyte concentrations found in the chyme at various time points up to 72 h after ingestion of a single meal were carried out in each section of the GI tract, allowing investigation of the concentration gradients between chyme and blood plasma at each stage of digestion. Ballotini beads were employed as nonabsorbable inert markers (37) to correct for the absorption of solid material and water from the chyme, which would otherwise create a bias affecting the perception of concentration changes and, hence, absorption and secretion. The inert marker overcomes this problem, allowing the calculation of net absorptive or secretory fluxes in each segment over various time points. We have demonstrated that the Ballotini beads move synchronously with a fluid phase maker and used them to quantify water fluxes in these same experiments (3).
Our overall hypotheses were that biphasic fluxes of Na+, K+, and Cl would accompany the previously observed water fluxes and that all three ions would be strongly absorbed from the chyme on a net basis, reflecting the ionorgeulatory need of an animal living in an ion-poor environment. Our results support the first hypothesis but, surprisingly, show that only two of the three monovalent ions are strongly absorbed on a net basis. An important role for the stomach in ion absorption is also identified.
| MATERIALS AND METHODS |
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Diet preparation and feeding schedule. Following the 2-wk acclimation period, a feeding schedule was implemented where repelleted commercial fish feed (Martin Mills) was fed at a 2% body wt ration every 48 h for 1 mo. Feeding was then suspended for 1 wk to allow for GI tract clearance before the fish were fed to satiation with the same repelleted commercial fish feed, but now also containing Ballotini beads (Jencons Scientific). The repelleting of both diets consisted of grinding commercial fish feed pellets (crude protein = 41%; carbohydrates = 30%; fat = 11%) into a fine mince (Braun PowerMax Jug Blender; Gillette), which was then transferred into a pasta maker (Popeil Automatic Pasta Maker; Ronco Inventions) with double-distilled water at a ratio of 2:1 (powder/water). Ballotini beads (4% dry feed wt) were incorporated into one of the minces. These two mixtures were then extruded and hand-rolled to approximate 5 point-sized fish feed, to which the fish were previously accustomed. The repelleted diets were air-dried for 2 days and stored at 20°C until use. The Ballotini beads (0.400.45 mm in diameter) were composed of lead-glass for radiographic quantification, and their addition did not appear to affect the palatability of the feed, since both diets were readily consumed (20, 21). The measured total concentrations of Na+, K+, and Cl in the feed are given in RESULTS. Tests demonstrated that the water content of the feed pellets approximately tripled during the brief period in which they were in contact with the tank water prior to ingestion (from 6.1 to 18.0%), but there was no loss of Na+, K+, or Cl (3).
Sampling of GI tract. After the diet containing Ballotini beads was provided, at least seven fish were killed at various time points by cephalic concussion. [Initial trials with chemical anesthesia (MS-222) proved unsuccessful as it induced vomiting in some fish]. A terminal blood sample was taken by caudal puncture and processed for plasma Na+, K+, and Cl measurements, as described by Bucking and Wood (3). A lateral incision was made into the body wall to reveal the peritoneal cavity, and each compartment of the GI tract (the stomach, the anterior intestine, including the ceca, the midintestine, and the posterior intestine) was then visually identified and isolated by ligating at both ends of the structure with sutures, followed by the removal of the entire GI tract via sections at the esophagus and the rectum. The intact GI tract was subsequently exposed at 50 kVp (kilovolts peak) for 5 s in a portable X-ray machine (Faxitron X-ray cabinet X-ray system). Following the X-ray, each section was emptied of its contents (i.e., chyme). A subsample of chyme was centrifuged (13,000 g, 60 s), and the fluid phase removed, placed into liquid nitrogen, and then stored at 80°C for later analysis of ion content. The remaining whole chyme was dried (at 80°C) to a constant weight (48 h) to determine the dry mass and water content of the original chyme. The chyme was then digested (5 volumes of 1 N HNO3; Fisher Scientific) and placed back in the oven for 48 h, during which time it was vortexed twice. Following digestion, samples were centrifuged (13,000 g, 60 s), and the extracted supernatant was analyzed for ion content. The experimental feed (7 samples taken from the feed containing the Ballotini beads) was also digested, and the supernatant was extracted in the same manner as for the chyme.
Analysis of gut contents and calculations. Ion concentrations in the digested feed, whole chyme (µmol/g wet wt), fluid phase (µmol/ml), and blood plasma (µmol/ml) were determined by using either a Varian 1275 Atomic Absorption Spectrophotometer (Na+ and K+) or a chloridometer (CMT 10 Chloride Titrator; Radiometer, Copenhagen, Denmark; Cl). Reference standards were used for the measurement of all ions studied [Fisher Scientific and Radiometer (Copenhagen, Denmark)]. Quantification of beads in each GI tract section occurred via manual counts of the beads observed in the X-ray of the GI tract, which was placed on a fine grid to ensure accuracy.
Ion concentrations in the chyme (or food) were then referenced to the beads located in each:
![]() | (1) |
where [X] was the concentration of the ion of interest in the chyme (µmol/g dry wt).
The apparent ion concentration (µmol/ml) of the secreted fluid added in the anterior intestine to the chyme entering from the stomach was calculated as the change in relative ion concentration ([X]; µmol/bead) between the stomach and ceca divided by the corresponding change in relative water concentration ([Y]; ml/bead) as reported for these same experiments by Bucking and Wood (3)
![]() | (2) |
Ion fluxes (mmol/kg) in various segments of the tract at different times were calculated according to
![]() | (3) |
where a is the compartment of interest and b is the preceding compartment at the same time point, Z is the total bead number in the specified GI tract section, [X] is the relative concentration of the ion (µmol/bead) in the specified GI tract section, and M is fish weight in kilograms. The "preceding compartment" for the stomach at 2 h was the ingested food and, thereafter, the stomach itself at the previous time point. The preceding compartment for the midintestine was the anterior intestine, and the preceding compartment for the posterior intestine was the midintestine.
Statistical analysis. Data have been reported as means ± SE (n = number of fish) unless otherwise stated. The effect of location was tested using a repeated-measures ANOVA with GI tract section as the main variable examined at each time point. The effect of time was tested using a one-way ANOVA with time as the main variable, and each GI tract section was examined individually. Significant effects (P < 0.05) were determined after applying a Tukey's honestly significant difference post hoc test. All statistical analyses were performed using SPSS (version 13).
| RESULTS |
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6.4 mmol/kg fish wt. The Na+ concentration found in the stomach chyme decreased from that in the original food by
95% over 72 h, from 215.6 ± 5.1 to 13.4 ± 3.3 µmol/g wet chyme wt (7; Fig. 1A). The concentration of Na+ in the fluid phase sampled from the stomach also decreased over time, falling by 90%, from 140.7 ± 3.0 (7) in the first chyme sample at 2 h to 14.0 ± 3.5 µmol/ml (7) at 72 h, between 22 and 90% lower than plasma Na+ values (µmol/ml) at all time points (Fig. 1B).
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Referencing the Na+ concentrations to the inert marker revealed more dramatic changes in Na+ dynamics. Approximately 90% of the original Na+ found in the ingested food (µmol/bead) was absorbed by the stomach, with the relative Na+ concentration consistently falling over 72 h from 2.17 ± 0.18 to 0.27 ± 0.22 µmol/bead (7; Fig. 2), similar to the pattern seen in absolute concentrations (Fig. 1). Again, there was a large appearance of Na+ in the anterior intestine at 8 h with the arrival of chyme (Fig. 2). However, the increase in the relative concentration of Na+ in the chyme was ninefold, almost triple the increase seen in the simple concentration data of Fig. 1A. In contrast to the impression given by the wet chyme Na+ concentration data, slightly more than 50% of the Na+ found in the anterior intestine was subsequently absorbed over the next 64 h (Fig. 2).
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Chloride. The measured concentration of Cl in the prepared diet was 186.5 ± 15.8 µmol/g original food wt (7), resulting in a total intake of Cl from the meal around 5.2 mmol/kg fish wt, slightly less than that of Na+. In marked contrast to Na+, the Cl concentration in the stomach chyme was maintained at about 185 µmol/g wet chyme wt for the duration of the experiment, while that in the fluid phase remained at a similar value (about 190 µmol/ml), excluding 4, 48, and 72 h when the fluid phase concentration appeared to increase slightly (Fig. 3, A and B). The Cl concentration in the fluid phase of the stomach chyme was also consistently higher than plasma values (130 µmol/ml; Fig. 3B). There was, again, a significant increase in concentration in total chyme at 8 h in the anterior intestine, although at twofold somewhat less on a relative basis than the threefold increase seen in Na+ (cf., Fig. 1A). However, the Cl concentration found along the intestine decreased to become similar in all three sections at 48 h, and by 72 h had become 75% lower than that found in the original food (Fig. 3A).
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The relative Cl concentration (µmol/bead; Fig. 4) exhibited a very different pattern than that seen with the actual Cl concentration (µmol/g wet chyme wt; Fig. 3A) and was also very different from that for Na+ (cf., Fig. 2). In contrast to the constancy in the actual Cl concentration, there was a marked increase in the relative concentration of Cl in the stomach, increasing from 1.87 ± 0.19 µmol/bead (7) found in the food to 6.41 ± 1.87 µmol/bead (7) at 24 h followed by a return to Cl levels found in the food by 48 h (Fig. 4). There was again (as with Na+; Fig. 2) a large increase in the relative concentration of Cl when the chyme first appeared in the anterior intestine at 8 h, increasing from the stomach by eightfold (Fig. 4), markedly greater than the twofold rise in actual concentration of Cl (Fig. 3A). This large peak traveled along the intestinal tract over time, appearing in the midintestine at 12 h and the posterior intestine at 24 h. Aside from this, the relative Cl concentration seen along the intestine decreased in all sections to eventually become similar at 24 h, followed by simultaneous decreases in all three sections to become 0.36 ± 0.09 µmol/bead (21), 81% less than the originally ingested relative Cl concentration [1.87 ± 0.19 µmol/bead (7)] in the food (Fig. 4).
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Potassium.
The measured concentration of K+ in the prepared diet was 96.5 ± 1.8 µmol/g original food wt (7). The amount of K+ ingested in the food was roughly half that of Na+ and Cl, around 3 mmol/kg fish wt. The K+ concentration found in the total wet chyme of the stomach (µmol/g wet chyme wt) displayed a decrease from an initial value of
95 mmol/l in the food, and by 48 h all GI tract segments contained similar K+ concentrations (510 mmol/l). These concentrations were
89% less than in the ingested food and were essentially maintained until 72 h (Fig. 5A). Notably, in contrast to Na+ and Cl (Figs. 1A and 3A), there was no increase but rather a marked decrease in K+ concentration when chyme first appeared in the anterior intestine at 8 h (Fig. 5A). The fluid phase extracted from the total chyme displayed similar temporal trends as seen in the total chyme (Fig. 5A), with the stomach fluid phase initially at about 55 µmol/ml at 2 h, decreasing over time to eventually become similar to the fluid phase found along the intestinal tract, which ranged between 4 and 12 µmol/ml (Fig. 5B). The fluid phase in the stomach (at all time points) and the intestine (with the exception of 24 and 48 h) contained significantly more K+ than the plasma (3 µmol/ml; Fig. 5B).
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| DISCUSSION |
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The production of HCl acid in the stomach of the rainbow trout appeared to peak at 12 h (Figs. 4 and 7B), and corresponded with the cessation of proposed fluid secretion reported in these same experiments by Bucking and Wood (3). The estimated concentration of Cl in the fluid secreted into the stomach between 2 and 12 h was about 240 mmol/l, a value similar to that seen in mammalian stomachs (16). If accompanied by equimolar H+, the fluid would have a pH of 0.6. A previous study by Dabrowski et al. (7) showed a similar peak in stomach Cl concentration between 10 and 20 h following ingestion of a meal in the rainbow trout. The production of HCl acid involves the transport of plasma Cl into the stomach lumen, a process which has been implicated in the production of hypochloremia. However, this was not observed in this study (Fig. 3B); a possible explanation may be found within the principles of piscine acid-base regulation.
In the currently accepted model of HCl acid production in the vertebrate stomach (reviewed in Ref. 42), the Cl obtained from the plasma at the basolateral membrane is exchanged for intracellular HCO3 left behind by the apical secretion of H+. The secretion of HCO3 into the plasma results in the well-known alkaline tide, a metabolic alkalosis in the systemic bloodstream. This phenomenon has been observed in mammals, reptiles, and amphibians (52) and recently in elasmobranchs (57), although it has not been documented in freshwater teleosts. If this occurred in the freshwater trout, the probable response would be an enhanced uptake of Cl in exchange for HCO3 at the gill so as to restore acid-base homeostasis (reviewed in Ref. 19). Such an exchange may have masked any losses of plasma Cl during the formation of HCl acid and would explain the lack of hypochloremia seen during the experiment (Fig. 3B). Clearly, Cl influx rate measurements at the gills immediately after feeding, as performed by Smith et al. (47) for Na+, as well as blood acid-base measurements would be helpful in further understanding the responses to feeding in future studies.
The observed net K+ absorption in the stomach of the rainbow trout from 12 h onward (Fig. 7C) corresponded with the probable reduction of HCl acid production after this time point, while up to that point the relative K+ concentration had been maintained (Fig. 6). This may be explained by the fact that the secretion of H+ ions (or most likely H3O+ ions) into the stomach lumen is produced by an apical H+-K+-ATPase, which uses the hydrolysis of ATP to drive the exchange of luminal K+ for cytoplasmic H+. The K+ is subsequently recycled back into the stomach lumen to continue acid production (16). There is evidence of a putative H+-K+-ATPase in the stomachs of both elasmobranchs and teleosts (6, 12, 18, 48).
The stomach was the location of marked absorption of Na+ and K+ from the diet (Figs. 2, 6, and 7, A and C), although in the case of Na+, this was against the concentration gradient from the chyme to the plasma (Fig. 1B). However, Smith et al. (47) also observed absorption of dietary Na+ in the stomach of the freshwater rainbow trout; in fact, 65% of the dietary load was absorbed by 7 h, very similar to the results seen here. The stomach epithelium of a rainbow trout consists mainly of columnar cells (2, 15, 30), cells that are often specialized for transport (58). Recently, the stomach has also been shown as a site of iron (5), Ca2+ (1), and Cu (41) absorption in freshwater rainbow trout. The estimated uptake rates of Na+ (Fig. 7A) were initially (02 h) about 0.8 mmol·kg1·h1, exceeding those found in the gills (e.g., 43, 47, 50, 56, 47). However, they fell dramatically over the next 2 h to 0.3 mmol·kg1·h1.
The flux rate of potassium out of the stomach lumen between 12 and 48 h was
0.030.1 mmol·kg1·h1 (Fig. 7C). This is comparable with the branchial influx rate observed in unfed rainbow trout (0.07 mmol·kg1·h1; 13) and higher than the renal reabsorption rates (0.01 mmol·kg1·h1; 56); however, no hyperkalemia was observed (Fig. 5B). In fact, despite large secretions of Cl into the stomach and almost complete absorption of dietary Na+, relatively few perturbations in blood plasma constituents were observed, with the exception of the rise in plasma Na+ levels at 2 h (Fig. 1B). This suggests that ion handling had been altered at one or more of the additional sites of electrolyte regulation; the gills, the kidney, and, in the case of K+, the extracellular/intracellular interface, as K+ is located mainly in the intracellular compartment. Indeed, Smith et al. (47) likewise observed little change in plasma Na+ levels following feeding and suggested that observed increases in electrolyte efflux and/or decreases in electrolyte influx rates were critical in maintaining optimal concentrations.
Another important secretion into the GI tract is bile. Bucking and Wood (3) postulated that the majority of fluid secreted into the anterior intestine at 8 h (
3.5 ml/kg) was mainly a result of gall bladder bile secretions [
2 ml/kg in rainbow trout (24)]. Secretion of bile may also explain, at least in part, the coinciding large secretions of Na+ and Cl (Figs. 2 and 4). The concentration of Na+ in the fluid secreted into the anterior intestine was calculated as 155.1 ± 22.7 µmol/ml (7), which is roughly equivalent to the observed concentration of Na+ found in the hepatic bile of the rainbow trout but half that seen in gall bladder bile released to the intestine (24). This may reflect absorption of ions occurring in the anterior intestine that, due to the nature of this study, cannot be seen against the large background of net secretion. In contrast, the calculated concentration of Cl in the secreted fluid was 287 ± 57 µmol/ml (7), roughly twofold higher than hepatic bile and over four times higher than that found in gall bladder bile (24).
A possible explanation could be the additional seepage of HCl acid from the stomach (earlier estimated at 240 mmol/l) in advance of the chyme front. Support is found in the noticeable traveling peak in the relative concentration of Cl along the intestinal tract (Fig. 4), as well as a slight movement of liquid (tracked with PEG-4000) from the stomach before the movement of chyme (tracked with Ballotini beads) (3). This could possibly aid in activating transport processes and GI secretions in anticipation of receiving chyme. Interestingly, there was no significant change in the relative K+ concentration when chyme moved from the stomach to the anterior intestine, the site and time of the proposed secretion of bile (Fig. 6). This is in accordance with the fact that bile contains only a relatively low concentration of K+,
8 mmol/l (Bucking C and Wood CM, unpublished observation).
There was only slight and variable Na+ absorption by the midintestine (Fig. 7A), the site of the majority of net water absorption, although there certainly could have been Na+ and water absorption present in the anterior intestine that was simply not visible due to large volumes of secreted bile (3). In contrast, Cl was clearly absorbed by the anterior intestine, especially during later time points (Figs. 4A and 7B). The Na+ absorbed by the intestine appears to be almost entirely endogenous in nature, secreted with bile and other intestinal secretions into the anterior intestine, while the Cl and K+ that was absorbed could be either endogenous or exogenous, in light of the proposed Cl section and K+ recycling that occurs in the stomach. In contrast to both Na+ (Fig. 1B) and Cl (Fig. 3B), the K+ absorption along the intestinal tract was down the concentration gradient observed from the chyme to the plasma (Fig. 5B).
While the prepared diet contained significantly less water than a natural diet (18 vs. 80%), the ion content was approximately equal. It has been suggested that the stomach is responsible for liquefying the ingested food to approximate natural prey water contents, potentially creating an avenue for endogenous water loss as a result (3). This would then render the commercial diets similar to natural prey.
When comparing ingested relative values (µmol/bead) to excreted values, i.e., food at 0 h to posterior intestine at 72 h, 85% of dietary Cl and 89% of dietary K+ was absorbed on a "net" basis by the GI tract (Figs. 4 and 6), the former in spite of the marked secretion of Cl in the stomach and the anterior intestine. This represents net absorption rates of 64 and 37 µmol·kg1·h1 for Cl and K+, respectively. Considering that the branchial net flux of Cl and K+ is minimal in freshwater fish [although slightly positive (e.g., 56)], this represents a substantial influx of ions while feeding. In contrast, there was a slight net secretion of
9% of the Na+ found in the food (not significantly different from 0%), indicating that dietary Na+ is not utilized on a net basis by the fish under normal conditions. However, under stressful conditions, dietary Na+ may be assimilated to a greater extent, as dietary Na+ has been shown to prevent physiological consequences of decreased Na+ uptake at the gills under various conditions, such as environmental acid and Cu exposure (9, 11, 28, 29, 43).
The fact that almost the entire dietary load of K+ was absorbed may relate to the low concentration of K+ in freshwater, with values < 10% of Na+ in the acclimation water of the present study. Cl absorption may have occurred because of its involvement in the alkalinization of the intestinal tract contents via a Cl/HCO3 exchanger, a transporter known to be found in the intestinal tract of marine teleosts (reviewed in Ref. 54). The same process may occur in freshwater rainbow trout due to the high pH of the intestinal lumen contents, which likely results from the linked secretion of endogenous HCO3 (44). Clearly, the amount of electrolyte absorbed from the diet may depend on many factors from the ion status of the fish at the time of feeding (46) to environmental conditions.
| ACKNOWLEDGMENTS |
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| FOOTNOTES |
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The costs of publication of this article were defrayed in part by the payment of page charges. The article must therefore be hereby marked "advertisement" in accordance with 18 U.S.C. Section 1734 solely to indicate this fact.
| REFERENCES |
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