Elsevier

Aquatic Toxicology

Volume 83, Issue 1, 5 June 2007, Pages 10-23
Aquatic Toxicology

In vitro analysis of the bioavailability of six metals via the gastro-intestinal tract of the rainbow trout (Oncorhynchus mykiss)

https://doi.org/10.1016/j.aquatox.2007.03.006Get rights and content

Abstract

An in vitro gut sac technique was used to compare the uptake rates of essential (copper, zinc and nickel) and non-essential metals (silver, cadmium and lead) at 50 μmol L−1 each (a typical nutritive level in solution in chyme) in the luminal saline in four sections of the gastro-intestinal tract (stomach, anterior, mid and posterior intestines) of the freshwater rainbow trout. Cu, Zn, Cd and Ag exhibited similar regional patterns: on an area-specific basis, uptake rates for these metals were highest in the anterior intestine, lowest in the stomach, and approximately equal in the mid and posterior intestinal segments. When these rates were converted to a whole animal basis, the predominance of the anterior intestine increased because of its greater area, while the contribution of the stomach rose slightly to approach those of the mid and posterior intestines. However, for Pb and Ni, area-specific and whole organism transport rates were greatest in the mid (Pb) and posterior (Ni) intestines. Surprisingly, total transport rates did not differ appreciably among the essential and non-essential metals, varying only from 0.025 (Ag) to 0.050 nmol g−1 h−1 (Ni), suggesting that a single rate constant can be applied for risk assessment purposes. These rates were generally comparable to previously reported uptake rates from waterborne exposures conducted at concentrations 1–4 orders of magnitude lower, indicating that both routes are likely important, and that gut transporters operate with much lower affinity than gill transporters. Except for Ni, more metal was bound to mucus and/or trapped in the mucosal epithelium than was transported into the blood space in every compartment except the anterior intestine, where net transport predominated. Overall, mucus binding was a significant predictor of net transport rate for every metal except Cd, and the strongest relationship was seen for Pb.

Introduction

There is increasing interest in the uptake and potential toxicity of metals through the gastro-intestinal tract of fish (see Clearwater et al., 2002, Bury et al., 2003, Meyer et al., 2005, for recent reviews). Essential metals such as copper and zinc are required for the normal growth and physiological function of fish, and the diet can be their main supply. Nickel is similarly thought to be essential, based on evidence in terrestrial vertebrates, though definitive evidence is not yet available for fish and other aquatic animals (see Muyssen et al., 2004, for a recent critical review). Non-essential metals such as silver, cadmium and lead have no known physiological function in fish, but can also be acquired from the diet. Both types of metals can originate from a variety of sources—for example, from domestic and agricultural/aquacultural sources for copper and zinc; industrial processes for copper, zinc, nickel, cadmium and lead; mining, forestry and waste disposal for cadmium; natural leaching and photographic processing for silver; geological weathering, smelting, coal burning, batteries and paint for lead (e.g. Pratap et al., 1989, Farag et al., 1994; World Health Organisation, 1995; Purcell and Peters, 1998, Wood, 2001).

In fish, some studies have indicated that the anterior intestine is a site of high absorptive capacity for copper, zinc and cadmium uptake compared to other parts of the tract, while the stomach in particular has been considered to exhibit low copper, zinc and cadmium absorption (Pentreath, 1976, Shears and Fletcher, 1983, Hardy et al., 1987, Clearwater et al., 2000, Clearwater et al., 2002, Chowdhury et al., 2004). However, at least with respect to copper, other studies have reached different conclusions, variously emphasizing the importance of the stomach, the mid and posterior intestines (Handy et al., 2000, Kamunde et al., 2002, Nadella et al., 2006a, Nadella et al., 2006b). An early study (Hodson et al., 1978) indicated that dietary lead was not absorbed in trout, though more recent studies have demonstrated that lead can be absorbed through the gastro-intestinal tract (Crespo et al., 1986, Mount et al., 1994, Alves et al., 2006). Based on accumulation patterns in dietary studies, the anterior intestine appears to be the most important site for lead uptake in trout (Alves and Wood, 2006) and for nickel uptake in whitefish (Ptashynski and Klaverkamp, 2002). Silver is also absorbed from the diet in trout (Galvez and Wood, 1999, Galvez et al., 2001), though the regional sites of uptake have not been investigated. Overall, while it is clear that the gastro-intestinal tract is an important site of metal uptake in fish, no clear picture has emerged as to the regional distribution of uptake capacity for the different metals in a single species.

At a mechanistic level, metal transport via the gastro-intestinal tract likely involves several steps (Campbell et al., 2005). The first step is binding of the metal to the mucus in the lumen, which may either facilitate or retard its uptake (Part and Lock, 1983, Whitehead et al., 1996). The second step involves the transfer of the metal from the lumen into the mucosal epithelium across the apical membranes of the enterocytes, while the third step involves the export of the metal out through the basolateral membranes of the enterocytes into the blood or extracellular fluid. Alternately or additionally, it is possible that metals may move through paracellular channels, thereby bypassing cellular transport mechanisms (Bronner, 1998, Foulkes, 2000).

In recent years, isolated gut sac techniques have proven to be a very powerful approach for studying transport processes in the fish gastro-intestinal tract (e.g. Grosell and Jensen, 1999, Grosell et al., 1999, Grosell et al., 2001, Grosell et al., 2005, Bury et al., 2001). The preparations generally absorb Na+ and Cl on a net basis, and this process constrains an accompanying osmotic absorption of water. Treatments which inhibit ion transport result in reduced fluid transport (e.g. Grosell et al., 1999). Recently, Nadella et al. (2006b) have demonstrated that in vitro preparations from the gastro-intestinal tract of trout remain viable for at least 4 h, transporting both a metal (copper) and fluid at a steady rate over this duration. The technique allows manipulation of both the luminal (mucosal) and serosal media, and the sampling of mucus, the mucosal epithelium (i.e. the enterocytes), and the blood side (muscle tissue and serosal saline), thereby enabling the study of three steps in the transport process (mucus binding; accumulation in the mucosal epithelium; and transport to the blood side). In the present study, we have used this approach to compare the transport of three essential (copper, zinc, nickel) and three non-essential metals (cadmium, silver, lead) in various segments (stomach, anterior, mid and posterior intestines) of the trout gastro-intestinal tract. All metals were presented individually at the same concentration (50 μmol L−1), and fluid transport rate was monitored as an indicator of possible toxicity to ion transport processes.

Our study was designed as a first step to understanding metal uptake in the fish gastro-intestinal tract under standardized conditions, with the long term goal of future mechanistic analyses and ionic competition studies (e.g. Nadella et al., 2006b, Nadella et al., 2007), an approach that has been very successful in modeling waterborne metal toxicity at fish gills (e.g. Playle et al., 1993, Di Toro et al., 2001, Playle, 2004, Niyogi and Wood, 2004). Based on the general belief that nutritive (essential) metal uptake in the fish gut may be facilitated by specific carriers (Bury et al., 2003), we hypothesized that essential metals would be taken up at a higher rate than non-essential metals. We further hypothesized that there would be regional differences in the uptake of various metals, due to differential distribution of these specific carriers or differences in passive permeability. Finally, we hypothesized that the rate of metal accumulation in the various compartments (mucus, mucosal epithelium, blood side) would differ among the various metals. For example, mucus might facilitate the uptake of essential metals and retard the uptake of non-essential metals, while the latter might reduce their own uptake by inhibiting specific transporters. In this regard, cadmium has been shown to have a high affinity for epithelial mucus (Part and Lock, 1983), to increase the rate of mucus secretion (Gardner and Yevich, 1970, Glover and Hogstrand, 2003), and to inhibit basolateral Ca2+-ATPase in fish enterocytes (Schoenmakers et al., 1992).

Section snippets

Experimental animals

Rainbow trout (Oncorhynchus mykiss, N = 101), ∼250 g (∼30 cm) were obtained from Humber Springs Fish Hatchery (Orangeville, Ont.). Fish were maintained in 500 L tanks with flowing aerated and dechlorinated Hamilton city tap water from Lake Ontario (approximate ionic composition in mmol L−1: 0.5 [Na+], 0.7 [Cl], 1.0 [Ca2+], 0.2 [Mg2+] and 0.05 [K+], pH 7.8–8.0, dissolved organic carbon ∼ 3 mg C L−1, hardness ∼140 mg L−1 as CaCO3). The fish were fed a maintenance ration of Martin's commercial dried trout

Fluid transport rates

Fluid transport rates were always in the direction of net fluid absorption, and were higher in the anterior intestine than in the other three segments of the gastro-intestinal tract, regardless of the presence or absence of any of the six metals (Fig. 1). Overall control mean values were 1.72 ± 0.18 μL−1 cm−2 h−1 at the stomach, 9.88 ± 0.68 μL cm−2 h−1 at the anterior intestine, 2.95 ± 0.15 μL cm−2 h−1 at the mid-intestine and 2.07 ± 0.59 μL cm−2 h−1 at the posterior intestine, respectively. Values were very

Fluid transport rates

Fluid absorption by the fish gastro-intestinal tract is driven by active ion transport (House and Green, 1965, Loretz, 1995), and the anterior intestine is usually the most active area in this regard due to the presence of the cecae (Buddington and Diamond, 1986, Buddington and Diamond, 1987, Buddington et al., 1997, Bergman et al., 2003). The present results (Fig. 1) agree with this pattern. For the essential metals (copper, zinc and nickel), the concentrations used in our experiments (50 μmol L

Acknowledgements

This work was supported by the Natural Sciences and Engineering Research Council of Canada CRD Program, the International Lead Zinc Research Organization, the International Zinc Association, the Nickel Producers Environmental Research Association, the International Copper Association, the Copper Development Association, Teck-Cominco, Noranda-Falconbridge, and Inco. CMW is supported by the Canada Research Chair Program. We thank Dr. Chris Glover for advice, Sunita Nadella for her help in these

References (78)

  • P.V. Hodson et al.

    Chronic toxicity of waterborne and dietary lead to rainbow trout (Salmo gairdneri) in Lake Ontario water

    Water Res.

    (1978)
  • C. Hogstrand et al.

    Binding and movement of silver in the intestinal epithelium of a marine teleost fish, the European flounder (Platichthys flesus)

    Comp. Biochem. Physiol. C

    (2002)
  • C.A. Loretz

    Electrophysiology of ion transport in teleost intestinal cells

  • T.P. Morgan et al.

    The time course of silver accumulation in rainbow trout during static exposure to silver nitrate: physiological regulation or an artifact of the exposure conditions

    Aquat. Toxicol.

    (2004)
  • S.R. Nadella et al.

    Gastrointestinal assimilation of Cu during digestion of a single meal in the freshwater rainbow trout (Oncorhynchus mykiss)

    Comp. Biochem. Physiol. C

    (2006)
  • E.F. Pane et al.

    Acute waterborne nickel toxicity in the rainbow trout (Oncorhynchus mykiss) occurs by a respiratory rather than ionoregulatory mechanism

    Aquat. Toxicol.

    (2003)
  • P. Part et al.

    Diffusion of calcium, cadmium and mercury in a mucus solution from rainbow trout

    Comp. Biochem. Physiol.

    (1983)
  • R.J. Pentreath

    Some further studies on the accumulation and retention of 65Zn and 54Mn by the plaice Pleuronectes platessa L.

    J. Exp. Mar. Ecol.

    (1976)
  • R.C. Playle

    Using multiple-metal gill binding models and the toxic unit concept to help reconcile multiple-metal toxicity results

    Aquat. Toxicol.

    (2004)
  • M.D. Ptashynski et al.

    Accumulation and distribution of dietary nickel in lake whitefish (Coregonus clupeaformis)

    Aquat. Toxicol.

    (2002)
  • Z.H. Shehadeh et al.

    The role of the intestine in salinity adaptation of the rainbow trout, Salmo gairdneri

    Comp. Biochem. Physiol.

    (1969)
  • A. Turner et al.

    Chemical versus enzymatic digestion of contaminated estuarine sediment: relative importance of iron and manganese oxides in controlling trace metal bioavailability

    Estuar. Coast. Shelf. Sci.

    (2000)
  • L. Alves et al.

    Dietary Pb accumulation in juvenile freshwater rainbow trout (Oncorhynchus mykiss)

    Arch. Environ. Contam. Toxicol.

    (2006)
  • J. Burke et al.

    Sodium-sensitive and -insensitive copper accumulation by isolated intestinal cells of rainbow trout Oncorhynchus mykiss

    J. Exp. Biol.

    (2005)
  • R.K. Buddington et al.

    Aristotle revisited: the function of pyloric ceca in fish

    Proc. Natl. Acad. Sci. U.S.A.

    (1986)
  • R.K. Buddington et al.

    Pyloric ceca of fish: a “new” absorptive organ

    Am. J. Physiol.

    (1987)
  • R.K. Buddington et al.

    The intestines of carnivorous fish: structure and functions and the relations with diet

    Acta Physiol. Scand.

    (1997)
  • C. Bucking et al.

    Gastrointestinal processing of monovalent ions (Na+, Cl, K+) during digestion: implications for homeostatic balance in freshwater rainbow trout

    Am. J. Physiol. R

    (2006)
  • Bucking, C., Wood, C.M., 2007. Gastrointestinal transport of Ca2+ and Mg2+ during the digestion of a single meal in the...
  • N.R. Bury et al.

    Intestinal iron uptake in the European flounder (Platichthys flesus)

    J. Exp. Biol.

    (2001)
  • N.R. Bury et al.

    Nutritive metal uptake in teleost fish

    J. Exp. Biol.

    (2003)
  • P.G.C. Campbell et al.

    Digestive physiology, chemistry, and nutrition

  • P.M. Chapman et al.

    Conducting ecological risk assessments of inorganic metals and metalloids: current status

    Hum. Ecol. Risk Assess

    (2003)
  • S.J. Clearwater et al.

    Gastrointestinal uptake and distribution of copper in rainbow trout

    J. Exp. Biol.

    (2000)
  • S.J. Clearwater et al.

    Appendix A: interactions of dietborne metals with digestive processes of fishes

  • E.M. Conrad et al.

    3H-l-histidine and 65Zn2+ are cotransported by a dipeptide transport system in intestine of lobster Homarus americanus

    J. Exp. Biol.

    (2005)
  • S. Crespo et al.

    Morphological and functional alterations induced in trout intestine by dietary cadmium and lead

    J. Fish. Biol.

    (1986)
  • D.M. Di Toro et al.

    Biotic Ligand Model of the acute toxicity of metals. 1. Technical basis

    Environ. Toxicol. Chem.

    (2001)
  • A.M. Farag et al.

    Physiological changes and tissue metal accumulation in rainbow trout exposed to foodborne and waterborne metals

    Environ. Toxicol. Chem.

    (1994)
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