Rat primary hepatocyte cultures are a good model for examining metallothionein-induced tolerance to cadmium toxicity

Summary The effect of Zn-induced metallothionein (MT) on the toxicity, uptake, and subcellular distribution of cadmium (Cd) was examined in rat primary hepatocyte cultures and compared to results obtained earlier in this laboratory from intact animals. Hepatocytes were isolated and grown in monolayer culture for 22 h and subsequently treated with ZnCl₂ (100 μM) for 24 h, which increased MT concentration about 15-fold. After Zn pretreatment, hepatocytes were exposed to Cd for 24 h. Cytotoxicity was assessed by enzyme leakage, intracellular potassium loss, and cellular glutathione content. The toxicity of Cd was much less in Zn-pretreated cells than in control cells, similar to that previously demonstrated in the intact animal. Zn pretreatment had no appreciable effect on the hepatocellular uptake of¹⁰⁹Cd, but markedly altered its subcellular distribution, with more Cd accumulating in the cytosol and less in the nuclear, mitochondrial, and microsomal fractions. In the cytosol of Zn-pretreated cells, Cd was associated mainly with MT; in contrast, cytosolic Cd in control cells was mainly associated with non-MT macromolecules. Zn-induced changes in the subcellular distribution of Cd in vitro are identical to those observed in vivo in Zn-pretreated rats challenged with Cd. In summary, Zn pretreatment of rat primary hepatocyte cultures protects cells against Cd toxicity. Protection seems to be due to MT-promotes sequestration of Cd and reduction of the amount of Cd associated with critical organelles and proteins. These observations are similar to those noted in the whole animal. These results indicate that cultured hepatocytes are an ideal model for examining MT-induced tolerance to Cd hepatotoxicity. This work was supported by grant ES-01142, and WCK was supported by training grant ES-07079, both from the Public Health Service, Department of Health and Human Services.     

Tissue susceptibility factors in cadmium carcinogenesis

Recently, in two separate studies we have observed cadmium (Cd)-induction of prostatic tumors (PT) in rats. Cd (sc or im) at doses nontoxic to the testes markedly increased PT formation (2.5 μmol/kg, sc, 8 PT/29 exposed, 28%; 30 μmol/kg, im, 11/26, 42%; control 14/127, 11%). The administration of zinc (Zn; 1 mmol/kg, sc, at ?6, 0 and +18 h) to prevent testicular toxicity and tumors from Cd (30 μmol/kg, sc, 0 h) also resulted in an elevated incidence of PT (8/27, 30%). The nature of the metal-binding proteins in the prostate has not been defined, although metallothionein (MT), a low M_r Cd-binding protein that confers tolerance to Cd, is deficient in other target tissues of Cd carcinogenesis, such as the rat testes. Using a technique that extracts MT from liver, a low-M_r Cd-binding protein was extracted from both ventral (VP) and dorsal prostate (DP) and isolated by gel filtration. In contrast to the two forms of rat MT, reverse phase HPLC of VP and DP extract eluted 1 and 5 forms, respectively. The amino acid compositions of the VP and DP proteins were quite distinct from MT, with much less cys than MT and the presence of residues not found in MT (leu, tyr, phe). Thus Cd-induction of PT appears to be dependent on functional testes and, as is the case with Cd-induced testicular formation, appears to be associated with a deficiency of MT.     

Isolation and partial characterization of the low-molecular-mass zinc/cadmium-binding protein from the testes of the patas monkey (Erythrocebus patas). Distinction from metallothionein.

The mammalian testes are generally quite susceptible to cadmium. A deficiency of metallothionein (MT), a metal-binding protein linked to Cd tolerance, has been observed in rat testes and may explain the sensitivity in rats. Little is known about the metal-binding proteins in primate testes. Thus this study examined the nature of these proteins in a non-human primate species, the patas monkey (Erythrocebus patas). In all cases proteins isolated from testes were compared with authentic MT isolated from the liver of a zinc-treated monkey. A low-molecular-mass Zn/Cd-binding protein was seen in testicular and hepatic cytosol after gel filtration. Neither protein had substantial amounts of associated copper. These proteins could be partially purified from both sources by heat treatment and acetone precipitation. When such extracts were further separated by reverse-phase h.p.l.c., four hepatic forms were isolated, all of which proved to be authentic MT by amino acid analysis. However, only two testicular forms were separated by h.p.l.c., both of which had amino acid compositions quite unlike that of MT, having a much lower cysteine content and amino acids which are absent from MT (leucine and phenylalanine). The testicular protein appeared to be uninducible by Zn treatment. These results suggest that the low-molecular-mass Cd/Zn-binding proteins in the patas testes are not MTs and further support the hypothesis that a MT deficiency may be an important determinate of the marked testicular sensitivity to Cd toxicity.     

Effects of cadmium, copper and metallothionein synthesis inhibiting and stimulating compounds on zinc uptake and accumulation in rat hepatoma HTC cells.

Experiments were carried out to investigate the uptake and accumulation of Zn in rat hepatoma HTC cells, as affected by interfering metals (Cd, Cu), metallothionein synthesis inhibiting compounds (Actinomycin D, cycloheximide) and metallothionein synthesis stimulating compounds (dexamethasone, dibu-cAMP). Cell viability was tested under all experimental conditions by the measurement of LDH leakage, K+ uptake and total cell protein. Determinations of Zn were performed by AAS (total Zn) or by gamma-ray spectrometry (65Zn). Metallothionein analysis was carried out by Cd-saturation tests. The results indicate that cellular responses in rat hepatoma HTC cells with respect to the uptake and accumulation of 65Zn are fully comparable with literature data existing for 65Zn accumulation in rat hepatocytes, under all experimental conditions applied. Cu2+ and dibutyryl-cAMP did not significantly affect rates of 65Zn accumulation. Cd2+, Actinomycin D and cycloheximide reduced 65Zn uptake, but dexamethasone additions resulted in increased 65Zn accumulation in the cells. Effects on 65Zn were shown both in cytosolic and in the membranes/organelles cell fractions. HPLC chromatography in control cells suggested that newly accumulated cytosolic 65Zn was predominantly MT-associated. Dexamethasone-induced 65Zn accumulation could not be related to elevated cellular MT levels, nor were the total cytosolic Zn levels significantly affected. Non-specific attenuations in MT levels (Actinomycin D, cycloheximide and dibu-cAMP) yielded linear relations between cytosolic 65Zn and MT levels, without any change in cytosolic Zn (AAS). Combined addition of Cd and dexamethasone yielded elevated MT levels, but severely reduced total cytosolic Zn and 65Zn concentrations. The results further indicate the non-Zn-specific nature of dexamethasone-action and suggest the relatively easy Zn-complexing and Zn-release of MT. The simultaneous determinations of total cytosolic zinc and cytosolic 65Zn levels showed that the application and sole measurement of radiotracers may yield only one-sided views of what is actually present or occurring in the cells.     

The influence of zinc on apical uptake of cadmium in the gills and cadmium influx to the circulatory system in zebrafish (Danio rerio)

Zn (0-16 microM) effects on apical Cd uptake from the water into the branchial epithelium and influx of Cd from the water to the circulatory system in zebrafish (Danio rerio) were studied in three experiments. Apical Cd uptake was decreased by Zn in all three experiments. In fish exposed to 1-600 nM Cd (experiment 1), apical Cd uptake showed saturation kinetics at 2 and 4 microM Zn, and a competitive interaction was indicated. At 16 microMZn, Cd uptake increased linearly. Cadmium influx did not show saturation kinetics, but was inhibited by 16 microM Zn at low Cd exposure concentrations. In fish exposed to 0.1-600 nM Cd (experiment 2), Cd uptake was inhibited by 16 microM Zn, whereas at 30 nM Cd uptake was inhibited by 2 microM Zn. Similarly, 2 microM Zn did not influence Cd uptake in fish exposed to 0.1-2 nM Cd (experiment 3), whereas 2 microM Zn inhibited uptake at 8-30 nM Cd. Zinc also inhibited Cd influx at higher Cd concentrations. However, at lower Cd exposures, a Zn-induced increased influx was indicated. Zinc influences the Cd uptake and influx processes at several sites in the branchial epithelial cells, indicating that influx of Zn2+ and Cd2+ occurs through common pathways.     

Testicular toxicity induced by dietary cadmium is associated with decreased testicular zinc and increased hepatic and renal metallothionein and zinc in the bank vole <Emphasis Type="Italic">(Clethrionomys glareolus)</Emphasis>

Mechanism of testicular toxicity induced by dietary cadmium (Cd) has been less investigated than that following acute Cd injection. In the present study we characterized testicular injury in a small rodent, the bank vole, exposed subchronically to dietary Cd in a quantity of 0.9 mol/g, and determined the importance of some factors (Cd accumulation, metallothionein (MT), oxidative stress, and zinc (Zn)) in the injury. Dietary Cd induced moderate histopathological changes (hemorrhage in interstitium, necrosis and apoptosis in seminiferous tubule epithelium) in young (1 month old) bank voles fed, for 6 weeks, Fe-adequate (1.1–1.4 mol/g) and Fe-enriched (4.5–4.8 mol/g) diets. In contrast, adult (5 months old) bank voles appeared to be resistant to the toxic effects of dietary Cd, despite the fact that testicular Cd contents were higher and MT levels lower than those in the young animals. The Cd-induced histopathological changes and apoptosis were accompanied by increased testicular lipid peroxidation, decreased testicular Zn concentration and elevated levels of hepatic and renal MT and Zn. Supplemental dietary Zn (1.7–1.8 mol/g) prevented the Cd-induced testicular Zn depletion and injury. The data indicate that dietary Cd produces testicular lesions indirectly, through decreasing testicular Zn, which seems to be due to the sequestration of this element by the Cd-induced hepatic and renal MT.     

Natural variation in cadmium tolerance and its relationship to metal hyperaccumulation for seven populations of Thlaspi caerulescens from western Europe

Thlaspi caerulescens J. & C. Presl is a distinctive metallophyte of central and western Europe that almost invariably hyperaccumulates Zn to> 1.0% of shoot dry biomass in its natural habitats, and can hyperaccumulate Ni to> 0.1% when growing on serpentine soils. Populations from the Ganges region of southern France also have a remarkable ability to accumulate Cd in their shoots to concentrations well in excess of 0.01% without apparent toxicity symptoms. Because hyperaccumulation of Cd appears to be highly variable in this species, the relationship between Cd tolerance and metal accumulation was investigated for seven contrasting populations of T. caerulescens grown under controlled conditions in solution culture. The populations varied considerably in average plant biomass (3.1‐fold), shoot : root ratio (2.2‐fold), Cd hyperaccumulation (3.5‐fold), shoot : root Cd‐concentration ratio (3.1‐fold), and shoot Cd : Zn ratio (2.6‐fold), but the degree of hyperaccumulation of Cd and Zn were strongly correlated. Two populations from the Ganges region were distinct in exhibiting high degrees of both Cd tolerance and hyperaccumulation (one requiring 3 µM Cd for optimal growth), whereas across the other five populations there was an inverse relationship between Cd tolerance and hyperaccumulation, as has been noted previously for Zn. Metal hyperaccumulation was negatively correlated with shoot : root ratio, which could account quantitatively for the differences between populations in shoot Zn (but not Cd) concentrations. On exposure to 30 µM Cd, the two Ganges populations showed marked reductions in shoot Zn and Fe concentrations, although Cd accumulation was not inhibited by elevated Zn; in the other five populations, 30 µM Cd had little or no effect on Zn or Fe accumulation but markedly reduced shoot Ca concentration. These results support a proposal that Cd is taken up predominantly via a high‐affinity uptake system for Fe in the Ganges populations, but via a lower‐affinity pathway for Ca in other populations. Total shoot Cd accumulated per plant was much more closely related to population Cd tolerance than Cd hyperaccumulation, indicating that metal tolerance may be the more important selection criterion in developing lines with greatest phytoremediation potential.     

Properties of metallothionein induced by zinc, copper and cadmium in the frog, Xenopus laevis

1. Repeated injections of zinc (Zn) and copper (Cu) into the frog Xenopus laevis caused accumulations of the respective metals in the liver and kidney. 2. The accumulated metals in the liver supernatant fractions were present as Zn- and Cu-binding proteins of the same properties as that of metallothionein (MT) induced by cadmium (Cd) injections. 3. The affinity of Zn, Cu and Cd ions to the metal-binding protein was in the decreasing order of Cu, Cd and Zn. 4. The Xenopus MT induced by Cd was unstable and disrupted easily to give two peaks as if the MT consists of two isometallothioneins.     

Inducibility and amounts of metallothionein as influenced by cadmium and zinc in the developing rat

Information on the accumulation and/or depletion of Zn in metallothionein (MT) of rat fetus, rat pup, and maternal rat liver at various ages was obtained with pregnant rats fed a basal casein diet or this diet plus either 100 ppm Zn or 50 ppm Cd. Rats fed each of the respective diets were sacrificed on 12, 16, and 20 d of gestation and 0, 7, 14, and 28 d post-partum. No Cd was detected in the placenta or fetal tissue and the Cd did not affect the accumulation of Zn in the fetal MT, but it did increase the Zn content in liver MT of the dams. Very little Zn in MT was found on day 12 of gestation, but Zn rapidly increased in MT to a maximum at time of birth. The accumulation of Zn in MT was independent of the diet for the fetuses, but the Zn accumulation in the dam and pup tissues was diet dependent. In order to study age-dependent difference in the inducibility of MT, newborn, 5-week-old, or 24-week-old rats were injected with zinc at the levels of 0, 3, 6, or 9 mg/kg and 5 h later injected with³⁵S-cystine. In rats sacrificed 1 h later, the amount of radioactivity in liver MT demonstrated that this protein in older animals was more readily induced by Zn than in younger animals.     

Strategies of cadmium and zinc resistance in willow by regulation of net accumulation

This work was performed to find out if metal resistant clones of Salix viminalis L. are capable to achieve high resistance to the metals by regulating their net accumulation. Salix clones with low or high resistance in combination with low or high accumulation capacity of either Zn or Cd were cultivated from cuttings in nutrient solution. The investigation included leakage and uptake experiments using ⁶⁵Zn or ¹⁰⁹Cd and analysis of root cation exchange capacity (CEC). Some plants were pre-treated with unlabeled 0.5 μM Cd or 2.5 μM Zn 24 h prior to the experiments to induce possible tolerance mechanisms. To find out if the regulation was a metabolic process, experiments were also performed with 2,4-dinitrophenol (DNP). Clones with high resistance and low Cd accumulation had higher efflux of Cd compared to the other clones, in both untreated and Cd pre-treated plants. This indicates a constitutive property to lower Cd accumulation by high Cd leakage. Pre-treatment with 0.5 μM Cd diminished the Cd net uptake to a level near zero in all clones, likely to be due to decreased the Cd uptake. In contrast, resistant clones with high Cd accumulation had the highest root CEC, which may be used to bind up Cd in the free space. No clear regulation of Zn net uptake was found in Zn-resistant clones. Pre-treatment with Zn decreased the uptake of Zn into the free space in Zn-resistant clones. The resistant high-accumulating clones, however, showed the highest leakage of Zn in both untreated and pre-treated plants, a constitutive process not related to high accumulation. Neither the influx nor the efflux of Cd or Zn was affected by DNP indicating passive transport across the plasma membrane.     

Metallothionein response to cadmium and zinc exposures compared in two freshwater bivalves, Dreissena polymorpha and Corbicula fluminea

Metallothionein (MT) response to cadmium (Cd) and zinc (Zn) bioaccumulation after single or combined direct exposure was compared in two freshwater bivalves, Dreissena polymorpha (zebra mussel) and Corbicula fluminea (Asiatic clam). Bivalves were exposed to 0.133 μM Cd and/or 15.3 μM Zn, with metal and MT concentrations analysed in the whole soft body after 1, 3, 10 and 24 days of exposure and compared with controls. Results showed significant increase in MT concentrations in both species exposed to Cd and Cd+Zn with a higher accumulation of the protein compared to the control in D. polymorpha for nevertheless similar Cd levels accumulated with time. Exposure to Zn alone led to a significant increase in MT concentrations only in C. fluminea, whereas there was a lack of MT gene induction in the zebra mussels which was confirmed by MT mRNA quantification in gills (RT-PCR). Mussel mortality after 10 days of exposure to Zn and Cd + Zn is discussed with regard to detoxification mechanisms, which include metallothioneins.     

Cadmium uptake in rat hepatocytes in relation to speciation and to complexation with metallothionein and albumin

Cadmium (Cd) uptake has been studied in primary cultures of rat hepatocytes focusing on the impact of inorganic and organic speciation. Uptake time-course studies over a 60-min exposure to 0.3 microM (109)Cd revealed a zero-time uptake and a slower process of accumulation which proceeds within minutes. (109)Cd uptake showed saturation kinetics (K(m) = 3.5 +/- 0.8 microM), and was highly sensitive to inhibition by Zn and Hg. There was no evidence for sensitivity to the external pH nor for any preferential transport of the free cation Cd(2+) over CdCl(n) (2-n) chloro-complexes. According to the assumption that only inorganic metal species are available, metal uptake decreased upon albumin (BSA) addition to the exposure media. In contrast, higher levels of (109)Cd accumulation were obtained under optimal conditions for Cd complexation by MT. Comparison among uptake data obtained under inorganic and organic conditions revealed that Cd-MT would be taken up 0.4 times as rapidly as Cd(inorg). We conclude that uptake of Cd in rat hepatocytes involves specific transport mechanism(s) subjected to Zn or Hg interactions. Uptake of inorganic Cd is not proportional to the levels of free Cd(2+) and does not involve the divalent cation transporter DCT1 nor the co-transporter Fe(2+)-H(+) NRAMP2. We found Cd-MT but not Cd-BSA to be available for the liver cells, and have estimated a binding affinity four orders of magnitude higher for Cd complexation with MT compared to BSA; MT may have a significant role in Cd delivery to the liver.     

The changes of heavy metal and metallothionein distribution in testis induced by cadmium exposure

Cadmium (Cd) is known to cause various disorders in the testis, and metallothionein (MT) is known as a protein, which has a detoxification function for heavy metals. However, the changes of Fe, Cu, and Zn distribution in the testis induced by Cd exposure have not been well examined. Moreover, only a few studies have been reported on the localization of MT after Cd exposure. In this study, we have investigated the changes of Fe, Cu, and Zn distribution in Cd-exposed testis by a newly developed in air micro-Particle Induced X-ray Emission (PIXE) method. Also, we examined the distribution of MT expression in testis. In the testis of Cd-treated rats with significant increases of lipid peroxidation, the sertoli cell tight junction was damaged by Cd exposure, resulting from disintegration of the blood testis barrier (BTB). Evaluation by in air micro-PIXE method revealed that Cd and Fe distribution were increased in the interstitial tissues and seminiferous tubules. The histological findings indicated that the testicular tissue damage was advanced, which may have been caused by Fe flowing into seminiferous tubules followed by disintegration of the BTB. As a result, Fe was considered to enhance the tissue damage caused by Cd exposure. MT was detected in spermatogonia, spermatocytes, and Sertoli’s cells in the testis of Cd-treated rats, but was not detected in interstitial tissues. These results suggested that MT was induced by Cd in spermatogonia, spermatocytes, and Sertoli’s cells, and was involved in the resistance to tissue damage induced by Cd.     

Some properties of a unique cadmium-binding moiety in the soluble fraction of rat testes.

A 30,000 molecular weight testicular Cd-binding peak (30,000 MW Cd-BP) previously implicated in Cd-induced testicular injury was unstable during storage with respect to apparent molecular weight determined by Sephadex G-75 chromatography. Storage of testicular cytosol labeled with 109Cd in vivo or in vitro for several days at 4 degrees C under nitrogen resulted in disappearance of the 30,000 MW Cd-BP and increased 109Cd uptake in other protein fractions. Rechromatography of the previously isolated 30,000 MW Cd-BP after storage gave rise to a 109Cd peak eluting in the higher molecular weight region. The latter effect was prevented by 1 mM dithiothreitol, suggesting that sulfhydryl groups were involved in the apparent aggregation. The 30,000 MW Cd-BP found in testes of rats was not present in testes of roosters, nor in liver and kidney of either species, providing further evidence of a correlation between the occurrence of 30,000 MW Cd-BP protein in the tissue and susceptibility to Cd-injury. The inability of parenterally administered HgCl2 to induce testicular injury compared to the same dose of CdCl2(0.011 mmol/kg) is apparently related to the poor uptake of Hg in the testes (one-eighteenth that of Cd) rather than to an inability of Hg to bind to the 30,000 MW Cd-BP. Our studies indicate that binding of Cd to this unique 30,000 MW testicular component, as yet unidentified, is a possible basis for the unique sensitivity of the testis to Cd injury.     

Concentrations of cadmium,zinc, copper,iron, and metallothionein in liver and kidney of nonhuman primates

To evaluate the species specificity of Cd accumulation and the relationship of Cd with other essential metals and metallothionein (MT), the concentrations of Cd, Zn, Cu, and Fe in the liver and kidney and the MT concentrations in the soluble fractions of the liver and kidney were determined in Cd-uncontaminated nonhuman primates (11 species, 26 individuals) kept in a zoo and two wild-caught Japanese macaques. The compositions of metal-binding proteins in the soluble fractions were also investigated by high-performance liquid chromatography (HPLC). The hepatic Cd concentration was 0.03–14.0 μg/g and the renal Cd concentration was 0.35–99.0 μg/g, both varying greatly and being higher in nonhuman primates, which were more closely related to man. The hepatic Zn concentration was 24.0–176 μg/g and the renal Zn concentration was 13.5–138 μg/g, showing 7- to 10-fold differences, and a correlation (r=0.558, p<0.01) was found between renal Zn and renal Cd concentrations. It was proved that in the liver, MT is more closely correlated with Zn (r=0.795, p<0.001) than with Cd (r=0.492, p<0.01) and that in the kidney MT is correlated with both Cd (r=0.784, p<0.001) and Zn (r=0.742, p<0.001). HPLC analysis of metals bound to MT-like protein in chimpanzees, de Brazza’s monkeys, and Bolivian squirrel monkeys showed that more than 90% of Cd in both the liver and kidney, approx 40% of Zn in liver and 28–69% of Zn in kidney were bound to MT-like protein. The higher percentage Zn was bound to high-molecular protein.     

Alterations of tissue glutathione levels and metallothionein mRNA in rainbow trout during single and combined exposure to cadmium and zinc

The objective of this study was to assess the effects of Cd and Zn exposure of rainbow trout (Oncorhynchus mykiss) on (a) hepatic glutathione (GSH) levels; and (b) hepatic and branchial metallothionein (MT) mRNA expression. Juvenile rainbow trout were exposed to waterborne Cd (nominal concentrations: 1.5 or 10 microg Cd l(-1)), Zn (150 or 1000 microg Zn l(-1)) or Cd/Zn mixtures (1.5 microg Cd l(-1) with 200 microg Zn l(-1) or 10 microg Cd l(-1) with 1000 microg Zn l(-1)). After 14 and 28 days of treatment, hepatic concentrations of total glutathione, oxidized glutathione (GSSG) and cysteine were determined by means of fluorometric high performance liquid chromatography (HPLC). Branchial and hepatic expression of MT mRNA was measured by means of semi-quantitative RT-PCR. Exposure of trout to Zn did not result in significantly elevated tissue levels of Zn, whereas Cd accumulation factors changed significantly with time and concentration. Despite of the absence of Zn accumulation, hepatic GSH but not MT mRNA levels were significantly altered in Zn-exposed fish. Cd, on the contrary, affected mainly the MT response but not GSH. Also tissue specific differences in the regulation of the two thiol pools were expressed. The thiol response after exposure to metal mixtures could not be explained by simple addition of the effects of the individual metals. The results indicate that cellular thiol pools show different reaction patterns with respect to specific metals and metal mixtures. Under conditions of long-term, low dose metal exposure, the function of GSH appears to go beyond that of a transitory, first line defense.     

Response of sugarcane to increasing concentrations of copper and cadmium and expression of metallothionein genes

Sugarcane (Saccharum spp.) offers the potential to be a phytoremediator species due to its outstanding biomass production, but its prospective metal accumulation and tolerance have not been fully characterized. Sugarcane plantlets were able to tolerate up to 100microM of copper in nutrient solution for 33 days, with no significant reduction in fresh weight, while accumulating 45mgCukg(-1) shoot dry weight. Higher levels of copper in solution (250 and 500microM) were lethal. Sugarcane displayed tolerance to 500microM Cd without symptoms of toxicity, accumulating 451mgCdkg(-1) shoot dry weight after 33 days, indicating its potential as Cd phytoremediator. DNA gel blot analyses detected 8 fragments using a metallothionein (MT) Type I probe, while 10 were revealed for the MT Type II and 8 for MT Type III. The number of genes for each type of MT in sugarcane might be similar to the ones identified in rice considering the interspecific origin of sugarcane cultivars. MT Type I gene appeared to present the highest level of constitutive expression, mainly in roots, followed by MT Type II, corroborating the expression pattern described based on large-scale expressed sequence tags sequencing. MT Type II and III genes were more expressed in shoots, where MT I was also importantly expressed. Increasing Cu concentration had little or no effect in modulating MT genes expression, while an apparent minor modulation of some of the MT genes could be detected in Cd treatments. However, the level of response was too small to explain the tolerance and/or accumulation of Cd in sugarcane tissues. Thus, cadmium tolerance and accumulation in sugarcane might derive from other mechanisms, although MT may be involved in oxidative responses to high levels of Cd. Sugarcane can be considered a potential candidate to be tested in Cd phytoremediation.     

Reduced uptake and enhanced release of cadmium in cadmium-resistant metallothionein null fibroblasts.

Metallothionein (MT) is known to play a predominant role in the protection of cells from cadmium (Cd) toxicity. To investigate other factors involved in Cd resistance, we established Cd-resistant cell lines from simian virus 40-transformed MT null fibroblasts. Cd-resistant MT null cells, Cd-rA7 and Cd-rB5, developed approximately 10-fold resistance to Cd compared to parental cells, but showed no cross-resistance to Zn, Cu, Hg, Ni, As, cisplatin or H2O2. Accumulation of Cd in the resistant cells was 13-18% of that of parental cells after treatment with Cd for 24 h. A short-term experiment revealed that the rate of Cd incorporation into the Cd-resistant cells was suppressed, and the rate of Cd release was enhanced in the resistant cells compared with that of parental cells. These results indicate that the altered transport of Cd, slow uptake and rapid release, may confer resistance to Cd on the Cd-resistant cells established from MT null fibroblasts.