Chronic cadmium exposure during pregnancy in the mouse: influence of exposure levels on fetal and maternal uptake

The uptake and distribution of orally administered cadmium-109 was studied in pregnant mice. Female outbred QS mice were given cadmium (Cd) supplemented drinking water for 1 mo before pregnancy and for the duration of pregnancy. The water contained either 0.0015 ppm Cd, 0.24 ppm Cd, or 40 ppm Cd. For the duration of pregnancy, 1.48 micrograms Cd/l (0.0015 ppm) in each solution was in the form of 109Cd (1 mCi/l). Control mice were given distilled/deionized water. On the day before term the mice were killed and a variety of adult and fetal tissues were examined in a gamma counter to determine their 109Cd concentrations. For each group the 109Cd concentration was highest in the maternal gastrointestinal tract, liver, and kidneys and lowest in the central nervous system (CNS) and blood. In general, the 109Cd concentrations in each organ were similar for each group of mice and were therefore independent of the overall oral Cd dose. A notable exception was the lower level in the duodenum in the 40 ppm group. In the fetal unit the chorioallantoic placenta contained the highest concentration of 109Cd. Concentrations in the fetuses were very low, comparable to those in the adult CNS. The 109Cd levels in the fetuses from group A were about fivefold greater than those of the fetuses from group C. There was no statistically significant evidence of specific localization in the fetal brain, kidney, or liver.     

Bioavailability of cadmium from infant diets in newborn rats

Infants are exposed to higher levels of cadmium (Cd) from infant and follow-on formulas than from breast milk. We studied the bioavailability of 109CdCl2 from cows' milk formula, soy formula, wheat/oat/milk formula, wholemeal/milk formula and water in 11-day-old rat pups. The pups received a single oral dose of one diet labelled with 109Cd, 0.1 or 0.3 mg Cd/kg body weight. After 2 or 24 h or 4, 9 or 12 days the fractional retention of 109Cd in the whole body, in segments of rinsed small intestine and in tissue was measured in a gamma counter. Pups receiving 109Cd in water or cows' milk formula had the highest mean whole-body retention. It ranged from 67% of the dose in the water group to 52% in the wholemeal/milk formula group 4 days after dosing. The retention of 109Cd in the rinsed small intestine was significantly higher in the water group and the cows' milk formula group than in the cereal-based formula groups at 24 h and 4 days after dosing. It was still high in all groups on day 9, ranging from 26 to 11%. Initially most of the 109Cd was retained in the duodenum but by day 4 it had moved further down into the jejunum. In the liver, the highest and lowest retention on day 4 was 16%, and 3 per thousand of the dose in the water group and wholemeal/milk formula group, respectively. In the kidney, 109Cd was still increasing 12 days after exposure in all groups. Whole-body retention and tissue levels were higher than previously reported in adult animals. The lower bioavailability of 109Cd from the cereal-based formulas compared to water and cows milk formula on the longer survival times is most likely explained by Cd binding to dietary fibre and phytic acid in the cereal-based formulas reducing the intestinal binding and decreasing the bioavailability of Cd. The high retention of 109Cd in the small intestine, leading to a prolonged absorption period, emphasizes the importance of extending studies on neonatal Cd absorption over a long time period in order to detect for example, endpoints, accumulation of Cd in the kidney.     

Influence of manganese on the gastrointestinal absorption of cadmium in rats

Four groups of male rats were given the following oral treatment: control group (n = 20) deionized drinking water, Mn group (n = 20) deionized drinking water containing 56 ppm Mn2+ (1 mmol/l), Cd group (n = 10) deionized drinking water containing 112 ppm Cd2+ (1 mmol/l) and Cd + Mn group (n = 10) deionized drinking water containing 112 ppm Cd2+ and 56 ppm Mn2+. Half of each group was sacrificed after 4 weeks and the other half after 8 weeks of treatment. At each time interval, the mean levels of Mn in blood, in urine and in the various tissues did not differ between the control and Mn groups. Furthermore, comparable Mn levels were found after 4 and 8 weeks of treatment. Microscopical examination of the brain failed to reveal any overt morphological alteration in the Mn group. With respect to the control group, the Cd and Cd + Mn groups exhibited increased levels of Cd in blood, urine, liver, whole kidney, kidney cortex and in brain (cortex, cerebellum, basal ganglia), but the Cd + Mn groups showed invariably lower levels than the Cd group after 4 weeks as well as after 8 weeks. These results suggest that the rate of gastrointestinal absorption of Cd is decreased by supplementation of the drinking water with a 'non-toxic' dose of Mn2+.     

The relative importance of water and food as cadmium sources to Daphnia magna Straus

Knowledge of the transport pathways of metals into aquatic organisms is paramount in determining the metal's potential mechanism of toxicity. To determine the relative importance of water and food as cadmium (Cd) sources for the cladoceran Daphnia magna grazing on the algae Chlorella vulgaris, we measured cadmium accumulation and toxicity (feeding inhibition and survival) in three genetically different clones of D. magna subsequent to water, food, and water and food exposures. We found that Cd uptake from water and food was independent of source and additive in effect, with D. magna juveniles accumulating twice as much Cd from water than from food (algae). However, the efficiency with which Cd was assimilated by D. magna from its algal diet was much higher (10%) than from water (0.3%). Uptake and toxic responses were inversely related: tolerant clones accumulated more Cd. As a consequence, models based on uptake of metals from the combined routes of water and food may be reliable to predict metal dynamics in the field, but may fail to predict toxic effects since tolerance to metals is not necessarily linked to reduced total uptake of metals.     

Uptake pathways and subcellular fractionation of Cd in the polychaete Nereis diversicolor

Polychaetes have often been utilized as indicator species to investigate the impacts of pollutants, such as heavy metals. The uptake of Cd by the polychaete Nereis diversicolor was determined at varying Ca concentrations and with pre-exposure to Ca ion channel blockers and metabolic inhibitors in simulated sea water over 1 week period. The supply of Ca in simulated sea water inhibited Cd uptake and increased Ca concentration in N. diversicolor after 10 μM Cd exposure. Pre-exposure to a Ca-channel blocker (Lanthanum) significantly inhibited Cd uptake, suggesting that the uptake of Cd was exerted at a Ca channel. N-ethylmaleimide, which specifically binds to sulfhydryl groups, inhibited Cd uptake at 10 μM, implying that the transport of Cd is carrier-mediated by proteins or other SH-containing compounds. Subcellular Cd distribution analysis showed that more than 60% of the total Cd associated with the cytosolic fraction. The presence of higher concentration of Ca in simulated sea water did not impact the proportional subcellular distribution of Cd in N. diversicolor. Nevertheless, the supply of Ca could significantly lower Cd concentration in cytosol and cellular debris. The present study provides evidence that Cd transport by N. diversicolor was mediated mainly through lanthanum- sensitive Ca ion channels and accumulated by SH-containing compounds. These results help to understand the uptake mechanism and subcellular distribution of Cd in polychaetes.     

Response of rat hepatocyte cultures to cadmium chloride and cadmium-diethyldithiocarbamate

Cellular effects of cadmium (Cd) were studied in primary cultures of rat hepatocytes incubated with cadmium chloride (CdCl2) or cadmium-diethyldithiocarbamate (Cd(DTC)2), labelled with 109Cd. The lipid-soluble complex Cd(DTC)2 was rapidly taken up into the cells and a maximal concentration was reached after 4 h incubation. On the other hand, incubation with CdCl2 resulted in a slow, continuous accumulation of Cd for up to 20 h. Cd was found to be associated with proteins to a higher extent when added to the incubation medium as CdCl2 than when added as Cd(DTC)2, which in addition to differences in lipophilicity of the Cd compounds partly explains the differences in Cd uptake. Subcellular distribution studies showed that a significantly higher proportion of Cd was associated with the total particulates fraction in cells after incubation with Cd(DTC)2 compared to CdCl2 (32 and 19%, respectively). The activities of glutathione reductase and succinic dehydrogenase were inhibited to a similar extent by the 2 Cd compounds. Alcohol dehydrogenase was more strongly affected by CdCl2 than by Cd(DTC)2, although the uptake of Cd was 3-4 times higher in cells incubated with Cd(DTC)2 than in those incubated with CdCl2. The results from the present study show that DTC can increase the transport of Cd into the cell by complex formation with Cd. Compared to CdCl2 the Cd(DTC)2 complex was less toxic as indicated by the biochemical parameters used.     

Influence of acclimation and cross-acclimation of metals on acute Cd toxicity and Cd uptake and distribution in rainbow trout (Oncorhynchus mykiss)

The development of chronic metal toxicity models for fresh water fish is complicated by the physiological adjustments made by the animal during exposure which results in acclimation. This study examines the influence of a pre-exposure to a chronic sublethal waterborne metal on acclimation responses as well as the uptake and distribution of new metal into juvenile rainbow trout. In one series of tests, trout were exposed to either 20 or 60 microg/L Cu, or 150 microg/L Zn for a month in moderately hard water and then cross-acclimation responses to Cd were measured in 96 h LC(50) tests. Cu exposed trout showed a cross-acclimation response but Zn exposed trout did not. Using these results, a detailed examination of Cd uptake and tissue distribution in metal-acclimated trout was done. Trout were exposed to either 75 microg/L Cu or 3 microg/L Cd for 1 month to induce acclimation and subsequently, the uptake and distribution of new Cd was assessed in both Cd- and Cu-acclimated fish using (109)Cd. The pattern of accumulation of new metal was dramatically altered in acclimated fish. For example, in 3 h gill Cd binding experiments, Cd- and Cu-acclimated trout both had a higher capacity to accumulate new Cd but only Cu-acclimated fish showed a higher affinity for Cd compared to unexposed controls. Experiments measuring Cd uptake over 72 h at 3 microgCd/L showed that the Cd uptake rate was lower for Cd-acclimated fish compared to both Cu-acclimated fish and unexposed controls. The results demonstrate the phenomenon of cross-acclimation to Cd and that chronic sublethal exposure to one metal can alter the uptake and tissue distribution of another. Understanding how acclimation influences toxicity and bioaccumulation is important in the context of risk assessment. This study illustrates that knowledge of previous exposure conditions is essential, not only for the metal of concern, but also for other metals as well.     

Dietary iron lowers the intestinal uptake of cadmium-metallothionein in rats.

It has been shown that addition of extra calcium/phosphorus (Ca/P), zinc (Zn) and iron (Fe2+) to the diet results in a significant protection against cadmium (Cd) accumulation and toxicity in rats fed inorganic Cd salt. However, it is not clear whether the presence of these mineral supplements in the diet also protects against the Cd uptake from cadmium-metallothionein. The present study examines the influence of Ca/P, Zn and Fe2+ on the Cd disposition in rats fed diets containing either 1.5 and 8 mg Cd/kg diet as cadmium-metallothionein (CdMt) or as cadmium chloride (CdCl2) for 4 weeks. The feeding of Cd resulted in a dose-dependent increase of Cd in intestine, liver and kidneys. The total Cd uptake in liver and kidneys after exposure to CdMt was lower than after exposure to CdCl2. At the low dietary Cd level and after addition of the mineral supplement, the kidney/liver concentration ratio increased. However, this ratio was always higher with CdMt than with CdCl2, suggesting a selective renal disposition of dietary CdMt. The uptake of Cd from CdCl2 as well as from CdMt was significantly decreased by the presence of a combined mineral supplement of Ca/P, Zn and Fe2+. The protection which could be achieved was 72 and 75% for CdMt and 85 and 92% for CdCl2 after doses of 1.5 mg/kg and 8 mg/kg respectively. In a following experiment it was shown that the protective effect of the mineral mixture against CdMt was mainly due to the presence of Fe2+. It seems clear that Cd speciation and the mineral status of the diet have a considerable impact on the extent of Cd uptake in rats.     

The influence of humic substances on the absorption and distribution of cadmium in mice.

The complex binding of cadmium ions to humic and fulvic acids in water may influence the absorption and distribution of drinking-water Cd in humans. Thus, in the present study mice were given a single oral dose of Cd (109CdCl2, 25 microg/l) in 100 microl Millipore water containing different concentrations of humic compounds (0, 1, 10 and 100 mg dissolved organic carbon/l). The complex binding of Cd was studied by dialysis. At neutral pH, 1 mg dissolved organic carbon/l caused complex binding of more than 50% of the Cd, whereas more than 90% of Cd was bound at 10 and 100 mg dissolved organic carbon/l. At pH 3 the complex binding of Cd decreased somewhat, but over 90% of the Cd was bound at 100 mg dissolved organic carbon/l. Complex binding of Cd increased the lipid solubility of Cd, expressed as an octanol/ water partition coefficient, Nevertheless, more than 99% of the bound Cd was present as hydrophilic binding forms. Irrespective of the bound of Cd, the intestinal uptake and intracellular distribution (gel filtration on Sephadex G-75 column) were not affected by the humic substances 6 hr after dosage. Moreover, complex binding did not influence the intestinal absorption of Cd 24 hr after exposure. The median Cd retention in the kidneys of the 100 mg dissolved organic carbon/l group was 23% and 46% lower than that of the control group 6 and 24 hr after administration, respectively, indicating alterations in the distribution of Cd after absorption. Thus humic substances may affect the metabolism of toxic heavy metals, such as Cd, in vivo in mice, indicating that the presence of humic and fulvic acids in drinking water should be considered in future risk assessments of metals in drinking water.     

Fulvic and humic acids decrease the absorption of cadmium in the rat intestine

 Dissolved organic carbon (DOC) in drinking water is mainly composed of fulvic and humic acids, which may form complexes with metal ions. The influence of DOC on the intestinal absorption of Cd in the rat was investigated using an “isolated intestinal segment” technique in anaesthetised rats. The lumens of segments were exposed for 60 min to different concentrations of CdCl₂ and DOC in intact animals. The fractional absorption (FA) was not dose dependent in the dosage interval 0.01–0.03 μg Cd/kg. However, at 15 and 150 μg Cd/kg both FA and intracellular Cd distribution in the segments were dose dependent, which is in line with results from other studies performed on similar experimental models. In the presence of 1 and 10 mg DOC/l, FA of Cd was just half as high as FA in animals that received Cd alone (0.01 μg/kg). Moreover, a higher percentage of Cd was associated with the metallothionein fraction in the intestinal segment of the DOC-dosed rats. An in vitro speciation experiment showed that only 0.2–7.9% of the Cd in the incubation solution was complexed to DOC. In deionized water, however, more than 99% of the Cd was complexed to DOC. This result indicates that the incubation solution contained substances that negatively affect complexation of Cd to DOC. Mechanisms other than complexation of Cd to DOC in the intestinal lumen may therefore be involved in the inhibitory effect of DOC on the absorption of Cd. Received: 15 March 1995/Accepted: 14 June 1995     

Effects of dietary calcium and cadmium on cadmium accumulation, calcium and cadmium uptake from the water, and their interactions in juvenile rainbow trout

The objective of this study was to examine the effects of chronically elevated dietary Ca2+ (as CaCO3), alone and in combination with elevated dietary Cd, on survival, growth, and Cd and Ca2+ accumulation in several internal compartments in juvenile rainbow trout (Oncorhynchus mykiss). In addition, effects on short-term branchial uptake and internal distribution of newly accumulated waterborne Ca2+ and Cd during acute waterborne Cd exposure (50 microg/L as CdNO3 for 3 h) were monitored using radiotracers (45Ca, 65Cd). Fish were fed with four diets: 20 mg Ca2+/g food (control), 50 mg Ca2+/g food, 300 microg Cd/g food, and 50 mg Ca2+/g + 300 microg Cd/g food for 30 days. There were no significant effects on growth, mortality, or total body Ca2+ accumulation. The presence of elevated Ca2+, Cd, or Ca2+ + Cd in the diet all reduced waterborne Ca2+ uptake in a short-term experiment (3 h), though the inhibitory mechanisms appeared to differ. The effects were marked after 15 days of feeding, but attenuated by 30 days, except when the diet was elevated in both Ca2+ and Cd. The presence of elevated Ca2+ in the diet had only modest influence on Cd uptake from the water during acute Cd challenges but greatly depressed Cd uptake from the diet and accumulation in most internal tissues. None of the treatment diets prevented the decreases in waterborne Ca2+ uptake and new Ca2+ accumulation in internal tissues caused by acute exposure to waterborne Cd. In conclusion, there are complex interactions between waterborne and dietary effects of Ca2+ and Cd. Elevated dietary Ca2+ protects against both dietary and waterborne Cd uptake, whereas both waterborne and dietary Cd elevations cause reduced waterborne Ca2+ uptake.     

Cadmium in milk and mammary gland in rats and mice

The purpose of the present investigation was to study the uptake of cadmium in mammary tissue, effects on milk secretion and composition, and lactational transport of cadmium to the sucklings. Cadmium exposure during lactation resulted in retention of cadmium in the mammary tissue in mice and rats. The uptake of cadmium in the mammary tissue was rapid, as shown in lactating mice by whole-body autoradiography 4 h after an intravenous injection of a tracer dose of (109)CdCl(2). Retention of cadmium in kidneys of suckling pups was observed in the autoradiograms at 7 days after exposure of the dams. Lactating rats were intravenously infused with (109)CdCl(2) in 0.9% saline via osmotic minipumps from day 3 to day 16 after parturition. The cadmium dose given was 0, 8.8, 62 and 300 microg Cd/kg body wt. per day. Plasma and milk were collected at day 10 and 16 after parturition. Plasma cadmium levels in dams increased from day 10 to day 16. Cadmium levels were higher in milk than in plasma, with milk/plasma ratios varying from 2 to 6. Zinc levels in milk were positively correlated to cadmium levels in milk (r(2)=0.26; P=0. 03). In milk, (109)Cd was distributed in fat (46-52%), casein fraction (40-46%), and whey fraction (6-8%). There was a high correlation between cadmium concentrations in pups' kidney and cadmium concentrations in dam's milk (r(2)=0.98; P < 0.001). Of the cadmium dose given to the dams <0.05% was retained in the litters on day 16 of lactation. No effects were observed due to cadmium exposure on body weight in pups or dams. Cadmium treatment did not cause any effect on the lactose or protein concentration in milk, the concentrations of DNA, RNA or the ratio RNA/DNA in the mammary gland. Histological evaluation of mammary tissue did not reveal any abnormalities at any dose level. (109)Cd was bound to metallothionein in mammary tissue. The fraction of radiolabelled cadmium bound to metallothionein increased in a dose-dependent manner in both the liver (88-98%) and mammary tissue (57-80%). The present results indicate a low transfer of cadmium to the suckling pup, which might be due to binding of cadmium to metallothionein in the mammary tissue. However, during the susceptible developmental period even a low cadmium exposure may be of concern.     

Effect of sodium diethyldithiocarbamate on placental passage and foetal distribution of cadmium and mercury in mice

The administration of sodium diethyldithiocarbamate to 18 day pregnant mice, which previously had been given 109Cd2+ or 203Hg2+ was found to result in increased levels of the metals in the foetuses, in comparison with mice given the 109Cd2+ or 203Hg2+ alone. The level of 109Cd2+ in some foetal tissues was increased 30-60 times. In the animals given 203Hg2+ 3-5 times higher concentrations were seen in most foetal tissues of the sodium diethyldithiocarbamate-treated animals compared with animals not treated with this substance. Cadmium and mercury were shown to form highly lipophilic complexes with diethyldithiocarbamate and a facilitated transfer of these complexes through the placental membranes probably explains the increased uptake of the metals in the foetuses.     

Health effects of low-level cadmium intake and the role of metallothionein on cadmium transport from mother rats to fetus

Female Wistar rats were given Cd (as CdCl(2)) at a dose of 0, 1, 2, and 5 mgCd/kg/day by gastric tube daily for 6 consecutive days each week for 10 weeks. After the birth, newborn rats were sacrificed on day 1 and at 4 weeks. Mother rats were sacrificed after 4 weeks of lactation The concentrations of Cd in uterus and placenta, and metallothionein (MT) in the uterus of mother rats were determined. The concentrations of Cd in kidney and liver of newborn rats were also determined. Expression of iso-MT genes (I, II, and III) in the uterus of mother rats was measured using RT-PCR. The Cd concentration in the liver of newborn rats at the first day after birth was higher than in the kidney, while the concentration in the kidney of newborn rats at the fourth week after the birth was significantly higher than in the liver. The uterine MT concentration increased with accumulation of Cd; however, the MT concentration did not increase enough to prevent Cd transport to the fetus. On the other hand, it was considered that more Cd was transported as the chemical form of nonMT-Cd from mother rat, and accumulated in the liver rather than kidney of the fetus. Based on analyses of the Cd distribution in the liver and kidney of newborn rats, we speculate that MT in the uterus and placenta does not play a significant role in preventing Cd transport through the placenta from the uterus to the fetus.     

The Influence of Humic Substances on the Absorption and Distribution of Cadmium in Mice

Abstract: The complex binding of cadmium ions to humic and fulvic acids in water may influence the absorption and distribution of drinking-water Cd in humans. Thus, in the present study mice were given a single oral dose of Cd (¹⁰⁹CdCl₂, 25 μg/l) in 100 μl Millipore® water containing different concentrations of humic compounds (0, 1, 10 and 100 mg dissolved organic carbon/l). The complex binding of Cd was studied by dialysis. At neutral pH, 1 mg dissolved organic carbon/l caused complex binding of more than 50% of the Cd, whereas more than 90% of Cd was bound at 10 and 100 mg dissolved organic carbon/l. At pH 3 the complex binding of Cd decreased somewhat, but over 90%) of the Cd was bound at 100 mg dissolved organic carbon/l. Complex binding of Cd increased the lipid solubility of Cd, expressed as an octanol/water partition coefficient, Nevertheless, more than 99% of the bound Cd was present as hydrophilic binding forms. Irrespective of the bound of Cd, the intestinal uptake and intracellular distribution (gel filtration on Sephadex G-75 column) were not affected by the humic substances 6 hr after dosage. Moreover, complex binding did not influence the intestinal absorption of Cd 24 hr after exposure. The median Cd retention in the kidneys of the 100 mg dissolved organic carbon/1 group was 23%> and 46% lower than that of the control group 6 and 24 hr after administration, respectively, indicating alterations in the distribution of Cd after absorption. Thus humic substances may affect the metabolism of toxic heavy metals, such as Cd, in vivo in mice, indicating that the presence of humic and fulvic acids in drinking water should be considered in future risk assessments of metals in drinking water.     

Glycine reduces cadmium-induced teratogenic damage in mice

The effect of glycine in preventing cadmium (Cd) teratogenicity in mice was studied. Cadmium chloride (CdCl2) was administered subcutaneously at 1, 2 or 4 mg/kg doses on gestation days (GD) 7, 8 and 9. Glycine was given ad libitum (in the drinking water) from GD0 through GD18 (the day when animals were killed), as a 1% and 2% drinking water solution. Cd and nucleic acid concentrations in embryos were determined. The most common finding seen after CdCl2 4 mg/kg exposure was exencephaly. The incidence of this malformation was significantly reduced in mice receiving 2% glycine while fetal Cd significantly decreased as compared to cadmium-treated positive control animals. Increased nucleic acid levels were seen in the same embryos. In glycine non-supplemented mice given CdCl2 4 mg/kg, embryonic lipid peroxidation proved to be increased. In conclusion, lipid peroxidation was associated with cadmium-induced teratogenicity, and glycine inhibited the cadmium-induced effect by inhibiting placental transport of cadmium. However, further detailed studies are needed to establish the mechanism(s) of action.     

Association between cadmium and calcium uptake and distribution during the moult cycle of female shore crabs, Carcinus maenas: an in vivo study

Net influxes into the haemolymph and tissue distribution of 45Ca and 109Cd were studied in vivo in female Carcinus maenas at different moult stages. Net influxes of 45Ca and 109Cd from water were higher in postmoult (A and B) C. maenas than in C3- and C4-intermoult crabs and the net influx of calcium was higher in C3-intermoult crabs than in C4-intermoult crabs. The net influxes of 45Ca and 109Cd increased in postmoult C. maenas with decreasing external calcium concentrations at constant salinity. At all external calcium concentrations a significant correlation existed between 45Ca and 109Cd accumulated in the haemolymph of individual animals. In vivo exposure of postmoult C. maenas to external lanthanum decreased the 45Ca and 109Cd uptake rates to 30 and 10%, respectively, of the control values. About 30% of injected 109Cd were found in the midgut gland, 10-20% in the gills and only a few (1-2) percent was lost to the seawater 24 h after injection. No major variations in tissue distribution of 109Cd were observed between moult stages in these tissues. Premoult crabs retained more cadmium in the haemolymph 24 h after injection than other moult stages, and postmoult crabs retained more in muscle. Between 20 and 40% of the injected 45Ca were excreted to the water, while only a few percent of the injected 45Ca were found in the soft tissues 24 h after injection. Large moult stage variations, however, were observed in the tissue distribution of internalised 45Ca. This study demonstrates that cadmium and calcium uptakes are elevated in postmoult C. maenas. The results indicate that cadmium and calcium in this stage are taken up via Ca2+-channels located in the apical membrane of gill epithelium cells. When internalised, however, cadmium and calcium are metabolised in fundamentally different ways, determined by the chemical properties and biological significance of the two metals.     

The influence of ascorbic acid on lipid peroxidation in guinea pigs intoxicated with cadmium

Cadmium (as CdCl₂) administered at a dose of 1 mg Cd/animal/day in drinking water to guinea pigs with a low intake of ascorbic acid (2 mg/animal/day) increased lipid peroxidation (LPO) in the kidney, liver and serum after 5 wk of treatment. A high intake of ascorbic acid (100 mg/animal/day) decreased LPO (determined from malondialdehyde levels) in the kidney, liver and serum of Cd-treated guinea pigs. Administration of Cd to guinea pigs with a low intake of ascorbic acid significantly increased LPO in the kidney at 5 wk, in comparison with controls given low levels of ascorbic acid but no Cd. However, at 12 wk, LPO in the kidney of Cd-treated guinea pigs was significantly lower than in the controls. These results indicate that the level of lipid peroxides in the kidney of guinea pigs with a low intake of ascorbic acid depends on the amount of accumulated cadmium.     

Branchial cadmium and copper binding and intestinal cadmium uptake in wild yellow perch (Perca flavescens) from clean and metal-contaminated lakes

Branchial binding kinetics and gastro-intestinal uptake of copper and cadmium where examined in yellow perch (Perca flavescens) from a metal-contaminated lake (Hannah Lake, Sudbury, Ontario, Canada) and an uncontaminated lake (James Lake, North Bay, Ontario, Canada). An in vivo approach was taken for gill binding comparisons while an in vitro gut binding assay was employed for gastro-intestinal tract (GIT) uptake analysis. By investigating metal uptake at the gill and the gut we cover the two main routes of metal entry into fish. Comparisons of water and sediment chemistries, metal burdens in benthic invertebrate, and metal burdens in the livers of perch from the two study lakes clearly show that yellow perch from Hannah L. are chronically exposed to a highly metal-contaminated environment compared to a reference lake. We found that metal-contaminated yellow perch showed no significant difference in gill Cd binding compared to reference fish, but they did show significant decreases in new Cd binding and absorption in their GITs. The results show that gill Cd binding may involve low-capacity, high-affinity binding sites, while gastro-intestinal Cd uptake involves binding sites that are high-capacity, low-affinity. From this we infer that Cd may be more critically controlled at the gut rather than gills. Significant differences in branchial Cu binding (increased binding) were observed in metal-contaminated yellow perch. We suggest that chronic waterborne exposure to Cu (and/or other metals) may be the dominant influence in gill Cu binding rather than chronic exposure to high Cu diets. We give supporting evidence that Cd is taken up in the GIT, at least in part, by a similar pathway as Ca(2+), principally that elevated dietary Ca(2+) reduces Cd binding and uptake. Overall our study reveals that metal pre-exposure via water and diet can alter uptake kinetics of Cu and Cd at the gill and/or the gut.     

Slc39a14 gene encodes ZIP14, a metal/bicarbonate symporter: similarities to the ZIP8 transporter

The mouse and human genomes contain 14 highly conserved SLC39 genes. Viewed from an evolutionary perspective, SLC39A14 and SLC39A8 are the most closely related, each having three noncoding exons 1. However, SLC39A14 has two exons 4, giving rise to Zrt- and Irt-related protein (ZIP)ZIP14A and ZIP14B alternatively spliced products. C57BL/6J mouse ZIP14A expression is highest in liver, duodenum, kidney, and testis; ZIP14B expression is highest in liver, duodenum, brain, and testis; and ZIP8 is highest in lung, testis, and kidney. We studied ZIP14 stably retroviral-infected mouse fetal fibroblast cultures and transiently transfected Madin-Darby canine kidney (MDCK) polarized epithelial cells. Our findings include: 1) ZIP14-mediated cadmium uptake is proportional to cell toxicity, but manganese is not; 2) ZIP14B has a higher affinity than ZIP14A toward Cd(2+) (K(m) = 0.14 versus 1.1 microM) and Mn(2+) uptake (K(m) = 4.4 versus 18.2 microM); 3) ZIP14A- and ZIP14B-mediated Cd(2+) uptake is most inhibited by Zn(2+), and next by Mn(2+) and Cu(2+); 4) like ZIP8, ZIP14A- and ZIP14B-mediated Cd(2+) uptake is dependent on extracellular HCO(3)(-); 5) like ZIP8, ZIP14 transporters are localized on the apical surface of MDCK-ZIP cells; and 6) like ZIP8, ZIP14 proteins are glycosylated. Tissues such as intestine and liver, located between the environment and the animal, show high levels of ZIP14; given the high affinity for ZIP14, Cd(2+) is likely to act as a rogue hitchhiker-displacing Zn(2+) or Mn(2+) and entering the body to cause unwanted cell damage and disease.