Cadmium uptake and depuration in different organs ofLymnaea stagnalis L. and the effect of cadmium on the natural zinc level

The uptake of cadmium (0.1 mg/L) into various organs of the pond snailLymnaea stagnalis L., the depuration of accumulated Cd, and the change in the natural Zn level under the influence of Cd treatment were investigated during a 2 month period. The snails were fed with lettuce (Latuca sativa). The concentrations of Cd were measured in the whole soft body, various organs (liver, viscera, foot), the shell and the lettuce; and zinc concentrations were measured in various organs and the lettuce. As its Cd concentration remained at 10 g/g, which was much lower than the initial value for the soft body (69.4±5.71 g/g), the shell, according to our results, is incapable of accumulating Cd. The uptake pattern of the soft body showed a correlation with the initial Cd levels depending on differences in the Cd concentration of the lettuce. At the higher initial value (69.4±5.71 g/g) the linear Cd uptake began later then it did at the lower initial value; afterwards the snail was saturated with Cd. In the case of the lower, 9.02±1.3 g/g initial concentration, a rapid linear Cd uptake occurred till the 7th day, then the intensity of the uptake decreased. Saturation occurred at 200 g/g Cd concentration, regardless of the initial value. At the lower initial tissue level, the foot and the viscera showed a linear uptake pattern, while the liver, which has the greatest accumulation ability, displayed a logarithmic uptake pattern. The initial and the final Cd concentrations in the foot, viscera, and liver of theL. stagnalis were as follows: 10.3±2.15–60.1±7.13, 5.15±1.04–156±27.2, 14.1±3.09–430±23.3 g/g respectively. The bioconcentration factors (CF) were in the 10² (foot) and 10³ (viscera, liver, soft body) orders of magnitude. Forty to 45% of the accumulated Cd was depurated in Cd-free tap water; during the first three days of the uptake period, a negative linear correlation was found between Cd and Zn levels in the snail organs.     

The influence of cadmium and zinc on cadmium turnover in the zebrafish,Brachydanio rerio

A study was made of the dynamics of non-dietary cadmium in fish exposed to different concentrations of cadmium and zinc in water. Zebrafish,Brachydanio rerio, were exposed to Cd and Zn for various periods. The fate of a short pulse of the radioactive tracer¹⁰⁹Cd (3 or 9 days) was studied during a post-pulse period of 53 or 83 days. The tracer elimination and accumulation were described by exponential equations. The constants obtained from regression analysis of the results were used as a tool for evaluation of the findings.The majority of the¹⁰⁹Cd taken up in the gills during the pulse period was retained in the gill tissue and slowly transferred to the internal organs or lost to the water during the post-pulse period. The retention of tracer in the gills after a 3-day¹⁰⁹Cd pulse was increased by Zn but not influenced by Cd. Continuous exposure to stable Cd increased the rate of turnover of the retained¹⁰⁹Cd. Both Cd and Zn increased the tracer accumulation in the liver and kidney. The results also indicated that the effect of Zn on the Cd turnover might be lost if the environmental Zn is withdrawn before the start of the¹⁰⁹Cd pulse.A tendency of increased mortality of the fish exposed to 1 g Cd/L for 2–3 months suggested that low concentrations of Cd is toxic to the fish during chronic exposure. The increased Cd uptake and transfer in the gills, caused by Zn, could have deleterious effects on the fish. It might also reflect a change in the form of transport and in the intracellular handling of the metal, which protects the fish from Cd toxicity. However, a Zn pre-exposure did not decrease the mortality, which suggests that Zn did not protect the fish from Cd toxicity.     

Effects of cadmium on metal composition and adenylate energy charge in the sea starAsterias rubens L

Sea stars,Asterias rubens, were exposed to 200 g Cd/L or fed with mussels which contained about 70 g Cd/g dry wt. After 5 weeks, cadmium in the pyloric caeca of directly and indirectly exposed sea stars had reached levels of 12 and 9 g Cd/g dry wt, respectively. For both types of exposure, a reduction of 30% of the zinc levels in the pyloric caeca was found, which was correlated with a comparable displacement of zinc from the metallothionein-like proteins. Copper levels were increased in the pyloric caeca of directly exposed sea stars.In gonads, stomachs, and body wall of directly exposed sea stars, cadmium concentrations were 4 to 9 times higher than those in animals fed with Cd-contaminated mussels. Cadmium exposure also affected metal composition in these tissues. The ovaries contained relatively large amounts of zinc. Gel filtration chromatography revealed that this zinc and the accumulated cadmium were distributed over a large range of high-molecular-weight proteins.Both direct and indirect cadmium exposure resulted in a small, but significant decrease of the adenylate energy charge (AEC) in the pyloric caeca. In the gonads, no effect of the cadmium exposure could be demonstrated on the AEC, but in the ovaries a reduction of the adenylate pool was found.In semi-field experiments, stars were exposed to 25 g Cd/L or fed with mussels collected from the heavily polluted Dutch Western Scheldt. After 6 months of direct or indirect exposure, cadmium in the pyloric caeca had reached comparable levels of 8 and 7 g/g dry wt, respectively. In the gonads of sea stars that had been fed with Western Scheldt mussels, cadmium levels were lower than those in directly exposed sea stars, but still about a factor 10 higher than those in unexposed animals. Exposure of sea stars to 25 g Cd/L for three months, had no effects on the levels of zinc, copper and magnesium or on the AEC in the pyloric caeca.     

Copper/Metal Ratios in the Gills of Rainbow Trout (Oncorhynchus mykiss) Provide Evidence of Copper Exposure Under Conditions of Mixed-Metal Exposure

Previous work has suggested that the ratio of copper residues to zinc in the gills of rainbow trout may indicate short-term exposure to increased levels of waterborne copper. However, the effect of exposure to a combination of increased copper and zinc concentrates in the water column was unknown. We exposed rainbow trout to 8 ± 2 g L^–1, 40 ± 2 g L^–1 and 90 ± 9 g L^–1 of waterborne copper and 21 ± 3 g L^–1, 129 ± 40 g L^–1, and 202 ± 40 g L^–1 of waterborne zinc in a 2-factor experiments and gill copper and zinc residues were examined. Other gill parameters analyzed included the concentrations of calcium, magnesium, sodium, and potassium, liver copper and zinc concentrations and plasma copper, calcium, sodium, and potassium are also reported here. Copper residues in the gill filaments were significantly higher in the highest level of copper exposure (high Cu, 4.06 g g^–1; low Cu 2.41 g g^–1; 0 Cu 2.01 g g^–1; P = 0.001), whereas no differences were seen in zinc concentrations at any treatment level. Gill sodium and plasma calcium concentrations were also decreased at the highest waterborne copper concentrations. Although copper–zinc ratios in the gills were significantly different between the highest and lowest copper treatments (P = 0.002, F = 6.59), copper–sodium and copper–magnesium ratios were more sensitive to waterborne copper exposure (P = 0.001, F = 17.91 and P = 0.002, F = 15.45, respectively). These copper–metal ratios may be better indicators of copper loading in the water column.     

Transfer of cadmium in a phytoplankton-oyster-mouse food chain

The trophic transfer of cadmium (Cd) was studied in a phytoplankton-oyster-mouse food chain. Phytoplankton, grown in a continuous culture chemostat system containing CdCl₂ plus the isotope¹⁰⁹Cd, accumulated 70% of the total supplied cadmium. Oysters filtered out 85 to 95% of the phytoplankton. The rate of oyster Cd accumulation at 15 C increased linearly with seawater Cd concentration according to: y=0.066X – 0.15 (n =12, r=0.96); where X=g Cd/L seawater (between 2 and 22) and y=g Cd/g dry wt oyster/ day. About 59% of the Cd accumulated by the oysters came from the phytoplankton food source and 41% from the cadmium dissolved in the water. Sixty-one percent of the total supplied cadmium was retained in the whole soft body of the osyters. Mice fed 0.4 g of oyster-bound Cd per g of diet, retained 0.83% of the dietary cadmium consumed. Mouse kidney retention for organic oyster-bound cadmium was 0.14%. Extrapolation of these results to human risk assessment indicates that moderate consumption of oysters, which are not highly contaminated with cadmium, poses no significant health risk in terms of elevating kidney cadmium levels.     

Binding of cadmium by cyanobacterial growth media: Free ion concentration as a toxicity index to the cyanobacteriumNostoc UAM 208

A quantitative study of cadmium binding to three different growth media for nitrogen-fixing cyanobacteria was done with the aid of a solid state ion-specific electrode. Kratz and Myers modified medium and Arnon medium bound large amounts of Cd²⁺, BG11₀ medium had less binding capacity. Of the media components, phosphate ion showed the greatest ability to bind Cd²⁺. Different pHs, the size of cell inoculum and two buffers (Tricine and HEPES, 25 mM) also changed the availability of free cadmium ion in solution.The effect of free Cd²⁺ ion towards the cyanobacteriumNostoc UAM 208, isolated from a heavy metal polluted environment, also was tested. The effective concentration affecting 50% of population (EC₅₀), at 120 h of exposure, was less for nitrogenase activity (0.26 g/mL) than for growth (0.55 g/mL), suggesting that this enzyme activity is more sensitive to cadmium than growth. Furthermore, cadmium toxicity was influenced by the addition of buffers to the growth medium. In the presence of buffer, Tricine (25 mM), growth and nitrogenase activity was reduced by 50% at a total cadmium concentration of about 115 g/mL, although no free ion was detected in this case.These results suggest that although generally cadmium toxicity is a function of free metal ion concentration, this can also vary in the presence of complexing agents.     

A pilot study of lead and cadmium exposure in young children in Stockholm,Sweden: Methodological considerations using capillary blood microsampling

A capillary blood microsampling technique was tested among urban young children in Stockholm. Blood lead (BPb) and hemoglobin (Hb) concentrations were determined in capillary blood obtained by fingerstick from 41 children, 13–20 months old, and the accompanying parent. The quality control included control for lead (Pb) and cadmium (Cd) contamination of material and equipment used for blood sampling, washing procedures for the hands and fingers to be punctured, comparisons of Pb and Cd concentrations in blood obtained by fingerstick and by brachial vein puncture from the same individuals, analysis of external quality control samples for Pb and Cd in blood together with the collected samples, and evaluation of the analytical performance using linear regression analysis.The results showed that blood sampling material may contaminate the blood samples with amounts of Pb and Cd that would seriously influence the monitoring results in the low concentration range (<100 g Pb/L and <1 g Cd/L). However, it is possible to obtain reliable BPb concentrations (>10 g Pb/L), but not BCd concentrations (<1 g Cd/L), with the capillary blood microsampling technique tested provided that a strict quality control is applied. The sampling procedure tested was well accepted by the children and their parents. The children's median BPb concentration (27 g/L; range 9–73 g/L) was similar to the median BPb concentration of their parents (27 g/L; range 7–74 g/L). However, the correlation between child and parent BPb concentrations was poor (R²=0.20), which may indicate different sources to Pb exposure in children and parents.     

The disposition of cadmium and zinc inPandalus montagui

Cadmium uptake rates in various tissues ofPandalus montagui exposed to sea water containing 37 gCd/L for 14 days ranged from 0.002–0.06 g/g dry tissue/hr. During depuration for 57 days, the levels in most tissues decreased slightly, but continued to rise in the hepatopancreas indicating Cd redistribution. Exposure to 65 g Zn/L produced no substantial change in Zn content of the tissues. An increase occurred in eggs and hepatopancreas during the first six days of depuration. During exposure to Cd and Zn combined (40 g Cd/L + 70 g Zn/L), tissue Zn levels responded as with Zn alone. In the presence of Zn, Cd concentration was doubled in the hepatopancreas, depressed by one-third in the carcass, and did not change in the other tissues. Increased amounts of Zn (up to 410 g Zn/L) had no effect on the Cd levels of the tissues except that the Cd level in the hepatopancreas was depressed, although the level was still greater than in the case of exposure to Cd alone. The possible role of metallothionein is discussed.     

Measurement of manganese amelioration of cadmium toxicity inChlorella pyrenoidosa using turbidostat culture

Cadmium (Cd) toxicity and amelioration of Cd toxicity by Mn were measured inChlorella pyrenoidosa, using turbidostat culture. The responses were measured in terms of the maximum specific growth rate, _max, of the populations. In turbidostat culture _max is a dependent variable that can be measured continuously. Cd (as CdCl₂· 2.5 H₂O) was added to control populations at a concentration of 1.8 M Cd. Toxicity was expressed after a 5 generation lag and resulted in a _max steady state 62% lower than the initial control after 2 generations. With continued Cd exposure, Mn (as MnCl₂ · 6H₂O) was then added stepwise to a concentration of 10.4 M Mn which caused a rapid, immediate increase in _max followed by linear increase until a steady-state plateau was reached at a _max 90% of control. The ameliorative response spanned 20 culture generations. After addition of Mn (10.4 M), cellular Cd concentration did not change and cellular Mn concentration increased. Increase in mean cell size accompanied Cd exposure and was significantly decreased when supplemented with 10.4 M Mn. Possible mechanisms of the amelioration are discussed.     

Effects of cadmium in freshwater clams. I. Interaction with essential elements inAnodonta cygnea

The elemental composition of the freshwater clam,Anodonta cygnea, was investigated in response to exposure to cadmium at 50 ppb (g/L) Cd during 12 weeks. Accumulation of cadmium affected the composition in various tissues and hemolymph. From 2 to 8 weeks of exposure considerable loss of sodium occurred, to about half the levels in control animals. During the last four weeks of exposure, sodium concentrations stabilized at the decreased level while those of potassium started to decline. Minor changes were noticeable for other elements. Calcium and iron tended to increase in all organs examined while magnesium levels remained constant. Zinc increased slightly during exposure to cadmium. For some elements, especially zinc and sulphur, hemolymph concentrations showed a response opposite to those in tissues. Concentrations of Al, B, Ba, Be, Ce, Co, Cr, Cu, Li, Mn, Mo, Ni, P, Pb, Sn, Sr, Ti, V, Y, and Zr did not change during Cd exposure. Possible sites of cadmium interaction with ionic regulation are discussed.     

Tissue-Specific Cadmium and Metallothionein Levels in Rainbow Trout Chronically Acclimated to Waterborne or Dietary Cadmium

Rainbow trout were exposed to a sublethal concentration of waterborne Cd (0 or 3 g/L) or dietary Cd (0 or 500 mg/kg dry wt) for 30 days to induce acclimation, and tissue Cd and metallothionein (MT) levels were examined. The greatest Cd concentrations were observed in the kidney followed by the gills and liver of the fish exposed to Cd via water, but in the gut tissues followed by the kidney, liver, and gills for dietary-exposed fish, reflecting a variation depending on the route of Cd exposure. Some MT was found in the nonacclimated naïve fish with no experience of elevated Cd exposure, and these background MT levels were quite high in the posterior intestine (480 g/g), cecae (257 g/g), and liver (248 g/g) relative to other tissues (7–50 g/g). With exposure to both waterborne and dietary Cd, MT levels rose significantly in all observed tissues. The increases relative to the control levels of MT in naïve fish were in the order: kidney (5.4 times) > gills (4.6) > liver (1.3) for the waterborne exposure group, and in the order kidney (19.3 times) >> cecae and posterior intestine (6.5 times) > liver and stomach (5 times) > midintestine (4.3 times) > gills (2.1 times) for the dietary exposure group. At 24 hours after an acute gastrointestinal dose of Cd (276 g/kg) infused into the stomach of dietary exposure groups, large increases of total Cd but not MT levels were found in the gut tissues of nonacclimated fish; in the Cd-acclimated fish, the posterior intestine was greatly affected with decreases in Cd (71%), Zn (33%), Cu (70%) and MT (46%) levels, suggesting an enhanced sloughing of tissue materials after infusion. Exposure to Cd did not cause any notable decrease of Zn or Cu in any tissue, except that found in the posterior intestine. However, a molar analysis indicated that although Cd levels remained less than MT binding capacity in both waterborne and dietary exposure groups, the total metal levels (Cd + Zn + Cu) greatly exceeded MT binding capacity in all tissues of Cd-exposed fish, suggesting a potential competition of Cd with other metals for binding sites on MT and non-MT proteins in the tissues.     

Cadmium and zinc accumulation and elimination by freshwater crayfish

A theoretical compartment model for the uptake of Cd and Zn by the freshwater crayfish,Procambarus acutus acutus (Girard), was constructed, and included a factorially designed experiment to study the relative importance of food and water as uptake vectors for¹⁰⁹Cd and⁶⁵Zn. Food and water were important pathways for Cd accumulation and the two uptake vectors were first order, independent, and additive. The rate of Cd elimination was not significantly different from zero during either the uptake or depuration phases. Rate constants for uptake from 5 and 10 g Cd · L^–1, calculated on a concentration basis, were 0.84 ± 0.031 and 0.83 ± 0.029 day^–1, respectively. Although there was no measurable Cd elimination, crayfish reached a steady state concentration of about 12.5g Cd · g^–1, dry weight. A small amount of Zn was accumulated via food, relative to that accumulated from water; the former had a much longer retention time than the latter, which was lost rapidly. When Zn in food was the only source, steady state was reached rapidly; Zn accumulation from food and water was not additive. Zn accumulated from water, reached no steady state. Zn uptake was proportional to water concentrations within the fed treatment groups and those not fed Zn-contaminated food. Zn elimination was first order to Zn concentration in the crayfish. Rate constants for Zn accumulation from 50 and 100 g Zn · L^–1 when fed Zn-contaminated food were 1.34 ± 0.064 and 1.46 ± 0.073 day^–1 (estimate ± 95% CI based on concentration), respectively, while rate constants for Zn elimination were 0.034 ±0.0021 and 0.05 ± 0.0032, respectively.     

Lead,cadmium, and aluminum accumulation in the red swamp crayfishProcambarus clarkii G. collected from roadside drainage ditches in louisiana

The concentration of Pb, Cd, and Al in tissues of crayfishProcambarus clarkii were evaluated from several wetland sites located adjacent to roadways and were compared to crayfish harvested from a commercial site free from roadside influences. Abdominal muscle, hepatopancreas, alimentary tract, exoskeleton and blood were analyzed for metal content. Results indicated that levels of contamination obtained in almost all tissues of crayfish from roadside ditches contained significantly higher amounts of metals than those of the commercially harvested control crayfish (p = .05–.001). Detection limits of Pb, Cd, and Al ranged from 0.04 g Pb/g to 16.15 g Pb/g.001 g Cd/g to .13 g Cd/g, and 1.22 g Al/g to 981 g Al/g, respectively. Concentrations of Pb, Cd, and Al were highest in the hepatopancreas and alimentary tract. High levels of these elements were also detected in the exoskeleton. In contrast, muscle tissue was the least affected tissue. Several significant correlations among concentrations of metals were found when comparing a variety of tissues inProcambarus clarkii.     

Accumulation of cadmium byNereis virens

Cadmium concentration inNereis virens exposed to sediment spiked with cadmium increased linearly with time, no equilibrium concentration being indicated by 24 days of exposure. The concentration withinN. virens also increased with concentration of Cd in the sediment, and smaller worms accumulated higher amounts per unit weight than larger worms. With exposure to sediment containing 1 to 4 ppm Cd, accumulation rates ranged from 0.018 to 0.037g Cd/g dry wt/hr for 1- to 2-g worms and from 0.014 to 0.024g Cd/g dry wt/hr for 5- to 7-g worms. N. virens exposed to 0.03 to 9.2 ppm Cd in sea water for 14 days had accumulation rates of 0.019 to 2.217g Cd/g dry wt/hr for 1- to 2-g worms and 0.013 to 1.327g Cd/g dry wt/hr for 5- to 7-g worms.There was practically no excretion of cadmium forN. virens with initial concentrations of 5 to 20g Cd/g dry wt during 75 days in clean conditions.Sediment containing 1 and 4 ppm Cd produced concentrations of about 0.03- and 0.1-ppm cd in the overlying water. The accumulation rates from sediment with 1 and 4 ppm Cd are equal to the rates from sea water with 0.03 and 0.1 ppm Cd, respectively, indicating that cadmium uptake byN. virens is primarily from the aqueous phase.     

Responses of hemocytes and gill tissues to sublethal cadmium chloride poisoning in the crabParatelphusa hydrodromous (Herbst)

The hemocytic and gill tissue responses of the crabParatelphusa hydrodromous (Herbst) to a wide range of sublethal concentrations of cadmium chloride (0.02–0.50 M/L) were examined after a 30-day exposure using hemocyte counts (THC and DHC) and lamellar pathology. A continued reduction in the hemocyte counts and selective changes in the numbers of hyalinocytes and eosinophilic granulocytes was evident in the toxified crabs. Under sublethal stress, the hyalinocytes developed eccentric nuclei, granular cytoplasm and membrane blebs. Atypical shape, lobate nucleus, dense cytoplasmic deposits and granuloplasmic vacuoles were frequently observed in the granulocytes. Greater proliferation of prohemocytes and abnormal hemocyte morphology indicated cadmium-induced neoplastic transformation of hemocytopoietic organs. No major structural changes in the gills were noted at 0.02 M CdCl₂. Nodular gill disease (NGD), hemocytic hyperplasia and sloughing of walled off hemocytes were prominant lesions after 0.50 M cadmium chloride exposure.     

Effects of cadmium on growth and bioaccumulation in the northwestern salamander Ambystoma gracile

Tests were conducted to determine the effects of cadmium (Cd) on survival, growth, and bioaccumulation in larvae and metamorphosed juveniles of the Northwestern salamander, Ambystoma gracile. A 96-h LC50 value of 468.4 g/L Cd was determined for 3-mo old larvae. Significant adverse effects of Cd (in water) on larval growth were observed at 227.3 g/L in a 10-day exposure and at 193.1 g/L Cd (LOAEL) in a 24-day exposure; no significant adverse effects were seen at 106.3 g/L Cd in the 10-day test and 48.9 g/L Cd (NOAEL) in the 24-day test. In the juvenile feeding tests, regurgitation of Cd-spiked food occurred at 5,701 and 2,458 g/g Cd, but not at 982 g/g. Cadmium tissue bioconcentration values up to 63 times the water concentration were seen in the water/larval tests. No bioaccumulation occurred in the larval and juvenile feeding tests, although similar tissue Cd levels were produced by both water and feeding exposures.The information in this document has been funded by the U.S. Environmental Protection Agency. It has been subjected to the Agency's peer and administrative review, and it has been approved for publication. Mention of trade names or commercial products does not constitute endorsement or recommendation for use.     

Bacteria and cadmium interactions in natural and laboratory model aquatic systems

Cadmium-resistant bacterial populations were examined in sediments of the Ottawa River, near Lima, Ohio, at a site that had elevated levels of Cd, Cr, Cu, Ni, Zn, and Fe. The percentage of the bacterial population that was resistant to cadmium was higher at the metal-contaminated site than at a less contaminated site downstream.Bacillus was the most abundant genus of the total river sediment population recovered andPseudomonas was the most abundant Cd-resistant genus recovered. Types and distribution of bacterial populations in 40 liter laboratory model aquatic systems were examined over a ten-week period during the continuous addition of 10 mg Cd⁺² per day. The Cd level in the water column rose rapidly through the first two weeks and reached a maximum of 3 g Cd/ ml. Sediment Cd levels rose most rapidly after 5 weeks and reached a concentration of 270 g Cd/g after 10 weeks. The bacteria in the water column responded to the Cd treatment with increased Cd resistance more quickly and to a greater degree than the bacteria in the sediment. The types of Cd-resistant bacteria isolated in the model systems were similar to Cd-resistant bacteria isolated from sediments of the Ottawa River.     

A suggestion on how to use measurements of cadmium in blood as a cumulative dose estimate

Summary The individual cumulative cadmium dose was estimated for 44 smelter workers in a cadmium-copper alloy plant. Two different principles were used: cumulative respiratory dose and cumulative average annual blood-cadmium dose. Out of eight workers with a cumulative respiratory dose exceeding 500 mg Cd · h/m³, two of them (25%) had signs of a cadmium-induced renal dysfunction. These two men were the only workers that had a cumulative average annual blood cadmium dose exceeding 200 g Cd · year/1. Our results suggest that measurements of cadmium in the blood can be used as an indicator of the cadmium exposure of each individual and that, in order to prevent renal dysfunction, the average blood-cadmium concentration should not exceed 10 Cd/1 over periods of many years (decades).     

Effect of waterborne and dietary cadmium on plasma ions of the teleostOreochromis mossambicus in relation to water calcium levels

The effects of cadmium administered via ambient water or food on plasma ions of the African freshwater cichlidOreochromis mossambicus were studied for 2, 4, 14, and 35 days, in low calcium (0.2 mM) and high calcium (0.8 mM) water. In low calcium water, an environmentally relevant concentration of 10 g/L water-borne cadmium induced a significant and dramatic hypocalcemia on days 2 and 4. Recovery of plasma calcium was observed on days 14 and 35. Hypermagnesemia was observed on day 2, but normal levels were already found on day 4. In high calcium water adapted fish, the extent of hypocalcemia and hypermagnesemia was less pronounced than in fish from low calcium water. Water-borne cadmium caused no significant changes in plasma phosphate, sodium, potassium, or osmolality. On days 2 and 4, dietary cadmium (averaging 10 g Cd/fish/day) caused hypermagnesemia and hypocalcemia in low calcium wateradapted fish. Recovery was observed on days 4 and 14, respectively. In fish from high calcium water, dietary cadmium caused a significant reduction in plasma calcium on day 4 only; plasma magnesium was unaffected. Hyperphosphatemia was apparent on day 14, irrespective of the water calcium concentration. No changes in plasma sodium, potassium, or osmolality were found.The results show that sublethal concentrations of cadmium, administered via the water as well as via the food, affect calcium and magnesium metabolism in tilapia. High water calcium ameliorates the effects of both water and dietary cadmium on plasma calcium and magnesium levels.Among the various heavy metal pollutants, cadmium is frequently present in natural water bodies as a result of discharges from industrial processes or other anthropogenic contamination. The harmful effects of cadmium on mammals and other terrestrial animals have been widely studied and reviewed (Flicket al. 1971; Vallee and Ulmer 1972; Webb 1979; Korte 1983; Foulkes 1986). Aquatic vertebrates such as fish, live in very intimate contact with the environment through their gills. This makes them very susceptible to aquatic pollutants.Since it is well established that freshwater fish take up most of the ions necessary for homeostasis from the water via the gills (Eddy 1982), cadmiuminduced plasma ionic disturbances are apparently caused by impaired uptake and diffusional losses of ions via these organs (Larssonet al. 1981; Giles 1984). Ionic disturbances have also been reported after exposure of fish to sublethal concentrations of heavy metals. For example, changes in the plasma ionic composition have been observed in fish exposed to copper and zinc (Lewis and Lewis 1971; Spry and Wood 1985), mercury (Locket al. 1981), and chromium (Van der Putteet al. 1983). With respect to cadmium, exposure of rainbow trout to sublethal levels induced hypocalcemia, with reduced plasma sodium, potassium, chloride and increased plasma magnesium (Giles 1984). In European flounder, cadmium-induced hypocalcemia and elevated levels of plasma phosphate, magnesium and potassium were observed (Larssonet al. 1981).In addition to water, food could also be a source of cadmium for fish, since it accumulates in aquatic organisms through trophic transfers (Anonymous 1971; Williams and Giesy 1978; Coombs 1979). Indeed, Bryan (1976) concluded that food as a source of Zn, Mn, Co, and Fe for molluscs, crustaceans and fish was more important than water. From various studies on both water-borne and food-containing metals, reviewed by Dallingeret al. (1987), there is evidence that uptake of heavy metals such as Cd, Cu, Co, Pb, Hg, and Zn from food is also the predominant pathway in freshwater fish. Koyama and Itazawa (1977) reported significant hypocalcemia and elevated plasma phosphate levels in cadmium-fed carps. Similarly, plaice and thornback ray both accumulated more cadmium from food than from seawater (Pentreath 1977). In general, cadmium concentrations in natural waters are extremely low and a more important route of cadmium uptake by fish may be represented via the gut. Experiments with dietary cadmium may therefore yield more representative information for field situations.In this investigation, we have compared the effects of a sublethal concentration of cadmium administered via the water or via the food in the African cichlid fishOreochromis mossambicus (tilapia). Plasma ions and osmolality were determined. Cadmium was administered at sublethal concentrations, in the order of magnitude that may occur in natural waters (10 g Cd/L). In many studies aimed at evaluating the effects of cadmium on fishes, high concentrations (>1 mg Cd/L) of cadmium have been used. Hence severe physiological, behavioral and detrimental effects have been reported. Such high concentrations are rarely found in nature, except in cases of spillage or heavily polluted waters. The Working Group on Cadmium Toxicity (EIFAC 1977) has suggested that chronic exposure to low cadmium concentrations is more relevant to understanding the mechanisms involved in the intoxication process in teleost fish.We further studied the influence of relatively low and high calcium concentration of the water on the toxic effects of cadmium. The effects of water hardness (mainly Ca²⁺ and Mg²⁺ ions) on heavy metal toxicity have been demonstrated in various species of teleosts (Pärtet al. 1985). Increased toxicity of cadmium to fish in soft water as compared to hard water has been demonstrated in catfish and guppies (Kinkade and Erdman 1975), goldfish (McCartyet al. 1978), striped bass (Palawskiet al. 1985), brook trout (Carrollet al. 1979) and rainbow trout (Calamariet al. 1980; Pascoet al. 1986). Similar observations on teleosts exposed to zinc, copper and lead (Sinleyet al. 1974; Zitko and Carson 1976; Judy and Davies 1979; Laurén and McDonald 1986) indicate a protective role of calcium against the toxic effects of heavy metals. It was also investigated whether the protective effect of the water-calcium concentration is limited to water-borne cadmium only, or also applies to dietary cadmium.     

Bioaccumulation and Toxicity of Dissolved Heavy Metals from the Guadalquivir Estuary After the Aznalcóllar Mining Spill Using Ruditapes philippinarum

The shore clam Ruditapes philippinarum was used as a biomonitoring organism to measure the potential impact that the mining spill in the Guadalquivir Estuary (SW, Spain) in 1998 may have exerted on local biota. Individuals were exposed to dissolved cadmium, copper, and zinc at concentrations found in local waters after the spill (3 g · L^–1 Cd, 15 g · L^–1 Cu, 700 g · L^–1 Zn) at two salinity values: 10 and 35. Residues of metals were measured in gill and digestive gland, together with metallothioneins in the digestive gland and histopathological lesions in gill, digestive gland, and gonad tissues over time. Heavy metals Zn and Cd associated with the mining spill, were bioaccumulated in clam tissues, associated with the activation of metallothioneins, and related to the histopathological lesions measured at all the clam tissues. The heavy metal Cu not related to the spill was not directly associated with effects measured. The bioaccumulation and adverse effects associated with Cd and Zn were significantly higher at low salinity (10) than at high salinity (35) values.