Cadmium removal by living cells of the marine microalga Tetraselmis suecica

Cadmium removal by living cells of the marine microalga Tetraselmis suecica was tested in cultures exposed to different cadmium concentrations (0.6, 3, 6, 15, 30 and 45 mg/l). The EC50 for growth was 7.9 mg Cd/l after six days of exposure. The cadmium removed was proportional to the concentration of this metal in the medium and it was dependent on the time of exposure; cultures with higher cadmium concentration removed a higher amount of this metal. In cultures exposed to 0.6 mg/l, T suecica cells removed 98.1% of added cadmium with 0.392 x 10(-6) microg Cd/cell, whereas in cultures with 45 mg/l only 7.7% was removed with 16.052 x 10(-6) microg Cd/cell. The highest amount of cadmium removed per liter of culture was observed in cultures exposed to 6 mg/l, with 3.577 mg/l of cadmium. After six days of incubation, the higher proportion of cadmium was bioaccumulated intracellularly in all cultures except in 45 mg/l cultures, the percentage of intracellular cadmium being always more than 50%. The highest percentage of bioadsorbed cadmium (60.1%) was found in cells of cultures with the highest cadmium concentration (45 mg/l). Furthermore, a relation between intracellular cadmium and the concentration of sulfhydryl groups was observed.     

Accumulation of cadmium by the fourth instar larva of the fly Chironomus thummi

Accumulation and effects of cadmium were investigated in Chironomus thummi larvae exposed to 10, 100 and 250 mug radiolabeled Cd/1 for up to 4 days. (1) After 4 days, average cadmium accumulation was 6.6 ng Cd/mg dry weight (10 mug Cd/1 exposure) and 177 ng Cd/mg dry weight (250 mug Cd/1 exposure). (2) Dissection studies showed that by 32 hr of exposure to both cadmium concentrations, 63.5-81.4% of accumulated cadmium was confined to the posterior midgut epithelium. Light microscope autoradiography similarly showed accumulations of cadmium in posterior midgut epithelium and smaller amounts in fat body and muscle. Little cadmium was associated with Malphigian tubules, haemocoel, anterior midgut or exoskeleton. (3) After exposure to 10 or 250 mug Cd/1, 60-75% of cadmium in ultracentrifuged homogenates of whole animals or dissected guts was associated with the resulting supernatant. When supernatants were further analyzed by gel chromatography, cadmium eluted with both a high and low molecular weight peak. The relative proportions of cadmium in the two peaks varied with concentration and length of exposure. (4) Transmission electron microscopy of posterior midgut cells from animals exposed to cadmium demonstrated frequent mitochondrial lesions. Exposure to high cadmium concentrations caused some posterior midgut cells to undergo generalized structural degeneration.     

Activities of superoxide dismutase and catalase in erythrocytes and plasma transaminases of goldfish (Carassius auratus gibelio Bloch.) exposed to cadmium

Four groups of goldfish were exposed to cadmium in a concentration of 20 mg Cd/l water under aquarium conditions. The duration of exposure was 1, 4, 7 and 15 days. It was shown that the activity of superoxide dismutase (SOD) in the red blood cells (RBC) significantly decreased after the first day of cadmium exposure. However, the SOD activity increased after 7 and 15 days of cadmium treatment. Elevated activity of catalase (CAT) was found in erythrocytes of cadmium-treated fishes after 15 days, whereas plasma GOT levels was increased after 7 and 15 days and GPT levels after 1, 4, 7 and 15 days of cadmium treatment. This was accompanied by a significant decrease of blood hemoglobin concentrations (after 15 days) and hematocrit values (after 7 and 15 days). However, the concentration of blood glucose significantly increased after 1, 4, 7 and 15 days of cadmium exposure. These results indicate that cadmium causes oxidative stress and tissue damage in the exposed fishes.     

Alterations in hepatic heme metabolism in fish exposed to sublethal cadmium levels

A study on hepatic heme metabolism with special emphasis to ALA synthetase, ALA dehydratase and heme oxygenase was carried out in cadmium exposed freshwater fish Channa punctatus to enlighten the mechanism of cadmium induced toxicity. Cadmium exposure (0.5-5.0 mg/1) for 7 days increased the hepatic level of ALA, along with the depletion in heme content, which are characteristic to chemical porphyria. The resultant enhancement in the activities of ALA synthetase and heme oxygenase were further shown to be dose dependent. ALA dehydratase activity on the other hand was enhanced only at higher exposure. Time course studies on the enzyme activities and heme content showed that ALA synthetase started to increase after 24 hrs., reached maximum at 7 days and came back nearly to normal level after 30 days of exposure. Simultaneously maximum depletion in heme level occurred on 7 days of exposure, tending to return to normal on 30 day. In addition, attempt has been made to correlate alterations in heme metabolism due to cadmium with the histopathological manifestations in liver.     

Sequential changes in hepatic polyamine, deoxyribonucleic acid, and cyclic adenosine 3',5'-monophosphate metabolism after subacute exposure to cadmium in rats.

Heavy metal treatment (2 X 1 mg/kg per day) for 3, 5, and 7 days resulted in progressive augmentation in the incorporation of [14C]thymidine into hepatic DNA. In contrast with the observed enhancement in DNA synthesis, cadmium exposure tended to produce a decrease in the activity of hepatic ornithine decarboxylase (EC 4.1.1.17) at 1, 3, or 5 days with the lowest (34% of control values) enzymic activity seen after 7 days. A similar reduction in the activity of S-adenosylmethionine decarboxylase (EC 4.1.1.50) was observed in livers of rats treated with cadmium for 1-7 days. Subacute exposure to cadmium significantly lowered the hepatic levels of spermidine and spermine whereas the endogenous concentrated of putrescine remained unaltered. In addition to the observed effects on the biosynthesis of polyamines and DNA, heavy metal treatment produced stimulation of the hepatic adenylate cyclase (EC 4.6.1.1)--cyclic AMP system. Significant increases in the activity of hepatic adenylate cyclase and endogenous cyclic AMP levels were detected as early as 1 day and the observed alterations persisted during the entire 1-week period of cadmium exposure. The depression in polyamine formation was accompanied by enhanced DNA biosynthesis as well as stimulation in the adenylate cyclase-cyclic AMP system of rat liver.     

Response of hepatic carbohydrate and cyclic AMP metabolism to cadmium treatment in rats.

Daily intraperitoneal injection of cadmium chloride (0.25 or 1 mg/kg) for 21 or 45 days into rats significantly stimulated the activities of hepatic pyruvate carboxylase, phosphoenolpyruvate carboxykinase, fructose-1, 6-diphosphatase, and glucose-6-phosphatase, increased the concentrations of glucose and urea in the blood, and decreased the levels of glycogen in the liver. Whereas chronic cadmium treatment failed to alter adenosine-3',5'-monophosphate phosphodiesterase (phosphodiesterase) activity, the endogenous levels of cyclic AMP (cAMP) and the activity of basal- and fluoride-stimulated forms of hepatic adenylate cyclase (AC) were markedly increased in cadmium-injected animals. Treatment with the higher dose (1.0 mg/kg) of cadmium chloride for 45 days produced greater metabolic alterations in hepatic tissue than those seen with the lower dose (0.25 mg/kg) given for a shorter period of time (21 days). Discontinuation of cadmium administration for 14 days in rats previously injected with cadmium chloride (1 mg/kg per day) for 21 days, failed to reverse the observed changes in hepatic cAMP or carbohydrate metabolism. A similar persistence of metabolic alterations was noted in rats treated with cadmium (1 mg/kg per day) for 45 days and subsequently maintained without additional treatment for 28 days. Administration of an acute dose of cadmium chloride (60 mg/kg) decreased hepatic phosphodiesterase activity and glycogen content 1 h after the injection. In addition, acute cadmium exposure increased blood glucose, serum urea, and hepatic cAMP levels, and produced an augmentation of basal- and fluoride-activated AC. However, the activities of various hepatic gluconeogenic enzymes remained unaffected in animals given an acute dose of cadmium chloride (60 mg/kg). Data provide evidence that suggests that the gluconeogenic potential of liver is markedly enhanced following chronic exposure to cadmium and that the cadmium-induced changes in carbohydrate metabolism may be associated with an enhanced synthesis of cAMP. In addition, the present study shows that the cadmium-induced metabolic alterations persist even after the cessation of cadmium treatment for a period of 28 days.     

Operant behavior in transition reflects neonatal exposure to cadmium

Male Long-Evans rats were injected with 0, 1, 3, or 6 mg/kg of cadmium chloride on the first day of life. Animals free of morphological stigmata at weaning were selected for study. Tissue concentrations of cadmium and operant behavior under various fixed-ratio (FR) schedules of reinforcement were evaluated when these rats were adults. Dose-related increases in cadmium were present in the brains, livers, and kidneys. Dose-related differences in behavior were most evident during the transition from fixed ratio 25 (FR 25 or 25 responses/reinforcer) to FR 75. An inverted U describes the relationship between response output during the transition to FR 75 and cadmium chloride dose response output increased at 3 mg/kg and decreased at 6 mg/kg. The rate decreases were not correlated with weight loss that appeared after some of the animals exposed to 6 mg/kg reached 60 days of age. Challenge doses of d-amphetamine revealed no interaction between neonatal exposure to cadmium and d-amphetamine. The occurrence of alterations in operant behavior in animals that appeared normal on a number of preweaning evaluations suggests that operant behavior in transition was sensitive to subtle effects not observed with other commonly used tests. The data provide evidence for delayed effects in the adult that are due to neonatal exposure to cadmium.     

Effect of exposure of pregnant rats to cadmium on prenatal and postnatal development of the young

Cadmium chloride in doses of 2, 12 and 40 mg Cd/kg was administered per os to pregnant rats from the 7th to 16th day of pregnancy. In another experiment female rats were exposed to cadmium oxide at a concentration of 0.02 mg Cd/m3 or 0.16 mg Cd/m3 for 5 hours a day and 5 days weekly for a period of 5 months or 1 mg Cd/m3 for 4 months. The exposure was then continued during mating and from the 1st to 20th day of pregnancy. A decrease in fertility was only observed in females exposed by inhalation to cadmium oxide at a concentration of 1 mg Cd/m3, at which concentration cadmium exhibits a considerable toxic effect on the whole organism. The young of females orally treated with CdCl2 in a dose of 40 mg Cd/kg displayed congenital defects in the form of sirenomelia or amelia, as well as raised cadmium levels in tissues. A retardation of intrauterine development manifested by lower body weight and slowed down osteogenesis was observed in the other groups. A cadmium concentration increase was not found in the tissues of the young in these groups. Inhalation exposure to 0.16 mg Cd/m3 of females prior to and during pregnancy induced in their young a decrease in viability, lower body weight gain, prolongation of latency in the negative-geotaxis test, lower locomotor activity and deteriorated development of the conditioned-reflex response. The offspring of females exposed to 0.02 mg Cd/m3 displayed lowered locomotor activity and worsened consolidation of the conditioned-reflex response.     

The effect of chronic exposure to cadmium and gamma radiation at low doses on the genetic structures in mice

The DNA-protein cross-links (DPC) in mouse thymocytes and spleen lymphocytes, the number of abnormal sperm heads (ASH) and the number of micronuclei (MN) in normochromatic erythrocytes (NCE) of peripheral blood were studied in mice exposed to long-term low-intensity gamma radiation (0.072 cGy/days) and/or cadmium with drinking water (0.01 mg Cd2+/l) for 20, 40 and 80 days. The dependence of DPC level on the total dose (exposure time) of gamma radiation and/or cadmium is nonlinear. The maximal level of DPC in cells of lymphoid organs upon exposure to gamma radiation or cadmium was recorded on the 40-th day, and under combined exposure on the 20-th day of the experiment. The long-term exposure to cadmium or gamma radiation causes an increase in the ASH frequency. The increase in frequencies of MN in NCE and reciprocal translocations in spermatocytes was not found.     

Effect of dietary calcium on cadmium absorption and retention in suckling rats

The effect of calcium supplementation on absorption and retention of cadmium in the suckling period was evaluated in Wistar rat pups of both sexes. Animals were maintained in the litters with the mother rats and supplemented with 1%, 3% or 6% calcium (as CaHPO₄×2H₂O) in cow's milk by artificial feeding from day of birth 6 through 14. All rats were exposed to cadmium (as CdCl₂×H₂O) either orally or parenterally. Oral cadmium dose of 0.5 mg/kg body weight a day was administered through nine-day period of calcium supplementation and parenteral cadmium dose was injected subcutaneously in a single dose of 0.5 mg Cd/kg body weight prior to calcium supplementation. On experimental day 10 (at the age of pups of 15 days) all animals were killed and the liver, kidneys, brain and carcass (body without organs and skin) were removed for element analyses. Cadmium and essential elements calcium, zinc and iron were analysed in the tissues by atomic absorption spectrometry. Results showed that after oral exposure cadmium concentrations in all calcium-supplemented groups were significantly decreased in the organs and carcass and that the effect was dose-related. No such effect of calcium was found after parenteral cadmium exposure. Calcium supplementation per se significantly increased calcium concentration in the carcass and had no effect on iron in organs and zinc in carcass. It was concluded that calcium supplementation during the suckling period could be an efficient way of reducing oral cadmium absorption and retention without affecting tissue essential trace element concentrations.     

Protective Effects of Lactobacillus plantarum CCFM8610 against Acute Cadmium Toxicity in Mice

This study evaluated the protective effects of Lactobacillus plantarum CCFM8610, a selected probiotic with good cadmium binding capacity, against acute cadmium toxicity in mice. Ninety mice were divided into prevention and therapy groups. In the prevention groups, CCFM8610 was administered at 10⁹ CFU once daily for 7 days, followed by a single oral dose of cadmium chloride at 1.8 mg cadmium for each mouse. In the therapy groups, the same dose of CCFM8610 was administered for 2 days after an identical single dose of cadmium exposure. Mice that received neither cadmium nor culture or that received cadmium alone served as negative and positive controls, respectively. The effects of both living and dead CCFM8610 on cadmium ion concentrations in feces, liver, and kidney were determined. Moreover, the alterations in reduced glutathione (GSH), malondialdehyde (MDA), superoxide dismutase (SOD), catalase (CAT), and histopathology in the liver and kidney were investigated. The results showed that compared to the mice that received cadmium only, CCFM8610 treatment can effectively decrease intestinal cadmium absorption, reduce tissue cadmium accumulation, alleviate renal and hepatic oxidative stress, and ameliorate hepatic histopathological changes. Living CCFM8610 administered after cadmium exposure offered the most significant protection. Our results suggested that CCFM8610 is more effective against acute cadmium toxicity than a simple antioxidant treatment due to its special physiological functions and that it can be considered a new dietary therapeutic strategy against acute cadmium toxicity.     

Interaction of benzo[a]pyrene, 2,3,3',4,4',5 hexachlorobiphenyl (PCB 156) and cadmium on biomarker responses in flounder (Platichthys flesus L.)

Interactive effects of a mixed pollutant exposure on biomarker responses were studied in European flounder (Platichthys flesus L.). The model chemicals, benzo[a]pyrene (BaP, 2.5 mg kg^-1), 2,3,3',4,4'5 hexachlorobiphenyl (PCB-156, 2.5 mg kg^-1), and cadmium (cadmium, 1 mg kg^-1), were administered to fish by subcutaneous injections. Biomarker responses were quantified both following administration of single chemicals and sequential combinations of the chemicals in pairs. Significant induction of CYP1A protein levels and corresponding ethoxyresorufin-O-deethylase (EROD) activities was observed in BaP and PCB treated flounder after 2 and 8 days, respectively. The strongest induction (44 fold) was caused by BaP. No further induction was observed after additional treatment with PCB 156. CYP1A induction caused by BaP was inhibited (40% compared with BaP treatment alone) in flounder pre treated with cadmium, whereas induction by PCB 156 appeared to be unaffected by pre treatment with cadmium. Flounder treated with cadmium only had significantly elevated hepatic levels of metallothionein (MT) after 15 days. Pre treatment with BaP and PCB prior to cadmium inhibited the MT induction (30-50%) compared with cadmium alone. Furthermore, significantly higher glutathione S transferase activities were observed in flounder administered cadmium alone, and in flounder treated with BaP or PCB 156 prior to cadmium. GST selenium independent peroxidase activities appeared to be unaffected by any of the treatments in the present study. The results indicate that chemical mixtures may affect biomarker responses differently from compounds administered alone, and that the sensitivity of both CYP1A and MT are influenced by pollutants other than their primary inducers.     

The effects of heavy metals on common carp white blood cells in vitro

The in vitro effects of cadmium, copper, lead and zinc, and various cadmium compounds (chloride, sulphate and nitrate) on common carp (Cyprinus carpio) lymphocyte viability and phagocyte activity, were evaluated. The percentage of dead lymphocytes was determined after Trypan blue staining, and phagocyte activity was measured by using the nitroblue tetrazolium (NBT) reduction test. Lead was the most toxic to lymphocytes--the maximum mortality exceeded 30%, and was significantly higher at 1 microM of lead, compared to the control. The maximum mortality caused by cadmium was below 10%, but was significantly elevated with 5 microM or more of cadmium. Zinc induced lymphocyte mortality from 10 microM, whilst no effect was observed with copper. The incubation of full blood with the three cadmium compounds (at 5mg/l of cadmium) showed that cadmium nitrate and cadmium sulphate were more toxic (over 35% and 25% mortality, respectively) than cadmium chloride (about 15% mortality). This was confirmed by the results of tests on isolated cells--1mg/l of cadmium as nitrate and sulphate increased lymphocyte mortality compared to the control and cadmium chloride. Phagocytic activity was less sensitive to heavy metals than was lymphocyte viability. It was significantly reduced following exposure to 50 microM and 100 microM cadmium, and 100 microM zinc, but no effects were observed with either lead or copper.     

Effects of chronic alternating cadmium exposure on the episodic secretion of prolactin in male rats.

Cadmium increases or decreases prolactin secretion depending on the dose and duration of the exposure to the metal. However, whether there are cadmium effects on the episodic prolactin secretion is less well known. This study was undertaken to address whether chronic alternating exposure to two different doses of cadmium affects the episodic pattern of prolactin and to what extent the effects of cadmium are age-dependent. Male rats were treated s.c. with cadmium chloride (0.5 or 1.0 mg/kg) from day 30 to 60, or from day 60 to 90 of age, with alteration of the doses every 4 days, starting with the smaller dose. Controls received vehicle every 4 days. The last dose of cadmium was given 48 h prior to the pulsatility study. Prolactin secretion in the 4 experimental groups studied was episodic and changed significantly after cadmium exposure. Cadmium administration from day 30 to 60 of life significantly decreased the mean half-life of prolactin. On the other hand, when administered from day 60 to 90 cadmium significantly decreased the mean as well as serum prolactin levels and the absolute amplitude of the prolactin pulses, their duration, the relative amplitude or the mean half-life of the hormone. The frequency of prolactin peaks was not changed by cadmium administration. The results indicate that low intermittent doses of cadmium chronically administered change the episodic secretion pattern of prolactin in rats. The effects of cadmium on prolactin secretion were age dependent.     

Uptake and distribution of cadmium in the egg of the teleost, Oryzias latipes

Eggs of Oryzius latipes in the blastula stage were exposed to M/100 artificial sea water which contained cadmium at the concentrations of 0.1, 1.0, 10.0, 20.0 or 50.0 mg 1⁻¹. The 96 h TL₅₀, value for cadmium was estimated to be 20 5 mg 1⁻¹. When the eggs were incubated for 24 h in the M/100 sea water with 10.0 mg Cd 1⁻¹ and then rinsed in glycine buffer solution (pH; 2.0), the cadmium content of the egg decreased markedly. Cadmium levels were determined in parts of the embryonic body, the chorion and the yolk sac. The most cadmium was detected in the chorion (94.6%). Prolonged cadmium exposure revealed that most of the cadmium was absorbed by the chorion and little was detected in the embryonic body and the yolk sac.     

Hyper-osmoregulatory capacity of the Chinese mitten crab (Eriocheir sinensis) exposed to cadmium; acclimation during chronic exposure

The aim of this study was to evaluate the effects of waterborne cadmium on hyper-osmoregulatory capacity of the Chinese mitten crab Eriocheir sinensis acclimated to freshwater. For this purpose, crabs were submitted to acute (0.5 mg Cd L(-1) for 1, 2 or 3 days), chronic (10 or 50 microg Cd L(-1) for 30 days) or chronic, immediately followed by acute, exposure. While no effect was observed after 1 or 2 days, hemolymph osmolality, Na(+) and Cl(-) concentrations were significantly reduced after 3 days of acute exposure. Under this latter condition, the respiratory anterior gill ultrastructure, Na(+)/K(+)-ATPase and cytochrome c oxidase activities were significantly impaired. In contrast, the osmoregulatory posterior gill was unaffected for all treatments. As a consequence, we suggest that the observed hyper-osmoregulatory capacity impairment is the result of increased dissipative flow of ions and/or water through anterior gills. In contrast to acute exposure, chronic exposure did not induce any observable effect. However, crabs submitted to a known deleterious acute condition (0.5 mg Cd L(-1) for 3 days) directly after chronic exposure to 50 microg Cd L(-1) for 30 days showed normal hyper-osmoregulatory capacity with no change in gill Na(+)/K(+)-ATPase activity, and only little disturbance of anterior gill ultrastructure. These results demonstrate that a chronic cadmium exposure can induce acclimation mechanisms related to osmoregulation in this euryhaline decapod crustacean.     

Interaction of benzo[a]pyrene, 2,3,3′,4,4′,5 hexachlorobiphenyl (PCB 156) and cadmium on biomarker responses in flounder (Platichthys flesus L.)

Interactive effects of a mixed pollutant exposure on biomarker responses were studied in European flounder (Platichthys flesus L.). The model chemicals, benzo[a]pyrene (BaP, 2.5 mg kg^-1), 2,3,3′,4,4′5 hexachlorobiphenyl (PCB-156, 2.5 mg kg^-1), and cadmium (cadmium, 1 mg kg^-1), were administered to fish by subcutaneous injections. Biomarker responses were quantified both following administration of single chemicals and sequential combinations of the chemicals in pairs. Significant induction of CYP1A protein levels and corresponding ethoxyresorufin-O-deethylase (EROD) activities was observed in BaP and PCB treated flounder after 2 and 8 days, respectively. The strongest induction (44 fold) was caused by BaP. No further induction was observed after additional treatment with PCB 156. CYP1A induction caused by BaP was inhibited (40% compared with BaP treatment alone) in flounder pre treated with cadmium, whereas induction by PCB 156 appeared to be unaffected by pre treatment with cadmium. Flounder treated with cadmium only had significantly elevated hepatic levels of metallothionein (MT) after 15 days. Pre treatment with BaP and PCB prior to cadmium inhibited the MT induction (30-50%) compared with cadmium alone. Furthermore, significantly higher glutathione S transferase activities were observed in flounder administered cadmium alone, and in flounder treated with BaP or PCB 156 prior to cadmium. GST selenium independent peroxidase activities appeared to be unaffected by any of the treatments in the present study. The results indicate that chemical mixtures may affect biomarker responses differently from compounds administered alone, and that the sensitivity of both CYP1A and MT are influenced by pollutants other than their primary inducers.     

镉胁迫后旱柳转录组变化分析

随着重金属镉(Cd)应用范围的扩大,由此引发的土壤镉污染问题日益严重。以具有植物恢复潜力的旱柳Salix matsudana作为研究对象,探究不同浓度的Cd (2.5 mg/L, 50 mg/L)胁迫后旱柳无性系1 d、7 d和30 d后基因表达与代谢通路的变化。转录组测序结果表明:共获得102 595个非冗余基因(Unigenes),相同浓度不同时间的差异基因总数为26 623个和32 154个;相同时间不同浓度的差异基因总数为8 550个、3 444个和11 428个。从中筛选得到与Cd胁迫响应密切相关的基因25个,其中金属硫蛋白、ABC转运蛋白、锌和锰转运蛋白等基因的表达不仅会随着Cd胁迫浓度变化而且同时受到胁迫时间的改变而发生改变;油菜素内酯合成通路的ROT3和黄酮类化合物合成通路的FLS、F3H均明显上调。此外Cd胁迫引起旱柳在代谢过程、细胞过程、膜、细胞器、细胞、细胞部分、催化活化和结合蛋白这8个方面发生改变,参与这些GO条目的差异表达基因数随着Cd浓度和胁迫时间的增加而增加。并对转录组信息的可靠性用RT-PCR和酶活性生理实验数据进行了验证。文中通过转录组测序分析旱柳Cd胁迫后的响应机制,从而为旱柳修复土壤Cd污染提供理论指导。     

Proteasome and antioxidant responses in Cottus gobio during a combined exposure to heat stress and cadmium

Temperature and trace metals are common environmental stressors, and their importance is increasing due to global climate change and anthropogenic pollution. Oxidative damage and antioxidant properties have been studied in liver and gills of the European bullhead (Cottus gobio) subjected to cadmium (CdCl(2) at nominal concentrations of 0.01 and 1mg/L) for 4 days at either 15°C or 21°C. First, exposure to 1mg Cd/L induced a high mortality rate (67%) in fish held at 21°C. Regarding the antioxidant enzymes, exposure to 0.01 mg Cd/L significantly increased the activity of superoxide dismutase (SOD) and decreased the activity of glutathione reductase (GR) in liver, independently of heat stress. In gills, exposure to 21°C resulted in a significantly increased activity of glutathione peroxidase (GPx), whereas the activity of glutathione S-transferase (GST) was significantly reduced as compared to fish exposed to 15°C. Furthermore, regardless of Cd stress, exposure to elevated temperature resulted in a significant decrease of lipid peroxidation (LPO) level in liver and in a significant increase in the activity of chymotrypsin-like 20S proteasome in both studied tissues of C. gobio. Overall, the present results indicated that elevated temperature and cadmium exposure independently influenced the antioxidant defense system in bullhead with clear tissue-specific and stress-specific antioxidant responses. Further, elevated temperature affected the hepatic lipid peroxidation and the activity of 20S proteasome in both tissues.     

Cadmium Removal by Lemna minor and Spirodela polyrhiza

The present study investigates the ability of two genus of duckweed (Lemna minor and Spirodela polyrhiza) to phytoremediate cadmium from aqueous solution. Duckweed was exposed to six different cadmium concentrations, such as, 0.5, 1.0, 1.5, 2.0, 2.5, and 3.0 mg/L and the experiment was continued for 22 days. Water samples were collected periodically for estimation of residual cadmium content in aqueous solution. At the end of treatment period plant samples were collected and accumulated cadmium content was measured. Cadmium toxicity was observed through relative growth factor and changes in chlorophyll content. Experimental results showed that Lemna minor and Spirodela polyrhiza were capable of removing 42–78% and 52–75% cadmium from media depending upon initial cadmium concentrations. Cadmium was removed following pseudo second order kinetic model. Maximum cadmium accumulation in Lemna minor was 4734.56 mg/kg at 2 mg/L initial cadmium concentration and 7711.00 mg/kg in Spirodela polyrhiza at 3 mg/L initial cadmium concentration at the end of treatment period. Conversely in both cases maximum bio-concentration factor obtained at lowest initial cadmium concentrations, i.e., 0.5 mg/L, were 3295.61 and 4752.00 for Lemna minor and Spirodela polyrhiza respectively. The present study revealed that both Lemna minor and Spirodela polyrhiza was potential cadmium accumulator.