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PubMed1982

[Arsenic emission and effects on the biosphere].

In the GDR, the arsenic emission in the surroundings of metallurgical plants have been reduced to a minimum, the contamination of the soil being not yet diminished in some cases. In the framework of a comprehensive research program, it was shown that the uptake of arsenic by man via the food chain is possible in the area of activity of an arsenic emitter (due to increased arsenic content in the sedimentary dust), even if the maximum emission concentration of arsenic in the aerosol is considerably lower than the permanent limit value. Apart from local sources of emission (e.g. non-ferrous smelteries and phosphate works), the extended burden on the air by traces of arsenic originating from power station exhalates deserves increasing attention. In regions where industrial plants are concentrated, but also in regions with intensive agriculture and horticulture, it is recommendable to determine regularly the arsenic contents in the air, soil, vegetable feeding stuffs and vegetable foodstuffs.

Air Pollutants↗
PubMedDate not supplied

Effect of Centella asiatica on arsenic induced oxidative stress and metal distribution in rats.

Concomitant oral supplementation of Centella asiatica (100, 200 or 300 mg kg(-1), orally once daily) during arsenic exposure (20 ppm in drinking water for 4 weeks) was investigated in rats for its protective value. The animals exposed to arsenic (III) showed a significant inhibition of delta-aminolevulinic acid dehydratase (ALAD) activity, a marginal decrease in glutathione (GSH) and an increase in zinc protoporphyrin (ZPP) level in blood. Hepatic and renal glutathione (GSH) decreased, while oxidized glutathione (GSSG) and thiobarbituric acid reactive substance (TBARS) levels increased significantly in the liver, kidney and brain. The activities of brain superoxide dismutase (SOD) and catalase decreased marginally on arsenic exposure. Concomitant administration of Centella asiatica showed a significant protective action on inhibited blood ALAD activity and restored the blood GSH level, whereas most of the other blood biochemical parameters remained unchanged on Centella asiatica supplementation. Interestingly, most of the hepatic biochemical variables indicative of oxidative stress showed protection. There was, however, a significant protection observed in the altered kidney GSSG level and hepatic and brain TBARS. Only a marginal beneficial effect of Centella asiatica on blood and liver arsenic concentration was noted, particularly at the highest dose studies (300 mg kg(-1)). No effect of Centella asiatica on most of the altered renal biochemical parameters was noted. The results thus lead to the conclusion that simultaneous supplementation of Centella asiatica significantly protects against arsenic-induced oxidative stress but does not influence the arsenic concentration in these organs. It can thus be suggested that co-administration of Centella asiatica protects animals from arsenic-induced oxidative stress but exhibits no chelating property. Further studies are recommended for determining the effect of co-administration of Centella asiatica during chelation therapy with a thiol chelator.

Animals↗
PubMed2002

Fetotoxicity caused by the interaction between zinc and arsenic in mice.

Arsenic is an environmental pollutant that induces congenital malformations in experimental models and can contribute to human birth defects. The environmental exposure to arsenic is relatively small when compared with the doses required to cause teratogenicity in mice and other laboratory animals. In order to study the action of zinc in the arsenic-induced teratogenicity, in the present work mice were either pretreated with zinc and later with arsenic or were treated simultaneously with zinc and arsenic in vivo and in vitro. Following administration of arsenate on gestation day 8, pregnant females were killed on the 17th day of gestation; maternal and fetal data were collected by laparotomy and used to calculate reproductive parameters. Fetuses were analyzed for the presence of external malformation and, after the appropriate processing, visceral and skeletal analyses were accomplished. Conceptuses were exposed in whole embryo culture to arsenicals on gestation day 8 (3-6 somite stage). After a 26 h culture period, morphological development was assessed. Neither pretreatment with zinc nor simultaneous administration of zinc prevented arsenic teratogenicity in these experimental models.

Abnormalities, Drug-Induced↗
PubMed1998

Using ecological data to estimate a regression model for individual data: the association between arsenic in drinking water and incidence of skin cancer.

In ecologic studies, participants are studied by groups, and the exposure status of each group is usually represented by a single indicator, mostly the mean exposure. In this paper, we propose using multiple variables derived from dummy variables at the individual level to describe the exposure. An analysis of the association between arsenic in drinking water and skin cancer was used as an example. Well water arsenic levels and skin cancer incidence from 1980 to 1987 were assessed for 243 townships in Taiwan. We first analyzed the data using the mean arsenic concentration in each township as the only exposure variable. The second analysis used multiple variables to describe arsenic exposure; each variable denoted the percentage of wells with arsenic levels within a specific range in each township. Although the first approach did not identify associations between arsenic levels and skin cancer, the multiple-variable approach identifies a positive association at the highest arsenic exposure category (>0.64 mg/L) in both men and women. Therefore, using multiple variables to describe an exposure in ecologic studies may facilitate a better description of the exposure status and thereby lead to more accurate risk assessment, especially when the dose-response relationship is not linear.

Arsenic↗
PubMed2001

Effects on levels of glutathione and some related enzymes in tissues after an acute arsenic exposure in rats and their relationship to dietary protein deficiency.

Arsenic is a potent toxin, carcinogen and modulator of antioxidant defense system. In this study, male rats of Wistar strain, maintained on either 18% or 6% protein (casein) diet, received an acute i.p. exposure to sodium arsenite (As3+) at its LD50 dose (15.86 mg/kg body weight). One hour after the arsenic exposure, glutathione (GSH) concentration was significantly depleted and lipid peroxidation was increased. A relationship between any two of tissue arsenic concentrations, GSH levels and lipid peroxidation values was observed only for liver when the proportional changes of respective parameters in either of the dietary groups of animals were compared. This suggests that, in liver, arsenic metabolism appears dependant upon the GSH concentration. Acute arsenic exposure significantly increased the glutathione peroxidase (GPx) activity in liver of both dietary groups and in kidney of only the 18% protein-fed group of animals. The glutathione-S-transferase (GST) activity significantly decreased in liver of the 18% protein-fed animals while GST increased in kidney of both the 18% and the 6% protein-fed groups. No significant change in glutathione reductase (GR) or glucose-6-phosphate dehydrogenase (G6PDH) activity was observed. In the present investigation, liver as a whole seems to be more affected in terms of GSH level and GST activity. The mode of responses of GPx and GR activities as well as the unaltered G6PDH activity might result in arsenic-induced GSH depletion and increase in lipid peroxidation. The animals of the 6% protein-fed group, appeared to be affected less in terms of tissue arsenic concentration, GSH level and GST activity. lipid peroxidation,

Acute Disease↗
PubMed2004

Determination of inorganic arsenic in white fish using microwave-assisted alkaline alcoholic sample dissolution and HPLC-ICP-MS.

An analytical method for the determination of inorganic arsenic in fish samples using HPLC-ICP-MS has been developed. The fresh homogenised sample was subjected to microwave-assisted dissolution by sodium hydroxide in ethanol, which dissolved the sample and quantitatively oxidised arsenite (As(III)) to arsenate (As(V)). This allowed for the determination of inorganic arsenic as a single species, i.e. As(V), by anion-exchange HPLC-ICP-MS. The completeness of the oxidation was verified by recovery of As(V) which was added to the samples as As(III) prior to the dissolution procedure. The full recovery of As(V) at 104 +/- 7% (n = 5) indicated good analytical accuracy. The uncertified inorganic arsenic content in the certified reference material TORT-2 was 0.186 +/- 0.014 ng g(-1) (n = 6). The method was employed for the determination of total arsenic and inorganic arsenic in 60 fish samples including salmon from fresh and saline waters and in plaice. The majority of the results for inorganic arsenic were lower than the LOD of 3 ng g(-1), which corresponded to less than one per thousand of the total arsenic content in the fish samples. For mackerel, however, the recovery of As(III) was incomplete and the method was not suited for this fat-rich fish.

Alcohols↗
PubMed2005

Comparison of mild extraction procedures for determination of plant-available arsenic compounds in soil.

In this work three mild extraction agents for determination of plant-available fractions of elements in soil were evaluated for arsenic speciation in soil samples. Pepper (Capsicum annum, L.) var. California Wonder was cultivated in pots, and aqueous solutions of arsenite, arsenate, methylarsonic acid, and dimethylarsinic acid, at a concentration of 15 mg As kg(-1) soil, were added at the beginning of the experiment. Control pots (untreated) were also included. Deionized water, 0.01 mol L(-1) CaCl2, and 0.05 mol L(-1) (NH4)2SO4 were used to extract the plant-available fraction of the arsenic compounds in soil samples collected during the vegetation period of the plants. Whereas in control samples the extractable arsenic fraction did not exceed 1% of total arsenic content, soil amendment by arsenic compounds resulted in extraction of larger amounts, which varied between 1.4 and 8.1% of total arsenic content, depending on soil treatment and on the extracting agent applied. Among arsenic compounds determined by HPLC-ICPMS arsenate was predominant, followed by small amounts of arsenite, methylarsonic acid, and dimethylarsinic acid, depending on the individual soil treatment. In all the experiments in which methylarsonic acid was added to the soil methylarsonous acid was detected in the extracts, suggesting that the soil bacteria are capable of reducing methylarsonic acid before a further methylation occurs. No significant differences were observed between analytical data obtained by using different extraction procedures.

Arsenic↗
PubMed2000

Normal values for arsenic and selenium concentrations in human lung tissue.

Normal values and ranges were determined for arsenic and selenium concentrations in lung and hilus tissue. The study group consisted of 50 deceased persons, who were examined by autopsy at the Institute for Pathology of the University of Erlangen-Nuremberg. Taking into consideration topographic-anatomical criteria, samples were taken of each lung lobe and the hilar lymph nodes. The dried tissue was analyzed using by means of hydride atomic absorption spectrometry after wet-oxidative digestion. Normal values ranged for the arsenic concentrations from <1-74 ng/g dry weight and for the selenium concentrations from <3-574 ng/g dry weight. Arsenic was found to accumulate in the hilus tissue, whereas selenium did not. Considerable intraindividual and interindividual variation was found for both arsenic and selenium. There were no statistically significant differences regarding age, smoking habits, and lung diseases. Lung tissue samples from three deceased persons from Houston, Texas, contained lower arsenic concentrations and somewhat higher levels of selenium compared to the German autopsies; these levels were, however, still within the indicated normal ranges. The following conclusions can be drawn from the results available at present: Intraindividual and interindividual variation is high for the arsenic and selenium concentrations in human lung tissue, so that only relatively wide normal ranges can be given for the general population. Smoking habits, age, and lung diseases do not seem to affect the indicated normal ranges. Postmortem determination of arsenic and selenium concentrations in human lung tissue can provide important information on former occupational or environmental exposure.

Adult↗
PubMed2005

Effects of arsenic on zebrafish innate immune system.

The innate immune response, the first line of defense against invading pathogens, can be perturbed by environmental toxicants such as arsenic. This study reports the effects of arsenic on innate immunity of zebrafish. Respiratory burst activity, messenger RNA expression of tumor necrosis factor alpha (TNF-alpha), a primer of the respiratory burst response, and mRNA expression of the antiviral cytokines interferon (IFN) and MX, : before and after viral infection, were examined in arsenic-exposed zebrafish larvae. Respiratory burst activity and TNF-alpha expression were decreased upon arsenic exposure, indicating inhibition of TNF-alpha priming of the respiratory burst response. Arsenic enhanced IFN expression slightly over time, but reduced MX : expression. In zebrafish infected with snakehead rhabdovirus, arsenic decreased induction and altered the kinetics of IFN and MX : upon infection. Differences in IFN and MX : expression in arsenic-exposed larvae point toward an interruption of the Janus kinase-signal transducer and activator of transcription (JAK/STAT) pathway.

Animals↗
PubMed2005

Arsenic speciation analysis in water samples: a review of the hyphenated techniques.

Interests in the determination of different arsenic species in natural waters is caused by the fact that toxic effects of arsenic are connected with its chemical forms and oxidation states. In determinations of water samples inorganic arsenate (As(III), As(V)), methylated metabolities (MMAA, DMAA) and other organic forms such as AsB, AsC, arsenosugars or arsenic containing lipids have the most importance. This article provides information about occurrence of the dominant arsenic forms in various water environments. The main factors controlling arsenic speciation in water are described. The quantification of species is difficult because the concentrations of different forms in water samples are relatively low compared to the detection limits of the available analytical techniques. Several hyphenated methods used in arsenic speciation analysis are described. Specific advantages and disadvantages of methods can define their application for a particular sample analysis. Insufficient selectivity and sensitivity of arsenic speciation methods cause searching for a new or modifications already existing techniques. Some aspects of improvement and modifications of the methods are highlighted.

Arsenates↗
PubMed2006

Arsenic and other metal contamination of groundwaters in the industrial area of Thessaloniki, Northern Greece.

In groundwater, used for drinking water supply in the greater industrial area of Thessaloniki, in Northern Greece, concentrations of total arsenic exceeded the WHO provisional guideline value and the EU maximum contaminant level (MCL) of 10 microg/L. The concentration of total arsenic was in the range between 4-130 microg/L, whereas the median value was 36 microg/L and the average concentration 46 microg/L. Nine out of the eleven wells contained total arsenic at concentration higher than 10 microg/L and it should be stressed that 6 of them contain arsenic at concentrations between 10 (new MCL) and 50 microg/L (previous MCL). The examined groundwaters were found to contain elevated concentrations of manganese and phosphate. Arsenic had a positive correlation with the pH, indicating the possible effect of pH on arsenic mobilisation. These findings emerge the problem of contamination from arsenic, since, according to the EU directive 98/83, all drinking water sources within the European Union should have achieved compliance with the new limits by 12/2003, implying that the situation requires urgent remedial action.

Arsenic↗
PubMed1991

Inhibition of muscarinic cholinergic receptors by disulfide reducing agents and arsenicals. Differential effect on locust and rat.

Muscarinic receptors are altered by sulfhydryl reagents. Arsenic compounds, which have been used as insecticides, exert their toxic effects by combining with sulfhydryl groups. We compared the action of arsenicals and other sulfhydryl reagents on the muscarinic receptor from invertebrate and vertebrate species (locust and rat). Disulfide-reducing reagents dithiothreitol (DTT) and British Anti-Lewisite (BAL), but not arsenicals, inhibited [3H]quinuclidinyl benzilate ([3H]QNB) binding. However, after disulfide reduction, arsenicals caused a further inhibition of muscarinic binding. The effect of DTT + arsenicals was largely irreversible. The locust receptors were more sensitive to the action of both disulfide reagents either in the absence or presence of arsenicals than the rat receptors. The sulfhydryl reagent p-chloromercuric benzoate (PCMB) was more effective at inhibiting the locust receptors than the rat receptors, but addition of arsenicals did not cause further inhibition in either the locust or rat receptors. In locust, DTT + cacodylate and DTT + arsenite caused a reduction in the number of sites without modifying the affinity of [3H]QNB binding. In rat, DTT + arsenite caused a decrease in the affinity, while DTT + cacodylate caused a decrease in the affinity of [3H]QNB binding and its number of sites. Competition experiments after DTT + cacodylate showed that the IC50 and the Hill coefficient (nH) remained unchanged in the locust. In the rat, the IC50 for atropine was increased without alteration in the nH, and both parameters were increased for carbachol. These results are explained assuming that the binding site of the locust receptor has a disulfide group similar to that of the mammalian receptor, but that the hydrophobic interactions within the binding site are weaker in the locust receptor. The higher sensitivity of the insect receptor to sulfhydryl reagents could be of interest for developing methods of pest control.

Animals↗
PubMedDate not supplied

Effect of arsenicals on biliary excretion of endogenous glutathione and xenobiotics with glutathione-dependent hepatobiliary transport.

Sodium arsenite (25-100 mumol/kg, i.v.) and arsenate (75-300 mumol/kg, i.v.) injected into anaesthetized rats increased the biliary excretion of endogenous non-protein thiols (NPSH) in a dose-dependent fashion up to 24- and 31-fold, respectively. Simultaneously with NPSH, glutathione (GS) excretion was increased to a similar extent suggesting that the increment in biliary thiol output originated from enhanced hepatobiliary transport of GS. After administration of labelled arsenicals, biliary excretion of 74As and NPSH followed similar time-courses. Biliary excretion of 74As was more efficient after arsenite than arsenate administration corresponding to the greater potency of arsenite compared to arsenate to increase biliary output of NPSH. Coadministered sulfobromophthalein (BSP) inhibited the biliary excretion of 74As and prevented the arsenical-induced increase in biliary NPSH. Thus, hepatobiliary transport of arsenic apparently proceeds coordinately with that of GS. However, excretion of each molecule of arsenic compound generates transport of several molecules of GS. Though mercuric, methylmercuric, cadmium and zinc ions are thought to be excreted into bile as complexes with GS, the marked arsenical-induced increase in GS excretion only doubled the biliary excretion of inorganic mercury and hardly influenced the transport of other metals into bile. This finding suggests that arsenicals markedly enhance biliary excretion of GS with a free thiol group but barely or not at all that of GS with a thiol group blocked by a firmly bound metal ion. Both arsenicals diminished the biliary excretion of BSP-glutathione conjugate after BSP administration presumably because they impaired conjugation of BSP with GSH due to decreased GS availability. It is assumed that arsenite, and arsenate after reduction to arsenite, forms an unstable complex with GS that is efficiently transported into bile resulting in increased biliary output of GS. It is demonstrated that arsenite-induced perturbation of hepatobiliary disposition of endogenous GS differentially affects biliary excretion of xenobiotics with GS-dependent hepatobiliary transport.

Animals↗
PubMed1986

Concentrations of arsenic in urine of the general population in Sweden.

The concentration of the sum of the metabolites of inorganic arsenic (inorganic arsenic, methylarsonic acid and dimethylarsinic acid) as well as the concentration of organic arsenic compounds, mainly in the form of arsenobetaine, in the urine of human subjects from two cities in Sweden have been studied. The median concentration of metabolites of inorganic arsenic was approximately 8 micrograms As/g creatinine, independent of place of residence, sex, smoking and consumption of beer and wine. However, subjects who frequently ate flatfish and crustacea had somewhat higher (1.5 times) concentrations than those who very seldom ate such food. Flatfish, mainly in the form of plaice, and crustacea were found to be the main source of organic arsenic compounds. Subjects eating this type of seafood more than once a week had approximately 40 micrograms organic As/g creatinine (median value), compared with about 12 micrograms organic As/g creatinine in subjects who very seldom ate it. Other types of seafish or freshwater fish did not give rise to elevated concentrations of arsenic in the urine. The total range of organic arsenic compounds in urine was less than 1 to 525 micrograms As/g creatinine.

Adult↗
PubMed2006

Long-term exposure to arsenic affects head kidney and impairs humoral immune responses of Clarias batrachus.

The present study was aimed at determining the effects of long-term arsenic exposure on the head kidney (HK) and ensuing humoral immune responses in Clarias batrachus L. Long-term exposure (150 days) to non-lethal concentrations of arsenic (42.42 microM) resulted in significant time-dependent alterations in HK cell number eventually affecting the HK somatic index. Prolonged exposure to arsenic also suppressed HK-B cell proliferation and led to significant reduction in serum immunoglobulin levels and antigen-specific serum bacterial agglutinin titers. A decline in the number of antigen-specific plaque-forming cells with duration of arsenic exposure was noted in the HK. Enzyme linked immunosorbent assays further revealed that arsenic exposure inhibited the release of "IL-4 like factors" from HK-T cells. Histological studies documented time-dependent changes in the structure and cellular composition of HK characterized by extensive lymphocytopenia, decrease in melano-macrophage population and hemosiderin accumulation. From exposure-challenge studies with Aeromonas hydrophila it was evident that pathogens could efficiently disseminate and colonize distant host tissues in the exposed fish. Moreover, the ability to decrease the pathogen load was also significantly reduced in the arsenic-exposed fish. Thus long-term exposure to non-lethal concentrations of arsenic affects HK and interferes with the humoral immune system of C. batrachus rendering them immunocompromised and susceptible to pathogenic challenge.

Aeromonas hydrophila↗
PubMed2004

Enhanced solubilization of arsenic and 2,3,4,6 tetrachlorophenol from soils by a cyclodextrin derivative.

The application of extracting aqueous solutions with cyclodextrins in several soil remediation technologies has been increasingly studied but little is known about their removal capacities toward the inorganic species. Herein, the effectiveness of cyclodextrins (CDs) in extracting arsenic, copper, and iron from a mining soil is presented. In a preliminary test of four types of CD aqueous solutions, only the addition of carboxylmethyl-beta-cyclodextrin CMCD (a cyclodextrin derivative) led to a significant enhancement in arsenic removal. An increase in the concentration of copper and iron in the leachates was also observed with CMCD. Kinetic study of arsenic release was carried out at two temperatures (20 and 35 degrees C). The arsenic concentration in the leachates increases with increasing cyclodextrin concentration. At an 80 mM CMCD concentration, arsenic, copper, and iron released in filtrates were about 20-, 1,000-, and 4,000-fold greater, respectively, than that obtained using deionized water. In the soil system, the CMCD capacity removal was found to be higher for cations than for arsenic. Because the tetrachlorophenol can co-occur with arsenic and copper in several contaminated sites, its solubilization by CMCD was also investigated. Extraction experiments were performed to extract 2,3,4,6 tetrachlorophenol (TeCP) in spiked soil with CMCD. The results of batch experiments have shown that CMCD could significantly increase the TeCP extraction from soil. CD sorption on soils as quantified by a fluorescence technique was low, indicating no significant loss of CD during the leaching experiments. The use of CMCD as a flushing agent to enhance the removal of both inorganic and organic pollutants from mixed-contaminated soils appears as a promising remediation method.

Arsenic↗
PubMed2005

Determination of total arsenic content in water by atomic absorption spectroscopy (AAS) using vapour generation assembly (VGA).

Analysis of arsenic in water is important in view of contamination of ground water with arsenic in some parts of the world including West Bengal in India and neighboring country Bangladesh. WHO has fixed the threshold for arsenic in drinking water to 10ppb (microg/l) level, hence the methodology for determination of arsenic is required to be sensitive at ppb level. Atomic absorption spectrophotometry with vapour generation assembly (AAS-VGA) is well known technique for the trace analysis of arsenic. However, total arsenic analysis [As(III)+As(V)] is very crucial and it requires reduction of As(V) to As(III) for correct analysis. As(III) is reduced to AsH3 vapours and finally to free As atoms, which are responsible for absorption signal in AAS. To accomplish this the vapour generation assembly attached to AAS has acid channel filled with 10 M HCl and the reduction channel with sodium borohydride. Further sample can be reduced either before aspiration for analysis, using potassium iodide (KI) or the sample can be introduced in the instrument directly and KI can be added in the reduction channel along with the sodium borohydride. The present work shows that samples prepared in 3 M HCl can be reduced with KI for 30 min before introduction in the instrument. Alternatively samples can be prepared in 6 M HCl and directly aspirated in AAS using KI in VGA reduction channel. The latter methodology is more useful when the sample size is large and time cycle is difficult to maintain. It is observed that the acid concentration of the sample in both the situations plays an important role. Further reduction in acid concentration and analysis time is achieved for the arsenic analysis by using modified method. Analysis in both the methods is sensitive at ppb level.

Arsenic↗
PubMed2006

The potential for kelp manufacture to lead to arsenic pollution of remote Scottish islands.

Burning seaweed to produce kelp, valued for its high potash and soda content, was formerly a significant industry in remote coastal areas of Scotland and elsewhere. Given the high concentrations of arsenic in seaweeds, up to 100 mg kg(-1), this study investigates the possibility that the kelp industry caused arsenic contamination of these pristine environments. A series of laboratory-scale seaweed burning experiments was conducted, and analysis of the products using HPLC ICP-MS shows that at least 40% of the arsenic originally in the seaweed could have been released into the fumes. The hypothesis that the burning process transforms arsenic from low toxicity arsenosugars in the original seaweeds (Fucus vesiculosus and Laminaria digitata) to highly toxic inorganic forms, predominantly arsenate, is consistent with As speciation analysis results. A field study conducted on Westray, Orkney, once a major centre for kelp production, shows that elevated arsenic levels (10.7+/-3.0 mg kg(-1), compared to background levels of 1.7+/-0.2 mg kg(-1)) persist in soils in the immediate vicinity of the kelp burning pits. A model combining results from the burning experiments with data from historical records demonstrates the potential for arsenic deposition of 47 g ha(-1) year(-1) on land adjacent to the main kelp burning location on Westray, and for arsenic concentrations exceeding current UK soil guideline values during the 50 year period of peak kelp production.

Animals↗