Arsenic transport by zebrafish aquaglyceroporins

Background  

Arsenic is one of the most ubiquitous toxins and endangers the health of tens of millions of humans worldwide. It is a mainly a water-borne contaminant. Inorganic trivalent arsenic (As^III) is one of the major species that exists environmentally. The transport of As^III has been studied in microbes, plants and mammals. Members of the aquaglyceroporin family have been shown to actively conduct As^III and its organic metabolite, monomethylarsenite (MAs^III). However, the transport of As^III and MAs^III in in any fish species has not been characterized.     

Exceptions in patterns of arsenic compounds in urine of acute promyelocytic leukaemia patients treated with As<Subscript>2</Subscript>O<Subscript>3</Subscript>

Arsenic trioxide (As(III) in solution) has been shown to be the most active single agent in combating acute promyelocytic leukemia (APL). It is metabolized and excreted via urine as monomethylarsonic acid (MMA), dimethylarsinic acid (DMA) and As(V), along with excess As(III). In our study eight APL patients were treated (intravenously) with 0.15 mg As₂O₃/kg/day. During the therapy As(III) and its metabolites were followed in pre- and post-infusion urine using HPLC for separation followed by on-line detection using hydride generation-atomic fluorescence spectrometry. Five patients had a normal excretion pattern of residual arsenic compounds in morning pre-infusion urine, with 15–25 % of As(III), 35–55 % of DMA, 25–30 % of MMA and 1–5 % of As(V), while three patients showed unexpected exceptions from typical excretion patterns of arsenic compounds (i) a high DMA/MMA ratio (factor 5.3), (ii) severe As(III) oxidation (10.2 % As(III) converted to As(V)) or (iii) the presence of an excessive amount of As(III) (average 30.4 % of total arsenic). Intriguing was the occurrence of post-infusion oxidation of As(III) to As(V) observed in almost all patients and being especially high (>40 %) in patient with increased residual As(V). Results indicate that arsenic metabolites patterns can be unpredictable. Observed high levels of un-metabolised As(III) are a warning signal for side effects and for routine determination of arsenic metabolites during first days of treatment. High or low percentages of MMA or DMA did not show any observable effect on treatment results, while clear presence of post-infusion As(V) supports theoretical claims of in vivo oxidation (detoxification) of As(III) to As(V) associated with various metabolic processes.     

Organic matter diagenesis at the oxic/anoxic interface in coastal marine sediments,with emphasis on the role of burrowing animals

The present paper reviews the current knowledge on diagenetic carbon transformations at the oxic/anoxic interface in coastal marine sediments. Oxygen microelectrodes have revealed that most coastal sediments are covered only by a thin oxic surface layer. The penetration depth of oxygen into sediments is controlled by the balance between downward transport and consumption processes. Consumption of oxygen is directly or indirectly caused by respiration of benthic organisms. Aerobic organisms have the enzymatic capacity for complete oxidation of organic carbon. Anaerobic decay occurs stepwise, involving several types of bacteria. Large organic molecules are first fermented into small moieties. These are then oxidized completely by anaerobic respirers using a sequence of electron acceptors: Mn⁴⁺, NO₃ ^-, Fe³⁺, SO₄ ^2- and CO₂. The quantitative role of each electron acceptor depends on the sediment type and water depth. Since most of the sediment oxygen uptake is due to reoxidation of reduced metabolites, aerobic respiration is of limited importance. It has been suggested that sediments contain three major organic fractions: (1) fresh material that is oxidized regardless of oxygen conditions; (2) oxygen sensitive material that is only degraded in the presence of oxygen; and (3) totally refractory organic matter. Processes occurring at the oxic/anoxic boundaries are controlled by a number of factors. The most important are: (1) temperature, (2) organic supply, (3) light, (4) water currents, and (5) bioturbation. The role of bioturbation is important because the infauna creates a three-dimensional mosaic of oxic/anoxic interfaces in sediments. The volume of oxic burrow walls may be several times the volume of oxic surface sediment. The infauna increases the capacity, but not the overall organic matter decay in sediments, thus decreasing the pool of reactive organic matter. The increase in decay capacity is partly caused by injection of oxygen into the sediment, and thereby enhancing the decay of old, oxygen sensitive organic matter several fold. Finally, some future research directions to improve our understanding of diagenetic processes at the oxic/anoxic interface are suggested.     

Attenuation of arsenic trioxide induced cardiotoxicity through flaxseed oil in experimental rats

Objectives: Arsenic trioxide (As₂O₃) is a potent drug for acute promyelocytic leukaemia, but its clinical trials are allied with some serious adverse events mainly cardiac functional abnormalities. So the objective of our investigation is to identify the cardioprotective action of flaxseed oil (FSO), a natural compound against As₂O₃ induced cardiotoxicity.

Methods: Male wistar rats were treated with As₂O₃ (4?mg/kg) to induce cardiotoxicity. FSO (250 and 500?mg/kg) was given in combination with As₂O₃ for evaluating its cardioprotective efficacy.

Results: Treatment with As₂O₃ resulted in deposition of arsenic in heart tissue, increased cardiac marker enzymes release, lipid peroxidation (LPO), oxidative insults and pathological damages in the heart. Co-treatment with FSO (500?mg/kg) significantly reduced the arsenic accumulation, cardiac marker enzymes, LPO and cardiac structural alterations. FSO treatment significantly improved cardiac glutathione content, antioxidant enzymes and reduced the pathological damages in cardiac tissue. Gas chromatographic–mass spectrometry analysis revealed that the major fatty acid content in the FSO is alpha-linolenic acid, which has a strong milieu in cardiac health.

Conclusion: The results of the current investigation suggested that FSO is an effective agent in reducing arsenic-induced cardiac toxicity and can be used as an adjunct/dietary supplement for the cancer patients on As₂O₃ therapy.     

Arsenic transport between water and sediments

Arsenic discharged into the Moira River has accumulated in the sediments of Moira Lake during the past century. The chronology of arsenic concentrations in the sediments, established using Pb-210 dating, has a subsurface concentration maximum (> 1000 g g^–1) that reflects higher inputs to the lake 15 to 45 years ago. The distribution coefficient (K_d) of arsenic in the surficial sediments was low (4000–6000 L kg^–1) and decreased below the sediment water interface. Higher concentrations of exchangeable As also were extracted deeper in the sediments. As a result, arsenic is mobile in the sediment column and the flux of arsenic via diffusion and particle resuspension from the sediments into the water is greater than current external loading from the Moira River. Less than 20% of the external input of arsenic is buried in the lake sediments. Using these flux measurements and a one dimensional model of arsenic transport in the sediment column, we constructed the history of arsenic exchange between water and sediments throughout the past century. The simulations predict that arsenic input into the water from the sediments has been > 20 % of external loading for the past 25 years and will continue to be important in the future as diffusion and resuspension regenerate arsenic from the mixed layer of the sediments into the overlying water.     

Arsenic Trioxide Reduces Global Histone H4 Acetylation at Lysine 16 through Direct Binding to Histone Acetyltransferase hMOF in Human Cells

Histone post-translational modification heritably regulates gene expression involved in most cellular biological processes. Experimental studies suggest that alteration of histone modifications affects gene expression by changing chromatin structure, causing various cellular responses to environmental influences. Arsenic (As), a naturally occurring element and environmental pollutant, is an established human carcinogen. Recently, increasing evidence suggests that As-mediated epigenetic mechanisms may be involved in its toxicity and carcinogenicity, but how this occurs is still unclear. Here we present evidence that suggests As-induced global histone H4K16 acetylation (H4K16ac) partly due to the direct physical interaction between As and histone acetyltransferase (HAT) hMOF (human male absent on first) protein, leading to the loss of hMOF HAT activity. Our data show that decreased global H4K16ac and increased deacetyltransferase HDAC4 expression occurred in arsenic trioxide (As₂O₃)-exposed HeLa or HEK293T cells. However, depletion of HDAC4 did not affect global H4K16ac, and it could not raise H4K16ac in cells exposed to As₂O₃, suggesting that HDAC4 might not directly be involved in histone H4K16 de-acetylation. Using As-immobilized agarose, we confirmed that As binds directly to hMOF, and that this interaction was competitively inhibited by free As₂O₃. Also, the direct interaction of As and C2CH zinc finger peptide was verified by MAIDI-TOF mass and UV absorption. In an in vitro HAT assay, As₂O₃ directly inhibited hMOF activity. hMOF over-expression not only increased resistance to As and caused less toxicity, but also effectively reversed reduced H4K16ac caused by As exposure. These data suggest a theoretical basis for elucidating the mechanism of As toxicity.     

As2O3 oxidation by vitamin C: cell culture studies

The ability of As₂O₃ to induce apoptosis in various malignant cell lines has made it a potential treatment agent for several malignancies. In this study the chemical stability of As₂O₃ (As(III)) in cell-free growth media with various compositions was studied (MEM with different amount of amino acids and DMEM). Special attention was given to evaluate the influence of serum (FBS; fetal bovine serum) absence and vitamin C addition on the oxidation of As(III) to As(V) in cell-free growth media. FBS is an important source of antioxidants and vitamin C (ascorbic acid) is acting as a prooxidant in millimolar concentrations. Media were incubated with As(III) (0.6, 2 and 7 μmol l⁻¹) up to 72 h. Experiments were performed at 37°C in light or/and in the dark, with or without added serum (10%) or vitamin C (1.4, 0.14 mM). Metabolites were followed with high-performance liquid chromatography directly coupled to a hydride generation-atomic fluorescence spectrometry system. After 72 h up to 30% of As(III) was transformed into As(V) in MEMs and up to 35% in DMEM when exposed in dark. Light had no influence on transformations in MEMs, but changed the situation dramatically in DMEM where almost all As(III) was oxidized to As(V) after 72 h when exposed to light. Except for some faster oxidation rate the absence of FBS had little effect on the transformation rate in all media. The most visible impact on As(III) oxidation was observed by addition of vitamin C. Addition of vitamin C (1.4 mM) transformed almost all As(III) to As(V) within 72 h. In lower concentrations (0.14 mM) a pro-oxidative effect was still observed reaching approximately 60% oxidation of As(III) during 72 h. All oxidation processes could be explained by pseudo first order reaction kinetics, yielding reaction rates increasing with initial As(III) concentration and vitamin C concentration whereas the FBS content additionally increased the As(III) oxidation rate in the DMEM (light). The temporal oxidation of As(III) to As(V) in various cell-free growth media necessitates routine checking of the valence state of arsenic during cell culture experiments and the results of biological effects attributed to As(III) should be interpreted with caution. Special attention is needed particularly in cases with vitamin C which was acting pro-oxidatively in all conditions examined.     

Biological Responses to Arsenic Compounds

Arsenic is a metalloid that generates various biological effects on cells and tissues. Depending on the specific tissue exposed and the time and degree of exposure, diverse responses can be observed. In humans, prolonged and/or high dose exposure to arsenic can have a variety of outcomes, including the development of malignancies, severe gastrointestinal toxicities, diabetes, cardiac arrhythmias, and death. On the other hand, one arsenic derivative, arsenic trioxide (As₂O₃), has important antitumor properties. This agent is a potent inducer of antileukemic responses, and it is now approved by the Food and Drug Administration for the treatment of acute promyelocytic leukemia in humans. The promise and therapeutic potential of arsenic and its various derivatives have been exploited for hundreds of years. Remarkably, research focused on the potential use of arsenic compounds in the treatment of human diseases remains highly promising, and it is an area of active investigation. An emerging approach of interest and therapeutic potential involves efforts to target and block cellular pathways activated in a negative feedback manner during treatment of cells with As₂O₃. Such an approach may ultimately provide the means to selectively enhance the suppressive effects of this agent on malignant cells and render normally resistant tumors sensitive to its antineoplastic properties.Arsenic forms complexes with other elements, and it exists in inorganic and organic forms (1–3). The three major inorganic forms of arsenic are arsenic trisulfide (As₂S₃, yellow arsenic), arsenic disulfide (As₂S₂, red arsenic), and arsenic trioxide (As₂O₃, white arsenic) (1–3). There are two different oxidative states of arsenic that correlate with its cytotoxic potential, As(III) and As(V). Among them, As(III) is the most potent form and primarily accounts for its pro-apoptotic and inhibitory effects on target cells and tissues (3). The various forms of arsenic exist in nature primarily in a complex with pyrite (4, 5), although under certain circumstances, arsenic can dissociate from soil and enter natural waters (6), providing a contamination source for humans or animals who ingest such waters. In fact, most associations between long term exposure to arsenic and development of malignancies or other health disorders result from drinking contaminated water, especially in developing countries. Interestingly, pollution of the air with arsenic can also occur under certain circumstances, such as in the case of emissions from coal burning in China (7), providing an additional source of human exposure.The metabolism of arsenic in humans includes reduction to the trivalent state and oxidative methylation to the pentavalent state (reviewed in Ref. 2). There is also reduction of arsenic acid to the arsenous form and subsequent methylation (2). The generation of inorganic or organic trivalent arsenic forms has important implications with regard to the toxicity of this agent, as such compounds are more toxic to the cells and exhibit more carcinogenic properties (2, 3). Thus, many of the consequences of exposure to arsenic as discussed below are the result of the activities and toxicities of the various metabolic products of arsenic compounds. It should be also noted that arsenic has the ability to bind to reduced thiols, including sulfhydryl groups in some proteins (2). Depending on the cellular context, such protein targeting may explain some of its cellular effects and generation of its toxicities and/or therapeutic effects.     

Various tolerances to arsenic trioxide between human cortical neurons and leukemic cells

Arsenic trioxide (As2O3) is very effective for treatment of acute promyelocytic leukaemia (APL) but little can pass through the blood-brain-barrier (BBB),which limits its use in the prevention and treatment of central nervous system leukaemia (CNSL). Before creating a non-invasive method to help As2O3 ’s access,the safe and effective therapeutic concentration of As2O3 in the CNS ought to be known. The changes of apoptosis biomarkers,[Ca2 ]i and PKC activity of both leukaemia cells and human cortical neurons,were monitored before and after being treated with As2O3 in vitro with laser confocal microscopy and Western blot. NSE concentration,the neuron invasive biomarker,was monitored by enzyme immunoassay (NSE-EIA). This study revealed that cortical neuron was more tolerable to As2O3 compared to NB4. 1.0 μmol / L As2O3 showed little influence on cortical neuron but effectively promoted apoptosis and induced differentiation of NB4.     

The influence of chemical form and concentration of arsenic on rice growth and tissue arsenic concentration

Arsenic absorption by rice (Oryza sativa, L.) in relation to the chemical form and concentration of arsenic added in nutrient solution was examined. A 4 × 3 × 2 factorial experiment was conducted with treatments consisting of four arsenic chemical forms [arsenite, As(III); arsenate, As(V); monomethyl arsenic acid, MMAA; and dimethyl arsenic acid, DMAA], three arsenic concentrations [0.05, 0.2, and 0.8 mg As L^-1], and two cultivars [Lemont and Mercury] with a different degree of susceptibility to straighthead, a physiological disease attributed to arsenic toxicity. Two controls, one for each cultivar, were also included. Arsenic phytoavailability and phytotoxicity are determined primarily by the arsenic chemical form present. Application of DMAA increased total dry matter production. While application of As(V) did not affect plant growth, both As(III) and MMAA were phytotoxic to rice. Availability of arsenic to rice followed the trend: DMAA<As(V)<MMAA<As(III). Upon absorption, DMAA was readily translocated to the shoot. Arsenic(III), As(V), and MMAA accumulated in the roots. With increased arsenic application rates the arsenic shoot/root concentration decreased for the As(III) and As(V) treatments. Monomethyl arsenic acid (MMAA), however, was translocated to the shoot upon increased application. The observed differential absorption and translocation of arsenic chemical forms by rice is possibly responsible for the straighthead disorder attributed to arsenic.     

Arsenic Release from a Natural Rock under Near‐natural Oxidizing Conditions

The effects of carbonate concentration and the presence of iron hydroxide phases on the process of arsenic release from an ore material were investigated under experimental oxic conditions and in the pH range from 6.0 to 9.0. These experimental conditions are pertinent to arsenic leaching from tailings and mining wastes. The leaching tests lasted for ≤ 99 days and were performed with materials of five different particle sizes (≤ 2 mm). Carbonate ions were produced in‐situ by dolomite dissolution or were contained in used waters (0 to 30 mM as HCO₃^–). Iron hydroxide phases were formed in situ by oxidative dissolution of metallic iron (Fe⁰) or pyrite (FeS₂). Non‐disturbed batch experiments and air‐homogenized experiments were conducted with a constant amount (10 g/L) of an arsenic‐bearing rock (ore material) of a given particle size and different types of water (deionized, tap and mineral water). For comparison, experiments were conducted with 0.1 M EDTA, 0.1 M Na₂CO₃, and 0.1 M H₂SO₄. Neither the use of dolomite nor the use of water containing various carbonate (HCO₃^–) concentrations could confirm the recent results on the favorable role of As^III‐carbonate complexes on the arsenic transport in the environment. On the other hand, iron hydroxide phases (from Fe⁰ and FeS₂) univocally delayed the As release in both experimental procedures. Furthermore, the theoretically expected effects of the particle size of the ore material was observed. If one takes into consideration that the used HCO₃^– concentrations were up to six times larger then those of natural surface waters (≤ 5.5 mM) but up to five times lower than those currently used in the literature (≥ 100 mM), it is concluded that the reported conflicting results for As leaching from sediments may be a misinterpretation of processes occurring in the sediment and yielding increased As release with increasing HCO₃^–/CO₃^2– concentration.     

Various tolerances to arsenic trioxide between human cortical neurons and leukemic cells

Arsenic trioxide (As₂O₃) is very effective for treatment of acute promyelocytic leukaemia (APL) but little can pass through the blood-brain-barrier (BBB), which limits its use in the prevention and treatment of central nervous system leukaemia (CNSL). Before creating a non-invasive method to help As₂O₃’s access, the safe and effective therapeutic concentration of As₂O₃ in the CNS ought to be known. The changes of apoptosis biomarkers, [Ca²⁺]_i and PKC activity of both leukaemia cells and human cortical neurons, were monitored before and after being treated with As₂O₃ in vitro with laser confocal microscopy and Western blot. NSE concentration, the neuron invasive biomarker, was monitored by enzyme immunoassay (NSE-EIA). This study revealed that cortical neuron was more tolerable to As₂O₃ compared to NB4. 1.0 μmol / L As₂O₃ showed little influence on cortical neuron but effectively promoted apoptosis and induced differentiation of NB4.     

Arsenic speciation in marine interstitial water. The occurrence of organoarsenicals

Arsenic speciation data are presented for pore waters squeezed from some native and anthropogenically influenced sediments.Ten stations were sampled with a box corer (to 20 cm) at two British Columbia coastal sites that are influenced by mine-tailings discharges. These are Rupert Inlet and Alice Arm as well as their associated systems of Quatsino Sound/Holberg Inlet and Hastings Arm respectively.Total dissolved arsenic concentrations (As _D) usually exhibited subsurface maxima at 5–10 cm and were generally related to solid phase arsenic (As _p) levels, but there was also a dependence on the nature of the substrate. Tailings exhibited both the lowest (Rupert Inlet) and the highest (Alice Arm) As _D values. Inorganic arsenicals, arsenate (AsV) and arsenite (AsIII) constituted the majority (>90%) of the dissolved species butevery sample contained organoarsenicals. This is the first report of mono-, di- and tri-methylated arsenic species in marine interstitial water.A strong positive correlation between the sum of the methylarsenic compounds (MeAs) and the total dissolved arsenic (As _D) was found, indicating in situ microbial methylation similar to that observed in non-aquatic systems. Flux values for arsenic at the sediment-water interface suggest that, at present, there is no significant mobilization of arsenic from these mine-derived sediments into the water column.     

Combination of arsenic trioxide and BCNU synergistically triggers redox-mediated autophagic cell death in human solid tumors

Arsenic trioxide (As₂O₃) is an effective treatment for relapsed or refractory acute promyelocytic leukemia (APL). After the discovery of As₂O₃ as a promising treatment for APL, several studies investigated the use of As₂O₃ as a single agent in the treatment of solid tumors; however, its therapeutic efficacy is limited. Thus, the systematic study of the combination of As₂O₃ with other clinically used chemotherapeutic drugs to improve its therapeutic efficacy in treating human solid tumors is merited. In this study, we demonstrate for the first time, using isobologram analysis, that As₂O₃ exhibits a synergistic interaction with N,N′-bis(2-chloroethyl)-N-nitrosourea (BCNU). The synergistic augmentation of the cytotoxicity of As₂O₃ with BCNU is in part through the autophagic cell death machinery in human solid tumor cells. As₂O₃ and BCNU in combination produce enhanced cytotoxicity via the depletion of reduced glutathione (GSH) and augmentation of reaction oxygen species (ROS) production. Further analysis indicated that the extension of GSH depletion by this combined regimen occurs through the inhibition of the catalytic activity of glutathione reductase. Blocking ROS production with antioxidants or ROS scavengers effectively inhibits cell death and autophagy formation, indicating that redox-mediated autophagic cell death involves the synergism of As₂O₃ with BCNU. Taken together, this is the first evidence that BCNU could help to extend the therapeutic spectrum of As₂O₃. These findings will be useful in designing future clinical trials of combination chemotherapy with As₂O₃ and BCNU, with the potential for broad use against a variety of solid tumors.     

Low-Concentration Arsenic Trioxide Inhibits Skeletal Myoblast Cell Proliferation via a Reactive Oxygen Species-Independent Pathway

Myoblast proliferation and differentiation are essential for skeletal muscle regeneration. Myoblast proliferation is a critical step in the growth and maintenance of skeletal muscle. The precise action of inorganic arsenic on myoblast growth has not been investigated. Here, we investigated the in vitro effect of inorganic arsenic trioxide (As₂O₃) on the growth of C2C12 myoblasts. As₂O₃ decreased myoblast growth at submicromolar concentrations (0.25–1 μM) after 72 h of treatment. Submicromolar concentrations of As₂O₃ did not induce the myoblast apoptosis. Low-concentration As₂O₃ (0.5 and 1 μM) significantly suppressed the myoblast cell proliferative activity, which was accompanied by a small proportion of bromodeoxyuridine (BrdU) incorporation and decreased proliferating cell nuclear antigen (PCNA) protein expression. As₂O₃ (0.5 and 1 μM) increased the intracellular arsenic content but did not affect the reactive oxygen species (ROS) levels in the myoblasts. Cell cycle analysis indicated that low-concentrations of As₂O₃ inhibited cell proliferation via cell cycle arrest in the G1 and G2/M phases. As₂O₃ also decreased the protein expressions of cyclin D1, cyclin E, cyclin B1, cyclin-dependent kinase (CDK) 2, and CDK4, but did not affect the protein expressions of p21 and p27. Furthermore, As₂O₃ inhibited the phosphorylation of Akt. Insulin-like growth factor-1 significantly reversed the inhibitory effect of As₂O₃ on Akt phosphorylation and cell proliferation in the myoblasts. These results suggest that submicromolar concentrations of As₂O₃ alter cell cycle progression and reduce myoblast proliferation, at least in part, through a ROS-independent Akt inhibition pathway.     

JWA enhances As<Subscript>2</Subscript>O<Subscript>3</Subscript>-induced tubulin polymerization and apoptosis via p38 in HeLa and MCF-7 cells

Arsenic trioxide (As₂O₃) has potential anti-cancer activity against a wide range of carcinomas via apoptosis induction or oncoprotein degradation. The mechanisms involved are not fully elucidated. Here, we demonstrated that As₂O₃ induced-apoptosis in HeLa and MCF-7 cancer cells was in part triggered by tubulin polymerization. High expression of JWA promoted tubulin polymerization and increased the sensitivity of the cancer cells to As₂O₃. The activation of the p38 MAPK (mitogen-activated protein kinases) signaling pathway was found to contribute to JWA-promoted tubulin polymerization. Our results suggest that JWA may serve as an effective enhancer of microtubule-targeted As₂O₃ anti-cancer therapy.     

Protection effect of taurine on nitrosative stress in the mice brain with chronic exposure to arsenic

Background

Arsenic exposure induces overproduction of reactive nitrogen species (RNS) in brain tissue and results in nucleic acid damage to the nerve cells. The 8-nitroguanine is one of the major products formed by the reaction of guanine, and ONOO^-, and has been used as a popular biomarker of nucleic acid damage due to RNS attacking. In the present study, we examined whether the administration of taurine can protect against nucleic acid damage of brain neurons by arsenic-induced RNS.

Materials and methods

Sixty mice (30 male and 30 female) weighing 19.5 ± 1.5 g were divided into 3 groups: (1) control group, (2) experimental group that received arsenic (As₂O₃), and (3) antagonistic group that received taurine with arsenic. Arsenic was administered for 60 days. 8-Nitroguanine expressions in brain neurons of mice were examined by the immunohistochemical method. Histopathological changes in brain tissues of mice were observed under light microscope and the immunohistochemistry method was used to investigate 8-nitroguanine expressions in cerebrum and cerebellum of mice.

Results

In the control group, no abnormal histopathological changes were observed in brain tissue of the mice. In brain tissue of the mice exposed to arsenic, histopathological results showed swells, evident vacuolar degeneration in cytoplasm, karyorrhexis and karyolysis. Relatively light pathological changes were observed in brain of the mice co-administered arsenic and taurine. Little or no expression of 8-nitroguanine in brain tissue was observed in controls. However, intensive expression of 8-nitroguanine was found in brain tissue of mice exposed to arsenic and it was mainly distributed in nucleus neighbouring the nuclear membrane, but a little in cytoplasm. A weak expression of 8-nitroguanine was observed in brain cells of mice co-administered arsenic and taurine.

Conclusions

The brain neurons may be the major target cells of arsenic neurotoxicity. Co-administration of arsenic and taurine can alleviate DNA damage of brain neurons caused by arsenic through the RNS signal pathway.

     

The degradation of arsenobetaine to inorganic arsenic by sedimentary microorganisms

Two growth media containing arsenobetaine [(CH₃)₃ As⁺ CH₂COO^–] were mixed with coastal marine sediments, the latter providing a source of microorganisms. The mixtures were kept at 25 °C in the dark and shaken for several weeks under an atmosphere of air. The disappearance of arsenobetaine and the appearance of two metabolites were followed by HPLC. The HPLC-retention time of the first metabolite agreed with that of trimethylarsine oxide [(CH₃)₃AsO]. The second metabolite was identified as arsenate (As(V)) using hydride generation/cold trap/GC MS analysis and thin layer chromatography. This is the first scientific evidence showing that arsenobetaine is degraded by microorganisms to inorganic arsenic via trimethylarsine oxide. The degradation of arsenobetaine to inorganic arsenic completes the marine arsenic cycle that begins with the methylation of inorganic arsenic on the way to arsenobetaine.     

Arsenic exposure alters activity behaviour of key nitrogen assimilatory enzymes in growing rice plants

Rice seedlings when grown in sand cultures for 5–20 days under 25 and 50 M As₂O₃ in the medium showed a marked decline in growth when compared to controls. Increased absorption of arsenic from the medium, against the concentration gradient was observed. Greater localization of absorbed arsenic was noted in roots than in shoots. Rice plants grown for 20 days with 50 mol l^–1 arsenic in the medium accumulated upto 370 mol arsenic kg^–1 dry weight in roots. Increasing levels of As₂O₃ in situ caused a marked decline in the activities of the nitrate assimilatory enzymes nitrate reductase (NR), nitrite reductase (NiR) and glutamine synthetase (GS), whereas an increase in the activities of alanine and aspartate aminotransferases was observed. The activities of aminating (NADH-GDH) and deaminating (NAD⁺-GDH) glutamate dehydrogenases increased at moderately toxic level (25 M) of As₂O₃ whereas a higher As level of 50 M was inhibitory to the enzymes. Addition of 1 M proline in the reaction medium caused significant restoration in As-led loss of NR and GS activities. NR and GS extracted from arsenic exposed seedlings showed higher K _m values compared to the enzymes extracted from control-grown seedlings, whereas GDHs extracted from As-stressed seedlings showed a decrease in K _m. Results suggest that inhibition in the activities of N assimilatory enzymes accompanied with decreased affinity of the enzymes towards their substrates would eventually lead to a marked suppression of N assimilation and impaired growth of rice seedlings in As polluted environment.     

Oxidation of arsenite to arsenate by a bacterium isolated from an aquatic environment

Arsenic is ubiquitous in the biosphere and frequently reported to be an environmental pollutant. Global cycling of arsenic is affected by microorganisms. This paper describes a new bacterial strain which is able to efficiently oxidize arsenite (As[III]) into arsenate (As[V]) in liquid medium. The rate of the transformation depends on the cell density. Arsenic species were separated by high performance liquid chromatography (HPLC) and quantified by inductively coupled plasma-atomic emission spectrometry (ICP-AES). The strain also exhibits high minimum inhibitory concentrations (MICs) for As[III] (6.65 mM (500 mg L^-1)) and other heavy metals, such as cadmium (1.42 mM (160 mg L^-1)) or lead (1.20 mM (250 mg L^-1)). Partial identification of the strain revealed a chemoorganotrophic, Gram-negative and motile rod. The results presented here demonstrate that this strain could represent a good candidate for arsenic remediation in heavily polluted sites.