Role of the Alkali Labile Sites,Reactive Oxygen Species and Antioxidants in DNA Damage Induced by Methylated Trivalent Metabolites of Inorganic Arsenic

In the last decade arsenic metabolism has become an important matter of discussion. Methylation of inorganic arsenic (iAs) to monomethylarsonic acid (MMA^V) and dimethylarsinic acid (DMA^V) is considered to decrease arsenic toxicity. However, in addition to these pentavalent metabolites, the trivalent metabolites monomethylarsonous (MMA^III) and dimethylarsinous acid (DMA^III) have been identified recently as intermediates in the metabolic pathway of arsenic in cultured human cells. To examine the role of oxidative damage in the generation of DNA strand breaks by methylated trivalent arsenic metabolites, we treated human lymphocytes with both metabolites at non-cytotoxic concentrations. We further tested whether these effects are sensitive to modulation by the antioxidants ascorbate (Vitamin C) and selenomethionine (Se-Met). Both trivalent metabolites produced oxidative stress related DNA damage, consisting of single strand breaks and alkali-labile sites, with MMA^III being more potent at low concentrations than DMA^III. Neither MMA^III nor DMA^III induced DNA-double strand breaks. The oxidative stress response profiles of the metabolites were parallel as determined by lipid peroxidation induction. MMA^III induced peroxidation from the lowest concentration tested, while effects of DMA^III were apparent only at concentrations above 10 μM. The antioxidant Se-Met exhibited a more pronounced inhibition of trivalent arsenic metabolite-induced oxidative-DNA damage than did vitamin C. The present findings suggest that DNA damage by methylated trivalent metabolites at non-cytotoxic concentrations may be mediated by a mix of reactive oxygen and nitrogen oxidized species.     

Oxidation and methylation status determine the effects of arsenic on the mitotic apparatus

We investigated the spindle inhibitory properties of six arsenicals differing in their methylation or oxidation state. Human lymphoblasts were exposed for 6 h to either sodium arsenate (NaAs^V), sodium arsenite (NaAs^III), monomethylarsonic acid (MMA^V), monomethylarsonous acid (MMA^III), dimethylarsinic acid (DMA^V), or dimethylarsinous acid (DMA^III). After exposure slides were prepared, and the mitotic indices (MI) were assessed. We also exposed tubulin directly to each arsenical and spectrophotometrically measured its effect on polymerization. NaAs^V caused a small but significant increase in MI. MMA^V also caused only a slight increase in MI that just reached statistical significance. In contrast, DMA^V caused a significant increase in MI, producing ∼75% the MI of demecolcine and ∼4 times the MI of the control. NaAs^III had no significant effect on MI and was quite toxic. MMA^III induced more than a twofold increase in MI compared to the control, which was about 40% that caused by demecolcine. On a micromolar basis, MMA^III was the most potent of the arsenicals tested. DMA^III gave inconsistent results. None of the pentavalent arsenicals had a substantial effect (either inhibition or enhancement) on GTP-induced polymerization of tubulin. In contrast, NaAs^III inhibited polymerization at concentrations of 1 mM and above and MMA^III and DMA^III at 10 μM and above. Taken together, these results present a complex picture of how arsenicals may affect cells. These studies demonstrate that the metabolites of arsenic are active not only as chromosome breaking and DNA damaging agents but can also interfere with cell division via tubulin disruption.     

Monomethylarsonous Acid (MMAIII) Has an Adverse Effect on the Innate Immune Response of Human Bronchial Epithelial Cells to Pseudomonas aeruginosa

Arsenic is the number one contaminant of concern with regard to human health according to the World Health Organization. Epidemiological studies on Asian and South American populations have linked arsenic exposure with an increased incidence of lung disease, including pneumonia, and chronic obstructive pulmonary disease, both of which are associated with bacterial infection. However, little is known about the effects of low dose arsenic exposure, or the contributions of organic arsenic to the innate immune response to bacterial infection. This study examined the effects on Pseudomonas aeruginosa (P. aeruginosa) induced cytokine secretion by human bronchial epithelial cells (HBEC) by inorganic sodium arsenite (iAs^III) and two major metabolites, monomethylarsonous acid (MMA^III) and dimethylarsenic acid (DMA^V), at concentrations relevant to the U.S. population. Neither iAs^III nor DMA^V altered P. aeruginosa induced cytokine secretion. By contrast, MMA^III increased P. aeruginosa induced secretion of IL-8, IL-6 and CXCL2. A combination of iAs^III, MMA^III and DMA^V (10 pbb total) reduced IL-8 and CXCL1 secretion. These data demonstrate for the first time that exposure to MMA^III alone, and a combination of iAs^III, MMA^III and DMA^V at levels relevant to the U.S. may have negative effects on the innate immune response of human bronchial epithelial cells to P. aeruginosa.     

Possible differences in the mechanism of malignant transformation of HaCaT cells by arsenite and its dimethyl metabolites,particularly dimethylthioarsenics

Background: As a confirmed human carcinogen, arsenic can cause skin cancer, lung cancer, etc. However, its carcinogenic mechanism is still unclear. In recent years, the oxidative stress hypothesis has become widely accepted. In mammals it has been found that arsenic can be converted to dimethylarsinous acid (DMA^III) and dimethylmonothioarsinic acid (DMMTA^V) through a series of methylation and redox reactions. DMA^III and DMMTA^V are highly toxic.Methods: Human keratinocytes (HaCaT) were exposed to different concentrations of NaAsO₂ (IAs^III), DMMTA^V and DMA^III for 24 h. Reactive oxygen species (hydrogen peroxide and superoxide), oxidative damage markers (8-hydroxydeoxyguanosine and malondialdehyde), and antioxidant markers (glutathione and superoxide dismutase) were measured. In addition, sulfane sulfurs were measured in HaCaT cells and a cell-free system.Results: In the DMMTA^V and DMA^III treatment groups, the levels of hydrogen peroxide and superoxide in HaCaT cells were higher than in the IAs^III treatment groups at the same dose. Levels of 8−OHdG and MDA in the DMMTA^V and DMA^III treatment groups were also higher than those in the IAs^III treatment groups at the same dose. However, in the DMMTA^V and DMA^III treatment groups, the levels of GSH and SOD activity were lower than that in the IAs^III treatment groups. In DMMTA^V-treated HaCaT cells, sulfane sulfurs were produced. Further, it was found that DMMTA^V could react with DMDTA^V to form persulfide in the cell-free system, which may explain the mechanism of the formation of sulfane sulfurs in DMMTA^V-treated HaCaT cells.Conclusions: DMMTA^V and DMA^III more readily induce reactive oxygen species (ROS) and cause oxidative damage in HaCaT cells than inorganic arsenic. Further, the persulfide formed by the reaction of DMMTA^V and DMDTA^V produced from the metabolism of DMMTA^V may induce a stronger reductive defense mechanism than GSH against the intracellular oxidative stress of DMMTA^V. However, the cells exposed to arsenite are transformed by the continuous nuclear translocation of Nrf2 due to oxidative stress, and the persulfide from dimethylthioarsenics may promote Nrf2 by the combination with thiol groups, especially redox control key protein, Keap1, eventually cause nuclear translocation of sustained Nrf2.     

Proposal for novel metabolic pathway of highly toxic dimethylated arsenics accompanied by enzymatic sulfuration,desulfuration and oxidation

The International Agency for Research on Cancer (IARC) has concluded that dimethylarsinic acid [(CH₃)₂AsO(OH), DMA^V], a main metabolite of inorganic arsenic, is responsible for carcinogenesis in urinary bladder and lung in rodents, and various modes of carcinogenic action have been proposed. One theory concerning the mode of action is that the biotransformation of dimethylarsinous acid [(CH₃)₂AsOH, DMA^III] from DMA^V plays an important role in the carcinogenesis by way of reactive oxygen species (ROS) production. Furthermore, dimethylmonothioarsinic acid [(CH₃)₂AsS(OH), DMMTA^V], a metabolite of DMA^V, has also been noted because of its higher toxicity. However, the metabolic mechanisms of formation and disappearance of DMA^III and DMMTA^V, and their toxicity are not fully understood. Thus, the purpose of the present study was to clarify the mechanism of metabolic formation of DMMTA^V and DMA^V from DMA^III. The in vitro transformation of arsenicals by treatment with liver homogenate from rodents and sulfur transferase was detected by HPLC-ICP-MS and HPLC-tandem MS. DMMTA^V is produced from DMA^III but not DMA^V by cellular fractions from mouse liver homogenates and by rhodanese from bovine liver in the presence of thiosulfate, a sulfur donor. Not only DMMTA^V thus produced but also DMA^III are re-converted into DMA^V by an in vitro addition of S9 mix. These findings indicate that the metabolic process not only of DMA^III to DMA^V or DMMTA^V but also of DMMTA^V to DMA^V consists of a complicated mode of interaction between monooxygenase including cytochrome P450 (CYP) and/or sulfur transferase.     

Cytogenetic insights into DNA damage and repair of lesions induced by a monomethylated trivalent arsenical

Arsenic is a human carcinogen, and only recently animal models have been developed that are useful in investigating its carcinogenic mode of action (MOA). However, how arsenic induces cancer is still an open question. In a previous paper, we proposed a model detailing how arsenic might induce DNA lesions leading to cytogenetic damage [A.D. Kligerman, A.H. Tennant, Toxicol. Appl. Pharmacol. 222 (2007) 281–288]. In this model we hypothesized that arsenic does not induce chromosome damage via DNA adduction but induces short-lasting lesions from the action of reactive oxygen species (ROS). These lesions cause single-strand breaks (SSB) that induce chromosome breakage when treatment is in late G₁- or S-phase. However, if treatment is confined to the G₀- or early G₁-phase of the cell cycle, it is predicted that little or no cytogenetic damage will result at the subsequent metaphase. Here, we describe the results from testing this model using monomethylarsonous acid (MMA^III) and cytosine arabinoside (araC), a DNA chain terminator, to extend the time that DNA lesions remain open during repair to allow the lesions to reach S-phase or interact to form DNA exchanges that would lead to exchange aberrations at metaphase. The results of our study only partially confirmed our hypothesis. Instead, the results indicated that the lesions induced by MMA^III are quickly repaired through base excision repair, that there is little chance for araC to extend the life of the lesions, and thus the DNA damage induced by arsenicals that leads to chromosome aberrations is very short lived.     

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.     

Bioadsorption of arsenic from aqueous solution by the extremophilic bacterium Acidithiobacillus ferrooxidans DLC-5

The bioadsorption of heavy metal ions to process industrial and solid wastes is an attractive technology from an economical and environmental point of view. This study investigated the equilibrium, thermodynamics and bioadsorption characteristics of arsenite (iAs^III) and dimethylarsinate (DMA^V) by Acidithiobacillus ferrooxidans (A. ferrooxidans) DLC-5 in aqueous solution. Optimum bioadsorption conditions were determined by identifying the optimum temperature, pH, biomass dosage, initial arsenic concentration and contact time. The equilibrium data were then applied to Langmuir and Freundlich isotherm models. The results indicated that the bioadsorption processes for both iAs^III and DMA^V involved pseudo-second-order kinetics. Additionally, the bioadsorption of iAs^III and DMA^V by A. ferrooxidans DLC-5 was feasible, spontaneous and endothermic under the tested conditions. Fourier transform infrared spectroscopy (FT-IR) showed that –OH and –NH groups were involved in the bioadsorption process. A. ferrooxidans DLC-5 demonstrates potential for use in removing arsenic from aqueous solutions, especially those with very low arsenic concentrations.     

Organic anion transporting polypeptide-C mediates arsenic uptake in HEK-293 cells

Summary Arsenic is an established human carcinogen. The role of aquaglyroporins (AQPs) in arsenic disposition was recently identified. In order to examine whether organic anion transporting polypeptide-C (OATP-C) also plays a role in arsenic transport, OATP-C cDNA was transfected into cells of a human embryonic kidney cell line (HEK-293). Transfection increased uptake of the model OATP-C substrate, estradiol-17β-D-glucuronide, by 10-fold. In addition, we measured uptake and cytotoxicity of arsenate, arsenite, monomethylarsonate(MMA^V), and dimethylarsinate (DMA^V). Transfection of OATP-C increased uptake and cytotoxicity of arsenate and arsenite, but not of MMA^V or DMA^V. Rifampin and taurocholic acid (a substrate of OATP-C) reversed the increased toxicity of arsenate and arsenite seen in OATP-C-transfected cells. The increase in uptake of inorganic arsenic was not as great as that of estradiol-17β-D-glucuronide. Our results suggest that OATP-C can transport inorganic arsenic in a (GSH)-dependent manner. However, this may not be the major pathway for arsenic transport.     

Phosphate starvation response controls genes required to synthesize the phosphate analog arsenate

Environmental arsenic poisoning affects roughly 200 million people worldwide. The toxicity and mobility of arsenic in the environment is significantly influenced by microbial redox reactions, with arsenite (As^III) being more toxic than arsenate (As^V). Microbial oxidation of As^III to As^V is known to be regulated by the AioXSR signal transduction system and viewed to function for detoxification or energy generation. Here, we show that As^III oxidation is ultimately regulated by the phosphate starvation response (PSR), requiring the sensor kinase PhoR for expression of the As^III oxidase structural genes aioBA. The PhoRB and AioSR signal transduction systems are capable of transphosphorylation cross‐talk, closely integrating As^III oxidation with the PSR. Further, under PSR conditions, As^V significantly extends bacterial growth and accumulates in the lipid fraction to the apparent exclusion of phosphorus. This could spare phosphorus for nucleic acid synthesis or triphosphate metabolism wherein unstable arsenic esters are not tolerated, thereby enhancing cell survival potential. We conclude that As^III oxidation is logically part of the bacterial PSR, enabling the synthesis of the phosphate analog As^V to replace phosphorus in specific biomolecules or to synthesize other molecules capable of a similar function, although not for total replacement of cellular phosphate.     

Pentavalent methylated arsenicals are substrates of human AQP9

Liver aquaglyceroporin AQP9 facilitates movement of trivalent inorganic arsenite (As^III) and organic monomethylarsonous acid (MAs^III). However, the transport pathway for the two major pentavalent arsenic cellular metabolites, MAs^V and DMAs^V, remains unknown in mammals. These products of arsenic metabolism, in particular DMAs^V, are the major arsenicals excreted in the urine of mammals. In this study, we examined the uptake of the two pentavalent organic arsenicals by human AQP9 in Xenopus laevis oocytes. Xenopus laevis oocytes microinjected with AQP9 cRNA exhibited uptake of both MAs^V and DMAs^V in a pH-dependent manner. The rate of transport was much higher at acidic pH (pH5.5) than at neutral pH. Hg(II), an aquaporin inhibitor, inhibited transport of As^III, MAs^III, MAs^V and DMAs^V via AQP9. However, phloretin, which inhibits water and glycerol permeation via AQP9, can only inhibit transport of pentavalent MAs^V and DMAs^V but not trivalent As^III and MAs^III, indicating the translocation mechanisms of these arsenic species are not exactly the same. Reagents such as FCCP, valinomycin and nigericin that dissipate transmembrane proton potential or change the transmemebrane pH gradient did not significantly inhibit all arsenic transport via AQP9, suggesting the transport of pentavalent arsenic is not proton coupled. The results suggest that in addition to the initial uptake of trivalent inorganic As^III inside cells, AQP9 plays a dual role in the detoxification of arsenic metabolites by facilitating efflux from cells.     

Flexible bacterial strains that oxidize arsenite in anoxic or aerobic conditions and utilize hydrogen or acetate as alternative electron donors

Arsenic is a carcinogenic compound widely distributed in the groundwater around the world. The fate of arsenic in groundwater depends on the activity of microorganisms either by oxidizing arsenite (As^III), or by reducing arsenate (As^V). Because of the higher toxicity and mobility of As^III compared to As^V, microbial-catalyzed oxidation of As^III to As^V can lower the environmental impact of arsenic. Although aerobic As^III-oxidizing bacteria are well known, anoxic oxidation of As^III with nitrate as electron acceptor has also been shown to occur. In this study, three As^III-oxidizing bacterial strains, Azoarcus sp. strain EC1-pb1, Azoarcus sp. strain EC3-pb1 and Diaphorobacter sp. strain MC-pb1, have been characterized. Each strain was tested for its ability to oxidize As^III with four different electron acceptors, nitrate, nitrite, chlorate and oxygen. Complete As^III oxidation was achieved with both nitrate and oxygen, demonstrating the novel ability of these bacterial strains to oxidize As^III in either anoxic or aerobic conditions. Nitrate was only reduced to nitrite. Different electron donors were used to study their suitability in supporting nitrate reduction. Hydrogen and acetate were readily utilized by all the cultures. The flexibility of these As^III-oxidizing bacteria to use oxygen and nitrate to oxidize As^III as well as organic and inorganic substrates as alternative electron donors explains their presence in non-arsenic-contaminated environments. The findings suggest that at least some As^III-oxidizing bacteria are flexible with respect to electron-acceptors and electron-donors and that they are potentially widespread in low arsenic concentration environments.     

Role of AQP9 in transport of monomethyselenic acid and selenite

AQP9 is an aquaglyceroporin with a very broad substrate spectrum. In addition to its orthodox nutrient substrates, AQP9 also transports multiple neutral and ionic arsenic species including arsenic trioxide, monomethylarsenous acid (MAs^III) and dimethylarsenic acid (DMA^V). Here we discovered a new group of AQP9 substrates which includes two clinical relevant selenium species. We showed that AQP9 efficiently transports monomethylselenic acid (MSeA) with a preference for acidic pH, which has been demonstrated in Xenopus laevis oocyte following the overexpression of human AQP9. Specific inhibitors that dissipate transmembrane proton potential or change the transmembrane pH gradient, such as FCCP, valinomycin and nigericin did not significantly inhibit MSeA uptake, suggesting MSeA transport is not proton coupled. AQP9 was also found to transport ionic selenite and lactate, with much less efficiency compared with MSeA uptake. Selenite and lactate uptake via AQP9 is pH dependent and inhibited by FCCP and nigericin, but not valinomycin. The selenite and lactate uptake via AQP9 can be inhibited by different lactate analogs, indicating that their translocation share similar mechanisms. AQP9 transport of MSeA, selenite and lactate is all inhibited by a previously identified AQP9 inhibitor, phloretin, and the AQP9 substrate arsenite (As^III). These newly identified AQP9 selenium substrates imply that AQP9 play a significant role in MSeA uptake and possibly selenite uptake involved in cancer therapy under specific microenvironments.     

Copper increases the damage to DNA and proteins caused by reactive oxygen species

Copper [Cu(II)] is an ubiquitous transition and trace element in living organisms. It increases reactive oxygen species (ROS) and free-radical generation that might damage biomolecules like DNA, proteins, and lipids. Furthermore, ability of Cu(II) greatly increases in the presence of oxidants. ROS, like hydroxyl (·OH) and superoxide (·O₂) radicals, alter both the structure of the DNA double helix and the nitrogen bases, resulting in mutations like the AT→GC and GC→AT transitions. Proteins, on the other hand, suffer irreversible oxidations and loss in their biological role. Thus, the aim of this investigation is to characterize, in vitro, the structural effects caused by ROS and Cu(II) on bacteriophage λ DNA or proteins using either hydrogen peroxide (H₂O₂) or ascorbic acid with or without Cu(II). Exposure of DNA to ROS-generating mixtures results in electrophoretic (DNA breaks), spectrophotometric (band broadening, hypochromic, hyperchromic, and bathochromic effects), and calorimetric (denaturation temperature [T _d], denaturation enthalpy [ΔH], and heat capacity [C _p] values) changes. As for proteins, ROS increased their thermal stability. However, the extent of the observed changes in DNA and proteins were distinct, depending on the efficiency of the systems assayed to generate ROS. The resulting effects were most evident when Cu(II) was present. In summary, these results show that the ROS, ·O₂ and ·OH radicals, generated by the Cu(II) systems assayed deeply altered the chemical structure of both DNA and proteins. The physiological relevance of these structural effects should be further investigated.     

Oxidative Damage Induced by Arsenic in Mice or Rats: A Systematic Review and Meta-Analysis

In this meta-analysis, studies reporting arsenic-induced oxidative damage in mouse models were systematically evaluated to provide a scientific understanding of oxidative stress mechanisms associated with arsenic poisoning. Fifty-eight relevant peer-reviewed publications were identified through exhaustive database searching. Oxidative stress indexes assessed included superoxide dismutase (SOD), catalase (CAT), glutathione (GSH), glutathione peroxidase (GPx), glutathione-s-transferase (GST), glutathione reductase (GR), oxidized glutathione (GSSG), malondialdehyde (MDA), and reactive oxygen species (ROS). Our meta-analysis showed that arsenic exposure generally suppressed measured levels of the antioxidants, SOD, CAT, GSH, GPx, GST, and GR, but increased levels of the oxidants, GSSG, MDA, and ROS. Arsenic valence was important and GR and MDA levels increased to a significantly (P < 0.05) greater extent upon exposure to As³⁺ than to As⁵⁺. Other factors that contributed to a greater overall oxidative effect from arsenic exposure included intervention time, intervention method, dosage, age of animals, and the sample source from which the indexes were estimated. Our meta-analysis effectively summarized a wide range of studies and detected a positive relationship between arsenic exposure and oxidative damage. These data provide a scientific basis for the prevention and treatment of arsenic poisoning.     

Characterization of an ecotype of brake-fern, Pteris vittata, for arsenic tolerance and accumulation in plant biomass

An ecotype of brake fern (Pteris vittata) was assessed for arsenic tolerance and accumulation in its biomass under in vivo and in vitro condition; using soil, and agar-gelled Murashige and Skoog (MS) medium supplemented with different concentrations of arsenic. The plants were raised in soil amended with 100–1000 mg arsenic kg⁻¹ soil, and MS medium was supplemented with 10–300 mg arsenic 1⁻¹ medium using Na₂HAsO₄ · 7H₂O. The spores and haploid gametophytic-prothalli were raised in vitro on MS medium supplemented with arsenic. The field plants showed normal growth and biomass formation in arsenic amended soil, and accumulated 1908–4700 mg arsenic kg⁻¹ dry aerial biomass after 10 weeks of growth. Arsenic toxicity was observed above >200 mg arsenic kg⁻¹ soil. The concentrations of arsenic accumulated in the plant biomass were statistically significant (p < 0.05). Normal plants were developed from spores and gametophyte prothalli on the MS media supplemented with 50–200 mg arsenic 1⁻¹ medium. The in vitro raised plants were tolerant to 300 mg arsenic kg⁻¹ of soil and accumulated up to 3232 mg arsenic kg⁻¹ dry aerial biomass that showed better growth performance, biomass generation and arsenic accumulation in comparison to the field plants. The text was submitted by the authors in English.     

Ellagic acid mitigates arsenic‐trioxide‐induced mitochondrial dysfunction and cytotoxicity in SH‐SY5Y cells

In the current study, neuroprotective significance of ellagic acid (EA, a polyohenol) was explored by primarily studying its antioxidant and antiapoptotic potential against arsenic trioxide (As₂O₃)‐induced toxicity in SH‐SY5Y human neuroblastoma cell lines. The mitigatory effects of EA with particular reference to cell viability and cytotoxicity, the generation of reactive oxygen species, DNA damage, and mitochondrial dynamics were studied. Pretreatment of SH‐SY5Y cells with EA (10 and 20 μM) for 60 min followed by exposure to 2 μM As₂O₃ protected the SH‐SY5Y cells against the harmful effects of the second. Also, EA pre‐treated groups expressed improved viability, repaired DNA, reduced free radical generation, and maintained altered mitochondrial membrane potential than those exposed to As₂O₃ alone. EA supplementation also inhibited As₂O₃‐induced cytochrome c expression that is an important hallmark for determining mitochondrial dynamics. Thus, the current investigations are more convinced for EA as a promising candidate in modulating As₂O₃‐induced mitochondria‐mediated neuronal toxicity under in vitro system.     

Non-enzymatic roles for the URE2 glutathione S-transferase in the response of Saccharomyces cerevisiae to arsenic

The response of Saccharomyces cerevisiae to arsenic involves a large ensemble of genes, many of which are associated with glutathione-related metabolism. The role of the glutathione S-transferase (GST) product of the URE2 gene involved in resistance of S. cerevisiae to a broad range of heavy metals was investigated. Glutathione peroxidase activity, previously reported for the Ure2p protein, was unaffected in cell-free extracts of an ure2Δ mutant of S. cerevisiae. Glutathione levels in the ure2Δ mutant were lowered about threefold compared to the isogenic wild-type strain but, as in the wild-type strain, increased 2–2.5-fold upon addition of either arsenate (As^V) or arsenite (As^III). However, lack of URE2 specifically caused sensitivity to arsenite but not to arsenate. The protective role of URE2 against arsenite depended solely on the GST-encoding 3′-end portion of the gene. The nitrogen source used for growth was suggested to be an important determinant of arsenite toxicity, in keeping with non-enzymatic roles of the URE2 gene product in GATA-type regulation.     

Arsenate and arsenite: the toxic effects on photosynthesis and growth of lettuce plants

Arsenate (As^V) and arsenite (As^III) contamination can promote several disturbances in plant metabolism, besides affecting directly human and animal health due to the insertion of this metalloid in the food chain. Therefore, the arsenic (As) uptake and accumulation, the changes in gas exchange and in chlorophyll a fluorescence parameters as well as the chloroplastic pigments content were measured. The As accumulation in leaves and roots increased with the increase of As^V and As^III concentration, except at the highest As^III concentration, probably because of As^III extrusion mechanism. Although the highest As concentration has been found in roots, significant amount was transported to the leaves, especially when plants were exposed to As^III. The As accumulation decreased the relative growth rate (RGR) of leaves and roots. However, at 6.6 μmol L^?1 As^V, an increase in leaves RGR was observed, possibly related to the changes in phosphate (P^V) nutrition caused by As. As^V and As^III interfered negatively in the photosynthetic process, except at 6.6 μmol L^?1 As^V. The observed reduction seemed to be associated to the interference in the photochemical and biochemical steps of photosynthesis; however, chlorophyll a fluorescence results indicate that the photosynthetic apparatus and chloroplastic pigments were not damaged. So, lettuce plants demonstrated to be able to accumulate As and also to protect the photosynthetic apparatus against the harmful effects of this metalloid, probably through the activation of tolerance mechanisms.