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5 protocols using asnao2

1

Chronic Arsenic Exposure in Mice

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All procedures involving mice were approved by the University of North Carolina (UNC) Institutional Animal Care and Use Committee. Male and female C57BL/6J WT mice were obtained from Jackson Laboratories (Bar Harbor, ME, USA) and let to acclimatize at the UNC Animal Facilities for one week. Male and female As3mt-KO mice on a C57BL/6 background (Drobná, et al. 2009 (link)) were bred at the UNC Animal Facilities. Both WT and As3mt-KO mice were housed under controlled conditions with 12-h light/dark cycle at 22±1°C and 50±10% relative humidity (3–5 mice per cage) and with unlimited access to pelleted 2920X Teklad rodent chow (Envigo, Madison, WI, USA). All mice were 21-week old at the beginning of the study when they were randomly assigned to treatment groups with 10–14 animals per group. Both WT and As3mt-KO mice drank for 24 weeks (ad libitum) either deionized water or deionized water containing sodium arsenite (AsNaO2, ≥99% pure; Sigma-Aldrich, St. Louis, MO, USA) at final concentrations of 0.1 or 1.0 mg As/L (i.e., 0.1 or 1 ppm). Water with sodium arsenite was prepared weekly to minimize oxidation of iAsIII to iAsV. Food and water consumption and body weight were monitored in all treatment groups weekly.
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2

Arsenite Stress Response in HuH7 Cells

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HuH7 human hepatocellular carcinoma cells (RRID:CVCL_0336) were grown in low glucose (1 g/l) Dulbeco's modified Eagle's medium (DMEM) (#21885108, Thermo Fisher Scientific) supplemented with 10% heat-inactivated fetal bovine serum (FBS), penicillin and streptomycin. Forty eight hours prior to stress experiments, the cells were seeded on culture plates at a density of 1.1 × 104 cells/cm2. For the stress-experiments the cells were changed into a culture media containing 100 μM arsenite (AsNaO2, #S7400-100G, Sigma Aldrich) for 1 h. For non-stressed controls, normal fresh culture media was used.
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3

Chronic Arsenic Exposure in Mice

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All procedures involving mice were approved by the University of North Carolina (UNC) Institutional Animal Care and Use Committee. Male and female C57BL6 WT mice were obtained from Jackson Laboratories (Bar Harbor, ME) and let to acclimatize at the UNC Animal Facilities for one week. These WT mice were 17 weeks (±3 days) old at the beginning of the study. Male and female As3mt-KO mice on a C57BL6 background (Drobna, et al. 2009 (link)) were bred at the UNC Animal Facilities and were 17–20 weeks old at the beginning of the study. All mice were housed under controlled conditions (12-h light/dark cycle at 22+−1°C and 50±10% relative humidity) with ad libitum access to pelleted rodent chow (Prolab Isopro RMH 3000, LabDiet, St. Louis, MO). Mice drank either deionized water or deionized water containing 1 ppm As as sodium arsenite (AsNaO2, ≥99% pure; Sigma-Aldrich, St. Louis, MO, USA) ad libitum for four weeks (N=15–21 per experimental group). Water with iAsIII was freshly prepared every week to minimize oxidation of iAsIII to iAsV. Food and water consumption and body weight were monitored in all treatment groups every week and two weeks, respectively.
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4

Heavy Metal Exposure Induction Protocol

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NaCl (Carl Roth), ZnCl2 (Carl Roth), AgNO3 (Carl Roth), HgCl2 (Carl Roth), NiCl2 (Applichem), AsNaO2 (Sigma Aldrich), NiCl2 x 6 H2O (Sigma Aldrich), CdSO4 x 8/3 H2O (Sigma-Aldrich), CuSO4 (Sigma Aldrich), Pb(NO3)2 (Carl Roth) and guanidine hydrochloride (Carl Roth), respectively D-Sorbitol (Carl Roth) were dissolved to a concentration of 1 M, stored at—20°C and diluted in DMEM complete. For continuous treatment, the medium in the well was removed and replaced with inducer, diluted in DMEM complete for 6 h or 24 h. For 1 h induction cells were induced for 1 h with DMEM complete containing heavy metals. After 1 h this medium was removed and replaced fresh DMEM complete.
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5

Arsenic Removal by Commercial Adsorbents

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Throughout the whole set of experiments (batch and column tests), 1000 mg L ¡1 stock solutions of As(III) and As (V) were prepared in ultrapure water (< 0.06 mS cm ¡1 ) from sodium (meta) arsenite (AsNaO 2 , 99%, Sigma-Aldrich, USA) and sodium arsenate dibasic heptahydrate (Na 2 HAsO 4 .7H 2 O, 99 -102%, Sigma-Aldrich, ACS reagent) respectively. The desired arsenic concentration for each run was obtained by fresh dilution of the stock solution on a daily basis.
Three commercial adsorbents were tested: granular titanium dioxide (TiO 2 , Adsorbsia As500, Dow Chemical Company, USA), granular ferric hydroxide (GFH, Pro H 2 O, USA) and activated alumina (AA, AxSorb A, Axens, France). The main characteristics and physical properties of the three materials are summarized in Table 1.
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