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PubMedDate not supplied

Measurement of bromate in bottled water by high-performance liquid chromatography with post-column flow reactor detection.

The objective of this work was to develop a reliable, rugged high-performance liquid chromatographic (HPLC) method for determination of trace levels of bromate (< 10 micrograms/l) in bottled water. HPLC separation was achieved by ion interaction chromatography using a C-18 reversed-phase column and a mobile phase consisting of methanol/water (20:80, v/v) with tetrabutylammonium acetate as the ion interaction reagent. A post-column reaction based on oxidation of o-dianisidine in acidic solution to a product detected at 500 nm provided selective measurement of the oxidants. The limit of detection and the limit of quantitation were 1 and 3 micrograms/l, respectively. Iodate, chlorite, and nitrite were chromatographically separated from bromate and measured by monitoring the post-column reaction. Chloride and chlorate at levels that might be found in bottled water did not interfere with the determination of bromate. Bromate was detected in bottled waters at concentrations up to 40 micrograms/l.

Bromates↗
PubMed1991

Structure of hexaaquanickel(II) bromate.

[Ni(H2O)6](BrO3)2, Mr = 422.60, cubic, Pa3, a = 10.2987 (6) A, V = 1092.3 (2) A3, Z = 4, F(000) = 824, Dx = 2.57 g cm-3, lambda(Mo K alpha) = 0.71073 A, mu = 90.79 cm-1, T = 296 K, R = 0.024 for 360 unique reflections having I greater than sigma I. The single type of nickel ion is coordinated by six water-molecule O atoms, each at an observed distance of 2.061 (2) A, in an almost regular octahedral array. The single type of bromate ion has an observed Br--O bond length of 1.655 (2) A and O--Br--O bond angle 104.25 (9) degrees. Both the nickel-oxygen complex and the bromate ion were found to manifest rigid-body behavior. The Ni--O distance corrected for rigid-body motion is 2.065 A, while the corrected Br--O bond length is 1.663 A. Location and refinement of the two inequivalent H atoms permitted a detailed analysis of the hydrogen bonding, which occurs principally between the oxygen octahedron and the bromate groups. This structure is isomorphic to the structures of hexaaquanickel(II) chlorate and hexaaquacobalt(II) bromate which have been reported recently from this laboratory.

Bromates↗
PubMed1984

Acute bromate poisoning associated with renal failure and deafness presenting as hemolytic uremic syndrome.

A case of bromate-induced acute renal failure (ARF) in an infant associated with hemolysis, thrombocytopenia and deafness is presented. The initial clinical and laboratory features suggested the diagnosis of hemolytic uremic syndrome (HUS). The serum bromide level was in the nontoxic range (1.2 mg/dl). However, further investigation of the ingested material revealed the toxic agent to be bromate rather than bromide. The spectrum of bromate (BrO3-) toxicity is different from bromide (Br-) and includes the induction of ARF and deafness. This combined with clinical evidence of behavioral regression and speech loss led to detection of deafness in this patient and confirmed the diagnosis of bromate toxicity.

Acute Kidney Injury↗
PubMed2006

An elderly patient with severe acute renal failure due to sodium bromate intoxication.

Accidental or deliberate ingestion of bromate solution has been reported in pediatric as well as adult cases; however there have been no reports of such intoxication in the elderly. We report a 78-year-old woman who suffered severe acute renal failure due to the accidental ingestion of sodium bromate solution. The patient was successfully treated with hemodialysis therapy and renal function recovered without hearing loss. This case suggests that emergency therapeutic measures, including hemodialysis, should be taken as soon as possible, and the rapid removal of bromate is essential to prevent severe intoxication and its sequelae. To the best of our knowledge this is the first report of an elderly patient that demonstrates the clinical benefit of hemodialysis therapy for bromate intoxication.

Acute Kidney Injury↗
PubMed2002

[Determination of trace level of bromate and perchlorate in drinking water by ion chromatography with microwave preconcentration].

A simple sample preconcentration technique for the determination of trace level of bromate and perchlorate in drinking water with ion chromatography is presented. With the hydrophobic anion-exchange column and a sodium hydroxide eluent in linear gradient, bromate and perchlorate can be determined in a single injection within 35 min. Prior to ion chromatographic analysis, the drinking water sample was treated with the OnGuard Ag cartridge to remove the superfluous chloride and concentrated in 20-fold with poly(tetrafluoroethylene)(PTFE) beaker in a domestic microwave oven in 15 min. The recoveries of the analytes are better than 90%. The detection limits for bromate, perchlorate, iodate and chlorate were 0.10 microgram/L, 0.20 microgram/L, 0.11 microgram/L and 0.21 microgram/L, respectively. The developed method is applicable for the quantitation of bromate and perchlorate in real drinking water samples.

Bromates↗
PubMedDate not supplied

The use of electrodialysis to prepare aqueous bread extracts for bromate determination by chemiluminescence.

A cleanup procedure based on electrodialysis is described for the preparation of aqueous bread extracts for bromate determination by chemiluminescence. The technique utilizes electrophoresis with 3 chambers separated by semipermeable membranes. The relative merits of reverse osmosis (RO), ultrafiltration, and nanofiltration membranes with various molecular weight cutoffs were evaluated. The best results were obtained with an RO membrane manufactured from thin-film (composite) polysulfone as support for polyamide. A 0.14 M sodium sulfate solution in the center or collection chamber provides optimum conductivity. Aqueous hydroxylamine sulfate (30 mM) was selected for the anode compartment as a reductant for the anode oxidation products. The constant current mode at 150 mA with a potential of ca 100 volts was used. After electrophoretic separation, the bromate concentration in the collection chamber was typically 2 to 3 times greater than the concentration in the bread extract. The chemiluminescent reaction of bromate with sulfite with hydrocortisone as the enhancer was selected for detection of bromate. The emission, with a wavelength maximum at 575 nm, was found to "glow" rather than "flash" after the reagents were mixed; therefore, it was possible to optimize the light collection period. The method was validated with a variety of commercial bread products. White bread, hot dog buns, hamburger rolls, and a multigrain bread from 7 different manufacturers were studied.

Bread↗
PubMed1999

Analysis of 500-ng/l levels of bromate in drinking water by direct-injection suppressed ion chromatography coupled with a single, pneumatically delivered post-column reagent.

In July 1997, the US Environmental Protection Agency (EPA) began sampling and analyzing drinking water matrices from US municipalities serving populations greater than 100,000 for low-level bromate (> 0.20 microgram/l) in support of the Information Collection Rule (ICR) using the selective anion concentration (SAC) method. In September 1997, EPA published Method 300.1 which lowered the Method 300.0 bromate method detection limit (MDL) from 20.0 to 1.4 micrograms/l. This paper describes the research conducted at the EPA's Technical Support Center laboratory investigating a single post-column reagent, o-dianisidine (ODA), which has been successfully coupled to EPA Method 300.1 to extend the MDL for bromate. Initial studies indicate that this method offers a MDL which approaches the EPA's SAC method with the added benefit of increased specificity, shortened analysis time and reduced sample preparation. The method provides excellent ruggedness and acceptable precision and accuracy with a bromate MDL in reagent water of 0.1 microgram/l, and a method reporting limit of 0.50 microgram/l.

Borates↗
PubMed2006

Uncatalyzed reactions in the classical Belousov-Zhabotinsky system. 2. The malonic acid-bromate reaction in acidic media.

The title reaction was studied with various techniques in 1 M sulfuric acid, a usual medium for the oscillatory Belousov-Zhabotinsky (BZ) reaction. It was found to be a more complex process than the bromomalonic acid (BrMA)-BrO3- reaction studied previously in the first part of this work. Malonic acid (MA) can react with acidic bromate by two parallel mechanisms. The main aim of the present research was to determine the mechanisms, the rate laws, and the rate constants for these parallel channels. In one reaction channel the first molecular products are glyoxalic acid (GOA) and CO2 while in the other channel mesoxalic acid (MOA) is the first molecular intermediate, that is, no CO2 is formed in this step. To prove these two independent routes specific colorimetric techniques were developed to determine GOA and MOA selectively. The rate of the GOA channel was determined by following the rate of the carbon dioxide evolution characteristic for this reaction route. In this step, regarding it as an overall process, one MA is oxidized to GOA and CO2 and one BrO3- is reduced to HOBr, which forms BrMA with another MA. The initial rate of the GOA channel is a bilinear function of the initial MA and BrO3- concentrations with a second-order rate constant k(GOA)= 2.4 x 10(-7) M(-1) s(-1). The rate of the other channel was calculated from the rate of the BrO3- consumption measured in separate experiments, assuming that the measured depletion is a sum of two separate terms reflecting the consumptions due to the two independent channels. In the MOA channel one MA is oxidized to MOA and one BrO3- is consumed while another MA is brominated as in the GOA channel. It was found that the initial rate of the MOA channel is also a bilinear function of the MA and BrO3- concentrations with a second-order rate constant k(MOA)= 2.46 x 10(-6) M(-1) s(-1). Separate chemical mechanisms are suggested for both channels. In all of the various bromate-substrate reactions of these mechanisms oxygen atom transfer from the bromate to the substrate occurs generating bromous acid intermediate. This can be of high importance in BZ systems as bromous acid is the autocatalytic intermediate there. GOA and MOA also can be oxidized by acidic bromate but a study of these reactions will be published later.

Journal Article↗
PubMed2006

New experimental data and mechanistic studies on the bromate-dual substrate-dual catalyst batch oscillator.

The bromate-hypophosphite-acetone-Mn(II)-Ru(bpy)(3)(2+) batch oscillator was recently suggested for studying two-dimensional pattern formation. The system meets all major requirements that are needed for generation of good quality traveling waves in a thin solution layer. The serious drawback of using the system for studying temporal and spatial dynamical phenomena is its unknown chemical mechanism. In order to develop a mechanism that explains the observed long-lasting batch oscillations the bromate-hypophosphite-acetone-Mn(II)-Ru(bpy)(3)(2+) oscillator was revisited. We studied the dynamics both in the total system and in some composite reactions, and kinetic measurements were carried out in three subsystems. From the new experimental results we concluded that the two oscillatory sequences observed in the full system are originated from two oscillatory subsystems, the Mn(II)-catalyzed bromate-hypophosphite-acetone and the Ru(bpy)(3)(2+)-catalyzed bromate-bromoacetone reactions. Here we propose a mechanism which is capable of simulating the dynamical features that appeared in the complex system.

Journal Article↗
PubMed2004

Determination of bromate and chlorinated haloacetic acids in bottled drinking water with chromatographic methods.

Disinfection by-products of interest such as bromate, chlorate and chlorinated haloacetic acids in 10 representative brands of bottled drinking water were investigated with ion chromatography. With the developed method, the detection limits of the disinfection by-products were in sub-microgl(-1) level. It was observed that bromate, chlorate and dichloroacetic acid could be detected in some water samples. In the bottled natural water, the concentrations for the three compounds were 0.1, 0.9 and 0.6 microgl(-1), respectively. The total concentration of disinfection by-products in the natural water sample was the highest among all the bottled drinking waters. The concentrations for the sum of disinfection by-products in the four types of bottled drinking water investigated were natural water > mineral water > spring water > purified water. The generation of disinfection by-products was much influenced by the original components and process procedure of the source water. The concentrations of bromate and chlorate in the bottled water samples hardly degraded with the increasing storage time. For dichloroacetic acid, with the prolonging of storage time, the concentration was much decreased.

Acetates↗
PubMed2005

Chloride interference in the determination of bromate in drinking water by reagent free ion chromatography with mass spectrometry detection.

Bromate, a well known by-product of the ozonation of drinking water, has been included among the substances which have to be monitored in the drinking water according to the last EC Directive 251/98 on potable water with a regulated limit of 10 microg l(-1). The need of performing routine analysis at this limit is a driving force for the developing of new simple and sensitive methods of detection, which should be also able to overcome the effect of matrix composition. This work explored the use of mass spectrometry detection with electrospray ionisation hyphenated to a reagent free ion chromatograph with hydroxide gradient elution for the determination of bromate in drinking water. The use of a high capacity hydroxide selective column operated in gradient mode allowed to avoid the interference by carbonate peak, which moved to longer retention times. The effect of increasing chloride concentrations from 0 to 250 mg l(-1), which is the guideline limit for drinking water in Directive 251/98/EC, was to decrease absolute mass spectrometric response and chromatographic efficiency and, on the consequence, to increase the effective detection limits. The effect of the chloride concentration on the detection of bromate is discussed.

Bromates↗
PubMed2006

A drinking water utility's perspective on bromide, bromate, and ozonation.

Application of ozone in drinking water treatment plants in the US is growing because of ozone's multiple benefits. Ozone functions as a powerful oxidizing agent and disinfecting agent, it improves finished water quality by reducing turbidity, it reduces the formation of many halogenated disinfection by-products, and it is capable of treating chlorine resistant organisms like cryptosporidia. However, when bromide ion is present, e.g. from the geology, runoff, or sea water intrusion, ozone will convert some of the bromide to bromate depending upon the treatment reaction conditions. Bromate can also be introduced into drinking water as a contaminant in the chlorine used for disinfection. The current maximum contaminant level (MCL) in the USA is 0.010 mg/L, and the maximum contaminant level goal (MCLG) is zero, because of the possibility that bromate may function as a genotoxic carcinogen. The level of the MCL, especially if it is lowered, will significantly impact the ability of many water suppliers to utilize ozone in their water treatment processes and also raise the costs of those applications.

Bromates↗
PubMed2004

Impact of a magnetic ion exchange resin on ozone demand and bromate formation during drinking water treatment.

The objective of this research was to examine the impact of a magnetic ion exchange resin (MIEX) on ozone demand and bromate formation in two different ozonated waters at bench scale. The first raw water had a high bromide ion concentration, a high ozone demand, and was highly colored. Based on experimental findings from the first water, the second water was selected as a model water in which more controlled experiments were performed. The waters were treated with the MIEX resin using jar test procedures to find the optimal MIEX dosage based upon the removal of ultraviolet (UV)-absorbing substances, dissolved organic carbon (DOC), and bromide. The optimal resin dosage was chosen for bulk MIEX treatment and subsequent ozonation in a semi-batch reactor. The ozone demand and formation of bromate were analyzed as a function of ozone dosage and dissolved ozone concentration for the MIEX pre-treated water, and compared to the results obtained by ozonating the water without MIEX pre-treatment. The results indicate that pre-treatment of the water with the MIEX resin significantly reduces total organic carbon, DOC, UV absorbance, color, and to some extent, bromide. MIEX pre-treatment of the water prior to ozonation substantially lowered the ozone demand and formation of bromate during subsequent ozonation.

Bromates↗
PubMed2001

Use of ion chromatography with post-column reaction for the measurement of tribromide to evaluate bromate levels in drinking water.

A user-friendly ion chromatography method in conjunction with a post-column reaction (PCR) achieves practical quantitation limits for the oxyhalides bromate and chlorite of 0.05 microg/l and 0.10 microg/l, respectively. This level of measurement allows for the accurate assessment of bromate contributed to finished drinking waters that have been chlorinated using sodium hypochlorite. The target sensitivity of oxyhalides in the presence of other major ion species typically found in drinking water is achieved by PCR using excess bromide under acidic conditions to form a tribromide species that is detected by ultraviolet spectrometry. The method setup involves non-hazardous materials, as opposed to other recently developed methods that employ somewhat hazardous chemicals for generating the reaction necessary for the detection of bromate at sub-microg/l levels. No pretreatment of the samples is required, other than filtration and quenching of oxidant residual.

Bromates↗
PubMed1998

New, sensitive and selective method for determining sub-microgram/l levels of bromate in drinking water.

Health effects studies suggest that bromate should be regulated at 0.5 microgram/l or less in drinking water. Accordingly, an analytical method is needed to quantify this contaminant with great sensitivity and selectivity. Past efforts to do this have focused on pre-concentration ion chromatographic (IC) separation followed by suppressed conductivity detection. Interfering chloride was removed by passing samples over a silver resin which increased sample analysis time to almost 1 h. In this paper, a new method which uses IC separation with no pre-treatment followed by a post-column reaction to produce tribromide (Br3-) from bromate, is applied to the analysis of a variety of aqueous samples. The tribromide ion is detected by UV absorbance at 267 nm. This method is very sensitive for bromate with a limit of quantitation of 0.2 microgram/l and is also very selective. Common anions typically separated by IC exhibit no interference, even at the levels normally found in drinking water.

Bromates↗
PubMed1999

Ion chromatographic determination of bromate in drinking water by post-column reaction with fuchsin.

Bromate deriving from ozonation treatment of bromide containing waters are analyzed by ion-exchange chromatography with spectrophotometric detection after post-column reaction with fuchsin in low pH medium. An anion-exchange column was used with 2.7 mM carbonate-0.3 mM hydrogencarbonate eluent. The eluent from the column was then allowed to react with a SO2-reduced fuchsin solution and then with a diluted HCl solution at 65 degrees C. The developed colour of the final product was measured spectrophotometrically at 530 nm. Linearity was checked up to 50 micrograms/l with a 200-microliter injection loop (r2 = 0.9997) and up to 100 micrograms/l of bromate with 100 microliters loop (r2 = 0.9939). Nitrate, sulfate, bromide, phosphate, fluoride did not interfere at 100 mg/l concentration level; only nitrite at concentration levels greater than 3 mg/l caused partial overlapping with bromate peak, but this value is not likely to occur in common drinking water. The detection limit (3 sigma) is 0.1 microgram/l (1 microgram/l propagation error approach).

Bromates↗
PubMed1998

S-(1,2-dichlorovinyl)-L-cysteine-induced dedifferentiation and p53 gene mutations in LLC-PK1 cells: a comparative investigation with S-(2-chloroethyl)cysteine, potassium bromate, cis-platinum and styrene oxide.

Exposure of cultured renal (LLC-PK1) cells for 7 weeks to non-cytotoxic concentrations of S-(1,2-dichlorovinyl)-L-cysteine had resulted in the induction of morphologically and biochemically dedifferentiated clones, which retained their altered properties after removal of the chemical. In this study we investigated by polymerase chain reaction-single strand conformational polymorphism (PCR-SSCP) analysis and direct sequencing if S-(1,2-dichlorovinyl)-L-cysteine-induced LLC-PK1 clones display mutations in the p53 gene in comparison with wild-type clones. In addition, the characteristics of S-(1,2-dichlorovinyl)-L-cysteine-induced clones were compared with clones induced by carcinogens/metabolites of carcinogens with different mechanisms of action: (i) The potent alkylating agent and bacterial mutagen chloroethylcysteine, the key metabolite of the carcinogen dichloroethane; (ii) potassium bromate, a nephrocarcinogen inducing reactive oxygen species, which give rise to the formation of 8OHdG and DNA strand-breaks; (iii) cis-platinum, a bifunctional cross-linking agent and strand-break inducer and (iv) styrene oxide, the main intermediate metabolite of styrene, an epoxide whose carcinogenicity is thought to be based on cytotoxicity. Three essential markers of the physiological integrity and renal tubule origin of the wild-type LLC-PK1 cells were disrupted in all chemical-derived clones: (i) the polarisation of the plasma membrane into a luminal and basolateral part; (ii) the sodium-dependent glucose uptake and (iii) the pH-dependent ammonia production. Compared with the wild-type clones, poly(ADP-ribosyl)ation, a posttranslational modification of nuclear proteins, was clearly increased in clones induced by S-(1,2-dichlorovinyl)-L-cysteine, potassium bromate and cis-platinum. These clones displayed also band shifts of p53 exon 7, indicating mutations, which were confirmed by sequencing: a double mutation consisting of a base substitution followed by one base insertion in the case of S-(1,2-dichlorovinyl)-L-cysteine and potassium bromate and a base substitution in the case of cis-platinum. The base insertions both lead to the formation of the stop codon UGA resulting in loss of protein function.

Ammonia↗
PubMed2004

Assessing the effectiveness of ozonation followed by GAC filtration in removing bromate and assimilable organic carbon.

Bromate (BrO3-) and assimilable organic carbon (AOC) removal by activated carbon after ozonation is a subject of concern, since BrO3- and AOC are commonly found in the ozonation of bromide-containing and organic-rich waters. In batch ozonation experiment of this study, the major ozonation by-products were bromate, bromform, aldehydes, and AOC, and the levels of these by-products is affected by operational parameters of ozonation. Results from rapid small-scale column tests (RSSCT) indicated that the granular activated carbon (GAC) capacity for BrO3- removal was dependent on the GAC type and empty bed contact time (EBCT). The GAC with a high number of basic groups and higher pH(pzc) values showed an increased BrO3- removal capacity. On the other hand, BrO3- removal was improved by increasing EBCT. In the GAC pilot plant, a GAC column (operating with 15 min EBCT) preloads for 12 months achieved a BrO3-, and AOC removal range from 7-96% and 41-85%, respectively. And the BrO3- amount removed was found to be proportional to the influent BrO3- concentration. However, the capacity of GAC for bromate adsorption apparently decreased with prolonged operational time (after 3 months). This may be a result of the bacterial biomass adsorbed on the GAC surface hindering BrO3- reduction by GAC either by blocking pores or adsorbing at the activated sites for BrO3- reduction.

Bromates↗