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Kinetics and mechanisms of aqueous ozone reactions with bromide, sulfite, hydrogen sulfite, iodide, and nitrite ions.

Reactions of ozone with Br(-), SO(3)(2-), HSO(3)(-), I(-), and NO(2)(-), studied by stopped-flow and pulsed-accelerated-flow techniques, are first order in the concentration of O(3)(aq) and first order in the concentration of each anion. The rate constants increase by a factor of 5 x 10(6) as the nucleophilicities of the anions increase from Br(-) to SO(3)(2-). Ozone adducts with the nucleophiles are proposed as steady-state intermediates prior to oxygen atom transfer with release of O(2). Ab initio calculations show possible structures for the intermediates. The reaction between Br(-) and O(3) is accelerated by H(+) but exhibits a kinetic saturation effect as the acidity increases. The kinetics indicate formation of BrOOO(-) as a steady-state intermediate with an acid-assisted step to give BrOH and O(2). Temperature dependencies of the reactions of Br(-) and HSO(3)(-) with O(3) in acidic solutions are determined from 1 to 25 degrees C. These kinetics are important in studies of annual ozone depletion in the Arctic troposphere at polar sunrise.

Journal Article↗

Role of sulfite additives in wine induced asthma: single dose and cumulative dose studies.

BACKGROUND: Wine appears to be a significant trigger for asthma. Although sulfite additives have been implicated as a major cause of wine induced asthma, direct evidence is limited. Two studies were undertaken to assess sulfite reactivity in wine sensitive asthmatics. The first study assessed sensitivity to sulfites in wine using a single dose sulfited wine challenge protocol followed by a double blind, placebo controlled challenge. In the second study a cumulative dose sulfited wine challenge protocol was employed to establish if wine sensitive asthmatics as a group have an increased sensitivity to sulfites. METHODS: In study 1, 24 asthmatic patients with a strong history of wine induced asthma were screened. Subjects showing positive responses to single blind high sulfite (300 ppm) wine challenge were rechallenged on separate days in a double blind, placebo controlled fashion with wines of varying sulfite levels to characterise their responses to these drinks. In study 2, wine sensitive asthmatic patients (n=12) and control asthmatics (n=6) were challenged cumulatively with wine containing increasing concentrations of sulfite in order to characterise further their sensitivity to sulfites in wine. RESULTS: Four of the 24 self-reporting wine sensitive asthmatic patients were found to respond to sulfite additives in wine when challenged in a single dose fashion (study 1). In the double blind dose-response study all four had a significant fall in forced expiratory volume in one second (FEV(1)) (>15% from baseline) following exposure to wine containing 300 ppm sulfite, but did not respond to wines containing 20, 75 or 150 ppm sulfite. Responses were maximal at 5 minutes (mean (SD) maximal decline in FEV(1) 28.7 (13)%) and took 15-60 minutes to return to baseline levels. In the cumulative dose-response study (study 2) no significant difference was observed in any of the lung function parameters measured (FEV(1), peak expiratory flow (PEF), mid phase forced expiratory flow (FEF(25-75))) between wine sensitive and normal asthmatic subjects. CONCLUSIONS: Only a small number of wine sensitive asthmatic patients responded to a single dose challenge with sulfited wine under laboratory conditions. This may suggest that the role of sulfites and/or wine in triggering asthmatic responses has been overestimated. Alternatively, cofactors or other components in wine may play an important role in wine induced asthma. Cumulative sulfite dose challenges did not detect an increased sensitivity to sulfite in wine sensitive asthmatics and an alternative approach to identifying sulfite/wine sensitive asthma may be required.

Adult↗

Sulfite enhancement of diolepoxide mutagenicity: the role of altered glutathione metabolism.

Sulfur dioxide is a cocarcinogen for benzo[a]pyrene in the respiratory tract of rats and hamsters. Sulfur dioxide exists under physiological conditions as the sulfite ion. Sulfite enhances the mutagenic potency of (+-)-7r,8t-dihydroxy-9t,-10t- epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (anti-BPDE) and 7r,8t-dihydroxy-9c10c-epoxy-7,8,9,10-tetrahydrobenzo[a]py ren e (syn-BPDE) in Salmonella typhimurium strains TA98 and TA100. This enhancement of diolepoxide mutagenicity is observed with sulfite concentrations between 1 and 20 mM, and the concentration dependence is identical for the two diolepoxides. Half-maximal enhancement of mutagenicity occurs at approximately 5 mM sulfite. Sulfite is neither toxic nor mutagenic to the bacteria under these conditions. The enhancement of diolepoxide mutagenicity requires that the bacteria be exposed to sulfite prior to the addition of the diolepoxide. Simultaneous addition of sulfite and diolepoxide significantly decreases the enhancing effect, and addition 15 min after the diolepoxide virtually abolishes the effect. This is consistent with sulfite serving to increase the efficiency of processes leading to DNA modification by the diolepoxides, rather than some effect subsequent to DNA adduct formation. Direct evidence for this hypothesis was provided by determining the effect of sulfite on mutagenicity and DNA binding in TA98 using [3H]anti-BPDE. Exposure of the bacteria to 10 mM sulfite for 5 min prior to the addition of the labeled mutagen led to as much as 170% increase in DNA binding levels relative to parallel incubations without sulfite. Corresponding increases in mutagenicity were seen as well. As sulfite can affect the glutathione/glutathione-S-transferase systems, the primary cellular defense against BPDE, the effect of sulfite on these pathways in Salmonella was determined. When strain TA98 was treated with N-acetoxy-2-acetamidofluorene, a direct-acting mutagen not scavenged by glutathione, prior addition of 10 mM sulfite to the bacteria had no effect on resultant viability or mutagenicity. Assessment of the bacterial glutathione levels revealed that 10 mM sulfite treatment results in an 82% decrease in the concentration of the cosubstrate. We were, however, unable to detect diolepoxide-glutathione conjugates in any of our incubations. Moreover, the presence of sulfite leads to significant trapping of the diolepoxide in the form of sulfonate derivatives. Based on these data, we conclude that the depletion of glutathione does indeed play a role in the enhancement of diolepoxide mutagenicity in S. typhimurium.(ABSTRACT TRUNCATED AT 400 WORDS)

7,8-Dihydro-7,8-dihydroxybenzo(a)pyrene 9,10-oxide↗

Simultaneous recording of calcium transients and reactive oxygen intermediates of human polymorphonuclear granulocytes in response to formyl-Met-Leu-Phe and the environmental agent sulfite.

BACKGROUND: Human polymorphonuclear granulocytes (PMN) are an essential component in the immunological defense network against a variety of harmful pathogens. We have studied the effects of the airborne pollutant sulfite on the calcium metabolism and respiratory burst of these cells simultaneously. METHODS: A flow cytometric method was developed using the fluochromes Indo-1 and DHR-123. This method allowed us to investigate the real-time kinetics of intracellular free calcium and reactive oxygen intermediates in viable cells with a temporal resolution of 1 s over a time course of 17 min. An additional feature was the possibility to discriminate between reacting and nonreacting cells after treatment with defined stimuli, thus gaining additional insight into the behavior of cell subpopulations. RESULTS: We analyzed the effects of sulfite on PMN before and after stimulation with formyl-Met-Leu-Phe (FMLP). Treatment with sulfite alone (0.001-1 mM) caused a small, nontransient increase in intracellular calcium. Preincubation with sulfite reduced the maximal calcium response elicited by FMLP. A significant increase in steady-state calcium levels after stimulation with FMLP was observed after treatment with sulfite in concentrations of 10 and 100 mM. Regarding the respiratory burst, treatment with sulfite alone in concentrations of 0.001-1 mM induced a significant increase in DHR-123-derived fluorescence, whereas concentrations of 5 and 10 mM caused a significant depression of this fluorescence below baseline values. Sulfite caused a maximal twofold increase of DHR-123-derived fluorescence compared with the FMLP response. Similar results were obtained after preincubation with sulfite before treatment with FMLP, showing that the effect of sulfite on the respiratory burst was additive to the FMLP response. Regarding the fractions of responding cells, treatment with sulfite up to 1 mM induced a concentration-dependent increase of burst-reactive PMN, whereas preincubation before stimulation with FMLP showed no correlation between sulfite concentration and fraction of burst-reacting cells. CONCLUSIONS: By simultaneous registration of [Ca(2+)](i) and [H(2)O(2)](i) of PMN after treatment with FMLP and sulfite, the essential responses were already observed within a short time interval (15 min). Striking differences were found in the response of calcium as second messenger and respiratory burst in PMN treated with sulfite. Until a critical concentration (0. 5-1 mM), sulfite caused a concentration-dependent increase of [H(2)O(2)](i), in addition to the FMLP-induced response. The [Ca(2+)](i) changes induced by sulfite alone, however, were found to be small and showed no correlation with the respiratory burst response.

Air Pollutants↗

Elevated levels of serum sulfite in patients with chronic renal failure.

Sulfite, a well known air pollutant, is toxic for humans, especially those with sulfite hypersensitivity. Sulfite is also generated endogenously, during normal metabolism of sulfur-containing amino acids. Mammalian tissues contain the enzyme sulfite oxidase, which detoxifies both endogenous and exogenous sulfite by oxidation to sulfate. Deficiency of sulfite oxidase in humans is fatal, demonstrating its physiologic importance. Nevertheless, information about serum and tissue levels of sulfite in normal and pathologic conditions is limited. Using a sensitive HPLC assay, it is shown here that sera from patients with chronic renal failure (CRF) contain significantly higher amounts of sulfite than those from healthy subjects. Mean +/- SD of serum sulfite in healthy subjects (n = 20) was 1.55 +/- 0.54 microM, whereas those in patients under maintenance hemodialysis (HD patients; n = 44) and CRF patients before introducing dialysis therapy (pre-HD patients; n = 33) were 3. 23 +/- 1.02 microM (P < 0.01) and 3.80 +/- 3.32 microM (P < 0.01), respectively. Among pre-HD patients, serum sulfite was positively correlated with serum creatinine (r = 0.714, P < 0.0001), and negatively with serum albumin (r = -0.407, P = 0.0188), hematocrit (r = -0.524, P = 0.0017), and total cholesterol (r = -0.375, P = 0. 0318). There was no significant association between sulfite and patient age, gender, or leukocyte counts. Multiple regression analysis revealed serum creatinine as the sole independent predictor of serum sulfite levels. Each HD treatment was associated with approximately 27% reduction in serum sulfite levels, suggesting the presence of a dialyzable form in serum. Thus, these results indicate that reduced glomerular filtration is a factor that determines serum sulfite levels. Chronic elevation in serum sulfite levels might contribute to tissue or organ dysfunction in patients with CRF.

Aged↗

Tryptic cleavage of rat liver sulfite oxidase. Isolation and characterization of molybdenum and heme domains.

Treatment of rat liver sulfite oxidase with trypsin leads to loss of ability to oxidize sulfite in the presence of cytochrome c as electron acceptor. Ability to oxidize sulfite with ferricyanide as acceptor is undiminished, while sulfite leads to O2 activity is partially retained. Gel filtration of the proteolytic products has led to the isolation of two major fragments of dissimilar size derived from sulfite oxidase. The smaller fragment has a molecular weight of 9500 and appears to be monomeric when detached from sulfite oxidase. It contains the heme in its cytochrome b5 structure, has no sulfite oxidase activity, and is reducible with dithionite but not with sulfite. The heme fragment can mediate electron transfer between pig liver microsomal NADH cytochrome b5 reductase and cytochrome c. The larger fragment has a molecular weight of 47,400 under denaturing conditions but elutes from Sephadex G-200 as a dimer. It contains no heme but retains all of the molybdenum and the modified sulfite-oxidizing capacity present in the proteolytic mixture. All of the EPR properties of the molybdenum center of native sulfite oxidase are retained in the molybdenum fragment. The molybdenum center is a weak chromophore with an absorption sectrum suggestive of coordination with sulfur ligands. Reduction by sulfite generates a spectrum attributable to molybdenum (V). Spectra of oxidized and sulfite-reduced preparations are sensitive to anions and pH. NH2-terminal analysis of native sulfite oxidase and the two tryptic fragments has permitted the conclusion that the sequence represented by the heme fragment is the NH2 terminus of native enzyme. These studies have demonstrated that the two cofactor moieties of sulfite oxidase are contained in distinct domains which are covalently held in contiguity by means of an exposed hinge region. Isolation of functional heme and molybdenum domains of sulfite oxidase after tryptic cleavage has demonstrated conclusively that the cytochrome b5 region of the molecule is required for electron transfer to the physiological acceptor, cytochrome c.

Animals↗

The role of tyrosine 343 in substrate binding and catalysis by human sulfite oxidase.

In the crystal structure of chicken sulfite oxidase, the residue Tyr(322) (Tyr(343) in human sulfite oxidase) was found to directly interact with a bound sulfate molecule and was proposed to have an important role in mediating the substrate specificity and catalytic activity of this molybdoprotein. In order to understand the role of this residue in the catalytic mechanism of sulfite oxidase, steady-state and stopped-flow analyses were performed on wild-type and Y343F human sulfite oxidase over the pH range 6-10. In steady-state assays of Y343F sulfite oxidase using cytochrome c as the electron acceptor, k(cat) was somewhat impaired ( approximately 34% wild-type activity at pH 8.5), whereas the K(m)(sulfite) showed a 5-fold increase over wild type. In rapid kinetic assays of the reductive half-reaction of wild-type human sulfite oxidase, k(red)(heme) changed very little over the entire pH range, with a significant increase in K(d)(sulfite) at high pH. The k(red)(heme) of the Y343F variant was significantly impaired across the entire pH range, and unlike the wild-type protein, both k(red)(heme) and K(d)(sulfite) were dependent on pH, with a significant increase in both kinetic parameters at high pH. Additionally, reduction of the molybdenum center by sulfite was directly measured for the first time in rapid reaction assays using sulfite oxidase lacking the N-terminal heme-containing domain. Reduction of the molybdenum center was quite fast (k(red)(Mo) = 972 s(-1) at pH 8.65 for wild-type protein), indicating that this is not the rate-limiting step in the catalytic cycle. Reduction of the molybdenum center of the Y343F variant by sulfite was more significantly impaired at high pH than at low pH. These results demonstrate that the Tyr(343) residue is important for both substrate binding and oxidation of sulfite by sulfite oxidase.

Animals↗

Sulfite-dependent mutagenicity of benzo[a]pyrene derivatives.

Benzo[a]pyrene (BP) and sulfur dioxide (SO2) are ubiquitous air pollutants and are also components of tobacco smoke. Although SO2 itself is not carcinogenic, concurrent administration with BP results in enhancement of respiratory tract tumorigenesis. In biological systems, SO2 exists as its hydrated form, sulfite (SO3(2-) ). Sulfite readily undergoes autoxidation, generating potent oxidant species. When 7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene (BP-7,8-diol) is included in sulfite autoxidation mixtures it is converted to more polar products, most notably 7,8,9,10-tetrahydroxy-7,8,9,10-tetrahydrobenzo[a]pyrenes (BP tetraols). This implies the intermediacy of 7,8-dihydroxy-9,10-epoxy- 7,8,9,10-tetrahydro-benzo[a]pyrenes (BPDE). We report here the sulfite-dependent conversion of BP-7,8-diol to forms highly mutagenic to Salmonella typhimurium strain TA 98. This activation is observed at BP-7,8-diol concentrations of from 2 to 40 microM and at sulfite concentrations of from 0.5 to 10 mM. In the presence of 10 microM BP-7,8-diol, half-maximal activation is observed at 1.6 mM sulfite. Sulfite itself is neither toxic nor mutagenic to the bacteria under these conditions. The time course of the activation of BP-7,8-diol and its sensitivity to inhibition by antioxidants indicate a requirement for sulfite autoxidation. These data further support the sulfite-dependent epoxidation of BP-7,8-diol. Not only does sulfite convert this promutagen to its active mutagenic form, sulfite also enhances the mutagenic activity of BP diolepoxides toward the tester strain. The reversion frequency in response to 0.1-0.5 microM anti-BPDE is increased by up to 33% in the presence of 1 mM sulfite, and by up to 270% with 10 mM sulfite. The mechanism of this enhancement of anti-BPDE activity is not known, but could be related to inhibition of the glutathione-S-transferase system which has been previously reported for sulfite. These results are discussed in regard to the noted cocarcinogenicity of sulfur dioxide for BP.

Benzo(a)pyrene↗

Review of sulfite sensitivity.

The occurrence of sulfites in foods, drug products, and the environment; the characteristics of sulfite-sensitivity reactions; and the management of sulfite-sensitive individuals are reviewed. Sulfites are used in foods, beverages, and pharmaceuticals for their antioxidant properties; they are frequently used in restaurant foods to keep vegetables and fruits looking fresh. Beer, wine, and dried, canned, or frozen fruits often contain sulfites, and seafood and fried potatoes are often prepared with these agents. Sulfites are also present as pollutants in the atmosphere. The incidence of sulfite sensitivity is unknown, but the condition is being recognized with increasing frequency. Bronchospasm is sometimes induced by sulfites in sensitive individuals, and anaphylaxis and death have been reported. Immediate or delayed reactions may occur. The mechanism of toxicity is unknown but is thought to be sulfite-induced stimulation of the afferent limb of the cholinergic reflex. Clinical management is based on avoiding strenuous exercise on days when atmospheric pollution is high and on avoiding foods and drug products containing sulfites. Treatment of sulfite-sensitivity reactions is usually supportive; subcutaneous epinephrine has been effective in some patients. Several drugs have been used investigationally to prevent sulfite-sensitivity reactions. However, few data are available to evaluate their efficacy. Sulfites may induce bronchospasm and anaphylaxis in sensitive individuals. These people should avoid foods and drug products containing sulfites.

Drug Hypersensitivity↗

Determination of total serum sulfite by HPLC with fluorescence detection.

An estimated 500,000 individuals in the US, mostly steroid-dependent asthmatics, suffer severe adverse reactions to sulfites in foods, beverages, and pharmaceutical products. In an attempt to understand the pathogenesis of sulfite hypersensitivity, we have developed an assay for the determination of total serum sulfite by utilizing: (a) reductive release of serum protein-bound sulfite; (b) derivatization of free sulfite with monobromobimane; (c) separation of sulfite-bimane from thiol-bimanes by reversed-phase HPLC; and (d) quantitation of sulfite-bimane by fluorescence detection. The detection limit of this assay was 0.44 mumol/L serum sulfite. The intra- and interassay CVs for total serum sulfite at 5.4 mumol/L were 8.1% and 22.0%, respectively. The standard addition method was used to determine total serum sulfite in normal subjects. More than 70 samples were prepared in 2-3 h, followed by automated overnight analysis. The mean concentrations (+/- SD) of total serum sulfite in female (n = 41) and male (n = 35) donors were 4.63 +/- 2.33 and 5.16 +/- 2.68 mumol/L, respectively (not statistically significant: P = 0.368). The combined mean concentration of total sulfite in both sexes was 4.87 +/- 2.49 mumol/L. There was no correlation between total serum sulfite and total serum cysteine, cysteinylglycine, homocysteine, subject age, serum cobalamin, or serum folic acid. The reference range (mean +/- 2 SD) for total serum sulfite in normal subjects is 0-9.85 mumol/L.

Bridged Bicyclo Compounds↗

Plant sulfite oxidase as novel producer of H2O2: combination of enzyme catalysis with a subsequent non-enzymatic reaction step.

Sulfite oxidase (EC 1.8.3.1) from the plant Arabidopsis thaliana is the smallest eukaryotic molybdenum enzyme consisting of a molybdenum cofactor-binding domain but lacking the heme domain that is known from vertebrate sulfite oxidase. While vertebrate sulfite oxidase is a mitochondrial enzyme with cytochrome c as the physiological electron acceptor, plant sulfite oxidase is localized in peroxisomes and does not react with cytochrome c. Here we describe results that identified oxygen as the terminal electron acceptor for plant sulfite oxidase and hydrogen peroxide as the product of this reaction in addition to sulfate. The latter finding might explain the peroxisomal localization of plant sulfite oxidase. 18O labeling experiments and the use of catalase provided evidence that plant sulfite oxidase combines its catalytic reaction with a subsequent non-enzymatic step where its reaction product hydrogen peroxide oxidizes another molecule of sulfite. In vitro, for each catalytic cycle plant SO will bring about the oxidation of two molecules of sulfite by one molecule of oxygen. In the plant, sulfite oxidase could be responsible for removing sulfite as a toxic metabolite, which might represent a means to protect the cell against excess of sulfite derived from SO2 gas in the atmosphere (acid rain) or during the decomposition of sulfur-containing amino acids. Finally we present a model for the metabolic interaction between sulfite and catalase in the peroxisome.

Acid Rain↗

Characterization of a new type of sulfite dehydrogenase from Paracoccus pantotrophus GB17.

The periplasmic sulfite dehydrogenase of Paracoccus pantotrophus GB17 was purified to homogeneity by a four-step procedure from cells grown lithoautotrophically with thiosulfate. The molecular mass of native sulfite dehydrogenase was 190 kDa as determined by native gradient PAGE. SDS-PAGE showed sulfite dehydrogenase to comprise two subunits with molecular masses of 47 kDa and 50 kDa, suggesting an alpha2beta2 structure. The N-terminal amino acid sequence and immunochemical analysis using SoxC-specific antibodies identified the 47-kDa protein as the soxC gene product. SoxD-specific antibodies identified the 50-kDa protein as SoxD. Based on the molecular masses deduced from the nucleotide sequence for mature SoxC (43,442 Da) and SoxD (37,637 Da) sulfite dehydrogenase contained 1.30 mol molybdenum/mol alpha2beta2 sulfite dehydrogenase. The iron content was 3.17 mol/mol alpha2beta2 sulfite dehydrogenase, and 3.53 mol heme/mol alpha2beta2 sulfite dehydrogenase was determined by pyridine hemochrome analysis. These data are consistent with the two heme-binding domains (CxxCH), characteristic for c-type cytochromes, deduced from the soxD nucleotide sequence. Electrospray ionization revealed two masses for SoxC of 43,503 and 43,897 Da. The difference in molecular mass was attributed to the molybdenum cofactor of SoxC. For SoxD a mass of 38,815 Da was determined; this accounted for the polypeptide and two covalently bound hemes. Reconstitution of the catalytic activity of sulfite dehydrogenase required additional fractions; these eluted from Q Sepharose at 0.05, 0.25, and 0.30 M NaCl. The K(m) of sulfite dehydrogenase for sulfite was 7.0 microM and for cytochrome c 19 microM. Sulfite dehydrogenase activity was inhibited by sulfate and phosphate. The structural and catalytic properties make sulfite dehydrogenase from P. denitrificans GB17 distinct from sulfite oxidases of other prokaryotic or eukaryotic sources.

Amino Acid Sequence↗