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Specific inhibition of nitrite oxidation by chlorate and its use in assessing nitrification in soils and sediments.

A method was developed to determine the ammonium oxidation rate (potential) of unenriched natural samples by measuring the nitrite produced in shaken slurries. Addition of chlorate to the samples prevented nitrite from being oxidized to nitrate. The effectiveness and specificity of chlorate were tested with pure cultures of nitrite and ammonium oxidizers, as well as in soil and sediment slurries. It was concluded that chlorate had relatively little inhibitory effect on ammonium oxidation. However, under some conditions chlorate was not completely effective in blocking nitrite oxidation, and the causes of this were investigated. The technique was designed to check for incomplete blockage.

Journal Article↗

Identification and characterization of a chlorate-resistant mutant of Arabidopsis thaliana with mutations in both nitrate reductase structural genes NIA1 and NIA2.

Mutant plants defective in the assimilation of nitrate can be selected by their resistance to the herbicide chlorate. In Arabidopsis thaliana, mutations at any one of nine distinct loci confer chlorate resistance. Only one of the CHL genes, CHL3, has been shown genetically to be a nitrate reductase (NR) structural gene (NIA2) even though two NR genes (NIA1 and NIA2) have been cloned from the Arabidopsis genome. Plants in which the NIA2 gene has been deleted retain only 10% of the wild-type shoot NR activity and grow normally with nitrate as the sole nitrogen source. Using mutagenized seeds from the NIA2 deletion mutant and a modified chlorate selection protocol, we have identified the first mutation in the NIA1 NR structural gene. nia1, nia2 double mutants have only 0.5% of wild-type shoot NR activity and display very poor growth on media with nitrate as the only form of nitrogen. The nia1-1 mutation is a single nucleotide substitution that converts an alanine to a threonine in a highly conserved region of the molybdenum cofactor-binding domain of the NR protein. These results show that the NIA1 gene encodes a functional NR protein that contributes to the assimilation of nitrate in Arabidopsis.

Alleles↗

Severe chlorate poisoning: report of a case.

A case of severe sodium chlorate poisoning was observed within 5 h after suicidal ingestion of 150-200 g of the herbicide. Methaemoglobinaemia was the early symptom of the intoxication. Treatment with methylene blue and ascorbic acid could not prevent a massive haemolysis with disseminated intravascular coagulation. Hypercoagulation and hyperfibrinolysis could be treated successfully with exchange transfusions, heparin and fresh plasma. During the first hours, 70 mmol chlorate were excreted before complete renal failure occurred which required haemodialysis for several weeks. Clinical observations and in vitro experiments provide evidence that methylene blue is effective only in the very early stages of chlorate poisoning. Consequently, the following treatment is suggested: gastric lavage, exchange transfusion, bicarbonate infusion, haemodialysis, anticoagulation with heparin and substitution of clotting factors if necessary.

Adult↗

Nif-hybrids of Enterobacter: selection for nif gene integration with chlorate.

The nif gene group from Klebsiella can be transferred into Enterobacter cloacae by conjugation using Escherichia coli donor cells carrying the composite self-transmissible nif-plasmid pRD1. A small fraction of the hybrids obtained is stable upon prolonged passaging without selection. Their stability is due to integration of pRD1 into the chromosome. Such integration hybrids were chlorate resistant, and nitrate reductase negative, which indicated that integration preferentially occurred within one of the genes for the production or functioning of this enzyme. Chlorate resistance could, therefore, be used to select for additional nitrate reductase-negative sublines with pRD1 in their chromosome. Such sublines have been analyzed further for the presence of nif genes, other pRD1 markers, and for stability. In all except one the complete plasmid seems to have been integrated. Some tend to revert to nitrate utilisation (chlorate sensitivity).

Chlorates↗

Characterization of purified nitrate reductase A and chlorate reductase C from Proteus mirabilis.

Nitrate reductase A has been solubilized from purified cytoplasmic membranes by extraction with tert-amyl alcohol. The resulting aqueous solution contained monomeric reductase which polymerized slowly to dimers and tetramers with sedimentation coefficients of respectively 10.5, 16 and 23 Svedbergunits. The polymerization could be stopped to some extent by addition of a small amount of Triton X-100. These distinct entities of nitrate reductase A were separable on electro-focusing, DEAE-column chromatography and polyacrylamide gel electrophoresis, and have been proved to consist of similar subunits with molecular weights of 104000, 63000, and 56000 daltons. The molecular weights of monomeric nitrate reductase A was found to be about 240000 daltons. Chlorate reductase C has been solubilized by a similar procedure, resulting in only monomeric enzyme. Chlorate reductase C exhibited a sedimentation coefficient of 7.7 Svedbergunits, an isoelectric point of pH = 4.55 and a molecular weight of approx. 180000 daltons. It was found to consist of three subunits with molecular weights of 75000, 63000 and 56000 daltons. The latter two subunits are most probably common in nitrate reductase A and chlorate reductase C.

Centrifugation, Density Gradient↗

The correlation between the protein composition of cytoplasmic membranes and the formation of nitrate reductase A, chlorate reductase C and tetrathionate reductase in Proteus mirabilis wild type and some cholate resistant mutants.

Three genotypically different chlorate resistant mutants, chl I, chl II and chl III, appeared to lack completely nitrate reductase A, chlorate reductase C and tetrathionate reductase activity. Fumarate reductase is only partially affected in chl I and chl III and unaffected in chl II. Formate dehydrogenase is only partially diminished in chl II, hydrogenase is diminished in chl I and chl II and completely absent in chl III. Subunits of nitrate reductase A, chlorate reductase C and tetrathionate reductase have been identified in protein profiles of purified cytoplasmic membranes from the wild type and the three mutant strains, grown under various conditions. Only the presence and absence of the largest subunits of these enzymes appeared to be correlated with their repression and derepression in the wild type membranes. On the cytoplasmic membranes of the chl I and chl III mutants these subunits lack for the greater part. In the chl II mutant, however, these subunits are inserted in the membrane all together after anaerobic growth with or without nitrate. A model for the repression/derepression mechanism for the reductases has been proposed. It includes repression by cytochrome b components, whereas the redox-state of the nitrate reductase A molecule itself is also involved in its derepression under anaerobic conditions.

Anaerobiosis↗

Chlamydomonas reinhardtii strains expressing nitrate reductase under control of the cabII-1 promoter: isolation of chlorate resistant mutants and identification of new loci for nitrate assimilation.

The Chlamydomonas reinhardtii strain Tx11-8 is a transgenic alga that bears the nitrate reductase gene (Nia1) under control of the CabII-1 gene promoter (CabII-1-Nia1). Approximately nine copies of the chimeric CabII-1-Nia1 gene were found to be integrated in this strain and to confer a phenotype of chlorate sensitivity in the presence of ammonium. We have used this strain for the isolation of spontaneous chlorate resistant mutants in the presence of ammonium that were found to be defective at loci involved in MoCo metabolism and light-dependent growth in nitrate media. Of a total of 45 mutant strains analyzed first, 44 were affected in the MoCo activity (16 Nit(-), unable to grow in nitrate, and 28 Nit(+), able to grow in nitrate). All the Nit(-) strains lacked MoCo activity. Diploid complementation of Nit(-), MoCo(-) strains with C. reinhardtii MoCo mutants and genetic analysis indicated that some strains were defective at known loci for MoCo biosynthesis, while three strains were defective at two new loci, hereafter named Nit10 and Nit11. The other 28 Nit(+) strains showed almost undetectable MoCo activity or activity was below 20% of the parental strain. Second, only one strain (named 23c(+)) showed MoCo and NR activities comparable to those in the parental strain. Strain 23c(+) seems to be affected in a locus, Nit12, required for growth in nitrate under continuous light. It is proposed that this locus is required for nitrate/chlorate transport activity. In this work, mechanisms of chlorate toxicity are reviewed in the light of our results.

Animals↗

Inhibition of pro-cholecystokinin (CCK) sulfation by treatment with sodium chlorate alters its processing and decreases cellular content and secretion of CCK 8.

Pro-cholecystokinin (CCK) has three sulfated tyrosine residues. Sulfation of the tyrosine residue in CCK 8 is known to be important for its activity at CCK A receptors. The role of these sulfated tyrosines in the sorting and processing of pro-CCK was examined by treatment of CCK-secreting rat thyroid medullary carcinoma cells with 10 nM sodium chlorate (a non-toxic inhibitor of tyrosine sulfation). This treatment caused a 50% decrease in the cellular content of immunoreactive CCK and an 80% decrease in its secretion. Sephadex G-50 chromatography of cellular extracts and culture media showed a selective depletion of CCK 8. There was a comparative sparing of CCK 33 and larger molecular forms in cellular extracts which was not observed in the media. These results suggest that the sulfation of the tyrosines of pro-CCK is clearly important for the correct sorting and/or processing of pro-CCK. The pattern of immunoreactive CCK peptides seen with chlorate treatment is consistent with the substrate specificity of a recently identified putative CCK cleaving enzyme and suggests that unsulfated pro-CCK is not efficiently processed to CCK 8 in vivo. The large decrease in CCK content and secretion observed with sodium chlorate may also be due to inefficient sorting of unsulfated pro-CCK into secretory vesicles.

Animals↗

Short-comings of irgasan ticarcillin chlorate broth for the enrichment of Yersinia enterocolitica biotype 2, serotype 9 from meat.

Recovery of Yersinia enterocolitica serotype 0:9 from artificially contaminated minced pork with the enrichment medium irgasan ticarcillin chlorate broth (ITC) was poor. This was due to the lower growth rate of this serotype in comparison with serotype 0:3. Tests on the behaviour of serotype 0:3 and 0:9 towards some selective agents in ITC broth showed that the minimal inhibitory concentration of chlorate was much lower for serotype 0:9 than for serotype 0:3. Omitting chlorate in the ITC enrichment stimulated the growth of pure cultures. Reduction of MgCl2 and malachite green to 80% of the original concentration further increased the growth, so that after 48 h of incubation similar counts (10(7)-10(8) cfu/ml) as for serotype 0:3 were obtained.

Animals↗

Methods for the stable isotopic analysis of chlorine in chlorate and perchlorate compounds.

Chlorate and perchlorate compounds, used as herbicides, solid fuel propellants, and explosives, are increasingly recognized as pollutants in groundwater. Stable isotope characterization would permit both environmental monitoring of extent of remediation and forensic characterization. Stoichiometric reduction to chloride (greater than 98% yield), by Fe(II) for chlorate and alkaline fusion-decomposition for perchlorate, allows analysis by standard methods to give highly reproducible and accurate delta37Cl results (0.05/1000, 2 x standard error). Analysis of various compounds from different suppliers yielded delta37Cl values for chlorate samples near to +0.2/1000 (SMOC), but one has within-sample heterogeneity of 0.5/1000, possibly due to crystallization processes during manufacture. Results for perchlorate samples also are generally near +0.2/1000, but one is +2.3/1000 (SMOC). The initial results suggest that both forensic and environmental applications might be feasible.

Chlorates↗

Determination of chlorate and chlorite and mutagenicity of seafood treated with aqueous chlorine dioxide.

The use of chlorine dioxide (ClO(2)) as a potential substitute for aqueous chlorine to improve the quality of seafood products has not been approved by regulatory agencies due to health concerns related to the production of chlorite (ClO(2)(-)) and chlorate (ClO(3)(-)) as well as possible mutagenic/carcinogenic reaction products. Cubes of Atlantic salmon (Salmo salar) and red grouper (Epinephelus morio) were treated with 20 or 200 ppm aqueous chlorine or ClO(2) solutions for 5 min, and extracts of the treated fish cubes and test solutions were checked for mutagenicity using the Ames Salmonella/microsome assay. No mutagenic activity was detected in the treated fish samples or test solutions with ClO(2). Only the sample treated with 200 ppm chlorine showed weak mutagenic activity toward S. typhimurium TA 100. No chlorite residue was detected in sea scallops, mahi-mahi, or shrimp treated with ClO(2) at 3.9-34.9 ppm. However, low levels of chlorate residues were detected in some of the treated samples. In most cases, the increase in chlorate in treated seafood was time- and dose-related.

Animals↗

Cholorate toxicity in Aspergillus nidulans: the selection and characterisation of chlorate resistant mutants.

Mutation in at least ten genes can result in chlorate reistance in Aspergillus nidulans. Mutation in seven of these genes also results in the inability to use nitrate as nitrogen source. The various classes of resistant mutant obtained occur in different proportions, depending on whether or not a mutagenic treatment is employed, and also on which nitrogen source is used for selection. The prinicipal effect of mutagen arises because mutations in the niaD gene, the nitrate reductase structural gene, are relatively much commoner when no mutagen is used than after treatment with N-methyl-N'-nitro-N-nitrosoguanidine. This may be connected with the finding that deletions involving the niaD gene are relatively more common among samples of spontaneous niaD mutants. Some of these deletions extend to the neighbouring niiA gene, the structural gene for nitrite reductase. The selection procedures used were designed to avoid bias in favour of any particular chlorate resistant phenotype. Even if biases existed however, these could not account for the variation found from nitrogren source to nitrogen source in the proportions of certain resistant classes having apparently identical chlorate resistance phenotypes.

Aspergillus nidulans↗

A mixture of ammonium perchlorate and sodium chlorate enhances alterations of the pituitary-thyroid axis caused by the individual chemicals in adult male F344 rats.

Ammonium perchlorate (AP) and sodium chlorate (SC) have been detected in public drinking water supplies in many parts of the United States. These chemicals cause perturbations in pituitary-thyroid homeostasis in animals by competitively inhibiting iodide uptake, thus hindering the synthesis of thyroglobulin and reducing circulating T(4) (thyroxine). Little is known about the short-term exposure effects of mixtures of perchlorate and chlorate. The present study investigated the potential for the response to a mixture of these chemicals on the pituitary-thyroid axis in rats to be greater than that induced by the individual chemicals. Adult male F-344 rats were exposed, via their drinking water, to the nominal concentrations of 0.1, 1.0, 10 mg/L AP or 10, 100, 1000 mg/L SC and their mixtures for 7 days. Serum T(4) levels were significantly (p < 0.05) reduced in rats following exposure to the mixtures, but not after exposure to the individual chemicals. Serum T(3) (triiodothyronine) was not altered by treatment and TSH (thyroid stimulating hormone) was only increased after the high-dose chlorate treatment. Histological examination of the thyroid gland showed colloid depletion and hypertrophy of follicular epithelial cells in high-dose single chemical and all mixture-treated rats, while hyperplasia was observed only in some of the rats treated with mixtures (AP 10 + SC 100, AP 0.1 + SC 1000, and AP 10 + SC 1000 mg/L). These data suggest that short-term exposure to the mixture of AP and SC enhances the effect of either chemical alone on the pituitary-thyroid axis in rats.

Animals↗

Low level nitrate or nitroethane preconditioning enhances the bactericidal effect of suboptimal experimental chlorate treatment against Escherichia coli and Salmonella Typhimurium but not Campylobacter in swine.

An experimental chlorate product that targets the respiratory nitrate reductase enzyme of bacteria such as Salmonella and Escherichia coli has shown promising results in reducing concentrations of these bacteria in the gut of food animals. Because expression of the target enzyme is induced by nitrate, we administered short-duration, low level nitrate or nitroethane preconditioning treatments to finishing swine to see if these would enhance the ability of an experimental chlorate product to kill these bacteria. Results from these studies showed that preconditioning the gut microflora of swine with low levels of nitrate or nitrocompounds enhanced (more than tenfold) the ability of the chlorate product to kill Salmonella and E. coli, but not Campylobacter. Further studies are needed before these compounds can be fed as feed additives to animals, although it is likely that nitrate preconditioning may be more near to market than the nitrocompounds, which may require more comprehensive review by regulatory authorities.

Animal Feed↗

Metabolic primers for detection of (Per)chlorate-reducing bacteria in the environment and phylogenetic analysis of cld gene sequences.

Natural attenuation of the environmental contaminant perchlorate is a cost-effective alternative to current removal methods. The success of natural perchlorate remediation is dependent on the presence and activity of dissimilatory (per)chlorate-reducing bacteria (DPRB) within a target site. To detect DPRB in the environment, two degenerate primer sets targeting the chlorite dismutase (cld) gene were developed and optimized. A nested PCR approach was used in conjunction with these primer sets to increase the sensitivity of the molecular detection method. Screening of environmental samples indicated that all products amplified by this method were cld gene sequences. These sequences were obtained from pristine sites as well as contaminated sites from which DPRB were isolated. More than one cld phylotype was also identified from some samples, indicating the presence of more than one DPRB strain at those sites. The use of these primer sets represents a direct and sensitive molecular method for the qualitative detection of (per)chlorate-reducing bacteria in the environment, thus offering another tool for monitoring natural attenuation. Sequences of cld genes isolated in the course of this project were also generated from various DPRB and provided the first opportunity for a phylogenetic treatment of this metabolic gene. Comparisons of the cld and 16S ribosomal DNA (rDNA) gene trees indicated that the cld gene does not track 16S rDNA phylogeny, further implicating the possible role of horizontal transfer in the evolution of (per)chlorate respiration.

Amino Acid Sequence↗

Assimilatory nitrate reductase in a chlorate-resistant mutant of Escherichia coli.

Nitrate reductase was investigated in extracts from cells of a chlorate-resistant mutant strain of E. coli which grew anaerobically on nitrate as the sole source of nitrogen. The nitrate reductase was of particulate nature and reduced chlorate like the nitrate reductase from the wild strain, but in contrast was inhibited only weakly by azide or cyanide. Nitrate reductase activity was found in extracts from the mutant cells grown on nitrate as the sole source of nitrogen, but not in extracts from cells grown in complex nutrient medium. Addition of ammonia also caused a decrease in activity. Accordingly, the nitrate reductase in the chlorate-resistant mutant is of the assimilatory type.

Ammonia↗

Isolation and characterization of a chlorate-resistant mutant of Spirulina platensis.

Three chlorate-resistant mutants of the cyanobacterium Spirulina platensis were obtained by UV irradiation and one of them (LL1) was further characterized for its nutritional requirements and for the capacity to reduce nitrate in vivo and in vitro. The results indicate that mutation leading to chlorate resistance is not due to inactivation of nitrate reductase but is most likely due to the loss of permeability to chlorate and nitrate. The other two mutants seem to have properties similar to those of LL1.

Chlorates↗

Effects of pulp mill chlorate on Baltic Sea algae.

The long-term effects of pulp mill chlorate on different algal species of the Baltic Sea were studied in land-based model ecosystems simulating the littoral zone. Brown algae (Phaeophyta) exhibited an extraordinarily high sensitivity to chlorate and pulp mill effluents containing chlorate. All brown algal species ceased growth or showed major signs of toxicity at all concentrations tested, down to microgram per litre levels. EC50 levels for growth of Fucus vesiculosus were about 80-100 microg ClO3- litre(-1). Blue-green algae (Cyanophyta) were not deleteriously affected nor were green algae (Chlorophyta). The perennial and annual species of red algae (Rhodophyta) were also unaffected by the effluents. Diatoms did not show any sensitivity and phytoplankton (fresh- and brackish water) were particularly insensitive. A phanerogam, Zostera marina was also unaffected by the treatments.

Journal Article↗