Elucidating the removal mechanism of N,N-dimethyldithiocarbamate in an anaerobic-anoxic-oxic activated sludge system.

N,N-Dimethyldithiocarbamate (DMDTC) is a typical precursor of N-nitrosodimethylamine (NDMA). Based on separate hydrolysis, sorption and biodegradation studies of DMDTC, a laboratory-scale anaerobic-anoxic-oxic (AAO) system was established to investigate the removal mechanism of DMDTC in this nutrient removal biological treatment system. DMDTC hydrolyzed easily in water solution under either acidic conditions or strong alkaline conditions, and dimethylamine (DMA) was the main hydrolysate. Under anaerobic, anoxic or oxic conditions, DMDTC was biodegraded and completely mineralized. Furthermore, DMA was the main intermediate in DMDTC biodegradation. In the AAO system, the optimal conditions for both nutrient and DMDTC removal were hydraulic retention time 8 hr, sludge retention time 20 day, mixed-liquor return ratio 3:1 and sludge return ratio 1:1. Under these conditions, the removal efficiency of DMDTC reached 99.5%; the removal efficiencies of chemical organic demand, ammonium nitrogen, total nitrogen and total phosphorus were 90%, 98%, 81% and 93%, respectively. Biodegradation is the dominant mechanism for DMDTC removal in the AAO system, which was elucidated as consisting of two steps: first, DMDTC is transformed to DMA in the anaerobic and anoxic units, and then DMA is mineralized to CO2 and NH3 in the anoxic and oxic units. The mineralization of DMDTC in the biological treatment system can effectively avoid the formation of NDMA during subsequent disinfection processes.

Application of process chemistry and SAR modelling to the evaluation of health findings of lower olefins.

Epidemiology studies show increased leukemia mortality among styrene butadiene rubber (SBR) workers but not among butadiene monomer production employees. A detailed review of the SBR manufacturing process indicates that sodium dimethyldithiocarbamate (DMDTC) introduced into the SBR manufacturing process for a period in the 1950s coincides with increased leukemia mortality. Using the Computer-Optimized Molecular Parametric Analysis of Chemical Toxicity (COMPACT), we assessed the enzyme (cytochrome P450) substrate specificity of an olefin series including 1,3-butadiene (BD) and also modeled its interaction with DMDTC. These analyses showed correlation of a structural/electronic parameter--the COMPACT radius--with the presence or absence of cytogenetic activity and also found that DMDTC would inhibit the oxidative metabolism of BD at least at high concentrations. Both DMDTC and its diethyl analog (DEDTC) bind with CYP 2E1 and CYP 2A6. Both of these isoforms are important in the initial oxidative metabolism of butadiene and other olefins. In co-exposure studies in mice of DMDTC with BD or with epoxybutene (EB), we found that there was a reduced increase in genotoxic activity based on micronuclei induction compared with BD or EB exposure alone. Treatment with DMDTC significantly increased the protein carbonyl contents of hepatic microsomes compared with that of controls, a finding that may be related to DMDTC's activity as a prooxidant. Co-exposure with DMDTC and EB increased hepatic microsomal carbonyls to levels significantly greater than those of DMDTC-treated mice, while EB administration in the absence of DMDTC did not change protein carbonyls relative to those of controls. The increase in hepatic microsomal protein carbonyls suggests that DMDTC may modulate EB metabolism towards the formation of reactive intermediates that react with proteins. The present molecular modeling and mechanistic studies suggest that co-exposure of BD and DMDTC is a plausible biological hypothesis regarding increased leukemia risk among SBR workers.

The influence of co-exposure to dimethyldithiocarbamate on butadiene metabolism.

Treatment of rats and mice with a single oral dose of dimethyldithiocarbamate (DMDTC; 250 mg/kg) had a marked effect on hepatic CYP2E1 and aldehyde dehydrogenase activities, measured in vitro, for up to 24 h after dosing. The same treatment did not affect CYP2A6, glutathione S-transferase, epoxide hydrolase, alcohol dehydrogenase activities or hepatic glutathione levels. As a consequence of the loss of CYP2E1 activity, butadiene metabolism in liver fractions from DMDTC treated rats and mice was markedly reduced, as was the metabolism of the mono-epoxide to the di-epoxide in mouse liver. The conversion of the mono-epoxide to the diol by epoxide hydrolases was not affected by DMDTC treatment. Urinary excretion of radioactivity, following dosing with DMDTC and exposure to 200 ppm C-14 butadiene for 6 h, was markedly reduced in rats, but increased in mice. The profiles of urinary metabolites were qualitatively similar from mice exposed to butadiene to those exposed after dosing with DMDTC. In the rat, pre-dosing with DMDTC resulted in the formation of three additional urinary metabolites following exposure to butadiene. Overall, DMDTC appears to impact qualitatively and quantitatively on the metabolism of butadiene. The nature and full significance of these changes has yet to be characterised.

Resistance of Rhizobium strains to phygon, spergon, and thiram.

Strains of Rhizobium meliloti, Rhizobium sp. nodulating cowpeas, and R. phaseoli derived from cultures susceptible to tetramethylthiuram disulfide (thiram), 2,3-dichloro-1,4-naphthoquinone (phygon), and 2,3,5,6-tetrachloro-p-benzoquinone (spergon), respectively, grew in the presence of high concentrations of the fungicides and converted them to products not toxic to the sensitive rhizobia. The results of chemical assays demonstrated that the pesticides were destroyed by the resistant bacteria but not by the susceptible parent rhizobia. Resting cells of thiram-metabolizing R. meliloti formed large quantities of dimethyldithiocarbamate, dimethylamine, and CS2 from the pesticide. The products were characterized by gas and thin-layer chromatography, colorimetric reactions, and ultraviolet spectrometry. Dimethylamine and CS2 were formed spontaneously from dimethyldithiocarbamate, but the yield was higher in the presence of R. meliloti. The phygon-resistant bacterium converted the fungicide to five metabolites and thereby rendered the chemical nontoxic to a test fungus. The resistant strain of R. phaseoli generated at least one organic product and released about one-third of the chlorine during its detoxication of spergon.