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[Occupational exposure to toxic substances during the production of vinyl chloride and chlorinated organic solvents].

Determinations of vinyl chloride and chlorinated organic solvent concentrations at the breathing zone of the industrial workers employed at the vinyl chloride synthesis process have revealed excessive exposure to certain chlorinated compounds. The average exposures of the operators of the vinyl chloride synthesis apparatus have been found to be 13 MAC for vinyl chloride and 2.5 MAC for 1,2-dichloroethane. The operators of the solvent synthesis apparatus have been exposed to average concentrations of carbon tetrachloride up to 3.5 MAC, the corresponding values for the fitters being 4.5 MAC for vinyl chloride, 3.5 MAC for 1,2-dichloroethane, and 3 MAC for carbon tetrachloride.

Air Pollutants, Occupational↗

[The evaluation of the mutagenic activity of public drinking water by the Ames test].

BACKGROUND: The sources of potential mutagens in our environment are many, but the most important of these is water for public consumption. This is a result of the chlorinating process which is the main reason for the appearance of these mutagens. With this in mind, the aim of our study was to check a possible mutagenic activity, using the Ames test, in organic concentrates taken from water for public consumption in Madrid. METHODS: Several bacterial strains were used, namely Salmonella histidine dependent TA1535, TA1538, TA98 and TA100, taken originally from Salmonella typhimurium LT2. Each test was performed twice, with or without the introduction of the mammalian-microsome activation (S9 mix), as per the indications in Ames. The plate incorporation assay was used to test the mutagenicity. All samples of the water in question were processed and treated so as to create concentrates of organic chlorinated compounds. RESULTS: The highest levels of mutagenicity appeared in the TA1535 strain and in the tests where the microsome fraction was not used (IM = 1.94). CONCLUSIONS: With regard to mutagenic evaluation in organic concentrates taken from water for public consumption, no positive activity was found in any of the tester strains.

Analysis of Variance↗

Dichloroacetic acid: metabolism in cytosol.

Dichloroacetic acid (DCA) arises from the chlorination of drinking water and the metabolism of trichloroethylene (TRI) and is used therapeutically. The toxicity of TRI exposure is dependent on metabolism, and DCA has been proposed to be one contributor to this toxicity. Beyond the identification of some metabolites of DCA and some pharmacokinetic studies, little is known about the tissue distribution and enzymology of DCA metabolism. We present data that indicate that DCA degradation occurs primarily in the cytosol. Low molecular weight components of cytosol are required for the reaction, including nicotinamide cofactor and glutathione (GSH). GSH plays a role in the removal of DCA from cytosol, although not through transferase-mediated conjugation. In rat cytosol, the KM is approximately 0.3 mM, and the apparent Vmax approximates 12 nmoles/min/mg cytosolic protein. These results set DCA apart from other chlorinated compounds that are metabolized by the cytochrome P450 enzyme family.

Animals↗

Concentrations of polychlorinated biphenyls and chlorinated pesticides in human breast milk--a case study.

Concentrations of chlorinated pesticides (p,p'-DDE, lindane), hexachlorobenzene (HCB), sum of polychlorinated biphenyls (PCBs), and PCB congeners in breast milk during lactation and the distribution of the chlorinated compounds in fat tissue, blood serum and breast milk were pursued in five primi- or secundipara from the hinterland of a clinic of gynaecology and obstetrics in Brno in 1993. Capillary gas chromatography with ECD detection was used for the determination of the residues. The concentrations of HCB, lindane, p,p'-DDe, and sum of PCBs ranged from 42.5 to 238.4, from < 1.0 to 7.4 from 231.4 to 557.6, and from 661.3 to 2888.9 micrograms.kg-1 of milk fat, respectively. Seventeen PCB congeners were screened, of which 11 were identified in most of the milk samples (IUPAC numbers 28, 101, 118, 126, 128, 138, 153, 156, 170, 180, 194). Congeners 138, 153, 170, and 180 were the most abundant and their concentrations in microgram.kg-1 of milk fat ranged from 122.9 to 501.0 for 153, from 103.4 to 372.1 for 138, from 66.1 to 407.9 for 180, from 26.8 to 183.1 for 170, and from 10.0 to 41.7 for 118.

Adipose Tissue↗

Contaminated site remedial investigation and feasibility removal of chlorinated volatile organic compounds from groundwater by activated carbon fiber adsorption.

Groundwater contaminated by dense, non-aqueous phase liquids (DNAPLs) such as chlorinated solvents has become a serious problem in some regions of Taiwan. The sources of these contaminants are due to industrial discharges. These chlorinated volatile organic compounds (VOCs) have been proven to be carcinogenic to humans. The groundwater is used for domestic drinking water supply in some cities of Taiwan and the severely contaminated groundwater has to be treated in order to meet the requirement of drinking water standards. This study covers two areas of work. In the first part, polluted groundwater samples were collected from the contaminated site and analytical results indicated measurable concentrations of 12 representative chlorinated VOCs in water samples. The primary VOCs detected included trichloroethene (TCE), tetrachloroethene (PCE), 1,1,2-trichloroethane (1,1,2-TCA), and 1,1-dichloroethene (1,1-DCE). Second, to remove VOCs groundwater was treated using adsorption on activated carbon fiber (ACF). This involved pumping groundwater through vessels containing ACF. Most VOCs, including TCE, PCE, 1,1,2-TCA, and DCE, were readily adsorbed onto ACF and are removed from the water stream. Our study showed that the technology was able to significantly reduce chlorinated VOCs concentrations in groundwater.

Adsorption↗

The fate of chlorinated volatile organic compounds in aeration basins using recirculated aeration: a pilot-plant evaluation.

The fate of chloroform, which was chosen to represent chlorinated volatile organic compounds sometimes found in publicly owned wastewater treatment works, has been followed in a pilot aeration basin utilizing aeration recirculation. Tests were conducted using real wastewaters spiked with two different concentration levels of chloroform and operated at conditions similar to those of a large-scale aeration basin of the Mill Creek Wastewater Treatment Plant in Cincinnati, Ohio. Aeration recirculation levels of 0, 25, 50, and 75% were used to evaluate the concept that aeration recirculation can be an effective method of reducing the release of these toxic compounds to the atmosphere. Data obtained demonstrated that the concentration of chloroform in the off-gas increased as the recirculation ratio increased, but that the total mass emission rate to the atmosphere decreased due to the decreased off-gas volumetric flow rate. Biodegradation in the pilot plant increased by 183% for the 75% recirculation level compared to 0% recirculation. Mass balance analysis results indicated that 60% of chloroform emissions could be reduced with 75% recirculation ratio with little or no effect of dissolved oxygen concentration.

Air↗

Modeling the cytochrome P450-mediated metabolism of chlorinated volatile organic compounds.

Comparative molecular field analysis (CoMFA), a three-dimensional quantitative structure-activity relationship (3D-QSAR) paradigm, has been used to analyze the metabolic rates, as intrinsic clearance, of a series of chlorinated volatile organic compounds (VOCs). A comparison between 3D-QSAR and conventional Hansch-type QSAR is provided. To develop predictive 3D-QSARs for metabolism, the standard CoMFA model based on steric and electrostatic potential fields must be supplemented with hydropathic and molecular orbital information also in the form of three-dimensional fields. A mechanistic interpretation of chlorinated VOC metabolism by cytochrome P450 isozymes is provided as a rationalization for the inclusion of multiple fields in the CoMFA 3D-QSAR model. Models of this type have practical utility in the development of generalized physiologically-based pharmacokinetic models, as well as the rational, structure-based, design and/or selection of compounds for use in the in vivo and in vitro metabolic studies.

Cytochrome P-450 Enzyme System↗

Determination of chlorinated volatile organic compounds in water and municipal wastewater using headspace-solid phase microextraction-gas chromatography.

The aim of this work was to develop a fast and simple analytical method for the determination of 14 chlorinated volatile organic compounds (VOCs) in water and wastewater samples. Headspace-solid-phase microextraction (HS-SPME) and gas chromatography (GC) were used for the determination of the VOCs. The extraction parameters were investigated in order to optimize the HS-SPME-GC method. The quality parameters of the method were also investigated.

Chromatography, Gas↗

Impact of transition metals on reductive dechlorination rate of hexachloroethane by mackinawite.

Mackinawite, an iron monosulfide, has been shown to be a potential reductant for chlorinated organic compounds under anaerobic conditions. Chlorinated organic compounds are often found with inorganic contaminants. This study investigates the impact of various transition metals on the reductive dechlorination by mackinawite using a readily degradable chlorinated organic compound, hexachloroethane (HCA). Different classes of transition metals show distinct patterns in their impact on the HCA dechlorination: 10(-3) M Cr(III) and Mn(II) (hard metals) decreased the dechlorination rates, while 10(-4), 10(-3), and 10(-2) M Co(II), Ni(II), Cu(II), Zn(II), Cd(II), and Hg(II) (intermediate/soft metals) increased the rates. The tested hard metals, due to their weak affinity for sulfides, are thought to form surface precipitates of hydroxides around FeS under the experimental conditions with these hydroxides hindering the electron transfer between FeS and HCA. Due to their high affinity for sulfides, however, the tested intermediate/soft metals can react with FeS in various ways: precipitation of pure metal sulfides (MS), formation of metal-substituted FeS by lattice exchange, and coprecipitation of the mixed sulfides in a Fe-M-S system. Fe(II), released as a result of the interaction of FeS with intermediate/soft metals, enhances the HCA dechlorination at the doses of 10(-4) and 10(-3) M through sorbed or dissolved Fe(II) species, while Fe(OH)2(s) formed at the higher dose of 10(-2) M also enhances the reductive dechlorination. Rate increases observed in Co(II)-, Ni(II)-, and Hg(II)-amended systems are not simply explained by the formation of pure MS; instead, metal-substituted FeS or coprecipitated sulfides are thought to be responsible for the significantly increased rates observed in these systems.

Anthelmintics↗

[Activation mechanisms in chlorinated aliphatic compounds/experimental possibilities and clinical significance (author's transl)].

Chemical reactivity, biotransformation and toxic effects of chlorinated aliphatic compounds are decisively determined by type and number of chlorine substitutions. In saturated compounds, chlorine substitution exerts a destabilization; metabolic reactions are free radical formation and dechlorination or dehydrochlorination, respectively, under formation of olefins. In saturated alkenes, Cl-substitution leads to a stabilization of the olefinic double bond. Biotransformation of this class of compounds starts with epoxidation. The epoxides are prone, among other reactions, to intramolecular rearrangement; more stable aldehydes or acid chlorides are formed. In the series of chlorinated ethylenes, the rearrangement mechanisms have been studied systematically in vitro and in vivo. As judged from the identified metabolites there is accordance in vitro and in vivo, with one important exception: trichloroethylene. The only formation of chloral in vivo may be due to a catalysis by the iron in P450. In a modified Ames test system the unsymmetrically substituted chlorinated ethylenes are found mutagenic (tri-,1,1-dichloroethylene and vinyl chloride), whereas symmetrically substituted molecules are inactive. The reason for this is seen in the high instability of the unsymmetric molecules caused by the electron withdrawal effect of chlorine.

Animals↗

Reduction of chlorinated ethanes by nanosized zero-valent iron: kinetics, pathways, and effects of reaction conditions.

Nanosized iron (< 100 nm in diameter) was synthesized in the laboratory and applied to the reduction of eight chlorinated ethanes (hexachloroethane (HCA), pentachloroethane (PCA), 1,1,2,2-tetrachloroethane (1,1,2,2-TeCA), 1,1,1,2-tetrachloroethane (1,1,1,2-TeCA), 1,1,2-trichloroethane (1,1,2-TCA), 1,1,1-trichloroethane (1,1,1-TCA), 1,2-dichloroethane (1,2-DCA), and 1,1-dichloroethane (1,1-DCA)) in batch reactors. Reduction of 1,1,1-TCA increased linearly with increasing iron loading between 0.01 and 0.05 g per 124 mL solution (0.08-0.4 g/L). Varying initial concentrations of PCA between 0.025 and 0.125 mM resulted in relatively constant pseudo-first-order rate constants, indicating PCA removal conforms to pseudo-first-order kinetics. The reduction of 1,1,2,2-TeCA decreased with increasing pH; however, dehydrohalogenation of 1,1,2,2-TeCA became important at high pH. All chlorinated ethanes except 1,2-DCA were transformed to less chlorinated ethanes or ethenes. The surface-area-normalized rate constants from first-order kinetics analysis ranged from < 4 x 10(-6) to 0.80 L m(-2) h(-1). In general, the reactivity increased with increasing chlorination. Among tri- and tetrasubstituted compounds, the reactivity was higher for compounds with chlorine atoms more localized on a single carbon (e.g., 1,1,1-TCA > 1,1,2-TCA). Reductive beta-elimination was the major pathway for the chlorinated ethanes possessing alpha,beta-pairs of chlorine atoms to form chlorinated ethenes, which subsequently reacted with nanosized iron. Reductive alpha-elimination and hydrogenolysis were concurrent pathways for compounds possessing chlorine substitution on one carbon only, forming less chlorinated ethanes.

Chlorine Compounds↗

Rapid reductive destruction of hazardous organic compounds by nanoscale Fe0.

Fe0-mediated reductive destruction of hazardous organic compounds such as chlorinated organic compounds (COCs) and nitroaromatic compounds (NACs) in the aqueous phase is one of the latest innovative technologies. In this paper, rapid reductive degradation of COCs and NACs by synthesized nanoscale Fe0 in anaerobic batch systems was presented. The nanoscale Fe0, characterized by high specific surface area and high reactivity, rapidly transformed trichloroethylene (TCE), chloroform (CF), nitrobenzene (NB), nitrotoluene (NT), dinitrobenzene (DNB) and dinitrotoluene (DNT) under ambient conditions, which results in complete disappearance of the parent compounds from the aqueous phase within a few minutes. GC analysis reported that the main products of the dechlorination of TCE and CF were ethane and methane as well as that most of the nitro groups in NACs were reductively transformed to amine groups. These results suggest that the rapid reductive destruction by nanoscale Fe0 is potentially a viable in situ or aboveground treatment of groundwater contaminated with hazardous organic compounds including COCs and NACs.

Feasibility Studies↗