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Rain and surface water samples from Southern Germany were investigated from 1991 to 1995 for terbuthylazine and one of its major metabolites, deethylterbuthylazine. The concentrations observed were compared to the concentrations found for atrazine and deethylatrazine in the same water samples. Concentrations ranged from < 0.02 μg/L to 0.7 μg/L for terbuthylazine and from < 0.02 μg/L to 0.6 μg/L for deethylterbuthylazine, compared to concentrations of < 0.02 μg/L to 3 μg/L and < 0.02 μg/L to 0.5 μg/L for atrazine and deethylatrazine, respectively. The ratios of metabolite concentrations to parent compound concentrations were calculated for deethylterbuthylazine to terbuthylazine (DTR) and deethylatrazine to atrazine (DAR). In rain water, DTR of 0.8…3.0 and DAR of 0.3… 1.9 were determined with mean values of 0.9… 1.7 for DTR and 0.6…0.9 for DAR in the different years. The ratios increased during summer periods. The highest ratios were observed in samples from forest stands, showing that degradation of the herbicide has occurred during transport between the source and the sampling site. The DTR in rain water were about 50… 100% higher than the DAR. This indicates a higher degradation rate of terbuthylazine during atmospheric transport. In surface water, DTR of 0.3… 1.2 with mean values of 0.5…0.8 and DAR of 0.2…2.2 with mean values of 0.2… 1.3 were observed. The ratios increased from June to September. 相似文献
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Harmful Algal Blooms caused by the marine ichthyotoxic dinoflagellate Cochlodinium polykrikoides are responsible for mass mortalities of wild and farmed fish worldwide. In this research, we investigated the cytotoxic mechanisms of aqueous extract of C. polykrikoides on isolated Rainbow trout (Oncorhynchus mykiss) liver hepatocytes. Algal extract exposure with isolated trout hepatocytes caused hepatocyte membrane lysis, reactive oxygen species (ROS) formation, glutathione depletion, lysosomal membrane rupture, collapse of mitochondrial membrane potential, ATP depletion and increase in ADP/ATP ratio, cytochrome C release into the hepatocyte cytosol, and activation of caspases cascade. Anti-oxidants, free radical scavengers, mitochondrial permeability transition (MPT) pore sealing agents, microsomal oxidases inhibitors, ATP generators and lysosomotropic agents protected fish hepatocytes against C. polykrikoides. Fish hepatocyte toxicity was also associated with mitochondrial and lysosomal membrane injury. These events caused cytochrome C release from the mitochondrial intra-membrane space into cytosol. The cytochrome C release could trigger activation of caspase-3 and apoptosis. 相似文献
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With the method used here, it was possible to determine the isotope content of both the initial compounds and their metabolites formed due to microbial degradation. The chemical analysis showed that the dominating degradation metabolite for both PCE and TCE degradation was cis-1,2-dichloroethene (cis-1,2-DCE). Apart from this, the formation of TCE, trans-1,2-DCE, 1,1-DCE, chloroethene (VC), ethene and ethane was observed. The isotope analysis showed no measurable fractionation of stable carbon isotopes, for the microbial degradation of PCE and TCE to cis-1,2-DCE. There was a small effect for trans-1,2-DCE and a stronger one for VC as metabolite of TCE. 相似文献
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Determination of Atrazine, Terbutylazine and their Deethyl- and Hydroxymetabolites in Soil by SFE and HPLC/UV-DAD The supercritical fluid extraction (SFE) (CO2 and CH3OH as modifier) of the herbicides atrazine and terbutylazine as well as their deethyl- and hydroxymetabolites from soil was investigated. The analytes were determined after extraction by HPLC/UV-DAD using a C18 column. The limits of detection of the chromatographic step were between 0.01 μg/mL and 0.07 μg/mL, the relative standard deviations between 0.8% and 1.4%. With the aid of a control chart, the stability of the chromatographic system was evaluated. For extraction, soil was spiked with 5 μg/g for each component. For SFE, CO2 and methanol as modifier were used, and a pressure program was applied. Beside SFE, Soxhlet extraction with methanol and a solid-liquid extraction with acetone/water by shaking were carried out. For chlorine-containing triazines, the recovery rates were comparable for all extraction methods. The following recovery rates for SFE were obtained: deethylterbutylazine 77.4%, terbutylazine 80.2%, deethylatrazine 87.4%, atrazine 92.6%. However, the recovery rates for the hydroxymetabolites (4.1% for hydroxyatrazine, 21% for hydroxyterbutylazine) were not satisfying compared with the “classical” methods of extraction (above 50%). The limits of detection for the total process (SFE and HPLC/UV-DAD) estimated by the signal to noise ratio amounted 0.08 μg/g soil for chlorine-containing derivates, for hydroxyatrazine 2…3 μg/g, and for hydroxyterbutylazine 0.8 μ/g. 相似文献
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Biodegradation of the Photolysis Products of FeIIIEDTA Ethylenediaminetetraacetate (EDTA) is not biodegraded by activated sludge from a wastewater treatment plant. This work shows that after photolysis of FeIIIEDTA, easily degradable metabolites are formed. The OECD Test 302 B yielded a 53% bioelimination with a sunlight irradiation time of 6.5 hours followed by a 4-week incubation. After 20 hours of sunlight irradiation, EDTA is bioeliminated to 92%. One of the photolytic degradation products, ethylenediaminediacetate (EDDA), has been quantitatively eliminated within 14 days following a lag-phase of 2 weeks. The photolysis of the iron complexes of the phosphonates ATMP and DTPMP did not result in biologically degradable metabolites. With these results, the environmental impact of EDTA can be re-evaluated emphasizing the amount and fate of FeIIIEDTA in the environment. FeIIIEDTA was found to be present in effluents of wastewater treatment plants at fractions from 20 to 90% of the total EDTA. FeIIIEDTA has a half life of about 2 hours in sunlit waters. Complexes of EDTA with other metals do not exchange with iron and are photostable. Therefore, EDTA behaves like 2 different compounds: – FeIIIEDTA undergoes fast photolysis with biodegradation of the metabolites. – The other metal-EDTA complexes are persistent in the environment. Ecological arguments against the use of EDTA are therefore still valid for all EDTA-complexes except the one of Fe(III). However, Fe(III) complexes with the phosphonates ATMP and DTPMP do not exhibit such favorable properties over other metal-complexes, and so all arguments against the use of phosphonates are still valid. 相似文献
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Carla G. B. Brenner Carlos A. Mallmann Daniel R. Arsand Francieli M. Mayer Ayrton F. Martins 《洁净——土壤、空气、水》2011,39(1):28-34
In this work, an analytical methodological study was carried out to determine the antimicrobials sulfamethoxazole and trimethoprim, as well as their metabolites, in hospital effluent. The determinations were conducted by liquid chromatography tandem mass spectrometry using a hybrid triple quadrupole‐linear ion trap mass spectrometer (LC‐QqLIT‐MS). The data acquisition was made in selected reaction monitoring (SRM) mode, in which two SRM transitions were monitored to ensure that the target compounds were accurately identified by the information dependent acquisition (IDA) function. The limits of detection (LOD) and quantification (LOQ) were 0.25 and 0.80 µg L?1 for sulfamethoxazole and 0.15 and 0.50 µg L?1 for trimethoprim. The linear range for the SMX was 0.8–100.0 µg L?1 and TMP was 0.5–100.0 µg L?1 on the basis of six‐point calibration curves generated by means of linear regression analysis. The coefficients of the correlation were higher than 0.999, which ensured the linearity of the method. The average concentration of sulfamethoxazole and trimethoprim found in hospital effluent was 27.8 and 6.65 µg L?1, respectively. The analytical methodology employed allowed two metabolites to be identified, N4‐acetyl‐sulfamethoxazole and α‐hydroxy‐trimethoprim. Fragmentation pathways were proposed. 相似文献
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Alkylated polycyclic aromatic hydrocarbons (alkyl-PAHs) are the predominant form of PAHs in oil, comprising 85–95% of total PAHs. However, little attention has been paid to these chemicals in ecological risk assessment of marine oil spill. A comparative study of the toxic effects of phenanthrene and retene (7-isopropyl-1-methylphenanthrene, an alkyl-phenanthrene) on the early life stage of marine medaka (Oryzias melastigma) was conducted. Results showed that retene was significantly more toxic than phenanthrene, and marine medaka could be more sensitive to retene than some freshwater fishes. Retene had a higher excretion rate than phenanthrene during the larvae stage. Both of compounds resulted in developmental malformation of marine medaka embryos, with phenanthrene affecting on peripheral vascular system and yolk sac, while retene affecting on cardiac tissues. The toxicity of phenanthrene might be mainly related to its anesthetic effects, and that of retene might be related to the CYP1A-mediated toxicity of its metabolites. 相似文献