Polychlorinated biphenyls-containing electrical insulating oil contaminated soil treatment with calcium and magnesium peroxides.

Calcium and magnesium peroxides were applied for the treatment of soil contaminated by polychlorinated biphenyls-containing electrical insulating oil (Aroclor 1016). The removal of PCB-containing electrical insulating oil was achieved with the addition of either calcium peroxide or magnesium peroxide alone and dependent on dosages of the chemical. A 21-d treatment of 60% watered soil with the moderate addition (chemical/oil weight ratio of 0.005/1) of either calcium peroxide or magnesium peroxide resulted in nearly complete (96 ± 2%) oil removal, unsubstantial increase in soil pH and almost no changes in oxygen consumption and dehydrogenase activity, making it suitable for the soil decontamination.

Degradation of aroclor 1242 in a single-stage coupled anaerobic/aerobic bioreactor.

Degradation of Aroclor 1242 was studied in granular biofilm reactors with limited aeration. An aerobic biphenyl degrader, Rhodococcus sp. M5, was used to supplement a natural bacterial population present in a "bioaugmented" reactor, while the "non-bioaugmented" reactor only contained natural granular sludge. The bioaugmentation, however appeared to have no effect on the reactor performance. Aroclor measurements showed its disappearance in both reactors with only 16-19% of Aroclor recovered from the reactor biomass and effluent. Simultaneously, a chlorine balance indicated that dechlorination occurred at a specific rate of 1.43 mg PCB (g volatile suspended solids)(-1) d(-1), which was comparable to the observed rate of Aroclor disappearance. Intermediates detected in both reactors were biphenyl, benzoic acid, and mono-hydroxybiphenyls. This suggests that a near-complete mineralization of Aroclor can be achieved in a single-stage anaerobic/aerobic system due to a combination of reductive and oxidative degradation mechanisms.

Plant compounds that induce polychlorinated biphenyl biodegradation by Arthrobacter sp. strain B1B.

Plant compounds that induced Arthrobacter sp. strain B1B to cometabolize polychlorinated biphenyls (PCBs) were identified by a screening assay based on the formation of a 4,4'-dichlorobiphenyl ring fission product. A chemical component of spearmint (Mentha spicata), l-carvone, induced Arthrobacter sp. strain B1B to cometabolize Aroclor 1242, resulting in significant degradation of 26 peaks in the mixture, including selected tetra- and pentachlorobiphenyls. Evidence for PCB biodegradation included peak disappearance, formation of a phenylhexdienoate ring fission product, and chlorobenzoate accumulation in the culture supernatant. Carvone was not utilized as a growth substrate and was toxic at concentrations of greater than 500 mg liter-1. Several compounds structurally related to l-carvone, including limonene, p-cymene, and isoprene, also induced cometabolism of PCBs by Arthrobacter sp. strain B1B. A structure-activity analysis showed that chemicals with an unsaturated p-menthane structural motif promoted the strongest cometabolism activity. These data suggest that certain plant-derived terpenoids may be useful for promoting enhanced rates of PCB biodegradation by soil bacteria.

Modulation by iron of hepatic microsomal and nuclear cytochrome P450, and cytosolic glutathione S-transferase and peroxidase in C57BL/10ScSn mice induced with polychlorinated biphenyls (Aroclor 1254).

Exposure of iron-loaded C57BL/10ScSn mice to the polychlorinated biphenyls (PCBs) mixture Aroclor 1254 in the diet (0.01%) for 5 weeks caused massive hepatic porphyria far greater than occurred with PCBs alone. This regime eventually causes hepatocellular carcinoma. Hepatic microsomal ethoxy-, pentoxy-, and benzyloxyresorufin dealkylase activities (respectively EROD, PROD, and BROD) catalyzed primarily by cytochrome P4501A1 and 2B isoenzymes were markedly induced after 2 weeks of diet (when no porphyria had developed) but showed little effect of iron. EROD activity in the nuclear membrane was also induced by the PCBs as was CYP1A1 protein when shown by immunoblotting. Nuclear dealkylase activities of PCBs-treated mice were considerably less than microsomal activities but were stimulated by iron pretreatment. The mechanism of the iron-enhanced toxicity may be due to oxidative damage associated with chronic induction of CYP1A1 isoforms. Lucigenin-enhanced chemiluminescence (CL) by microsomes and nuclear membranes was used as a method to estimate their potential to form reactive oxygen species. Despite CL being induced by PCBs it was less with microsomes from iron-treated mice. In a comparison of a variety of inducers of microsomal cytochrome P450 there was no correlation between inducer, uroporphyrogenic agent, and intensity of CL. On the other hand, cytosolic glutathione S-transferase (GST) activities with 1-chloro-2,4-dinitrobenzene and 1,2-dichloro-4-nitrobenzene (DCNB) as substrates, were also induced by the PCBs mixture, the induction with DCNB being synergistically potentiated by iron pretreatment. Complementary results were observed by immunocytochemistry using anti alpha-GST antibody. In contrast, total glutathione peroxidase activity and selenium-dependent glutathione peroxidase activity were depressed by PCBs but particularly in mice also administered iron. The results illustrate that PCBs not only induce CYP1A1 in microsomes but also in the nuclear membrane, which may be of significance in the mechanism of the iron-enhanced carcinogenicity of these chemicals. The iron-enhanced induction of GST with accompanying depletion of glutathione peroxidase provides evidence for oxidative processes induced in vivo by the PCBs.

Degradation of Aroclor 1221 in soil by a hybrid pseudomonad.

The hybrid Pseudomonas cepacia strain JHR22 was tested for its ability to degrade Aroclor 1221 in soil. The influence of supplements--mineral salts and trace elements--on the degradation was investigated. Disappearance of Aroclor 1221 congeners, occurrence of metabolites, and release of chloride were measured under different conditions. After 45 days the hybrid organism, strain JHR22, was still present at high numbers in soil, independently of whether the soil had been sterilized prior to inoculation or not. There was only a minor difference in degradation efficiency between sterilized and untreated soil with about 70% release of chloride when 10(7) cells/g soil were inoculated. The whole hybrid pathway, originating from three different strains, was found to be stable under the conditions tested. Mineral salts did not significantly affect the degradation rate or survival of the hybrid strain.

Differential expression and induction of UDP-glucuronosyltransferase isoforms in hepatic and extrahepatic tissues of a fish, Pleuronectes platessa: immunochemical and functional characterization.

Glucuronidation of three substrates prototypical for different UDP-glucuronosyltransferase (UDPGT) isoforms in hepatic, renal, intestinal, and branchial microsomes of corn oil, 3-methylcholanthrene, Aroclor 1254, and clofibrate-pretreated plaice was investigated. The differential expression of UDPGT in the four tissues clearly demonstrated for the first time that multiple isoforms with differing substrate specificities were present in fish. The liver was quantitatively the most important site for the glucuronidation of all three compounds studied. Phenol UDPGT activity was ubiquitous to all tissues and was induced by 3-methylcholanthrene and Aroclor 1254 in hepatic tissue and by Aroclor 1254 in renal tissue. The glucuronidation of testosterone was restricted to liver and intestinal tissue, while conjugation of bilirubin was expressed solely in hepatic tissue. The biotransformation of the endogenous compounds was not induced in the xenobiotic-treated animals. The presence of immunoreactive UDPGTs in the four tissues was demonstrated by immunoblot analysis using sheep anti-plaice UDPGT antibodies. Hepatic tissue displayed a range of immunoreactive polypeptides of 52 to 57 kDa, while a 55-kDa polypeptide was detected in extrahepatic tissues. An increased intensity of the latter polypeptide species was demonstrated in liver and kidney microsomes in which there was a concomitant induction of phenol UDPGT activity in xenobiotic-treated fish. The results indicate that the 55-kDa polypeptide was the major polyaromatic hydrocarbon-inducible UDPGT isoenzyme in hepatic and renal microsomes.