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Effects of the inoculant strain Pseudomonas putida KT2442 (pNF142) and of naphthalene contamination on the soil bacterial community.

The naphthalene-degrading activity of a Pseudomonas sp. strain isolated from a creosote-contaminated soil was shown to be encoded by the IncP9 plasmid pNF142 by transfer to Pseudomonas putida KT2442. The effects of the inoculant strain KT2442 (pNF142) and of naphthalene contamination on the soil bacterial community were studied in microcosms with the following treatments: (I) soil, (II) soil with naphthalene, (III) soil with naphthalene and inoculated with KT2442 (pNF142). The inoculant became the dominant bacterial population in treatment (III) as evidenced by cultivation and denaturing gradient gel electrophoresis (DGGE) analysis. The bacterial DGGE profiles revealed drastically reduced complexity due to the numerical dominance of the inoculant. However, group-specific fingerprints (beta-proteobacteria, actinobacteria) that excluded KT2442 (pNF142) showed less severe changes in the bacterial community patterns. A major effect of naphthalene on the soil bacterial community was observed in treatment (II) after 21 days. Two dominant bands appeared whose sequences showed the highest similarity to those of Burkholderia sp. RP007 and Nocardia vinaceae based on 16S rRNA gene sequencing. These bands were less intense in treatment (III). The increased abundance of RP007-like populations due to naphthalene contamination was also confirmed by PCR amplification of the phnAc gene. The nahAc and nahH genes were detected in DNA and cDNA only in treatment III. Although the inoculant strain KT2442 (pNF142) showed good survival and expression of genes involved in naphthalene degradation, this study suggests that KT2442 (pNF142) suppressed the enrichment of indigenous naphthalene degraders.

Bacteria↗

Dietary curcumin prevents ocular toxicity of naphthalene in rats.

Administration of naphthalene is known to cause cataract formation in rats and rabbits and naphthalene-initiated cataract is frequently used as a model for studies on senile cataract in humans. Oxidative stress has been implicated in the mechanism of naphthalene-induced cataract. Curcumin, a constituent of turmeric, a spice used in Indian curry dishes, is an effective antioxidant and is known to induce the enzymes of glutathione-linked detoxification pathways in rats. During the present studies, we have examined whether low levels of dietary curcumin could prevent naphthalene-induced opacification of rat lens. The presence of apoptotic cells in lens epithelial cells was also examined by catalytically incorporating labeled nucleotide to DNA with either Klenow fragment of DNA polymerase or by terminal deoxynucleotidyl transferase (TdT), which forms polymeric tail using the principle of TUNEL assay. The results of these studies demonstrated that the rats treated with naphthalene and kept on a diet supplemented with only 0.005% (w/w) curcumin had significantly less opacification of lenses as compared to that observed in rats treated only with naphthalene. Our studies also demonstrate, for the first time, that naphthalene-initiated cataract in lens is accompanied and perhaps preceded by apoptosis of lens epithelial cells and that curcumin attenuates this apoptotic effect of naphthalene.

Administration, Oral↗

Prediction of naphthalene bioaccumulation using an adipocyte cell line model.

A long-term goal of this research is to develop an in vitro model to study the metabolism, distribution, and fate of chemicals or pharmaceuticals in animals and humans. An important component of such a system is an in vitro model to study bioaccumulation of specific chemicals in adipose tissue. Due to the difficulties in maintaining primary adipocytes in culture and conducting reproducible experiments, transformed adipocyte cell lines have been used as an alternative. In this paper, several rodent preadipocyte cell lines (3T3-L1, 3T3-F442A, and TA1 cells) that differentiate into adipocytes when exposed to the appropriate stimuli are tested as an investigative tool to study naphthalene accumulation. The in vitro model is tested by comparison of its performance to that of primary adipocytes. All the experimental evidence supports the hypothesis that naphthalene accumulation is primarily dependent on the level of intracellular lipid. Furthermore, the level of naphthalene bioaccumulation is linearly correlated with the amount of triglyceride content with the slope of 37.7 +/- 0.5 microg of naphthalene/(mg of triglyceride). Indomethacin/dexamethasone/insulin are shown to be more effective in promoting preadipocyte differentiation than methylisobutylxanthine/dexamethasone/insulin. Additionally, external factors, such as the presence of albumin and serum in the medium, affect the cellular naphthalene uptake by decreasing the amount of naphthalene transported into fat cells. Among the three cell lines tested, 3T3-L1 adipocytes accumulated the highest intracellular lipid and, hence, yielded the highest level of naphthalene accumulation. Its ability to accumulate naphthalene is comparable to that of primary adipocytes. The 3T3-L1 adipocyte model is appropriate for studying the bioaccumulation of xenobiotics that are aromatic hydrocarbons.

3T3 Cells↗

Combining cell culture analogue reactor designs and PBPK models to probe mechanisms of naphthalene toxicity.

An alternative method of evaluating the toxicology of a chemical is to use cultured mammalian cells in a novel cell culture analogue reactor (CCA) together with a corresponding physiologically based pharmacokinetic model (PBPK). The PBPK is a mathematical model that divides the body into compartments representing organs, integrating the kinetic, thermodynamic, and anatomical parameters of the animal. The bioreactor is a physical replica of the PBPK; where the PBPK specifies an organ or tissue compartment, the bioreactor contains compartments with a corresponding cell type. The device is a continuous, dynamic system composed of multiple cell types that interact through a common circulating cell culture medium. The bioreactor and the model are coupled to evaluate the plausibility of the molecular mechanism that is input into the model. This concept is tested with naphthalene as a model of PAH (polycyclic aromatic hydrocarbons) toxicants. Two physically different CCA reactors were tested with naphthalene, and different results were observed. In the prototype system using cells attached to glass dilution bottles, naphthalene dosing resulted in generation of a circulating metabolite from the "liver" compartment (based on H4IIE cells from a rat hepatoma) that caused cell death in the "lung" compartment (L2 cells from a rat lung), as well as depletion of glutathione in the L2 cells. An improved CCA using packed bed reactors of microcarrier cultured cells did not show differences between naphthalene-dosed and nondosed controls. To explain the different responses of the two CCA designs, PBPKs of the two reactors were tested with variations in physical and kinetic parameters, and toxic mechanism. When the toxic metabolite of naphthalene was naphthoquinone rather than naphthalene epoxide as initially assumed, the PBPK results were consistent with the results of the two CCA designs. This result indicates that the mechanism of naphthalene toxicity in the CCAs may be mediated through naphthoquinone formation. The CCA-PBPK concept is demonstrated to be applicable to the study of toxic mechanisms. In particular, use of this approach suggests that in vitro naphthalene toxicity is mediated through the naphthoquinone metabolite.

Animals↗

Micellar solubilization of naphthalene and phenanthrene from nonaqueous-phase liquids.

The equilibrium partitioning of the polycyclic aromatic hydrocarbon (PAH) compounds naphthalene and phenanthrene, from nonaqueous-phase liquids (NAPLs) into micellar solutions of five different nonionic polyethoxylated surfactants, is evaluated in this study. A series of synthesized NAPLs, comprised of naphthalene and/or phenanthrene dissolved in hexadecane at varying concentrations, were equilibrated with surfactant solutions in well-mixed batch systems. It was observed that the extent of micellar partitioning of PAH compounds increases linearly with their relative abundance in the NAPLs. A theoretical liquid-liquid partitioning framework that describes PAH equilibrium partitioning between the NAPL, aqueous, and the liquid-like micellar phases is presented. Although the maximum solubilization capacity of micelles is generally higher for naphthalene as compared to phenanthrene, results indicate that with certain NAPLs phenanthrene may be solubilized to a similar extent as naphthalene, even when equal mole fractions of the compounds are present in the NAPLs. Selective solubilization of naphthalene over phenanthrene into micellar solutions of Brij 35 was observed in systems where naphthalene and phenanthrene were both present. The extent of micellar partitioning of phenanthrene was decreased by approximately 18% in the presence of naphthalene, while naphthalene partitioning was unaffected by the presence of phenanthrene.

Environmental Monitoring↗

Naphthalene contamination of sterilized milk drinks contained in low-density polyethylene bottles. Part 1.

Naphthalene contamination was observed in sterilized milk drinks contained in low-density polyethylene bottles. The determination of naphthalene in the packaging material by gas chromatography showed levels of naphthalene ranging from 0.7 to 2.0 micrograms g-1. Analysis of the milk samples at the time of purchase by gas chromatography after extraction using a Dean and Stark apparatus showed levels of naphthalene in the range 0.01-0.03 microgram ml-1. The level of contamination in milk increased with storage time at room temperature (25 degrees C) and, depending on the concentration of naphthalene in the packaging material, values of 0.08-0.27 microgram ml-1 were found at the expiry date. Migration studies were carried out using peanut oil as a food stimulant. The amount of naphthalene extracted by milk from the polyethylene at 25 degrees C over a period of 60 d was related to the amount that could be extracted using peanut oil at 66 degrees C for 30 h. A mathematical model was established to describe the observed migration of naphthalene into milk, and proved valid for calculating the level of naphthalene in milk using the optimum determined values of K and Dp.

Animals↗

nahR, encoding a LysR-type transcriptional regulator, is highly conserved among naphthalene-degrading bacteria isolated from a coal tar waste-contaminated site and in extracted community DNA.

In Pseudomonas putida strain G7, a LysR-type positive transcriptional activator protein encoded by nahR is necessary for activation of two operons involved in naphthalene catabolism [Schell, M. A. & Poser, E. F. (1989). J Bacteriol 171, 837-846]. The role of an nahR homologue, NCIB-nahR, in another naphthalene-metabolizing bacterium, P. putida NCIB 9816-4 was verified. Targeted disruption of NCIB-nahR by homologous recombination resulted in a growth defect in the presence of naphthalene or salicylate as sole carbon and energy source. The nahR homologues and intergenic regions between nahR-like and nahG-like genes from P. putida NCIB 9816-4 and seven bacteria native to a naphthalene-rich coal tar contaminated site were amplified by PCR using degenerate primers. The amplified nahR homologues and the intergenic regions were cloned and sequenced. Alignment of the deduced amino acid sequences from NahR homologues revealed that NahR-like proteins showed only minor variations in all investigated naphthalene-degrading isolates. The intergenic regions, together with known NahR-binding sites showed the consensus NahR-protein-binding sites (5'-ATTCACGCTN(2)TGAT-3'). Surprisingly, amplified intergenic regions from naphthalene-degrading micro-organisms native to this study site were 100% identical to that of the pDTG1 plasmid (an archetypal naphthalene-catabolic plasmid from Pseudomonas putida NCIB 9816-4), but the nahR coding regions were not. DNA representing the uncultured microbial community was extracted from six sediment samples with varying coal tar exposure histories. PCR amplification of nahR from sediment DNA was observed in contaminated samples, but in uncontaminated samples only following laboratory incubation with naphthalene. The sediment-derived PCR products were sequenced and also found to be almost identical to known nahR genes. Thus, the structure and function of nahR-nahG regulatory genes appear to be highly conserved.

Amino Acid Sequence↗

Differential bioavailability of soil-sorbed naphthalene to two bacterial species.

Prediction of the fate of hydrophobic organic contaminants in soils is complicated by the competing processes of sorption and biodegradation. To test the hypothesis that sorbed naphthalene is unavailable to degradative microorganisms, we developed a simple kinetic method to examine the rates and extents of naphthalene degradation in soil-free and soil-containing systems in a comparison of two bacterial species. The method is predicated on the first-order dependence of the initial mineralization rate on the naphthalene concentration when the latter is below the Michaelis-Menten half-saturation constant (Km) for naphthalene for the organism under study. Rates and extents of mineralization were estimated by nonlinear regression analysis of data by using both a simple first-order model and a three-parameter, coupled degradation-desorption model described for the first time here. Bioavailability assays with two bacterial species (Pseudomonas putida ATCC 17484 and a gram-negative soil isolate, designated NP-Alk) gave dramatically different results. For NP-Alk, sorption limited both the rate and extent of naphthalene mineralization, in accordance with values predicted on the basis of the equilibrium aqueous-phase naphthalene concentrations. For strain 17484, both the rates and extents of naphthalene mineralization exceeded the predicted values and resulted in enhanced rates of naphthalene desorption from the soils. We conclude that there are important organism-specific properties which make generalizations regarding the bioavailability of sorbed substrates inappropriate.

Biodegradation, Environmental↗

Maintenance and induction of naphthalene degradation activity in Pseudomonas putida and an Alcaligenes sp. under different culture conditions.

The expression of xenobiotic-degradative genes in indigenous bacteria or in bacteria introduced into an ecosystem is essential for the successful bioremediation of contaminated environments. The maintenance of naphthalene utilization activity is studied in Pseudomonas putida (ATCC 17484) and an Alcaligenes sp. (strain NP-Alk) under different batch culture conditions. Levels of activity decreased exponentially in stationary phase with half-lives of 43 and 13 h for strains ATCC 17484 and NP-Alk, respectively. Activity half-lives were 2.7 and 5.3 times longer, respectively, in starved cultures than in stationary-phase cultures following growth on naphthalene. The treatment of starved cultures with chloramphenicol caused a loss of activity more rapid than that measured in untreated starved cultures, suggesting a continued enzyme synthesis in starved cultures in the absence of a substrate. Following growth in nutrient medium, activity decreased to undetectable levels in the Alcaligenes sp. but remained at measurable levels in the pseudomonad even after 9 months. The induction of naphthalene degradation activities in these cultures, when followed by radiorespirometry with 14C-labeled naphthalene as the substrate, was consistent with activity maintenance data. In the pseudomonad, naphthalene degradation activity was present constitutively at low levels under all growth conditions and was rapidly (in approximately 15 min) induced to high levels upon exposure to naphthalene. Adaptation in the uninduced Alcaligenes sp. occurred after many hours of exposure to naphthalene. In vivo labeling with 35S, to monitor the extent of de novo enzyme synthesis by naphthalene-challenged cells, provided an independent confirmation of the results.

Adaptation, Physiological↗

Anaerobic naphthalene degradation by a sulfate-reducing enrichment culture.

Anaerobic naphthalene degradation by a sulfate-reducing enrichment culture was studied by substrate utilization tests and identification of metabolites by gas chromatography-mass spectrometry. In substrate utilization tests, the culture was able to oxidize naphthalene, 2-methylnaphthalene, 1- and 2-naphthoic acids, phenylacetic acid, benzoic acid, cyclohexanecarboxylic acid, and cyclohex-1-ene-carboxylic acid with sulfate as the electron acceptor. Neither hydroxylated 1- or 2-naphthoic acid derivatives and 1- or 2-naphthol nor the monoaromatic compounds ortho-phthalic acid, 2-carboxy-1-phenylacetic acid, and salicylic acid were utilized by the culture within 100 days. 2-Naphthoic acid accumulated in all naphthalene-grown cultures. Reduced 2-naphthoic acid derivatives could be identified by comparison of mass spectra and coelution with commercial reference compounds such as 1,2,3, 4-tetrahydro-2-naphthoic acid and chemically synthesized decahydro-2-naphthoic acid. 5,6,7,8-Tetrahydro-2-naphthoic acid and octahydro-2-naphthoic acid were tentatively identified by their mass spectra. The metabolites identified suggest a stepwise reduction of the aromatic ring system before ring cleavage. In degradation experiments with [1-(13)C]naphthalene or deuterated D(8)-naphthalene, all metabolites mentioned derived from the introduced labeled naphthalene. When a [(13)C]bicarbonate-buffered growth medium was used in conjunction with unlabeled naphthalene, (13)C incorporation into the carboxylic group of 2-naphthoic acid was shown, indicating that activation of naphthalene by carboxylation was the initial degradation step. No ring fission products were identified.

Anaerobiosis↗

Measurement of biologically available naphthalene in gas and aqueous phases by use of a Pseudomonas putida biosensor.

Genetically constructed microbial biosensors for measuring organic pollutants are mostly applied in aqueous samples. Unfortunately, the detection limit of most biosensors is insufficient to detect pollutants at low but environmentally relevant concentrations. However, organic pollutants with low levels of water solubility often have significant gas-water partitioning coefficients, which in principle makes it possible to measure such compounds in the gas rather than the aqueous phase. Here we describe the first use of a microbial biosensor for measuring organic pollutants directly in the gas phase. For this purpose, we reconstructed a bioluminescent Pseudomonas putida naphthalene biosensor strain to carry the NAH7 plasmid and a chromosomally inserted gene fusion between the sal promoter and the luxAB genes. Specific calibration studies were performed with suspended and filter-immobilized biosensor cells, in aqueous solution and in the gas phase. Gas phase measurements with filter-immobilized biosensor cells in closed flasks, with a naphthalene-contaminated aqueous phase, showed that the biosensor cells can measure naphthalene effectively. The biosensor cells on the filter responded with increasing light output proportional to the naphthalene concentration added to the water phase, even though only a small proportion of the naphthalene was present in the gas phase. In fact, the biosensor cells could concentrate a larger proportion of naphthalene through the gas phase than in the aqueous suspension, probably due to faster transport of naphthalene to the cells in the gas phase. This led to a 10-fold lower detectable aqueous naphthalene concentration (50 nM instead of 0.5 micro M). Thus, the use of bacterial biosensors for measuring organic pollutants in the gas phase is a valid method for increasing the sensitivity of these valuable biological devices.

Bacterial Proteins↗

Naphthalene dioxygenase: purification and properties of a terminal oxygenase component.

Naphthalene dioxygenase from Pseudomonas sp. strain NCIB 9816 is a multicomponent enzyme system that oxidized naphthalene to cis-(1R, 2S)-dihydroxy-1,2-dihydronaphthalene. The terminal oxygenase component B was purified to homogeneity by a three-step procedure that utilized ion-exchange and hydrophobic interaction chromatography. The purified enzyme oxidized naphthalene only in the presence of NADH, oxygen, and partially purified preparations of components A and C. An estimated Mr of 158,000 was obtained by gel filtration. Polyacrylamide gel electrophoresis in the presence of sodium dodecyl sulfate revealed the presence of two subunits with molecular weights of ca. 55,000 and 20,000, indicative of an alpha 2 beta 2 quaternary structure. Absorption spectra of the oxidized enzyme showed maxima at 566 (shoulder), 462, and 344 nm, which were replaced by absorption maxima at 520 and 380 nm when the enzyme was reduced anaerobically by stoichiometric quantities of NADH in the presence of the other two components of the naphthalene dioxygenase system. Component B bound naphthalene. Enzyme-bound naphthalene was oxidized to product upon the addition of components A and C, NADH, and O2. These results, together with the detection of the presence of 6.0 g-atoms of iron and 4.0 g-atoms of acid-labile sulfur per mol of the purified enzyme, suggest that component B of the naphthalene dioxygenase system is an iron-sulfur protein which functions in the terminal step of naphthalene oxidation.

Dioxygenases↗

Protective effect of aqueous garlic extract against naphthalene-induced oxidative stress in mice.

The aim of this study was to investigate the possible protective effects of aqueous garlic extract (AGE) against naphthalene-induced oxidative changes in liver, kidney, lung and brain of mice. Balb/c mice (25-30 g) of either sex were divided into five groups each comprising 10 animals. Mice received for 30 days: 0.9% NaCl, i.p. (control); corn oil, i.p; AGE in a dose of 125 mg kg-1, i.p.; naphthalene in a dose of 100 mg kg-1, i.p. (dissolved in corn oil); and AGE (in a dose of 125 mg kg-1, i.p.) plus naphthalene (in a dose of 100 mg kg-1, i.p.). After decapitation, liver, kidney, lung and brain tissues were excised. Malondialdehyde (MDA) and glutathione (GSH) levels and myeloperoxidase activity (MPO) were determined in the tissues, while oxidant-induced tissue fibrosis was determined by collagen content. Tissues were also examined microscopically. Serum aspartate aminotransferase, alanine aminotransferase levels and blood urea nitrogen and creatinine concentrations were measured for the evaluation of hepatic and renal function, respectively. MDA and GSH levels were also assayed in serum samples. In the naphthalene-treated group, GSH levels decreased significantly, while MDA levels, MPO activity and collagen content increased in the tissues (P<0.01-0.001), suggesting oxidative organ damage, which was also verified histologically. In the AGE-treated naphthalene group, all of these oxidant responses were reversed significantly (P<0.05-0.01). Hepatic and renal function test parameters, which increased significantly (P<0.001) following naphthalene administration, decreased (P<0.05-0.001) after AGE treatment. The results demonstrate the role of oxidative mechanisms in naphthalene-induced tissue damage. The antioxidant properties of AGE ameliorated oxidative organ injury due to naphthalene toxicity.

Animals↗

Genetics of naphthalene catabolism in pseudomonads.

In pseudomonads, naphthalene is catabolized in a series of reactions to salicylic acid, which is further degraded via the catechol meta-cleavage, ortho-cleavage, or gentisic acid pathway to Krebs cycle intermediates. The naphthalene catabolic genes have been located on self-transmissible plasmids, in most cases, and implicated to have chromosomal locations in other cases. The best-studied naphthalene catabolic plasmid is NAH7. It carries two operons, one of which enables the host to utilize naphthalene and the other to utilize salicylate as a carbon and energy source. The product of another NAH7 gene, nahR, is required to turn on both operons in the presence of the inducer, salicylate. Several different naphthalene and salicylate catabolic plasmids have been shown to share sequence homology with NAH7. These plasmids can undergo structural alterations involving insertions and deletions during conjugations and changes in nutritional conditions. Available evidence suggests that salicylate catabolic plasmids can form from the naphthalene catabolic plasmids by structural alterations of the plasmid DNA. The gene organization and regulation, as well as the genetic instability of the naphthalene catabolic plasmids, are reminiscent of the TOL plasmids and suggest that the naphthalene catabolic plasmids and other catabolic plasmids may have evolved in a short period of time by acquiring and modifying preevolved gene clusters from host chromosomes or other plasmids.

Naphthalenes↗

Effect of aldose reductase inhibitors on naphthalene cataract formation in the rat.

Naphthalene feeding can result in cataract formation in rats and rabbits due to specific metabolites of naphthalene. The concomitant administration of the aldose reductase inhibitor Al1576 to naphthalene-fed rats was proven to prevent cataract formation. To determine whether this effect was directly linked to the ability of Al1576 to inhibit enzyme aldose reductase, a variety of structurally diverse aldose reductase inhibitors, including the carboxylic acids tolrestat, Ponalrestat, and FK366, and the spirohydantoins, sorbinil and Al1576, were investigated for their ability to inhibit naphthalene-induced cataracts. Brown Norway rats, administered naphthalene by gavage, were fed normal rat chow containing these aldose reductase inhibitors at levels known to inhibit sugar cataract formation. The lens changes in these rats were monitored over a 90-day period by portable slit-lamp microscopy and histologic study. Al1576 showed a dose-dependent reduction in naphthalene-induced cataract formation, with no naphthalene-associated deposits seen in toluidine blue-stained lens sections. Sorbinil also reduced lens changes, whereas tolrestat, Ponalrestat, and FK366 had no effect. These results suggest that inhibition of naphthalene-induced cataract formation by structurally diverse aldose reductase inhibitors was not linked to the inhibition of aldose reductase.

Aldehyde Reductase↗

Hepatic and pulmonary microsomal metabolism of naphthalene to glutathione adducts: factors affecting the relative rates of conjugate formation.

Earlier studies demonstrating marked differences in the profile of polar metabolites formed during incubations of glutathione, naphthalene and microsomes from target (lung) and nontarget (liver and kidney) tissues of the mouse suggested that the formation of a particular reactive metabolite may be the underlying basis for the highly organ selective toxicity of this hydrocarbon. The studies reported here were done to characterize more fully the microsomal metabolism of naphthalene to 1,2-dihydro-1,2-dihydroxynaphthalene and to three glutathione-derived conjugates that were separated by high-pressure liquid chromatography. The microsomal formation of polar naphthalene metabolites was linear with time and microsomal protein; the relative proportions of each of the metabolites remained relatively stable over the range of time and protein concentrations studied. The rate of formation of naphthalene glutathione adducts, but not the dihydrodiol, was dependent upon the amount of 100,000 X g supernatant protein added. Addition of lung cytosol to liver microsomal incubations or liver cytosol to lung microsomal incubations altered the overall rate of conjugate formation but not the relative proportions of each of the three conjugate peaks. Epoxide hydrolase induction by dietary butylated hydroxyanisole or inhibition by cyclohexene oxide altered the rate of hepatic microsomal formation of naphthalene dihydrodiol in the expected manner and increased the production of conjugate peak 2. Butylated hydroxyanisole or cyclohexene oxide failed to alter the rate of formation of conjugate peak 1 or 3. Addition of piperonyl butoxide or SKF 525-A to hepatic microsomal incubations markedly decreased covalent binding of naphthalene metabolites but only slightly decreased glutathione adduct formation. Dihydrodiol formation was increased by both inhibitors. Phenobarbital or 3-methylcholanthrene pretreatment produced a marked increase in the pulmonary microsome-catalyzed formation of all four polar naphthalene metabolites. In comparison, phenobarbital increased the rates of formation of the dihydrodiol, conjugate peaks 1 and 2 but not 3 in hepatic microsomes. 3-Methylcholanthrene increased the rate of formation of the dihydrodiol and conjugate peak 2 but not 1 or 3. These studies indicate that the predominant formation of conjugate peak 2 in lung microsomal incubations in comparison to liver microsomal incubations is due to the regio- or stereoselectivity of naphthalene metabolism by cytochrome P-450 monooxygenases or epoxide hydrolases but not by the glutathione transferases.

Animals↗

Biochemical responses of fish sac fry and a primary cell culture of fish hepatocytes exposed to polychlorinated naphthalenes.

Chlorinated naphthalenes are planar halogenated aromatic compounds, which are widespread in the environment. Knowledge of their biochemical and toxicological actions in aquatic biota is, however, limited. The objective of this study was to assess the toxicity of highly chlorinated naphthalene congeners found in the aquatic environment on fish sac fry and to study their effects on xenobiotic metabolizing enzymes (CYP) using a short-term primary culture of fish hepatocytes and liver microsomes. A few days after hatching, rainbow trout sac fry were administered either Hallovax 1014, a mixture of 1,2,3,4,6,7-hexachloronaphthalene and 1,2,3,5,6, 7-hexachloronaphthalene (HxCN-mix), or 1,2,3,4,5,6, 7-heptachloronaphthalene (HpCN) (0.08, 0.8, and 4 microg/sac fry injected into the yolk sac). The exposure was terminated 2 weeks later. The naphthalene preparations did not cause any clinical signs of toxicity or difference in mortality rates between the control and treated groups. Immunohistochemical analysis of CYP1A expression in the treated sac fry revealed that staining was most pronounced in the hepatocytes and thereafter in kidney tubular epithelial cells. Moderate CYP1A staining was also seen in the mucosal epithelium of pyloric caecae and mild staining in the epithelium of olfactory organ. Staining in control sac fry was weak or absent. Exposure of the primary cell culture of trout hepatocytes to a low doses (</=10 ng/ml) of the chlorinated naphthalenes increased significantly CYP1A-associated EROD activity and CYP1A mRNA content, HxCN-mix being the most potent and thereafter HpCN and Hallovax 1014. The higher doses (50-100 ng/ml) of each naphthalene also inhibited EROD activity. However, the content of CYP1A mRNA or the intensity of the CYP1A protein band (58 kDa) recognized by anti-trout CYP1A peptide antibodies were not decreased with increasing polychlorinated naphthalene (PCN) concentration, indicating that the inhibition was not due to reduced protein synthesis. Furthermore, in vitro analyses of the inhibitory potential of PCNs on CYP1A activity with trout liver microsomes suggested that these naphthalene preparations may be CYP1A substrates and act as competitive inhibitors of CYP1A catalyst. Our results demonstrate that highly chlorinated naphthalenes are potent modulators of fish CYP1A enzyme and suggest that hepatocytes and tubular epithelial cells are the cell types that may be vulnerable to their metabolic products for cell injury in fish sac fry.

Animals↗

Metabolism of Naphthalene, 1-Naphthol, Indene, and Indole by Rhodococcus sp. Strain NCIMB 12038.

The regulation of naphthalene and 1-naphthol metabolism in a Rhodococcus sp. (NCIMB 12038) has been investigated. The microorganism utilizes separate pathways for the degradation of these compounds, and they are regulated independently. Naphthalene metabolism was inducible, but not by salicylate, and 1-naphthol metabolism, although constitutive, was also repressed during growth on salicylate. The biochemistry of naphthalene degradation in this strain was otherwise identical to that found in Pseudomonas putida, with salicylate as a central metabolite and naphthalene initially being oxidized via a naphthalene dioxygenase enzyme to cis-(1R,2S)-1,2-dihydroxy-1,2-dihydronaphthalene (naphthalene cis-diol). A dioxygenase enzyme was not expressed under growth conditions which facilitate 1-naphthol degradation. However, biotransformations with indene as a substrate suggested that a monooxygenase enzyme may be involved in the degradation of this compound. Indole was transformed to indigo by both naphthalene-grown NCIMB 12038 and by cells grown in the absence of an inducer. Therefore, the presence of a naphthalene dioxygenase enzyme activity was not necessary for this reaction. Thus, the biotransformation of indole to indigo may be facilitated by another type of enzyme (possibly a monooxygenase) in this organism.

Journal Article↗