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Constitutive and inducible hydroxylase activities involved in the degradation of naphthalene by Cunninghamella elegans.

The non-ligninolytic fungus Cunninghamella elegans was investigated for its ability to produce naphthalene hydroxylase (NAH) and naphthol hydroxylase (NOH) activities under various conditions. When the organism was cultivated on a rich growth medium, the mycelia exhibited significant constitutive NAH activity in the late exponential growth phase, but not in the early-exponential-growth-phase. On incubating the early-exponential-growth-phase mycelia with naphthalene, NAH activity was increased five-fold; however, this increase did not occur in the presence of the protein synthesis inhibitor cycloheximide. Since incubation of the late-phase mycelia with naphthalene did not lead to a higher degradation rate of naphthalene, mycelia in this physiological state have apparently lost the ability to induce synthesis of the enzyme exhibiting NAH activity. This is not due to an overall inability to perform de novo protein synthesis, since NOH activity, non-constitutive at all growth phases, could be induced by incubating late-phase mycelia with naphthalene. Whether inducible and constitutive NAH activity originate from one and the same enzyme remains to be elucidated. It is suggested that naphthalene oxidizing enzyme(s) may also oxidize pyrene, but not anthracene or benzo[a]pyrene, although the latter are degradable by C. elegans.

Biodegradation, Environmental↗

Competition of plasmid-bearing Pseudomonas putida strains catabolizing naphthalene via various pathways in chemostat culture.

Plasmid-carrying Pseudomonas putida strains degrade naphthalene through different biochemical pathways. The influence of various combinations of host bacteria and plasmids on growth characteristics and competitiveness of P. putida strains was studied in chemostat culture at a low dilution rate (D = 0.05 h-1) with naphthalene as the sole source of carbon and energy. Under naphthalene limitation, the plasmid-bearing strains degrading naphthalene that use catechol 1,2-dioxygenase for catechol oxidation (ortho pathway), were the most competitive. The strains bearing plasmids that control naphthalene catabolism via catechol 2,3-dioxygenase (meta pathway), were less competitive. Under these conditions the strain carrying plasmid pBS4, which encodes for naphthalene catabolism via gentisic acid, was the least competitive.

Bacterial Proteins↗

Monitoring of accelerated naphthalene-biodegradation in a bioaugmented soil slurry.

The effect of microbial inoculation on the mineralization of naphthalene in a bioslurry treatment was evaluated in soil slurry microcosms. Inoculation by Pseudomonas putida G7 carrying the naphthalene dioxygenase (nahA) gene resulted in rapid mineralization of naphthalene, whereas indigenous microorganisms in the PAH-contaminated soil required a 28 h adaptation period before significant mineralization occurred. The number of nahA-like gene copies increased in both the inoculated and non-inoculated soil as mineralization proceeded, indicating selection towards naphthalene dioxygenase producing bacteria in the microbial community. In addition, 16S rRNA analysis by denaturing gradient gel electrophoresis (DGGE) analysis showed that significant selection occurred in the microbial community as a result of biodegradation. However, the indigenous soil bacteria were not able to compete with the P. putida G7 inoculum adapted to naphthalene biodegradation, even though the soil microbial community slightly suppressed naphthalene mineralization by P. putida G7.

Biodegradation, Environmental↗

Evidence that 1-naphthol is not an obligate intermediate in the covalent binding and the pulmonary bronchiolar necrosis by naphthalene.

Recent studies of a number of volatile aromatic hydrocarbons have suggested that the formation of covalently bound metabolites arises solely through the intermediate formation of phenols. This study further examines the involvement of 1-naphthol in the in vivo and in vitro formation of covalently bound metabolites and pulmonary bronchiolar necrosis by naphthalene. Marked differences were observed in the rate of 1-naphthol formation in lung and liver microsomal incubations without correspondingly large differences between the rates of formation of covalently bound metabolites from naphthalene and 1-naphthol. Glutathione decreased covalent binding in hepatic microsomal incubations containing 14[C]1-naphthol but did not result in the formation of any of the glutathione adducts isolated from identical incubations containing 14[C]naphthalene. Tissue levels of covalently bound radioactivity in mice treated with 14[C]1-naphthol or 14[C]naphthalene were similar; however, in contrast to studies with naphthalene, 1-naphthol administration did not deplete tissue glutathione nor result in detectable tissue injury. These studies indicate that 1-naphthol is not an obligate intermediate in the formation of covalently bound metabolites from naphthalene nor does it appear to be a more proximate lung toxic metabolite.

Animals↗

Evidence for cytochrome P-450 mediated metabolism in the bronchiolar damage by naphthalene.

Intraperitoneal administration of the volatile hydrocarbon, naphthalene, resulted in severe bronchiolar epithelial cell necrosis in mice, while hepatic or renal necrosis was not observed. Pulmonary damage and mortality by naphthalene were increased by prior treatment with diethyl maleate and decreased by prior treatment with piperonyl butoxide (1600 mg/kg). SKF 525A pretreatment had no effect on naphthalene-induced pulmonary damage. Administration of [14C]naphthalene resulted in the covalent binding of radiolabel to tissue macromolecules. Highest levels of binding occurred in lung, liver and kidney. Levels of covalent binding reached a maximum 2--4 h after treatment and corresponded to rapid glutathione depletion in lung and liver. Covalent binding was dose-dependent and showed a threshold between 200 and 400 mg/kg which coincided with almost total depletion of tissue glutathione levels. Covalent binding of reactive metabolites was increased 3--4-fold by prior treatment with diethyl maleate, and was decreased 3--4-fold by pretreatment with piperonyl butoxide. These studies support the view that naphthalene-induced pulmonary damage is mediated by the cytochrome P-450-dependent metabolism of naphthalene and that glutathione plays an important role in the detoxification of the lung damaging metabolite(s).

Animals↗

A mechanism of action for the inhibition of black pigment dispersion in the fiddler crab, Uca pugilator, by naphthalene.

The polycyclic aromatic hydrocarbon, naphthalene, inhibits the circadian dispersion of epidermal black pigment in the fiddler crab, Uca pugilator, by inhibiting the release of black pigment dispersing hormone. Naphthalene caused no permanent neural damage in Uca pugilator. Naphthalene did not cause a chemically-induced phase shift in the circadian rhythm of black pigment dispersion but reduced the daytime peak of that dispersion. Black pigment concentration, which occurs at night, was not affected by exposure to naphthalene. Black pigment dispersing hormone in naphthalene-exposed crabs can be released by an injection of norepinephrine. Given the points above, and previously published data, it is concluded that naphthalene inhibits circadian black pigment dispersion in Uca pugilator by inhibiting the release of the neurotransmitter, norepinephrine.

Animals↗

Interactive effects of naphthalene treatment and the onset of vitellogenesis on energy metabolism in liver and gonad, and plasma steroid hormones of rainbow trout Oncorhynchus mykiss.

The purpose of the study was to assess in female fish the possible interaction between treatment with a polycyclic aromatic hydrocarbon (PAH) like naphthalene and the onset of vitellogenesis. In a first experiment, female rainbow trout (Oncorhynchus mykiss) at stages 2-3 (previtellogenesis) or 4 (early vitellogenesis) were intraperitoneally injected (2 microl g(-1)) with vegetable oil alone (control) or containing naphthalene (50 mg kg(-1)) to be sampled 3 h later. A second experiment was similarly designed but using fish intraperitoneally implanted (10 microl g(-1)) with slow-release coconut oil implants alone (control) or containing 50 mg naphthalene kg(-1) body mass that were sampled 3 days after injection. On each sampling time, plasma levels of cortisol and 17beta-estradiol, and several metabolic parameters in plasma, liver and gonad were assessed. In controls, early vitellogenic fish compared with previtellogenic fish displayed changes that in some cases are confirmatory of previous studies whereas in other cases provide new information in plasma (increased amino acid levels), liver (decreased capacity for exporting glucose and reduced amino acid levels) and gonad (decreased amino acid levels). Naphthalene treatment produced in previtellogenic fish decreased 17beta-estradiol levels in plasma, increased plasma glucose or decreased liver gluconeogenic capacity whereas no major effects were noticed on parameters involved in lipid, amino acid and lactate metabolism. Differential effects of naphthalene treatment were noticed in early vitellogenic fish such as decreased 17beta-estradiol and glucose levels in plasma, increased hexokinase and glucokinase and lack of changes in fructose 1,6-bisphosphatase activities in liver, and a lower decrease of amino acid levels in gonad. Those alterations produced by naphthalene treatment resulted in a decreased capacity for covering the energy demand of vitellogenesis in liver and gonad that could contribute to a delay and/or impairment of the onset of maturation.

Amino Acids↗

The abundance of nahAc genes correlates with the 14C-naphthalene mineralization potential in petroleum hydrocarbon-contaminated oxic soil layers.

In this study, we evaluated whether the abundance of the functional gene nahAc reflects aerobic naphthalene degradation potential in subsurface and surface samples taken from three petroleum hydrocarbon contaminated sites in southern Finland. The type of the contamination at the sites varied from lightweight diesel oil to high molecular weight residuals of crude oil. Samples were collected from both oxic and anoxic soil layers. The naphthalene dioxygenase gene nahAc was quantified using a replicate limiting dilution-polymerase chain reaction (RLD-PCR) method with a degenerate primer pair. In the non-contaminated samples nahAc genes were not detected. In the petroleum hydrocarbon-contaminated oxic soil samples nahAc gene abundance [range 3 x 10(1)-9 x 10(4) copies (g dry wt soil)(-1)] was correlated (Kendall non-parametric correlation r2=0.459, p<0.01) with the aerobic 14C-naphthalene mineralization potential (range 1 x 10(-5)-0.1 d(-1)) measured in microcosms at in situ temperatures (8 degrees C for subsurface and 20 degrees C for surface soil samples). In these samples nahAc gene abundance was also correlated with total microbial cell counts (r2=0.471, p<0.01), respiration rate (r2=0.401, p<0.01) and organic matter content (r2=0.341, p<0.05). NahAc genes were amplified from anoxic soil layers indicating that, although involved in aerobic biodegradation of naphthalene, these genes or related sequences were also present in the anoxic subsurface. In the samples taken from the anoxic layers, the aerobic 14C-naphthalene mineralization rates were not correlated with nahAc gene abundance. In conclusion, current sequence information provides the basis for a robust tool to estimate the naphthalene degradation potential at oxic zones of different petroleum hydrocarbon-contaminated sites undergoing in situ bioremediation.

Bacteria, Aerobic↗

Anaerobic degradation of naphthalene in a fluvial aquifer: a radiotracer study.

A radiotracer study was conducted in a creosote-contaminated aquifer beneath the Fraser River, British Columbia Canada to investigate the in situ degradation of naphthalene. The groundwater is anaerobic, with abundant methane, ferrous iron and carbon dioxide. This study followed earlier work at the site where the contaminant distribution could only be explained by invoking a mass loss through degradation, even though extensive field and laboratory microcosm studies closer to the source zone onshore could not confirm degradation. Accordingly, 14C-naphthalene was injected into the aquifer offshore, further from the source zone where modeling suggested degradation was occurring. During the 230-day monitoring period, 14CO2 was detected, confirming the degradation of the radio-labeled naphthalene tracer. A zero-order degradation rate of naphthalene of 5 microg/L-day was estimated based on the decrease in 14C-naphthalene concentration with time. While the degradation pathway could not be determined from the radiotracer study alone, the geochemistry of the site suggests that either iron reduction or methanogenesis is the terminal electron accepting processes responsible for naphthalene oxidation.

Anaerobiosis↗

Enhanced electrokinetic dissolution of naphthalene and 2,4-DNT from contaminated soils.

Electrokinetic soil remediation has been proven to remove heavy metals and polar organics from low hydraulic conductivity subsurface environment. In this study, carboxymethyl-beta-cyclodextrin (CMCD) was used as a carrier to assist electrokinetic treatment for removal of low polarity organic contaminants from soils (2.2% organic carbon content). Naphthalene and 2,4-dinitrotoluene (2,4-DNT) were selected as the test compounds. The results from columns experiments showed that 46 and 43% of naphthalene and 2,4-DNT, respectively, were removed using 0.01 N NaNO(3) flushing solution with 40 V electrical potential while 70 and 72% of naphthalene and 2,4-DNT were removed using 2 g/L CMCD solution. Naphthalene and 2,4-DNT removal was enhanced to 83 and 89%, respectively, by using 2 g/L CMCD with 40 V electrical potential. Findings from this study also demonstrated that cyclodextrin assisted electrokinetics can enhance the removal rate of naphthalene and 2,4-DNT. Electric potential applied has more influence on the contaminant removal than the amount of CMCD used. Higher voltage application caused increase in the removal rate of naphthalene and 2,4-DNT, and appeared to be one of the critical factors in obtaining higher contaminant removal while increasing CMCD solution concentration above 2 g/L appeared to have little effect on the contaminant removal.

Dinitrobenzenes↗

Changes in whole cell-derived fatty acids induced by naphthalene in bacteria from genus Pseudomonas.

Fatty acid composition during naphthalene utilization was investigated in three strains of bacteria Pseudomonas vesicularis, Pseudomonas stutzeri and Pseudomonas sp. JS150 that expressed different naphthalene degradation abilities. All strains significantly changed their cellular fatty acid profiles as a response to naphthalene exposure. Since naphthalene was present in the medium P. stutzeri increased ratio of saturated/unsaturated fatty acids from 1.1 to 2.1 and Pseudomonas sp. JS150 from 7.5 to 12.0, respectively. In contrast, this ratio decreased from 2.1 to 1.1 in P. vesicularis under the same growth conditions. The changes comprised also alterations in the percentage of selected groups of fatty acids: iso and anteiso, hydroxy and cyclopropane fatty acids. Our results showed that naphthalene induced in tested strains different changes in fatty acids composition. It may suggest that in the presence of naphthalene microorganisms used different adaptive mechanisms to maintain the cells in appropriate physiological state.

Biodegradation, Environmental↗

Mass transfer and bioremediation of naphthalene particles in a roller bioreactor.

Naphthalene particles in a water slurry have been bioremediated in a sealed, roller bioreactor using a pure strain of Pseudomonas putida. High stripping losses of particles due to both splashing and aeration made the use of the traditional CSTR bioreactor unsuitable for bioremediation of naphthalene particles. The overall dissolution mass transfer coefficient of naphthalene particles in the roller bioreactor was low, 0.055 h(-1) at 50 RPM. The dissolution mass transfer rate was the limiting step for bioremediation. Although mass transfer was identified as the rate limiting step, the addition of hydroxypropyl-beta-cyclodextrin (a solubility enhancer) failed to improve naphthalene slurry bioremediation. In order to successfully bioremediate naphthalene particles at concentrations over 300 mg/L, intermittent aeration was applied in the sealed roller bioreactor on a daily basis. By operating in sequential batch mode with intermittent aeration, the roller bioreactor was successfully used to continuously bioremediate naphthalene particles at concentrations up to 1000 mg/L and at rates up to 10 mg/Lh.

2-Hydroxypropyl-beta-cyclodextrin↗

Enhanced naphthalene solubility in the presence of sodium dodecyl sulfate: effect of critical micelle concentration.

Surfactants can increase the solubility of non-polar compounds, and have been applied in areas such as soil washing and treatment of non-aqueous phase liquids (NAPLs). This investigation explored the feasibility of removing vapor phase polycyclic aromatic hydrocarbon (PAH) from gases using an anionic surfactant. The solubility of vapor phase naphthalene was measured herein using gas chromatograph (GC) with a photon ionization detector (PID). The measurement results indicated that surfactant molecules were not favorable to micelle formation when temperatures increased from 25 degrees C to 50 degrees C. Regardless of whether solutions were quiescent or agitated, equilibrium naphthalene apparent solubility increased linearly with surfactant concentrations exceeding critical micelle concentration (CMC). The pH effects on naphthalene apparent solubility were small. Agitation increased naphthalene apparent solubility and lumped mass transfer coefficients. Furthermore, lumped mass transfer coefficients decreased with increasing surfactant concentration owing to increase in interfacial resistance and viscosity and decreased spherical micelle diffusion coefficients. Finally, the net absorption rate increased because the solubilization effects of micelles exceeded the reduction effects of mass transfer coefficient above the CMC. The enhanced naphthalene apparent solubility from the addition of surfactant can be expressed by an enrichment factor (EF). The EF value of naphthalene for the surfactant solution at 0.1 M with agitation at 270 rpm relative to quiescent water could reach 18.6. This work confirms that anionic surfactant can improve the removal efficiency of hydrophobic organic compound (HOC) from the gas phase.

Chromatography, Gas↗

Naphthalene-induced differential tissue damage association with circulating fish phagocyte induction.

The effect of naphthalene on phagocytes and associated abnormal cellular activities was studied in Anguilla anguilla L. Fish were exposed to sublethal concentrations (0.1, 0.3, 0.9, 2.7 microM) of naphthalene for 8, 16, 24, 48, and 72 h. Gill, head kidney, and peritoneum phagocyte respiratory burst activity (RBA) was measured by nitroblue tetrazolium reduction assay, whereas lipid peroxidation in fish gill, kidney, and liver was measured by thiobarbituric acid reaction substance. A significant increase (P < 0.05-P < 0.001) in total cell count (TCC) of phagocytes (TCCPH) isolated from gill, head kidney, and peritoneum was observed after 8 h of naphthalene exposure and persisting at 16 h exposure. However, long-term exposures (24, 48, and 72 h) induced a significant (P < 0.05-P < 0.001) decrease in TCC at all the concentration levels. Naphthalene exposure caused a significant (P < 0.05-P < 0.001) RBA induction after 8 and 16 h in gill, head kidney, and peritoneal phagocytes, which consequently resulted in a significant (P < 0.01 and P < 0.001) peroxidative tissue damage increase measured as lipid peroxidation (LPO) in gill, kidney, and liver at the same time intervals. Considering TCCPH, RBA, and LPO, the most affected tissues were gill and kidney after 8 and 16 h exposure to all naphthalene concentrations. RBA was significantly decreased after 24, 48, and 72 h of exposure (P < 0.05-P < 0.001), whereas peroxidative damage increased significantly (P < 0.05-P < 0.001) and persisted in long-term exposures (72 h) at all concentration levels in gill and kidney. Liver short-term exposure (8 and 16 h) to all naphthalene concentrations did not alter LPO activity. Long-term exposures (48 and 72 h) caused a significant (P < 0.01 and P < 0.001) LPO increase, which was more pronounced at 72 h. The results demonstrate that the activation pattern of RBA was corroborated by the extent of phagocyte-induced peroxidative damage in the tissues, as demonstrated by a significant increase of circulating phagocytes. However, the route of exposure and mode of entry of a pollutant may affect the activation pattern of circulating fish phagocytes. It is proposed that measurement of phagocyte-induced reactive oxygen species and their association with peroxidative damage in fish tissues may prove to be useful in biomonitoring fish exposure to aquatic pollutants.

Anguilla↗

Complete dechlorination of 1-chloronaphthalene by electrochemical reduction with naphthalene radical anion as mediator.

The possibility of electrochemical reduction for the complete dechlorination of toxic chlorinated aromatic compounds was investigated using 1-chloronaphthalene as a substrate. Sufficient current was obtained at the reduction potential of naphthalene rather than that of the substrate, and complete (>99.99%) dechlorination was achieved in tetra-n-butylammonium perchlorate/dimethylformamide solution in less than 1 h. The reaction was considered to proceed autocatalytically with the naphthalene radical anion, which was derived from the reduction of the initial dechlorination product (naphthalene) of the substrate, as mediator. The reaction rate was increased by the use of an excess of naphthalene at the start of the reaction, and complete dechlorination was possible without significant loss of current efficiency even if the water concentration was 0.3% v/v. The order of reaction of the mediated reduction was determined kinetically to be 0.5 for the substrate and 1 for naphthalene. Although the reaction of the naphthalene radical anion with 1-chloronaphthalene was very fast, it was considered to be the rate-determining step.

Catalysis↗

Nitration and photonitration of naphthalene in aqueous systems.

The nitration of naphthalene was studied in aqueous solution to gain insight into the processes leading to the nitration of aromatic compounds in atmospheric hydrometeors. Reactants used were nitric acid, nitrogen dioxide and peroxynitrous acid in the dark, nitrate, and nitrite/nitrous acid under illumination. Naphthalene nitration can lead to two possible isomers, 1- and 2-nitronaphthalene. The former nitrocompound preferentially forms upon electrophilic processes and in the presence of nitrogen dioxide. Electrophilic nitration of naphthalene takes place in the presence of concentrated nitric acid, but nitration with nitric acid and oxidants (charge-transfer nitration) occurs under much milder conditions than with nitric acid alone. Charge-transfer nitration may have some environmental significance in particular cases, e.g. in acidic aerosols in the presence of HNO3 and oxidants. Nitrogen dioxide is thought to have a role in PAH nitration in the Antarctic particulate matter. In previous papers we have found that nitration induced by peroxynitrous acid, HOONO, can follow two pathways, the former electrophilic (leading for instance to the formation of nitrophenols from phenol) and the latter probably involving HOONO itself (accounting for the formation of nitrobenzene from benzene). In the case of naphthalene and HOONO the electrophilic pathway mainly leads to 1-nitronaphthalene, while the other one preferentially yields 2-nitronaphthalene. The nitration of naphthalene in the presence of nitrite/nitrous acid under irradiation leads to both nitroisomers in similar ratios, and the process is not inhibited by hydroxyl scavengers. This excludes nitrogen dioxide as reactive species for nitration and marks a difference with phenol photonitration and a similarity with the behavior of benzene under comparable conditions. Nitrite photochemistry (and nitrite-induced photonitration as well) is expected to be relevant in fog and cloudwater in polluted areas. An important difference with the gas-phase nitration is that the radicals OH and NO3 are unlikely to play a relevant role in the nitration of naphthalene in aqueous solution.

Benzene↗

Effect of current density on enhanced transformation of naphthalene.

The effect of current density on electrochemically enhanced transformation of naphthalene is evaluated. Electrochemical reactors, composed of an anode and a cathode separated by a Nafion membrane, were used to evaluatethe effect of three current densities (1,9, and 18 mA/ L) on the transformation of naphthalene at two concentration levels (13 and 25 mg/L). Transformation rates varied based on the concentration and current density. Almost 88% of the 13 mg/L naphthalene is degraded after 8 h of treatment under 18.2 mA/L. At the same time, more than 90 h was required to degrade the same amount under 9 mA/ L. The results show that most of the naphthalene degradation occurred in the first 4 h under transformation rates of 2.24 and 1.11 mg/L h under applied currents of 18.2 and 9 mA/L, respectively. Increasing the naphthalene concentration to 25 mg/L produced similar results. Under 18.2 mA/L, the redox potential increased significantly at the anolyte in the first 8 h to about 900 mV. After that, the redox potential continued to increase, but at a lower rate, until it reached 1380 mV at the end of processing. Similar behavior is noted for the anolyte pH, which decreased significantly in the first 8 h to less than 2.5 and continued to decrease until it reached a pH value of 1.86 at the end of testing. Naphthalene transformation can be attributed to electrochemically enhanced oxidation at the anolyte by chlorine gas produced by electrolysis.

Electrolysis↗

Effects of naphthalene quinonoids on the induction of oxidative DNA damage and cytotoxicity in calf thymus DNA and in human cultured cells.

The purpose of this study was to examine the differences in the induction of DNA damage and cytotoxic effects by quinonoid derivatives of naphthalene in calf thymus DNA (ct-DNA) and in human T47D breast cancer cells. Results indicated that copper(II) and NADPH were essential for causing oxidant-mediated aldehydic DNA lesions (ADLs), including abasic sites and aldehydic base/sugar lesions, in ct-DNA exposed to 1,2-naphthalenediol (NCAT), 1,4-naphthalenediol (NHQ), 1,2-naphthoquinone (1,2-NQ), and 1,4-naphthoquinone (1,4-NQ). The ADLs induced by naphthalene quinonoids in ct-DNA decrease in the rank order NCAT congruent with 1,2-NQ > NHQ >> 1,4-NQ. Results from the analyses in cells indicated that after 1.5-5 h of exposure all naphthalene quinonoids induced a cytotoxic response in T47D cells at concentrations 10-100 microM or above, where NHQ and 1,4-NQ were approximately 5-10 times more efficient than NCAT and 1,2-NQ in the induction of cell death. In addition, NHQ, 1,2-NQ, and 1,4-NQ were not able to produce measurable levels of ADLs in cells at concentrations up to 1.25 mM, whereas NCAT (0.75-1.25 mM) induced a significant increase in the number of ADLs in T47D cells after 1.5 h of exposure when compared to control. The specific type of ADLs induced by NCAT is resistant to cellular excision repair pathway. Results from the measurements of reactive oxygen species (ROS) indicated that all naphthalene quinonoids induced increases in ROS formation in T47D cells. The induction of ROS formation in cells by naphthalene quinonoids decreases in the rank order 1,4-NQ congruent with 1,2-NQ > NHQ > NCAT. Overall, results from our investigation suggest that naphthalene quinonoids cause cell death at concentrations well below the concentrations at which they induce the formation of ADLs, perhaps by altering intracellular redox status.

Aldehydes↗